DRC-2019-014452 - 0901a06880b67a94

ENERGY FUELS
November 4, 2019
Sent VIA OVERNIGHT DELIVERY
Mr. Ty L. Howard
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
Salt Lake City, UT 84116
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600 Lakewood, CO, US, 80228
303 974 2140
www.energyfuels.com
Div of Waste Management
and Radiation Control
NOV -8 2019 17W-2019-n 4452

Re: Transmittal of 3rd Quarter 2019 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Mr. Howard:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 3rd Quarter of
2019 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager

CC: David C. Frydenlund
Paul Goranson
Logan Shumway
Scott Bakken
Terry Slade
November 4, 2019
Sent VIA OVERNIGHT DELIVERY
Mr. Ty L. Howard
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
Salt Lake City, UT 84116
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www .encrgyfuels.com
Re: Transmittal of 3rd Quarter 2019 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Mr. Howard:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 3rd Quarter of
2019 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Paul Goranson
Logan Shumway
Scott Bakken
Terry Slade
White Mesa Uranium Mill
Chloroform Monitoring Report
State of Utah
Stipulation and Consent Order Docket No. UGW-20-01
3rd Quarter
(July through September)
2019
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
November 4, 2019
TABLE OF CONTENTS
1.0 INTRODUCTION ................................................................................................. 1
2.0 CHLOROFORM MONITORING ...................................................................... 1
2.1 Samples and Measurements Taken During the Quarter ..................................... 1
2.1.1 Chloroform Monitoring .............................................................................. L
2.1.2 Parameters Analyzed .................................................................................. 2
2.1.3 Groundwater Head Monitoring ................................................................... 2
2.2 Sampling Methodology and Equipment and Decontamination Procedures ....... 3
2.2.1 Decontamination Procedures ...................................................................... 3
2.2.2 Well Purging and Depth to Groundwater ................................................... 4
2.2.3 Sample Collection ....................................................................................... 5
2.3 Field Data ............................................................................................................ 6
2.4 Depth to Groundwater Data and Water Table Contour Map .............................. 6
2.5 Laboratory Results .............................................................................................. 6
2.5.1 Copy of Laboratory Results ........................................................................ 6
2.5.2 Regulatory Framework ............................................................................... 6
3.0 QUALITY ASSURANCE AND DATA VALIDATION ................................... 6
3.1 Field QC Samples ............................................................................................... 7
3.2 Adherence to Mill Sampling SOPs ..................................................................... 7
3.3 Analyte Completeness Review ........................................................................... 7
3.4 Data Validation ................................................................................................... 8
3.4.1 Field Data QNQC Evaluation .................................................................... 8
3.4.2 Holding Time Evaluation ............................................................................ 9
3.4.3 Receipt Temperature Evaluation ................................................................. 9
3.4.4 Analytical Method Checklist ...................................................................... 9
3.4.5 Reporting Limit Evaluation ........................................................................ 9
3.4.6 Receipt pH Evaluation .............................................................................. 10
3.4.7 Trip Blank Evaluation ............................................................................... 10
3.4.8 QNQC Evaluation for Sample Duplicates ............................................... 10
3.4.9 Rinsate Sample Check .............................................................................. 10
3.4.10 Other Laboratory QNQC ......................................................................... 11
4.0 INTERPRETATION OF DATA ....................................................................... 12
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions ........... 12
4.1.1 Current Site Groundwater Contour Map ................................................... 12
4.1 .2 Comparison of Current Groundwater Contour Maps to Groundwater
Contour Maps for Previous Quarter. ........................................................ 19
4.1.3 Hydrographs .............................................................................................. 20
4.1.4 Depth to Groundwater Measured and Groundwater Elevation ................. 20
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture ............................ 21
4.2 Review of Analytical Results ............................................................................ 25
4.2.1 Current Chloroform Isoconcentration Map .............................................. 25
4.2.2 Chloroform Concentration Trend Data and Graphs .................................. 25
4.2.3 Interpretation of Analytical Data .............................................................. 25
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND
TW4-4 OPERATIONS REPORT ..................................................................... 29
5.1 Introduction ....................................................................................................... 29
5.2 Pump Test Data Collection ............................................................................... 29
5.3 Water Level Measurements .............................................................................. 30
5 .4 Pumping Rates and Volumes ............................................................................ 30
5.5 Mass Removed and Plume Residual Mass ....................................................... 30
5.6 Inspections ........................................................................................................ 31
5. 7 Conditions That May Affect Water Levels in Piezometers .............................. 31
6.0 CORRECTIVE ACTION REPORT ................................................................. 31
6.1 Assessment of Previous Quarter's Corrective Actions ..................................... 31
7.0 CURRENT COMPLIANCE STATUS ............................................................. 32
7 .1 Long Term Chloroform Plume Control ............................................................ 32
7.2 Well Construction, Maintenance and Operation ............................................... 32
7.3 Disposal of Extracted Groundwater. ................................................................. 32
7.4 Compliance Well Performance ......................................................................... 3 2
7 .5 Chloroform Plume Monitoring for Wells within 500 Feet of the Property
Boundary .......................................................................................................... 33
8.0 CONCLUSIONS AND RECOMMENDATIONS ............................................ 33
9.0 ELECTRONIC DATA FILES AND FORMAT .............................................. 38
10.0 SIGNATURE AND CERTIFICATION ........................................................... 39
LIST OF TABLES
Table 1 Summary of Well Sampling for the Period
11
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture
Zone Details Map and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater
Elevations over Time for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells
over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QNQC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank Evaluations
I-7 QNQC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform lsoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs over
Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
Tab N Exceedance Notices for the Reporting Period
iii
1.0 INTRODUCTION
The presence of chloroform was initially identified in groundwater at the White Mesa Mill (the
"Mill") as a result of split sampling performed in May 1999. The discovery resulted in the
issuance of State of Utah Notice of Violation ("NOV") and Groundwater Corrective Action
Order ("CAO") State of Utah Department of Environmental Quality ("UDEQ"), Division of
Waste Management and Radiation Control ("DWMRC") Docket No. UGW-20-01, which
required that Energy Fuels Resources (USA) Inc. ("EFRI") submit a Contamination Investigation
Plan and Report pursuant to the provisions of UAC R317-6-6.15(D). In response to the NOV,
EFRI submitted a series of documents outlining plans for investigation of the chloroform
contamination. This plan of action and preliminary schedule was set out in EFRI submittals
dated: September 20, 1999; June 30, 2000; April 14, 2005; and November 29, 2006. EFRI
submitted a draft Groundwater Corrective Action Plan ("GCAP") dated August 22, 2007. The
draft GCAP was reviewed by the Director, who advised EFRI in 2013 that modifications were
required. In an effort to expedite and formalize active and continued remediation of the
chloroform plume, both parties have agreed to the GCAP found in Attachment 1, of the final
Stipulation and Consent Order ("SCO") dated September 14, 2015.
This is the Quarterly Chloroform Monitoring Report for the third quarter of 2019 as required
under the SCO. This report also includes the Operations Report for MW-04, TW4-0l, TW4-04,
TW4-02, TW4-11, TW4-19, TW4-20, TW4-21, MW-26, TW4-22, TW4-24, TW4-25, TW4-37,
TW4-39, TW4-40, and TW4-41 for the quarter.
2.0 CHLOROFORM MONITORING
2.1 Samples and Measurements Taken During the Quarter
A map showing the location of all groundwater monitoring wells, piezometers, existing wells,
temporary chloroform contaminant investigation wells and temporary nitrate investigation wells
is attached under Tab A. Chloroform samples and measurements taken during this reporting
period are discussed in the remainder of this section.
2.1.1 Chloroform Monitoring
Quarterly sampling for chloroform monitoring parameters is currently required in the following
wells:
MW-4 TW4-9 TW4-18 TW4-27 TW4-36
TW4-1 TW4-10 TW4-19 TW4-28 TW4-37
TW4-2 TW4-11 TW4-20 TW4-29 TW4-38
TW4-3 TW4-12 TW4-21 TW4-30 TW4-39
TW4-4 TW4-13 TW4-22 TW4-31 TW4-40
TW4-5 TW4-14 TW4-23 TW4-32 TW4-41
TW4-6 MW-26 (formerly TW4-15) TW4-24 TW4-33 TW4-42
TW4-7 TW4-16 TW4-25 TW4-34
TW4-8 MW-32 (formerly TW4-17) TW4-26 TW4-35
1
Chloroform monitoring was performed in all of the required chloroform monitoring wells. Table
1 provides an overview of all wells sampled during the quarter, along with the date samples were
collected from each well, and the date(s) when analytical data were received from the contract
laboratory. Table 1 also identifies equipment rinsate samples collected, as well as sample
numbers associated with the deionized field blank ("DIFB") and any required duplicates.
2.1.2 Parameters Analyzed
Wells sampled during this reporting period were analyzed for the following constituents:
• Chloroform
• Chloromethane
• Carbon tetrachloride
• Methylene chloride
• Chloride
• Nitrate plus Nitrite as Nitrogen
Use of analytical methods is consistent with the requirements of the Chloroform Investigation
Monitoring Quality Assurance Program (the "Chloroform QAP") attached as Appendix A to the
White Mesa Uranium Mill Groundwater Monitoring QAP Revision 7.6, dated August 22, 2019.
2.1.3 Groundwater Head Monitoring
Depth to groundwater was measured in the following wells and/or piezometers, pursuant to Part
I.E.3 of the Groundwater Discharge Permit (the "GWDP"):
• The quarterly groundwater compliance monitoring wells
• Existing monitoring well MW-4 and all of the temporary chloroform investigation wells
• Piezometers P-1, P-2, P-3, P-4 and P-5
• MW-20 and MW-22
• Nitrate monitoring wells
• The DR piezometers that were installed during the Southwest Hydrologic Investigation
In addition to the above, depth to water measurements are routinely observed in conjunction with
sampling events for all wells sampled during quarterly and accelerated efforts, regardless of the
sampling purpose.
Weekly and monthly depth to groundwater measurements were taken in the chloroform pumping
wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-ll, TW4-19, TW4-20, TW4-21, TW4-37,
TW4-39, TW4-40, and TW4-41 and the nitrate pumping wells TW4-22, TW4-24, TW4-25, and
TWN-02. In addition, monthly water level measurements were taken in non-pumping wells
MW-27, MW-30, MW-31, TW4-21, TWN-1, TWN-3, TWN-4, TWN-7, and TWN-18.
2
2.2 Sampling Methodology and Equipment and Decontamination Procedures
EFRI completed, and transmitted to DWMRC on May 25, 2006, a revised QAP for sampling
under the Mill's GWDP. While the water sampling conducted for chloroform investigation
purposes has conformed to the general principles set out in the QAP, some of the requirements in
the QAP were not fully implemented prior to DWMRC's approval of the QAP, for reasons set
out in correspondence to DWMRC dated December 8, 2006. Subsequent to the delivery of the
December 8, 2006 letter, EFRI discussed the issues brought forward in the letter with DWMRC
and has received correspondence from DWMRC about those issues. In response to DWMRC's
letter and subsequent discussions with DWMRC, EFRI modified the chloroform Quality
Assurance ("QA") procedures within the Chloroform QAP. The Chloroform QAP describes the
requirements of the chloroform investigation program and identifies where they differ from the
Groundwater QAP. On June 20, 2009 the Chloroform QAP was modified to require that the
quarterly chloroform reports include additional items specific to EFRI's ongoing pump testing
and chloroform capture efforts. The Groundwater QAP as well as the Chloroform QAP were
revised again on June 6, 2012, August 15, 2017, July 23, 2018, May 14, 2019, and August 22,
2019. The revised Groundwater QAP and Chloroform QAP, Revision 7.6 were approved by
DWMRC on September 10, 2019.
The sampling methodology, equipment and decontamination procedures used in the chloroform
contaminant investigation, as summarized below, are consistent with the approved QAP and the
Chloroform QAP.
2.2.1 Decontamination Procedures
Non-dedicated sampling equipment is decontaminated prior to use as described in the DWMRC-
approved QAP and as summarized below.
The water level meter is decontaminated with a detergent/deionized ("DI") water mixture by
pouring the solutions over the water level indicator. The water level meter is then rinsed with DI
water.
The field measurement instrument probe is decontaminated by rinsing with DI water prior to
each calibration. The sample collection cup is washed with a detergent/DI water solution and
rinsed with fresh DI water prior to each calibration.
The non-dedicated purging pump is decontaminated after each use and prior to use at subsequent
sampling locations using the following procedures:
a) the pump is submerged into a 55-gallon drum of nonphosphate detergent/DI water mixture;
b) the detergent/DI water solution is pumped through the pump and pump outlet lines into the
drain line connected to Cell 1;
c) the pump is submerged into a 55-gallon drum of DI water;
3
d) the DI water solution is pumped through the pump and pump outlet lines into the drain line
connected to Cell 1 ;
2.2.2 Well Purging and Depth to Groundwater
The non-pumping wells are purged prior to sampling by means of a portable pump. A list of the
wells in order of increasing chloroform concentration is generated quarterly. The order for
purging the non-pumping wells is thus established. The list is included with the Field Data
Worksheets under Tab B. Mill personnel start purging with all of the non-detect wells and then
move to the wells with detectable chloroform concentrations staring with the lowest
concentration and proceeding to the wells with the highest concentration. One deviation to this
practice is made for the continuously pumping well . The e well are ampled throughout the
sampling event and are not sampled in the order of contamination. Thi practice does not affect
the samples for this reason: the pumping wells have dedicated pomp and there will be no cro -
contamination resulting from the sampling order.
Samples are collected by means of disposable bailer(s) the day following the purging. The
disposable bailer is used only for the collection of a sample from an individual well and disposed
subsequent to the sampling. As noted in the approved QAP, sampling will generally follow the
same order as purging; however; the sampling order may deviate slightly from the generated list.
This practice does not affect the samples for these reasons: any wells sampled in slightly
different order either have dedicated pumps or are sampled via a disposable bailer. This practice
does not affect the quality or usability of the data as there will be no cross-contamination
resulting from the sampling order.
Before leaving the Mill office, the portable pump and hose are rinsed with DI water. Where
portable (non-dedicated) sampling equipment is used, a rinsate sample i collected at a frequency
of one rinsate sample per 20 field sample . Well depth measurement · are taken and the one
casing volume is calculated for those wells which do not have a dedicated pump a de cribed in
Attachment 2-3 of the QAP. Purging is completed to remove stagnant water from the casing and
to assure that representative samples of formation water are collected for analysis. There are
three purging strategies that are used to remove stagnant water from the casing during
groundwater sampling at the Mill. The three strategies are as follows:
1. Purging three well casing volumes with a single measurement of field parameters
specific conductivity, turbidity, pH, redox potential, Dissolved Oxygen ("DO") and water
temperature
2. Purging two casing volumes with stable field parameters for specific conductivity,
turbidity, pH, redox potential, DO, and water temperature (within 10% Relative Percent
Difference ["RPD"])
3. Purging a well to dryness and stability (within 10% RPD) of field parameters for pH,
specific conductivity, and water temperature only after recovery
If the well has a dedicated pump, it is pumped on a set schedule per the remediation plan and is
considered sufficiently evacuated to immediately collect a sample; however, if a pumping well
has been out of service for 48 hours or more, EFRI will follow the purging requirements outlined
in Attachment 2-3 of the QAP. The dedicated pump is used to collect parameters and to collect
4
the samples as described below. If the well does not have a dedicated pump, a Grundfos pump
(9 -10 gpm pump) is then lowered to the screened interval in the well and purging is started.
The purge rate is measured for the well by using a calibrated 5 gallon bucket. This purging
process is repeated at each well location moving from least contaminated to the most
contaminated well. All wells are capped and secured prior to leaving the sampling location.
Wells with dedicated pumps are sampled when the pump is in the pumping mode. If the pump is
not pumping at the time of sampling, it is manually switched on by the Mill Personnel. The well
is pumped for approximately 5 to 10 minutes prior to the collection of the field parameters. Per
the approved QAP, one set of parameters is collected. Samples are collected following the
measurement of one set of field parameters. After sampling, the pump is turned off and allowed
to resume its timed schedule.
2.2.3 Sample Collection
Prior to sampling, a cooler with ice is prepared. The trip blank is also gathered at that time (the
trip blank for these events is provided by the analytical laboratory). Once Mill Personnel arrive
at the well sites, labels are filled out for the various sample to be collected. All personnel
involved with the collection of water and samples are then outfitted with disposable gloves.
Chloroform investigation samples are collected by means of disposable hailers.
Mill personnel use a disposable bailer to sample each well that does not have a dedicated pump.
The bailer is attached to a reel of approximately 150 feet of nylon rope and then lowered into the
well. After coming into contact with the water, the bailer is allowed to sink into the water in
order to fill. Once full, the bailer is reeled up out of the well and the sample bottles are filled as
follows:
• Volatile Organic Compound ("VOC") samples are collected first. This sample consists
of three 40 ml vials provided by the Analytical Laboratory. The VOC sample is not
filtered and is preserved with HCl;
• A sample for nitrate/nitrite is then collected. This sample consists of one 250 ml. bottle
that is provided by the Analytical Laboratory. The nitrate/nitrite sample is not filtered
and is preserved with H2S04;
• A sample for chloride is then collected. This sample consists of one 500 ml. bottle that is
provided by the Analytical Laboratory. The chloride sample is not filtered and is not
chemically preserved.
After the samples have been collected for a particular well, the bailer is disposed of and the
samples are placed into the cooler that contains ice. The well is then recapped and Mill personnel
proceed to the next well.
5
2.3 Field Data
Attached under Tab B are copies of the Field Data Worksheets that were completed during the
quarter for the chloroform contaminant investigation monitoring wells identified in paragraph
2.1.1 above, and Table 1.
2.4 Depth to Groundwater Data and Water Table Contour Map
Attached under Tab C are copies of the Depth to Water Sheets for the weekly monitoring of
MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22, TW4-
24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41 and TWN-2 as well as the monthly depth to
groundwater data for the chloroform contaminant investigation wells and the non-pumped wells
measured during the quarter. Depth to groundwater measurements that were utilized for
groundwater contours are included on the Quarterly Depth to Water Worksheet at Tab D of this
report, along with the kriged groundwater contour map for the current quarter generated from
this data. A copy of the kriged groundwater contour map generated from the previous quarter's
data is provided under Tab E.
2.5 Laboratory Results
2.5.1 Copy of Laboratory Results
All analytical results were provided by American West Analytical Laboratory ("AWAL"). Table
1 lists the dates when analytical results were reported to the QA Manager for each sample.
Results from the analyses of samples collected for this quarter's chloroform contaminant
investigation are provided under Tab Hof this Report. Also included under Tab Hare the results
of the analyses for duplicate samples, the DIFB, and rinsate samples for this sampling effort, as
identified in Table 1, as well as results for trip blank analyses required by the Chloroform QAP.
2.5.2 Regulatory Framework
As discussed in Section 1.0, above, the SCO triggered a series of actions on EFRI's part. In
addition to the monitoring program, EFRI has equipped one nitrate well and fifteen chloroform
wells with pumps to recover impacted groundwater, and has initiated recovery of chloroform
from the perched zone.
Sections 4 and 5, below, interpret the groundwater level and flow information, contaminant
analytical results, and pump test data to assess effectiveness of EFRI' s chloroform capture
program.
3.0 QUALITY ASSURANCE AND DATA VALIDATION
The QA Manager performed a QA/Quality Control ("QC") review to confirm compliance of the
monitoring program with requirements of the QAP. As required in the QAP, data QA includes
preparation and analysis of QC samples in the field, review of field procedures, an analyte
completeness review, and QC review of laboratory methods and data. Identification of field QC
6
samples collected and analyzed is provided in Section 3.1. Discussion of adherence to Mill
sampling Standard Operating Procedures ("SOPs") is provided in Section 3.2. Analytical
completeness review results are provided in Section 3.3. The steps and tests applied to check
laboratory data QA/QC are discussed in Sections 3.4.4 through 3.4.9 below.
The analytical laboratory has provided summary reports of the analytical QA/QC measurements
necessary to maintain conformance with National Environmental Laboratory Accreditation
Conference ("NELAC") certification and reporting protocol. The Analytical Laboratory QA/QC
Summary Reports, including copies of the Mill's Chain of Custody and Analytical Request
Record forms for each set of Analytical Results, follow the analytical results under Tab H.
Results of the review of the laboratory QA/QC information are provided under Tab I and are
discussed in Section 3.4, below.
3.1 Field QC Samples
The following QC samples were generated by Mill personnel and submitted to the analytical
laboratory in order to assess the quality of data resulting from the field sampling program.
Field QC samples for the chloroform investigation program consist of one field duplicate sample
for each 20 samples, a trip blank for each shipped cooler that contains VOCs, one DIFB and
rinsate samples.
During this quarter, three duplicate samples were collected as indicated in Table 1. The
duplicates were sent blind to the analytical laboratory and analyzed for the same parameters as
the chloroform wells.
Two trip blanks were provided by AW AL and returned with the quarterly chloroform monitoring
samples.
Two rinsate blank samples were collected as indicated on Table 1. Rinsate samples were labeled
with the name of the subsequently purged well with a terminal letter "R" added (e.g. TW4-7R).
The results of these analyses are included with the routine analyses under Tab H.
In addition, one DIFB, while not required by the Chloroform QAP, was collected and analyzed
for the same constituents as the well samples and rinsate blank samples.
3.2 Adherence to Mill Sampling S0Ps
The QA Manager's review of Mill Personnel's adherence to the existing SOPs, confirmed that
the QA/QC requirements established in the QAP and Chloroform QAP were met.
3.3 Analyte Completeness Review
All analyses required by the GCAP for chloroform monitoring for the period were performed.
7
3.4 Data Validation
The QAP and GWDP identify the data validation steps and data QC checks required for the
chloroform monitoring program. Consistent with these requirements, the QA Manager performed
the following evaluations: a field data QNQC evaluation, a holding time check, a receipt
temperature check, an analytical method check, a reporting limit evaluation, a trip blank check, a
QNQC evaluation of sample duplicates, a QC Control Limit check for analyses and blanks
including the DIFB and a rinsate sample check. Each evaluation is discussed in the following
sections. Data check tables indicating the results of each test are provided under Tab I.
3.4.1 Field Data QA/QC Evaluation
The QA Manager performs a review of the field recorded parameters to assess their adherence
with QAP requirements. The assessment involved review of two sources of information: the
Field Data Sheets and the Quarterly Depth to Water summary sheet. Review of the Field Data
Sheets addresses well purging volumes and measurement of field parameters based on the
requirements discussed in section 2.2.1 above. The purging technique employed determines the
requirements for field parameter measurement and whether stability criteria are applied. Review
of the Depth to Water data confirms that all depth measurements used for development of the
groundwater contour maps were conducted within a five-day period as indicated by the
measurement dates in the summary sheet under Tab D. The results of this quarter's review of
field data are provided under Tab I.
Based upon the review of the field data sheets, the purging and field measurements were
completed in conformance with the QAP requirements. A summary of the purging techniques
employed and field measurements taken is described below:
Purging Two Casing VoJome with Stable Field Parameters (within 10% RPD)
Wells TW4-5, TW4-8, TW4-9, TW4-16, MW-32, TW4-18, TW4-23, TW4-32, and TW4-38
were sampled after two casing volumes were removed. Field parameters (pH, specific
conductivity, turbidity, water temperature, DO, and redox potential) were measured during
purging. All field parameters for this requirement were stable within 10% RPD.
Purging a Well to Dryness and Stability of a Limited Li t of Field Parameters
Wells TW4-3, TW4-6, TW4-7, TW4-10, TW4-12, TW4-13, TW4-14, TW4-26, TW4-27, TW4-
28, TW4-29, TW4-30, TW4-31, TW4-33, TW4-34, TW4-35, TW4-36, and TW4-42 were
pumped to dryness before two casing volumes were evacuated. After well recovery, one set of
measurements of pH, conductivity and temperature were taken. The samples were then collected,
and another set of measurements of pH, conductivity and temperature were taken. Stabilization
of pH, conductivity and temperature are required within 10% RPD under the QAP. The QAP
requirements for stabilization were met.
Continuou ly Pumped Wells
Wells MW-4, TW4-1, TW4-2, TW4-4, TW4-11, MW-26, TW4-19, TW4-20, TW4-21, TW4-22,
TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, and TW4-41 are continuously pumped wells.
These wells are pumped on a set schedule per the remediation plan and are considered
sufficiently evacuated to immediately collect a sample.
8
During review of the field data sheets, the QA Manager confirmed that sampling personnel
consistently recorded depth to water to the nearest 0.01 foot.
The review of the field sheets for compliance with QAP requirements resulted in the
observations noted below. The QAP requirements in Attachment 2-3 specifically state that field
parameters must be stabilized to within 10% over at least 2 consecutive measurements for wells
purged to 2 casing volumes or purged to dryness. The QAP Attachment 2-3 states that turbidity
should be less than 5 NTU prior to sampling unless the well is characterized by water that has a
higher turbidity. The QAP Attachment 2-3 does not require that turbidity measurements be less
than 5 NTU prior to sampling. As such, the noted observations below regarding turbidity
measurements greater than 5 NTU are included for information purposes only.
Wells TW4-1, TW4-5, TW4-9, TW4-16, MW-26, MW-32, TW4-18, TW4-19, TW4-22, TW4-
23, TW4-32, TW4-38, TW4-40, and TW4-41 exceeded the QAP's 5 NTU goal. EFRI's letter to
DWMRC of March 26, 2010 discusses fmther why turbidity does not appear to be an appropriate
parameter for assessing well stabilization. In response to DWMRC's subsequent correspondence
dated June 1, 2010 and June 24, 2010, EFRI completed a monitoring well redevelopment
program. The redevelopment report was submitted to DWMRC on September 30, 2011.
DWMRC responded to the redevelopment report via letter on November 15, 2012. Per the
DWMRC letter dated November 15, 2012, the field data generated this quarter are compliant
with the turbidity requirements of the approved QAP.
3.4.2 Holding Time Evaluation
QAP Table 1 identifies the method holding times for each suite of parameters. Sample holding
time checks are provided in Tab I. The samples were received and analyzed within the required
holding times.
3.4.3 Receipt Temperature Evaluation
Chain of Custody sheets were reviewed to confirm compliance with the QAP requirement which
specifies that samples be received at 6°C or lower. Sample temperatures checks are provided in
Tab I. The samples were received within the required temperature limit.
3.4.4 Analytical Method Checklist
The analytical methods reported by the laboratory were checked against the required methods
enumerated in the Chloroform QAP. Analytical method checks are provided in Tab I. The
analytical methods were consistent with the requirements of the Chloroform QAP.
3.4.5 Reporting Limit Evaluation
The analytical method reporting limits reported by the laboratory were checked against the
reporting limits enumerated in the Chloroform QAP. Reporting Limit Checks are provided
under Tab I. The analytes were measured and reported to the required reporting limits; several
sets of sample results had the reporting limit raised for at least one analyte due to matrix
interference and/or sample dilution. In these cases, the reported value for the analyte was higher
9
than the increased detection limit.
3.4.6 Receipt pH Evaluation
Appendix A of the QAP states that volatile samples are required to be preserved and arrive at the
laboratory with a pH less than 2. A review of the laboratory data revealed that the volatile
samples were received at the laboratory with a pH less than 2.
3.4. 7 Trip Blank Evaluation
Trip blank results were reviewed to identify any VOC contamination resulting from transport of
the samples. Trip blank checks are provided in Tab I. All of the trip blank samples were
nondetect.
3.4.8 QA/QC Evaluation for Sample Duplicates
Section 9 .1.4 a) of the QAP states that RPDs will be calculated for the comparison of duplicate
and original field samples. The QAP acceptance limits for RPDs between the duplicate and
original field sample is less than or equal to 20% unless the measured results are less than 5
times the required detection limit. This standard is based on the EPA Contract Laboratory
Program National Functional Guidelines for Inorganic Data Review, February 1994, 9240.1-05-
01 as cited in the QAP. The RPDs are calculated for the duplicate pairs for all analytes
regardless of whether or not the reported concentrations are greater than 5 times the required
detection limits; however, data are considered noncompliant only when the results are greater
than 5 times the reported detection limit and the RPD is greater than 20%. The additional
duplicate information is provided for information purposes.
Duplicate results were within a 20% RPD in the quarterly samples. Duplicate results are included
in Tab I.
3.4.9 Rinsate Sample Check
Rinsate blank sample checks are provided in Tab I. The rinsate blank sample concentration
levels were compared to the QAP requirements i.e., that rinsate sample concentrations be one
order of magnitude lower than that of the actual well.
Rinsate blank sample TW4-03R had a reported chloroform detection of 17.6 ug/L. TW4-03 was
non detect for chloroform. Rinsate blank sample TW 4-16R had a reported chloroform detection
of 19.4 ug/L. TW4-16 had a chloroform detection of 99.8 ug/L. Both rinsate blank results were
outside of acceptance limits for the rinsate blank results.
TW 4-03R was collected after decontamination and prior to the pump being used to collect any
Q3 2019 chloroform samples. Because the pump was not used prior to the rinsate sample
collection, the detection is not the result of cross contamination. TW 4-16R was collected after
the decontamination completed after purging well TW4-9. The rinsate blank was collected prior
to purging TW4-16. TW4-16 had a chloroform detection of 66.0 ug /L. The chloroform detection
of 99.8 ug/L in TW4-16 is within the historic range of detections and is not likely the result of
cross contamination.
10
Prior to the Q3 2019 sampling event EFRI serviced the DI water system and all filters and media
were changed. The DI blank from the on-site DI system which generates the water for rinsate
blank samples was nondetect, but has had reported concentrations in recent quarters. EFRI is
continuing the investigation of the chloroform in the DI samples. The results of this
investigation will be provided in future reports. EFRI is currently contacting the media and filter
provider and looking at plumbing systems to determine if the chloroform is originating within
the physical system.
The data for both TW 4-3 and TW 4-16 are usable as reported. Even if there were contribution of
chloroform to the sample results, it would bias the data high and would result in a more
conservative data application. EFRI does not believe the data quality has been affected.
3.4.10 Other Laboratory QA/QC
Section 9.2 of the QAP requires that the laboratory's QA/QC Manager check the following items
in developing data reports: (1) sample preparation information is correct and complete, (2)
analysis information is correct and complete, (3) appropriate analytical laboratory procedures are
followed, (4) analytical results are correct and complete, (5) QC samples are within established
control limits, (6) blanks are within QC limits, (7) special sample preparation and analytical
requirements have been met, and (8) documentation is complete. In addition to other laboratory
checks described above, EFRI's QA Manager rechecks QC samples and blanks (items (5) and
(6)) to confirm that the percent recovery for spikes and the relative percent difference for spike
duplicates are within the method-specified acceptance limits, or that the case narrative
sufficiently explains any deviation from these limits. Results of this quantitative check are
provided in Tab I.
The lab QA/QC results met these specified acceptance limits except as noted below.
The QAP Section 8.1.2 requires that a Matrix Spike/Matrix Spike Duplicate ("MS/MSD") pair
be analyzed with each analytical batch. The QAP does not specify acceptance limits for the
MS/MSD pair, and the QAP does not specify that the MS/MSD pair be prepared on EFRI
samples only. Acceptance limits for MS/MSDs are set by the laboratories. The review of the
information provided by the laboratories in the data packages verified that the QAP requirement
to analyze an MS/MSD pair with each analytical batch was met. While the QAP does not require
it, the recoveries were reviewed for compliance with the laboratory established acceptance limits.
The QAP does not require this level of review, and the results of this review are provided for
information only.
The information from the Laboratory QA/QC Summary Reports indicates that the MS/MSDs
recoveries and the associated RPDs for the samples were within acceptable laboratory limits for
the regulated compounds. The requirement in the QAP to analyze a MS/MSD pair with each
analytical batch was met and as such the data are compliant with the QAP.
The QAP specifies that surrogate compounds shall be employed for all organic analyses, but the
QAP does not specify acceptance limits for surrogate recoveries. The analytical data associated
with the routine quarterly sampling met the requirement specified in the QAP. The information
11
from the Laboratory QA/QC Summary Reports indicates that the surrogate recoveries for the
quarterly chloroform ample were within acceptable laboratory limits for the surrogate
compounds. The requirement in the QAP to analyze surrogate compounds was met and the data
are compliant with the QAP. Furthermore, there are no QAP requirements for surrogate
recoveries.
The QAP, Section 8.1.2 requires that each analytical batch shall be accompanied by a method
blank. The analytical batches routinely contain a blank, which is a blank sample made and
carried through all analytical steps. For the Mill samples, a method blank was prepared for the
analytical methods. Per the approved QAP, contamination detected in analysis of method blanks
will be used to evaluate any analytical laboratory contamination of environmental samples. The
QAP states that non-conformance conditions will exist when contaminant levels in the
samples(s) are not an order of magnitude greater than the blank result. There were no detections
in the method blanks in this quarter. Method blank results are included in Tab H.
The information from the Laboratory QA/QC Summary Reports indicates that the LCS
recoveries for the samples were within acceptable laboratory limits for the regulated compounds
as indicated in Tab I.
The information from the Laboratory QA/QC Summary Reports indicates that there was a low
Continuing Calibration Verification ("CCV") recovery for chloromethane. The CCV recovery
affected samples TW4-3, TW4-3R, TW4-5, TW4-6, TW4-12, TW4-13, TW4-14, MW-32, TW4-
18, TW4-23, TW4-27, TW4-28, TW4-30, TW4-31, TW4-32, TW4-34, TW4-35, TW4-36, TW4-
38, and TW4-42. The data were flagged in accordance with the changes specified in EPA
Method 8260D. The flagging requirements are new to the revised method and do not adversely
affect the data. The data are usable for the intended purpose because chloromethane is not
frequently detected in non-pumping wells; all of the wells listed above are non-pumping wells.
Further, the wells listed above do not have recent historical detections of chloromethane and the
nondetect data are likely accurate.
4.0 INTERPRETATION OF DATA
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.
4.1.1 Current Site Groundwater Contour Map
The water level contour maps (See Tab D) indicate that perched water flow ranges from
generally southwesterly beneath the Mill site and tailings cells to generally southerly along the
eastern and western margins of White Mesa south of the tailings cells.
Perched water mounding associated with the wildlife ponds locally changes the generally
southerly perched water flow patterns. For example, northeast of the Mill site, mounding
associated with formerly used wildlife ponds is still evident and disrupts the generally
southwesterly flow pattern, to the extent that locally northerly flow occurs near MW-19 and
PIEZ-1. The impact of the mounding associated with the northern ponds, to which water has not
been delivered since March 2012, is diminishing and is expected to continue to diminish as the
12
associated mound decays due to reduced recharge. The perched groundwater mound associated
with the southern wildlife pond is also diminishing due to reduced recharge at that location.
Not only has recharge from the wildlife ponds impacted perched water elevations and flow
directions at the site, but the cessation of water delivery to the northern ponds, which are
generally upgradient of the nitrate and chloroform plumes at the site, resulted in changing
conditions that were expected to impact constituent concentrations and migration rates within the
plumes. Specifically, past recharge from the northern ponds helped limit many constituent
concentrations within the plumes by dilution while the associated groundwater mounding
increased hydraulic gradients and contributed to plume migration. Since use of the northern
ponds was discontinued in March 2012, increases in constituent concentrations in many wells,
and decreases in hydraulic gradients within the plumes, are attributable to reduced recharge and
the decay of the associated groundwater mound. EFRI and its consultants anticipated these
changes and discussed these and other potential effects with DWMRC in March 2012 and May
2013.
The impacts associated with cessation of water delivery to the northern ponds were expected to
propagate downgradient (south and southwest) over time. Wells close to the ponds were
generally expected to be impacted sooner than wells farther downgradient of the ponds.
Therefore, constituent concentrations were generally expected to increase in downgradient wells
close to the ponds before increases were detected in wells farther downgradient of the ponds.
Although such increases were anticipated to result from reduced dilution, the magnitude and
timing of the increases were anticipated to be and have been difficult to predict due to the
complex permeability distribution at the site and factors such as pumping and the rate of decay of
the groundwater mound. Because of these complicating factors, some wells completed in higher
permeability materials were expected to be impacted sooner than other wells completed in lower
permeability materials even though the wells completed in lower permeability materials were
closer to the ponds.
In general, chloroform and nitrate concentrations within and in the vicinity of the chloroform
plume appear to have been impacted to a greater extent than nitrate concentrations within and
adjacent to the nitrate plume. This behavior is reasonable considering that the chloroform plume
is generally more directly downgradient of and more hydraulically connected (via higher
permeability materials) to the northern wildlife ponds.
In addition, the southern wildlife pond is in relatively close proximity to the downgradient
(southern) extremity of the chloroform plume. Reduced recharge at the southern pond, and decay
of the associated groundwater mound, can be expected to impact water level behavior and
chloroform and nitrate concentrations in wells within this portion of the chloroform plume.
Localized increases in concentrations of constituents such as chloroform and nitrate within and
near the chloroform plume, and of nitrate and chloride within and near the nitrate plume, may
occur even when these plumes are under control. Ongoing mechanisms that can be expected to
increase constituent concentrations locally as a result of reduced wildlife pond recharge include
but are not limited to:
13
1) Reduced dilution -the m1xmg of low constituent concentration pond recharge into
existing perched groundwater will be reduced over time.
2) Reduced saturated thicknesses -dewatering of higher permeability layers rece1vmg
primarily low constituent concentration pond water will result in wells intercepting these
layers receiving a smaller proportion of the low constituent concentration water.
The combined impact of the above two mechanisms was anticipated to be more evident at
chloroform pumping wells MW-4, MW-26, TW4-4, TW4-19, and TW4-20; nitrate pumping
wells TW4-22, TW4-24, TW4-25, and TWN-2; and non-pumped wells adjacent to the pumped
wells. hnpacts were also expected to occur over time at wells subsequently added to the
chloroform pumping network: TW4-1, TW4-2, TW4-ll, TW4-21 and TW4-37 (added during
2015); TW4-39 (added during the fourth quarter of 2016); TW4-41 (added during the second
quarter of 2018); and TW4-40 (added during the second quarter of 2019). The overall impact
was expected to be generally higher constituent concentrations in these wells over time until
mass reduction resulting from pumping and natural attenuation eventually reduces
concentrations. Short-term changes in concentrations at pumping wells and wells adjacent to
pumping wells are also expected to result from changes in pumping conditions.
In addition to changes in the flow regime caused by wildlife pond recharge, perched flow
directions are locally influenced by operation of the chloroform and nitrate pumping wells. Well
defined cones of depression were typically evident in the vicinity of all chloroform pumping
wells except TW4-4 and TW4-37, which began pumping in the first quarter of 2010 and the
second quarter of 2015, respectively. The third quarter of 2018 was the first quarter that a well-
defined cone of depression was associated with TW4-4, primarily the result of pumping at
adjacent well TW4-41.
The lack of well-defined capture associated with chloroform pumping well TW4-4 was
consistent prior to the third quarter of 2018, even though pumping since the first quarter of 2010
has depressed the water table in the vicinity of this well. The lack of a well-defined cone of
depression near TW4-4 likely resulted from 1) variable permeability conditions in the vicinity of
TW 4-4, and 2) historical relatively low water levels at adjacent well TW 4-14.
Nitrate pumping wells TW4-22, TW4-24, TW4-25, and TWN-2 started pumping during the first
quarter of 2013. By the fourth quarter of 2013, operation of the nitrate pumping system had
produced well-defined impacts on water levels. Water level impacts of the nitrate and chloroform
pumping systems overlap; however the long-term interaction between the nitrate and chloroform
pumping systems is evolving, and changes will be reflected in data collected during routine
monitoring.
Water level patterns near nitrate pumping wells are expected to be influenced by the presence of,
and the decay of, the groundwater mound associated with the northern wildlife ponds, and by the
historically relatively low water level at TWN-7. Since 2012, water levels in TWN-7 have risen
while water levels in nearby wells have generally dropped due to pumping and the decay of the
northern groundwater mound. These factors have reduced water level differences between TWN-
7 and nearby wells.
14
As discussed above, variable permeability conditions likely contributed to the lack of a well-
defined cone of depression near chloroform pumping well TW4-4. Changes in water levels at
wells immediately south and southeast ( downgradient) of TW 4-4 resulting from TW 4-4 pumping
were expected to be muted because TW4-4 is located at a transition from relatively high to
relatively low permeability conditions south and southeast of TW4-4. As will be discussed
below, the permeability of the perched zone at TW4-6, TW4-26, TW4-29, TW4-30, TW4-31,
TW4-33, TW4-34, and TW4-35 is one to two orders of magnitude lower than at TW4-4, and the
permeability at TW4-27 is approximately three orders of magnitude lower than at TW4-4.
Detecting water level drawdowns in wells immediately south and southeast of TW4-4 resulting
from TW4-4 pumping has also been complicated by a general, long-term increase in water levels
in this area that has been attributable to past wildlife pond recharge. Between the fourth quarter
of 2007 and the fourth quarter of 2009 (just prior to the start of TW 4-4 pumping), water levels at
TW4-4 and TW4-6 increased by nearly 2.7 and 2.9 feet at rates of approximately 1.2 feet/year
and 1.3 feet/year, respectively. However, between the start of pumping at TW4-4 (first quarter of
2010) and the fourth quarter of 2013, the rate of increase in water levels at TW4-6 was reduced
to less than 0.5 feet/year suggesting that TW 4-6 is within the hydraulic influence of TW 4-4.
Water levels in all wells currently within the chloroform plume south of TW4-4 (TW4-26, TW4-
29, TW4-33 and TW4-40) are trending generally downward. The downward trend is evident at
TW4-26, TW4-29 and TW4-33 since the fourth quarter of 2013, and at TW4-40 since
installation in the first quarter of 2018. The water level in TW4-6 (remaining just outside the
plume again this quarter) has also trended downward since the fourth quaiter of 2013.
Downward trends are attributable to both the cessation of water delivery to the wildlife ponds
and pumping. Although water levels at some of the wells marginal to the chloroform plume such
as TW4-14, TW4-27, TW4-30 and TW4-31 were generally increasing until about the first
quarter of 2018, these water levels now appear to be relatively stable.
These spatially variable water level trends likely result from pumping conditions, the
permeability distribution, and distance from the wildlife ponds. Wells that are relatively
hydraulically isolated (due to completion in lower permeability materials or due to intervening
lower permeability materials) and that are more distant from pumping wells and the wildlife
ponds, are expected to respond more slowly to pumping and reduced recharge than wells that are
less hydraulically isolated and are closer to pumping wells and the wildlife ponds. Wells that are
more hydraulically isolated will also respond more slowly to changes in pumping.
The previous lack of a well-defined cone of depression associated with TW4-4 was also
influenced by the historically relatively low water level at non-pumping well TW 4-14, located
east of TW4-4 and TW4-6. Prior to 2018, although water level differences among these three
wells had diminished, and TW4-4 has been pumping since 2010, the water level at TW4-14 was
typically lower than the water level at TW4-6 and lower to an even greater extent than the water
level at TW 4-4. For the current quarter, as during the previous quarter, the water level at TW 4-
14 is higher than water levels at both TW4-4 and TW4-6: the water level at TW4-14
(approximately 5535.2 feet above mean sea level ["ft amsl"]) is nearly 3 feet higher than the
water level at TW4-6 (approximately 5532.3 ft amsl), and 8 feet higher than the water level at
TW4-4 (approximately 5527.2 ft amsl). This pattern is attributable to the cone of depression
induced by pumping both TW 4-4 and TW 4-41.
15
The static water levels at wells TW4-14 and downgradient well TW4-27 (installed south of
TW4-14 in the fourth quarter of 2011) were similar (within 1 to 2 feet) until the third quarter of
2014; both appeared anomalously low. TW4-27 was positioned at a location considered likely to
detect any chloroform present and/or to bound the chloroform plume to the southeast and east
(respectively) of TW4-4 and TW4-6. As will be discussed below, groundwater data collected
since installation indicates that TW4-27 does indeed bound the chloroform plume to the
southeast and east of TW4-4 and TW4-6 (respectively); however, chloroform exceeding 70 µg/L
has been detected at more recently installed temporary perched wells TW4-29 (located south of
TW4-27) and TW4-33 (located between TW4-4 and TW4-29).
Prior to the installation of TW4-27, the persistently low water level at TW4-14 was considered
anomalous because it appeared to be downgradient of all three wells TW 4-4, TW 4-6, and TW 4-
26, yet chloroform had not been detected at TW4-14. Chloroform had apparently migrated from
TW4-4 to TW4-6 and from TW4-6 to TW4-26. This suggested that TW4-26 was actually
downgradient of TW4-6, and TW4-6 was actually downgraclient of TW4-4, regardless of the
flow direction implied by the relatively low water level at TW4-14. The water level at TW4-26
(5531 ft. amsl) is, however, lower than water levels at adjacent wells TW4-6 (5532.3 ft. amsl)
and TW4-23 (5534 ft. amsl), as shown in the detail water level map under Tab C.
Hydraulic tests indicate that the permeability at TW4-27 i an order of magnitude lower than at
TW4-6 and three orders of magnitude lower than at TW4-4 ( ee Hydro Geo Chem Inc. [HGC]
September 20, 2010: Hydraulic Testing of TW4-4 TW4-6 and TW4-26, White Me a Uranium
Mill, July 2010; and HGC, November 28, 2011: Installation, Hydraulic Testing, and Perched
Zone Hydrogeology of Perched Monitoring Well TW4-27, White Mesa Uranium Mill Near
Blanding, Utah). Past similarity of water levels at TW4-14 and TW4-27, and the low
permeability estimate at TW4-27, suggested that both wells were completed in materials having
lower permeability than nearby wells. The low permeability condition likely reduced the rate of
long-term water level increase at TW4-14 and TW4-27 compared to nearby wells, yielding water
levels that appeared anomalously low. This behavior is consistent with hydraulic test data
collected from more recently installed wells TW4-29, TW4-30, TW4-31, TW4-33, TW4-34 and
TW4-35, which indicate that the permeability of these wells is one to two orders of magnitude
higher than the permeability of TW4-27 ( ee: HGC, January 23 2014, Contamination
Investigation Report, TW4-12 and TW4-27 Area White Me a Uranium Mill Near Blanding,
Utah; and HGC, July 1, 2014, Installation and Hydraulic Te ting of TW4-35 and TW4-36,
White Mesa Uranium Mill Near Blanding, Utah [As-Built Report]). Hydraulic tests also indicate
that the permeability at TW4-36 is slightly higher than but comparable to the low permeability at
TW4-27, suggesting that TW4-36, TW4-14 and TW4-27 are completed in a continuous low
permeability zone.
The current quarterly water level at TW4-27 (approximately 5529.2 ft. amsl) is nearly 6 feet
lower than the water level at TW4-I4 (5535.2 ft. amsl). Increases in water level differences
between TW4-14 and TW4-27 since 2013 are attributable to more rapid increases in water levels
at TW4-14 compared to TW4-27. This behavior likely results primarily from: the relative
positions of the wells; past water delivery to the northern wildlife ponds; and the permeability
distribution. Past seepage from the ponds caused propagation of water level increases in all
16
directions including downgradient to the south. The relative hydraulic isolation of TW4-14 and
TW4-27 delayed responses at these locations. Until pumping started at TW4-41, water levels at
both these wells were consistently lower than in surrounding higher permeability materials even
though water levels in surrounding materials were generally decreasing due to reduced pond
seepage and pumping. Although water levels at TW4-14 and TW4-27 appear to have stabilized,
the previous rate of increase was higher at TW4-14 due to factors that include: closer proximity
to the northern pond seepage source; and a smaller thickness of low permeability materials
separating TW 4-14 from surrounding higher permeability materials. In addition, hydraulic
gradients between TW4-14 and surrounding higher permeability materials were relatively large
and were directed toward TW 4-14 prior to TW 4-41 pumping. Slowing of the rates of water level
increase at TW4-14 (since 2015) and TW4-27 (since early 2014), and stabilization since about
the first quarter of 2018, are attributable to changes in hydraulic gradients between these wells
and surrounding higher permeability materials.
In addition, water levels in this area are affected by reduced recharge at the southern wildlife
pond and the decay of the associated groundwater mound. The decay of the mound is expected to
contribute to changes in hydraulic gradients between the low permeability materials penetrated
by TW4-14 and TW4-27 and the surrounding higher permeability materials. Because TW4-27 is
closer to the southern wildlife pond than TW 4-14, changes in hydraulic gradients attributable to
decay of the southern groundwater mound are expected to impact TW 4-27 sooner and to a
greater extent than TW 4-14, consistent with the lower rate of increase in water levels at TW 4-27,
and the earlier reduction in the rate of increase (since early 2014) as discussed above).
The low permeability at TW4-14 and TW4-27 is expected to retard the transpo11 of chloroform
to these wells (compared to nearby wells). As will be discussed in Section 4.2.3, TW4-14 and
TW4-27 remain outside the plume with current quarter chloroform concentrations of
approximately 6.1 µg/L and 7.6 µg/L, respectively.
Chloroform exceeding 70 µg/L detected at TW4-29 and TW4-33 since their installation in 2013
indicates that, in addition to migrating south from TW4-4 to TW4-6 and TW4-26, chloroform
also migrated along a relatively narrow path to the southeast from the vicinity of TW 4-4 to TW 4-
33 then TW4-29. Such migration was in a direction nearly cross-gradient with respect to the
direction of groundwater flow implied by the historic groundwater elevations in this area, which,
until about 2014, placed TW4-14 almost directly downgradient of TW4-4. Such migration was
historically possible because the water levels at TW4-29 were lower than the water levels at
TW4-4 (and TW4-6). The permeability and historic water level distributions are generally
consistent with the apparent nearly cross-gradient migration of chloroform from TW4-4 around
the low permeability zone defined by TW4-36, TW4-14, and TW4-27.
Chloroform during the current quarter was detected at approximately 34.8 µg/L at TW4-30
(located east and cross-to downgradient of TW4-29), and was not detected at wells TW4-31
(located east of TW4-27), TW4-34 (located south and cross-gradient of TW4-29), nor TW4-35
(located southeast and generally downgradient of TW4-29).
Data from wells within and adjacent to the southern portion of the chloroform plume indicate
that:
17
1. Chloroform exceeding 70 µg/L at TW4-29 is bounded by concentrations below 70 µg/L at
wells TW4-6, TW4-23, TW4-27, TW4-30, TW4-34, TW4-35 and TW4-42. TW4-30 is
cross-to downgradient of TW4-29; TW4-6 and TW4-23 are generally cross-to
upgradient of TW4-29; TW4-27, TW4-34 and TW4-42 are generally cross-gradient of
TW4-29; and TW4-35 is generally downgradient of TW4-29.
2. Chloroform concentrations at TW4-33 that are lower than concentrations at TW4-29, and
the likelihood that a pathway exists from TW4-4 to TW4-33 to TW4-29, suggest that
concentrations in the vicinity of TW4-33 were likely higher prior to initiation of TW4-4
pumping, and that lower concentrations currently detected at TW4-33 are due to its closer
proximity to TW 4-4.
3. Chloroform concentrations at TW4-26 exceeded 70 µg/L for the first time during the
second quarter of 2017. Chloroform at TW4-26 is bounded by concentrations below 70
µg/L at TW4-6 and TW4-23 (located up-to cross-gradient of TW4-26); and at TW4-34
(located cross-to downgradient of TW4-26). Chloroform has not been detected at either
TW4-23 or TW4-34. Although chloroform exceeding 70 µg/L was detected at well TW4-
40, installed approximately 200 feet south of TW4-26 in February, 2018, chloroform has
not been detected at TW4-42, installed approximately 200 feet south of TW4-40 in April,
2019. TW4-42 is generally downgradient of both TW4-26 and TW4-40 and bounds the
chloroform plume to the south.
Eventually, TW4-4 pumping, enhanced by operation of adjacent pumping well TW4-41, is likely
to reduce chloroform at both TW4-33 and TW4-29 by cutting off the source. The decrease at
TW4-33 is expected to be faster than at TW4-29 because TW4-33 is in closer proximity to TW4-
4 pumping. Such behavior is expected by analogy with the temporary decreases in chloroform
concentrations that occurred at TW4-6 and TW4-26 once TW4-4 pumping began (discussed in
Section 4.2.3). Since installation in 2013, however, concentrations at TW4-33 appear to be
relatively stable; since the third quarter of 2014, concentrations at TW4-29 appear to be
generally increasing.
Relatively stable chloroform at TW4-33 and generally increasing concentrations at TW4-29
suggest that chloroform migration has been arrested at TW4-33 by TW4-4 (and TW4-41)
pumping and that increasing chloroform at downgradient well TW4-29 results from a remnant of
the plume that continues to migrate downgradient (generally toward TW 4-30, which bounds the
plume to the east). The influence of TW4-4 pumping at the distal end of the plume is consistent
with generally decreasing water levels at both TW4-29 and TW4-33. Pumping at TW4-41 since
the second quarter of 2018 is expected to help maintain or enhance this decline.
Decreasing water level trends are also consistent with reduced wildlife pond seepage. The decay
of the groundwater mound associated with the southern wildlife pond, which is 3 to 4 times
closer to the southern extremity of the chloroform plume than the northern ponds, is expected to
impact water levels within and adjacent to this portion of the plume. Reduced wildlife pond
seepage, in particular, reduced seepage from the southern wildlife pond, likely contributes to
decreasing water level trends (since about the fourth quarter of 2013), and increased
concentrations (since the first quarter of 2014 and the third quarter of 2016, respectively) at
TW4-6 and TW4-26.
18
As the groundwater mound associated with the southern pond decays, groundwater flow
directions in the southern extremity of the plume are likely to become more southerly, and plume
migration is likely to turn more to the south. An increasingly southerly direction of plume
migration is consistent with increased concentrations at TW 4-26.
In addition, generally decreasing concentrations at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 since the third quarter of 2016, suggest that TW4-
4 pumping has arrested chloroform migration between TW 4-4 and TW 4-6, and that increased
chloroform at TW4-26 results from a remnant of the plume that continues to migrate south from
TW4-6 to TW4-26. The enhancement of pumping in the vicinity of TW4-4 by the start-up of
TW4-41 pumping in the second quarter of 2018 is likely to increase this apparent separation and
to have resulted in concentrations at TW 4-6 dropping below 70 µg/L after the second quarter of
2018. Fmthermore, the initiation of pumping at TW4-40 during the second quarter of 2019 is
expected to reduce or prevent chloroform migration to the south of TW 4-40.
Detectable chloroform concentrations at TW 4-14 ( since the fomth quarter of 2014) and TW 4-27
(since the third quarter of 2015) suggest ongoing, but slow, downgradient migration of
chloroform from the southeastern extremity of the plume (near TW4-29 and TW4-33) into the
low permeability materials penetrated by TW4-14 and TW4-27. Pumping at TW4-41 is expected
to reduce or prevent future migration of chloroform toward these wells.
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater Contour
Maps for Previous Quarter
The groundwater contour map for the Mill site for the second quarter of 2019, as submitted with
the Chloroform Monitoring Report for the second quarter of 2019, is attached under Tab E. A
comparison of the water table contour maps for the current quarter (third quarter of 2019) to the
water table contour maps for the previous quarter (second quarter of 2019) indicates the
following: water level changes at the majority of site wells were small ( < Hoot); water level
contours have not changed significantly except in the vicinities of many of the nitrate and
chloroform pumping wells. Overall, total pumping capture is smaller than last quarter.
Drawdown patterns and overall capture associated with pumping of the original chloroform
pumping wells MW-4, MW-26, and TW4-19 have changed as additional groups of wells have
been added to the pumping network. A large expansion in capture occurred within a year of the
initiation of pumping at nitrate pumping wells TW4-22, TW4-24, TW4-25, and TWN-2 in the
first quarter of 2013. Additional large expansions occurred once chloroform pumping wells
TW4-1, TW4-2, TW4-11 , TW4-21 and TW4-37 became operational in 2015, and once TW4-39
became operational in the fourth quarter of 2016. Significant expansion of capture to the south
has resulted from pumping of TW4-41 since the second quarter of 2018 and from initiation of
pumping at TW 4-40 during the second quarter of 2019.
The drawdowns at chloroform pumping wells TW4-19 and TW4-37; and nitrate pumping well
TWN-2 increased by more than 2 feet this quarter. However drawdowns at chloroform pumping
wells MW-4, TW4-21 and TW4-41; and nitrate pumping wells TW4-22 and TW4-24 decreased
by more than 2 feet this quarter. Water level changes at other nitrate and chloroform pumping
19
wells were 2 feet or less, although both increases (decreases in drawdown) and decreases
(increases in drawdown) occurred. Water level fluctuations at pumping wells typically occur in
part because of fluctuations in pumping conditions just prior to and at the time the measurements
are taken. The reported water level for chloroform pumping well TW 4-11 is below the depth of
the Brushy Basin contact this quarter. Although both increases and decreases in drawdown
occurred in pumping wells, the overall apparent capture area of the combined pumping system is
smaller than last quarter.
As discussed in Section 4.1.1, pumping at chloroform well TW4-4, which began in the first
quarter of 2010, depressed the water table near TW4-4, but a well-defined cone of depression
was not clearly evident until the third quarter of 2018, likely due to variable permeability
conditions near TW4-4 and the historically relatively low water level at adjacent well TW4-14.
The expanded cone of depression associated with TW 4-4 and adjacent pumping well TW 4-41
since the initiation of pumping at TW4-41 in the second quarter of 2018 has contributed to
southerly expansion of total pumping system capture. As discussed above, southerly expansion
of capture was additionally enhanced in the second quarter of 2019 by the initiation of pumping
at TW4-40.
Reported water level decreases of up to 0.28 feet at Piezometers 1 through 3A may result from
cessation of water delivery to the northern wildlife ponds as discussed in Section 4.1.1 and the
consequent continuing decay of the associated perched water mound. Reported water level
decreases of up to 0.15 feet at Piezometers 4 and 5 likely result primarily from reduced recharge
at the southern wildlife pond. Reported water level decreases of approximately 0.06 and 0.01
feet, respectively, at TWN-1 and TWN-4 are consistent with continuing decay of the northern
groundwater mound.
The reported water level at MW-20 increased by approximately 2 feet, partly compensating for
the decrease reported last quarter. Water level variability at MW-20 likely results from low
permeability and variable intervals between purging/sampling and water level measurement.
Measurable water was not reported at DR-22. Although DR-22 is typically dry, measurable
water was reported in the bottom of its casing between the second quarter of 2015 and the third
quarter of 2016.
4.1.3 Hydrographs
Attached under Tab F are hydrographs showing groundwater elevation in each chloroform
contaminant investigation monitor well over time.
4.1.4 Depth to Groundwater Measured and Groundwater Elevation
Attached under Tab F are tables showing depth to groundwater measured and groundwater
elevation over time for each of the wells listed in Section 2.1.1 above.
20
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture
Perched water containing chloroform has been removed from the subsurface by operating
chloroform pumping wells MW-4, MW-26 and TW4-19 since 2003; TW4-20 since 2005; TW4-
4 since 2010; TW4-1, TW4-2, TW4-11, TW4-21 and TW4-37 since 2015; TW4-39 since the
fourth quarter of 2016; TW4-41 since the second quarter of 2018; and TW4-40 since the second
quarter of 2019. The primary purpose of the pumping is to reduce total chloroform mass in the
perched zone as rapid! y as is practical.
The original pumping wells upgradient of TW4-4 were chosen because 1) they were located in
areas of the perched zone having relatively high permeability and saturated thickness, and 2)
high concentrations of chloroform were detected at these locations. The relatively high
transmissivity of the perched zone in the vicinity of these original pumping wells resulted in the
wells having a relatively high productivity. The combination of relatively high productivity and
high chloroform concentrations allowed for a high rate of chloroform mass removal. TW 4-4 and
TW4-41 are located in a downgradient area having relatively high chloroform concentrations but
relatively small saturated thickness, and at a transition from relatively high to relatively low
permeability conditions downgradient of TW 4-4. As with the other chloroform pumping wells,
pumping TW 4-4 and TW 4-41 helps to reduce the rate of chloroform migration in downgradient
portions of the plume.
Although pumping of TW4-6 and TW4-26 (located south of TW4-4 and TW4-41) is impractical
due to low permeability and small saturated thicknesses, the permeability in the vicinity of TW 4-
40 (located south of TW4-26) is large enough to make pumping practical. TW4-40 is valuable in
that it is located within the downgradient (southern) toe of the plume and is relatively productive.
Pumping of TW4-40 is likely to more effectively reduce or prevent fmther downgradient plume
migration than can be expected by pumping at the more upgradient locations.
The impact of chloroform pumping is indicated by the water level contour maps attached under
Tabs D and E. Cones of depression are evident in the vicinity of MW-4, MW-26, TW4-19, and
TW 4-20 which continue to remove significant quantities of chloroform from the perched zone.
Relatively large cones of depression have developed in the vicinities of wells TW4-1, TW4-2,
and TW4-11 which began pumping during the first quarter of 2015. As discussed in Section
4.1.1, although chloroform pumping well TW4-4 became operational in 2010, the drawdown
associated with TW4-4 was likely less apparent due to variable permeability conditions near
TW4-4 and the persistently low water level at adjacent well TW4-14. However, pumping at
adjacent well TW4-41 since the second quarter of 2018 has generally increased drawdowns in
this area; the third quarter of 2018 was the first quarter that a well-defined cone of depression
was associated with TW4-4. As discussed in Section 4.1.2 the combined pumping of TW4-4 and
TW4-41, enhanced by initiation of pumping at TW4-40 during the second quarter of 2019, has
contributed to southerly expansion of total pumping system capture. Overall, the water level
contour maps indicate effective capture of water containing high chloroform concentrations in
the vicinities of the pumping wells.
Compared to last quarter, both increases and decreases in water levels occurred at nitrate and
chloroform pumping wells, although changes in water levels in chloroform pumping wells MW-
21
26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-20 and TW4-39; and nitrate pumping well TW4-25
were less than two feet. The water levels in chloroform pumping wells TW4-1, TW4-2, TW4-4,
TW4-11, TW4-19 and TW4-37 decreased by approximately 1.3, 0.2, 2, 1.1, 3.7 and 9.8 feet,
respectively; and the water level in nitrate pumping well TWN-2 decreased by approximately
3.7 feet. Water level increases of approximately 2.5, 1.8, 0.9, 2.7, 1.2 and 2.9 feet occurred in
chloroform pumping wells MW-4, MW-26, TW4-20, TW4-21, TW4-39 and TW4-41; and
increases of 16.4, 2.9 and 0.6 feet occurred in nitrate pumping wells TW4-22, TW4-24 and
TW4-25, respectively. The overall apparent combined capture area of the nitrate and
chloroform pumping systems is smaller than last quarter, with capture decreasing within the
northern portion of the pumping system due to reduced drawdowns at TW4-22 and TW4-24.
The capture associated with nitrate pumping wells and chloroform pumping wells added since
the beginning of 2015 is expected to increase over time as water levels continue to decline due to
cessation of water delivery to the northern wildlife ponds and continued pumping. Slow
development of hydraulic capture in the vicinities of many wells is consistent with and expected
based on the relatively low permeability of the perched zone at the site.
The hydraulic capture effectiveness of both chloroform and nitrate pumping systems depends to
some extent on the continued productivity of chloroform and nitrate pumping wells. Decreases in
productivity have been noted since the third quarter of 2014 in chloroform pumping well TW4-
19 and nitrate pumping well TW4-24. The impact of reduced productivity of these wells on
chloroform capture was discussed in Attachment N (Tab N) of the third quarter, 2015 report. The
report also included a discussion of the effectiveness of chloroform pumping on chloroform
capture. 'Background' flow through the chloroform plume was calculated in Attachment N as
approximately 3.3 gpm. A more refined 'background' flow calculation of 3.4 gpm was provided
in the CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah).
Decreases in productivity at TW4-4 since the third quarter of 2016 have been addressed by the
operation of adjacent pumping well TW4-41 since the second quarter of 2018.
Pumping from wells within and immediately adjacent to the chloroform plume during the current
quarter (from wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20,
TW4-21, TW4-22, TW4-24, TW4-37, TW4-39, TW4-40 and TW4-41) is approximately 5.5
gpm. This calculation is based on the total volume pumped by these wells over the 90 day
quarter (707,218 gallons) and accounts for times that the pumps are off due to insufficient water
columns in the wells. Pumping from these wells exceeds the calculated background flow by 2.1
gpm or 62 %, and is considered adequate at the present time even with the reduced productivities
of some wells. In addition, because of continued reductions in saturated thicknesses and
hydraulic gradients resulting from reduced wildlife pond recharge, 'background' flow through
the plume is expected to continue to diminish, thereby reducing the pumping needed to control
the plume.
Chloroform concentrations at many locations have been or appear to be affected by changes
associated with reduced dilution from the wildlife ponds and nitrate pumping. For example,
increases in chloroform at TW4-22 and TW4-24 after these wells were converted to nitrate
22
pumping wells are attributable to westward migration of chloroform from the vicinity of TW 4-20
toward these wells. The increase in concentration at TW 4-8 from non-detect to 100 µg/L in the
first quarter of 2014 (and to 75.4 µg/L this quarter) is likely related to reduced dilution. Although
the chloroform concentration in TW4-6 has decreased from 1,180 µg/L during the first quarter of
2015 to 15.8 µg/L this quarter (and remains outside the plume), concentrations at TW4-6 have
increased from approximately 10 µg/L since the second quarter of 2014. The generally increased
concentration is likely related to both reduced dilution and more westward flow induced by
nitrate pumping.
TW 4-6 is located immediately south and historically cross-to downgradient of chloroform
pumping well TW 4-4. TW 4-6 has been incorporated into the chloroform plume twice: from the
first quarter of 2009 through the third quarter of 201 O; and from the third quarter of 2014 through
the second quarter of 2018. Pumping of TW4-6 (and TW4-26) is impractical because of
relatively low permeability and relatively small saturated thicknesses. However, pumping at
more productive locations upgradient of TW4-6 (such as TW4-4) enhances mass removal and
lowers hydraulic gradients, thereby reducing the rate of downgradient chloroform migration and
allowing natural attenuation to be more effective. Pumping at TW 4-4 was implemented during
the first quarter of 2010 to improve capture downgradient of TW4-4 to the extent allowable by
the lower productivity conditions present in this area.
The beneficial effect of pumping TW 4-4 was demonstrated by the net decreases in TW 4-6
chloroform concentrations from 1,000 µg/L to 10.3 µg/L, and in TW4-26 from 13 µg/L to 4.2
µg/L, between the initiation of TW4-4 pumping and the second quaiter of 2014. Concentrations
at these wells decreased substantially even though they did not unambiguously appear to be
within the hydraulic capture of TW 4-4. As discussed in Section 4.1.1, however, the decrease in
the long-term rate of water level rise at TW4-6 after TW4-4 began pumping does suggest that
TW 4-6 was within the hydraulic influence of TW 4-4. The decline in water levels at TW 4-6 since
the fourth quarter of 2013 likely reflects the additional influences of cessation of water delivery
to the wildlife ponds and the addition of chloroform pumping wells TW4-1, TW4-2, TW4-ll
and TW4-41. Regardless of whether TW4-6 was demonstrably within the hydraulic capture of
TW4-4, pumping TW4-4, and relatively recently installed adjacent pumping well TW4-41, helps
to reduce chloroform migration to TW4-6, TW4-26, and other downgradient locations by the
mechanisms discussed above.
Likewise, pumping at other productive upgradient locations has a beneficial impact on
downgradient chloroform even if the downgradient chloroform is not completely within the
hydraulic capture of the productive upgradient well(s). For example, pumping at MW-26 likely
reduced chloroform concentrations at TW4-16 from a maximum of 530 µg/L in the second
quarter of 2004 to less than 70 µg/L by the fourth quarter of 2005, and maintained concentrations
below 70 µg/L until the second quarter of 2014, even though TW4-16 appears to be beyond the
hydraulic capture of MW-26. Furthermore, the overall hydraulic capture of the chloroform
pumping system has expanded since initiation of pumping at wells TW4-1, TW4-2, TW4-ll
TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 since the beginning of 2015. In particular, the
addition of wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-37 and TW4-39 likely halted the
mid-2013 to end of 2014 increase in concentration at TW4-16 from non-detect to 387 µg/L.
Concentrations at TW4-16 dropped from 387 µg/L in the fourth quarter of 2014 to less than 70
23
µg/L by the second quarter of 2015. Chloroform at TW4-16 has been above and below 70 µg/L
since the second quarter of 2015 and was detected at 99.8 µg/L this quarter.
Chloroform exceeding 70 µg/L was detected in the second quarter of 2013 at TW4-29, installed
during the first quarter of 2013 and located south of TW4-27 and east of TW4-26. With respect
to historic groundwater flow directions implied by historic groundwater elevations in this area,
TW4-29 was positioned generally cross-gradient of TW4-4 and TW4-6. As discussed in Section
4.1.1, chloroform detected at TW4-29 may have migrated around the low permeability area
defined by TW4-27, TW4-14 and TW4-36. The apparent migration pathway from TW4-4 to
TW4-29 is consistent with chloroform exceeding 70 µg/L detected in the fourth quarter of 2013
at TW4-33, installed during the third quarter of 2013 and located between TW4-4 and TW4-29.
Chloroform concentrations at TW4-33 that are lower than concentrations at TW4-29, and the
likelihood that a pathway exists from TW4-4 to TW4-33 to TW4-29, suggest that concentrations
in the vicinity of TW4-33 were likely higher prior to initiation of TW4-4 pumping.
TW4-4 pumping (augmented by pumping at adjacent well TW4-41) is likely to eventually
reduce chloroform at both TW4-33 and TW4-29 by cutting off the source. The impact at TW4-
33 is expected to be greater than at TW4-29 because TW4-33 is in closer proximity to TW4-4
(and TW4-41) pumping. Such behavior is expected by analogy with the decreases in chloroform
concentrations at TW4-6 and TW4-26 that occurred once TW4-4 pumping began. However,
concentrations at both TW4-29 and TW4-33 were relatively stable (rather than decreasing) for
several quarters after installation. Concentrations at TW4-29 appear to be on an upward trend
since the third quarter of 2014. As discussed in Section 4.1.1, although decreasing concentration
trends at both wells are eventually expected to occur, relatively stable chloroform at TW4-33 and
increases in concentration at TW4-29 since the third quarter of 2014 suggest that chloroform
migration has been arrested at TW4-33 by TW4-4 (and TW4-41) pumping and that increasing
chloroform at downgradient well TW4-29 results from a remnant of the plume that continues to
migrate downgradient (toward TW4-30, which bounds to plume to the east). The influence of
TW4-4 pumping at the distal end of the plume is consistent with generally decreasing water
levels at both TW4-29 and TW4-33. However, as discussed in Section 4.1.1, decreasing water
level trends are also consistent with reduced wildlife pond seepage. The decay of the
groundwater mound associated with the southern wildlife pond, which is 3 to 4 times closer to
the southern extremity of the chloroform plume than the northern ponds, is likely to have an
impact on water levels within and adjacent to this portion of the plume.
As discussed in Section 4.1.1, generally decreasing water level trends ( since about the fourth
quarter of 2013), and increased concentrations (since the first quarter of 2014 and the third
quarter of 2016, respectively) at TW4-6 and TW4-26, are also consistent with reduced wildlife
pond seepage, in particular reduced seepage from the southern wildlife pond. As the groundwater
mound associated with the southern pond decays, groundwater flow directions in the southern
extremity of the plume are likely to become more southerly, and plume migration is likely to tum
more to the south. An increasingly southerly direction of plume migration is consistent with
increased concentrations at TW4-26 (from less than 10 µg/L in the third quruter of 2016 to 877
µg/L this quarter).
24
In addition, as in the area near TW4-29 and TW4-33, generally decreasing concentrations at
TW4-6 since the third quarter of 2015, and generally increased concentrations at TW4-26 since
the third quarter of 2016, suggest that TW4-4 (and TW4-41) pumping has arrested chloroform
migration between TW4-4 and TW4-6, and that increased chloroform at TW4-26 results from a
remnant of the plume that continues to migrate south from TW4-6 to TW4-26. The enhancement
of pumping in the vicinity of TW 4-4 by the start-up of TW 4-41 pumping in the second quarter of
2018 is likely to increase this apparent separation and to have resulted in concentrations at TW4-
6 dropping below 70 µg/L beginning in the third quarter of 2018.
Furthermore, detectable chloroform concentrations at TW4-14 (since the fourth quarter of 2014)
and TW4-27 (since the third quarter of 2015) suggest ongoing, but slow, downgradient migration
of chloroform from the southeastern extremity of the plume into the low permeability materials
penetrated by these wells.
Chloroform analytical results from TW4-35 and TW4-36 (as discussed in Section 4.2.3)
demonstrate that chloroform is bounded to the southeast of TW4-29 and to the east of TW4-8.
4.2 Review of Analytical Results
4.2.1 Current Chloroform Isoconcentration Map
Included under Tab J of this Report is a current chloroform isoconcentration map for the Mill
site. Details of the gridding procedure used to generate the chloroform isoconcentration map
(consistent with Part III.B.2.a through Part III.B.2.c of the GCAP) are provided in Tab L.
4.2.2 Chloroform Concentration Trend Data and Graphs
Attached under Tab K are tables summarizing values for all required parameters, chloride,
nitrate/nitrite, carbon tetrachloride, chloroform, chloromethane, and methylene chloride, for each
well over time.
Attached under Tab K are graphs showing chloroform concentration trends in each monitor well
over time.
4.2.3 Interpretation of Analytical Data
Comparing the chloroform analytical results to those of the previous quarter, as summarized in
the tables included under Tab K, the following observations can be made:
a) Chloroform concentrations have increased by more than 20% in the following wells
compared to last quarter: TW 4-14, TW 4-16 and TW 4-40;
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: TW4-2, TW4-8, TW4-19, TW4-20, TW4-22, TW4-37 and
TW4-39;
25
c) Chloroform concentrations have remained within 20% in the following wells compared
to last quarter: MW-4, MW-26, TW4-1, TW4-4, TW4-5, TW4-6, TW4-7, TW4-9, TW4-
10, TW4-ll, TW4-18, TW4-21, TW4-24, TW4-26, TW4-27, TW4-29, TW4-30, TW4-
33 and TW4-41; and
d) Chloroform concentrations have remained non-detect in the following wells: MW-32,
TW4-3, TW4-12, TW4-13, TW4-23, TW4-25, TW4-28, TW4-31, TW4-32, TW4-34,
TW4-35, TW4-36, TW4-38 and TW4-42.
As indicated, chloroform concentrations at many of the wells with detected chloroform were
within 20% of the values reported for the wells during the previous quarter, suggesting that
variations are within the range typical for sampling and analytical error. Wells TW4-2, TW4-8,
TW4-14, TW4-16, TW4-19, TW4-20, TW4-22, TW4-37, TW4-39 and TW4-40 had changes in
concentration greater than 20%. Of these, TW4-2, TW4-19, TW4-20, TW4-37, TW4-39 and
TW4-40 are chloroform pumping wells; and TW4-22 is a nitrate pumping well. TW4-8 is
located adjacent to chloroform pumping well MW-4; TW4-14 is located adjacent to chloroform
pumping wells TW 4-4 and TW 4-41; and TW 4-16 is located near chloroform pumping wells
MW-26 and TW4-1 l. Fluctuations in concentrations at both chloroform and nitrate pumping
wells and wells adjacent to pumping wells likely result in part from changes in pumping.
In addition, TW4-14 is located just outside, and TW4-8 and TW4-16 just inside the plume
boundary. Fluctuations in concentrations at these wells are expected based on their locations near
the plume margins.
Chloroform pumping wells TW4-ll, TW4-19, TW4-20, TW4-37 and TW4-39; and nitrate
pumping well TW4-22, had the highest detected chloroform concentrations of 2,790; 6,670;
10,500; 11,900; 4,240 and 3,460 µg/L, respectively. Since last quarter, the chloroform
concentrations in TW4-ll decreased from 2,970 to 2,790 µg/L; TW4-19 decreased from 11,500
to 6,670 µg/L; TW4-20 decreased from 13,700 µg/L to 10,500 µg/L; TW4-37 decreased from
16,200 µg/L to 11,900 µg/L; and TW4-39 decreased from 8,640 to 4,240 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 decreased from 734 to 596 µg/L;
the concentration in nitrate pumping well TW4-22 decreased from 4,690 to 3,460 µg/L; and the
concentration in nitrate pumping well TW4-24 increased slightly from 28.8 to 31.1 µg/L. TW4-
24 remains just outside the chloroform plume and nitrate pumping well TW4-25 remained non-
detect. TW4-25, located north of TW4-21, bounds the chloroform plume to the north.
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased from 96 µg/L to 75.4 µg/L. TW4-8 is located immediately east of
chloroform pumping well MW-4, where chloroform was detected at a concentration of 1,180
µg/L. From the first quarter of 2005 through the fourth quarter of 2013, the plume boundary
remained between MW-4 and TW4-8. The occurrence of elevated chloroform at TW4-8 is likely
related to its location along the eastern plume boundary immediately east of pumping well MW-
4. Changes in the plume boundary near TW 4-8 are expected to result from changes in pumping
and reduced dilution resulting from cessation of water delivery to the northern wildlife ponds.
Chloroform at TW4-8 is bounded to the north by TW4-3 and TW4-38 (both non-detect), to the
26
northeast by TW4-13 (non-detect), to the east by TW4-36 (non-detect), and to the southeast by
TW4-14 (6.1 µg/L).
Chloroform at TW4-29 (located at the southeastern extremity of the plume, to the east of TW4-
26 and to the south of TW4-27) increased slightly from 537 µg/L to 549 µg/L, and chloroform at
TW4-30, located immediately cross-to downgradient of TW4-29, increased from approximately
32 µg/L to approximately 35 µg/L. Chloroform at TW4-14 increased from 4.2µg/L to 6.1 µg/L
and chloroform at TW4-27 decreased from approximately 8.2 µg/L to 7.6 µg/L. Concentration
trends at these wells are generally consistent with ongoing, but slow, downgradient migration of
chloroform at these locations. Chloroform at TW4-29 is bounded to the north by TW4-27 (7.6
µg/L), to the east by TW4-30 (35 µg/L), to the southeast by TW4-35 (non-detect), to the south
by TW4-34 (non-detect), and to the west-northwest by TW4-6 (approximately 16 µg/L) and
TW4-23 (non-detect). General increases in concentrations at TW4-26 since the third quarter of
2016 are also consistent with continuing downgradient chloroform migration which is likely
enhanced by the decay of the groundwater mound associated with the southern wildlife pond.
Chloroform at TW4-33 (located between TW4-4 and TW4-29) showed a decrease in
concentration, from approximately 121 µg/L to 101 µg/L. Chloroform at TW4-33 is bounded to
the north by TW4-14 (6.1 µg/), to the east by TW4-27 (7.6 µg/L), and to the west by TW4-6
(approximately 16 µg/L) and TW4-23 (non-detect). Recent increases in concentration at TW4-26
have widened the southeast extremity of the plume which historically was narrow compared to
more upgradient locations.
The chloroform concentration in TW4-6 remained at 16 µg/L; TW4-6 has remained outside the
chloroform plume since the third quarter of 2018. Installed in the second quarter of 2000, TW4-6
was the most downgradient temporary perched well prior to installation of TW4-23 in 2007 and
TW4-26 in the second quarter of 2010. TW4-6 remained outside the chloroform plume between
installation in the second quarter of 2000 and the fourth quarter of 2008 likely due to a
combination of 1) slow rates of downgradient chloroform migration in this area due to low
permeability conditions and the effects of upgradient chloroform removal by pumping, and 2)
natural attenuation.TW4-6 was subsequently incorporated into the plume twice: from the first
quarter of 2009 through the third quarter of 2010; and from the third quarter of 2014 through the
second quarter of 2018. Between initiation of pumping of TW4-4 in the first quarter of 2010 and
the second quarter of 2014, concentrations at TW4-6 showed a net decrease from 1,000 µg/L to
10.3 µg/L.
The relatively slow rate of chloroform migration in the vicinity of TW4-6 in the past is
demonstrated by comparing the rate of increase in chloroform at this well to the rate of increase
in the nearest upgradient well TW4-4. Concentrations at TW4-4 increased from non-detect to
more than 2,200 µg/L within only two quarters whereas 16 quarters were required for
concentrations in TW4-6 to increase from non-detect to only 81 µg/L. This behavior is consistent
with hydraulic tests performed at TW4-4, TW4-6, and TW4-26 during the third quarter of 2010
that indicate a nearly two orders of magnitude decrease in permeability south (downgradient) of
TW4-4. Chloroform migration rates in the vicinities of wells TW4-26, TW4-29 and TW4-33
have been expected to be relatively slow due to upgradient pumping and relatively low
permeability conditions. By analogy with the decreases in concentration at TW4-6 and TW4-26
27
that occurred after initiation of TW4-4 pumping, chloroform concentrations at both TW4-29 and
TW4-33 are expected to eventually trend downward.
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for a slight
expansion near TW4-16 and a slight contraction near TW4-21. Chloroform concentrations at
TW4-21 decreased from approximately 734 µg/L to 596 µg/L shifting the plume boundary away
from TW4-25 (non-detect) located immediately to the north.
TW 4-9 remained outside the plume this quarter. TW 4-9 was incorporated into the plume from
the first quarter of 2016 until the first quarter of 2019 due to increased concentrations
attributable to reduced recharge (and dilution) from the northern wildlife ponds. Prior to the first
quarter of 2016, however, TW4-9 was outside the plume except during the fourth quarter of
2014.
Nitrate pumping generally caused the western boundary of the northern portion of the
chloroform plume to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-
24 has been both inside and outside the plume and remains outside the plume this quarter, likely
due to initiation of TW4-37 pumping in the second quarter of 2015 and reduced productivity at
TW4-24 (since the third quarter of 2014). Since the second quarter of 2014, generally higher
concentrations at TW4-6 and TW4-16 (both of which were within the chloroform plume in the
past) indicate that the plume boundary migrated to the southwest and re-incorporated both wells.
This quarter, TW4-6 remains outside the plume while TW4-16 remains just inside the plume.
Generally increased concentrations at these wells since the first quarter of 2014 are likely related
to reduced dilution from cessation of water delivery to the northern wildlife ponds and more
westerly flow induced by nitrate pumping. In addition, concentrations at TW4-6 are likely
influenced by reduced recharge at the southern wildlife pond and the decay of the associated
groundwater mound. A decreasing trend in chloroform concentration at TW 4-6 since the third
quarter of 2015, and generally increased concentrations at TW4-26 since the third quarter of
2016, suggest that TW 4-4 pumping has arrested chloroform migration between TW 4-4 and
TW4-6, and that increased chloroform at TW4-26 results from a remnant of the plume that
continues to migrate south from TW4-6 to TW4-26. Pumping at TW4-41, located adjacent to
TW4-4, and pumping at TW4-40, located just south (downgradient) of TW4-26, is expected to
reduce or halt plume expansion to the south.
Although the nitrate pumping system may redistribute chloroform within the plume and cause
changes in the chloroform plume boundaries, continued operation of the nitrate pumping system
is expected to enhance capture associated with the chloroform pumping system. Furthermore,
since the beginning of 2015, the addition of chloroform wells TW4-1, TW4-2, TW4-11, TW4-
21, TW4-37, TW4-39, TW4-40 and TW4-41, is expected to have a beneficial impact. Generally
reduced concentrations at TW4-6 (since the first quarter of 2015) and TW4-16 (since the fourth
quarter of 2014) after previous increases are likely the result of initiation ofTW4-1, TW4-2, and
TW4-11 pumping during 2015. Continued reductions at TW4-6 are anticipated to result from
pumping at TW 4-41.
28
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND TW4-4
OPERATIONS REPORT
5.1 Introduction
As a part of the investigation of chloroform contamination at the Mill site, EFRI has been
conducting a Long Term Pump Test on MW-4, TW4-19, MW-26, and TW4-20, and, since
January 31, 2010, TW4-4. The purpose of the test is to serve as an interim action that will
remove a significant amount of chloroform-contaminated water while gathering additional data
on hydraulic properties in the area of investigation.
Beginning in January 2013, EFRI began long term pumping of TW4-22, TW4-24, TW4-25, and
TWN-02 as required by the Nitrate CAP, dated May 7, 2012 and the Stipulated Consent Order
(the "SCO") dated December 12, 2012. Because wells TW4-22, TW4-24, and TW4-25 are
chloroform program wells, they are included in this report and any chloroform removal realized
as part of this pumping is calculated and included in the chloroform quarterly reports.
Beginning on January 14, 2015, EFRI began long term pumping of TW4-1, TW4-2, and TW4-11
and began long term pumping of TW4-21 and TW4-37 on June 9, 2015. Beginning in December
2016 EFRI began long term pumping of TW4-39. Beginning in April 2018 EFRI began Jong
term pumping of TW4-41. Beginning in May 2019 EFRI began long term pumping of TW4-40.
The following information documents the operational activities during the quarter.
5.2 Pump Test Data Collection
The long term pump test for MW-4 was started on April 14, 2003, followed by the start of
pumping from TW4-19 on April 30, 2003, from MW-26 on August 8, 2003, from TW4-20 on
August 4, 2005, from TW4-4 on January 31, 2010, and from TW4-22, TW4-24, and TW4-25 on
January 26, 2013. Personnel from Hydro Geo Chem, Inc. were on site to conduct the first phase
of the pump test and collect the initial two days of monitoring data for MW-4. EFRI personnel
have gathered subsequent water level and pumping data.
Analyses of hydraulic parameters and discussions of perched zone hydrogeology near MW-4 has
been provided by Hydro Geo Chem in a separate report, dated November 12, 2001, and in the
May 26, 2004 Final Report on the Long Term Pumping Test.
Data collected during the quarter included the following:
• Measurement of water levels at MW-4, TW4-1, TW4-2, TW4-4, TW4-11, TW4-
19, MW-26, TW4-20, TW4-21, TWN-2, TW4-22, TW4-24, TW4-25, TW4-37,
TW4-39 TW4-40, and TW4-41 on a weekly basis, and at selected temporary
wells and permanent monitoring wells on a monthly basis.
• Measurement of pumping history, including:
pumping rates
total pumped volume
29
operational and non-operational periods.
• Periodic sampling of pumped water for chloroform and nitrate/nitrite analysis and
other constituents.
5.3 Water Level Measurements
Beginning August 16, 2003, the frequency of water level measurements from MW-4, MW-26,
and TW4-19 was reduced to weekly. From commencement of pumping TW4-20, and regularly
after March 1, 2010 for TW4-4, water levels in these wells have been measured weekly. From
commencement of pumping, water levels in wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-22,
TW4-24, TW4-25, TW4-37, TW4-39, TW4-41, and TWN-2 have been measured weekly. Depth
to groundwater in all other chloroform contaminant investigation wells is monitored monthly.
Copies of the weekly Depth to Water monitoring sheets for MW-4, MW-26, TW4-1, TW4-2,
TW4-11, TW4-19, TW4-20, TW4-21, TW4-4, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39,
TW4-40 (beginning May 2019), TW4-41 and TWN-2 and the monthly Depth to Water
monitoring sheets for the chloroform contaminant investigation wells and the selected temporary
wells and permanent monitoring wells are included under Tab C. Monthly depth to water
measurements for the quarter are recorded in the Field Data Worksheets included under Tab C.
5.4 Pumping Rates and Volumes
Table G-2 summarizes the recovered mass of chloroform by well per quarter and historically
since the inception of the chloroform recovery program for the active pumping wells. It is
important to note that TWN-2 is a nitrate program well and is sampled only for nitrate and
chloride as required by the nitrate program. Because TWN-2 is not sampled or analyzed for
chloroform, the mass of chloroform recovered is not calculated.
The pumping wells do not pump continuously, but are on a delay device. The wells purge for a
set amount of time and then shut off to allow the well to recharge. Water from the pumping
wells is transferred to a holding tank. The water in the holding tank is used in the Mill processes.
The pumping rates and volumes for each of the pumping wells are shown in Table G-3.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Unless specifically noted below, no operational problems were observed with the well or
pumping equipment during the quarter.
5.5 Mass Removed and Plume Residual Mass
Chloroform removal was estimated as of the first quarter 2007. Since that estimation, the mass
removed by well for each quarter has been compiled in Table G-2, which shows the pounds of
chloroform that have been removed to date. The mass of chloroform removed from the plume
this quarter is approximately 18.3 lb., which is approximately 30% smaller than the
30
approximately 26.2 lb. removed last quarter. The smaller rate of mass removal is attributable
primarily to the decreased concentrations at TW4-19, TW4-37 and TW4-39.
The re idual mass of chloroform within the plume is estimated as 1,050 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 358 lb. smaller than last quarter's estimate of 1,408 lb. As per
Part ID.B.2 of the GCAP, electronic files used in calculating the mass estimate are provided with
this report. Details of the procedure are provided in Tab L.
The residual mass is plotted in Figure L.1. Since the third quarter of 2015 the trend is downward;
the current quarter's estimate of 1,050 lb. is substantially lower than both the third quarter 2015
estimate of 1,712 lb., and the maximum of 2,261 lb. estimated for the second quarter of 2016.
Subsequent residual plume mass estimates will be calculated quarterly, added to the graph, and
the trendline updated as per Pait III.B.3 of the GCAP.
As discussed in the CACME Report, the calculated chloroform mass is larger since the cessation
of water delivery to the two northern wildlife ponds in the first quarter of 2012. These ponds are
located immediately upgradient of the chloroform plume. The increase in calculated mass results
from increased plume area and increased average concentrations within the plume. The increases
in both plume area and average concentrations are attributable to reduced dilution due to the
reduction in chloroform-free wildlife pond seepage.
The general decrease in the residual mass estimates since the second quarter of 2016 suggests
stabilization. Although the residual mass estimates are generally larger since 2012, the rate of
mass removed per quarter by pumping is also generally larger, in particular since the addition of
8 new pumping wells since the beginning of 2015. Furthermore, although the pumping system is
not designed to hydraulically capture the entire plume, the proportion of the mass of the plume
under capture has historically been large. The proportion of the mass of the plume under capture
during the fourth quarters of 2012, 2013, 2014, 2015, 2016, 2017 and 2018 ranged from
approximately 84% to 93%. The approximate proportion of the mass of the plume under capture
this quarter is 97 %, slightly below last quarter's 99%.
5.6 Inspections
All of the required inspections were completed and the inspection forms are included in Tab C.
5.7 Conditions That May Affect Water Levels in Piezometers
No water was added to the any of the wildlife ponds during the quarter.
6.0 CORRECTIVE ACTION REPORT
No corrective actions were necessary for the current reporting period.
6.1 Assessment of Previous Quarter's Corrective Actions
There were no corrective actions required during the previous quarters' monitoring period.
31
7.0 CURRENT COMPLIANCE STATUS
7.1 Long Term Chloroform Plume Control
The chloroform plume is currently entirely within the Mill property boundary and is bounded on
all sides by wells having chloroform concentrations that are either non-detect or less than 70
µg/L (Tab J). The plume is bounded to the north by TW4-25 (non-detect); to the west and
southwest by MW-31 (non-detect), MW-32 (non-detect), TW4-6 (approximately 16 µg/L),
TW4-23 (non-detect), and TW4-24 (approximately 31 µg/L); to the east by TW4-3 (non-detect),
TW4-5 (approximately 15 µg/L), TW4-9 (approximately 66 µg/L), TW4-13 (non-detect), TW4-
14 (approximately 6 µg/L), TW4-18 (approximately 56 µg/L), TW4-27 (approximately 8 µg/L),
TW4-30 (approximately 35 µg/L), TW4-36 (non-detect) and TW4-38 (non-detect); to the south
by TW4-34 (non-detect) and TW4-42 (non-detect); and to the southeast by TW4-35 (non-detect).
Because TW4-26 no longer bounded the chloroform plume to the south-southwest, TW4-40 was
installed south (downgradient) of TW4-26 during the first quarter of 2018. Because the second
quarter of 2018 was the second consecutive quarter that chloroform in TW4-40 exceeded 70
µg/L, the required Plan and Time Schedule was submitted and TW4-42 was installed
approximately 200 feet south of TW4-40 during April, 2019. Chloroform has not been detected
in TW4-42, indicating that TW4-42 bounds the plume immediately to the south-southwest.
Regardless, MW-17 (non-detect) and MW-38 (non-detect) bound the plume to the far southwest
(cross-gradient), and MW-22 (non-detect), MW-39 (non-detect) and MW-40 (non-detect) bound
the plume far to the south (cross-to downgradient). Data collected to date indicate there are
sufficient chloroform monitoring and pumping wells to effectively define, control, and monitor
the plume.
7 .2 Well Construction, Maintenance and Operation
Part II of the GCAP specifies that EFRI must construct, maintain and operate the chloroform
wells in accordance with the specifications delineated therein. The two new wells that were
installed during the quarter as well as all previously installed wells were installed in accordance
with the GCAP requirements. The wells were maintained and operated as required. Additional
details regarding any specific pumping well operations and maintenance issues noted during the
quarter are discussed in Section 5.0 above.
7 .3 Disposal of Extracted Groundwater
Part II of the GCAP requires that all extracted groundwater be disposed of in the tailings
management system or fed in the Mill process. All extracted groundwater was handled as
required by the GCAP.
7 .4 Compliance Well Performance
Part II.G of the GCAP states that an exceedance of the compliance well performance standard is
defined as the presence of chloroform in any compliance monitoring well in excess of 70 ug/L
for two or more quarters.
32
The compliance well chloroform concentrations were below the 70 ug/L except as noted in
previous reports. The previously noted exceedances have been addressed in Plans and Time
Schedules. There are no new exceedances in this reporting period.
7.5 Chloroform Plume Monitoring for Wells within 500 Feet of the Property Boundary
Currently there are no compliance wells within 500 feet of the property boundary.
8.0 CONCLUSIONS AND RECOMMENDATIONS
The residual mass of chloroform within the plume is estimated as 1,050 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 358 lb. less than last quarter's estimate of 1,408 lb. The mass of
chloroform removed from the plume this quarter is approximately 18.3 lb., which is
approximately 30% smaller than the approximately 26.2 lb. removed last quarter. The smaller
rate of mass removal is attributable primarily to the decreased chloroform concentrations at
TW4-19, TW4-37 and TW4-39.
The chloroform plume is currently entirely within the Mill property boundary and is bounded on
all sides by wells having chloroform concentrations that are either non-detect or less than 70
µg/L (Tab J). The plume is bounded to the north by TW4-25 (non-detect); to the west and
southwest by MW-31 (non-detect), MW-32 (non-detect), TW4-6 (approximately 16 µg/L),
TW4-23 (non-detect), and TW4-24 (approximately 31 µg/L); to the east by TW4-3 (non-detect),
TW4-5 (approximately 15 µg/L), TW4-9 (approximately 66 µg/L), TW4-13 (non-detect), TW4-
14 (approximately 6 µg/L), TW4-18 (approximately 56 µg/L), TW4-27 (approximately 8 µg/L),
TW4-30 (approximately 35 µg/L), TW4-36 (non-detect) and TW4-38 (non-detect); to the south
by TW4-34 (non-detect) and TW4-42 (non-detect); and to the southeast by TW4-35 (non-detect).
Because TW4-26 no longer bounded the chloroform plume to the south-southwest, TW4-40 was
installed south (downgradient) of TW4-26 during the first quarter of 2018. Because the second
quarter of 2018 was the second consecutive quarter that chloroform in TW4-40 exceeded 70
µg/L, the required Plan and Time Schedule was submitted and TW4-42 was installed
approximately 200 feet south of TW4-40 during April, 2019. Chloroform has not been detected
in TW4-42, indicating that TW4-42 bounds the plume immediately to the south-southwest.
Regardless, MW-17 (non-detect) and MW-38 (non-detect) bound the plume to the far southwest
(cross-gradient), and MW-22 (non-detect), MW-39 (non-detect) and MW-40 (non-detect) bound
the plume far to the south (cross-to downgradient). Data collected to date indicate there are
sufficient chloroform monitoring and pumping wells to effectively define, control, and monitor
the plume.
The water level contour maps for the second quarter, 2019 indicate effective capture of water
containing high chloroform concentrations over most of the chloroform plume. Capture in the
southeastern portion of the plume (vicinity of MW-4) was enhanced by start-up of chloroform
pumping wells TW4-1, TW4-2, and TW4-11 during the first quarter of 2015. Capture in the
northwestern portion of the plume was enhanced by start-up of chloroform pumping wells TW4-
21 and TW4-37 during the second quarter of 2015; and of TW4-39 during the fourth quarter of
2016. Capture in the southernmost portion of the plume was enhanced by start-up of pumping at
33
TW4-41 during the second quarter of 2018 and of TW4-40 during the second quarter of 2019.
All pumping wells added since the beginning of 2015 have enhanced the effectiveness of
chloroform mass removal.
Although pumping began in the first quarter of 2010, a well-defined capture zone was not clearly
evident at chloroform pumping well TW4-4 until the third quarter of 2018. Increased drawdowns
in this area since the second quarter of 2018, and development of a definable capture zone, is
attributable to pumping at adjacent well TW4-41.
The capture zone associated with TW4-4 was likely obscured prior to the second quarter of 2018
by the historically relatively low water level at adjacent well TW 4-14 and the two orders of
magnitude decrease in permeability south of TW4-4. However, as noted in previous reports,
between the first quarter of 2010 and the second quarter of 2014, decreases in chloroform
concentrations and the rate of water level rise at TW4-6 (located downgradient of TW4-4) likely
resulted from TW 4-4 pumping.
Cones of depression associated with the nitrate pumping wells became evident as of the fourth
quarter of 2013, and capture associated with the nitrate pumping is expected to continue to
develop. Overall, the apparent capture area of the combined chloroform and nitrate pumping
systems is smaller than last quarter, primarily due to decreased drawdowns at TW4-22 and TW4-
24.
'Background' flow through the chloroform plume was calculated as approximately 3.4 gpm as
presented in CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah). Pumping from
wells within and immediately adjacent to the chloroform plume during the current quarter (from
wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22,
TW4-24, TW4-37, TW4-39, TW4-40 and TW4-41) is approximately 5.5 gpm, which exceeds
the calculated background flow by 2.1 gpm or 62%, and is considered adequate at the present
time.
Chloroform concentrations at many of the wells with detected chloroform were within 20% of
the values reported during the previous quarter, suggesting that variations are within the range
typical for sampling and analytical error. Wells TW4-2, TW4-8, TW4-14, TW4-16, TW4-19,
TW4-20, TW4-22, TW4-37, TW4-39 and TW4-40 had changes in concentration greater than
20%. Of these, TW4-2, TW4-19, TW4-20, TW4-37, TW4-39 and TW4-40 are chloroform
pumping wells; and TW4-22 is a nitrate pumping well. TW4-8 is located adjacent to chloroform
pumping well MW-4; TW4-14 is located adjacent to chloroform pumping wells TW4-4 and
TW 4-41; and TW 4-16 is located near chloroform pumping wells MW-26 and TW 4-11.
Fluctuations in concentrations at both chloroform and nitrate pumping wells and wells adjacent
to pumping wells likely result in part from changes in pumping. In addition, TW4-14 is located
just outside, and TW4-8 and TW4-16 just inside the plume boundary. Fluctuations in
concentrations at these wells are expected based on their locations near the plume margins.
Furthermore, changes in concentrations at chloroform wells are expected to result from
34
continued operation of nitrate pumping wells as the capture associated with nitrate pumping
expands and flow directions change locally.
Chloroform pumping wells TW4-ll, TW4-19, TW4-20, TW4-37 and TW4-39; and nitrate
pumping well TW4-22, had the highest detected chloroform concentrations of 2,790; 6,670;
10,500; 11,900; 4,240 and 3,460 µg/L, respectively. Since last quarter, the chloroform
concentrations in TW4-ll decreased from 2,970 to 2,790 µg/L; TW4-19 decreased from 11,500
to 6,670 µg/L; TW4-20 decreased from 13,700 µg/L to 10,500 µg/L; TW4-37 decreased from
16,200 µg/L to 11,900 µg/L; and TW 4-39 decreased from 8,640 to 4,240 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 decreased from 734 to 596 µg/L;
the concentration in nitrate pumping well TW4-22 decreased from 4,690 to 3,460 µg/L; and the
concentration in nitrate pumping well TW4-24 increased slightly from 28.8 to 31.1 µg/L. TW4-
24 remains just outside the chloroform plume and nitrate pumping well TW4-25 remained non-
detect. TW4-25, located north of TW4-21, bounds the chloroform plume to the north.
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased from 96 µg/L to 75.4 µg/L. TW4-8 is located immediately east of
chloroform pumping well MW-4, where chloroform was detected at a concentration of 1,180
µg/L. From the first quarter of 2005 through the fourth quarter of 2013, the plume boundary
remained between MW-4 and TW4-8. The occurrence of elevated chloroform at TW4-8 is likely
related to its location along the eastern plume boundary immediately east of pumping well MW-
4. Changes in the plume boundary near TW4-8 are expected to result from changes in pumping
and reduced dilution resulting from cessation of water delivery to the northern wildlife ponds.
Chloroform at TW4-8 is bounded to the north by TW4-3 and TW4-38 (both non-detect), to the
northeast by TW4-13 (non-detect), to the east by TW4-36 (non-detect), and to the southeast by
TW4-14 (6.1 µg/L).
Detectable chloroform concentrations at TW4-14 (since the fourth quarter of 2014) and TW4-27
(since the third quarter of 2015) are consistent with continued, but slow, downgradient migration
of chloroform from the distal end of the plume (near TW4-29 and TW4-33) into the low
permeability materials penetrated by TW4-14 and TW4-27. Chloroform at TW4-14 increased
from approximately 4.2 µg/L to 6.1 µg/L and chloroform at TW 4-27 decreased from
approximately 8.2 µg/L to approximately 7.6 µg/L. Pumping at TW4-41 is expected to reduce or
prevent future migration of chloroform toward these wells.
Concentration trends at TW4-29 (located at the southeastern extremity of the plume, to the east
of TW4-26 and to the south of TW4-27) and at TW4-30 (located immediately cross-to
downgradient of TW4-29), are also generally consistent with ongoing, but slow, downgradient
migration of chloroform. Chloroform at TW4-29 increased slightly from 537 µg/L to 549 µg/L,
and chloroform at TW4-30, located immediately cross-to downgradient of TW4-29, increased
from approximately 32 µg/L to approximately 35 µg/L. Concentration trends at these wells are
generally consistent with ongoing, but slow, downgradient migration of chloroform at these
locations. Chloroform at TW4-29 is bounded to the north by TW4-27 (7.6 µg/L), to the east by
TW4-30 (35 µg/L), to the southeast by TW4-35 (non-detect), to the south by TW4-34 (non-
detect), and to the west-northwest by TW4-6 (approximately 16 µg/L) and TW4-23 (non-detect).
In addition, general increases in concentrations at TW4-26 since the third quarter of 2016 are
35
consistent with continuing downgradient chloroform migration, which is likely enhanced by the
decay of the groundwater mound associated with the southern wildlife pond.
Chloroform at TW4-33 (located between TW4-4 and TW4-29) showed a decrease in
concentration, from approximately 121 µg/L to 101 µg/L. Chloroform at TW4-33 is bounded to
the north by TW4-14 (6.1 µg/), to the east by TW4-27 (7.6 µg/L), and to the west by TW4-6
(approximately 16 µg/L) and TW4-23 (non-detect). Increases in concentration at TW4-26 since
the third quarter of 2016 have widened the southeast extremity of the plume, which historically
was narrow compared to more upgradient locations.
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for a slight
expansion near TW 4-16 and a slight contraction near TW 4-21. Chloroform concentrations at
TW4-21 decreased from approximately 734 µg/L to 596 µg/L shifting the plume boundary away
from TW4-25 (non-de_tect) located immediately to the north.
TW 4-9 remained outside the plume this quarter. Chloroform concentrations at TW 4-9 decreased
from approximately 68 µg/L to 66 µg/L further shifting the plume boundary away from TW4-38
(non-detect) located immediately to the east-southeast. TW4-9 was incorporated into the plume
from the first quarter of 2016 until the first quarter of 2019 due to increased concentrations
attributable to reduced recharge (and dilution) from the northern wildlife ponds. However, except
for the fourth quarter of 2014, TW4-9 was outside the plume prior to the first quarter of 2016.
Nitrate pumping generally caused the western boundary of the n01thern portion of the
chloroform plume to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-
24 has been both inside and outside the plume and remains outside the plume this quarter, likely
due to initiation of TW4-37 pumping in the second quarter of 2015 and reduced productivity at
TW4-24 (since the third quarter of 2014). Since the second quarter of 2014, generally increased
concentrations at TW4-6 and TW4-16, (both of which were within the chloroform plume in the
past) indicate that the plume boundary migrated to the southwest and re-incorporated both wells.
TW 4-16 remains within and TW 4-6 remains outside the plume this quarter. Increased
concentrations at these wells since the first quarter of 2014 are likely related to reduced dilution
from cessation of water delivery to the northern wildlife ponds and more westerly flow induced
by nitrate pumping. In addition, concentrations at TW4-6 may be influenced by reduced recharge
at the southern wildlife pond and the decay of the associated groundwater mound.
A decreasing trend in chloroform concentration at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 since the third quarter of 2016, suggest that TW4-
4 pumping has arrested chloroform migration between TW 4-4 and TW 4-6, and that the increased
chloroform at TW4-26 results from a remnant of the plume that continues to migrate south
toward TW4-26. Pumping at adjacent well TW4-41 since the second quarter of 2018 has likely
enhanced the decreases at TW 4-6 and resulted in concentrations at TW 4-6 that have dropped
below 70 µg/L.
Although the nitrate pumping system may redistribute chloroform within the plume and cause
changes in the chloroform plume boundaries, continued operation of the nitrate pumping system
36
is expected to enhance capture associated with the chloroform pumping system. Furthermore, the
addition of chloroform pumping wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-37, TW4-39,
TW 4-40 and TW 4-41 since the beginning of 2015 is expected to have a beneficial impact.
Generally reduced concentrations at TW4-6 (since the first quarter of 2015) and TW4-16 (since
the fourth quarter of 2014) after previous increases are likely the result of initiation of TW4-1,
TW4-2, and TW4-11 pumping.
Continued operation of chloroform pumping wells MW-4, MW-26, TW4-19, and TW4-20 is
recommended. Pumping these wells, regardless of any short-term fluctuations in concentrations
detected at the wells, helps to reduce downgradient chloroform migration by removing
chloroform mass and reducing hydraulic gradients, thereby allowing natural attenuation to be
more effective. Continued operation of chloroform pumping well TW4-4, augmented by
pumping at adjacent well TW4-41, is recommended to improve capture of chloroform to the
extent practical in the southern portion of the plume. The overall decrease in chloroform
concentrations at TW4-6 from 1,000 µg/L in the first quarter of 2010 to 10.3 µg/L in the second
qua1ter of 2014 is likely related to pumping at TW4-4. The decrease in the long-term rate of
water level rise at TW 4-6 once TW 4-4 pumping began, which suggests that TW 4-6 is within the
hydraulic influence of TW 4-4, is also consistent with the decrease in chloroform concentrations
at TW4-6 between the first quarter of 2010 and the second quarter of 2014. The decreasing trend
in water levels beginning in 2014 and, as noted above, the generally decreasing chloroform
concentrations since the first quarter of 2015 at TW4-6 are also attributable in part to TW4-4
pumping. Continued operation of TW4-1, TW4-2, TW4-11, TW4-21, TW4-37, TW4-39, TW4-
40 and TW 4-41 is recommended because pumping these wells has increased overall capture and
improved chloroform mass removal.
Furthermore, because of the influence of TW4-4 pumping (augmented by TW4-41 pumping
since the second quarter of 2018), and by analogy with the concentration decreases at TW4-6 and
TW4-26 that occurred after initiation of TW4-4 pumping, chloroform concentrations at TW4-29
and TW4-33 are expected to eventually trend downward. Since installation in 2013, however,
concentrations at TW 4-33 appear to be relatively stable to decreasing, while, since the third
quarter of 2014, concentrations at TW4-29 appear to be on an upward trend. The relatively stable
chloroform at TW4-33 and recent increases in concentration at TW4-29 suggest that chloroform
migration has been arrested at TW4-33 by TW4-4 pumping and that increasing chloroform at
downgradient well TW4-29 results from a remnant of the plume that continues to migrate
downgradient (toward TW4-30, which bounds to plume to the east). The influence of TW4-4
pumping at the distal end of the plume is consistent with decreasing water levels at both TW4-29
and TW4-33. Pumping at adjacent well TW4-41 is likely to help maintain or enhance these
decreasing trends in water levels and to augment the expected reductions in concentrations in the
distal end of the plume. Continued evaluation of trends at TW4-29 and TW4-33 will be provided
in subsequent quarters.
EFRI and its consultants have raised the issues and potential effects associated with cessation of
water delivery to the northern wildlife ponds in March, 2012 during discussions with DWMRC
in March 2012 and May 2013. While past recharge from the ponds has helped limit many
constituent concentrations within the chloroform and nitrate plumes by dilution, the associated
groundwater mounding has increased hydraulic gradients and contributed to plume migration.
37
Since use of the northern wildlife ponds ceased in March 2012, the reduction in recharge and
decay of the associated groundwater mound are expected to increase constituent concentrations
within the plumes while reducing hydraulic gradients and rates of plume migration. Generally
increased chloroform concentrations at TW4-6 (since the first quarter of 2014); and at TW4-8,
TW4-9 and TW4-16 (since 2013), are likely related in part to reduced dilution (although
concentrations at TW 4-6 and TW 4-8 have been trending downward since the first quarter of
2015). As discussed above, increased concentrations at TW4-26 since the third quarter of 2016
that are consistent with continuing downgradient chloroform migration are also likely enhanced
by the decay of the groundwater mound associated with the southern wildlife pond.
The net impact of reduced wildlife pond recharge is expected to be beneficial even though it is
also expected to result in higher concentrations that will persist until continued mass reduction
via pumping and natural attenuation ultimately reduce concentrations. Temporary increases in
chloroform concentrations are judged less important than reduced chloroform migration rates.
The actual impacts of reduced recharge on concentrations and migration rates will be defined by
continued monitoring.
9.0 ELECTRONIC DATA FILES AND FORMAT
EFRI has provided to the Director an electronic copy of the laboratory results for groundwater
quality monitoring conducted under the chloroform contaminant investigation during the quarter,
in Comma Separated Values format. A copy of the transmittal e-mail is included under Tab M.
38
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc.
Energy Fuels Resources (USA) Inc.
By:
Scott A. Bakken Da\e \
Senior Director Regulatory Affairs
39
Certification:
I certify, under penalty of law, that this document and all attachments were prepared
under my direction or supervision in accordance with a system designed to assure that qualified
personnel properly gather and evaluate the information submitted. Based on my inquiry of the
person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate,
and complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations.
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
40
Tables
Table 1: Summary of Well Sampling for the Period
Well Sample Date Date of Lab Report
MW-04 9/4/2019 9/20/2019
TW4-01 9/4/2019 9/20/2019
TW4-02 9/4/2019 9/20/2019
TW4-03 9/11/2019 9/30/2019 10/23/19
TW4-03R 9/10/2019 9/30/2019 10/23/19
TW4-04 9/4/2019 9/20/2019
TW4-05 9/11/2019 9/30/2019 10/23/19
TW4-06 9/11/2019 9/30/2019 10/23/19
TW4-07 9/12/2019 9/30/2019 10/23/l 9
TW4-08 9/12/2019 9/3012019 10/23/19
TW4-09 9/11/2019 9/30/2019 10/23/19
TW4-10 9/12/2019 9/30/2019 10/23/19
TW4-ll 9/4/2019 9/20/2019
TW4-I2 9/11/2019 9/30/2019 10/23/19
TW4-13 9/11/2019 9/30/2019 10/23/19
TW4-14 9/11/2019 9/30/2019 10/23/19
MW-26 9/4/2019 9/20/2019
TW4-16 9/12/2019 9/30/2019 10/23/19
TW4-16R 9/11/2019 9/30/2019 10/23/19
MW-32 9/11/2019 9/30/2019 10/23/19
TW4-18 9/11/2019 9/30/2019 10/23/19
TW4-I9 9/4/2019 9/20/2019
TW4-20 9/4/2019 9/20/2019
TW4-21 9/4/2019 9/20/2019
TW4-22 9/4/2019 9/20/2019
TW4-23 9/11/2019 9/3012019 10/23/19
TW4-24 9/4/2019 9/20/2019
TW4-25 9/4/2019 9/20/2019
TW4-26 9/12/2019 9/30/2019 10/23/19
TW4-27 9/11/2019 9/30/2019 10/23/19
TW4-28 9/11/2019 9/30/2019 10/23/19
TW4-29 9/12/2019 9/30/2019 10/23/19
TW4-30 9/11/2019 9/30/2019 10/23/19
TW4-3I 9/11/2019 9/30/2019 10/23/J 9
TW4-32 9/11/2019 9/30/2019 10/23/19
TW4-33 9/12/2019 9/30/2019 10/23/19
TW4-34 9/11/2019 9/30/2019 10/23/19
TW4-35 9/11/2019 9/30/2019 10/23/19
TW4-36 9/11/2019 9/30/2019 10/23/19
TW4-37 9/4/2019 9/20/2019
TW4-38 9/11/2019 9/30/2019 10/23/19
TW4-39 9/4/2019 9/20/2019
TW4-40 9/4/2019 9/20/2019
TW4-41 9/4/2019 9/20/2019
TW4-42 9/11/2019 9/30/2019 10/23/19
TW4-60 9/4/2019 9/20/2019
TW4-65 9/11/2019 9/30/2019 10/23/19
TW4-70 9/11/2019 9/30/2019 10/23/ 19
TW4-75 9/12/2019 9/30/2019 10/23/19
All sample locations were sampled for Chloroform, Carbon Tetrachloride, Chloromethane,
Methylene Chloride, Chloride and Nitrogen.
"R" following a well number deisgnates a rinsate sample collected prior to purging of the well of that#.
TW4-60 is a DI Field Blank, TW4-65 is a duplicate of TW4-03, and TW4-70 is a duplicate of
TW4-05 and TW4-75 is a duplicate of TW4-08.
Highlighted wells are continuously pumped.
Notes:
Dates in italics are the original laboratory submission dates. Resubmissions were required to
correct reporting errors or to address reanalyses.
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture Zone Details
Map, and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater Elevations over Time
for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QNQC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank Evaluations
I-7 QNQC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform Isoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
Tab N Exceedance Notices for the Reporting Period
Tab A
Site Plan and Perched Well Locations White Mesa Site
TW4-42
¢ temporary perched monitoring well
installed April 2019
TW4-40 perched chloroform pumping well EB installed February 2018
TW4-19 perched chloroform or EB nitrate pumping well
MW-38
-¢-perched monitoring well installed
February 2018
MW-5 • perched monitoring well
TW4-12
0 temporary perched monitoring well
TWN-7 temporary perched nitrate monitoring ~ well
PIEZ-1
~ perched piezometer
RUIN SPRING o seep or spring
HYDRO
GEO
CHEM,INC.
WHITE MESA SITE PLAN SHOWING LOCATIONS OF
PERCHED WELLS AND PIEZOMETERS
APPROVED DATE REFERENCE
H:/718000/aug19/Uwelloc0619.srf
FIGURE A-1
TabB
Order of Sampling and Field Data Worksheets
Order of Contamination for 3rd Quarter 2019 Chlorofonn Purging Event
Chloroform Water Well
Well ., .Sample time Levels Rlnsate date/time level Oeplb
' . ..,.,.'f,.,..,y.'4~,()~3..,,..q/~ll,.a,./.,.,,19~07=15....,,ND-=---------===--=----:-:14~1 """"i"vJ'-l -0 ~ R _ 09 IO zo IC\
TW4~28ti·W /19 oi~D ND ---107
TW4-32~· . "f8ND 115.1
TW4-12 075.S ND 101.5
TW4-1J ~ II ND 102.5
TW4-36 'j/11/lq QgJ"Z ND 99
TW4-31'\lll/L'f s)g'20, ND ---106
TW4-42 9,/ll/(o\ Q~,· ND 86
TW4-34 qJl\/l9 0~':f3 ND 97.2
TW4-35<J/ll /l'I QS53 ND 87.5
TW4-231£U m oCJo-z. ND 114
MW-32 "'lit lfl: I "l:!>5 ND 130.6 Bladder pump
TW4-38 Vt17 ~ OCjZC\ ND ---112.75 ·
TW4-25 'U:!Lli Jz.;~ ND 134.8 Cont. Pumping
TW4-!4 '1/W.j<:j Oj~l) 4.18 93
TW4-27.ffi<\"1"7 8.24 96
TW4-05 0 Q 15.8 ---120
TW4-06 /Ill 010 15.8 ---97.5 fii ·TW4-24'\/':i lq J1'\8 . ·28.8 112.5 Cont. Pumping ·••
TW4-3b / 31.5 92.5
TW4-18 / 54.2 137.5
TW4-09 120
TW4-16 ~~t--::-::~~ ---_-_-146.3 "'T"w'-l-l&R. _ O'lll20l'\ Jl LO
TW4-08 125
TW4 .. 33.J/-i,--,'--;~~ ---87.9
TW4-40 ~"-'-''--'~~ 86 Cont. Pumping
TW4-60 D.I. Blank ~t~m
TW4-65 Duplicate ~-lllLI~ TW4-70 Duplicate ~£~2\1 TW4-75 Duplicate
Comments:
J.500
07t5
JOOD
0117
93.5
121 Cont. Pumping
Ill
120
110 Cont. Pumping
86
112 Cont. Pumping
___ 122.5 Cont. Pumping
124 Cont. Pumping
___ 97.75 Cont. Pumping
120 Cont. Pumping
100 Cont. Pumping
113.5 Cont. Pumping
120 Cont. Pumping
125 Cont. Pumping
l 06 Cont. Pumping
112 Cont. Pumping
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-04 Sampling Program Chloroform Monitorin_g_
Field Sample ID MW-04 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:01
Sample Date & Time 9/4/2019 14:02 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature {C) 31
Purging Method 2 Casings Previous Well Sampled TW4-02
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 123.60
pH Buffer 4.0 4.0 Well Casing Diameter (in) 3
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 83.67
DatefTime Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/4/2019 14:01 1790 6.86 17.89 271 1.5 31.5
Pumping Rate Calculations
[volume of water purged O Flow Rate (Q = S/60) (gal/min) 4.0
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 89.21 Number of casing Volumes
Volume, if well evacuated to dryness {) 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived~ site at 1_3~9. Samples collected at 1402. Water was clear. Left site at 1405.
Signature of Field Technician
..:.:'>~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan -e-.. ~Ii_.,.. I 1 ,,
:
,..l!!l!!!!!!I! ~,~Y~S
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-01 -. Sampling Program Chloroform Monitoring
Field Sample ID TW4-01_09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:10
Sample Date & Time 9/4/2019 14:11 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled MW-04
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 111.30
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 85.22
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO I Before/ After
9/4/2019 14:10 2201 6.87 19.16 329 5.6 85.2
[volume <>f water purged ()
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 14.0
I Final Depth to Water (feet) 99.98
Time to evacuate 2 Casing Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2}, 4 Deg C y
Comments:
[Arrived on site at 1407. Samples collected at 1411. Water was clear. Left site at 1413.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-02 Sampling P!og_ram Chloroform Monitoring
Field Sample ID TW4-02 09042019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:52
Sample Date & Time 9/4/2019 13:53 [sameler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-11
Casing Volume {)
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 120.90
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 88.63
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity_ DO Before/After
9/4/2019 13:52 3590 6.74 22.11 403 0 81.5
Pumping Rate Calculations
!Volume of water purged () Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 106.11 Number of casing Volumes
Volume, if well evacuated to dryness O 0
Name of Certified Anal}'tical Laboratory
AWSL
Anal}'tical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[P.r!ived <>n~ite at 1350. Samples collected at 1353. Water was clear. Left site at 1356.
Signature of Field Technician
~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
c. :s-Field Data Worksheet For Groundwater
Location ID TW4-03 Sampling Program Sampling Program Chloroform Monitoring Chloroform Monitoring
Field Sample ID TW4-03 09112019 Sampling Event Sampling Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 6:48
Sample Date & Time 9/11/2019 7:15 !sampler [sampler I TH/DL TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 16
Purging Method 2 Casings Previous Well Sampled TW4-03R
Casing Volume (gal) 50.94
Calculated Casing Volumes Purge Duration (min) 9.26
pH Buffer 7.0 7.0 Well Depth (ft) 140.30
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 62.28
Dateffime Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/ After
9/10/2019 6:54 71.50 1720 6.57 14.74 248 11.2 82.4
9/11/2019 7:14 1687 6.85 15.12 Before
9/11/2019 7:17 1695 6.84 15.17 After
Pumping Rate Calculations
!volume of water purged (gals) 71.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 6.50 I Final Depth to Water (feet) 138.45 Number of casing Volumes 1.40
Volume, if well evacuated to dryness (gals) 71.50
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0644. Purge began at 0648. Purged well for a total of 6 minutes and 30 seconds. Purged well dry. Purge ended at 0654. Water was clear. Left site at 0657. Arrived on site
at 0711 . Depth to water was 62.55. Samples bailed and collected at 0715. Left site at 0721.
Signature of Field Technician
I
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mm
Field Data Worksheet For Groundwater
Location ID TW4-03R Sampling Program
Field Sample ID TW4-03R 09102019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time
Sample Date & Time 9/10/2019 6:27 !sampler I TH/DL I
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sampled
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing Diameter (}
Specific Conductance () Depth to Water Before Purging (ft)
Date/Time I Gallons Purged Conductivity pH Temp (Deg C) I Redox Turbidity I DO I Before/After
9/10/2019 6:26 I 130.00 9.5 7.15 21.31 I 231 1.8 I 87.4 I
Pumping Rate Calculations
[volume of water purged O Flow Rate (Q = S/_§0) ()
Time to evacuate 2 Casing Volumes ()
[ Fi'!!II _Qepth to W~ter (feet) Number of casing Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
Chloride y WATER 1 500-ml Poly u None N
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Signature of Field Technician
~uAJ\
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-04 Sami>_ling Program rogram Chloroform Monitoring Chloroform Monitoring
Field Sample ID TW4-04 09042019 Sampling Event Sameling Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:24
Sample Date & Time 9/4/2019 14:25 !sampler I TH/Dl I [sampler TH/Dl
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-41
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 114.50
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.45
Date/Time I Gallons Purged Conductivity pH Temp (Deg C) l Redox Turbidity I DO I Before/After
9/4/2019 14:24 I 2198 6.79 17.75 I 348 2.1 I 111.5 I
Pumping_ Rate Calculations
[volume of water purged () Flow Rate (Q = S/60) (gal/min) 16.0
Time to evacuate 2 Casing Volumes O
[Final Depth to Water (feet} 83.87 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Anal~ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2}, 4 Deg C y
Comments:
[Arrived on site at 1420. Samples collected at 1425. Water was clear. Left site at 1428.
Signature of Field Technician
...:3~t>-Z:
Groundwater Discharge Permit
~-F-:: .. ::,----1 -.~ ,
.,.-I ~
.. ., ,r~y~
•' I
Groundwater Monitoring Quality Assurance Plan
s
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-05 Sampling Program Chloroform Monitoring
Field Sample ID TW4-05 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 14:34
Sample Date & Time 9/11/2019 10:00 !sampler I TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature {C) 24
Purging Method 2 Casings Previous Well Sampled TW4-27
Casing Volume (gal) 34.08
Calculated Casing Volumes Purge Duration (min) 6.19
pH Buffer 7.0 7.0 Well Depth (ft) 121.85
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 69.65
DatefTime Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 14:39 55.00 1415 7.15 15.48 295 6.1 57.9
9/10/2019 14:40 66.00 1406 6.95 15.49 310 6.0 58.2
9/10/2019 14:41 77.00 1398 6.89 15.49 330 6.2 54.0
9/10/2019 14:42 88.00 1391 6.89 15.49 340 6.1 52.0
!volume of water purged (gals)
Pum_eing Rate Calculations
88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
!Final Dep_th to Water (feet) 71.02 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1431. Purge began at 1434. Purged well for a total of 8 minutes. Purge ended at 1442. Water was clear. Left site at 1445. Arrived on site at 0956. Depth to water was
69.92. Samples bailed and collected at 1000. Left site at 1005.
Signature of Field Technician
I
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-06 Sampling Program Chloroform Monitoring
Field Sample ID TW4-06 09112019 Samp_li.ng Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 15:10
Sample Date & Time 9/11/2019 10:10 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-05
Casing Volume (gal) 14.99
Calculated Casing Volumes Purge Duration (min) 2.72
pH Buffer 7.0 7.0 Well Depth (ft) 99.60
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 76.64
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 15:13 16.50 3618 6.45 15.85 286 18.4 24.0
9/11/2019 10:09 3614 6.49 15.22 Before
9/11/2019 10:11 3612 6.49 15.25 After
Pumping Rate Calculations
[ Volume of water purged (gals) 16.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min} 1.50
[Final Depth to Water (feet) 97.67 Number of casing Volumes 1.10
Volume, if well evacuated to dryness (gals) 16.50
Name of Certified Anal~ical Laboratory_
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 SOO-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1507. Purge began at 1510. Purged well for a total of 1 minute and 30 seconds. Water was mostly clear. Purge ended at 1512. Left site at 1515. Arrived on site at 1007.
Depth to water was 77.21 . Samples bailed and collected at 1010. Left site at 1013.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-07 Sampling Program Same_l_Lng_ Program Chloroform Monitoring Chloroform Monitoring
Field Sample ID TW4-07 09122019 Sampling Event Samp_li_ng Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 14:20
Sample Date & Time 9/12/2019 8:08 !sampler [same_ler I TH/DL TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 26
Purging Method 2 Casings Previous Well Sampled TW4-10
Casing Volume (gal) 25.76
Calculated Casing Volumes Purge Duration (min) 4.68
pH Buffer 7.0 7.0 Well Depth (ft) 121.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 81.55
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 14:24 52.25 1568 7.13 15.01 300 57.0 23.6
9/12/2019 8:07 1431 6.98 13.80 Before
9/12/2019 8:09 1430 7.02 13.82 After
~olume of water purged (gals)
Pumping_ Rate Calculations
52.25 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.75
[Final Depth to Water (feet) 118.89 Number of casing Volumes 2.00
Volume, if well evacuated to dryness (gals) 52.25
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1417. Purge began at 1420. Purged well for a total of 4 minutes and 45 seconds. Purged well dry. Purge ended at 1425. Water was clear. Left site at 1427. Arrived on
site at 0804. Depth to water was 84.75. Sami:,les bailed and collected at 0808. Left site at 0811 .
Signature of Field Technician
I
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-08 Sampling Program Chloroform Monitoring
Field Sample ID TW4-08 09122019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 12:16
Sample Date & Time 9/12/2019 7:17 !sampler I TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-16
Casing Volume (gal) 27.09
Calculated Casing Volumes Purge Duration (min) 4.92
pH Buffer 7.0 7.0 Well Depth (ft) 126.20
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 84.71
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 12:19 33.00 4619 6.71 15.16 120 2.0 0
9/11/2019 12:20 44.00 4626 6.70 15.13 126 2.0 0
9/11/2019 12:21 55.00 4631 6.65 15.12 130 1.9 0
9/11/2019 12:22 66.00 4629 6.65 15.12 134 1.9 0
Pumping Rate Calculations
!Volume of water purged (gals) 66.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 6.00
[Final Dept'!_ to Wate_l"_(feet) 102.23 Number of casing Volumes 2.00
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2}, 4 Deg C y
Comments:
Arrived on site at 1213. Purge began at 1216. Purged well for a total of 6 minutes. Purge ended at 1222. Water was clear. Left site at 1224. Arrived on site at 0713. Depth to water
was 85.14. Samples bailed and collected at 0717. Left site at 0721 .
Signature of Field Technician
~G<.r~.rv-~
I
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-09 Sampling_ Program Chloroform Monitoring_
Field Sample ID TW4-09 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 16:43
Sample Date & Time 9/11/2019 10:45 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-18
Casing Volume (gal) 34.23
Calculated Casing Volumes Purge Duration (min) 6.22
pH Buffer 7.0 7.0 Well Depth (ft) 120.10
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 67.67
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 16:48 55.00 2318 6.80 15.10 120 22.4 0
9/10/2019 16:49 66.00 2320 6.80 15.10 124 24.0 0
9/10/2019 16:50 77.00 2317 6.75 15.09 127 25.0 0
9/10/2019 16:51 88.00 2317 6.70 15.07 130 25.0 0
Pumping Rate Calculations
!Volume of water purged (gals) 88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
[ Final Depth to Water (feet) 69.45 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Ch loroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2504 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1640. Purge began at 1643. Purged well for a total of 8 minutes. Purge ended at 1651. Water was mostly clear. Left site at 1655. Arrived on site at 1042. Depth to
water was 67.85. Samples bailed and collected at 1045. Left site at 1047.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-10 Sampling Program SamJ!IJng _F>_rogram Chloroform Monitoring Chloroform Monitoring
Field Sample ID TW4-10 09122019 Sampling Event Sam_eling Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 13:47
Sample Date & Time 9/12/2019 7:54 !sampler [sampler I TH/DL TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 26
Purging Method 2 Casings Previous Well Sampled TW4-29
Casing Volume (gal) 30.03
Calculated Casing Volumes Purge Duration (min) 5.46
pH Buffer 7.0 7.0 Well Depth (ft) 113.20
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 67.20
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 13:51 41.25 2712 6.77 15.27 202 12.8 5.4
9/12/2019 7:54 2556 6.58 13.80 Before
9/12/2019 7:55 2570 6.60 13.85 After
Pumping Rate Calculations
!Volume of water purged (gals) 41.25 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.75 I Final Depth to Water (feet) 111.10 Number of casing Volumes 1.37
Volume, if well evacuated to dryness (gals) 41.25
Name of Certified Analytical Laboratory
AWSL
AnalY!ical Sameles Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1344. Purge began at 1347. Purged well for a 3 minutes and 45 seconds. Purged well dry. Purge ended at 1351. Left site at 1353. Arrived on site at 0751. Depth to
water was 67.48. Sameles bailed and collected at 0754. Left site at 0757.
Signature of Field Technician
I
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-11 Sam_e_ling Program Chloroform Monitoring
Field Sample ID TW4-11 09042019 Sam_e_ling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:44
Sample Date & Time 9/4/2019 13:45 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled MW-26
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 102.40
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 92.99
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/4/2019 13:44 3463 6.73 20.82 307 0 89.1
Pumping Rate Calculations
[ Volume of w~te_!_purged () Flow Rate (Q = S/60) (gal/min) 16.0
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 101.32 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at ! 340. Samples collected at 1345. Water was clear. Left site at 1348.
Signature of Field Technician
~al>Jll..
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-12 Sampling__l'rogram Chloroform Monitoring
Field Sample ID TW4-12 09112019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 8:40
Sample Date & Time 9/11/2019 7:55 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled TW4-32
Casing Volume (gal) 32.22
Calculated Casing Volumes Purge Duration (min) 5.85
pH Buffer 7 .0 7.0 Well Depth (ft) 103.20
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 53.85
DatefTime Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 8:44 44.00 1500 7.30 14.93 227 4.9 21.2
9/11/2019 7:54 1308 7.23 14.61 Before
9/11/2019 7:56 1308 7.22 14.64 After
Pumping Rate Calculations
!volume of water eurged (g_als) 44.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.00
Number of casing Volumes 1.36 [Fi11~1 Depth to Wate_!_(feet) 100.89
Volume, if well evacuated to dryness (gals) 44.00
Name of Certified Analytical Laboratory_
AWSL
Analytical Same_les Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0837. Purge began at 0840. Purged well for a total of 4 minutes. Purged well dry. Purge ended at 0844. Water was clear. Left site at 0847. Arrived on site at 0752. Depth
to water was 53.92. Samples bailed and collected at 0755. Left site at 0758.
Signature of Field Technician
~-~r/"6'~
Groundwater Discharge Permit e~ . -i r o;I ..._ -r ~ ,· . '
. ~ .,. _ _)' E7tRSR!Gi'Y,::;a;_ s
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-13 Sampling Program Chloroform Monitoring
Field Sample ID TW4-13 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 9:14
Sample Date & Time 9/11/2019 8:04 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled TW4-12
Casing Volume (gal) 32.93
Calculated Casing Volumes Purge Duration (min) 5.98
pH Buffer 7 .o 7.0 Well Depth (ft) 105.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 55.26
Date/Time Gallons Purged Conductivity pH Temp (Deg C} Redox Turbidity DO Before/After
9/10/2019 9:18 41.25 1960 7.17 15.26 326 15.0 88.4
9/11/2019 8:03 1932 7.21 14.84 Before
9/11/2019 8:05 1934 7.20 14.86 After
Flow Rate {Q = S/60) (gal/min) 11.00 [volume of water pw·_ged (gals} 41.25
Pumping Rate Calculations
Time to evacuate 2 Casing Volumes (min) 3.75
[ Final Dep!h to_ Water (feet) 103.87 Number of casing Volumes 1.25
Volume, if well evacuated to dryness (gals) 41.25
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0911 . Purge began at 0914. Purged well for a total of 3 minutes and 45 seconds. Purged well dry. Purge ended at 0918. Water was mostly clear. Left site at 0921 . Arrived
on site at 0801 . Depth to water was 55.41 . Samples bailed and collected at 0804. Left site at 0807.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-14 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-14 09112019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 13:33
Sample Date & Time 9/11/2019 9:40 !sa111eler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-38
Casing Volume (gal) 11.41
Calculated Casing Volumes Purge Duration (min) 2.07
pH Buffer 7 .0 7.0 Well Depth (ft) 95.10
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 77.62
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/ After
9/10/2019 13:34 14.66 4866 6.57 16.13 199 28.4 92.0
9/11/2019 9:39 4876 6.24 15.30 Before
9/11/2019 9:41 4872 6.23 15.35 After
!Volume of water purg_ed (_g_als)
Pum_e_in_g_ Rate Calculations
14.66 -
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.34
!Final Depth~o Water (feet} 93.24 Number of casing Volumes 1.28
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Analytical Labo~1ory
AWSL
AnalY!i_cal Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1330. Purge began at 1333. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 1334. Water was mostly clear. Left site at 1337. Arrived on site
at 0936. Depth to water was 77.72. Samples bailed and collected at 0940. Left site at 0942.
Signature of Field Technician
~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-26 ----, Sampling Program Chloroform Monitoring
Field Sample ID MW-26 09042019 Samelin_g_ Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:29
Sample Date & Time 9/4/2019 13:30 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-39
Casing Volume ()
Calculated Casing Volumes Purge Duration O
pH Buffer 7.0 7.0 Well Depth (ft) 121.33
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 75.23
Date/Time Gallons Purged Conductivity _e_H Temi:> (Deg C) Redox Turbidity DO Before/After
9/4/2019 13:29 3277 6.62 18.49 399 10.9 12.9
[volume of water purged()
Pump_i_llg Rate Calculations
Flow Rate (Q = S/60) (gal/min) 10.0
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 87.89 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sam_e_les Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
!Arrived on site at 1327. Samples collected at 1330. Water was clear. Left site at 1333.
Signature of Field Technician
Groundwater Discharge Permit e .. l . ' ., --. a,/_~FLearS
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-16 Sampling Program Chloroform Monitoring_
Field Sample ID T\N4-16 09122019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 11:32
Sample Date & Time 9/12/2019 7:08 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-16R
Casing Volume (gal) 49.48
Calculated Casing Volumes Purge Duration (min) 8.99
pH Buffer 7.0 7.0 Well Depth (ft) 147.60
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 71.82
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 11:40 88.00 3401 6.96 14.92 211 14.2 0
9/11/2019 11:41 99.00 3405 6.78 14.92 208 11.8 0
9/11/2019 11:42 110.00 3380 6.75 14.92 210 11.2 0
9/11/2019 11:43 121.00 3360 6.72 14.92 208 11.5 0
Pumping Rate Calculations
[volu!"e of water pu!ged (gals) 121.00 Flow Rate {Q = S/60) (gal/min) 11.00
Time to evacuate 2 CasingVolumes (min) 11.00
§:nal Depth to _Water (fe~l 140.11 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Anal~P!I Laborat~ry
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y \NATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y \NATER 1 500-ml Poly u None N
Nitrate/nitrite as N y \NATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1129. Purge began at 1132. Purged well for a total of 11 minutes. Purge ended at 1143. \Nater was mostly clear. Left site at 1146. Arrived on site at 0704. Depth to water
was 72.19. Samples bailed and collected at 0708. Left site at 071 o.
Signature of Field Technician
~~/"6 ~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-16R Sampling Program
Field Sample ID TW4-16R 09112019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time
Sample Date & Time 9/11/2019 11:10 !sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sampled
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing_ Diameter O
Specific Conductance () Depth to Water Before Purging (ft)
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/ After
9/11/2019 11:09 130.00 2.0 5.95 20.12 312 5.5 72.0
Pumping Rate Calculations
[volume of water purged() Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) Number of casing Volumes
Volume, if well evacuated to drynes~l
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2}, 4 Deg C y
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Comments:
Signature of Field Technician
-.:3 ~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~'F-:. ,/ .· .~ .· I·· ,•
~---!~: 1· __ · --~~-eez:s
,_.. j
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-32 Sampling !1_!_ogram rogram Chloroform Monitoring Chloroform Monitoring
Field Sample ID MW-32 09112019 Sampling Event Sampling Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 9:25
Sample Date & Time 9/11/2019 14:35 !sampler [sampler I TH/DL TH/DL I
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type QED External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled N/A
Casing Volume (gal) 32.74
Calculated Casing Volumes Purge Duration (min) 301.76
pH Buffer 7.0 7.0 Well Depth (ft) 130.60
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 80.46
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 14:32 66.61 3435 6.38 15.43 287 35.0 0
9/11/2019 14:33 66.83 3458 6.37 15.40 283 36.0 0
9/11/2019 14:34 67.05 3466 6.36 15.34 280 36.9 0
9/11/2019 14:35 67.27 3464 6.35 15.30 278 37.0 0
Pumping Rate Calculations
[volume of water purged (gals) 67.27 Flow Rate (Q :a S/60) (gal/min) .217
Time to evacuate 2 Casing Volumes (min) 310.00
[ Final Depth to Water (feet) 86.22 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Anal}'t_ical Laboratory
AWSL
Analytical Same_les Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 0920. Purge began at 0925. Purged well for a total of 31 O minutes._EtJr~~n.c!ed and samples._c;ollected at 1435. Water was a little murky. Left site at 1441 .
Signature of Field Technician
Groundwater Discharge Permit e.·~ •. ~ I ·' -_ ... ,. .. ~. -...,,,~_,v ~~ s
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-18 Sampling_Program Chloroform Monitoring
Field Sample ID TW4-18 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 16:07
Sample Date & Time 9/11/2019 10:35 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-30
Casing Volume (gal) 43.19
Calculated Casing Volumes Purge Duration (min) 7.85
pH Buffer 7.0 7.0 Well Depth (ft) 136.90
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 70.75
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 16:13 66.00 1657 6.80 15.45 170 14.6 16.8
9/10/2019 16:14 77 .00 1625 6.71 15.46 174 13.8 17.9
9/10/2019 16:15 88.00 1594 6.63 15.46 180 13.7 18.0
9/10/2019 16:16 99.00 1563 6.60 15.46 183 13.5 18.5
Pumping Rate Calculations
[volume~f water purged (gals) 99.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 9.00
[ Fina~ Depth to Water (feet) 71.20 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sameles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1604. Purge began at 1607. Purged well for a total of 9 minutes. Purge ended at 1616. Water was mostly clear. Left site at 1619. Arrived on site at 1032. Depth to water
was 70.91 . Samples bailed and collected at 1035. Left site at 1037.
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-19 Sampling Program Chloroform Monitoring
Field Sample ID TW4-19 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:44
Sample Date & Time 9/4/2019 14:45 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-40
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 126.86
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.98
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 14:44 2745 6.77 18.90 227 10.2 33.3
Pumping Rate Calculations
lvolum~ of water purged O Flow Rate (0 == S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 78.23 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
AnalytJcal Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at 1441 . Samples collected at 1445. Water was clear. Left site at 1448.
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-20 Sampling Program Chloroform Monitoring
Field Sample ID TW4-20 09042019 Samf)ling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:13
Sample Date & Time 9/4/2019 13:14 jsampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-37
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 105.90
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 73.77
DatefTime Gallons Purged Conductivity eH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 13:13 3934 6.35 18.76 400 1.5 45.0
Pumping Rate Calculations
jvolume of water purged () Flow Rate (Q = S/60) (gal/min) 6.4
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 76.85 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
jArrived on site at 1311. Samples collected at 1314. Water was clear. Left site at 1317.
Signature of Field Technician
~«J~t'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-21 Sampling Program Chloroform Monitoring
Field Sample ID TW4-21 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 12:27
Sample Date & Time 9/4/2019 12:28 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 30
Purging Method 2 Casings Previous Well Sampled N/A
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .0 7.0 Well Depth (ft) 118.80
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 81.33
Date!Time Gallons Purged Conductivity eH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 12:27 3124 6.65 18.25 393 0 47.4
Pumping Rate Calculations
jvolume of water purged() Flow Rate (Q = S/60) (gal/min) 12.8
I f'inal Depth to Water (feet) 90.89
Time to evacuate 2 Casing Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at 1225. Samples collected at 1228. Water was clear. Left site at 1232.
Signature of Field Technician
-:3"'~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-22 Sampling Program Chloroform Monitoring
Field Sample ID TW4-22 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 12:57
Sample Date & Time 9/4/2019 12:58 !sampler TH/GP
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-24
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .0 7.0 Well Depth {ft) 114.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 76.22
Date/Time Gallons Purged Conductivity pH Temp (De_g_ C) Redox Turbidity DO Before/After
9/4/2019 12:57 5161 7.14 18.10 248 5.1 104.3
jvolume of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes O
[ Final Depth to Water (feet) 100.34 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at 1255. Samples collected at 1258. Water was mostly clear. Left site at 1302.
Signature of Field Technician
~~~
Groundwater Discharge Permrt
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-23 Sampli11_g__!'ro_g_ram Chloroform Monitoring
Field Sample ID TW4-23 09112019 Sameli11_9_ Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 12:23
Sample Date & Time 9/11/2019 9:02 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-35
Casing Volume (gal) 28.00
Calculated Casing Volumes Purge Duration (min) 5.09
pH Buffer 7.0 7.0 Well Depth (ft) 116.40
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 73.52
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 12:28 55.00 3282 7.00 14.46 190 19.6 85.7
9/10/2019 12:29 66.00 3298 6.97 14.44 194 20.0 87.9
9/10/2019 12:30 77 .00 3307 6.89 14.45 200 20.5 91.0
9/10/2019 12:31 88.00 3288 6.83 14.50 204 21.1 92.0
Pumpin_g_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00 [volume of water purgl!d (galsl 88.00
Time to evacuate 2 Casing Volumes (min) 8.00
[Final Depth to Water (feet) 92.65 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analyt_ic:al Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1220. Purge began at 1223. Purged well for a total of 8 minutes. Purge ended at 1231. Water had an orange coloration but was clearing as purge went on. Left site at 1234.
Arrived on site at 0859. Depth to water was 73.64. Samples bailed and collected at 0902. Left site at 0904.
Signature of Field Technician
~u..,·>..rVL,,c---l-:,rL--~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-24 Sampling Program Chloroform Monitoring
Field Sample ID TW4-24 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 12:46
Sample Date & Time 9/4/2019 12:48 [sampler TH/GP
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-25
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .O 7.0 Well Depth (ft) 114.80
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 75.98
Date!Time Gallons Purged Conductivity pH Temp (De_g_ C) Redox Turbidity DO Before/After
9/4/2019 12:47 8219 6.71 17.65 337 0 29.2
Flow Rate (Q = S/60) (gal/min) 16.0 §1ume of water purged ()
Pumping Rate Calculations
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 84.23 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytic~t Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at 1245. Samples collected at 1248. Water was clear with little air bubbles surfacing. Left site at 1252.
Signature of Field Technician
Groundwater Discharge Permit e-·F-,' .·· ,,_---, I .r .
~· ~/j . . _~ !1.:". _/~y~-s,;s
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-25 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-25 09042019 Samplin_g_ Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 12:36
Sample Date & Time 9/4/2019 12:38 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 30
Purging Method 2 Casings Previous Well Sampled TW4-21
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 136.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 71.89
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 12:37 2256 6.91 17.60 368 1.8 31.7
[yol_lJ_111e of water purged ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 12.8
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 85.12 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 {pH<2), 4 Deg C y
Comments:
!Arrived on site at 1235. Samples collected at 1238. Water was clear. Left site at 1241 .
Signature of Field Technician
-::3~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-26 Sampling Program Chloroform Monitoring
Field Sample ID TW4-26 09122019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 15:06
Sample Date & Time 9/12/2019 8:17 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 26
Purging Method 2 Casings Previous Well Sampled TW4-07
Casing Volume (gal) 10.87
Calculated Casing Volumes Purge Duration (min) 1.97
pH Buffer 7.0 7.0 Well Depth (ft) 87.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 71.05
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 15:07 11.00 4384 7.07 15.93 241 4.6 89.3
9/12/2019 8:16 4465 6.97 14.14 Before
9/12/2019 8:18 4461 6.98 14.15 After
Pumping Rate Calculations -
!Volume of water purged (gals) 11.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (mln) 1.00
[!:Jnal Depth to Water (feet) 85.88 Number of casing Volumes 1.01
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 {pH<2), 4 Deg C y
Comments:
Arrived on site at 1503. Purge began at 1506. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1507. Water was clear. Left site at 151 o. Arrived on site at 0813. Depth
to water was 71.65. Samples bailed and collected at 0817. Left site at 0819.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-27 Sampling Program Chloroform Monitoring
Field Sample ID TW4-27 09112019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 14:04
Sample Date & Time 9/11/2019 9:47 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-14
Casing Volume (gal) 11.14
Calculated Casing Volumes Purge Duration (min) 2.02
pH Buffer 7 .0 7.0 Well Depth (ft) 95.75
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 78.68
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 14:05 11.00 4782 6.80 15.90 207 15.9 33.1
9/11/2019 9:46 4658 6.52 15.11 Before
9/11/2019 9:48 4654 6.53 15.19 After
Pumping Rate Calculations
[~olume of water purged (gals) 11.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
[Final Depth to Water (feet) 93.65 Number of casing Volumes 0.98
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1401. Purge began at 1404. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1405. Water was mostly clear. Left site at 1408. Arrived on site at 0944.
Depth to water was 79.08. Samples bailed and collected at 0947. Left site at 0949.
Signature of Field Technician
~~=-~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-28 Sampling Pro_gram Chloroform Monitoring
Field Sample ID TW4-28 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 7:23
Sample Date & Time 9/11/2019 7:40 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 17
Purging Method 2 Casings Previous Well Sampled TW4-03
Casing Volume (gal) 40.29
Calculated Casing Volumes Purge Duration (min) 7.32
pH Buffer 7.0 7.0 Well Depth (ft) 108.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 46.77
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 7:27 49.50 1450 6.92 14.81 217 13.5 66.2
9/11/2019 7:39 1425 7.10 14.45 Before
9/11/2019 7:42 1429 7.12 14.46 After
[yolume of water purged (ga~) 49.50
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.50
!Final Depth to Water (feet) 106.23 Number of casing Volumes 1.22
Volume, if well evacuated to dryness (gals) 49.50
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0720. Purge began at 0723. Purged well for a total of 4 minutes and 30 seconds. Purged well dry. Purge ended at 0727. Water was clear. Left site at 0730. Arrived on
site at 0735. Depth to water was 46.92. Samples bailed and collected at 0740. Left site at 0743.
Signature of Field Technician
-2>~~
Groundwater Discharge Permtt
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-29 Sampli11_g Program Chloroform Monitoring
Field Sample ID TW4-29 09122019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 13:18
Sample Date & Time 9/12/2019 7:42 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature {C) 25
Purging Method 2 Casings Previous Well Sampled TW4-33
Casing Volume (gal) 11.63
Calculated Casing Volumes Purge Duration (min) 2.11
pH Buffer 7.0 7.0 Well Depth (ft) 94.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging {ft) 76.66
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/11/2019 13:19 11.00 3781 6.88 15.83 235 6.4 83.1
9/12/2019 7:41 3784 7.00 14.07 Before
9/12/2019 7:43 3788 6.98 14.10 After
!Volume of water purged (gals) 11.00
Puml)i'llg Rate Calculations -Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
[Final Depth to Water (feet) 92.17 Number of casing Volumes 0.94
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1315. Purge began at 1318. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1319. Left site at 1322. Water was clear. Arrived on site at 0738. Depth to
water was 76.86. Samf)_les bailed and collected at 0742. Left site at 0744.
Signature of Field Technician
Groundwater Discharge Permtt e ·w;=:· -· -,-.·. •. ,· .. : ' .,,, ...GY.F"L-S,:$ . ~. {' EJJL3 .,. ' '
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monttoring Quality Assurance Plan
Location ID TW4-30 Sampling Program Chloroform Monitoring
Field Sample ID TW4-30 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 15:39
Sample Date & Time 9/11/2019 10:22 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-06
Casing Volume (gal) 12.25
Calculated Casing Volumes Purge Duration (min) 2.22
pH Buffer 7.0 7.0 Well Depth (ft) 93.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.72
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 15:40 14.66 4402 5.25 15.90 382 143.0 61.8
9/11/2019 10:21 4161 5.60 15.03 Before
9/11/2019 10:23 4163 5.59 15.00 After
[volume of water purged (gals) 14.66
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.33
[ Final Depth to Water (feet) 91.20 Number of casing Volumes 1.19
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Analytical Laboratory
AWSL
Analytical_Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix . Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1536. Purge began at 1539. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 1540. Water was murky. Left site at 1542. Arrived on site at
1018. Depth to water was 7 4.91 . Samples bailed and collected at 1022. Left site at 1024.
Signature of Field Technician
~a~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-31 Sampling Program Chloroform Monitoring
Field Sample ID TW4-31 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 10:17
Sample Date & Time 9/11/2019 8:20 jsampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 22
Purging Method 2 Casings Previous Well Sampled TW4-36
Casing Volume (gal) 20.19
Calculated Casing Volumes Purge Duration (min) 3.67
pH Buffer 7 .0 7.0 Well Depth (ft) 107.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 76.55
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 10:19 22.00 3800 6.90 15.57 295 25.7 36.0
9/11/2019 8:19 3871 6.94 14.98 Before
9/11/2019 8:21 3873 6.94 14.99 After
Flow Rate (Q = S/60) (gal/min) 11.00 jvolume of water purged (gals) 22.00
Pumping_ Rate Calculations
Time to evacuate 2 Casing Volumes (min) 2.00 I Final Depth to Water (feet) 106.02 Number of casing Volumes 1.08
Volume, if well evacuated to dryness (gals} 22.00
Name of Certified Analytical Laboratory
AWSL
Anal}'t_ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1014. Purge began at 1017. Purged well for a total of 2 minutes. Purge well dry. Purge ended at 1019. Water was mostly clear. Left site at 1022. Arrived on site at 0817.
Depth to water was 76.64. Samples bailed and collected at 0820. Left site at 0823.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ---e~ .. ~-.· . ; . ,· ~M51:S ,, 1~ --~, '/~ --:-_!i'i .
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-32 Sampling Program Sampling Program Chloroform Monitoring Chloroform Monitoring
Field Sample ID TW4-32 09112019 Sampling Event Sampling Event 2019 Q3 Chloroform 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 8:01
Sample Date & Time 9/11/2019 7:48 !sampler I TH/DL l~mpler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 18
Purging Method 2 Casings Previous Well Sampled TW4-28
Casing Volume (gal) 39.05
Calculated Casing Volumes Purge Duration (min) 7.10
pH Buffer 7 .O 7.0 Well Depth (ft) 114.64
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 54.83
DatefTime Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 8:07 55.00 6090 4.36 14.81 333 15.4 0
9/10/2019 8:08 66.00 6093 4.35 14.83 332 15.6 0
9/10/2019 8:09 77.00 6095 4.33 14.85 331 16.0 0
9/10/2019 8:10 88.00 6099 4.32 14.85 330 16.0 0
!volume of water purg_~5f (gals) 88.00
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
[Final D_E!pth to Water'jfeet) 81.02 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical_ Laboratory
AWSL
Anal}'t_ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0758. Purge began at 0802. Purged well for a total of 8 minutes. Purge ended at 0810. Water started a milky white but slowly cleared. Pump and line had a salt like crystal
on it when pulled. Left site at 0812. Arrived on site at 0744. Depth to water was 54.84. Same_les bailed and collected at 0748. Left site at 0751.
Signature of Field Technician
2)~M~
I
Groundwater Discharge Permit
~F-:/ 7:-, :· .. ~
..... .~~ i --~ ~'
-. . I ----~. v ~Y'~ White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-33 Sampling Program Chloroform Monitoring
Field Sample ID TW4-33 09122019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/11/2019 12:50
Sample Date & Time 9/12/2019 7:32 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-08
Casing Volume (gal) 6.66
Calculated Casing Volumes Purge Duration (min) 1.21
pH Buffer 7.0 7.0 Well Depth (ft) 86.23
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 76.02
Date/Time Gallons Purged Conductivity pH Temp(Deg C) Redox Turbidity DO Before/After
9/11/2019 12:51 6.00 4420 6.77 17.10 258 10.8 75.2
9/12/2019 7:31 3956 7.30 14.81 Before
9/12/2019 7:33 3960 7.28 14.82 After
Pumping_ Rate Calculations
jvolum~ of water purged (gals) 6.00 Flow Rate (Q ::: S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) .52
jFinal Depth to Water (feet) 85.00 Number of casing Volumes 0.90
Volume, if well evacuated to dryness (gals) 6.00
Name of Certified Analytical Laboratory_
AWSL
Analytical Sami:>_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1247. Purge began at 1250. Purged well for a total of 35 seconds. Purged well dry. Purge ended at 1251 . Water was clear. Left site at 1253. Arrived on site at 0728. Depth to
water was 76.35. Samples bailed and collected at 0732. Left site at 0734.
Signature of Field Technician
2>a~~
Groundwater Discharge Penni!
Groundwater Monitoring Quality Assurance Plan e'"--~·· ,·' . . r -,. I . ...----,.
•. ,-r ....... --· 7.. . . ..-A· ' ,I '."I' ... ~..,,..~ ...... -~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-34 Sampling Program Chloroform Monitoring
Field Sample ID TW4-34 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 11:23
Sample Date & Time 9/11/2019 8:43 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-42
Casing Volume (gal) 13.69
Calculated Casing Volumes Purge Duration (min) 2.48
pH Buffer 7 .0 7.0 Well Depth (ft) 95.74
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.77
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 11:24 16.50 3372 6.88 15.75 239 15.7 33.8
9/11/2019 8:42 3272 6.98 14.94 Before
9/11/2019 8:44 3268 6.96 14.98 After
!volume ~f water purged (gals)
Pumping Rate Calculations
16.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.50 I Final Depth to Water (feet) 93.48 Number of casing Volumes 1.20
Volume, if well evacuated to dryness (gals) 16.50
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at, 120. Purge began at 1123. Purged well for a total of 1 minute and 30 seconds. Purged well dry. Purge-enc!effafTr24. Water-was mostly clear. Left site at 1127. Arrived
on site at 0840. Depth to water was 74.83. Samp_les bailed and collected at 0843. Left site at 0845.
Signature of Field Technician
~c,~7&-~
Groundwater Discharge Permit e·-~-_.·' ... ;,----:r::::=. . . .
r·' /< -·· _i' .
~· ~/ ,/~~ s
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-35 Sampling Program Chloroform Monitoring
Field Sample ID TW4-35 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 11:54
Sample Date & Time 9/11/2019 8:53 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-34
Casing Volume (gal) 7.75
Calculated Casing Volumes Purge Duration (min) 1.40
pH Buffer 7 .0 7.0 Well Depth {ft) 86.50
pH Buffer 4.0 4.0 Well Casing Diameter {in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging {ft) 74.63
Date/Time Gallons Purged Conductivity pH Temp {Deg C) Redox Turbidity DO Before/After
9/10/2019 11:55 7.33 4056 6.55 16.30 302 9.8 50.7
9/11/2019 8:52 4036 6.56 14.98 Before
9/11/2019 8:54 4040 6.53 15.00 After
Pumping Rate Calculations
[volume of water purged (gal_s) 7.33 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.66
[ Fina_l_D_t,_pth to Water (feet) 84.59 Number of casing Volumes 0.94
Volume, if well evacuated to dryness (gals) 7.33
Name of Certified Anal}'t_ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1151. Purge began at 1154. Purged well for a total of 40 seconds. Purged well dry. Purge ended at 1155. Water was mostly clear. Left site at 1158. Arrived on site at
0849. De.e_t_h to water was 74.68. Samples bailed and collected at 0853. Left site at 0855.
Signature of Field Technician
~~ ~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-36 Sampling P_l'ogram Chloroform Monitoring
Field Sample ID TW4-36 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 9:46
Sample Date & Time 9/11/2019 8:12 [same_ler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 22
Purging Method 2 Casings Previous Well Sampled TW4-13
Casing Volume (gal) 27.60
Calculated Casing Volumes Purge Duration (min) 5.01
pH Buffer 7.0 7.0 Well Depth (ft) 99.41
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 57.13
Date/Time Gallons Purged Conductivity pH Temp(Deg C) Redox Turbidity DO Before/After
9/10/2019 9:49 33.00 2279 6.75 15.32 267 99.0 2.4
9/11/2019 8:11 2275 6.95 14.99 Before
9/11/2019 8:13 2275 6.95 15.00 After
!Volume of water purged (gals) 33.00
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.00
[F=_inal Dei:,_th to Water (feet) 97.46 Number of casing Volumes 1.19
Volume. if well evacuated to dryness (gals) 33.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2504 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0943. Purge began at 0946. Purged well for a total of 3 minutes. Purged well dry. Water was murky. Purge ended at 0949. Left site at 0952. Arrived on site at 0808. Depth
to water was 57.87. Samples bailed and collected at 0812. Left site at 0815.
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-37 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-37 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:04
Sample Date & Time 9/4/2019 13:05 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-22
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .O 7.0 Well Depth (ft) 113.72
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 73.92
Date!Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 13:04 3512 6.64 17.60 339 0 82.6
jvolume of water purged ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes ()
ji=ina~ D~pth to Water (feet) 80.67 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Same_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VO Cs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HDPE u H2S04 (pH<2}, 4 Deg C y
Comments:
[ Arrived on ~ite at 1302. Sal'l'lples collected at 1305. Water was clear. Left site at 1309.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-38 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-38 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 12:58
Sample Date & Time 9/11/2019 9:29 !sam_i:>ler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-23
Casing Volume (gal) 36.65
Calculated Casing Volumes Purge Duration (min) 6.66
pH Buffer 7.0 7.0 Well Depth (ft) 113.92
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 57.79
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/ After
9/10/2019 13:02 44.00 1731 6.85 14.73 226 23.3 56.8
9/10/2019 13:03 55.00 1668 6.83 14.71 235 23.0 65.3
9/10/2019 13:04 66.00 1644 6.83 14.70 243 22.9 64.0
9/10/2019 13:05 77.00 1718 6.87 14.70 248 22.5 63.5
Pumping Rate Calculations
@_olume of water purged _(gals} 77.00 Flow Rate (Q = S/60) (gal/min) 11.00
Tlme to evacuate 2 Casing Volumes (min) 7.00
!Final Depth to Water (feet) 106.59 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1255. Purge began at 1258. Purged well for a total of 7 minutes. Purge ended at 1305. Water was mostly clear. Left site at 1308. Arrived on site at 0926. Depth to water
was 58.06. Samples bailed and collected at 0929. Left site at 0931 .
Signature of Field Technician
~
Groundwater Discharge Permit e -·~-:,---f r-----, ~ . ~. --f -< ;_ -7
---~' .'.c. ~ ~YFV!ELS
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-39 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-39 09042019 Same_ling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 13:21
Sample Date & Time 9/4/2019 13:22 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-20
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .0 7.0 Well Depth (ft) 120.74
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 72.29
Date!Time Gallons Pur_g_ed Conductivity e_H Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 13:21 2189 6.71 17.79 312 4.9 91.7
Pumping Rate Calculations
!volume of water purged() Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 79.53 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 1319. Samples collected at 1322. Water was clear. Left site at 1326.
Signature of Field Technician
-2>=~~
Groundwater Discharge Permit ------a ·~~ r ·., I, ,,,-..._--r ······ /L!!!!!!!! , /~y~s
. ~i _,,
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-40 Sampling Program Chloroform Monitoring
Field Sample ID TW4-40 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:32
Sample Date & Time 9/4/2019 14:33 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-04
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 86.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 70.70
Date/Time Gallons Purged Conductivity pH Temp {Deg C) Redox Turbidity DO Before/ After
9/4/2019 14:32 3667 6.35 17.00 345 14.9 83.1
Pumping Rate Calculations
!Volume of water purged() Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes ()
!Final Depth to Wate!Jfeet) 85.23 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Anal}'tical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2}, 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[Arrived on site at 1430. Samples collected at 1433. Water was clear. Left site at 1435.
Signature of Field Technician
~~/v~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-41 Sampling Program Chloroform Monitoring_
Field Sample ID TW4-41 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:17
Sample Date & Time 9/4/2019 14:18 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-01
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .0 7.0 Well Depth (ft) 97.75
pH Buffer 4.0 4.0 Well Casing Diameter (in) 6
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 86.10
Date/Time Gallons Purg_ed Conductivity pH Temp (Deg C) Redox Turbidity DO I Before/After
9/4/2019 14:17 2581 6.95 19.20 341 15.0 109.1
!volume of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 3.5
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 93.20 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Anal\fl_ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
!Arrived on site at 1_ 415. _SGt__ITlples collected at 1418. Water was clear. Left site at 1420.
Signature of Field Technician
--=:3~
Groundwater Discharge Permtt
Groundwater Monttoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-42 Sampling Program Chloroform Monitoring
Field Sample ID TW4-42 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/10/2019 10:46
Sample Date & Time 9/11/2019 8:33 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 22
Purging Method 2 Casings Previous Well Sampled TW4-31
Casing Volume (gal) 12.36
Calculated Casing Volumes Purge Duration (min) 2.24
pH Buffer 7.0 7.0 Well Depth (ft) 86.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 67.06
Date/Time Gallons Purged Conductivity pH Temp (Deg C) Redox Turbidity DO Before/After
9/10/2019 10:49 16.50 3012 7.25 15.80 235 3.9 110.5
9/11/2019 8:32 3165 7.21 14.77 Before
9/11/2019 8:34 3160 7.23 14.78 After
!Volume of water purged (gals) 16.50
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.50
!Final Depth to Water (feet) 84.21 Number of casing Volumes 1.33
Volume, if well evacuated to dryness (gals) 16.50
Name of Certified Anal)'t_ical Laboratory
AWSL
Analytical Sam_eles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-mLHDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1043. Purge began at 1046. Purged well for a total of 1 minute and 30 seconds. Purge ended at 1048. Purged well dry. Water was clear. Left site at 1053. Arrived on site
at 0830. De~h to water was 67.17. Sam1>_les bailed and collected at 0833. Left site at 0836.
Signature of Field Technician
..:=)-~·
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-60 Sampling Program Chloroform Monitoring
Field Sample ID TW4-60 09042019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time 9/4/2019 14:57
Sample Date & Time 9/4/2019 15:00 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 31
Purging Method 2 Casings Previous Well Sampled TW4-19
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft)
pH Buffer 4.0 4.0 Well Casing Diameter ()
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft)
Date/Time Gallons Purged Conductivity pH Temp (Deg_ C) Redox Turbidity DO I Before/After
9/4/2019 14:59 1.0 7.54 25.70 148 8.1 14.3
Pumping Rate Calculations
@~lume _of water purged () Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
[ i:=i_lial Depth to Water (feet) Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 {pH<2), 4 Deg C y
Comments:
[ Samples collected in lab at 1500
Signature of Field Technician
-:3~.
Groundwater Discharge Permit
;-e _--w;:-/ _-~-,' .. -
~~ f'i .•' / ~YF:a:1FrS ~·~.,,
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-65 Sampling Program
Field Sample ID TW4-65 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time
Sample Date & Time 9/11/2019 7:15 [sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature _Q
Purging Method Previous Well Sampled
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Dee_th (ft)
pH Buffer 4.0 Well Casing Diameter ()
Specific Conductance () Depth to Water Before Purging_ (ft)
Date/Time Gallons Purged Conductivity pH [ Temp (Deg C) [ Redox Turbidity DO [ Before/After I
Pumping Rate Calculations
[volume of water purged () Flow Rate (Q = S/60) ()
[Final _Qepth to Water (feet)
Time to evacuate 2 Casing_ Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory_
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Comments:
[ Duplicate of TW 4-03
Signature of Field Technician
--.:3~ -~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-70 Sampling Program
Field Sample ID TW4-70 09112019 Sampling Event 2019 Q3 Chloroform
Purge Date & Time
Sample Date & Time 9/11/2019 10:00 [sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sam_e_led
Casing Volume ()
Calculated Casing Volumes Purge Duration O
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing Diameter ()
Specific Conductance {) Depth to Water Before Purging (ft)
Date/Time Gallons Purg_ed Conductivity pH Temp (Deg Cl Redox Turbidity DO [ Before/After l
[volume of water purged()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) ()
! Final Depth to Water (feet)
Time to evacuate 2 Casing_ Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness()
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
Chloride y WATER 1 500-ml Poly u None N
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments: ! Duplicate of TW4-05
Signature of Field Technician
~=~
Groundwater Discharge Permit
~
. ~ ... ·· ,i'-:;-d ,,1 ~~ ..ENERG'YF'l:.M?P"S ~-'
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-75 Sampling Program
Field Sample ID TW4-75_09122019 Sampling_ Event 2019 Q3 Chloroform
Purge Date & Time
Sample Date & Time 9/12/2019 7:17 !sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature {)
Purging Method Previous Well Sam_e_led
Casing Volume {)
Calculated Casing Volumes Purge Duration {)
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing_Q_iameter ()
Specific Conductance {) Depth !O Water Before Purging (ft)
Date/Time Gallons Purged Conductivity pH I Temp (Deg C) I Redox Turbidity DO I Before/After I
Pumping Rate Calculations
!volume of water purged() Flow Rate (Q = S/60} ()
I Final Depth!o Water (feet)
Time to evacuate 2 Casing Volumes_()
Number of casing Volumes
Volume, if well evacuated to dry_ness ()
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VO Cs-Chloroform y WATER 3 40ml VOA u HCI (pH<2}, 4 Deg C y
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 {pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Comments:
!Duplicate ofTW4-08
Signature of Field Technician
TabC
Weekly and Monthly Depth to Water Data
Weekly Inspection Form
Date 1-,-Jq Name Duo G: '?a>Ao ,
System Operational Clf no note
T' 1me W II e D th* ep C ommen ts bl / ct· ctl ) an}! ero ems corre 1ve a ons
() s:11/.. MW-4 ~O.'I~ Flow ~.fl ._ No
Meter ~ /ct ~44'T. <"R ..... No
1/J~I~ MW-26 .., "" ~ c:, Flow I J q -No
Meter ~q tsui, q :ae No
J/Jn,;-TW4-19 -,~ . .,~ Flow 18.D .... No
Meter / 'fl n e; ~ ,. ~ ,a ... No
()7z,q TW4-20 7.1/. ~SI Flow C. i:J Va No
Meter 3 ()'f 1 7.:, qq ~ No
I) A 'i' ,.:z TW4-4 Q1.Q4 Flow / I,, I,/ .. No
Meter t:.11( n 1 1 .:J. 1 .... No
n1:i/,,. TWN-2 r;.~ :31,,, Flow 17.::t V. No
Meter I I , ~ t. ' ( ... R ._ No
/) 11/~ TW4-22 7~.7a Flow l '9.17 --No
Meter /'A / s:I ~ ~ /.. &;"' ... No
n1~r: TW4-24 -,'{, "" Flow 1.t;, I. ._ No
Meter J O i t. ~ .:l ~. ":\ ~ )a No
()'1/i TW4-25 7.:1. 01# Flow I I 1./ "'5 No
\ Meter , ., "D q • . ~ ,:; '* No
IJP."_,g TW4-1 <,1/J ~~ Flow ' .::l .'R .... No
Meter .:i q ':J 7 o I'-. q ~ No
IJs=l ~ I TW4-2 J 0/,,. flC/ Flow 1-8 n ... No
Meter '3 ~ t. ~ ~ 1. ~ Ve, No
()fl:J .~ TW4-11 q,, :ll Flow /~.~ V. No
Meter t; I 7.:::, /. ~ ._ No
07/'li'J TW4-21 '1'~. 1< Flow 17~ t. V. No
Meter 1 " ¥ 7 ~ ~ 1. ~ t? .. No
117~~ TW4-37 '"1~ ~ ~ Flow I fl l) ._ No
Meter 1 ~ 1 'I "Io I 1 ; ..... No
ntt~u:. TW4-39 ~I IA 1 Flow ,~.o -No
Meter "'q R J 'f ~. :J .... No
/)qt),< TW4-40 ...___ ..... ,,
"""1'1· .. -Flow !ff. {J -No
7tf.1CJ~ Meter ~ L 1c.:1 .78 "-No
ORr;J TW4-41 'RI;.~;/. Flow .<.~ .... No
Meter ~J I I 7 L/. '-1 I ~ No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Oate 7-9-l'l Name e D,10 6-: L7'rnaw,
System Operational (If no note
Tl me W II e D th* eo C t bl / ctl ti l ommen s an:it: ero ems corre ve ac ons
i14LJ!:l_ MW-4 81. ''7 Flow II. I) ... No
Meter -.:2 -1 n 1 ~ , "I • ..., q ~ No
1)4}1~3 MW-26 71/. 7., Flow , 2. -~ .... No
Meter ~t:/~7/JJ.1? ... No
/,I'},, 1/j"" TW4-19 71..~/ Flow I 9-.../'J 499 No
Meter 11/~f ll.lw\ 'ea No
09 l.ll TW4-20 -,-i_-,7 Flow
t.::. " -No
Meter -JO~ I~~. JR )&s No
"74 .!J.,. TW4-4 117. ~· Flow ,/.... t:J 'ea, No
Meter '-,.-, .,, '=I ct.~ -No
0"7a.f ,;' TWN-2 C'I! ~ &,, Flow JSI. IJ .... No
Meter , , fl ,, tHI 7i. 1. >alt No
IJtllJI{' TW4-22 ittA ..,, Flow ,-,_ ~ .. ~ No
Meter /-~ n 7,; 7., ::im... No
t) 7K'r;' TW4-24 'It"' 111:. Flow Jib. n *-No
Meter //JR l'1 7 ~ r:. ~ .:t... Via, No
07~~ TW4-25 .,~ ,!IC-Flow II.~ ,_. No
Meter UI §"'SI ::ti. ~'3 ~ No
--1 CJ--TW4-1 7~.~.., Flow /'\ _Cl -No
IJ«~ I Meter .:1 ~ 11 II 'I«.,. -No
01 ... ~ TW4-2 '"':a. . .., 7 Flow / '7 . .., -. No
Meter -;i ~ 7"/ ;3_q. D ~ No
nQ"I\CII TW4-11 QC'#, ct~ Flow It:,• a.4 ._ No
Meter t:._1• '1 !l . ct ¥:la No
0"1:::t..'"7 TW4-21 7~. 2-\ Flow I~ ~ ~ No
Meter 111 r:c.:, 71:': er t ~ No
/Jct I~ TW4-37 .., .,. • '.l ~ Flow /9..0 V.., No
Meter I J:' 1 q 7 <~. 'r' ~ No
Oil :i 7 TW4-39 .,, ... ., Flow 114."' v.. No
Meter 't; n J s? 1 ~ .~ -No
.1'0 'I' TW4-40 71. ~'f Flow ,. L7 ~ No
Meter q 13~<1.~~ ~ No
/J4t~ TW4-41 qO.A~ Flow ~n .. No
Meter !:1.11 o o fll. t:. < *AP No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Monthly Depth Check Form
Date 7 -g ... ,., Name 12«a.Crry«nan
Time Well Depth* Time Well De~th*
t:>gaa. MW-4 Sl,1~ Qq"IS TWN-1 "7.01
iJ 8S:I TW4-1 Z9:,3~ Q':t.~lf" TWN-2 S:4, "'
08!f£ TW4-2 lf2.~1 l:Z 09'1~ TWN-3 L./_;t . 07
l~.&.I TW4-3 --~ .. ~ ~q41 TWN-4 bO. Ot
a9a3 TW4-4 tll.:'.:ll 09:~&./ TWN-7 e.a.as
£~JS TW4-5 ~~.S'.t. 01~g TWN~18 "J.1,7
l~l2 TW4-6 :z,l;~a.. QS,'V) MW-27 Sb,77 ,~ ... TW4-7 !I & !i.:i IQIO MW-30 15.11.
,~~!/. TW4-8 ,~.:ia 100.~ MW-31 ~8 .93
l~3S: TW4-9 ,I. 5:S:
l~!:I I TW4-10 ti~.~~
(Z11!! TW4-11 S9s!S
l 3S'.Q TW4-12 23.~I
ll~Z TW4-13 ~ti l'l 5.'f TW4-28 ~f.u!I~
13!:ill TW4-14 1.1.1 I:3 1331 TW4-29 1'-,11
QSJ3 TW4-15 7..~J7~ li.l~ TW4-30 ~.It
l~YS: TW4-16 71,:1~ 132...2... TW4-31 2'id~9
\OQQ TW4-17 Y2Q .~I 13l8 TW4-32 5~.~"'" oqso TW4-18 "10.76 131, TW4-33 l 5'.1 :t 2.._
Ul.tl.~ TW4-19 l3.~I 131~ TW4-34 ':1.~. ,a
Qll2.Q TW4-20 :Z:3.'.?7 132,g TW4-35 :z~.-'aa.
Ql~ TW4-21 :t!.11 13~Y TW4-36 f.t.,.Q3
08.ll.< TW4-22 8~1:Zl l1Sll TW4-37 't.."l.,22
l!t. l '3 TW4-23 13,aS I !:I ?ai TW4-38 !Zt. l
a7.r;-,r TW4-24 S3.Q~ asa1 TW4-39 x,.1~
a,:\s::: TW4-25 :z.a"'a.£: D!3( TW4-40 ~(. £!I
L '1(}.! TW4-26 1.4.,£.G.. b41 l3 TW4-41 9Qd23
l319 TW4-27 7,r, 80 I 3 ,;.,_ TW4-42 t..4, ,a.
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Date 7-,s:-,1
Weekly Inspection Form
Name Vf!.U"L_.G---J.ym-A...-
System Operational (If no note
y· ~ 1me W II e D th* 8D' C t ommen s an)l l!ro bl / ti ti ) ems correc ve ac ons
,n,n MW-4 g .2 ,., " Flow "'. I) Via No
Meter ~ !l n « R :.J ~ , J ;) v.. No
nO"iff MW-26 77. q4 Flow ,~,4 '-No
Meter 3q c; 7~4.1-~ No
1"2"0 TW4-19 "TC. I I/" Flow I fl /I -No
I -Meter HJ~l 17~ r; .. No
n q ":\"' TW4-20 7;J.. '(fl:/ Flow ~ I"--No
Meter 1 o t:. a '5 ~. q !l V:elJ No
I I) 1n TW4-4 9.z;-. .,. ':l.i Flow I~ (J ~ No
Meter t. r; .2 r: st 7. ~ 'Im No
r,QOI,, TWN-2 ~Y . .:Jt:. Flow ,~. (] .._ No
Meter , , fl -=11 Ii ~ '!l. ._ No
l?Q~~ TW4-22 71/.'1 I Flow I A .IJ ..... No
Meter ~ '.l _~ ~ ~ r::. ~ 'm No
Ot:/ I?. TW4-24 -, "' ./-"' Flow 11-1. Cl ... No
Meter , tJ ,011:. • -:,, -:a ,. --No
t?flcq TW4-25 71.":IQ Flow 1 '.l SI ~ No
Meter , q ..:1 ~ ~ n ':\ 1-1 -..No
IIJl"1 TW4-1 Sl'1. ".11 Flow J "' I} ~ No
Meter .Q_q; 1.., 1. ~ ._ No
;!}/)~ TW4-2 I() '2, ~~ Flow , .., " ~ No
Meter 3 3 8 5"'" :.l 3. :i -No
l}q~ll; TW4-11 01.1?,<'" Flow //.,. 4 .... No
M~ter t. .2t, ~ ~ .eJ ... No
I t1 f!l t::"" TW4-21 74.0Q Flow /Y.~ -No
Meter , ,::r~ .,,~ ~ "3 =1 . q -. No
/)q~q TW4-37 -,::a.. oq Flow /f/f. /J 'lfA.. No
Meter ''"'!I.ta /JI:'.-, '*-No
/J41./,> TW4-39 "'1':l .118i Flow ,q t1 ~ No
Meter zr n4' .r;7;7. q ~ No
,n-iQ TW4-40 70. ;Jr-Flow 1R.O -No Meter J 11A 7qO. Q c;--~ No
J ()~I./ TW4-41 stq,-, fl Flow ~ tJ ~No
Meter !Jl'/A~~,<?. -. No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date 1-,.:;..-,, Name V«n 6-1rmeo
System Operational (If no note
T" ,me ·w II D th* C ts bl I ti ti l e ep ommen anl£ ero ems correc ve ac ons
ne,1.1" MW-4 4.1). 4ill:?. Flow ~ I.. -No
Meter ~ !2 11..".l •t:1 ctcr -No .
na,.., MW-26 To. " r Flow ,n .,. ... No
Meter '".\ q., ~ '11::" 'R ... No
,n "'n TW4-19 "11, -,-J, Flow 1« a .. No
Meter ,., ~~si-,n. , Ya No
/'Jt:lt"U../ TW4-20 '"'11 /) q Flow
(,, " ... No
Meter ~"..,.., l"?/1 -,z.--No
1nll TW4-4 QQ /)/ Flow , "7 /_ .... No
Meter r.,,.-~.,_...,..:z .-, -No
/J4'!l• TWN-2 ,: "1 .., '1 Flow ,.,.« -No
Meter II~ I~ T ., , • "2t YIII No
ll')fl"I" TW4-22 -,~.~· Flow IQ l"J -No
Meter ~ -:J. "'" ._ n ,:,. .. No
l'>Q":I'-TW4-24 ..,"' ~Q Flow '~ « --No
Meter Jo 1J t.nl.f ,._ ~,g -No
.n«~2 TW4-25 "'7 '-. I flt Flow ,,,_g -No
Meter 1 '1'111-.,, '!I • 11 ~ No
t')CIC'• TW4-1 711('_ I'> rl Flow '~·"" ~ No
Meter :iq~, .,.. ~ ~ No
n4-i.:t TW4-2 JI'.)/,.. !J.. "::I Flow ,.,.,, ... No
Meter ~~ q ~ .:2 < . .., Y.-No
t.,q,2,;"' TW4-11 C=ll.17 Flow I(",~ --No
Meter it;. 2. ~ o-,. ~ ._ No
t11J Ii:' TW4-21 7n. , .. .., Flow I/.. Q ... No
Meter , o. .., !l_"T ct, ~a ..... No
n«,;,: TW4-37 f.11 ~ Ii. Flow l~,A '*9 No
Meter ,i:2.crq.("q ,a Yialt No
n.:,,, TW4-39 ., ~. «,., Flow J«. 0 ¥a No
Meter , "t. 2 "~ L'J ... No
101« TW4-40 '"1/J. ~Cl Flow JQ.o -No
Meter II o I t. "1 • ~ ~ ~ No
lfUJ I TW4-41 «">..11 Flow I./ 0 ~ No
Meter ~ , t.11'. /.... '-I, -No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
-Date
System Operational {If no note
T" 1me W II e D th* C ts bl / ti r ) eo· ommen an){: ero ems correc ve ac ions
1~!2"1 MW-4 '"7Q nn Flow I./ /) 'Ma, No
Meter ,, .., ~ -:a.1.1,:. o /J t:. -No
,~nt:' MW-26 7/. ,,~ Flow It:" !I .. No
Meter ~qq ~~q :?, -No
J LI-.,. I TW4-19 7/ ~Cl Flow I 9. I] ._ No
Meter Jt!J.'\t.., t n. < '-No
J~C () TW4-20 7-::J ,qi Flow "1.~ -No ~. Meter -:i,Ht .2 !:l, t:." ~ No
i?.LJ/_ TW4-4 71"-. ~ I Flow J f,,,;. t;, Var, No
Meter ,t:, < 41 7 n "". , ~ No
n~n1 TWN-2 ~'1. "7 I Flow lt\,f1 Vaill No
Meter II q D o .q , • .n "-No
17~ 2.1 TW4-22
"7 "'· ' ""
Flow i t;t n --No
Meter I'.. ~ L. _j , , /J <W!I No
I) 9. / l;'" TW4-24 Q() ,. ~ Flow 17. 4,/ '*=it No
Meter , nQ "ll. 2. 1 ,;-41 '1 ~ No
n.,~2.. TW4-25 7~-//. Flow I tJ. if *-No
Meter :2 n ~ _:l ~ ~ :>. ,. ... No
I ':\ ~ --t TW4-1 '"'Tl.I. ii Flow I~~ .. No
Meter 3CI/ ... 1..1.~ ~q -. No
l~:1() TW4-2 I !JI.. t.4 Flow It. ~ )faia, No
Meter 1.'lt)1 ~ct.7 .. No
I"\ I ".\ TW4-11 Qn n"I Flow 1'1 ,I) .. No
Meter r.~ 3 A/'/,~ '*'8 No
0 7"1~ TW4-21 7R ~ ::1. Flow J fA "' .... No
Meter ; tt fl n q" 3. --1-z. ..... No
I) 'R '?J 0 TW4-37 7~.'5"ff Flow Ji () Via No
Meter , z; ~ L/ ~ Gt.. '7 V.V No
,~ .C'1 TW4-39 "11 1~ Flow J '1 I) )la No
Meter t:' n c:,.q, t. 11 '.ca, No
I ~,;'°jf TW4-40 7/?. ~Jf Flow !'iii t1 *" No
Meter II t'4 :i_n ::2 , ., n ¥98 No
,~110 TW4-41 (J.D q ~ Flow ~~'it "-' No
Meter ~ , « L q " .., , ... No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
'* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date 8-5-19 Name p ... so {.....-'fctl<>Q
System Operational Cit no note
Time Well Deoth* Comments anv problems/corrective actions)
,n11n MW-4 iU 1.U Flow 4 IJ ¥1111 No
Meter ~ .!'.> ~07'11 '10 ._. No .
J/J(Jq MW-26 7~ <t: Flow ,n 1 .... No
Meter .1./0l&lt.2..":4. >.i8t No
':l I~ TW4-19 t:;_q I :J Flow ! 9. I) ... No
Meter I 8 '-/LIL/ t. '.l ~ ~ No
l?q,; fa TW4-20 7:l. .tf.:t Flow "7 "'
.._. No
Meter ~ n 4 !l -:,. -,. nil .. No
--:i ---
lr.t9..I:/ TW4-4 ~ Flow , I#. " IC"' ~.r-~14' 'a. No
Meter -..: , -. ~ • / ._ No
no-:Jc TWN-2 <'11 '"' Flow , 7 !2 --No
Meter II er '1 ~ , t a ._ No
lnqu~ TW4-22 ~\ IQ Flow I fl I) ~No
Meter e.. :1 ta, 7'1 q '*9 No
nq~~ TW4-24 ,t;". ":Pi~ Flow I "4 « -No
Meter , ncn ",,. 1... 1.. -No
na1A TW4-25 7fl."77 Flow } :,._. {,. 'a No
Meter :2.1 -,. l :2. t:. ., -:i .... No
110'( TW4-1 ~ti 01 Flow ,-z,,/] ._ No
Meter ~4Al.74,-,.. /_ ~ No
,n-:J.7 TW4-2 / I} R .:2..;"' Flow //,. "'-'a No
Meter ~.,,.,/;n., .. No
J/)IQ TW4-11 cu.,~ Flow ,,. I. ._ No
Meter r:.~~11 "I. ~ .... No
oq" TW4-21 7~ O'I Flow ./~ -.:1
._ No
Meter 1,u,c:1~'9~. q~ ... No
n4,;n TW4-37 74J.1q Flow IR." '*9 No
Meter 1t;£10JJ::J.1.7 V:lls'" No
1nn.:l TW4-39 '7q 41./ Flow JR n v.. No
Meter .; 11 , ,; -r. -,. ...... No
rr~o TW4-40 7/"J. ~4 Flow I~.() ._ No
Meter , 2,1~~-; 44 ... No
111'.:1 TW4-41 71t.q7 Flow ~ " --No
Meter .2:, n,;-,sr~ ,uJ ... No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
D_ate 8· •a-,q Name Oeen C-: 41mon
System Operational (If no note r· 1me W II e D th* eo C t ommen s anl£ ~ro bl I ti ) ems corrective ac ons
nti('C MW-4 ~~-(,,.(.,. Flow .. ,1' ~ No
Meter 2. :i. '3 ao 11 (", cu Va No
n«.,. '.l MW-26 7&.. '=t~ Flow J J. ~ .., No
Meter "IO~";Jt. q -. No
Jdb"7. TW4-19 '11J'. I~ Flow 1 9t t'J 'a No
Meter I 'R l:j' !1 ~ .'\~ r. '.-,. No
"~ ,., TW4-20 .,~ .&lt: Flow ~4/ -No Meter ~,n~7'1.'1fl -No
o~,~ TW4-4 r;u:.. 'tc.l Flow It:.. 9. 28119 No
Meter t:a~ ~ qq '1-" -.....No
n-r£1 t:. TWN-2 r..1 ~ I Flow /ff . ./) ._ No
Meter 11 qr. "'l. 7'1. • v.e No
n1tn=1 TW4-22 7/.CII Flow I ti /J .. No
Meter ~ ~-q q ~"/.-, -No
l'J7<t:. TW4-24 7C.'!.1Q Flow '~-~ ... No
Meter I Jo J ,;-.g-~. ~,2 .. No
o,~~ TW4-25 "7 !2 . -, t:. Flow ,, ~ Y.-No
Meter ~ , q • 7 t. , .. q :... No
/)QI)~ TW4-1 'ilD.IJ~ Flow ,~ . .., *9 No
Meter .!JQ1lfct'f .q ~No
/J~l./7 TW4-2 //J ':j L/":I Flow /&,. ~ ... No
Meter '=I &l..:I _~ 'I\ !l . ~ *' No
(J (). ,JI') TW4-11 cu.," Flow I l.. L./ ... No
Meter I"!. '::l. ,:. t:.. I ~ ... No
071.D TW4-21 ..,~.19 Flow , .., • '.1 ._ No
Meter 1 • q., /-n:, WIJ ~ No
/J9. In TW4-37 *Al. t>I Flow I 7 .~ ..... No
Meter , r;. ",: ~ 1 n . "1 ._.. No
/HI~~ TW4-39 71./. ~~ Flow ,~.n ..._ No
Meter e;, ,_, ~~o. ~ 'a No
/)q;_J"'7 TW4-40 7'11 ,._,., Flow /1t,l"J "-No
Meter 1 ~ 7 ~ 7 '5. 'I '?J ~ No
nq1n TW4-41 ~ ... 'l l Flow
"'· 0 "-No
Meter :.:2_ ~ ~ "2.~n.q~ ... No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
'1Q Ir..,_ 2
Weekly Inspection Form
Oate g-,,-a.a _N_a_m_e~D~=+f:t--,..~--rt__-----------
System Operational (If no note
T' W II D th* C bl / I ti ) 1me e ec· omments an)!! ~ro ems correct ve ac ons
/~IA MW-4 4 ... "'~ Flow £/. I} "9 No
Meter .2. '::l_l./ ~ '/ t 11 '.1 n ~ No ,
nq!JQ MW-26 7~ 'R'=I Flow IIJ. 9. -No
Meter "'n,~ J.JJJ. ~ *-No
/..:1 ~.I> TW4-19 7'1. ~, Flow 111 I? ~ No
Meter J fl r;-q q, , q, ~ ~No
non1:1 TW4-20 7~.G.7 Flow (.. &/ -No
Meter 1 1 1 ~ :J :::> :11 ~ No
JI) ~5' TW4-4 c!)---' ., n Flow It, I./ ~ No ..
#/'I.DI Meter , ~910 ol g 1 ~ No
OS\~~ TWN-2 ,:;q, /9 Flow 1"1,/;. ... No
Meter 1 , qq o '7' .... ii. 'I ~ No
r
/')fl ~t!t TW4-22 7/./. :r~ Flow ,«J.n --No
Meter 1. ':\ 111 q I. q ._ No
t?«l./7 TW4-24 7q_11 Flow 17.n ¥ala No
Meter 11n~71 If'. J./1./ ... No
nf4:J t:. TW4-25 7/.A;J Flow 1:J 0 -No
Meter :i :::i ~ ,.:i_ ::::i.._111 • Q 1 -No
//)JQ TW4-1 ----Flow J-2 {. .. No . <J..,
/()3,«f~ Meter ~q~.,., ~ 7. q ._, No
JO. nt. TW4-2 f f1Q IQ Flow It:. ,,:c; ., No
Meter ~,.,~~li'7. I:, -No
oq~1 TW4-11 OIJ «'I Flow I~ ,:, ... No
Meter ~.::.9.. :l4.C1 ... No
OfJ/q TW4-21 "1'i ,77 Flow J.,_1.. ... No
Meter 14n~o 11, 4''3 -No
0t11')J TW4-37 7/.':I" Flow l'd./J -No
Meter J e:;t; n 7 7;: o -No
/)9/11 TW4-39 7q, .1:...< Flow Ji.O -No
Meter I;'/ 1"19.~.~ .. No
/nLf< TW4-40 "'7-:J I~ Flow 1 fl 0 'tea No
Meter 1'-/,;'-,IJ~/J, Ya-No
/ fJ-:1,C TW4-41 41~_-.,q Flow "{ 1./ , v.. No
Meter ".3 ".'I "-! ~ () /., 'I Ii' -No
Operational Problems {Please list well number):
CorrectiveAction(s) Taken {Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Date st-U -Jq
Weekly Inspection Form
Name O~~
System Operational (If no note
Tl me W II e D h* ect C ommen ts anl! ero bl / I I ) ems correct ve act ons
l)<fJf; MW-4 fl/_ ~ t.. Flow 4/. /') ¥88 No
Meter 'l ~ ~ !l .t"-q':I. '.l 1 ~ No
OQl;'O MW-26 1'JIJ. ~-,. Flow IJ. fn 'm No
Meter 407:J 7~. a., '-No
, nu "1 TW4-19 7f. "'' Flow Jfl ~ No
Meter JR~ 77~/ .I/ ~ No
01'~!1 TW4-20 7/3Ut Flow /. "' ~ No
Meter -:\ \ :l~J.O.•lf \a No
oq~, TW4-4 q~./J~ Flow 17 fJ ._ No
Meter ,t;..l(q I -.::2 '2 ,~ v-. No
l'J7l(O TWN-2 t=. I .:l.G Flow Jfl. lJ ..., No
Meter J 2 D ~ I Al I I "-No
l'J~ I SI TW4-22 QL 1a Flow It 0 ..... No
Meter ~ \ '17 /;'Cf. 'i ... No
ntA.n'fl. TW4-24 '-" 4,,//-. Flow
'"'· ::2.
.._ No
Meter 1111qqn7 n~ .... No
o,~o TW4-25 7/ "'" Flow ,-:1 .0 "-No
07"!,0 Meter ~ .,_ ~ :?.~, '3.., ._ No
oc,~ a. TW4-1 SJ~.~. Flow l"i.1 'a No
Meter ::,._qtq 1a 11 1 ~ No
oqna TW4-2 Jl'J ,. /. "A Flow / '7 I../
._ No
Meter 7,'I~ l'JJ/. !:J -~ No
/)q/Jl'.J TW4-11 Ol.nl Flow '7."' *-No
Meter t:.~ lf~r.. ~ ,._ No
/17 !J l'J TW4-21 7:J. ~7 Flow 17, "'I .... No
Meter , q 1 ""1 "~ • q 'J --No
/Hl~.r:"' TW4-37 ., !J. '19 Flow ,4 .0 v.. No
Meter 1 :;:;~~l;'~e, y., No
no.1./1 TW4-39 7~.,q Flow ,~ n ._ No
Meter ~21'1-:Jn7,q 'a No
/)fl..,., TW4-40 ;n r..« Flow ,~.o ~ No
Meter ,~uuq~. /..~ ~ No
oq1~ TW4-41 Ciel__,. Flow "1.tJ Y.es No
Cll'!.../JI",. Meter ~ ~ /_,""'.-:a i v... No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
... Depth is measured to the nearest 0.01 feet.
Date s-,-,,
Weekly Inspection Form
Name p~,,_.
System Operational Uf no note
Ti me W II e D th* e p C ommen ts anlt: ~ro bl s/ . . I ) em corrective act ons
O<f!:t_/'. MW-4 OQ .t.11.f Flow I,.}. IJ ~ No
Meter !l ~ '-11 !J .':I . "l ~ 'M!le No
O<Ilnt MW-26 st &i..11<" Flow q,LI Y!M No
Meter 'fOq'.172..&/ .._ No
/I)'( f, TW4-19 71 "8 Flow ,-z n ..... No
Meter •~11'..t.Z:n 9 --No
1Hllt'9 TW4-20 7'!:J,"',t;"" Flow I':.. "I ._ No
Meter '=l.l':l("7/.tr"-' ¥111 No
1001 TW4-4 ~~-C't:l Flow It. t} v.. No
Meter /./.1),.,~Q. Q .... No
t?Qlli TWN-2 ,:q_ ¥"I Flow I I O ¥ae No
Meter 1 2.. n t. .,,, v ~. o Y• No
o~~~ TW4-22 .,<', ~ 7 Flow ,~.n ..... No
Meter ~-,.~Q7SI q "-No
,1i.2~ TW4-24 7&/" Flow J t.. '.'.l.. '89 No
Meter / I I ..., ~ '1 ~ ,,,, .... No
O'Rn7 TW4-25 7l. 4,/ ~ Flow J.!I. ~ ~ No
Meter ~u"q"~ .cu, .. No
/)QI./&. TW4-1 la/..,.,-, Flow l"f ... ~ No
Meter '.:l D 01-f o ~ '1 -No
LJ'f~~ TW4-2 JJ'JO ~-/ Flow I~ n v.. No
Meter ':J "{ {,. '1 ,; ~ • I 'wee-No
/J'IJ< TW4-11 Cfl.l~ Flow I I'-.. ~ ... No
Meter 1:.-;1~.!LO ._ No
11"'1 r:'", _ TW4-21 q1.. ".l I Flow , 2. •• ... No
Meter ,ct 2 .~ 7 '7 D. ".l. ~ '8lt-No
tJQ'-1~ TW4-37 "J''\\. fft Flow I« n Ma No
Meter ,,:;.1.,,u .. :, 1 ... No
"41.t;'~ TW4-39 72. ~.I) Flow I« t, -No
Meter ,2'-11«0. t 'U!II No
IIJI '1 TW4-40 7/J. t.1' Flow ,«. n 'tdl No
Meter u.11unq_,,,,, ._ No
~t:IYI/ TW4-41 «L.Jt. Flow '3.« --No
Meter ----:.. .:1 '7 .. ,r" -No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
.. Depth is measured to the nearest 0.01 feet.
Monthly Depth Check Form
Date 9-3-2.0lj Name -f'Mo,.-U0)f;~ 1 Pe e" l-jtri«-"-
Time Well Depth* Time Well Depth*
09;,;n: .. MW-4 g~.~~ 073..1. TWN-1 b7, lS
Q~ttb TW4-1 ~~.,] o«l5 TWN-2 sq.~~
D'iz:z ... TW4-2 !Q5,bl 073(:. TWN-3 ~I. 8K
o~,::z TW4-3 (;;2.~~ QT~ TWN-4 bQ,gQ
IQQI TW4-4 ~:1.sg o;~ TWN-7 3,;i.,33
oz 1:;z. TW4-5 ~:L8;;i._ 01~D TWN-18 fu18l
D830 TW4-6 7'1..~D 07~ MW-27 .Sb,~(
O~'Zi TW4-7 ~I. (:.Q o,sg MW-30 75d l
Q~z~ TW4-8 a~.~1 QSQI MW-31 b8: ,Cf~
~~!~ TW4-9 b.]1&~
Q~Q~ TW4-10 t~7.~
0~15 TW4-11 9!, 1.3
0£S llS , TW4-12 5~.D~
Q~I~ TW4-13 !:i~.s~ C, §l~ TW4-28 ~7. jl
QfiQ~ TW4-14 1].7'o O'o07 TW4-29 -:1.r...-:11
QtfOl TW4-15 ~~.OS OT51 TW4-30 J 5,0:!)
08D'-TW4-16 71 ,go o-,53 TW4-31 7b18I
Q(SQ~ TW4-17 ~o.sa oi;2.:~ TW4-32 ~-1-~
07~ TW4-18 :ZQ,jl 07Yi TW4-33 7{;., ll
lQ:\5 TW4-19 J~.b~ 08.0~ TW4-34 ,~,9~
Q~~g TW4-20 7 :::t ,~5 D~.00 TW4-35 7~ ,[G
tf7s4 TW4-21 GJk IC} D&l~ TW4-36 S7.'3'1
Q~~ TW4-22 i'S :11 og~i TW4-37 73.18
0()32 TW4-23 73.b.5 Q8.2Q TW4-38 .57. q_s;
0~ TW4-24 ]~.S3 Qg.SS TW4-39 7.2, 2.0
D,~O, TW4-25 7 1.~3 IQlQ TW4-40 7Q,bB
0~:j TW4-26 ,1.;2.1 Q1S~ TW4-41 B'3J.b
o,SD TW4-27 78.93 qz~ TW4-42 4?1.Z:if(
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
9 _ , ... 13 Name ~?d]'"' • r!:r::
System Operational Clf no note
Date
Tl me W II D th* C bl / I ctl > e eo· omments anll: ~ro ems correct ve a ons
un.n MW-4 "111 . .., &; Flow ~ g ~ No
Meter 1:11.. 7 5"'~ \.qa;-... No
11?/HI. MW-26 '7L 'KC"° Flow I I. 'il ... No
Meter '-ll01fl.~., 1M No
J:JJ,:j TW4-19 7,q, q, Flow J~ D ~ No
Meter / s:r ~ ~ .:J ".:J • ., ~ Ve No
nQl.'1-TW4-20 «~-'"'' Flow I ... "I --No
Meter ~l'i~~G..i .... No
I IJl:i(J TW4-4 til/7. ~q Flow It, '-/ ~-No
Meter fa l. I 'I 'R '2, • I ~ No
~4-i, TWN-2 l.D. lt. Flow , .., ~ 'e No
Meter , ~n q tl.h'I .. /.. )(D No
11q~7 TW4-22 "7 •. QI Flow 111 n .... No
Meter ~~..,I/ti~ . ., ..... No
()q::,,('J TW4-24 7:1 J:::J Flow 11 •• c./ -No
Meter 1 , 1 " 1 '1 t ::2. q --No
nq 11:; TW4-25 Q!t. <11 Flow I~.« '9 No
Meter ~-"'~ -,~ 7, OJ s No
I '1-:tR TW4-1 7~.RIC Flow I :J 'jf ... No
Meter 3011 ~it.s:l gs-No
Jn:l.'-1 TW4-2 ,nfl 1_.1 Flow ,~ n ._ No
Meter 3 'I 1 ~O.q -No
,nu .. TW4-11 OG.Oi Flow IL. I/ .. No
Meter t.;3149 .g 'i:11!!1-No
/)
Olltl'J "\ TW4-21 7~«1 Flow /7. ~ '19 No
Meter , "~ ,tt11. ·~ Ym No
rJQI/~ TW4-37 "1'1 -,. /,,. Flow ""-1« .IJ ~ No
Meter , c-~ r.. i ,; -:a • ~ 11119 No
,nn~ TW4-39 ',la:;' -,q Flow I«./\ ~ No
Meter ,; ~ 1.. lo/" t:. r;--No
IL71/'7 TW4-40 7l'J.7<° Flow Iii, 0 _. No
Meter , -, .:1 n :1. ~. , ... "7 ...... No
J/J'II.I TW4-41 74 ~ c"' Flow "I. D -No
Meter .l-, _q '1 lt/tfl ,£ ~ "-No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Date CJ.I t~llj
Tl m~ W II e
l'Z~ MW-4
, -z,.... ~ MW-26
l~ne) TW4-19
,~,, TW4-20
I /'5/""J i.l TW4-4
"qn TWN-2
1:31"2 TW4-22
I ~I~ TW4-24
r,cuz. TW4-25
I "Z.53 TW4-1
·1 '.3.~o TW4-2
1:Jc,4 TW4-11
l'cto, TW4-21
r ~'ZY TW4-37
l~"Zb TW4-39
IOI~ TW4-40
•~z~ TW4-41
Weekly Inspection Form
Name 6c..tri6 J?q, lM:4:r
System Operational (If no note
D h* eot C t ommen s bl / I ti ) anl£ (!ro ems correct ve ac ons
7~.72 Flow :3. S" ~No
Meter ,z -Z 11 t ~ 2.. St..1 c'Ye's) No
71.30 Flow 10. 0 ;fesi No
Meter YI '2.AL ,. So ("7""es) No
72.~o Flow ,~. {} n'ei ~ No
Meter I ~4'~~ f.:r,k (Ye,~ No
67.92 Flow h,n ~No
Meter ~1Sli"2c..l.O'l ('Va's') No
q7_ "'o Flow ,~.(') lfes1J No
Meter t.L 2 ~ I 7 .. '1 0 cre-_s;,1 No
~~ .. "~ Flow 16.0 KeP No
Meter I 2 I :i~g "4 e:,n Yes) No -
7z.oS Flow Jl,.n ?(~ No
Meter b.'3~ ~09, l{6 ~e~ No --,z,t;() Flow 14 ~A (?es }No
Meter I l 'Z. "I.I{ t'l "3. "iA ~No -
67.Z5 Flow tn.4 <Ye5J No
Meter '2 5' .\ l.j _i;-2 .6 2 (Ye~ No
77J'>4 Flow ,2 .. t.\ ?re~ No
Meter 2~'2 0 C:J 4. 'Z.I~ ~ No -10.c. 1o Flow Ii .l"'l ta$) No
Meter 3481.17_AI) (res) No -
q~ -"'4 Flow 16.o ("reS) No
Meter 6 35'8'.~ o.o (i"e.s No
7 3,." 'Z. Flow 1,.2. (JeS\ No
Meter I c, &.4, 1.1_.or;,,_ o '2. ~es) No
7~.t.o Flow 1,,60 ~No
Meter I ~7Joc:>6. 30 L Ye~No
g 1.,4 _ ~'l Flow 1&1.0 ~.No
Meter 5z.g 20 I C,) ~ej No
7o .. qo Flow I l?.o CY"es") No
Meter 1~31 ~.,;:. 3t') '(es) No
7'i. 'liJ Flow L#.O (Y~ No
Meter 232J7(. Y3 tre~ No
Operational Problems (Please list well number): -~N~A:1...-____________ _
Corrective Action(s) Taken (Please list well number): __._N........,.A-....:....--------------
* Depth Is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date
\ 9-;r,-,, Name Df'¢A V'r,zu7ef?
System Operational {If no note
T" 1me W II D th* C t bl / r ti ) e eo ommen s anll ~ro ems correc 1ve ac ons
ncn:a MW-4 '1& .M,. Flow ~~ )ill No
Meter ::1 '!I. a !l..1 7 0 , "' 'el& No
nq1~ MW-26 fl/ 1/9 Flow JO.&/ -No
Meter "f, "!l... q :.i. ~ ... No
1~05"" TW4-19 7'a ~, Flow Jft.t) .. No
Meter 11? q « 7 ., a q --No
n«<., TW4-20 -,, q~ Flow ~~ -No
Meter -a It.~ ~~ t..Q -No
L)q~~ TW4-4 qi.o<. Flow / ii;, (l ~ No
Meter "~ '\ ~ , n . I( ~ No
nf/1~ TWN-2 l'..,.LK Flow I 'i. 0 ~ No
Meter , :::u ,; tJ :, ~ . 1. -No
n"""~ TW4-22 7-11 91 Flow J ~.o ~ No
Meter t:.. 'I 11 n 3 • ~ ~ No
/)f.l/11 TW4-24 7 ~. '}('" Flow , , .. :2. '69 No
Meter II .;3..'-2 ~ 7. ~ .,3 Vs" No
n«~1 TW4-25 "11 .., ,., Flow II.I. -No
Meter ~L.. 0 q "ii 7. 7 t:, VD No
noun TW4-1 I fJ'), oq Flow ,~ ... "-No
Meter 1 n 1. ,: 1J 1 . , V. No
nq,!\~ TW4-2 I/JI I.II Flow JI,.-~
._ No
Meter ~" q ·:u:· (" .., .._ No
nq1Q TW4-11 an c:an Flow JI. (J ... No
Meter t.1.l'..n1t.11 ... No
nQ1< TW4-21 7'11..&/I Flow /&. Ir' Via No
Meter 1 "I "I 7 'I ff 1. -, ,;---No
n•.r~ TW4-37 7~.-:a., Flow J t;l {J ._ No
Meter , z:-, r.-, *' q ,41 "95 No
Otfl/tJ~ TW4-39 «"' ~'#l Flow 1-r a ~ No
Meter ,.. ~ ~ '.1 :a.~.,.« "'8> No
IOlJI TW4-40 "'1 I q / Flow J~,O -No
Meter 1Qq":\1q ~~ .... No
nqu, TW4-41 • .,,, . 73 Flow 4.0 Ye) No
Meter ~ '1.'llcJ 7111.•.., -No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feef.
Weekly Inspection Form
~e 9-3P-rs Name o~n c:-'7ht9:'!'b
System Operational (If no note
T" 1me W II D th* C t bl / I · > e eo ommen s an)! Qro ems correct ve actions
nq.:1~ MW-4 ~q qq Flow "'· 0 Ya No
Meter .2~_~q§"J"7,~~ -No
IJ 9/"J I MW-26 ~Lf1II Flow /() ~ -No
Meter 'II~"~ 3,0 ~ No
JOLI.~ TW4-19 l(q 'l.i;' Flow J'J n Ya No
Meter Jqni'A'I n/J t. *-No
/Jil/'3 TW4-20 7~.t:'ll Flow "'. "/ )a& No
Meter ~f 7q6,t} t?:J.. 'a No
/)qi/{. TW4-4 qLL~I Flow ,,_ 2. 'la No
Meter ~ t. I/ 7 ~ ~ . I ._. No
1)7,;lfl TWN-2 C. -,, '3' Flow I/,._~ \fa No
Meter , ':l. , 7 q t:t "I , ..,,, Vat No
noA.1.q TW4-22 7/-. r;-J; Flow /fl 0 ~ No
Meter /.. "I ~ o ~ 9. .::1 ... No -
n~~::2.. TW4-24 7~. ,~ Flow It. 0 -No
Meter 11 "1 IJ IA "11. n 7 ~ No
071/C/ TW4-25 '71.'I~ Flow J.n /.o Ya No
Meter ..:2. ,t;.;:,..., no q11 ~ No
/JQ':ll'J TW4-1 q~.n~ Flow /~"( .._. No
Meter 3 r,~ "I "I 1. d -No
t)q1,;-TW4-2 I/)/,. -,'I Flow /7,, ... No
Meter '1~AA/~1 . .:2 ._. No
nqni TW4-11 q I. l)I Flow It.~ )a No
Meter t. ?17 "6-"1. g >a No
ID7¥.::1 TW4-21 7t:. I:.. Flow /t:.." ~ No
Meter J •s-~,t;.~ ,Y, 1~ -No
l)r/~ 1 TW4-37 -,:1.n-, Flow J'R I) 'M No
Meter 1< R1q 71 ~ 'tm No
n~<.:i TW4-39 /!Q Q~ Flow ,,, 11 ~ No
Meter ,r~ r:'J :J 4." }161& No
11,tJ~ TW4-40 70.1q Flow 1ft n ~ No
Meter J q ~ 1 ; , .... qfi .._ No
17q~q TW4-41 tJ. t. . (,,, la Flow ~.o -No
Meter :, \ < .:2 ~ n. tJ"I ~ No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
TabD
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary
Name: Tanner Holliday, Deen Lyman
Date: 8/12/2019-8/ 13/2019
Depth to Depth to
Date Time Well Water (ft.) Date Time Well Water (ft.)
8/13/2019 1248 MW-01 64.75 8/12/2019 855 MW-04 83.66
8/13/2019 1416 MW-02 109.68 8/12/2019 903 TW4-01 80.02
8/13/2019 1310 MW-03A 84.17 8/12/2019 847 TW4-02 102.43
8/13/2019 1408 MW-05 108.62 8/12/2019 1311 TW4-03 62.19
8/13/2019 1429 MW-11 85.40 8/12/2019 918 TW4-04 86.34
8/13/2019 1406 MW-12 107.88 8/12/2019 1317 TW4-05 69.58
8/13/2019 1344 MW-14 102.28 8/12/2019 1303 TW4-06 76.50
8/13/2019 1347 MW-15 105.60 8/12/2019 1305 TW4-07 81.32
8/13/2019 1314 MW-17 71.97 8/12/2019 1308 TW4-08 84.58
8/13/2019 1245 MW-18 73.39 8/12/2019 1315 TW4-09 67.58
8/13/2019 1237 MW-19 64.94 8/12/2019 1320 TW4-10 67.03
8/13/2019 1212 MW-20 86.80 8/12/2019 840 TW4-ll 91.13
8/13/2019 1153 MW-22 67.50 8/12/2019 1252 TW4-12 53.69
8/13/2019 1404 MW-23 114.04 8/12/2019 1250 TW4-13 55.16
8/13/2019 1421 MW-24 111.32 8/12/2019 1246 TW4-14 77.60
8/13/2019 1335 MW-25 79.78 8/12/2019 1313 TW4-16 71.82
8/12/2019 832 MW-26 76.38 8/12/2019 1334 TW4-18 70.75
8/13/2019 1325 MW-27 56.61 8/12/2019 1003 TW4-19 77.13
8/13/2019 1424 MW-28 74.71 8/12/2019 817 TW4-20 73.45
8/13/2019 1413 MW-29 107.77 8/12/2019 730 TW4-21 75.18
8/13/2019 1327 MW-30 75.05 8/12/2019 803 TW4-22 71.91
8/13/2019 1323 MW-31 68.84 8/12/2019 1301 TW4-23 73.36
8/12/2019 1317 MW-32 80.37 8/12/2019 756 TW4-24 78.29
8/13/2019 1353 MW-33 DRY 8/12/2019 738 TW4-25 72.76
8/13/2019 1351 MW-34 107.54 8/12/2019 1259 TW4-26 70.72
8/13/2019 1400 MW-35 112.27 8/12/2019 1232 TW4-27 78.70
8/13/2019 1358 MW-36 110.51 8/12/2019 1249 TW4-28 46.76
8/13/2019 1349 MW-37 106.41 8/12/2019 1234 TW4-29 76.40
8/13/2019 1158 MW-38 70.81 8/12/2019 1241 TW4-30 74.77
8/13/2019 1201 MW-39 65.39 8/12/2019 1243 TW4-31 76.55
8/13/2019 1318 MW-40 80.01 8/12/2019 1246 TW4-32 54.81
8/12/2019 1230 TW4-33 75.75
MW-26 = TW4-15 8/12/2019 1236 TW4-34 74.59
MW-32 = TW4-17 8/12/2019 1239 TW4-35 74.56
Comments 8/12/2019 1248 TW4-36 57.04
8/12/2019 810 TW4-37 81.01
8/12/2019 1313 TW4-38 57.68
8/12/2019 825 TW4-39 74.53
8/12/2019 927 TW4-40 70.60
8/12/2019 910 TW4-41 84.21
8/12/2019 1256 TW4-42 66.80
Date Time
8/13/2019 1239
8/13/2019 1234
8/13/2019 1215
8/13/2019 1338
8/13/2019 1341
8/13/2019 1338
8/12/2019 746
8/13/2019 1335
8/13/2019 1331
8/13/2019 1242
8/13/2019 1340
8/13/2019 1231
8/13/2019 1228
8/13/2019 1328
8/13/2019 1224
8/13/2019 1254
8/13/2019 1251
8/13/2019 1355
8/13/2019 1246
8/13/2019 1244
8/13/2019 1241
8/13/2019 1301
8/13/2019 1304
8/13/2019 1307
8/13/2019 1237
8/13/2019 1207
8/13/2019 1234
8/13/2019 1225
8/13/2019 1223
8/13/2019 1216
8/13/2019 1231
8/13/2019 1219
8/13/2019 1228
Well
PJEZ-01
PJEZ-02
PJEZ-03A
PJEZ-04
PJEZ-05
TWN-01
TWN-02
TWN-03
TWN-04
TWN-06
TWN-07
TWN-14
TWN-16
TWN-18
TWN-19
DR-05
DR-06
DR-07
DR-08
DR-09
DR-10
DR-11
DR-12
DR-13
DR-14
DR-15
DR-17
DR-19
DR-20
DR-21
DR-22
DR-23
DR-24
Depth to
Water (ft.)
66.73
44.03
55.14
64.43
63.82
66.97
61.31
42.00
59.91
80.08
81.98
60.21
47.83
61.69
53.97
83.14
94.21
91.86
51.50
86.53
78.44
98.06
91.75
69.81
76.21
92.83
64.78
63.24
55.43
100.80
DRY
70.42
44.51
@
TW4-42
¢5528
MW-38
-¢"5462
estimated dry area
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
perched monitoring well
installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
+5527 installed February, 2018 showing
elevation in feet amsl
M;'t503 perched monitoring well showing
elevation in feet amsl
TW4-12 0 5571 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 t h d . . . <>5567 emporary perc e nitrate monitoring
well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5589 elevation in feet amsl
RUIN SPRING
~ 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4·24, TW4-2S and TWN-2 are nitrate pumping wells; TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM, INC.
KRIGED 3rd QUARTER, 2019 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE
H:n18000/nov19/WL/Uwl0919.srf
FIGURE
D-1
--,, ,,
I I
• ®
TW4-42
¢5528
MW-38
"9-5462
estimated chloroform capture zone boundary
stream tubes resulting from pumping. (note:
combined capture shown for MW-4, TW4-1,
TW4-2, TW4-4, TW4-11, TW4-40 and TW4-41 ;
and for MW-26. TW4-19, TW4-20,
TW4-21, TW4-37 and TW4-39)
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
includes capture for nitrate pumping wells
TW4-22, TW4-24, TW4-25 and TWN-2)
estimated dry area
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
perched monitoring well
installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
+5527 installed February, 2018 showing
elevation in feet amsl
M;'55
503 perched monitoring well showing
elevation in feet amsl
TW4-12 0 5571 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 t ched . t ·t . A emporary per mtra e mom onng
v 5567 well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5589 elevation in feet amsl
RUIN SPRING b 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells; TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM,INC. APPROVED
KRIGED 3rd QUARTER, 2019 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
DATE REFERENCE
H:/718000/nov19/WUUwl0919cz2.srf
FIGURE
0-2
--,, ,,
I I
• TW4-42
9 5528
TW4-40
+5527
MW-25
• 5533
TW4-7
0 5540
PIEZ-2
"1 5585
estimated chloroform capture zone boundary
stream tubes resulting from pumping. (note:
combined capture shown for MW-4, TW4-1,
TW4-2, TW4-4, TW4-11, TW4-40 and TW4-41;
and for MW-26, TW4-19, TW4-20,
TW4-21, TW4-37 and TW4-39)
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
includes capture for nitrate pumping wells
TW4-22, TW4-24, TW4-25 and TWN-2)
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
temporary perched monitoring well
installed February, 2018 showing
elevation in feet amsl
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well
showing elevation in feet amsl
perched piezometer showing
elevation in feet ams I
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells; TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
KRIGED 3rd QUARTER, 2019 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
detail ma CHEM, INC. APPROVED DATE REFERENCE FIGURE
H :/718000/nov19/WL/Uwl0919cz.srf D-3
TabE
Kriged Previous Quarter Groundwater Contour Map
@
TW4-42
9 5528
MW-38
-<:>-5462
estimated dry area
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
perched monitoring well
installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
+5528 installed February, 2018 showing
elevation in feet amsl
M;'5~04 perched monitoring well showing
elevation in feet amsl
TW4-12 0 5571 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 h d . . . A.5567 temporary perc e nitrate monitoring
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
g 5589 elevation in feet amsl
RUIN SPRING
c!, 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4·25 and TWN-2 are nitrate pumping wells; TW4-11 water level is below the base of the Burro Can¥_on Formation
HYDRO
GEO
CHEM, INC.
KRIGED 2nd QUARTER, 2019 WATER LEVELS
WHITE MESA SITE
APPROI/ED DATE REFERENCE
H:/718000/aug19/WUUwl0619.srf
FIGURE E-1
TabF
Depths to Groundwater and Elevations and Hydrographs of Groundwater Elevations over Time for
Chloroform Monitoring Wells
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,527.63 09/25/79 94.70 93.14
5,527.63 10/10/79 94.70 93.14
5,528.43 01/10/80 93 .90 92.34
5,529.93 03/20/80 92.40 90.84
5,528.03 06/17/80 94.30 92.74
5,528.03 09/15/80 94.30 92.74
5,527.93 10/08/80 94.40 92.84
5,527.93 02/12/81 94.40 92.84
5,525.93 09/01/84 96.40 94.84
5,528.33 12/01/84 94.00 92.44
5,528.13 02/01/85 94.20 92.64
5,528.33 06/01/85 94.00 92.44
5,528.93 09/01/85 93.40 91.84
5,528.93 10/01/85 93.40 91.84
5,528.93 11/01/85 93.40 91.84
5,528.83 12/01/85 93.50 91.94
5,512.33 03/01/86 110.00 108.44
5,528.91 06/19/86 93.42 91.86
5,528.83 09/01/86 93.50 91.94
5,529.16 12/01/86 93.17 91.61
5,526.66 02/20/87 95.67 94.11
5,529.16 04/28/87 93.17 91.61
5,529.08 08/14/87 93.25 91.69
5,529.00 11/20/87 93.33 91.77
5,528.75 01/26/88 93.58 92.02
5,528.91 06/01/88 93.42 91.86
5,528.25 08/23/88 94.08 92.52
5,529.00 11/02/88 93.33 91.77
5,528.33 03/09/89 94.00 92.44
5,529.10 06/21/89 93.23 91.67
5,529.06 09/01/89 93.27 91.71
5,529.21 11/15/89 93.12 91.56
5,529.22 02/16/90 93.11 91.55
5,529.43 05/08/90 92.90 91 .34
5,529.40 08/07/90 92.93 91.37
5,529.53 11/13/90 92.80 91.24
5,529.86 02/27/91 92.47 90.91
5,529.91 05/21/91 92.42 90.86
5,529.77 08/27/91 92.56 91.00
5,529.79 12/03/91 92.54 90.98
5,530.13 03/17/92 92.20 90.64
5,529.85 06/11/92 92.48 90.92
5,529.90 09/13/92 92.43 90.87
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,529.92 12/09/92 92.41 90.85
5,530.25 03/24/93 92.08 90.52
5,530.20 06/08/93 92.13 90.57
5,530.19 09/22/93 92.14 90.58
5,529.75 12/14/93 92.58 91.02
5,530.98 03/24/94 91.35 89.79
5,531.35 06/15/94 90.98 89.42
5,531.62 08/18/94 90.71 89.15
5,532.58 12/13/94 89.75 88.19
5,533.42 03/16/95 88.91 87.35
5,534.70 06/27/95 87.63 86.07
5,535.44 09/20/95 86.89 85.33
5,537.16 12/11/95 85.17 83.61
5,538.37 03/28/96 83.96 82.40
5,539.10 06/07/96 83.23 81.67
5,539.13 09/16/96 83.20 81.64
5,542.29 03/20/97 80.04 78.48
5,551.58 04/07/99 70.75 69.19
5,552.08 05/11/99 70.25 68.69
5,552.83 07/06/99 69.50 67.94
5,553.47 09/28/99 68.86 67.30
5,554.63 01/03/00 67.70 66.14
5,555.13 04/04/00 67.20 65.64
5,555.73 05/02/00 66.60 65.04
5,556.03 05/11/00 66.30 64.74
5,555.73 05/15/00 66.60 65.04
5,555.98 05/25/00 66.35 64.79
5,556.05 06/09/00 66.28 64.72
5,556.18 06/16/00 66.15 64.59
5,556.05 06/26/00 66.28 64.72
5,556.15 07/06/00 66.18 64.62
5,556.18 07/13/00 66.15 64.59
5,556.17 07/18/00 66.16 64.60
5,556.26 07/25/00 66.07 64.51
5,556.35 08/02/00 65.98 64.42
5,556.38 08/09/00 65.95 64.39
5,556.39 08/15/00 65.94 64.38
5,556.57 08/31/00 65.76 64.20
5,556.68 09/08/00 65.65 64.09
5,556.73 09/13/00 65 .60 64.04
5,556.82 09/20/00 65.51 63.95
5,556.84 09/29/00 65.49 63.93
5,556.81 10/05/00 65.52 63.96
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,556.89 10/12/00 65.44 63.88
5,556.98 10/19/00 65.35 63.79
5,557.01 10/23/00 65.32 63.76
5,557.14 11/09/00 65.19 63.63
5,557.17 11/14/00 65.16 63.60
5,556.95 11/21/00 65.38 63.82
5,557.08 11/30/00 65.25 63.69
5,557.55 12/07/00 64.78 63.22
5,557.66 01/14/01 64.67 63.11
5,557.78 02/09/01 64.55 62.99
5,558.28 03/29/01 64.05 62.49
5,558.23 04/30/01 64.10 62.54
5,558.31 05/31/01 64.02 62.46
5,558.49 06/22/01 63.84 62.28
5,558.66 07/10/01 63.67 62.11
5,559.01 08/20/01 63.32 61.76
5,559.24 09/19/01 63 .09 61.53
5,559.26 10/02/01 63.07 61.51
5,559.27 11/08/01 63.06 61.50
5,559.77 12/03/01 62.56 61.00
5,559.78 01/03/02 62.55 60.99
5,559.96 02/06/02 62.37 60.81
5,560.16 03/26/02 62.17 60.61
5,560.28 04/09/02 62.05 60.49
5,560.76 05/23/02 61.57 60.01
5,560.58 06/05/02 61.75 60.19
5,560.43 07/08/02 61.90 60.34
5,560.44 08/23/02 61.89 60.33
5,560.71 09/11/02 61.62 60.06
5,560.89 10/23/02 61.44 59.88
5,557.86 11/22/02 64.47 62.91
5,561.10 12/03/02 61.23 59.67
5,561.39 01/09/03 60.94 59.38
5,561.41 02/12/03 60.92 59.36
5,561.93 03/26/03 60.40 58.84
5,561.85 04/02/03 60.48 58.92
5,536.62 05/01/03 85 .71 84.15
5,528.56 06/09/03 93.77 92.21
5,535.28 07/07/03 87.05 85.49
5,534.44 08/04/03 87 .89 86.33
5,537.10 09/11/03 85.23 83.67
5,539.96 10/02/03 82.37 80.81
5,535.91 11/07/03 86.42 84.86
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,550.70 12/03/03 71.63 70.07
5,557.58 01/15/04 64.75 63.19
5,558.80 02/10/04 63.53 61.97
5,560.08 03/28/04 62.25 60.69
5,560.55 04/12/04 61.78 60.22
5,561.06 05/13/04 61.27 59.71
5,561.48 06/18/04 60.85 59.29
5,561.86 07/28/04 60.47 58.91
5,529.17 08/30/04 93.16 91.60
5,536.55 09/16/04 85.78 84.22
5,529.00 10/11/04 93.33 91.77
5,541.55 11/16/04 80.78 79.22
5,541.12 12/22/04 81.21 79.65
5,540.59 01/18/05 81.74 80.18
5,542.85 02/28/05 79.48 77.92
5,537.91 03/15/05 84.42 82.86
5,548.67 04/26/05 73.66 72.10
5,549.53 05/24/05 72.80 71.24
5,544.36 06/30/05 77.97 76.41
5,545.16 07/29/05 77.17 75.61
5,544.67 09/12/05 77.66 76.10
5,541.28 09/27/05 81.05 79.49
5,536.96 12/07/05 85.37 83.81
5,546.49 03/08/06 75.84 74.28
5,546.15 06/13/06 76.18 74.62
5,545.15 07/18/06 77.18 75.62
5,545.91 11/17/06 76.42 74.86
5,545.90 02/27/07 76.43 74.87
5,548.16 05/02/07 74.17 72.61
5,547.20 08/13/07 75.13 73.57
5,547.20 10/10/07 75.13 73.57
5,547.79 03/26/08 74.54 72.98
5,545.09 06/25/08 77.24 75.68
5,550.36 08/26/08 71.97 70.41
5,550.39 10/14/08 71.94 70.38
5,542.25 03/03/09 80.08 78.52
5,542.25 06/24/09 80.08 78.52
5,550.19 09/10/09 72.14 70.58
5,550.94 12/11/09 71.39 69.83
5,546.08 03/11/10 76.25 74.69
5,550.98 05/11/10 71.35 69.79
5,548.33 09/29/10 74.00 72.44
5,551.01 12/21/10 71.32 69.76
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,547.00 02/28/11 75.33 73.77
5,557.54 06/21/11 64.79 63.23
5,551.14 09/20/11 71.19 69.63
5,550.32 12/21/11 72.01 70.45
5,551.22 03/27/12 71.11 69.55
5,551.29 06/28/12 71.04 69.48
5,550.29 09/27/12 72.04 70.48
5,549.31 12/28/12 73.02 71.46
5,552.30 03/28/13 70.03 68.47
5,550.18 06/27/13 72.15 70.59
5,552.55 09/27/13 69.78 68.22
5,553.23 12/20/13 69.10 67.54
5,551.91 03/27/14 70.42 68.86
5,552.93 06/25/14 69.40 67.84
5,552.23 09/25/14 70.10 68.54
5,552.08 12/17/14 70.25 68.69
5,551.13 03/26/15 71.20 69.64
5,556.02 06/22/15 66.31 64.75
5,543.38 09/30/15 78.95 77.39
5,551.13 12/02/15 71.20 69.64
5,542.10 03/30/16 80.23 78.67
5,542.31 06/30/16 80.02 78.46
5,540.96 09/29/16 81.37 79.81
5,540.65 12/21/16 81.68 80.12
5,542.05 03/30/17 80.28 78.72
5,550.28 06/27/17 72.05 70.49
5,534.84 09/28/17 87.49 85.93
5,532.41 11/30/17 89.92 88.36
5,534.64 03/28/18 87.69 86.13
5,539.53 06/22/18 82.80 81.24
5,537.04 09/24/18 85.29 83.73
5,537.82 12/17/18 84.51 82.95
5,536.10 03/25/19 86.23 84.67
5,536.20 06/24/19 86.13 84.57
5,538.67 08/12/19 83.66 82.10
......
N 0
......
0 0
Depth Below Measuring Point (ft.)
00 0 0\ 0 .i,.. 0 N 0 0
09/25/79
02/06/81
06/21/82
11/03/83
03/17/85
07/30/86
12/12/87
04/25/89
09/07/90
01/20/92 s=
06/03/93 ~
.i.
10/16/94 ~
02/28/96 -~ ..,
07/12/97 ~ ~
11/24/98 "Cl Er
04/07/00 0 ~
08/20/01 ~ ..,
01/02/03 ~ ...
9
05/16/04 ~ ,-..
09/28/05 ?
C"' -02/10/07 9 "Cl
06/24/08 --
11/06/09
03/21/11
08/02/12
12/15/13
04/29/15
09/10/16
01/23/18
06/07/19
10/19/20
03/03/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,5 7.23 11/08/99 81.35 80.33
5,537.38 11/09/99 81.20 80.18
5,537.48 01/02/00 81.10 80.08
5,537.48 01/10/00 81.10 80.08
5,537.23 01/17/00 81.35 80.33
5,537.28 01/24/00 81.30 80.28
5,537.28 02/01/00 81.30 80.28
5,537.18 02/07/00 81.40 80.38
5,537.48 02/14/00 81.10 80.08
5,537.48 02/23/00 81.10 80.08
5,537.58 03/01/00 81.00 79.98
5,537.68 03/08/00 80.90 79.88
5,537.98 03/15/00 80.60 79.58
5,537.68 03/20/00 80.90 79.88
5,537.68 03/29/00 80.90 79.88
5,537.43 04/04/00 81.15 80.13
5,537.18 04/13/00 81.40 80.38
5,537.48 04/21/00 81.10 80.08
5,537.68 04/28/00 80.90 79.88
5,537.58 05/01/00 81.00 79.98
5,537.88 05/11/00 80.70 79.68
5,537.58 05/15/00 81.00 79.98
5,537.88 05/25/00 80.70 79.68
5,537.88 06/09/00 80.70 79.68
5,537.90 06/16/00 80.68 79.66
5,537.88 06/26/00 80.70 79.68
5,538.10 07/06/00 80.48 79.46
5,538.04 07/13/00 80.54 79.52
5,538.16 07/18/00 80.42 79.40
5,538.42 07/27/00 80.16 79.14
5,538.56 08/02/00 80.02 79.00
5,538.68 08/09/00 79.90 78.88
5,538.66 08/15/00 79.92 78.90
5,538.33 08/31/00 80.25 79.23
5,539.18 09/01/00 79.40 78.38
5,539.12 09/08/00 79.46 78.44
5,539.34 09/13/00 79.24 78.22
5,539.50 09/20/00 79.08 78.06
5,539.69 10/05/00 78.89 77.87
5,540.33 11/09/00 78.25 77.23
5,540.74 12/06/00 77.84 76.82
5,542.39 01/14/01 76.19 75.17
5,543.69 02/02/01 74.89 73.87
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,544.96 03/29/01 73.62 72.60
5,545.45 04/30/01 73.13 72.11
5,545.89 05/31/01 72.69 71.67
5,546.19 06/21/01 72.39 71.37
5,546.50 07/10/01 72.08 71.06
5,547.18 08/20/01 71.40 70.38
5,547.59 09/19/01 70.99 69.97
5,547.84 10/02/01 70.74 69.72
5,548.12 11/08/01 70.46 69.44
5,548.65 12/03/01 69.93 68.91
5,548.87 01/03/02 69.71 68.69
5,549.37 02/06/02 69.21 68.19
5,550.00 03/26/02 68.58 67.56
5,550.22 04/09/02 68.36 67 .34
5,550.81 05/23/02 67.77 66.75
5,550.79 06/05/02 67.79 66.77
5,551.08 07/08/02 67.50 66.48
5,551.54 08/23/02 67.04 66.02
5,551.79 09/11/02 66.79 65 .77
5,552.19 10/23/02 66.39 65.37
5,552.27 11/22/02 66.31 65.29
5,552.48 12/03/02 66.10 65.08
5,552.74 01/09/03 65.84 64.82
5,552.92 02/12/03 65.66 64.64
5,553.40 03/26/03 65.18 64.16
5,553.48 04/02/03 65.10 64.08
5,552.32 05/01/03 66.26 65.24
5,550.53 06/09/03 68.05 67.03
5,550.09 07/07/03 68.49 67.47
5,549.64 08/04/03 68.94 67.92
5,549.31 09/11/03 69.27 68.25
5,549.58 10/02/03 69.00 67.98
5,549.50 11/07 /03 69.08 68.06
5,550.07 12/03/03 68.51 67.49
5,551.86 01/15/04 66.72 65.70
5,552.57 02/10/04 66.01 64.99
5,553.63 03/28/04 64.95 63.93
5,554.04 04/12/04 64.54 63.52
5,554.60 05/13/04 63.98 62.96
5,556.28 06/18/04 62.30 61.28
5,556.61 07/28/04 61.97 60.95
5,554.21 08/30/04 64.37 63.35
5,553.49 09/16/04 65 .09 64.07
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,552.53 10/11/04 66.05 65 .03
5,552.42 11/16/04 66.16 65.14
5,552.46 12/22/04 66.12 65.10
5,552.07 01/18/05 66.51 65.49
5,552.21 02/28/05 66.37 65.35
5,552.26 03/15/05 66.32 65.30
5,552.30 04/26/05 66.28 65.26
5,552.25 05/24/05 66.33 65.31
5,552.22 06/30/05 66.36 65.34
5,552.15 07/29/05 66.43 65.41
5,552.47 09/12/05 66.11 65.09
5,552.50 12/07/05 66.08 65.06
5,552.96 03/08/06 65.62 64.60
5,553.23 06/14/06 65.35 64.33
5,557.20 07/18/06 61.38 60.36
5,553.32 11/07/06 65.26 64.24
5,554.35 02/27/07 64.23 63.21
5,554.07 05/02/07 64.51 63.49
5,554.07 08/14/07 64.51 63.49
5,553.88 10/10/07 64.70 63.68
5,555.73 03/26/08 62.85 61.83
5,556.60 06/24/08 61.98 60.96
5,556.83 08/26/08 61.75 60.73
5,556.87 10/14/08 61.71 60.69
5,556.90 03/10/09 61.68 60.66
5,556.91 06/24/09 61.67 60.65
5,556.61 09/10/09 61.97 60.95
5,556.78 12/11/09 61.8 60.78
5,556.75 03/11/10 61.83 60.81
5,556.19 05/11/10 62.39 61.37
5,555.26 09/29/10 63.32 62.30
5,554.66 12/21/10 63.92 62.90
5,554.74 02/28/11 63.84 62.82
5,554.57 06/21/11 64.01 62.99
5,554.13 09/20/11 64.45 63.43
5,554.54 12/21/11 64.04 63.02
5,553.64 03/27/12 64.94 63.92
5,553.66 06/28/12 64.92 63.90
5,553.73 09/27/12 64.85 63.83
5,553.59 12/28/12 64.99 63.97
5,554.73 03/28/13 63.85 62.83
5,554.44 06/27/13 64.14 63.12
5,554.37 09/27/13 64.21 63.19
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,553.92 12/20/13 64.66 63.64
5,553.20 03/27/14 65.38 64.36
5,552.20 06/25/14 66.38 65.36
5,551.13 09/25/14 67.45 66.43
5,550.72 12/17/14 67.86 66.84
5,546.50 03/26/15 72.08 71.06
5,544.18 06/22/15 74.40 73.38
5,535.85 09/30/15 82.73 81.71
5,529.54 12/02/15 89.04 88.02
5,527.55 03/30/16 91.03 90.01
5,525.92 06/30/16 92.66 91.64
5,524.48 09/29/16 94.10 93.08
5,533.15 12/21/16 85.43 84.41
5,527.92 03/30/17 90.66 89.64
5,534.48 06/27/17 84.10 83.08
5,524.98 09/28/17 93.60 92.58
5,525.88 11/30/17 92.70 91.68
5,526.18 03/28/18 92.40 91.38
5,515.78 06/22/18 102.80 101.78
5,510.83 09/24/18 107.75 106.73
5,542.47 12/17/18 76.11 75.09
5,531.82 03/25/19 86.76 85.74
5,539.90 06/24/19 78.68 77.66
5,538.56 08/12/19 80.02 79.00
--~ -0
Depth Below Measuring Point (ft.) -8 'Cl 0 00 0 -....J 0 0\ 0 Vl 0
11/08/99
04/06/00
09/03/00
01/31/01
06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04
03/11/05
08/08/05 ~
01/05/06 ~
06/04/06 ...
I
11/01/06 ~
03/31/07 ~ 08/28/07 -01/25/08 ~ "1
06/23/08 C,
11/20/08 ~ ~ 04/19/09 -=-09/16/09 0 -02/13/10 < 07/13/10 ~ "1
12/10/10 ~
05/09/11 ... a 10/06/11 ~
03/04/12 ,-...
08/01/12 ?
-12/29/12 a" -05/28/13 a
10/25/13 ~ -03/24/14
08/21/14
01/18/15
06/17/15
11/14/15
04/12/16
09/09/16
02/06/17
07/06/17
12/03/17
05/02/18
09/29/18
02/26/19
07/26/19
12/23/19
05/21/20
10/18/20
Water Levels and Data over Time
White Mesa Mill-Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,548.57 11/08/99 76.15 74.53
5,548.57 11/09/99 76.15 74.53
5,548.32 01/02/00 76.40 74.78
5,548.52 01/10/00 76.20 74.58
5,548.32 01/17/00 76.40 74.78
5,548.72 01/24/00 76.00 74.38
5,548.62 02/01/00 76.10 74.48
5,548.62 02/07/00 76.10 74.48
5,549.02 02/14/00 75.70 74.08
5,549.12 02/23/00 75.60 73.98
5,549.22 03/01/00 75.50 73.88
5,549.32 03/08/00 75.40 73.78
5,549.22 03/15/00 75.50 73.88
5,549.92 03/20/00 74.80 73.18
5,549.72 03/29/00 75.00 73.38
5,549.42 04/04/00 75.30 73.68
5,549.52 04/13/00 75.20 73.58
5,549.72 04/21/00 75.00 73.38
5,549.82 04/28/00 74.90 73.28
5,549.82 05/01/00 74.90 73.28
5,550.12 05/11/00 74.60 72.98
5,549.82 05/15/00 74.90 73 .28
5,550.12 05/25/00 74.60 72.98
5,550.12 06/09/00 74.60 72.98
5,550.22 06/16/00 74.50 72.88
5,550.07 06/26/00 74.65 73.03
5,550.17 07/06/00 74.55 72.93
5,550.17 07/13/00 74.55 72.93
5,550.18 07/18/00 74.54 72.92
5,550.33 07/27/00 74.39 72.77
5,550.38 08/02/00 74.34 72.72
5,550.40 08/09/00 74.32 72.70
5,550.42 08/15/00 74.30 72.68
5,550.54 08/31/00 74.18 72.56
5,550.87 09/08/00 73.85 72.23
5,550.97 09/13/00 73.75 72.13
5,551.04 09/20/00 73.68 72.06
5,545.83 10/05/00 78.89 77.27
5,546.47 11/09/00 78.25 76.63
5,546.88 12/06/00 77.84 76.22
5,552.18 01/26/01 72.54 70.92
5,552.20 02/02/01 72.52 70.90
5,551.10 03/29/01 73.62 72.00
Water Levels and Data over Time
White Mesa Mill-Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,551.59 04/30/01 73.13 71.51
5,552.03 05/31/01 72.69 71.07
5,552.33 06/21/01 72.39 70.77
5,552.64 07/10/01 72.08 70.46
5,553.32 08/20/01 71.40 69.78
5,553.73 09/19/01 70.99 69.37
5,553.98 10/02/01 70.74 69.12
5,554.14 11/08/01 70.58 68.96
5,554.79 12/03/01 69.93 68.31
5,554.74 01/03/02 69.98 68.36
5,554.91 02/06/02 69.81 68.19
5,555.15 03/26/02 69.57 67.95
5,555.39 04/09/02 69.33 67.71
5,555.73 05/23/02 68.99 67.37
5,555.79 06/05/02 68.93 67.31
5,555.91 07/08/02 68.81 67.19
5,556.04 08/23/02 68.68 67.06
5,556.25 09/11/02 68.47 66.85
5,556.72 10/23/02 68.00 66.38
5,556.42 11/22/02 68.30 66.68
5,557.01 12/03/02 67.71 66.09
5,557.20 01/09/03 67.52 65.90
5,557.35 02/12/03 67.37 65.75
5,557.83 03/26/03 66.89 65.27
5,557.87 04/02/03 66.85 65.23
5,553.71 05/01/03 71.01 69.39
5,548.98 06/09/03 75.74 74.12
5,548.14 07/07/03 76.58 74.96
5,547.75 08/04/03 76.97 75.35
5,547.22 09/11/03 77.50 75.88
5,547.68 10/02/03 77.04 75.42
5,547.52 11/07/03 77.20 75.58
5,548.29 12/03/03 76.43 74.81
5,554.00 01/15/04 70.72 69.10
5,555.46 02/10/04 69.26 67.64
5,556.90 03/28/04 67.82 66.20
5,557.49 04/12/04 67.23 65.61
5,558.07 05/13/04 66.65 65.03
5,558.19 06/18/04 66.53 64.91
5,559.00 07/28/04 65.72 64.10
5,554.26 08/30/04 70.46 68.84
5,551.97 09/16/04 72.75 71.13
5,549.65 10/11/04 75.07 73.45
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,549.89 11/16/04 74.83 73.21
5,550.37 12/22/04 74.35 72.73
5,549.95 01/18/05 74.77 73.15
5,550.09 02/28/05 74.63 73.01
5,550.13 03/15/05 74.59 72.97
5,550.18 04/26/05 74.54 72.92
5,550.32 05/24/05 74.40 72.78
5,550.21 06/30/05 74.51 72.89
5,550.11 07/29/05 74.61 72.99
5,550.33 09/12/05 74.39 72.77
5,550.29 12/07/05 74.43 72.81
5,551.30 03/08/06 73.42 71.80
5,551.42 06/14/06 73.3 71.68
5,550.52 07/18/06 74.20 72.58
5550.52 11/07/06 74.20 72.58
5552.89 02/27/07 71.83 70.21
5,552.06 05/02/07 72.66 71.04
5,552.02 08/14/07 72.7 71.08
5,552.20 10/10/07 72.52 70.90
5,554.58 03/26/08 70.14 68.52
5,555.23 06/24/08 69.49 67.87
5,555.29 08/26/08 69.43 67.81
5,555.43 10/14/08 69.29 67.67
5,555.73 03/10/09 68.99 67.37
5,556.25 06/24/09 68.47 66.85
5,555.94 09/10/09 68.78 67.16
5,556.53 12/11/09 68.19 66.57
5,557.87 03/11/10 66.85 65.23
5,557.63 05/11/10 67.09 65.47
5,557.24 09/29/10 67.48 65.86
5,557.00 12/21/10 67.72 66.10
5,557.61 02/28/11 67.11 65.49
5,557.58 06/21/11 67.14 65.52
5,557.46 09/20/11 67.26 65.64
5,557.84 12/21/11 66.88 65.26
5,557.86 03/27/12 66.86 65.24
5,557.87 06/28/12 66.85 65.23
5,557.46 09/27/12 67.26 65.64
5,557.82 12/28/12 66.9 65.28
5,559.39 03/28/13 65.33 63.71
5,559.21 06/27/13 65.51 63.89
5,559.26 09/27/13 65.46 63.84
5,559.27 12/20/13 65.45 63.83
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,558.92 03/27/14 65.8 64.18
5,557.99 06/25/14 66.73 65.11
5,557.09 09/25/14 67.63 66.01
5,557.07 12/17/14 67.65 66.03
5,549.93 03/26/15 74.79 73.17
5,551.30 06/22/15 73.42 71.80
5,547.12 09/30/15 77.60 75.98
5,538.34 12/02/15 86.38 84.76
5,542.22 03/30/16 82.50 80.88
5,538.31 06/30/16 86.41 84.79
5,536.70 09/29/16 88.02 86.40
5,540.40 12/21/16 84.32 82.70
5,536.61 03/30/17 88.11 86.49
5,547.16 06/27/17 77.56 75.94
5,522.65 09/28/17 102.07 100.45
5,532.64 11/30/17 92.08 90.46
5,506.94 03/28/18 117.78 116.16
5521.60 06/22/18 103.12 101.50
5510.01 09/24/18 114.71 113.09
5543.01 12/17/18 81.71 80.09
5522.70 03/25/19 102.02 100.40
5522.49 06/24/19 102.23 100.61
5522.29 08/12/19 102.43 100.81
--I.J,) N -0 0 0
Depth Below Measuring Point (ft.) -8 \0 0 00 0 -..J 0 °' 0
u,
0
11/08/99
04/06/00
09/03/00
01/31/01
06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04
03/11/05
08/08/05 ~
01/05/06 ~
06/04/06 ,&;..
I
11/01/06 N
03/31/07 ~ 08/28/07 """' 01/25/08 ~ "1
06/23/08 ~
11/20/08 ~ "Cl 04/19/09 ;.
09/16/09 0 02/13/10 -< 07/13/10 ~ "1
12/10/10 ~
05/09/11 .... e 10/06/11 ~
03/04/12 ---08/01/12 ?
12/29/12 1:1" -05/28/13 e
10/25/13 "Cl _.,
03/24/14
08/21/14
01/18/15
06/17/15
11/14/15
04/12/16
09/09/16
02/06/17
07/06/17
12/03/17
05/02/18
09/29/18
02/26/19
07/26/19
12/23/19
05/21/20
10/18/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
{z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,565.78 11/29/99 66.45 65.43
5,566.93 01/02/00 65.30 64.28
5,567.03 01/10/00 65.20 64.18
5,566.83 01/17/00 65.40 64.38
5,567.13 01/24/00 65.10 64.08
5,567.33 02/01/00 64.90 63.88
5,567.13 02/07/00 65.10 64.08
5,567.43 02/14/00 64.80 63.78
5,567.63 02/23/00 64.60 63.58
5,567.73 03/01/00 64.50 63.48
5,567.83 03/08/00 64.40 63.38
5,567.70 03/15/00 64.53 63.51
5,568.03 03/20/00 64.20 63.18
5,567.93 03/29/00 64.30 63.28
5,567.63 04/04/00 64.60 63.58
5,567.83 04/13/00 64.40 63.38
5,568.03 04/21/00 64.20 63.18
5,568.23 04/28/00 64.00 62.98
5,568.13 05/01/00 64.10 63.08
5,568.53 05/11/00 63.70 62.68
5,568.23 05/15/00 64.00 62.98
5,568.53 05/25/00 63.70 62.68
5,568.61 06/09/00 63.62 62.60
5,568.69 06/16/00 63.54 62.52
5,568.45 06/26/00 63.78 62.76
5,568.61 07/06/00 63.62 62.60
5,568.61 07/06/00 63.62 62.60
5,568.49 07/13/00 63.74 62.72
5,568.55 07/18/00 63.68 62.66
5,568.65 07/27/00 63.58 62.56
5,568.73 08/02/00 63.50 62.48
5,568.77 08/09/00 63.46 62.44
5,568.76 08/16/00 63.47 62.45
5,568.95 08/31/00 63.28 62.26
5,568.49 09/08/00 63.74 62.72
5,568.67 09/13/00 63.56 62.54
5,568.96 09/20/00 63.27 62.25
5,568.93 10/05/00 63.3 62.28
5,569.34 11/09/00 62.89 61.87
5,568.79 12/06/00 63.44 62.42
5,569.11 01/03/01 63.12 62.10
5,569.75 02/09/01 62.48 61.46
5,570.34 03/28/01 61.89 60.87
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,570.61 04/30/01 61.62 60.60
5,570.70 05/31/01 61.53 60.51
5,570.88 06/21/01 61.35 60.33
5,571.02 07/10/01 61.21 60.19
5,571.70 08/20/01 60.53 59.51
5,572.12 09/19/01 60.11 59.09
5,572.08 10/02/01 60.15 59.13
5,572.78 11/08/01 59.45 58.43
5,573.27 12/03/01 58.96 57.94
5,573.47 01/03/02 58.76 57.74
5,573.93 02/06/02 58.30 57.28
5,574.75 03/26/02 57.48 56.46
5,574.26 04/09/02 57.97 56.95
5,575.39 05/23/02 56.84 55.82
5,574.84 06/05/02 57.39 56.37
5,575.33 07/08/02 56.90 55.88
5,575.79 08/23/02 56.44 55.42
5,576.08 09/11/02 56.15 55.13
5,576.30 10/23/02 55.93 54.91
5,576.35 11/22/02 55.88 54.86
5,576.54 12/03/02 55.69 54.67
5,576.96 01/09/03 55.27 54.25
5,577.11 02/12/03 55.12 54.10
5,577.61 03/26/03 54.62 53.60
5,572.80 04/02/03 59.43 58.41
5,577.89 05/01/03 54.34 53.32
5,577.91 06/09/03 54.32 53.30
5,577.53 07/07/03 54.70 53.68
5,577.50 08/04/03 54.73 53.71
5,577.71 09/11/03 54.52 53.50
5,577.31 10/02/03 54.92 53.90
5,577.33 11/07/03 54.90 53.88
5,577.34 12/03/03 54.89 53.87
5,578.24 01/15/04 53.99 52.97
5,578.38 02/10/04 53.85 52.83
5,578.69 03/28/04 53.54 52.52
5,579.15 04/12/04 53.08 52.06
5,579.47 05/13/04 52.76 51.74
5,579.53 06/18/04 52.70 '51.68
5,580.17 07/28/04 52.06 51.04
5,580.20 08/30/04 52.03 51.01
5,580.26 09/16/04 51.97 50.95
5,580.12 10/11/04 52.11 51.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitorin; (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,579.93 11/16/04 52.30 51.28
5,580.07 12/22/04 52.16 51.14
5,579.80 01/18/05 52.43 51.41
5,580.35 02/28/05 51.88 50.86
5,580.57 03/15/05 51.66 50.64
5,580.86 04/26/05 51.37 50.35
5,581.20 05/24/05 51.03 50.01
5,581.51 06/30/05 50.72 49.70
5,581.55 07/29/05 50.68 49.66
5,581.68 09/12/05 50.55 49.53
5,581.83 12/07/05 50.4 49.38
5,564.92 03/08/06 67.31 66.29
5,582.73 06/13/06 49.50 48.48
5,582.33 07/18/06 49.90 48.88
5,582.75 11/07/06 49.48 48.46
5583.35 02/27/07 48.88 47.86
5,559.57 05/02/07 72.66 71.64
5,583.29 08/14/07 48.94 47.92
5,583.49 10/10/07 48.74 47.72
5,584.95 03/26/08 47.28 46.26
5,584.59 06/24/08 47.64 46.62
5,584.55 08/26/08 47.68 46.66
5,584.03 10/14/08 48.2 47.18
5,583.64 03/03/09 48.59 47.57
5,587.34 06/24/09 44.89 43.87
5,582.90 09/10/09 49.33 48.31
5,583.27 12/11/09 48.96 47.94
5,583.63 03/11/10 48.6 47.58
5,583.82 05/11/10 48.41 47.39
5,583.51 09/29/10 48.72 47.70
5,582.86 12/21/10 49.37 48.35
5,582.60 02/28/11 49.63 48.61
5,590.00 06/21/11 42.23 41.21
5,582.70 09/20/11 49.53 48.51
5,583.05 12/21/11 49.18 48.16
5,581.93 03/27/12 50.30 49.28
5,582.03 06/28/12 50.20 49.18
5,582.08 09/27/12 50.15 49.13
5,581.94 12/28/12 50.29 49.27
5,581.52 03/28/13 50.71 49.69
5,580.88 06/27/13 51.35 50.33
5,580.58 09/27/13 51.65 50.63
5,580.38 12/20/13 51.85 50.83
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,579.62 03/27/14 52.61 51.59
5,578.52 06/25/14 53.71 52.69
5,577.59 09/25/14 54.64 53.62
5,577.40 12/17/14 54.83 53.81
5,576.73 03/26/15 55.50 54.48
5,576.62 06/22/15 55.61 54.59
5,576.16 09/30/15 56.07 55.05
5,575.57 12/02/15 56.66 55.64
5,575.62 03/30/16 56.61 55.59
5,574.89 06/30/16 57.34 56.32
5,574.37 09/29/16 57.86 56.84
5,574.23 12/21/16 58.00 56.98
5,574.23 03/30/17 58.00 56.98
5,573.72 06/27/17 58.51 57.49
5,573.28 09/28/17 58.95 57.93
5,572.66 11/30/17 59.57 58.55
5,572.19 03/28/18 60.04 59.02
5571.83 06/22/18 60.40 59.38
5571.34 09/25/18 60.89 59.87
5570.99 12/17/18 61.24 60.22
5570.21 03/25/19 62.02 61.00
5570.28 6/24/2019 61.95 60.93
5570.04 8/12/2019 62.19 61.17
-..J Vl -..J 0
Depth Below Measuring Point (ft.)
0\ Vl 0\ 0 Vl Vl Vl 0
.j:::,.
Vl
.j:::,.
0
l l/29/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
,_ 03/13/03
08/10/03
01/07/04
06/05/04
11/02/04
04/01/05
08/29/05 ~
01/26/06 ~
06/25/06 J;.
I
11/22/06 ~
04/21/07 ~ 09/18/07 -02/15/08 ~ ~
07/14/08 ~
12/11/08 ~ "'Q 05/10/09 ~ 10/07/09 0 -03/06/10 ~
08/03/10 ~ ~
12/31/10 ~
05/30/11 ... a 10/27/11 ~
03/25/12 .-..
08/22/12 ?
01/19/13 'r::r' -06/18/13 a
11/15/13 "'Q '-'
04/14/14
09/11/14
02/08/15
07/08/15
12/05/15
05/03/16
09/30/16
02/27/17
07/27/17
12/24/17
05/23/18
10/20/18
03/19/19
08/16/19
01/13/20
06/11/20
11/08/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,612.301 5,613.485 1.184 114.5
5,512.145 05/25/00 101.34 100.16
5,518.985 06/09/00 94.50 93.32
5,512.145 06/16/00 101.34 100.16
5,517.465 06/26/00 96.02 94.84
5,520.145 07/06/00 93.34 92.16
5,521.435 07/13/00 92.05 90.87
5,522.005 07/18/00 91.48 90.30
5,522.945 07/27/00 90.54 89.36
5,523.485 08/02/00 90.00 88.82
5,523.845 08/09/00 89.64 88.46
5,523.885 08/15/00 89.60 88.42
5,524.555 09/01/00 88.93 87.75
5,513.235 09/08/00 100.25 99.07
5,516.665 09/13/00 96.82 95.64
5,519.085 09/20/00 94.40 93.22
5,522.165 10/05/00 91.32 90.14
5,524.665 11/09/00 88.82 87.64
5,518.545 12/06/00 94.94 93.76
5,527.695 01/03/01 85.79 84.61
5,529.085 02/09/01 84.40 83.22
5,529.535 03/27/01 83.95 82.77
5,530.235 04/30/01 83.25 82.07
5,530.265 05/31/01 83.22 82.04
5,534.405 06/22/01 79.08 77.90
5,533.145 07/10/01 80.34 79.16
5,534.035 08/20/01 79.45 78.27
5,534.465 09/19/01 79.02 77.84
5,533.285 10/02/01 80.20 79.02
5,533.865 11/08/01 79.62 78.44
5,534.275 12/03/01 79.21 78.03
5,534.715 01/03/02 78.77 77.59
5,535.435 02/06/02 78.05 76.87
5,536.445 03/26/02 77.04 75.86
5,536.405 04/09/02 77.08 75.90
5,537.335 05/23/02 76.15 74.97
5,537.325 06/05/02 76.16 74.98
5,537.975 07/08/02 75.51 74.33
5,538.825 08/23/02 74.66 73.48
5,539.275 09/11/02 74.21 73.03
5,539.765 10/23/02 73.72 72.54
5,540.205 11/22/02 73.28 72.10
5,540.295 12/03/02 73.19 72.01
5,540.795 01/09/03 72.69 71.51
Water Levels and Data over Time
White Mesa Mill · Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,612.301 5,613.485 1.184 114.5
5,540.985 02/12/03 72.50 71.32
5,541.675 03/26/03 71.81 70.63
5,541.765 04/02/03 71.72 70.54
5,541.885 05/01/03 71.60 70.42
5,542.025 06/09/03 71.46 70.28
5,541.925 07/07/03 71.56 70.38
5,541.885 08/04/03 71.60 70.42
5,541.825 09/11/03 71.66 70.48
5,541.885 10/02/03 71.60 70.42
5,541.995 11/07/03 71.49 70.31
5,542.005 12/03/03 71.48 70.30
5,542.555 01/15/04 70.93 69.75
5,542.705 02/10/04 70.78 69.60
5,543.225 03/28/04 70.26 69.08
5,543.555 04/12/04 69.93 68.75
5,543.865 05/13/04 69.62 68.44
5,543.915 06/18/04 69.57 68.39
5,544.655 07/28/04 68.83 67.65
5,544.795 08/30/04 68.69 67.51
5,544.845 09/16/04 68.64 67.46
5,544.705 10/11/04 68 .78 67.60
5,544.525 11/16/04 68.96 67.78
5,544.625 12/22/04 68.86 67.68
5,544.305 01/18/05 69.18 68.00
5,544.585 02/28/05 68.90 67.72
5,544.685 03/15/05 68.80 67.62
5,544.675 04/26/05 68.81 67.63
5,544.785 05/24/05 68.70 67.52
5,544.795 06/30/05 68.69 67.51
5,544.775 07/29/05 68.71 67.53
5,545.005 09/12/05 68.48 67.30
5,545.225 12/07/05 68.26 67.08
5,545.735 03/08/06 67.75 66.57
5,545.785 06/14/06 67.70 66.52
5,545.855 07/18/06 67.63 66.45
5,545.805 11/07/06 67.68 66.50
5546.675 02/27/07 66.81 65.63
5,546.535 05/02/07 66.95 65.77
5,547.155 08/15/07 66.33 65.15
5,547.215 10/10/07 66.27 65.09
5,548.305 03/26/08 65.18 64.00
5,548.865 06/24/08 64.62 63.44
5,549.235 08/26/08 64.25 63.07
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,612.301 5,613.485 1.184 114.5
5,549.305 10/14/08 64.18 63.00
5,549.725 03/03/09 63.76 62.58
5,549.905 06/24/09 63.58 62.40
5,549.695 09/10/09 63.79 62.61
5,549.865 12/11/09 63.62 62.44
5,545.60 03/11/10 67.89 66.71
5,530.88 05/11/10 82.61 81.43
5,545.24 09/29/10 68.25 67 .07
5,533.66 12/21/10 79.83 78.65
5,544.44 02/28/11 69.05 67.87
5,543.73 06/21/11 69.76 68.58
5,540.48 09/20/11 73.01 71.83
5,544.36 12/21/11 69.13 67.95
5,543.48 03/27/12 70.01 68.83
5,543.49 06/28/12 70.00 68.82
5,543.36 09/27/12 70.13 68.95
5,543.51 12/28/12 69.98 68.80
5,543.49 03/28/13 70.00 68.82
5,543.36 06/27/13 70.13 68.95
5,544.59 09/27/13 68.90 67.72
5,543.33 12/20/13 70.16 68.98
5,544.11 03/27/14 69.38 68.20
5,543.61 06/25/14 69.88 68.70
5,543.67 09/25/14 69.82 68.64
5,543.69 12/17/14 69.80 68.62
5,541.49 03/26/15 72.00 70.82
5,539.67 06/22/15 73.82 72.64
5,541.35 09/30/15 72.14 70.96
5,541.63 12/02/15 71.86 70.68
5,540.38 03/30/16 73.11 71.93
5,539.46 06/30/16 74.03 72.85
5,540.39 09/29/16 73.10 71.92
5,539.21 12/21/16 74.28 73.10
5,539.53 03/30/17 73.96 72.78
5,539.89 06/27/17 73.60 72.42
5,540.09 09/28/17 73.40 72.22
5,539.07 11/30/17 74.42 73.24
5,540.45 03/28/18 73.04 71.86
5,531.79 06/22/18 81.70 80.52
5,531.94 09/24/18 81.55 80.37
5,540.22 12/17/18 73.27 72.09
5,514.10 03/25/19 99.39 98.21
5,529.11 06/24/19 84.38 83.20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring {blw.MP) (blw.LSD) Well
5,612.301 5,613.485 1.184 114.5
5,527.15 08/12/19 86.34 85.16
-......
0 -8
Depth Below Measuring Point (ft.)
'° 0 00 0
-...,l
0 0\ 0
V,
0
05/25/00
10/22/00
03/21/01
08/18/01
01/15/02
06/14/02
11/11/02
04/10/03
09/07/03
02/04/04
07/03/04
11/30/04
04/29/05
09/26/05 ~ 02/23/06 ~ 07/23/06 ,I;..
12/20/06 I ,I;..
05/19/07 ~ 10/16/07
03/14/08 -~
08/11/08 "1
~ 01/08/09 ~
06/07/09 "O -11/04/09 =-
04/03/10 0
08/31/10 ~ ~
01/28/11 "1
~ 06/27/11 -· 11/24/11 a ~ 04/22/12 ,,-..._
09/19/12 ?
02/16/13 O" -07/16/13 a 12/13/13 "O '-' 05/12/14
10/09/14
03/08/15
08/05/15
01/02/16
05/31/16
10/28/16
03/27/17
08/24/17
01/21/18
06/20/18
11/17/18
04/16/19
09/13/19
02/10/20
07/09/20
12/06/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.75 5 640.70 1.95 12 1.85
5,579.30 01/02/00 61.40 59.45
5,579.60 01/10/00 61.10 59.15
5,579.35 01/17/00 61.35 59.40
5,579.60 01/24/00 61.10 59.15
5,579.50 02/01/00 61.20 59.25
5,579.50 02/07/00 61.20 59.25
5,579.90 02/14/00 60.80 58.85
5,579.90 02/23/00 60.80 58.85
5,580.20 03/01/00 60.50 58.55
5,580.00 03/08/00 60.70 58.75
5,580.04 03/15/00 60.66 58.71
5,580.70 03/20/00 60.00 58.05
5,580.30 03/29/00 60.40 58.45
5,580.00 04/04/00 60.70 58.75
5,580.20 04/13/00 60.50 58.55
5,580.40 04/21/00 60.30 58.35
5,580.50 04/28/00 60.20 58.25
5,580.50 05/01/00 60.20 58.25
5,580.90 05/11/00 59.80 57.85
5,580.50 05/15/00 60.20 58.25
5,580.75 05/25/00 59.95 58.00
5,580.80 06/09/00 59.90 57.95
5,580.92 06/16/00 59.78 57.83
5,580.80 06/26/00 59.90 57.95
5,580.90 07/06/00 59.80 57.85
5,581.05 07/13/00 59.65 57.70
5,580.90 07/18/00 59.80 57.85
5,581.05 07/27/00 59.65 57.70
5,581.06 08/02/00 59.64 57.69
5,581.08 08/09/00 59.62 57.67
5,581.07 08/16/00 59.63 57.68
5,581.25 08/31/00 59.45 57.50
5,581.32 09/08/00 59.38 57.43
5,581.34 09/13/00 59.36 57.41
5,581.41 09/20/00 59.29 57.34
5,581.37 10/05/00 59.33 57.38
5,581.66 11/09/00 59.04 57.09
5,581.63 12/06/00 59.07 57.12
5,581.92 01/03/01 58.78 56.83
5,582.20 02/09/01 58.50 56.55
5,582.54 03/28/01 58.16 56.21
5,582.72 04/30/01 57.98 56.03
5,582.72 05/31/01 57.98 56.03
5,582.81 06/22/01 57.89 55.94
5,582.92 07/10/01 57.78 55.83
5,583.17 08/20/01 57.53 55.58
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 121.85
5,583.28 09/19/01 57.42 55.47
5,583.36 10/02/01 57.34 55.39
5,583.49 11/08/01 57.21 55.26
5,583.84 12/03/01 56.86 54.91
5,583.79 01/03/02 56.91 54.96
5,583.96 02/06/02 56.74 54.79
5,584.39 03/26/02 56.31 54.36
5,584.12 04/09/02 56.58 54.63
5,584.55 05/23/02 56.15 54.20
5,584.42 06/05/02 56.28 54.33
5,583.65 07/08/02 57 .05 55.10
5,584.90 08/23/02 55.80 53.85
5,585.02 09/11/02 55.68 53.73
5,585.20 10/23/02 55.50 53.55
5,585.15 11/22/02 55.55 53.60
5,585.42 12/03/02 55 .28 53.33
5,585.65 01/09/03 55.05 53.10
5,585.65 02/12/03 55.05 53.10
5,585.92 03/26/03 54.78 52.83
5,586.22 04/02/03 54.48 52.53
5,586.01 05/01/03 54.69 52.74
5,584.81 06/09/03 55.89 53.94
5,584.34 07/07/03 56.36 54.41
5,584.40 08/04/03 56.30 54.35
5,583.88 09/11/03 56.82 54.87
5,583.57 10/02/03 57.13 55.18
5,583.39 11/07/03 57.31 55.36
5,583.97 12/03/03 56.73 54.78
5,585.28 01/15/04 55.42 53.47
5,585.50 02/10/04 55.20 53.25
5,585.87 03/28/04 54.83 52.88
5,586.20 04/12/04 54.50 52.55
5,586.45 05/13/04 54.25 52.30
5,586.50 06/18/04 54.20 52.25
5,587.13 07/28/04 53.57 51.62
5,586.22 08/30/04 54.48 52.53
5,585.69 09/16/04 55.01 53.06
5,585.17 10/11/04 55.53 53.58
5,584.64 11/16/04 56.06 54.11
5,584.77 12/22/04 55.93 53.98
5,584.65 01/18/05 56.05 54.10
5,584.98 02/28/05 55.72 53.77
5,585.15 03/15/05 55.55 53.60
5,586.25 04/26/05 54.45 52.50
5,586.79 05/24/05 53.91 51.96
5,586.52 06/30/05 54.18 52.23
Water Levels and Data over Time
White Mesa Mill -Well TW4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.L D) Well
5,638.75 5 640.70 l.95 121.85
5,586.03 07/29/05 54.67 52.72
5,586.05 09/12/05 54.65 52.70
5,585.80 12/07/05 54.90 52.95
5,587.06 03/08/06 53.64 51.69
5,585.90 06/13/06 54.80 52.85
5,585.32 07/18/06 55.38 53.43
5,585.35 11/07/06 55.35 53.40
5585.81 02/27/07 54.89 52.94
5,585.20 05/02/07 55.50 53.55
5,586.66 08/14/07 54.04 52.09
5,586.80 10/10/07 53.90 51.95
5,588.48 03/26/08 52.22 50.27
5,586.51 06/24/08 54.19 52.24
5,586.45 08/26/08 54.25 52.30
5,585.40 10/14/08 55.3 53.35
5,584.80 03/03/09 55.9 53.95
5,584.73 06/24/09 55.97 54.02
5,584.36 09/10/09 56.34 54.39
5,585.02 12/11/09 55 .68 53.73
5,585.66 03/11/10 55.04 53.09
5,584.86 05/11/10 55.84 53.89
5,584.55 09/29/10 56.15 54.20
5,584.17 12/21/10 56.53 54.58
5,583.55 02/28/11 57.15 55.20
5,584.72 06/21/11 55.98 54.03
5,584.62 09/20/11 56.08 54.13
5,585.04 11/21/11 55.66 53.71
5,583.89 03/27/12 56.81 54.86
5,583.92 06/28/12 56.78 54.83
5,583.89 09/27/12 56.81 54.86
5,583.89 12/28/12 56.81 54.86
5,582.88 03/28/13 57.82 55.87
5,582.05 06/27/13 58.65 56.70
5,581.35 09/27/13 59.35 57.40
5,580.52 12/20/13 60.18 58.23
5,579.44 03/27/14 61.26 59.31
5,578.11 06/25/14 62.59 60.64
5,577.15 09/25/14 63.55 61.60
5,577.44 12/17/14 63.26 61.31
5,577.37 03/26/15 63.33 61.38
5,577.46 06/22/15 63.24 61.29
5,576.92 09/30/15 63.78 61.83
5,576.33 12/02/15 64.37 62.42
5,576.30 03/30/16 64.40 62.45
5,575.72 06/30/16 64.98 63.03
5,575.12 09/29/16 65.58 63.63
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 12 1. 5
5,574.77 12/21/16 65.93 63.98
5,575.03 03/30/17 65.67 63.72
5,574.55 06/27/17 66.15 64.20
5,574.09 09/28/17 66.61 64.66
5,573.48 11/30/17 67.22 65.27
5,573.05 03/28/18 67.65 65.70
5572.68 06/22/18 68.02 66.07
5571.89 09/24/18 68.81 66.86
5571.86 12/17/18 68.84 66.89
5571.15 03/25/19 69.55 67.60
5571.26 06/24/19 69.44 67.49
5571.12 08/12/19 69.58 67.63
...J VI ...J 0
Depth Below Measuring Point (ft.)
0\ VI 0\ 0
VI
VI
VI 0
1---------1------+------~1-----1-----+ 01/02/00
05/31/00
10/28/00
03/27/01
08/24/01
01/21/02
06/20/02
11/17/02
04/16/03
09/13/03
02/10/04
07/09/04
12/06/04
05/05/05
10/02/05
03/01/06
07/29/06
12/26/06
05/25/07
10/22/07
03/20/08
08/17/08
01/14/09
06/13/09
11/10/09
04/09/10
09/06/10
02/03/11
07/03/11
11/30/11
-04/28/12
09/25/12
02/22/13
07/22/13
12/19/13
05/18/14
10/15/14
03/14/15
08/11/15
01/08/16
06/06/16
11/03/16
04/02/17
08/30/17
01/27/18
06/26/18
11/23/18
04/22/19
09/19/19
02/16/20
07/15/20
'-------'------------J'--------'-----.J.. 12/12/20
~ ~ ,I;;,,.
I
(I)
~ ;-
"1
t:,
~ ~ ~
0 < ~ "1
~ .... a ~ ,,-..,
?
'a" §"
~ '-'
Water Levels and Data over Time
White Mesa Mill -Well TW 4-6
Total or
Measuring Measured Total Total
Water Land Point Depth to Depth to Depth Of
Elevation Surface Elevation Length Of Date Of Water Water Well
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (bhv.L D
5,607.33 5,608.78 1.450 99.60
5,522.28 05/25/00 86.50 85.05
5,521.51 06/09/00 87.27 85.82
5,522.35 06/16/00 86.43 84.98
5,522.14 06/26/00 86.64 85.19
5,522.25 07/06/00 86.53 85.08
5,522.13 07/13/00 86.65 85.20
5,522.17 07/18/00 86.61 85.16
5,522.26 07/25/00 86.52 85.07
5,522.31 08/02/00 86.47 85.02
5,522.33 08/09/00 86.45 85.00
5,522.35 08/15/00 86.43 84.98
5,522.40 08/31/00 86.38 84.93
5,522.40 09/08/00 86.38 84.93
5,522.45 09/13/00 86.33 84.88
5,522.53 09/20/00 86.25 84.80
5,522.39 10/05/00 86.39 84.94
5,522.42 11/09/00 86.36 84.91
5,522.29 12/06/00 86.49 85.04
5,522.63 01/03/01 86.15 84.70
5,522.72 02/09/01 86.06 84.61
5,522.90 03/26/01 85.88 84.43
5,522.70 04/30/01 86.08 84.63
5,522.89 05/31/01 85.89 84.44
5,522.88 06/20/01 85.90 84.45
5,522.96 07/10/01 85.82 84.37
5,523.10 08/20/01 85.68 84.23
5,523.23 09/19/01 85.55 84.10
5,523.21 10/02/01 85.57 84.12
5,523.25 11/08/01 85.53 84.08
5,523.46 12/03/01 85.32 83.87
5,523.36 01/03/02 85.42 83.97
5,523.50 02/06/02 85.28 83.83
5,523.94 03/26/02 84.84 83.39
5,523.75 04/09/02 85.03 83.58
5,524.23 05/23/02 84.55 83.10
5,523.98 06/05/02 84.80 83.35
5,524.31 07/08/02 84.47 83.02
5,524.36 08/23/02 84.42 82.97
5,524.49 09/11/02 84.29 82.84
5,524.71 10/23/02 84.07 82.62
5,524.60 11/22/02 84.18 82.73
5,524.94 12/03/02 83.84 82.39
5,525.10 01/09/03 83.68 82.23
5,525.15 02/12/03 83.63 82.18
5,525.35 03/26/03 83.43 81.98
5,525.68 04/02/03 83.10 81.65
Water Levels and Data over Time
White Mesa Mill -Well TW 4-6
Total or
Measuring Measured Total Total
Water Land Point Depth to Depth to Depth Of
Elevation Surface Elevation Length Of Date Of Water Water Well
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,607.33 5,608.78 1.450 99.60
5,525.74 05/01/03 83.04 81.59
5,525.98 06/09/03 82.80 81.35
5,526.04 07/07/03 82.74 81.29
5,526.07 08/04/03 82.71 81.26
5,526.42 09/11/03 82.36 80.91
5,526.30 10/02/03 82.48 81.03
5,526.41 11/07/03 82.37 80.92
5,526.46 12/03/03 82.32 80.87
5,526.83 01/15/04 81.95 80.50
5,526.81 02/10/04 81.97 80.52
5,527.14 03/28/04 81.64 80.19
5,527.39 04/12/04 81.39 79.94
5,527.64 05/13/04 81.14 79.69
5,527.70 06/18/04 81.08 79.63
5,528.16 07/28/04 80.62 79.17
5,528.30 08/30/04 80.48 79.03
5,528.52 09/16/04 80.26 78.81
5,528.71 10/11/04 80.07 78.62
5,528.74 11/16/04 80.04 78.59
5,529.20 12/22/04 79.58 78.13
5,528.92 01/18/05 79.86 78.41
5,529.51 02/28/05 79.27 77.82
5,529.74 03/15/05 79.04 77.59
5,529.96 04/26/05 78.82 77.37
5,530.15 05/24/05 78.63 77.18
5,530.35 06/30/05 78.43 76.98
5,530.47 07/29/05 78.31 76.86
5,530.95 09/12/05 77.83 76.38
5,531.50 12/07/05 77.28 75.83
5,532.43 03/08/06 76.35 74.90
5,533.49 06/13/06 75.29 73.84
5,532.58 07/18/06 76.20 74.75
5,532.88 11/07/06 75.90 74.45
5534.09 02/27/07 74.69 73.24
5,534.04 05/02/07 74.74 73.29
5,534.43 08/14/07 74.35 72.90
5,554.54 10/10/07 54.24 52.79
5,535.40 03/26/08 73.38 71.93
5,535.55 06/24/08 73.23 71.78
5,535.90 08/26/08 72.88 71.43
5,535.87 10/14/08 72.91 71.46
5,536.42 03/10/09 72.36 70.91
5,536.71 06/24/09 72.07 70.62
5,536.83 09/10/09 71.95 70.50
5,537.35 12/11/09 71.43 69.98
5,537.93 03/11/10 70.85 69.40
Water Levels and Data over Time
White Mesa Mill -Well TW 4-6
Total or
Measuring Measured Total Total
Water Land Point Depth to Depth to Depth Of
Elevation Surface Elevation Length Of Date Of Water Water Well
(z) (LSD) (MP Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,607.33 5,608.78 1.450 99.60
5,538.14 05/11/10 70.64 69.19
5,538.03 09/29/10 70.75 69.30
5,538.04 12/21/10 70.74 69.29
5,537.98 02/28/11 70.8 69.35
5,538.46 06/21/11 70.32 68.87
5,538.37 09/20/11 70.41 68.96
5,538.87 12/21/11 69.91 68.46
5,538.73 03/27/12 70.05 68.60
5,538.80 06/28/12 69.98 68.53
5,539.04 09/27/12 69.74 68.29
5,538.74 12/28/12 70.04 68.59
5,539.53 03/28/13 69.25 67.80
5,539.46 06/27/13 69.32 67.87
5,539.62 09/27/13 69.16 67.71
5,539.85 12/20/13 68.93 67.48
5,539.65 03/27/14 69.13 67.68
5,538.85 06/25/14 69.93 68.48
5,538.69 09/25/14 70.09 68.64
5,538.71 12/17/14 70.07 68.62
5,538.03 03/26/15 70.75 69.30
5,537.78 06/22/15 71.00 69.55
5,537.40 09/30/15 71.38 69.93
5,537.44 12/02/15 71.34 69.89
5,536.76 03/30/16 72.02 70.57
5,536.08 06/30/16 72.70 71.25
5,535.54 09/29/16 73.24 71.79
5,535.38 12/21/16 73.40 71.95
5,535.48 03/30/17 73.30 71.85
5,535.13 06/27/17 73.65 72.20
5,534.78 09/28/17 74.00 72.55
5,534.54 11/30/17 74.24 72.79
5,534.38 03/28/18 74.40 72.95
5,533.92 06/22/18 74.86 73.41
5,533.49 09/25/18 75.29 73.84
5,533.17 12/17/18 75.61 74.16
5,532.63 03/25/19 76.15 74.70
5,532.56 06/24/19 76.22 74.77
5,532.28 08/12/19 76.50 75.05
\0 0 00
V,
00 0
Depth Below Measuring Point (ft.)
-.J V, -.J 0 0\ V, ~ V, V,
V, 0
05/25/00
10/22/00
03/21/01
08/18/01
01/15/02
06/14/02
11/11/02
04/10/03
09/07/03
02/04/04
07/03/04
11/30/04
04/29/05
09/26/05 ~ 02/23/06 ~ 07/23/06 "'"' 12/20/06 I ="' 05/19/07 ~ 10/16/07
03/14/08 """" (0
08/11/08 ""1
01/08/09 ~ (0
06/07/09 "Cl
"""" 11/04/09 =-
04/03/10 0
08/31/10 < (0
01/28/11 ""1
06/27/11 ~ ...
11/24/11 e
04/22/12
(0 --09/19/12 ?
02/16/13 -a-
07/16/13 -e
12/13/13 "Cl '-' 05/12/14
10/09/14
03/08/15
08/05/15
01/02/16
05/31/16
10/28/16
03/27/17
08/24/17
01/21/18
06/20/18
11/17/18
04/16/19
09/13/19
02/10/20
07/09/20
12/06/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,552.37 11/29/99 68.70 67.50
5,553.57 01/02/00 67.50 66.30
5,553.87 01/10/00 67.20 66.00
5,553.72 01/17/00 67.35 66.15
5,553.97 01/24/00 67.10 65.90
5,553.87 02/01/00 67.20 66.00
5,553.87 02/07/00 67.20 66.00
5,554.17 02/14/00 66.90 65.70
5,554.27 02/23/00 66.80 65.60
5,554.37 03/01/00 66.70 65.50
5,554.37 03/08/00 66.70 65.50
5,554.27 03/15/00 66.80 65.60
5,554.77 03/20/00 66.30 65.10
5,554.57 03/29/00 66.50 65.30
5,554.27 04/04/00 66.80 65.60
5,554.57 04/13/00 66.50 65.30
5,554.77 04/21/00 66.30 65.10
5,554.87 04/28/00 66.20 65.00
5,554.87 05/01/00 66.20 65.00
5,555.27 05/11/00 65.80 64.60
5,554.97 05/15/00 66.10 64.90
5,555.27 05/25/00 65.80 64.60
5,555 .33 06/09/00 65.74 64.54
5,555.45 06/16/00 65.62 64.42
5,555.22 06/26/00 65.85 64.65
5,555.45 07/06/00 65.62 64.42
5,555.40 07/13/00 65.67 64.47
5,555.45 07/18/00 65.62 64.42
5,555.59 07/27/00 65.48 64.28
5,555.65 08/02/00 65.42 64.22
5,555.70 08/09/00 65.37 64.17
5,555.74 08/16/00 65.33 64.13
5,555 .96 08/31/00 65.11 63.91
5,555.87 09/08/00 65.20 64.00
5,555.95 09/13/00 65.12 63.92
5,556.05 09/20/00 65.02 63.82
5,556.06 10/05/00 65.01 63.81
5,556.17 10/12/00 64.90 63.70
5,556.20 10/19/00 64.87 63.67
5,556.22 10/23/00 64.85 63.65
5,556.36 11/09/00 64.71 63.51
5,556.42 11/14/00 64.65 63.45
5,556.45 11/30/00 64.62 63.42
5,556.15 12/06/00 64.92 63.72
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,556.89 01/14/01 64.18 62.98
5,557.07 02/09/01 64.00 62.80
5,557.62 03/29/01 63.45 62.25
5,557.51 04/30/01 63.56 62.36
5,557.77 05/31/01 63.30 62.10
5,557.84 06/21/01 63.23 62.03
5,557.98 07/10/01 63.09 61.89
5,558.33 08/20/01 62.74 61.54
5,558.57 09/19/01 62.50 61.30
5,558.53 10/02/01 62.54 61.34
5,558.62 11/08/01 62.45 61.25
5,559.03 12/03/01 62.04 60.84
5,559.08 01/03/02 61.99 60.79
5,559.32 02/06/02 61.75 60.55
5,559.63 03/26/02 61.44 60.24
5,559.55 04/09/02 61.52 60.32
5,560.06 05/23/02 61.01 59.81
5,559.91 06/05/02 61.16 59.96
5,560.09 07/08/02 60.98 59.78
5,560.01 08/23/02 61.06 59.86
5,560.23 09/11/02 60.84 59.64
5,560.43 10/23/02 60.64 59.44
5,560.39 11/22/02 60.68 59.48
5,560.61 12/03/02 60.46 59.26
5,560.89 01/09/03 60.18 58.98
5,560.94 02/12/03 60.13 58.93
5,561.28 03/26/03 59.79 58.59
5,561.35 04/02/03 59.72 58.52
5,546.20 05/01/03 74.87 73.67
5,539.47 06/09/03 81.60 80.40
5,541.87 07/07/03 79.20 78.00
5,542.12 08/04/03 78.95 77.75
5,541.91 09/11/03 79.16 77.96
5,544.62 10/02/03 76.45 75.25
5,542.67 11/07/03 78.40 77.20
5,549.96 12/03/03 71.11 69.91
5,557.17 01/15/04 63.90 62.70
5,558.65 02/10/04 62.42 61.22
5,559.90 03/28/04 61.17 59.97
5,560.36 04/12/04 60.71 59.51
5,560.87 05/13/04 60.20 59.00
5,560.95 06/18/04 60.12 58.92
5,561.64 07/28/04 59.43 58.23
5,543.00 08/30/04 78.07 76.87
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,541.91 09/16/04 79.16 77.96
5,540.08 10/11/04 80.99 79.79
5,546.92 11/16/04 74.15 72.95
5,546.97 12/22/04 74.10 72.90
5,546.51 01/18/05 74.56 73.36
5,546.66 02/28/05 74.41 73.21
5,546.81 03/15/05 74.26 73.06
5,548.19 04/26/05 72.88 71.68
5,547.11 05/24/05 73.96 72.76
5,546.98 06/30/05 74.09 72.89
5,546.92 07/29/05 74.15 72.95
5,547.26 09/12/05 73.81 72.61
5,547.26 12/07/05 73.81 72.61
5,548.86 03/08/06 72.21 71.01
5,548.62 06/13/06 72.45 71.25
5,550.04 07/18/06 71.03 69.83
5,548.32 11/07 /06 72.75 71.55
5,550.44 02/27/07 70.63 69.43
5,549.69 05/02/07 71.38 70.18
5,549.97 08/14/07 71.10 69.90
5,550.30 10/10/07 70.77 69.57
5,551.92 03/26/08 69.15 67.95
5,552.94 06/24/08 68.13 66.93
5,552.34 08/26/08 68.73 67.53
5,552.61 10/14/08 68.46 67.26
5,552.81 03/10/09 68.26 67.06
5,553.11 06/24/09 67.96 66.76
5,552.55 09/10/09 68.52 67.32
5,553.06 12/11/09 68.01 66.81
5,554.64 03/11/10 66.43 65.23
5,554.20 05/11/10 66.87 65.67
5,553.45 09/29/10 67.62 66.42
5,553.40 12/21/10 67.67 66.47
5,553.93 02/28/11 67.14 65.94
5,553.67 06/21/11 67.4 66.20
5,553.46 09/20/11 67.61 66.41
5,553.78 12/21/11 67.29 66.09
5,553.17 03/27/12 67.90 66.70
5,553.21 06/28/12 67.86 66.66
5,552.90 09/27/12 68.17 66.97
5,553.15 12/28/12 67.92 66.72
5,556.23 03/28/13 64.84 63.64
5,556.04 06/27/13 65.03 63.83
5,556.09 09/27/13 64.98 63.78
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,555.80 12/20/13 65.27 64.07
5,555.40 03/27/14 65.67 64.47
5,554.20 06/25/14 66.87 65.67
5,552.96 09/25/14 68.11 66.91
5,552.62 12/17/14 68.45 67.25
5,548.57 03/26/15 72.50 71.30
5,555.88 06/22/15 65.19 63.99
5,546.22 09/30/15 74.85 73.65
5,539.47 12/02/15 81.60 80.40
5,545.08 03/30/16 75.99 74.79
5,544.62 06/30/16 76.45 75.25
5,544.61 09/29/16 76.46 75.26
5,544.09 12/21/16 76.98 75.78
5,546.07 03/30/17 75.00 73.80
5,549.36 06/27/17 71.71 70.51
5,541.91 09/28/17 79.16 77.96
5,540.51 11/30/17 80.56 79.36
5,540.71 03/28/18 80.36 79.16
5,540.12 06/22/18 80.95 79.75
5,540.17 09/25/18 80.90 79.70
5,538.26 12/17/18 82.81 81.61
5,538.81 03/25/19 82.26 81.06
5,539.11 06/24/19 81.96 80.76
5,539.75 08/12/19 81.32 80.12
00 VI 00 0
Depth Below Measuring Point (ft.)
-.J VI -.J 0 0\ VI 0\ 0 VI VI VI 0
11/29/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04
11/02/04
04/01/05
08/29/05 ~
01/26/06 ~
06/25/06 ,I:... I
11/22/06 '1
04/21/07 ~ 09/18/07 -02/15/08 ~ '"1
07/14/08 0
-12/11/08 ~ "CS 05/10/09 ~ 10/07/09 0 03/06/10 < 08/03/10 ~ '"1 12/31/10 ~
05/30/11 .... 9 10/27/11 ~
03/25/12 --08/22/12 ?
01/19/13 O"" -06/18/13 9
11/15/13 "CS --04/14/14
09/11/14
02/08/15
07/08/15
12/05/15
05/03/16
09/30/16
02/27/17
07/27/17
12/24/17
05/23/18
10/20/18
03/19/19
08/16/19
01/13/20
06/11/20
11/08/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-8
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,616.80 5,621.40 4.60 126.2
5,546.40 11/29/99 75.00 70.40
5,546.20 01/02/00 75.20 70.60
5,546.50 01/10/00 74.90 70.30
5,546.30 01/17/00 75.10 70.50
5,546.60 01/24/00 74.80 70.20
5,546.50 02/01/00 74.90 70.30
5,546.50 02/07/00 74.90 70.30
5,546.90 02/14/00 74.50 69.90
5,546.95 02/23/00 74.45 69.85
5,547.05 03/01/00 74.35 69.75
5,547.05 03/08/00 74.35 69.75
5,547.10 03/15/00 74.30 69.70
5,547.50 03/20/00 73.90 69.30
5,547.40 03/29/00 74.00 69.40
5,547.20 04/04/00 74.20 69.60
5,547.40 04/13/00 74.00 69.40
5,547.60 04/21/00 73.80 69.20
5,547.70 04/28/00 73.70 69.10
5,547.70 05/01/00 73.70 69.10
5,548.00 05/11/00 73.40 68.80
5,547.70 05/15/00 73.70 69.10
5,547.90 05/25/00 73.50 68.90
5,547.90 06/09/00 73.50 68.90
5,548.00 06/16/00 73.40 68.80
5,547.87 06/26/00 73.53 68.93
5,547.95 07/06/00 73.45 68.85
5,547.96 07/13/00 73.44 68.84
5,547.95 07/18/00 73.45 68.85
5,548.11 07/27/00 73.29 68.69
5,548.15 08/02/00 73.25 68.65
5,548.17 08/09/00 73.23 68.63
5,548.16 08/15/00 73.24 68.64
5,548.40 08/31/00 73.00 68.40
5,548.50 09/08/00 72.90 68.30
5,548.62 09/13/00 72.78 68.18
5,548.75 09/20/00 72.65 68.05
5,548.76 10/05/00 72.64 68.04
Water Levels and Data over Time
White Mesa Mill -Well TW4-8
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,616.80 5,621.40 4.60 126.2
5,549.00 11/09/00 72.40 67.80
5,548.85 12/06/00 72.55 67.95
5,549.47 01/03/01 71.93 67.33
5,549.89 02/09/01 71.51 66.91
5,550.37 03/27/01 71.03 66.43
5,550.50 04/30/01 70.90 66.30
5,550.68 05/31/01 70.72 66.12
5,550.68 06/20/01 70.72 66.12
5,551.02 07/10/01 70.38 65.78
5,551.32 08/20/01 70.08 65.48
5,551.49 09/19/01 69.91 65.31
5,551.64 10/02/01 69.76 65.16
5,551.81 11/08/01 69.59 64.99
5,552.22 12/03/01 69.18 64.58
5,552.16 01/03/02 69.24 64.64
5,552.38 02/06/02 69.02 64.42
5,552.85 03/26/02 68.55 63.95
5,552.83 04/09/02 68.57 63.97
5,553.20 05/23/02 68.20 63.60
5,553.16 06/05/02 68.24 63.64
5,553.32 07/08/02 68.08 63.48
5,553.49 08/23/02 67.91 63.31
5,553.69 09/11/02 67.71 63.l 1
5,554.09 10/23/02 67.31 62.71
5,554.02 11/22/02 67.38 62.78
5,554.23 12/03/02 67 .17 62.57
5,554.43 01/09/03 66.97 62.37
5,554.42 02/12/03 66.98 62.38
5,554.71 03/26/03 66.69 62.09
5,554.83 04/02/03 66.57 61.97
5,552.21 05/01/03 69.19 64.59
5,547.93 06/09/03 73.47 68.87
5,546.97 07/07/03 74.43 69.83
5,546.58 08/04/03 74.82 70.22
5,546.24 09/11/03 75.16 70.56
5,546.38 10/02/03 75.02 70.42
5,546.40 11/07/03 75.00 70.40
Water Levels and Data over Time
White Mesa Mill -Well TW4-8
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,616.80 5,621.40 4.60 126.2
5,546.59 12/03/03 74.81 70.21
5,551.29 01/15/04 70.11 65.51
5,552.69 02/10/04 68.71 64.11
5,554.06 03/28/04 67.34 62.74
5,554.52 04/12/04 66.88 62.28
5,555.06 05/13/04 66.34 61.74
5,555.11 06/18/04 66.29 61.69
5,555.88 07/28/04 65.52 60.92
5,552.97 08/30/04 68.43 63.83
5,550.65 09/16/04 70.75 66.15
5,548.40 10/11/04 73.00 68.40
5,548.28 11/16/04 73.12 68.52
5,548.80 12/22/04 72.60 68.00
5,548.43 01/18/05 72.97 68.37
5,548.61 02/28/05 72.79 68.19
5,548.64 03/15/05 72.76 68.16
5,548.65 04/26/05 72.75 68.15
5,548.85 05/24/05 72.55 67.95
5,548.73 06/30/05 72.67 68.07
5,548.62 07/29/05 72.78 68.18
5,548.80 09/12/05 72.60 68.00
5,548.71 12/07/05 72.69 68.09
5,549.72 03/08/06 71.68 67.08
5,549.70 06/13/06 71 .70 67.10
5,549.70 07/18/06 71.70 67.10
5,549.65 11/07/06 71.75 67.15
5,551.11 02/27/07 70.29 65.69
5,550.20 05/02/07 71.20 66.60
5,550.59 08/14/07 70.81 66.21
5,550.76 10/10/07 70.64 66.04
5,551.95 03/26/08 69.45 64.85
5,552.36 06/24/08 69.04 64.44
5,552.50 08/26/08 68.90 64.30
5,552.56 10/14/08 68.84 64.24
5,552.91 03/03/09 68.49 63.89
5,553.27 06/24/09 68.13 63.53
5,553.12 09/10/09 68.28 63.68
Water Levels and Data over Time
White Mesa Mill -Well TW4-8
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,616.80 5,621.40 4.60 126.2
5,553.63 12/11/09 67.77 63.17
5,554.65 03/11/10 66.75 62.15
5,554.57 05/11/10 66.83 62.23
5,554.34 09/29/10 67.06 62.46
5,554.09 12/21/10 67.31 62.71
5,554.50 02/28/11 66.9 62.30
5,554.79 06/21/11 66.61 62.01
5,554.63 09/20/11 66.77 62.17
5,555.01 12/21/11 66.39 61.79
5,554.85 03/27/12 66.55 61.95
5,554.90 06/28/12 66.5 61.90
5,554.85 09/27/12 66.55 61.95
5,554.86 12/28/12 66.54 61.94
5,556.48 03/28/13 64.92 60.32
5,556.35 06/27/13 65.05 60.45
5,556.60 09/27/13 64.80 60.20
5,556.56 12/20/13 64.84 60.24
5,556.38 03/27/14 65.02 60.42
5,555.56 06/25/14 65.84 61.24
5,554.82 09/25/14 66.58 61.98
5,554.95 12/17/14 66.45 61.85
5,546.89 03/26/15 74.51 69.91
5,547.80 06/22/15 73.60 69.00
5,544.84 09/30/15 76.56 71.96
5,540.22 12/02/15 81.18 76.58
5,542.00 03/30/16 79.40 74.80
5,542.10 06/30/16 79.30 74.70
5,541.70 09/29/16 79.70 75.10
5,539.90 12/21/16 81.50 76.90
5,541.70 03/30/17 79.70 75.10
5,542.19 06/27/17 79.21 74.61
5,540.58 09/28/17 80.82 76.22
5,538.52 11/30/17 82.88 78.28
5,537.95 03/28/18 83.45 78.85
5,537.73 06/22/18 83.67 79.07
5,537.38 09/25/18 84.02 79.42
5,536.86 12/17/18 84.54 79.94
Water Land
Elevation Surface
(WL) (LSD)
5,616.80
5,536.30
5,536.67
5,536.82
Water Levels and Data over Time
White Mesa Mill -Well TW4-8
Total or
Measuring Measured
Point Depth to
Elevation Length Of Date Of Water
(MP) Riser (L) Monitoring (blw.MP)
5,621.40 4.60
03/25/19 85.10
06/24/19 84.73
08/12/19 84.58
Total Depth Total
to Water Depth Of
(blw.LSD) Well
126.2
80.50
80.13
79.98
\0 0 00 0 -..J 0
Depth Below Measuring Point (ft.)
0\ 0 Ul 0 ~ 0
u.)
0 N 0
.....
0 0
11/29/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04
11/02/04
04/01/05
08/29/05 ~
01/26/06 ~
06/25/06 """ I
11/22/06 00
04/21/07 ~ 09/18/07 '""" 02/15/08 ~ "1
07/14/08 ~
12/11/08 ~ "Cl 05/10/09 ~ 10/07/09 0 03/06/10 ~
08/03/10 ~ "1 12/31/10 ~
05/30/11 .... a 10/27/11 ~
03/25/12 -08/22/12 ?
01/19/13 a' -06/18/13 a
11/15/13 "Cl .._,
04/14/14
09/11/14
02/08/15
07/08/15
12/05/15
05/03/16
09/30/16
02/27/17
07/27/17
12/24/17
05/23/18
10/20/18
03/19/19
08/16/19
01/13/20
06/11/20
11/08/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.1
5,577.09 12/20/99 60.50 59.02
5,577.09 01/02/00 60.50 59.02
5,577.29 01/10/00 60.30 58.82
5,577.09 01/17/00 60.50 59.02
5,577.39 01/24/00 60.20 58.72
5,577.29 02/01/00 60.30 58.82
5,577.19 02/07/00 60.40 58.92
5,577.69 02/14/00 59.90 58.42
5,577.69 02/23/00 59.90 58.42
5,577.79 03/01/00 59.80 58.32
5,577.79 03/08/00 59.80 58.32
5,577.89 03/15/00 59.70 58.22
5,568.49 03/20/00 69.10 67 .62
5,578.14 03/29/00 59.45 57.97
5,577.84 04/04/00 59.75 58.27
5,578.04 04/13/00 59.55 58.07
5,578.24 04/21/00 59.35 57.87
5,578.39 04/28/00 59.20 57.72
5,578.39 05/01/00 59.20 57.72
5,578.79 05/11/00 58.80 57.32
5,578.39 05/15/00 59.20 57.72
5,578.79 05/25/00 58.80 57.32
5,578.81 06/09/00 58.78 57.30
5,578.89 06/16/00 58.70 57 .22
5,578.74 06/26/00 58.85 57.37
5,578.86 07/06/00 58.73 57.25
5,578.87 07/13/00 58.72 57.24
5,578.84 07/18/00 58.75 57.27
5,579.03 07/27/00 58.56 57.08
5,579.03 08/02/00 58.56 57.08
5,579.05 08/09/00 58.54 57.06
5,579.04 08/15/00 58.55 57.07
5,579.25 08/31/00 58.34 56.86
5,579.35 09/08/00 58.24 56.76
5,579.40 09/13/00 58.19 56.71
5,579.46 09/20/00 58.13 56.65
5,579.44 10/05/00 58.15 56.67
5,579.79 11/09/00 57.80 56.32
5,579.73 12/06/00 57.86 56.38
5,580.01 01/03/01 57.58 56.10
5,580.30 02/09/01 57.29 55.81
5,580.66 03/27/01 56.93 55.45
5,580.75 04/30/01 56.84 55.36
Water Levels and Data over Time
White Mesa Mill -Well TW 4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.1
5,581.04 05/31/01 56.55 55.07
5,581.12 06/21/01 56.47 54.99
5,581.15 07/10/01 56.44 54.96
5,581.51 08/20/01 56.08 54.60
5,581.70 09/19/01 55.89 54.41
5,581.61 10/02/01 55.98 54.50
5,581.83 11/08/01 55.76 54.28
5,582.17 12/03/01 55.42 53.94
5,582.21 01/03/02 55.38 53.90
5,582.57 02/06/02 55.02 53.54
5,583.12 03/26/02 54.47 52.99
5,582.77 04/09/02 54.82 53.34
5,583.21 05/23/02 54.38 52.90
5,582.94 06/05/02 54.65 53.17
5,582.71 07/08/02 54.88 53.40
5,583.67 08/23/02 53.92 52.44
5,583.82 09/11/02 53.77 52.29
5,584.01 10/23/02 53.58 52.10
5,583.88 11/22/02 53.71 52.23
5,583.81 12/03/02 53.78 52.30
5,584.28 01/09/03 53.31 51.83
5,584.41 02/12/03 53.18 51.70
5,584.68 03/26/03 52.91 51.43
5,584.49 04/02/03 53.10 51.62
5,584.51 05/01/03 53.08 51.60
5,583.59 06/09/03 54.00 52.52
5,582.96 07/07/03 54.63 53.15
5,582.98 08/04/03 54.61 53.13
5,582.57 09/11/03 55.02 53.54
5,582.25 10/02/03 55.34 53.86
5,582.09 11/07/03 55.50 54.02
5,582.48 12/03/03 55.11 53.63
5,583.69 01/15/04 53.90 52.42
5,583.89 02/10/04 53.70 52.22
5,584.30 03/28/04 53.29 51.81
5,584.59 04/12/04 53.00 51.52
5,584.87 05/13/04 52.72 51.24
5,584.96 06/18/04 52.63 51.15
5,585.50 07/28/04 52.09 50.61
5,584.81 08/30/04 52.78 51.30
5,584.40 09/16/04 53.19 51.71
5,583.91 10/11/04 53.68 52.20
5,583.39 11/16/04 54.20 52.72
Water Levels and Data over Time
White Mesa Mill -Well TW 4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (L D) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.1
5,583.54 12/22/04 54.05 52.57
5,583.34 01/18/05 54.25 52.77
5,583.66 02/28/05 53.93 52.45
5,583.87 03/15/05 53.72 52.24
5,584.74 04/26/05 52.85 51.37
5,585.26 05/24/05 52.33 50.85
5,585.06 06/30/05 52.53 51.05
5,584.67 07/29/05 52.92 51.44
5,584.75 09/12/05 52.84 51.36
5,584.51 12/07/05 53.08 51.60
5,585.74 03/08/06 51.85 50.37
5,584.74 06/13/06 52.85 51.37
5,584.26 07/18/06 53.33 51.85
5,584.21 11/07/06 53.38 51.90
5,584.67 02/27/07 52.92 51.44
5,584.06 05/02/07 53.53 52.05
5,585.33 08/14/07 52.26 50.78
5,585.42 10/10/07 52.17 50.69
5,587.01 03/26/08 50.58 49.10
5,585.44 06/24/08 52.15 50.67
5,585.23 08/26/08 52.36 50.88
5,584.42 10/14/08 53.17 51.69
5,583.59 03/03/09 54.00 52.52
5,583.35 06/24/09 54.24 52.76
5,582.91 09/10/09 54.68 53.20
5,583.43 12/11/09 54.16 52.68
5,584.00 03/11/10 53.59 52.11
5,583.27 05/11/10 54.32 52.84
5,582.92 09/29/10 54.67 53.19
5,583.08 12/21/10 54.51 53.03
5,582.63 02/28/11 54.96 53.48
5,583.62 06/21/11 53.97 52.49
5,583.52 09/20/11 54.07 52.59
5,583.91 12/21/11 53.68 52.20
5,582.84 03/27/12 54.75 53.27
5,582.84 06/28/12 54.75 53.27
5,582.92 09/27/12 54.67 53.19
5,582.84 12/28/12 54.75 53.27
5,581.97 03/28/13 55.62 54.14
5,581.19 06/27/13 56.40 54.92
5,580.50 09/27/13 57.09 55.61
5,579.73 12/20/13 57.86 56.38
5,578.61 03/27/14 58.98 57.50
Water Levels and Data over Time
White Mesa Mill-Well TW4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.l
5,577.24 06/25/14 60.35 58.87
5,576.24 09/25/14 61.35 59.87
5,576.44 12/17/14 61.15 59.67
5,576.35 03/26/15 61.24 59.76
5,576.48 06/22/15 61.11 59.63
5,575.98 09/30/15 61.61 60.13
5,575.41 12/02/15 62.18 60.70
5,575.38 03/30/16 62.21 60.73
5,574.74 06/30/16 62.85 61.37
5,574.26 09/29/16 63.33 61.85
5,573.88 12/21/16 63.71 62.23
5,573.99 03/30/17 63.60 62.12
5,573.49 06/27/17 64.10 62.62
5,573.05 09/28/17 64 .54 63.06
5,572.34 11/30/17 65.25 63.77
5,574.97 03/28/18 62.62 61.14
5571.69 06/22/18 65.90 64.42
5571.20 09/25/18 66.39 64.91
5570.92 12/17 /18 66.67 65.19
5570.16 03/25/19 67.43 65.95
5570.17 06/24/19 67.42 65.94
5570.01 08/12/19 67.58 66.10
-..J 0 O'I 00 O'I O'I
Depth Below Measuring Point (ft.)
'.l: O'I N O'I 0 Vl 00 Vl O'I Vl .j::,. Vl N Vl 0
12/20/99
05/18/00
10/15/00
03/14/01
08/11/01
01/08/02
06/07/02
11/04/02
04/03/03
08/31/03
01/28/04
06/26/04
11/23/04
04/22/05
09/19/05 ~
02/16/06 ~ 07/16/06 ,l;;I,..
12/13/06 I \0
05/12/07 ~ 10/09/07 -03/07/08 ~ "1 08/04/08 I:, 01/01/09 ~
05/31/09 "C -10/28/09 =r"
03/27/10 0 < 08/24/10 ~
01/21/11 "1
~ 06/20/11 ...
11/17/11 e ~ 04/15/12 --09/12/12 ?
02/09/13 a" -07/09/13 e 12/06/13 "C '-' 05/05/14
10/02/14
03/01/15
07/29/15
12/26/15
05/24/16
10/21/16
03/20/17
08/17/17
01/14/18
06/13/18
11/10/18
04/09/19
09/06/19
02/03/20
07/02/20
11/29/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5 631.99 5,634.24 2.25 113.2
5,576.75 01/03/02 57.49 55.24
5,576.92 02/06/02 57.32 55.07
5,577.43 03/26/02 56.81 54.56
5,577.22 04/09/02 57.02 54.77
5,577.80 05/23/02 56.44 54.19
5,577.47 06/05/02 56.77 54.52
5,577.55 07/08/02 56.69 54.44
5,578.10 08/23/02 56.14 53.89
5,578.24 09/11/02 56.00 53.75
5,578.49 10/23/02 55.75 53.50
5,578.43 11/22/02 55.81 53.56
5,578.43 12/03/02 55.81 53.56
5,578.66 01/09/03 55.58 53.33
5,578.66 02/12/03 55.58 53.33
5,578.78 03/26/03 55.46 53.21
5,578.90 04/02/03 55.34 53.09
5,578.83 05/01/03 55.41 53.16
5,578.05 06/09/03 56.19 53.94
5,577.38 07/07/03 56.86 54.61
5,577.15 08/04/03 57.09 54.84
5,576.76 09/11/03 57.48 55.23
5,576.36 10/02/03 57.88 55.63
5,576.05 11/07/03 58.19 55.94
5,576.20 12/03/03 58.04 55.79
5,577.43 01/15/04 56.81 54.56
5,577.81 02/10/04 56.43 54.18
5,578.47 03/28/04 55.77 53.52
5,578.69 04/12/04 55.55 53.30
5,578.93 05/13/04 55.31 53.06
5,578.99 06/18/04 55.25 53.00
5,579.18 07/28/04 55.06 52.81
5,579.06 08/30/04 55.18 52.93
5,578.78 09/16/04 55.46 53.21
5,577.80 10/11/04 56.44 54.19
5,577.13 11/16/04 57.11 54.86
5,576.96 12/22/04 57.28 55.03
5,576.63 01/18/05 57.61 55.36
5,576.82 02/28/05 57.42 55.17
5,576.86 03/15/05 57.38 55.13
5,577.52 04/26/05 56.72 54.47
5,578.01 05/24/05 56.23 53.98
5,578.15 06/30/05 56.09 53.84
5,577.90 07/29/05 56.34 54.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5,631.99 5,634.24 2.25 113.2
5,578.02 09/12/05 56.22 53.97
5,577.56 12/07/05 56.68 54.43
5,579.69 03/08/06 54.55 52.30
5,578.34 06/13/06 55.90 53.65
5,577.94 07/18/06 56.30 54.05
5,578.01 11/07/06 56.23 53.98
5578.43 02/27/07 55.81 53.56
5,577.84 05/02/07 56.40 54.15
5,578.74 08/14/07 55.50 53.25
5,579.04 10/10/07 55.20 52.95
5,580.69 03/26/08 53.55 51.30
5,579.87 06/24/08 54.37 52.12
5,579.47 08/26/08 54.77 52.52
5,578.87 10/14/08 55.37 53.12
5,578.01 03/10/09 56.23 53.98
5,577.85 06/24/09 56.39 54.14
5,577.49 09/10/09 56.75 54.50
5,577.98 12/11/09 56.26 54.01
5,578.38 03/11/10 55.86 53.61
5,578.16 05/11/10 56.08 53.83
5,577.85 09/29/10 56.39 54.14
5,577.28 12/21/10 56.96 54.71
5,577.14 02/28/11 57.10 54.85
5,578.09 06/21/11 56.15 53.90
5,578.24 09/20/11 56.00 53.75
5,578.74 12/21/11 55.50 53.25
5,577.89 03/27/12 56.35 54.10
5,577.90 06/28/12 56.34 54.09
5,578.29 09/27/12 55.95 53.70
5,577.87 12/28/12 56.37 54.12
5,577.92 03/28/13 56.32 54.07
5,577.19 06/27/13 57.05 54.80
5,576.77 09/27/13 57.47 55.22
5,576.22 12/20/13 58.02 55.77
5,575.36 03/27/14 58.88 56.63
5,574.11 06/25/14 60.13 57.88
5,573.19 09/25/14 61.05 58.80
5,573.19 12/17/14 61.05 58.80
5,573.12 03/26/15 61.12 58.87
5,573.33 06/22/15 60.91 58.66
5,572.98 09/30/15 61.26 59.01
5,572.39 12/02/15 61.85 59.60
5,572.64 03/30/16 61.60 59.35
Water Levels and Data over Time
White Mesa Mill -Well TW 4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5,631.99 5,634.24 2.25 113.2
5,571.79 06/30/16 62.45 60.20
5,571.27 09/29/16 62.97 60.72
5,570.94 12/21/16 63.3 61.05
5,571.09 03/30/17 63.15 60.90
5,570.59 06/27/17 63.65 61.40
5,570.12 09/28/17 64.12 61.87
5,569.42 11/30/17 64.82 62.57
5,569.06 03/28/18 65.18 62.93
5568.81 06/22/18 65.43 63.18
5568.33 09/25/18 65.91 63.66
5568.08 12/17/18 66.16 63.91
5567.33 03/25/19 66.91 64.66
5567.39 06/24/19 66.85 64.60
5567.21 08/12/19 67.03 64.78
00 0 -:i 0 °' 0
Depth Below Measuring Point (ft.)
u-,
0 +'" 0
\;.)
0 N 0
_.
0 0
01/03/02
06/02/02
10/30/02
03/29/03
08/26/03
01/23/04
06/21/04
11/18/04
04/17/05
09/14/05
02/11/06
07/11/06
12/08/06 1-3 05/07/07 ~ 10/04/07 ,I::..
I
03/02/08 ~ 0
07/30/08 ~ 12/27/08
05/26/09 """ ~ "1 10/23/09 0 03/22/10 ~ ~ 08/19/10 ;.
01/16/11 0 06/15/11 <
11/12/11 ~ "1
04/10/12 1-3 ....
09/07/12 a
02/04/13 ~ ,-.._
07/04/13 ?
12/01/13 a' -04/30/14 a
09/27/14 ~ --02/24/15
07/24/15
12/21/15
05/19/16
10/16/16
03/15/17
08/12/17
01/09/18
06/08/18
11/05/18
04/04/19
09/01/19
01/29/20
06/27/20
11/24/20
Water Levels and Data over Time
White Mesa Mill · Well TW 4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitorin; (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 102.4
5,548.32 01/03/02 75.30 73.60
5,548.73 02/06/02 74.89 73.19
5,549.03 03/26/02 74.59 72.89
5,548.84 04/09/02 74.78 73.08
5,549.30 05/23/02 74.32 72.62
5,549.01 06/05/02 74.61 72.91
5,549.22 07/08/02 74.40 72.70
5,549.44 08/23/02 74.18 72.48
5,549.57 09/11/02 74.05 72.35
5,549.64 10/23/02 73.98 72.28
5,549.58 11/22/02 74.04 72.34
5,549.62 12/03/02 74.00 72.30
5,549.85 01/09/03 73.77 72.07
5,549.91 02/12/03 73.71 72.01
5,550.15 03/26/03 73.47 71.77
5,550.01 04/02/03 73.61 71.91
5,550.31 05/01/03 73.31 71.61
5,550.44 06/09/03 73.18 71.48
5,550.33 07/07/03 73.29 71.59
5,550.35 08/04/03 73.27 71.57
5,550.44 09/11/03 73.18 71.48
5,550.47 10/02/03 73.15 71.45
5,550.60 11/07/03 73.02 71.32
5,550.60 12/03/03 73.02 71.32
5,550.94 01/15/04 72.68 70.98
5,551.00 02/10/04 72.62 70.92
5,550.34 03/28/04 73.28 71.58
5,551.54 04/12/04 72.08 70.38
5,551.89 05/13/04 71.73 70.03
5,551.94 06/18/04 71.68 69.98
5,552.49 07/28/04 71.13 69.43
5,552.74 08/30/04 70.88 69.18
5,553.01 09/16/04 70.61 68.91
5,553.11 10/11/04 70.51 68.81
5,553.19 11/16/04 70.43 68.73
5,553.53 12/22/04 70.09 68.39
5,553.31 01/18/05 70.31 68.61
5,553.84 02/28/05 69.78 68.08
5,554.04 03/15/05 69.58 67.88
5,554.23 04/26/05 69.39 67.69
5,553.87 05/24/05 69.75 68.05
5,554.46 06/30/05 69.16 67.46
5,554.57 07/29/05 69.05 67.35
Water Levels and Data over Time
White Mesa Mill -Well TW 4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 102.4
5,553.86 09/12/05 69.76 68.06
5,555.30 12/07/05 68.32 66.62
5,556.20 03/08/06 67.42 65.72
5,556.48 06/14/06 67.14 65.44
5,556.37 07/18/06 67.25 65.55
5,556.94 11/07 /06 66.68 64.98
5557.92 02/27/07 65.70 64
5,557.84 05/02/07 65.78 64.08
5,558.02 08/15/07 65.60 63.90
5,557.13 10/10/07 66.49 64.79
5,569.74 03/26/08 53.88 52.18
5,561.01 06/24/08 62.61 60.91
5,562.07 08/26/08 61.55 59.85
5,562.47 10/14/08 61.15 59.45
5,563.80 03/10/09 59.82 58.12
5,564.27 06/24/09 59.35 57.65
5,564.32 09/10/09 59.30 57.60
5,564.70 12/11/09 58.92 57.22
5,565.14 03/11/10 58.48 56.78
5,565.61 05/11/10 58.01 56.31
5,565.67 09/29/10 57.95 56.25
5,565.62 12/21/10 58.00 56.30
5,565.42 02/28/11 58.20 56.50
5,566.01 06/21/11 57.61 55.91
5,566.03 09/20/11 57.59 55.89
5,566.63 12/21/11 56.99 55.29
5,565.81 03/27/12 57.81 56.11
5,565.82 06/28/12 57.80 56.10
5,566.66 09/27/12 56.96 55.26
5,565.77 12/28/12 57.85 56.15
5,566.89 03/28/13 56.73 55.03
5,566.32 06/27/13 57.30 55.60
5,565.92 09/27/13 57.70 56.00
5,565.63 12/20/13 57.99 56.29
5,565.03 03/27/14 58.59 56.89
5,564.18 06/25/14 59.44 57.74
5,563.52 09/25/14 60.10 58.40
5,563.37 12/17/14 60.25 58.55
5,532.62 03/26/15 91.00 89.30
5,527.07 06/22/15 96.55 94.85
5,533.27 09/30/15 90.35 88.65
5,532.67 12/02/15 90.95 89.25
5,531.44 03/30/16 92.18 90.48
Water Levels and Data over Time
White Mesa Mill -Well TW 4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 102.4
5,529.85 06/30/16 93.77 92.07
5,530.64 09/29/16 92.98 91.28
5,530.61 12/21/16 93.01 91.31
5,538.48 03/30/17 85.14 83.44
5,529.93 06/27/17 93.69 91.99
5,530.41 09/28/17 93.21 91.51
5,531 .26 11/30/17 92.36 90.66
5,530.28 03/28/18 93.34 91.64
5530.36 06/22/18 93.26 91.56
5530.41 09/24/18 93.21 91.51
5531.96 12/17/18 91.66 89.96
5532.84 03/25/19 90.78 89.08
5533.62 06/24/19 90.00 88.30
5532.49 08/12/19 91.13 89.43
.....
8 I.O Vl I.O 0
Depth Below Measuring Point (ft.)
00 Vl 00 0 -..J Vl -..J 0 0\ Vl 0\ 0 Vl Vl Vl 0
01/03/02
06/02/02
10/30/02
03/29/03
08/26/03
01/23/04
06/21/04
11/18/04
04/17/05
09/14/05
02/11/06
07/11/06
12/08/06 ~
05/07/07 ~ 10/04/07 ,&;..
I
03/02/08 ,_. ,_.
07/30/08 ~ 12/27/08
05/26/09 -(0
""1 10/23/09 ~
03/22/10 (0
"C 08/19/10 Er 01/16/11 0 -06/15/11 < (0 11/12/11 ""1
04/10/12 ~ ....
09/07/12 a
02/04/13 (0 --07/04/13 ?
12/01/13 'r:::1" -04/30/14 a
09/27/14 "C '-"
02/24/15
07/24/15
12/21/15
05/19/16
10/16/16
03/15/17
08/12/17
01/09/18
06/08/18
11/05/18
04/04/19
09/01/19
01/29/20
06/27/20
11/24/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 103.2
5,580.91 08/23/02 43.32 41.47
5,581.54 09/11/02 42.69 40.84
5,581.33 10/23/02 42.90 41.05
5,581.47 11/22/02 42.76 40.91
5,581.55 12/03/02 42.68 40.83
5,582.58 01/09/03 41.65 39.80
5,582.47 02/12/03 41.76 39.91
5,582.71 03/26/03 41.52 39.67
5,582.11 04/02/03 42.12 40.27
5,582.92 05/01/03 41.31 39.46
5,583.13 06/09/03 41.10 39.25
5,583.21 07/07/03 41.02 39.17
5,583.31 08/04/03 40.92 39.07
5,583.55 09/11/03 40.68 38.83
5,583.72 10/02/03 40.51 38.66
5,583.77 11/07/03 40.46 38.61
5,584.01 12/03/03 40.22 38.37
5,584.37 01/15/04 39.86 38.01
5,584.39 02/10/04 39.84 37.99
5,584.51 03/28/04 39.72 37.87
5,584.90 04/12/04 39.33 37.48
5,584.88 05/13/04 39.35 37.50
5,584.93 06/18/04 39.30 37.45
5,585.36 07/28/04 38.87 37.02
5,585.38 08/30/04 38.85 37.00
5,585.49 09/16/04 38.74 36.89
5,585.85 10/11/04 38.38 36.53
5,585.91 11/16/04 38.32 36.47
5,586.35 12/22/04 37.88 36.03
5,586.14 01/18/05 38.09 36.24
5,586.56 02/28/05 37.67 35.82
5,586.95 03/15/05 37.28 35.43
5,587.20 04/26/05 37.03 35.18
5,587.35 05/24/05 36.88 35.03
5,587.58 06/30/05 36.65 34.80
5,587.58 07/29/05 36.65 34.80
5,587.94 09/12/05 36.29 34.44
5,588.43 12/07/05 35.80 33.95
5,588.92 03/08/06 35.31 33.46
5,588.34 06/13/06 35.89 34.04
5,588.33 07/18/06 35.90 34.05
5,584.70 11/07/06 39.53 37.68
5588.85 02/27/07 35.38 33.53
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitorini (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 103.2
5,588.53 05/02/07 35.70 33.85
5,586.49 08/14/07 37.74 35.89
5,586.68 10/10/07 37.55 35.70
5,587.76 03/26/08 36.47 34.62
5,587.59 06/24/08 36.64 34.79
5,587.35 08/26/08 36.88 35.03
5,586.84 10/14/08 37 .39 35.54
5,586.17 03/03/09 38.06 36.21
5,585.74 06/24/09 38.49 36.64
5,585.54 09/10/09 38.69 36.84
5,585.77 12/11/09 38.46 36.61
5,585.88 03/11/10 38.35 36.50
5,586.35 05/11/10 37.88 36.03
5,585.68 09/29/10 38.55 36.70
5,585.09 12/21/10 39.14 37.29
5,584.65 02/28/11 39.58 37.73
5,584.76 06/21/11 39.47 37.62
5,584.32 09/20/11 39.91 38.06
5,584.22 12/21/11 40.01 38.16
5,577.07 03/27/12 47.16 45.31
5,577.05 06/28/12 47.18 45.33
5,583.14 09/27/12 41.09 39.24
5,577.10 12/28/12 47.13 45.28
5,582.71 03/28/13 41.52 39.67
5,582.25 06/27/13 41.98 40.13
5,582.24 09/27/13 41.99 40.14
5,582.12 12/20/13 42.11 40.26
5,581.67 03/27/14 42.56 40.71
5,581.03 06/25/14 43.20 41.35
5,580.49 09/25/14 43.74 41.89
5,580.33 12/17/14 43.90 42.05
5,579.28 03/26/15 44.95 43.10
5,579.23 06/22/15 45.00 43.15
5,578.87 09/30/15 45.36 43.51
5,578.53 12/02/15 45.70 43.85
5,578.53 03/30/16 45.70 43.85
5,578.03 06/30/16 46.20 44.35
5,577.54 09/29/16 46.69 44.84
5,577.27 12/21/16 46.96 45.11
5,577.00 03/30/17 47.23 45.38
5,576.59 06/27/17 47.64 45.79
5,576.00 09/28/17 48.23 46.38
5,575.27 11/29/17 48.96 47.11
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 103.2
5,573.64 03/28/18 50.59 48.74
5,572.58 06/22/18 51.65 49.80
5,571.91 09/25/18 52.32 50.47
5,571.49 12/17/18 52.74 50.89
5,570.77 03/25/19 53.46 51.61
5,570.78 06/24/19 53.45 51.60
5,570.54 08/12/19 53.69 51.84
V,
\C
V,
.i,..
Depth Below Measuring Point (ft.)
~ \C t u,)
\0
u,) ~
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07
12/25/07
05/23/08
10/20/08
03/19/09
08/16/09
01/13/10
06/12/10
11/09/10
04/08/11
-09/05/11
02/02/12
07/01/12
11/28/12
04/27/13
09/24/13
02/21/14
07/21/14
12/18/14
05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
~ ~ ...
I ~
N
~ -~
""S
~ ~ "O e-
0 < ~ ""S
~ .... a ~ -?
O"' -a "O --
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,529.66 08/23/02 90.28 88.43
5,530.66 09/11/02 89.28 87.43
5,529.10 10/23/02 90.84 88.99
5,530.58 11/22/02 89.36 87.51
5,530.61 12/03/02 89.33 87.48
5,529.74 01/09/03 90.20 88.35
5,531.03 02/12/03 88.91 87.06
5,531.82 03/26/03 88.12 86.27
5,524.63 04/02/03 95.31 93.46
5,531.54 05/01/03 88.40 86.55
5,538.46 06/09/03 81.48 79.63
5,539.38 07/07/03 80.56 78.71
5,540.72 08/04/03 79.22 77.37
5,541.25 09/11/03 78.69 76.84
5,541.34 10/02/03 78.60 76.75
5,541.69 11/07/03 78.25 76.40
5,541.91 12/03/03 78.03 76.18
5,542.44 01/15/04 77.50 75.65
5,542.47 02/10/04 77.47 75.62
5,542.84 03/28/04 77.10 75.25
5,543.08 04/12/04 76.86 75.01
5,543.34 05/13/04 76.60 74.75
5,543.40 06/18/04 76.54 74.69
5,544.06 07/28/04 75.88 74.03
5,544.61 08/30/04 75.33 73.48
5,545.23 09/16/04 74.71 72.86
5,546.20 10/11/04 73.74 71.89
5,547.43 11/16/04 72.51 70.66
5,548.96 12/22/04 70.98 69.13
5,549.02 01/18/05 70.92 69.07
5,550.66 02/28/05 69.28 67.43
5,551.26 03/15/05 68.68 66.83
5,552.23 04/26/05 67.71 65.86
5,552.87 05/24/05 67.07 65.22
5,553.42 06/30/05 66.52 64.67
5,554.00 07/29/05 65.94 64.09
5,555.21 09/12/05 64.73 62.88
5,558.13 12/07/05 61.81 59.96
5,562.93 03/08/06 57.01 55.16
5,564.39 06/13/06 55.55 53.70
5,562.09 07/18/06 57.85 56.00
5,565.49 11/07/06 54.45 52.60
5571.08 02/27/07 48.86 47.01
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,570.63 05/02/07 49.31 47.46
5,565.24 08/14/07 54.70 52.85
5,565.83 10/10/07 54.11 52.26
5,569.29 03/26/08 50.65 48.80
5,570.00 06/24/08 49.94 48.09
5,570.41 08/26/08 49.53 47.68
5,570.64 10/14/08 49.30 47.45
5,570.43 03/03/09 49.51 47.66
5,570.56 06/24/09 49.38 47.53
5,570.42 09/10/09 49.52 47.67
5,571.15 12/11/09 48.79 46.94
5,572.01 03/11/10 47.93 46.08
5,572.88 05/11/10 47.06 45.21
5,573.17 09/29/10 46.77 44.92
5,573.14 12/21/10 46.80 44.95
5,573.10 02/28/11 46.84 44.99
5,573.75 06/21/11 46.19 44.34
5,573.63 09/20/11 46.31 44.46
5,573.94 12/21/11 46.00 44.15
5,572.79 03/27/12 47.15 45.30
5,572.77 06/28/12 47.17 45.32
5,573.04 09/27/12 46.90 45.05
5,572.79 12/28/12 47.15 45.30
5,573.03 03/28/13 46.91 45.06
5,572.44 06/27/13 47.50 45.65
5,573.46 09/27/13 46.48 44.63
5,573.46 12/20/13 46.48 44.63
5,572.90 03/27/14 47.04 45.19
5,571.79 06/25/14 48.15 46.30
5,571.04 09/25/14 48.90 47.05
5,571.08 12/17/14 48.86 47.01
5,569.50 03/26/15 50.44 48.59
5,569.16 06/22/15 50.78 48.93
5,568.66 09/30/15 51.28 49.43
5,568.02 12/02/15 51.92 50.07
5,568.39 03/30/16 51.55 49.70
5,567.49 06/30/16 52.45 50.60
5,566.99 09/29/16 52.95 51.10
5,566.94 12/21/16 53.00 51.15
5,567.24 03/30/17 52.70 50.85
5,566.79 06/27/17 53.15 51.30
5,566.43 09/28/17 53.51 51.66
5,566.28 11/29/17 53.66 51.81
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,566.24 03/28/18 53.70 51.85
5,566.03 06/22/18 53.91 52.06
5,565.61 09/25/18 54.33 52.48
5,565.32 12/17 /18 54.62 52.77
5,564.78 03/25/19 55.16 53.31
5,564.99 06/24/19 54.95 53.10
5,564.78 08/12/19 55.16 53.31
-8 \0 0
Depth Below Measuring Point (ft.)
00 0 -J 0 0-, 0 Ul 0
.j::,.
0
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07 ~ 07/28/07 ~ 12/25/07 ,&.
I 05/23/08 ~ w 10/20/08 ~ 03/19/09
08/16/09 -~ ""'l 01/13/10 ~
06/12/10 ~ "C 11/09/10 -=-04/08/11 0
09/05/11 ~ ~
02/02/12 ""'l
07/01/12 ~ -· 11/28/12 a ~
04/27/13 ,,-.,
09/24/13 ?
C" 02/21/14 -07/21/14 a "C
12/18/14 --
05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 95.1
5,518.90 08/23/02 93.87 92.02
5,519.28 09/11/02 93.49 91.64
5,519.95 10/23/02 92.82 90.97
5,520.32 11/22/02 92.45 90.60
5,520.42 12/03/02 92.35 90.50
5,520.70 01/09/03 92.07 90.22
5,520.89 02/12/03 91.88 90.03
5,521.12 03/26/03 91.65 89.80
5,521.12 04/02/03 91.65 89.80
5,521.24 05/01/03 91.53 89.68
5,521.34 06/09/03 91.43 89.58
5,521.36 07/07/03 91.41 89.56
5,521.35 08/04/03 91.42 89.57
5,521.30 09/11/03 91.47 89.62
5,521.35 10/02/03 91.42 89.57
5,521.36 11/07/03 91.41 89.56
5,521.16 12/03/03 91.61 89.76
5,521.29 01/15/04 91.48 89.63
5,521.36 02/10/04 91.41 89.56
5,521.46 03/28/04 91.31 89.46
5,521.54 04/12/04 91.23 89.38
5,521.59 05/13/04 91.18 89.33
5,521.69 06/18/04 91.08 89.23
5,521.71 07/28/04 91.06 89.21
5,521.76 08/30/04 91.01 89.16
5,521.77 09/16/04 91.00 89.15
5,521.79 10/11/04 90.98 89.13
5,521.80 11/16/04 90.97 89.12
5,521.82 12/22/04 90.95 89.10
5,521.82 01/18/05 90.95 89.10
5,521.86 02/28/05 90.91 89.06
5,521.85 03/15/05 90.92 89.07
5,521.91 04/26/05 90.86 89.01
5,521.93 05/24/05 90.84 88.99
5,521.94 06/30/05 90.83 88.98
5,521.84 07/29/05 90.93 89.08
5,521.99 09/12/05 90.78 88.93
5,522.04 12/07/05 90.73 88.88
5,522.05 03/08/06 90.72 88.87
5,522.27 06/13/06 90.50 88.65
5,521.92 07/18/06 90.85 89.00
5,520.17 11/07/06 92.60 90.75
5522.24 02/27/07 90.53 88.68
Water Levels and Data over Time
White Mesa Mill -Well TW4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 95.1
5,522.47 05/02/07 90.30 88.45
5,520.74 08/14/07 92.03 90.18
5,518.13 10/10/07 94.64 92.79
5,522.85 03/26/08 89.92 88.07
5,522.91 06/24/08 89.86 88.01
5,523.01 08/26/08 89.76 87.91
5,522.96 10/14/08 89.81 87.96
5,523.20 03/03/09 89.57 87.72
5,523.33 06/24/09 89.44 87.59
5,523.47 09/10/09 89.30 87.45
5,523.54 12/11/09 89.23 87.38
5,522.98 03/11/10 89.79 87.94
5,524.01 05/11/10 88.76 86.91
5,524.37 09/29/10 88.40 86.55
5,524.62 12/21/10 88.15 86.30
5,524.78 02/28/11 87.99 86.14
5,525.23 06/21/11 87.54 85.69
5,525.45 09/20/11 87.32 85.47
5,525.72 12/21/11 87.05 85.20
5,525.88 03/27/12 86.89 85.04
5,525.97 06/28/12 86.80 84.95
5,526.32 09/27/12 86.45 84.60
5,525.88 12/28/12 86.89 85.04
5,526.91 03/28/13 85.86 84.01
5,526.99 06/27/13 85.78 83.93
5,527.68 09/27/13 85.09 83.24
5,528.19 12/20/13 84.58 82.73
5,528.75 03/27/14 84.02 82.17
5,529.21 06/25/14 83.56 81.71
5,529.78 09/25/14 82.99 81.14
5,530.41 12/17/l4 82.36 80.51
5,530.86 03/26/15 81.91 80.06
5,531.40 06/22/15 81.37 79.52
5,532.15 09/30/15 80.62 78.77
5,532.12 12/02/15 80.65 78.80
5,533.12 03/30/16 79.65 77.80
5,533.13 06/30/16 79.64 77.79
5,533.24 09/29/16 79.53 77.68
5,533.42 12/21/16 79.35 77.50
5,533.97 03/30/17 78.80 76.95
5,534.05 06/27/17 78.72 76.87
5,534.07 09/28/17 78.70 76.85
5,534.29 11/29/17 78.48 76.63
Water Levels and Data over Time
White Mesa Mill -Well TW4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 95.1
5,534.56 03/28/18 78.21 76.36
5,534.67 06/22/18 78.l 76.25
5,534.75 09/25/18 78.02 76.17
5,534.71 12/17/18 78.06 76.21
5,534.71 03/25/19 78.06 76.21
5,535.04 06/24/19 77.73 75.88
5,535.17 08/12/19 77.60 75.75
-0 0
~ ,
I
•
'
\0 0
~
~.
0
•
• •
~
0
' ' 0
0
• . ~
~
'
00 0
• •
•
0
0
0
0
~
Depth Below Measuring Point (ft.)
-....I 0 0\ 0 Ul 0 .j::.. 0
l.;)
0 N 0 -0 0
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07 ~
12/25/07 ~ ,&;;I,.
05/23/08 I ~
10/20/08 ,&;;I,.
03/19/09 ~
08/16/09 -~
01/13/10 "1
~ 06/12/10 ~
11/09/10 ts ;.
04/08/11 0 09/05/11 -<
02/02/12 ~ "1
07/01/12 ~ ...
11/28/12 = ~
04/27/13 --09/24/13 ?
02/21/14 C" -07/21/14 = ts
12/18/14 "-'
05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
Water Levels and Data over Time
White Mesa Mill -Well MW-26
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,624.15 5,625.45 1.30 121.33
5,574.75 08/23/02 50.70 49.40
5,574.97 09/11/02 50.48 49.18
5,575.10 10/23/02 50.35 49.05
5,574.99 11/22/02 50.46 49.16
5,575.28 12/03/02 50.17 48.87
5,575.41 01/09/03 50.04 48.74
5,575.43 02/12/03 50.02 48.72
5,575.63 03/26/03 49.82 48.52
5,575.91 04/02/03 49.54 48.24
5,575.81 05/01/03 49.64 48.34
5,572.36 06/09/03 53.09 51.79
5,570.70 07/07/03 54.75 53.45
5,570.29 08/04/03 55.16 53.86
5,560.94 09/11/03 64.51 63.21
5,560.63 10/02/03 64.82 63.52
5,560.56 11/07/03 64.89 63.59
5,564.77 12/03/03 60.68 59.38
5,570.89 01/15/04 54.56 53.26
5,572.55 02/10/04 52.90 51.60
5,574.25 03/28/04 51.20 49.90
5,574.77 04/12/04 50.68 49.38
5,575.53 05/13/04 49.92 48.62
5,575.59 06/18/04 49.86 48.56
5,576.82 07/28/04 48.63 47.33
5,527.47 09/16/04 97.98 96.68
5,553.97 11/16/04 71.48 70.18
5,562.33 12/22/04 63.12 61.82
5,550.00 01/18/05 75.45 74.15
5,560.02 04/26/05 65.43 64.13
5,546.11 05/24/05 79.34 78.04
5,556.71 06/30/05 68.74 67.44
5,554.95 07/29/05 70.50 69.20
5,555.48 09/12/05 69.97 68.67
5,551.09 12/07/05 74.36 73.06
5,552.85 03/08/06 72.60 71.30
5,554.30 06/13/06 71.15 69.85
5,554.87 07/18/06 70.58 69.28
5,550.88 11/07/06 74.57 73.27
5558.77 02/27/07 66.68 65.38
5,548.54 05/02/07 76.91 75.61
5,551.33 10/10/07 74.12 72.82
5,545.56 03/26/08 79.89 78.59
5,545.56 06/25/08 79.89 78.59
Water Levels and Data over Time
White Mesa Mill -Well MW-26
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,624.15 5,625.45 1.30 121.33
5,545.82 08/26/08 79.63 78.33
5,545.64 10/14/08 79.81 78.51
5,544.45 03/03/09 81.00 79.70
5,545.32 06/24/09 80.13 78.83
5,544.61 09/10/09 80.84 79.54
5,549.33 12/11/09 76.12 74.82
5,543.78 03/11/10 81.67 80.37
5,545.61 05/11/10 79.84 78.54
5,547.43 09/29/10 78.02 76.72
5,544.14 12/21/10 81.31 80.01
5,546.77 02/28/11 78.68 77.38
5,537.60 06/21/11 87.85 86.55
5,551.46 09/20/11 73.99 72.69
5,549.12 12/21/11 76.33 75.03
5,557.30 03/27/12 68.15 66.85
5,557.38 06/28/12 68.07 66.77
5,550.86 09/27/12 74.59 73.29
5,557.30 12/28/12 68.15 66.85
5,565.37 03/28/13 60.08 58.78
5,563.55 06/27/13 61.90 60.60
5,560.12 09/27/13 65.33 64.03
5,559.27 12/20/13 66.18 64.88
5,556.65 03/27/14 68.80 67.50
5,552.23 06/25/14 73.22 71.92
5,554.05 09/25/14 71.40 70.10
5,550.65 12/17/14 74.80 73.50
5,557.55 03/26/15 67.90 66.60
5,558.51 06/22/15 66.94 65.64
5,560.81 09/30/15 64.64 63.34
5,560.25 12/02/15 65.20 63.90
5,561.07 03/30/16 64.38 63.08
5,560.51 06/30/16 64.94 63.64
5,557.99 09/29/16 67.46 66.16
5,561.26 12/21/16 64.19 62.89
5,559.85 03/30/17 65.60 64.30
5,559.35 06/27/17 66.10 64.80
5,553.30 09/28/17 72.15 70.85
5,557.38 11/30/17 68.07 66.77
5,543.85 03/28/18 81.60 80.30
5,553.27 06/22/18 72.18 70.88
5,547.57 09/24/18 77.88 76.58
5,547.63 12/20/18 77.82 76.52
5,545.54 03/25/19 79.91 78.61
Water Levels and Data over Time
White Mesa Mill -Well MW-26
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) WeJI
5,624.15 5,625.45 1.30 121.33
5,547.27 06/24/19 78.18 76.88
5,549.07 08/12/19 76.38 75.08
Depth Below Measuring Point (ft.)
.....
0 \0 00 -.l 0\ u, .j::.
0 0 0 0 0 0 0
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07 a: 07/28/07
12/25/07 ~ I
05/23/08 N O'\
10/20/08 ~ 03/19/09 -· 08/16/09 ~ "1
01/13/10 0
06/12/10 ~ "C
11/09/10 -=--
04/08/11 0
09/05/11 < ~
02/02/12 "1
~
07/01/12 .... a 11/28/12 ~
04/27/13 ,-..
? 09/24/13 O"
02/21/14 -a 07/21/14 "C --~ 12/18/14
05/17/15
10/14/15
03/12/16
08/09/16
,_ 01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,562.91 08/23/02 61.11 57.74
5,563.45 09/11/02 60.57 57.20
5,563.75 10/23/02 60.27 56.90
5,563.68 11/22/02 60.34 56.97
5,563.68 12/03/02 60.34 56.97
5,564.16 01/09/03 59.86 56.49
5,564.25 02/12/03 59.77 56.40
5,564.53 03/26/03 59.49 56.12
5,564.46 04/02/03 59.56 56.19
5,564.79 05/01/03 59.23 55.86
5,564.31 06/09/03 59.71 56.34
5,563.29 07/07/03 60.73 57.36
5,562.76 08/04/03 61.26 57.89
5,561.73 09/11/03 62.29 58.92
5,561.04 10/02/03 62.98 59.61
5,560.39 11/07/03 63.63 60.26
5,559.79 12/03/03 64.23 60.86
5,561.02 01/15/04 63.00 59.63
5,561.75 02/10/04 62.27 58.90
5,562.98 03/28/04 61.04 57.67
5,563.29 04/12/04 60.73 57.36
5,564.03 05/13/04 59.99 56.62
5,564.09 06/18/04 59.93 56.56
5,565.08 07/28/04 58.94 55.57
5,564.56 08/30/04 59.46 56.09
5,563.55 09/16/04 60.47 57.10
5,561.79 10/11/04 62.23 58.86
5,560.38 11/16/04 63.64 60.27
5,559.71 12/22/04 64.31 60.94
5,559.14 01/18/05 64.88 61.51
5,558.65 02/28/05 65.37 62.00
5,558.54 03/15/05 65.48 62.11
5,558.22 04/26/05 65.80 62.43
5,558.54 05/24/05 65.48 62.11
5,559.24 06/30/05 64.78 61.41
5,559.38 07/29/05 64.64 61.27
5,559.23 09/12/05 64.79 61.42
5,557.67 12/07/05 66.35 62.98
5,557.92 03/08/06 66.10 62.73
5,558.47 06/13/06 65.55 62.18
5,558.42 07/18/06 65.60 62.23
5,558.09 11/07/06 65.93 62.56
5,557.34 02/27/07 66.68 63.31
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,547.11 05/02/07 76.91 73.54
5,558.52 08/14/07 65.50 62.13
5,559.02 10/10/07 65.00 61.63
5,561.04 03/26/08 62.98 59.61
5,560.06 06/24/08 63.96 60.59
5,559.32 08/26/08 64.70 61.33
5,558.89 10/14/08 65.13 61.76
5,558.40 03/03/09 65 .62 62.25
5,558.32 06/24/09 65.70 62.33
5,558.03 09/10/09 65.99 62.62
5,558.81 12/11/09 65.21 61.84
5,559.80 03/11/10 64.22 60.85
5,559.85 05/11/10 64.17 60.80
5,560.54 09/29/10 63.48 60.11
5,558.65 12/21/10 65.37 62.00
5,559.26 02/28/11 64.76 61.39
5,560.48 06/21/11 63.54 60.17
5,561.52 09/20/11 62.50 59.13
5,562.95 12/21/11 61.07 57.70
5,563.76 03/27/12 60.26 56.89
5,563.90 06/28/12 60.12 56.75
5,564.65 09/27/12 59.37 56.00
5,563.77 12/28/12 60.25 56.88
5,564.74 03/28/13 59.28 55.91
5,563.66 06/27/13 60.36 56.99
5,562.27 09/27/13 61.75 58.38
5,562.17 12/20/13 61.85 58.48
5,561.17 03/27/14 62.85 59.48
5,559.53 06/25/14 64.49 61.12
5,558.36 09/25/14 65.66 62.29
5,558.00 12/17/14 66.02 62.65
5,559.02 03/26/15 65.00 61.63
5,560.62 06/22/15 63.40 60.03
5,560.62 09/30/15 63.40 60.03
5,560.85 12/02/15 63.17 59.80
5,560.92 03/30/16 63.10 59.73
5,559.95 06/30/16 64.07 60.70
5,559.72 09/29/16 64.30 60.93
5,559.71 12/21/16 64.31 60.94
5,559.53 03/30/17 64.49 61.12
5,569.02 06/27/17 59.63 56.26
5,558.97 09/28/17 69.68 66.31
5,558.51 11/30/17 70.14 66.77
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,558.00 03/29/18 70.65 67.28
5,557.94 06/22/18 70.71 67.34
5,557.67 09/25/18 70.98 67.61
5,557.66 12/17/18 70.99 67.62
5,548.49 03/25/19 80.16 76.79
5,556.98 06/24/19 71.67 68.30
5,556.83 08/12/19 71.82 68.45
00 V, 00 0
Depth Below Measuring Point (ft.)
-.J V, -.J 0 0\ V, ~ V,
V,
V,
0
1-----+-----+------lf------+-------<11ar+------1---+ 08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07
12/25/07
05/23/08
10/20/08
03/19/09
08/16/09
01/13/10
06/12/10
11/09/10
04/08/11
09/05/11
-02/02/12
07/01/12
11/28/12
04/27/13
09/24/13
02/21/14
07/21/14
12/18/14
05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
~---'-------L..~~---J'-----.....__ __ __._ __ ___,.___ __ ....,_09/17/20
~ ~ .&;.
I ~
0-.
l ~ "1
0 ~ -= g.
0 < ~ "1
~ ... a ~ --?
-a-a -= '-'
Water Levels and Data over Time
White Mesa Mill -Well MW-32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5,542.17 08/23/02 83.07 81 .24
5,542.39 09/11/02 82.85 81.02
5,542.61 10/23/02 82.63 80.80
5,542.49 11/22/02 82.75 80.92
5,542.82 12/03/02 82.42 80.59
5,543.03 01/09/03 82.21 80.38
5,543.04 02/12/03 82.20 80.37
5,543.41 03/26/03 81.83 80.00
5,543.69 04/02/03 81.55 79.72
5,543.77 05/01/03 81.47 79.64
5,544.01 06/09/03 81.23 79.40
5,544.05 07/07/03 81.19 79.36
5,543.99 08/04/03 81.25 79.42
5,544.17 09/11/03 81.07 79.24
5,544.06 10/02/03 81.18 79.35
5,544.03 11/07/03 81.21 79 .38
5,543.94 12/03/03 81.30 79.47
5,543.98 01/15/04 81.26 79.43
5,543.85 02/10/04 81.39 79.56
5,544.05 03/28/04 81.19 79.36
5,544.33 04/12/04 80.91 79.08
5,544.55 05/13/04 80.69 78.86
5,544.59 06/18/04 80.65 78.82
5,545.08 07/28/04 80.16 78.33
5,545.26 08/30/04 79.98 78.15
5,545.48 09/16/04 79.76 77.93
5,545.61 10/11/04 79.63 77.80
5,545.46 11/16/04 79.78 77.95
5,545.66 12/22/04 79.58 77.75
5,545.33 01/18/05 79.91 78.08
5,545.51 02/28/05 79.73 77.90
5,545.57 03/15/05 79.67 77.84
5,545.46 04/26/05 79.78 77.95
5,545.45 05/24/05 79.79 77.96
5,545.33 06/30/05 79.91 78.08
5,545.16 07/29/05 80.08 78.25
5,545.54 09/12/05 79.70 77.87
5,545.77 12/07/05 79.47 77.64
5,546.09 03/08/06 79.15 77.32
5,545.94 06/13/06 79.30 77.47
5,545.94 07/18/06 79.30 77.47
5,546.24 11/07/06 79.00 77.17
5546.81 02/27/07 78.43 76.60
Water Levels and Data over Time
White Mesa Mill -Well MW-32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5546.56 05/02/07 78.68 76.85
5546.81 08/15/07 78.43 76.6
5546.96 10/10/07 78.28 76.45
5547.9 03/26/08 77 .34 75.51
5548.08 06/25/08 77.16 75.33
5548.42 08/26/08 76.82 74.99
5548.05 10/14/08 77.19 75.36
5548.29 03/03/09 76.95 75.12
5548.09 06/24/09 77.15 75.32
5547.79 09/10/09 77.45 75.62
5548.09 12/11/09 77.15 75.32
5,548.50 03/11/10 76.74 74.91
5,548.89 05/11/10 76.35 74.52
5,548.83 09/29/10 76.41 74.58
5,548.97 12/21/10 76.27 74.44
5,548.68 02/28/11 76.56 74.73
5,549.33 06/21/11 75.91 74.08
5,549.19 09/20/11 76.05 74.22
5,550.06 12/21/11 75.18 73.35
5,550.31 03/27/12 74.93 73.10
5,550.32 06/28/12 74.92 73.09
5,550.88 09/27/12 74.36 72.53
5,550.29 12/28/12 74.95 73.12
5,551.54 03/28/13 73.70 71.87
5,550.34 06/27/13 74.90 73.07
5,551.35 09/27/13 73.89 72.06
5,551.33 12/20/13 73.91 72.08
5,550.97 03/27/14 74.27 72.44
5,550.16 06/25/14 75.08 73.25
5,549.29 09/25/14 75.95 74.12
5,548.99 12/17/14 76.25 74.42
5,548.24 03/26/15 77.00 75.17
5,548.29 06/22/15 76.95 75.12
5,548.33 09/30/15 76.91 75.08
5,547.98 12/02/15 77.26 75.43
5,548.24 03/30/16 77.00 75.17
5,547.68 06/30/16 77.56 75.73
5,547.29 09/29/16 77.95 76.12
5,547.09 12/21/16 78.15 76.32
5,547.34 03/30/17 77.90 76.07
5,546.94 06/27/17 78.30 76.47
5,546.59 09/28/17 78.65 76.82
5,546.32 11/30/17 78.92 77.09
Water Levels and Data over Time
White Mesa Mill -Well MW-32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5,546.19 03/29/18 79.05 77.22
5545.99 06/22/18 79.25 77.42
5545.57 09/26/18 79.67 77.84
5545.56 12/17/18 79.68 77.85
5545.08 03/26/19 80.16 78.33
5544.99 06/24/19 80.25 78.42
5544.87 08/12/19 80.37 78.54
Depth Below Measuring Point (ft.)
00 00 00 -..J -..J -..J -..J ~ N 0 00 °'" ~ N
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07 a:
12/25/07 ~
05/23/08 I ~
10/20/08 N
03/19/09 ~ 08/16/09 """ ~
01/13/10 ~
06/12/10 ~ ~
11/09/10 "'O ~ 04/08/11 0 09/05/11 ~
02/02/12 ~ ~
07/01/12 ~ ....
11/28/12 51 ~ 04/27/13 --09/24/13 ?
02/21/14 C"
07/21/14 a "'O 12/18/14 .._,
05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5 639.13 5,641.28 2.15 136.9
5,585.13 08/23/02 56.15 54.00
5,585.41 09/11/02 55.87 53.72
5,585.47 10/23/02 55.81 53.66
5,585.40 11/22/02 55.88 53.73
5,585.68 12/03/02 55.60 53.45
5,585.90 01/09/03 55.38 53.23
5,590.79 02/12/03 50.49 48.34
5,586.18 03/26/03 55.10 52.95
5,586.36 04/02/03 54.92 52.77
5,586.24 05/01/03 55.04 52.89
5,584.93 06/09/03 56.35 54.20
5,584.46 07/07/03 56.82 54.67
5,584.55 08/04/03 56.73 54.58
5,584.01 09/11/03 57.27 55.12
5,583.67 10/02/03 57.61 55.46
5,583.50 11/07/03 57.78 55.63
5,584.08 12/03/03 57.20 55.05
5,585.45 01/15/04 55.83 53.68
5,585.66 02/10/04 55.62 53.47
5,586.13 03/28/04 55.15 53.00
5,586.39 04/12/04 54.89 52.74
5,586.66 05/13/04 54.62 52.47
5,586.77 06/18/04 54.51 52.36
5,587.35 07/28/04 53.93 51.78
5,586.34 08/30/04 54.94 52.79
5,585.85 09/16/04 55.43 53.28
5,585.22 10/11/04 56.06 53.91
5,584.70 11/16/04 56.58 54.43
5,584.81 12/22/04 56.47 54.32
5,584.68 01/18/05 56.60 54.45
5,585.02 02/28/05 56.26 54.11
5,585.25 03/15/05 56.03 53.88
5,586.31 04/26/05 54.97 52.82
5,586.97 05/24/05 54.31 52.16
5,586.58 06/30/05 54.70 52.55
5,586.10 07/29/05 55.18 53.03
5,586.05 09/12/05 55.23 53.08
5,585.86 12/07/05 55.42 53.27
5,587.13 03/08/06 54.15 52.00
5,585.93 06/13/06 55.35 53.20
5,585.40 07/18/06 55.88 53.73
5,585.38 11/07/06 55.90 53.75
5585.83 02/27/07 55.45 53.30
Water Levels and Data over Time
White Mesa Mill -Well TW 4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,639.13 5,641.28 2.15 136.9
5585.15 05/02/07 56.13 53.98
5586.47 06/24/08 54.81 52.66
5586.30 08/26/08 54.98 52.83
5585.21 10/14/08 56.07 53.92
5584.47 03/03/09 56.81 54.66
5584.35 06/24/09 56.93 54.78
5583.88 09/10/09 57.4 55.25
5584.43 12/11/09 56.85 54.70
5,585.26 03/11/10 56.02 53.87
5,584.17 05/11/10 57.11 54.96
5,583.61 09/29/10 57.67 55.52
5,604.29 12/21/10 36.99 34.84
5,583.56 02/28/11 57.72 55.57
5,584.73 06/21/11 56.55 54.40
5,584.71 09/20/11 56.57 54.42
5,585.03 12/21/11 56.25 54.10
5,584.63 03/27/12 56.65 54.50
5,584.67 06/28/12 56.61 54.46
5,583.98 09/27/12 57.30 55.15
5,584.65 12/28/12 56.63 54.48
5,582.88 03/28/13 58.40 56.25
5,584.63 06/27/13 56.65 54.50
5,581.38 09/27/13 59.90 57.75
5,579.71 12/20/13 61.57 59.42
5,579.26 03/27/14 62.02 59.87
5,577.73 06/25/14 63.55 61.40
5,576.79 09/25/14 64.49 62.34
5,577.11 12/17/14 64.17 62.02
5,577.18 03/26/15 64.10 61.95
5,577.13 06/22/15 64.15 62.00
5,576.63 09/30/15 64.65 62.50
5,576.20 12/02/15 65.08 62.93
5,576.05 03/30/16 65.23 63.08
5,575.35 06/30/16 65.93 63.78
5,575.02 09/29/16 66.26 64.11
5,574.34 12/21/16 66.94 64.79
5,574.73 03/30/17 66.55 64.40
5,574.13 06/27/17 67.15 65.00
5,573.51 09/28/17 67.77 65.62
5,572.93 11/29/17 68.35 66.20
5,572.51 03/29/18 68.77 66.62
5,572.28 06/22/18 69.00 66.85
5,571.72 09/26/18 69.56 67.41
Water Levels and Data over Time
White Mesa Mill -Well TW 4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,639.13 5,641.28 2.15 136.9
5,571.45 12/17/18 69.83 67.68
5,570.86 03/26/19 70.42 68.27
5,570.60 06/24/19 70.68 68.53
5,570.53 08/12/19 70.75 68.60
Depth Below Measuring Point (ft.)
00 -....J O'I Vt .j::,. (;.) N ......
0 0 0 0 0 0 0 0 0
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07 ~
12/25/07 ~ ......
05/23/08 I .....
10/20/08 00
03/19/09 ~
08/16/09 """' ~
01/13/10 "'1
0 06/12/10 ~
11/09/10 "Cl ;.
04/08/11 0 09/05/11 <
02/02/12 ~ "'1
07/01/12 ~ ...
11/28/12 e ~
04/27/13 --09/24/13 ?
02/21/14 "a' -07/21/14 e "Cl 12/18/14 --
-05/17/15
10/14/15
03/12/16
08/09/16
01/06/17
06/05/17
11/02/17
04/01/18
08/29/18
01/26/19
06/25/19
11/22/19
04/20/20
09/17/20
Water Levels and Data over Time
White Mesa Mill-Well TW4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 126.86
5,581.88 08/23/02 49.51 47.65
5,582.14 09/11/02 49.25 47.39
5,582.06 10/23/02 49.33 47.47
5,582.07 11/22/02 49.32 47.46
5,582.16 12/03/02 49.23 47.37
5,582.28 01/09/03 49.11 47.25
5,582.29 02/21/03 49.10 47.24
5,582.74 03/26/03 48.65 46.79
5,582.82 04/02/03 48.57 46.71
5,548.47 05/01/03 82.92 81.06
5,564.76 06/09/03 66.63 64.77
5,562.53 07/07/03 68.86 67.00
5,564.10 08/04/03 67.29 65.43
5,566.01 08/30/04 65.38 63.52
5,555.16 09/16/04 76.23 74.37
5,549.80 10/11/04 81.59 79.73
5,546.04 11/16/04 85.35 83.49
5,547.34 12/22/04 84.05 82.19
5,548.77 01/18/05 82.62 80.76
5,551.18 02/28/05 80.21 78.35
5,556.81 03/15/05 74.58 72.72
5,562.63 04/26/05 68.76 66.90
5,573.42 05/24/05 57.97 56.11
5,552.94 07/29/05 78.45 76.59
5,554.00 09/12/05 77.39 75.53
5,555.98 12/07/05 75.41 73.55
5,552.00 03/08/06 79.39 77.53
5,545.74 06/13/06 85.65 83.79
5,544.06 07/18/06 87.33 85.47
5,548.81 11/07/06 82.58 80.72
5543.59 02/27/07 87.80 85.94
5544.55 05/02/07 86.84 84.98
5558.97 08/15/07 72.42 70.56
5559.73 10/10/07 71.66 69.8
5569.26 03/26/08 62.13 60.27
5535.47 06/25/08 95.92 94.06
5541.41 08/26/08 89.98 88.12
5558.45 10/14/08 72.94 71.08
5536.90 03/03/09 94.49 92.63
5547.76 06/24/09 83.63 81.77
5561.48 09/10/09 69.91 68.05
5548.14 12/11/09 83.25 81.39
5,570.58 03/11/10 60.81 58.95
Water Levels and Data over Time
White Mesa Mill -Well TW 4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (bhv.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 126.86
5,561.35 05/11/10 70.04 68.18
5,535.26 09/29/10 96.13 94.27
5,568.40 12/21/10 62.99 61.13
5,550.36 02/28/11 81.03 79.17
5,570.41 06/21/11 60.98 59.12
5,567.84 09/20/11 63.55 61.69
5,571.32 12/21/11 60.07 58.21
5,572.40 03/27/12 58.99 57.13
5,572.39 06/28/12 59.00 57.14
5,571.40 09/27/12 59.99 58.13
5,568.21 12/28/12 63.18 61.32
5,572.51 03/28/13 58.88 57.02
5,566.00 06/27/13 65.39 63.53
5,568.37 09/27/13 63.02 61.16
5,564.55 12/20/13 66.84 64.98
5,565.11 03/27/14 66.28 64.42
5,561.49 06/25/14 69.90 68.04
5,562.67 09/25/14 68.72 66.86
5,562.99 12/17/14 68.40 66.54
5,567.99 03/26/15 63.40 61.54
5,562.79 06/22/15 68.60 66.74
5,568.16 09/30/15 63.23 61.37
5,567.51 12/02/15 63.88 62.02
5,566.38 03/30/16 65.01 63.15
5,566.91 06/30/16 64.48 62.62
5,567.38 09/29/16 64.01 62.15
5,567.41 12/21/16 63.98 62.12
5,566.87 03/30/17 64.52 62.66
5,566.76 06/27/17 64.63 62.77
5,565.19 09/28/17 66.20 64.34
5,565.79 11/30/17 65.60 63.74
5,563.79 03/28/18 67.60 65.74
5,564.58 06/22/18 66.81 64.95
5,562.56 09/24/18 68.83 66.97
5,555.78 12/18/18 75.61 73.75
5,547.86 03/25/19 83.53 81.67
5,557.99 06/24/19 73.40 71.54
5,554.26 08/12/19 77.13 75.27
......
8 \0 0
Depth Below Measuring Point (ft.)
00 0 ....J 0 O'I 0
V,
0 """' 0
06/08/01
11/05/01
04/04/02
09/01/02
01/29/03
06/28/03
11/25/03
04/23/04
09/20/04
02/17/05
07/17/05
12/14/05
05/13/06 1-3
10/10/06 ~ 03/09/07 ... I 08/06/07 lo-
\0 01/03/08 ~ 06/01/08
10/29/08 f"'I" ~
03/28/09 "'1
~ 08/25/09 ~
01/22/10 "'C f"'I"
06/21/10 =-
11/18/10 0 ~
04/17/11 ~ "'1 09/14/11 1-3
02/11/12 ...
9 07/10/12 ~
12/07/12 --? 05/06/13 C" 10/03/13 -9 03/02/14 "'C
07/30/14 --
12/27/14
05/26/15
10/23/15
03/21/16
08/18/16
01/15/17
06/14/17
11/11/17
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
09/26/20
Water Levels and Data over Time
White Mesa Mill-Well TW4-20
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.52 5,629.53 1.01 105.9
5,565.70 07/29/05 63.83 62.82
5,546.53 08/30/05 83.00 81.99
5,540.29 09/12/05 89.24 88.23
5,541.17 12/07/05 88.36 87.35
5,540.33 03/08/06 89.20 88.19
5,530.43 06/13/06 99.10 98.09
5,569.13 07/18/06 60.40 59.39
5,547.95 11/07/06 81.58 80.57
5,549.25 02/27/07 80.28 79.27
5,550.58 05/02/07 78.95 77.94
5,563.60 08/14/07 65.93 64.92
5,555.85 10/10/07 73.68 72.67
5,569.10 03/26/08 60.43 59.42
5,560.00 06/25/08 69.53 68.52
5,539.64 08/26/08 89.89 88.88
5,539.51 10/14/08 90.02 89.01
5,553.00 03/03/09 76.53 75.52
5,534.18 06/24/09 95.35 94.34
5,558.39 09/10/09 71.14 70.13
5,560.99 12/11/09 68.54 67.53
5,564.09 03/11/10 65.44 64.43
5,564.22 05/11/10 65.31 64.30
5,560.33 09/29/10 69.20 68.19
5,561.35 12/21/10 68.18 67.17
5,560.18 02/28/11 69.35 68.34
5,576.23 06/21/11 53.30 52.29
5,548.50 09/20/11 81.03 80.02
5,558.58 12/21/11 70.95 69.94
5,567.73 03/27/12 61.80 60.79
5,567.77 06/28/12 61.76 60.75
5,569.58 09/27/12 59.95 58.94
5,572.58 12/28/12 56.95 55.94
5,571.52 03/28/13 58.01 57.00
5,569.93 06/27/13 59.60 58.59
5,568.53 09/27/13 61.00 59.99
5,559.44 12/20/13 70.09 69.08
5,562.17 03/27/14 67.36 66.35
5,558.98 06/25/14 70.55 69.54
5,561.03 09/25/14 68.50 67.49
5,559.39 12/17/14 70.14 69.13
5,565.65 03/26/15 63.88 62.87
5,568.25 06/22/15 61.28 60.27
Water Levels and Data over Time
White Mesa Mill -Well TW4-20
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.52 5,629.53 1.01 105.9
5,566.78 09/30/15 62.75 61.74
5,565.43 12/02/15 64.10 63.09
5,565.87 03/30/16 63.66 62.65
5,564.42 06/30/16 65.11 64.10
5,565.43 09/29/16 64.10 63.09
5,564.93 12/21/16 64.60 63.59
5,564.27 03/30/17 65.26 64.25
5,564.46 06/27/17 65.07 64.06
5,564.23 09/28/17 65.30 64.29
5,556.13 11/30/17 73.40 72.39
5,562.98 03/28/18 66.55 65.54
5,562.81 06/22/18 66.72 65.71
5,562.58 09/24/18 66.95 65.94
5,558.49 12/17/18 71.04 70.03
5,553.96 03/25/19 75.57 74.56
5,555.22 06/24/19 74.31 73.30
5,556.08 08/12/19 73.45 72.44
.......
8 '° 0
Depth Below Measuring Point (ft.)
00 0 -..J 0 O'I 0
Ul 0 ~ 0
07/29/05
12/26/05
05/25/06
10/22/06
03/21/07
08/18/07
01/15/08
06/13/08
11/10/08
04/09/09 11-3
09/06/09 ~ ,I:;,.. 02/03/10 I N
07/03/10 = ~ 11/30/10 -~ 04/29/1 l lo1
09/26/1 l ~ ~ "'Cl
02/23/12 ~
07/22/12 0 ~
12/19/12 ~ lo1
OS/ 18/13 11-3 ...
10/15/13 a ~ ---03/14/14 ?
08/11/14 0--
01/08/15 a "'Cl "-'
06/07/15
11/04/15
04/02/16
08/30/16
01/27/17
06/26/17
11/23/17
04/22/18
09/19/18
02/16/19
07/16/19
12/13/19
05/11/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-21
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.20 5,639.35 1.15 118.8
5,582.98 07/29/05 56.37 55.22
5,583.43 08/30/05 55.92 54.77
5,581.87 09/12/05 57.48 56.33
5,580.50 12/07/05 58.85 57.70
5,583.64 03/08/06 55.71 54.56
5,580.55 06/13/06 58.80 57.65
5,578.95 07/18/06 60.40 59.25
5,578.47 11/07/06 60.88 59.73
5,579.53 02/27/07 59.82 58.67
5,578.07 05/02/07 61.28 60.13
5,583.41 08/15/07 55 .94 54.79
5,583.45 10/10/07 55.90 54.75
5,586.47 03/26/08 52.88 51.73
5,579.16 06/24/08 60.19 59.04
5,579.92 08/26/08 59.43 58.28
5,577.37 10/14/08 61.98 60.83
5,578.00 03/10/09 61.35 60.20
5,580.14 06/24/09 59.21 58.06
5,578.72 09/10/09 60.63 59.48
5,579.99 12/11/09 59.36 58.21
5,582.81 03/11/10 56.54 55.39
5,582.23 05/11/10 57.12 55.97
5,576.60 09/29/10 62.75 61.60
5,581.14 12/21/10 58.21 57.06
5,579.53 02/28/11 59.82 58.67
5,584.17 06/21/11 55.18 54.03
5,584.80 09/20/11 54.55 53.40
5,585.68 12/21/11 53.67 52.52
5,585.24 03/27/12 54.11 52.96
5,585.26 06/28/12 54.09 52.94
5,585.16 09/27/12 54.19 53.04
5,585.25 12/28/12 54.10 52.95
5,582.84 03/28/13 56.51 55.36
5,581.79 06/27/13 57.56 56.41
5,580.89 09/27/13 58.46 57.31
5,577.45 12/20/13 61.90 60.75
5,576.01 03/27/14 63.34 62.19
5,574.08 06/25/14 65.27 64.12
5,573.20 09/25/14 66.15 65.00
5,576.13 12/17/14 63.22 62.07
5,578.19 03/26/15 61.16 60.01
5,574.85 06/22/15 64.50 63.35
Water Levels and Data over Time
White Mesa Mill -Well TW4-21
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.20 5,639.35 1.15 118.8
5,573.05 09/30/15 66.30 65.15
5,569.88 12/02/15 69.47 68.32
5,571.81 03/30/16 67.54 66.39
5,571.86 06/30/16 67.49 66.34
5,570.82 09/29/16 68.53 67.38
5,570.45 12/21/16 68.90 67.75
5,574.53 03/30/17 64.82 63.67
5,569.91 06/27/17 69.44 68.29
5,569.49 09/28/17 69.86 68.71
5,566.87 11/30/17 72.48 71.33
5,568.10 03/28/18 71.25 70.10
5,568.17 06/22/18 71.18 70.03
5,567.50 09/24/18 71.85 70.70
5,554.80 12/17/18 84.55 83.40
5,560.92 03/25/19 78.43 77.28
5,561.49 06/24/19 77.86 76.71
5,564.17 08/12/19 75.18 74.03
\0 0 00 0 -:i 0
Depth Below Measuring Point (ft.)
g V,
0 ""' 0 '->l 0 N 0 -0 0
07/29/05
12/26/05
05/25/06
10/22/06
03/21/07
08/18/07
01/15/08
06/13/08
11/10/08
04/09/09
09/06/09
02/03/10
07/03/10
11/30/10
04/29/11
09/26/11
02/23/12
07/22/12
12/19/12
05/18/13
10/15/13
03/14/14
08/11/14
01/08/15
06/07/15
11/04/15
04/02/16
08/30/16
01/27/17
06/26/17
11/23/17
04/22/18
09/19/18
02/16/19
07/16/19
12/13/19
05/11/20
~ ! I N ~
~ ~ ;-
~
t:,
~ 't:S ~
0 <Id ~ ~
~ ... e ~ --?
C" 9 't:S --
Water Levels and Data over Time
White Mesa Mill -Well TW4-22
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,627.83 5,629.00 1.17 114.7
5,571.89 07/29/05 57.11 55.94
5,572.20 08/30/05 56.80 55.63
5,572.08 09/12/05 56.92 55.75
5,571.61 12/07/05 57.39 56.22
5,571.85 03/08/06 57.15 55.98
5,571.62 06/13/06 57.38 56.21
5,571.42 07/18/06 57.58 56.41
5,571.02 11/07/06 57.98 56.81
5571.24 02/27/07 57.76 56.59
5,570.75 06/29/07 58.25 57.08
5,571.82 08/14/07 57.18 56.01
5,571.99 10/10/07 57.01 55.84
5,573.05 03/26/08 55.95 54.78
5,573.04 06/24/08 55.96 54.79
5,573.04 08/26/08 55.96 54.79
5,573.02 10/14/08 55.98 54.81
5,573.19 03/10/09 55.81 54.64
5,573.32 06/24/09 55.68 54.51
5,573.17 09/10/09 55.83 54.66
5,573.52 12/11/09 55.48 54.31
5,573.88 03/11/10 55.12 53.95
5,574.29 05/11/10 54.71 53.54
5,574.88 09/29/10 54.12 52.95
5,574.44 12/21/10 54.56 53.39
5,574.49 02/28/11 54.51 53.34
5,574.97 06/21/11 54.03 52.86
5,575.06 09/20/11 53.94 52.77
5,575.69 12/21/11 53.31 52.14
5,575.61 03/27/12 53.39 52.22
5,575.62 06/28/12 53.38 52.21
5,575.90 09/27/12 53.10 51.93
5,575.59 12/28/12 53.41 52.24
5,573.50 03/28/13 55.50 54.33
5,572.45 06/27/13 56.55 55.38
5,572.25 09/27/13 56.75 55.58
5,569.93 12/20/13 59.07 57.90
5,569.36 03/27/14 59.64 58.47
5,569.02 06/25/14 59.98 58.81
5,570.00 09/25/14 59.00 57.83
5,568.60 12/17/14 60.40 59.23
5,557.00 03/26/15 72.00 70.83
5,570.93 06/22/15 58.07 56.90
Water Levels and Data over Time
White Mesa Mill -Well TW4-22
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,627.83 5,629.00 1.17 114.7
5,571.24 09/30/15 57.76 56.59
5,568.23 12/02/15 60.77 59.60
5,570.28 03/30/16 58.72 57.55
5,570.75 06/30/16 58.25 57.08
5,544.60 09/29/16 84.40 83.23
5,565.11 12/21/16 63.89 62.72
5,567.99 03/30/17 61.01 59.84
5,569.17 06/27/17 59.83 58.66
5,569.37 09/28/17 59.63 58.46
5,566.48 11/30/17 62.52 61.35
5,568.30 03/28/18 60.70 59.53
5,568.42 06/22/18 60.58 59.41
5,567.98 09/24/18 61.02 59.85
5,553.65 12/17/18 75.35 74.18
5,550.09 03/25/19 78.91 77.74
5,540.65 06/24/19 88.35 87.18
5,557.09 08/12/19 71.91 70.74
-8 \Ci 0
~
00 0
Depth Below Measuring Point (ft.)
c5 O'I 0
J
• •• ••
• •
't
•
'
•
• •
0
~
'
~
• 0
• •
0
•
0
•
~ •
~ ~ r--[l
4
l
~ •
~~
Vl 0
.j::,.
0
(.,.)
0
r ~
~ ....
N 0 -0 0
07/29/05
12/26/05
05/25/06
10/22/06
03/21/07
08/18/07
01/15/08
06/13/08
11/10/08
04/09/09
09/06/09
02/03/10
07/03/10
11/30/10
04/29/11
09/26/11
02/23/12
07/22/12
12/19/12
05/18/13
10/15/13
03/14/14
08/11/14
01/08/15
06/07/15
11/04/15
04/02/16
08/30/16
01/27/17
06/26/17
11/23/17
04/22/18
09/19/18
02/16/19
07/16/19
12/13/19
05/11/20
""'3 ~ .&;.
I N N
~ ..... ~ ""l
0 ~ "Cl ..... =--0 < ~ ""l
""'3 ... e ~ ,-.,
?
a" -e "Cl '--"
Water Levels and Data over Time
White Mesa Mill-Well TW4-23
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,605.77 5,607.37 1.60 116.4
5,538.89 09/13/07 68.48 66.88
5,538.80 10/10/07 68.57 66.97
5,539.25 11/30/07 68.12 66.52
5,539.49 12/11/07 67.88 66.28
5,539.19 01/08/08 68.18 66.58
5,539.44 02/18/08 67.93 66.33
5,539.54 03/26/08 67.83 66.23
5,539.71 04/23/08 67.66 66.06
5539.48 05/30/08 67.89 66.29
5,539.53 06/24/08 67.84 66.24
5,539.44 07/16/08 67.93 66.33
5,539.68 08/26/08 67.69 66.09
5,541.18 09/10/08 66.19 64.59
5,539.57 10/14/08 67.80 66.20
5,539.29 11/26/08 68.08 66.48
5,539.55 12/29/08 67.82 66.22
5,540.15 01/26/09 67.22 65.62
5,539.74 02/24/09 67.63 66.03
5,539.86 03/06/09 67.51 65.91
5,539.72 04/07/09 67.65 66.05
5,539.84 05/29/09 67.53 65.93
5,540.12 06/30/09 67.25 65.65
5,540.12 07/31/09 67.25 65.65
5,540.27 08/31/09 67.10 65.50
5,540.13 09/10/09 67.24 65.64
5,540.64 12/11/09 66.73 65.13
5,541.15 03/11/10 66.22 64.62
5,541.61 05/11/10 65.76 64.16
5,541.47 09/29/10 65.90 64.30
5,541.54 12/21/10 65.83 64.23
5,541.54 02/28/11 65.83 64.23
5,541.98 06/21/11 65.39 63.79
5,541.90 09/20/11 65.47 63.87
5,542.58 12/21/11 64.79 63.19
5,542.59 03/27/12 64.78 63.18
5,542.61 06/28/12 64.76 63.16
5,542.92 09/27/12 64.45 62.85
5,542.61 12/28/12 64.76 63.16
5,543.48 03/28/13 63.89 62.29
5,543.23 06/27/13 64.14 62.54
5,543.12 09/27/13 64.25 62.65
5,542.96 12/20/13 64.41 62.81
Water Levels and Data over Time
White Mesa Mill -Well TW4-23
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,605.77 5,607.37 1.60 116.4
5,542.35 03/27/14 65.02 63.42
5,541.42 06/25/14 65.95 64.35
5,540.65 09/25/14 66.72 65.12
5,540.34 12/17/14 67.03 65.43
5,539.47 03/26/15 67.90 66.30
5,539.22 06/22/15 68.15 66.55
5,538.82 09/30/15 68.55 66.95
5,538.28 12/02/15 69.09 67.49
5,538.29 03/30/16 69.08 67.48
5,537.60 06/30/16 69.77 68.17
5,537.07 09/29/16 70.30 68.70
5,536.86 12/21/16 70.51 68.91
5,536.91 03/30/17 70.46 68.86
5,536.49 06/27/17 70.88 69.28
5,536.18 09/28/17 71.19 69.59
5,535.72 11/30/17 71.65 70.05
5,535.62 03/28/18 71.75 70.15
5,535.34 06/22/18 72.03 70.43
5,534.93 09/25/18 72.44 70.84
5,534.64 12/17/18 72.73 71.13
5,534.23 03/25/19 73.14 71.54
5,534.22 06/24/19 73.15 71.55
5,534.01 08/12/19 73 .36 71.76
-.....}
.fa. -J N
Depth Below Measuring Point (ft.)
-.....}
0 0\ 00 0\ 0\ i 0\ N
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10 ~
05/25/11 ~ ...
10/22/11 I N ~
03/20/12 ~ 08/17/12 """' ~ "'1
01/14/13 ~ ~
06/13/13 "Cl g.
11/10/13 0 -< 04/09/14 ~ "'1
09/06/14 ~ ... a
02/03/15 ~ --07/03/15 ?
C"
11/30/15 -a
04/28/16 "Cl ..._,
09/25/16
02/22/17
07/22/17
12/19/17
05/18/18
10/15/18
03/14/19
08/11/19
01/08/20
06/06/20
Water Levels and Data over Time
White Mesa Mill-Well TW4-24
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.70 5,627.83 2.13 114.8
5,570.61 09/13/07 57.22 55.09
5,570.53 10/10/07 57.30 55.17
5,571.16 11/30/07 56.67 54.54
5,571.30 12/11/07 56.53 54.40
5,571.03 01/08/08 56.80 54.67
5,571.22 02/18/08 56.61 54.48
5,571.43 03/26/08 56.40 54.27
5,571.68 04/23/08 56.15 54.02
5571.52 05/30/08 56.31 54.18
5,571.34 06/24/08 56.49 54.36
5,571.28 07/16/08 56.55 54.42
5,571.34 08/26/08 56.49 54.36
5,571.23 09/10/08 56.60 54.47
5,571.12 10/14/08 56.71 54.58
5,570.95 11/26/08 56.88 54.75
5,570.92 12/29/08 56.91 54.78
5,571.65 01/26/09 56.18 54.05
5,571.31 02/24/09 56.52 54.39
5,571.37 03/06/09 56.46 54.33
5,571.21 04/07/09 56.62 54.49
5,571.23 05/29/09 56.60 54.47
5,571.42 06/30/09 56.41 54.28
5,571.38 07/31/09 56.45 54.32
5,571.48 08/31/09 56.35 54.22
5,571.28 09/10/09 56.55 54.42
5,571.64 12/11/09 56.19 54.06
5,571.86 03/11/10 55.97 53.84
5,571.91 05/11/10 55.92 53.79
5,572.18 09/29/10 55.65 53.52
5,571.86 12/21/10 55.97 53.84
5,571.78 02/28/11 56.05 53.92
5,572.40 06/21/11 55.43 53.30
5,572.19 09/20/11 55.64 53.51
5,573.02 12/21/11 54.81 52.68
5,573.03 03/27/12 54.80 52.67
5,573.02 06/28/12 54.81 52.68
5,573.13 09/27/12 54.70 52.57
5,573.05 12/28/12 54.78 52.65
5,566.53 03/28/13 61.30 59.17
5,564.63 06/27/13 63.20 61.07
5,570.01 09/27/13 57.82 55.69
5,566.85 12/20/13 60.98 58.85
5,562.33 03/27/14 65.50 63.37
Water Levels and Data over Time
White Mesa Mill -Well TW4-24
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.70 5,627.83 2.13 114.8
5,563.43 06/25/14 64.40 62.27
5,563.43 09/25/14 64.40 62.27
5,560.97 12/17/14 66.86 64.73
5,561.95 03/26/15 65.88 63.75
5,565.38 06/22/15 62.45 60.32
5,562.61 09/30/15 65 .22 63.09
5,560.91 12/02/15 66.92 64.79
5,563.69 03/30/16 64.14 62.01
5,565.64 06/30/16 62.19 60.06
5,565.35 09/29/16 62.48 60.35
5,563.33 12/21/16 64.50 62.37
5,565.27 03/30/17 62.56 60.43
5,565.86 06/27/17 61.97 59.84
5,565.21 09/28/17 62.62 60.49
5,559.24 11/30/17 68.59 66.46
5,564.78 03/28/18 63.05 60.92
5,564.83 06/22/18 63.00 60.87
5,565.47 09/24/18 62.36 60.23
5,549.72 12/17/18 78.11 75.98
5,559.52 03/25/19 68.31 66.18
5,546.68 06/24/19 81.15 79.02
5,549.54 08/12/19 78.29 76.16
\0 0 0
00 0
0
-.J 0
0
Depth Below Measuring Point (ft.)
~
0
VI
0 0
~ 0
0
u.l 0
0
N 0
0
-0
0
0 0
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10 ~
05/25/11 ~ ...
10/22/11 I N ...
03/20/12 ~
08/17/12 -~ "'1
01/14/13 ~ ~
06/13/13 "C -=-11/10/13 0 ~
04/09/14 ~ "'1
09/06/14 ~ .... e 02/03/15 ~ -.
07/03/15 ?
C"
11/30/15 -e
04/28/16 "C --
09/25/16
02/22/17
07/22/17
12/19/17
05/18/18
10/15/18
03/14/19
08/11/19
01/08/20
06/06/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-25
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,642.82 5,644.91 2.09 136.7
5,601.86 09/13/07 43.05 40.96
5,601.89 10/10/07 43.02 40.93
5,602.57 11/30/07 42.34 40.25
5,602.82 12/11/07 42.09 40.00
5,601.94 01/08/08 42.97 40.88
5,599.13 02/18/08 45.78 43.69
5,597.11 03/26/08 47.80 45.71
5,595.51 04/23/08 49.40 47.31
5594.42 05/30/08 50.49 48.40
5,594.26 06/24/08 50.65 48.56
5,586.67 07/16/08 58.24 56.15
5,594.17 08/26/08 50.74 48.65
5,594.23 09/10/08 50.68 48.59
5,594.12 10/14/08 50.79 48.70
5,594.06 11/26/08 50.85 48.76
5,594.87 12/29/08 50.04 47.95
5,595.89 01/26/09 49.02 46.93
5,596.27 02/24/09 48.64 46.55
5,596.47 03/06/09 48.44 46.35
5,596.74 04/07/09 48.17 46.08
5,597.55 05129/09 47.36 45.27
5,598.11 06/30/09 46.80 44.71
5,598.22 07/31/09 46.69 44.60
5,598.52 08/31/09 46.39 44.30
5,598.49 09/10/09 46.42 44.33
5,599.48 12/11/09 45.43 43.34
5,599.75 03/11/10 45.16 43.07
5,599.63 05/11/10 45.28 43.19
5,598.68 09/29/10 46.23 44.14
5,598.66 12/21/10 46.25 44.16
5,598.18 02/28/11 46.73 44.64
5,598.61 06/21/11 46.30 44.21
5,598.08 09/20/11 46.83 44.74
5,598.23 12/21/11 46.68 44.59
5,597.41 03/27/12 47.50 45.41
5,597.41 06/28/12 47.50 45.41
5,595.60 09/27/12 49.31 47.22
5,597.41 12/28/12 47.50 45.41
5,597.43 03/28/13 47.48 45.39
5,587.61 06/27/13 57.30 55.21
5,585.91 09/27/13 59.00 56.91
5,561.00 12/20/13 83.91 81.82
Water Levels and Data over Time
White Mesa Mill -Well TW4-25
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,642.82 5,644.91 2.09 136.7
5,584.79 03/27/14 60.12 58.03
5,582.44 06/25/14 62.47 60.38
5,583.95 09/25/14 60.96 58.87
5,581.13 12/17/14 63.78 61.69
5,587.40 03/26/15 57.51 55.42
5,581.91 06/22/15 63.00 60.91
5,581.40 09/30/15 63.51 61.42
5,578.42 12/02/15 66.49 64.40
5,579.42 03/30/16 65.49 63.40
5,579.25 06/30/16 65.66 63.57
5,579.68 09/29/16 65.23 63.14
5,577.73 12/21/16 67.18 65.09
5,584.44 03/30/17 60.47 58.38
5,580.19 06/27/17 64.72 62.63
5,573.63 09/28/17 71.28 69.19
5,577.88 11/30/17 67.03 64.94
5,543.71 03/28/18 101.20 99.11
5,575.26 06/22/18 69.65 67.56
5,578.78 09/24/18 66.13 64.04
5,567.86 12/17/18 77.05 74.96
5,572.46 03/25/19 72.45 70.36
5,571.58 06/24/19 73.33 71.24
5,572.15 08/12/19 72.76 70.67
--N 0 0 0
Depth Below Measuring Point (ft.)
00 0 °' 0 ~ N 0 0
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10 ""'3
05/25/11 ~ .&;.
10/22/11 I N Ul
03/20/12 ~
08/17/12 ~ ~ "1
01/14/13 0 ~
06/13/13 "e ~ ::r
11/10/13 0 < 04/09/14 ~ "1
09/06/14 ""'3 .... a
02/03/15 ~ --07/03/15 ?
-r:
11/30/15 -a
04/28/16 "e '--'
09/25/16
02/22/17
07/22/17
12/19/17
05/18/18
10/15/18
03/14/19
08/11/19
01/08/20
06/06/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-26
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,599.98 5,601.68 1.70 87.7
5,536.90 06/14/10 64.78 63.08
5,536.95 09/29/10 64.73 63.03
5,537.17 12/21/10 64.51 62.81
5,537.16 02/28/11 64.52 62.82
5,537.57 06/21/11 64.11 62.41
5,537.59 09/20/11 64.09 62.39
5,538.16 12/21/11 63.52 61.82
5,538.18 03/27/12 63.50 61.80
5538.23 06/28/12 63.45 61.75
5,538.57 09/27/12 63.11 61.41
5,538.20 12/28/12 63.48 61.78
5,539.13 03/28/13 62.55 60.85
5,539.00 06/27/13 62.68 60.98
5,538.94 09/27/13 62.74 61.04
5,538.97 12/20/13 62.71 61.01
5,538.53 03/27/14 63.15 61.45
5,537.85 06/25/14 63.83 62.13
5,537.33 09/25/14 64.35 62.65
5,537.14 12/17/14 64.54 62.84
5,536.43 03/26/15 65.25 63.55
5,536.16 06/22/15 65.52 63.82
5,535.76 09/30/15 65.92 64.22
5,535.23 12/02/15 66.45 64.75
5,535.15 03/30/16 66.53 64.83
5,534.61 06/30/16 67.07 65.37
5,534.12 09/29/16 67.56 65.86
5,533.96 12/21/16 67.72 66.02
5,533.97 03/30/17 67.71 66.01
5,533.66 06/27/17 68.02 66.32
5,533.43 09/28/17 68.25 66.55
5,533.39 11/30/17 68.29 66.59
5,532.99 03/28/18 68.69 66.99
5,532.74 06/22/18 68.94 67.24
5,532.32 09/25/18 69.36 67.66
5,532.04 12/17/18 69.64 67.94
5,531.48 03/25/19 70.20 68.50
5,531.20 06/24/19 70.48 68.78
5,530.96 08/12/19 70.72 69.02
-.J N 8
-.J -0 0
-.J 0
8
Depth Below Measuring Point (ft.)
°' \0
8 °' 00
0 0
°' -.J
8 °' °' 8 °' v-,
0 0
~
8 °' u.)
0 0
°' N
8
08/25/09
01/22/10
06/21/10
11/18/10
04/17/11
09/14/11
02/11/12
07/10/12 ~ ~
12/07/12 ,&;;;.. I N 0,.,
05/06/13 ~
10/03/13 '""' tti "'1
03/02/14 ~ tti "'Q
'""' 07/30/14 =-0
12/27/14 ~ tti "'1
05/26/15 ~ ....
9
10/23/15 tti .-.. ?
03/21/16 O"' -
08/18/16 9 "'Q ..._,
01/15/17
06/14/17
11/11/17
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-27
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,606.19 5,607.94 1.75 95.75
5,517.78 12/21/11 90.16 88.41
5,524.84 03/27/12 83.10 81.35
5,524.93 06/28/12 83.01 81.26
5,525.59 09/27/12 82.35 80.60
5,524.86 12/28/12 83.08 81.33
5,526.37 03/28/13 81.57 79.82
5,526.29 06/27/13 81.65 79.90
5,527.04 09/27/13 80.90 79.15
5,527.14 12/20/13 80.80 79.05
5,527.55 03/27/14 80.39 78.64
5,527.43 06/25/14 80.51 78.76
5,527.48 09/25/14 80.46 78.71
5,527.81 12/17/14 80.13 78.38
5,527.71 03/26/15 80.23 78.48
5,527.86 06/22/15 80.08 78.33
5,528.13 09/30/15 79.81 78.06
5,527.92 12/02/15 80.02 78.27
5,528.59 03/30/16 79.35 77.60
5,528.34 06/30/16 79.60 77.85
5,528.32 09/29/16 79.62 77.87
5,528.44 12/21/16 79.50 77.75
5,528.85 03/30/17 79.09 77.34
5,528.81 06/27/17 79.13 77.38
5,528.84 09/28/17 79.10 77.35
5,528.85 11/29/17 79.09 77.34
5,529.14 03/28/18 78.80 77.05
5,529.06 06/21/18 78.88 77.13
5,529.18 09/25/18 78.76 77.01
5,529.09 12/17/18 78.85 77.10
5,528.96 03/25/19 78.98 77.23
5,529.20 06/24/19 78.74 76.99
5,529.24 08/12/19 78.70 76.95
ID t,J
0 0
ID 0
0 0
Depth Below Measuring Point (ft.)
00 00
0 0
00
CTI
0 0
00 .i:,.
0 0
00 t,J
0 0
00 '-I 0 00
0 0 0 0
04/17/11
09/14/11
02/11/12
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14 ~ ~ ,&;:..
07/30/14 I N .....J
12/27/14 ~ """ ~
05/26/15 "'1
0 ~
10/23/15 "CS """ =-
03/21/16 0 ~ ~ "'1
08/18/16 ~ ....
9
01/15/17 ~ ,-..,
?
06/14/17 C" -9
11/11/17 "CS --
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
Water Levels and Data over Time
White Mesa Mill -Well TW4-28
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,613.52 5,617.00 3.48 108.48
5,580.69 03/28/13 36.31 32.83
5,580.30 06/27/13 36.70 33.22
5,580.35 09/27/13 36.65 33.17
5,580.25 12/20/13 36.75 33.27
5,579.83 03/27/14 37.17 33.69
5,579.21 06/25/14 37.79 34.31
5,578.84 09/25/14 38.16 34.68
5,578.72 12/17/14 38.28 34.80
5,578.11 03/26/15 38.89 35.41
5,577.83 06/22/15 39.17 35.69
5,577.56 09/30/15 39.44 35.96
5,577.27 12/02/15 39.73 36.25
5,577.25 03/30/16 39.75 36.27
5,576.75 06/30/16 40.25 36.77
5,576.36 09/29/16 40.64 37.16
5,576.13 12/21/16 40.87 37.39
5,575.92 03/30/17 41.08 37.60
5,575.50 06/27/17 41.50 38.02
5,575.08 09/28/17 41.92 38.44
5,574.80 11/29/17 42.20 38.72
5,574.36 03/28/18 42.64 39.16
5,573.92 06/22/18 43.08 39.60
5,572.37 09/25/18 44.63 41.15
5,571.74 12/17/18 45.26 41.78
5,570.65 03/25/19 46.35 42.87
5,570.60 06/24/19 46.40 42.92
5,570.24 08/12/19 46.76 43.28
Vl 0
8
~ Vl
8
.l
• ~
~
•
Depth Below Measuring Point (ft.)
~ W W N N ,_. 0 Vl O Vl O Vl o o o o o o 0 0 0 0 0 0
~
•
••
' .
'
0
0
•
• •
•
'
0
•
•
.....
0
8
Vl
0 0
0
8
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14
05/26/15
10/23/15
03/21/16
08/18/16
01/15/17
06/14/17
11/11/17
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
~ ~ ,i;;;..
I N 00
~ ~ ~ '"'l
t,
~ "'C ~ =-0 ~ ~ '"'l
~ -· e ~ ,-..
?
C" -e "'C '-"
Water Levels and Data over Time
White Mesa Mill -Well TW4-29
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,602.56 5,606.04 3.48 94.48
5,533.98 03/28/13 72.06 68.58
5,533.84 06/27/13 72.20 68.72
5,534.27 09/27/13 71.77 68.29
5,534.43 12/20/13 71.61 68.13
5,534.32 03/27/14 71.72 68.24
5,533.85 06/25/14 72.19 68.71
5,533.53 09/25/14 72.51 69.03
5,533.60 12/17 /14 72.44 68.96
5,533.04 03/26/15 73.00 69.52
5,532.93 06/22/15 73.11 69.63
5,532.79 09/30/15 73.25 69.77
5,532.34 12/02/15 73.70 70.22
5,532.54 03/30/16 73.50 70.02
5,532.01 06/30/16 74.03 70.55
5,531.58 09/29/16 74.46 70.98
5,531.49 12/21/16 74.55 71.07
5,531.60 03/30/17 74.44 70.96
5,531.24 06/27/17 74.80 71.32
5,530.95 09/28/17 75 .09 71.61
5,530.83 11/29/17 75.21 71.73
5,530.74 03/28/18 75.30 71.82
5,530.54 06/21/18 75.50 72.02
5,530.28 09/25/18 75.76 72.28
5,530.11 12/17/18 75.93 72.45
5,527.99 03/25/19 78.05 74.57
5,529.77 06/24/19 76.27 72.79
5,529.64 08/12/19 76.40 72.92
-....}
'° 0 0
-....}
00 0 0
Depth Below Measuring Point (ft.) ...J -....} -....} -....} -....} -....} ~ ~ ~ w g g g g g
-....} N g
-....} ......
0 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~ ~
12/27/14 ,I;,,,.
I N 'C
05/26/15 ~
"""' ('O
10/23/15 "'1
~ ('O
03/21/16 e,
0 08/18/16 < ('O
"'1
01/15/17 ~ .... a ('O
06/14/17 --~
C"' -11/11/17 a "O -04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-30
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monito1ing (blw.MP) (blw.LSD) Well
5,599.33 5,602.81 3.48 93.48
5,524.78 03/28/13 78.03 74.55
5,524.79 06/27/13 78 .02 74.54
5,525.54 09/27/13 77.27 73.79
5,525.81 12/20/13 77.00 73.52
5,525.98 03/27/14 76.83 73.35
5,525.91 06/25/14 76.90 73.42
5,526.00 09/25/14 76.81 73.33
5,526.41 12/17/14 76.40 72.92
5,526.23 03/26/15 76.58 73.10
5,526.48 06/22/15 76.33 72.85
5,526.74 09/30/15 76.07 72.59
5,526.56 12/02/15 76.25 72.77
5,527.26 03/30/16 75.55 72.07
5,527.04 06/30/16 75.77 72.29
5,526.97 09/29/16 75.84 72.36
5,527.17 12/21/16 75.64 72.16
5,527.65 03/30/17 75.16 71.68
5,527.54 06/27/17 75.27 71.79
5,527.56 09/28/17 75.25 71.77
5,527.59 11/29/17 75.22 71.74
5,527.88 03/28/18 74.93 71.45
5,527.86 06/21/18 74.95 71.47
5,525.76 09/25/18 77.05 73.57
5,527.87 12/17/18 74.94 71.46
5,527.69 03/25/19 75.12 71.64
5,528.01 06/24/19 74.80 71.32
5,528.04 08/12/19 74.77 71.29
Depth Below Measuring Point (ft.)
-...I -...I -...I -...I -...I -...I -...I -...I -...I 00 00 -...I -...I °'" °'" VI VI f', Vl 0 Vl 0 Vl 8 Vl 0 VI 0 0 0 0 0 0 0 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~ ~ ,I;;;,.
12/27/14 I ~ =
05/26/15 ~
"""' ~ "'1 10/23/15 ~ ~ "'C
03/21/16 ;.
0
08/18/16 ~ ~ "'1
~ 01/15/17 ....
9 ~
06/14/17 ,-._
?
'a' -11/11/17 9 "'C ---04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
Water Levels and Data over Time
White Mesa Mill-Well TW4-31
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,601.10 5,604.58 3.48 107.48
5,520.17 03/28/13 84.41 80.93
5,520.36 06/27/13 84.22 80.74
5,521.22 09/27/13 83.36 79.88
5,521.81 12/20/13 82.77 79.29
5,522.25 03/27/14 82.33 78.85
5,522.32 06/25/14 82.26 78.78
5,522.64 09/25/14 81.94 78.46
5,523.27 12/17/14 81.31 77.83
5,523.33 03/26/15 81.25 77.77
5,523.82 06/22/15 80.76 77.28
5,524.34 09/30/15 80.24 76.76
5,524.29 12/02/15 80.29 76.81
5,525.32 03/30/16 79.26 75.78
5,525.33 06/30/16 79.25 75.77
5,525.43 09/29/16 79.15 75.67
5,525.81 12/21/16 78.77 75.29
5,526.48 03/30/17 78.10 74.62
5,526.53 06/30/17 78.05 74.57
5,526.68 09/28/17 77.90 74.42
5,526.82 11/29/17 77.76 74.28
5,527.28 03/28/18 77.30 73.82
5,527.36 06/21/18 77.22 73.74
5,529.67 09/25/18 74.91 71.43
5,527.58 12/17/18 77.00 73.52
5,527.53 03/25/19 77.05 73.57
5,527.94 06/24/19 76.64 73.16
5,528.03 08/12/19 76.55 73.07
00 0\ 8
00 .j:>.
8
Depth Below Measuring Point (ft.)
00 N 8
00 0 8
-.J 00
8
-.J -.J 0\ .j:>.
0 8 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14 ~
07/30/14 ~ .&;.
I ~ ~
12/27/14 ~ -05/26/15 t,
""1
~
10/23/15 t,
"'Cl -=-03/21/16 0 < t,
08/18/16 ""1
~ ....
01/15/17 a t,
,.-..
06/14/17 ?
-r::r
11/11/17 e
"'Cl '-"
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.20 5,611.84 1.64 114.64
5,564.43 09/27/13 47.41 45.77
5,563.74 12/20/13 48.10 46.46
5,563.24 03/27/14 48.60 46.96
5,562.43 06/25/14 49.41 47.77
5,561.90 09/25/14 49.94 48.30
5,560.93 12/17/14 50.91 49.27
5,561.35 03/26/15 50.49 48.85
5,561.15 06/22/15 50.69 49.05
5,560.96 09/30/15 50.88 49.24
5,560.58 12/02/15 51.26 49.62
5,560.85 03/30/16 50.99 49.35
5,560.25 06/30/16 51.59 49.95
5,559.69 09/29/16 52.15 50.51
5,559.75 12/21/16 52.09 50.45
5,560.14 03/30/17 51.70 50.06
5,559.44 06/27/17 52.40 50.76
5,558.99 09/28/17 52.85 51.21
5,558.84 11/29/17 53.00 51.36
5,558.85 03/28/18 52.99 51.35
5,558.52 06/22/18 53.32 51.68
5,557.92 09/25/18 53.92 52.28
5,557.89 12/17/18 53.95 52.31
5,557.24 03/25/19 54.60 52.96
5,557.41 06/24/19 54.43 52.79
5,557.03 08/12/19 54.81 53.17
Ul O'I
8
Ul Ul
0 0
Ul .i:,..
8
Depth Below Measuring Point (ft.)
Ul w
8
Ul N
8
Ul _.
8
Ul 0 0 0
.i:,.. \0 0 0
.i:,.. .i:,..
00 -....)
8 8
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14
05/26/15
10/23/15
03/21/16
08/18/16
01/15/17
06/14/17
11/11/17
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
~ ~ I ~ N
~ ;'
"1
~ ~ "O ;.
0 < ~ "1
~ ....
9 ~ --?
a-§"
"O --
Water Levels and Data over Time
White Mesa Mill -Well TW 4-33
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,605.20 5,606.73 1.53 86.23
5,536.70 09/27/13 70.03 68.50
5,536.62 12/20/13 70.11 68.58
5,536.49 03/27/14 70.24 68.71
5,536.06 06/25/14 70.67 69.14
5,535.73 09/25/14 71.00 69.47
5,535.73 12/17/14 71.00 69.47
5,535.14 03/26/15 71.59 70.06
5,534.98 06/22/15 71.75 70.22
5,534.81 09/30/15 71.92 70.39
5,534.34 12/02/15 72.39 70.86
5,534.33 03/30/16 72.40 70.87
5,533.90 06/30/16 72.83 71.30
5,533.48 09/29/16 73.25 71.72
5,533.39 12/21/16 73.34 71.81
5,533.28 03/30/17 73.45 71.92
5,533.01 06/27/17 73.72 72.19
5,532.67 09/28/17 74.06 72.53
5,532.53 11/29/17 74.20 72.67
5,532.37 03/28/18 74.36 72.83
5,532.13 06/21/18 74.60 73.07
5,531.82 09/25/18 74.91 73.38
5,531.61 12/17/18 75.12 73.59
5,531.14 03/25/19 75.59 74.06
5,531.08 06/24/19 75.65 74.12
5,530.98 08/12/19 75.75 74.22
-.J -.J
8
-.J 0\
8
-.J Vl
0 0
Depth Below Measuring Point (ft.)
-.J .j:::..
8
-.J v.l
0 0
-.J N
8
-.J .....
0 0
-.J 0\ 0 \0
0 0 0 0
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14 ~ ~ ,&;:..
I
05/26/15 ~ ~
~ 10/23/15 -('r>
"'1
t::,
03/21/16 ('r>
"Cl -=-
08/18/16 0 -od ('r>
"'1
01/15/17 ~ ... 9 ('r> --06/14/17 ~
O"" -11/11/17 9 "Cl '-'
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
Water Levels and Data over Time
White Mesa Mill -Well TW 4-34
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,601.60 5,603.34 1.74 95.74
5,534.04 09/27/13 69.30 67.56
5,534.14 12/20/13 69.20 67.46
5,533.89 03/27/14 69.45 67.71
5,533.32 06/25/14 70.02 68.28
5,532.94 09/25/14 70.40 68.66
5,532.99 12/17/14 70.35 68.61
5,532.37 03/26/15 70.97 69.23
5,532.24 06/22/15 71.10 69.36
5,532.08 09/30/15 71.26 69.52
5,531.79 12/02/15 71.55 69.81
5,531.80 03/30/16 71.54 69.80
5,531.28 06/30/16 72.06 70.32
5,530.87 09/29/16 72.47 70.73
5,530.74 12/21/16 72.60 70.86
5,530.79 03/30/17 72.55 70.81
5,530.43 06/27/17 72.91 71.17
5,530.12 09/28/17 73.22 71.48
5,530.01 11/29/17 73.33 71.59
5,529.84 03/28/18 73.50 71.76
5,529.64 06/21/18 73.70 71.96
5,529.39 09/25/18 73.95 72.21
5,529.23 12/17/18 74.11 72.37
5,528.83 03/25/19 74.51 72.77
5,528.84 06/24/19 74.50 72.76
5,528.75 08/12/19 74.59 72.85
--Q. e -,,t:J.
~ '-'
~ e ... ~
'"' ~ ;...
0
..c= ....
Q. ~
Q
'"' ~ .... t
""' ~ I
""' ~ ~
61/170/ZO
ll/ZZ/60
91/01/!;0
tl/LZ/ZI
£1/tl/80
~
00 \0
8 0 r-
0 0 "<t' r-
Water Levels and Data over Time
White Mesa Mill -Well TW 4-35
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,598.67 5,599.87 1.20 86.5
5,525.52 09/25/14 74.35 73.15
5,525.72 12/17 /14 74.15 72.95
5,525.56 03/26/15 74.31 73.11
5,525.67 06/22/15 74.20 73.00
5,525.81 09/30/15 74.06 72.86
5,525.57 12/02/15 74.30 73.10
5,526.01 03/30/16 73.86 72.66
5,525.75 06/30/16 74.12 72.92
5,525.57 09/29/16 74.30 73.10
5,525.62 12/21/16 74.25 73.05
5,525.87 03/30/17 74.00 72.80
5,525.70 06/27/17 74.17 72.97
5,525.57 09/28/17 74.30 73.10
5,525.56 11/29/17 74.31 73.11
5,525.64 03/28/18 74.23 73.03
5,525.56 06/21/18 74.31 73.11
5,525.46 09/25/18 74.41 73.21
5,525.37 12/17/18 74.50 73.30
5,525.12 03/25/19 74.75 73.55
5,525.35 06/24/19 74.52 73.32
5,525.31 08/12/19 74.56 73.36
61/S'l/S'O
81/LZ/Ol
--Q.i e 81/01/170 -.Q
¢:
'-'
~ e ll/ZZ/60 .... ~ -~ ;...
0 l 1/90/£0 -= -Q.i ~ Q -~ 91/81/80 -~
I.()
~ I "'!' 91/1£/10 ~ ~
S'l/S'l/ LO
171/LZ/Zl
tl/01/90
0 0 0 0 0 0 0 0 0 0 0 00 ~ 0 -N C') -.::t" ,ri I.O t-00
C') C') ~ ~ ~ ~ ~ ~ ~ ~ ~ t-t-t-t-t-t-t-t-t-t-t-
(':y:) lUfOd ~uµnsugw MOPS: qldga
Water Levels and Data over Time
White Mesa Mill -Well TW 4-36
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,615.18 5,616.59 1.41 99.41
5,559.14 09/25/14 57.45 56.04
5,559.77 12/17/14 56.82 55.41
5,559.79 03/26/15 56.80 55.39
5,560.08 06/22/15 56.51 55.10
5,560.18 09/30/15 56.41 55.00
5,559.95 12/02/15 56.64 55.23
5,560.53 03/30/16 56.06 54.65
5,560.20 06/30/16 56.39 54.98
5,560.00 09/29/16 56.59 55.18
5,560.04 12/21/16 56.55 55.14
5,560.43 03/30/17 56.16 54.75
5,560.26 06/27/17 56.33 54.92
5,560.12 09/28/17 56.47 55.06
5,560.07 11/29/17 56.52 55.11
5,560.18 03/28/18 56.41 55.00
5,560.11 06/22/18 56.48 55.07
5,560.14 09/25/18 56.45 55.04
5,559.78 12/17/18 56.81 55.40
5,559.43 03/25/19 57.16 55.75
5,559.61 06/24/19 56.98 55.57
5,559.55 08/12/19 57.04 55.63
6rn;vs-o
8I/LZ/Ol
---81/0I/170 Q.
8 -~
¢! .._,
~ ll/ZZ/60
8 .... ~
$.i ~ ~ LI/90/£0 0
..c= ....
Q. ~ Q
$.i 9I/8I/80 ~ .... ~
\C ~ 91/1£/10 I "" ~ ~
S'I/S'I/ LO
tl/LZ/Zl
tl/OI/90
0 0 0 0 0 0 0 0 0 0 ~ 0 N 'tj" \0 00 ~ C"J "": \0
or, ID ID ID ID ID r-r-r-r-..: or, or, or, or, or, or, or, or, or, or,
(":y:) lU!Od ~uµnsugw MOJgS: qldgQ
Water Levels and Data over Time
White Mesa Mill -Well TW 4-37
Total or
Measuring Measured
Water Point Depth to Total Depth
Elevation Land Surface Elevation Length Of Date Of Water to Water Total Depth
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Of Well
5,630.13 5,631.85 1.72 113.72
5,571.99 06/22/15 59.86 58.14
5,570.67 09/30/15 61.18 59.46
5,568.25 12/02/15 63.60 61.88
5,569.80 03/30/16 62.05 60.33
5,569.07 06/30/16 62.78 61.06
5,569.40 09/29/16 62.45 60.73
5,568.35 12/21/16 63.50 61.78
5,524.05 03/30/17 107.80 106.08
5,566.35 06/27/17 65.50 63.78
5,568.47 09/28/17 63.38 61.66
5,567.57 11/30/17 64.28 62.56
5,567.83 03/28/18 64.02 62.30
5,567.87 06/22/18 63.98 62.26
5,567.35 09/24/18 64.50 62.78
5,555.12 12/17/18 76.73 75.01
5,558.24 03/25/19 73.61 71.89
5,560.63 06/24/19 71.22 69.50
5,550.84 08/12/19 81.01 79.29
61/~l/~O
81/LZ/OI
,,-..,
Q.. e 81/01/170 -~
~ '-'
QJ e .... ~ l l/ZZ/60
~ QJ ~ 0
;i
Q.. ll/90/£0 QJ ~
~ QJ .... ~
r--91/81/80 ~ I ~ :s ~
91/1£/IO
~l/~l/LO
171/LZ/Zl
0 0 0 0 0 0 0 0 0 0 0 0 0 0
c:i c:i c:i c:i c:i c:i c:i N 'tj" \0 00 0 N
("u) lll!Od ~uµnst?;}Ji\I MOPS: q1dga --
Water Levels and Data over Time
White Mesa Mill -Well TW 4-38
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.82 5,629.99 1.17 113.92
5,576.59 12/21/16 53.40 52.23
5,576.62 03/30/17 53.37 52.20
5,576.07 06/27/17 53.92 52.75
5,577.49 09/28/17 52.50 51.33
5,575.68 11/30/17 54.31 53.14
5,574.69 03/28/18 55.30 54.13
5,574.25 06/22/18 55.74 54.57
5,573.63 09/25/18 56.36 55.19
5,572.31 12/17 /18 57.68 56.51
5,572.51 03/25/19 57.48 56.31
5,572.53 06/24/19 57.46 56.29
5,572.31 08/12/19 57.68 56.51
6 I/S'I/S'O
---Col a 81/LZ/OI -.c
¢! --a.> a .... ~
.i a.> ~ 0 81/01/tO
..= .,._
Col a.> ~
.i a.> .,._
~
QO LIIZZ/60 "" I "" ~ ~
LI/90/£0
91/81/80
0 0 0 0 0 0 0 0 ~ 0 ~ 0 0 ~ N ~ ,.,f, on '° r--= 00 on on on on on on on
("y) lll!Od ~foµnsl?,lW MOPS: q1dga
Water Levels and Data over Time
White Mesa Mill -Well TW 4-39
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.82 5,629.56 0.74 120.74
5,566.39 12/21/16 63.17 62.43
5,567.57 03/30/17 61.99 61.25
5,567.11 06/27/17 62.45 61.71
5,567.26 09/28/17 62.30 61.56
5,560.52 11/30/17 69.04 68.30
5,565.51 03/28/18 64.05 63.31
5,529.91 06/22/18 99.65 98.91
5,565.04 09/24/18 64.52 63.78
5,557.32 12/17/18 72.24 71.50
5,564.12 03/25/19 65.44 64.70
5,553.85 06/24/19 75.71 74.97
5,555.03 08/12/19 74.53 73.79
61/~l/~O
-Q. e 81/LZ/OI -,,t:J.
¢:
'-'
~ e .... ~
'"' ~ ;..,.
0 81/0l/tO
,fj
Q.
~ ~
'"' ~ ..... ~
°' LI/ZZ/60 ("')
I ~ ~ ~
LI/90/£0
9I/8I/80
0 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N "<:f" \0 00 0 N
("lJ) lUfOd guµnsugW MOpg l{ldgQ ...... ......
Water Levels and Data over Time
White Mesa Mill -Well TW 4-40
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (hlw.LSD) Well
5,595.66 5,597.58 1.92 86
5,531.12 03/28/18 66.46 64.54
5,530.83 06/22/18 66.75 64.83
5,530.34 09/25/18 67.24 65.32
5,530.06 12/17/18 67.52 65.60
5,529.52 03/25/19 68.06 66.14
5,527.69 06/24/19 69.89 67.97
5,526.98 08/12/19 70.60 68.68
61/ZZ/OI
61/~Z/~O
,-.,
~ .§
~
~ '-'
Q,) s .... ~
So. Q,> ;... 8I/9Z/ZI 0 ~ ,s
~ Q,>
~
So. Q,) ..... ~ = "" I
"" ~ ~
8I/6Z/LO
~
81/I0/£0
/
00 \0
V
~ V
V V
0 r-0 r-..... r-..... r-
Water Levels and Data over Time
White Mesa Mill -Well TW4-41
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,613.31 5,614.96 1.65 97.8
5,539.24 03/28/18 75.72 74.07
5,526.18 06/22/18 88.78 87.13
5,513.86 09/24/18 101.10 99.45
5,536.53 12/17/18 78.43 76.78
5,521.88 03/25/19 93.08 91.43
5,527.89 06/24/19 87.07 85.42
5,530.75 08/12/19 84.21 82.56
--~
= -..c
~ '-"
~
= .... ~
I,,;
~ ~ 0 -= .,._
~ ~ ~
I,,; ~ .,._
~
~ "" I "" ~ ~
611s;z1s;o
8l/9Z/ZI
8I/6Z/l0
0 0 N 0 00 8 ......
0 N ......
Water Levels and Data over Time
White Mesa Mill -Well TW 4-42
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,592.39 5,594.70 2.31 86.0
5,518.98 03/28/18 75.72 73.41
5,528.28 06/24/19 66.42 64 .11
5,527.90 08/12/19 66.80 64.49
,,-...
i:::l. a -,,t:J.
¢!
"--1
Q,j a ... ~
$,,; Q,j .....
0
,fi
i:::l. Q,j
~
$,,;
Q,j .... ~
N "" I ~ ~ ~
61/~Z/~O
8l/9Z/ZI
8l/6Z/LO
00 I.O 0 r-N r-00 r-
TabG
Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells over Time
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
MW-4 TW.~15 (forme:rly1MW~ -
Total
Pumped Total Pumped Total Total Total Total Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) Pumped (gal) Cone (liters) Total (ug) (grams) (pounds)
QI 2007 1307110 3370 4947411.4 l.6673E+10 16673 36.8 930510 1660 3521980.4 5846487381 5846 12.9
Q2 2007 81230 2000 307455.6 614911100 615 1.4 54400 300 205904.0 61771200 62 0.1
Q3 2007 100700 2600 381149.5 990988700 991 2.2 72080 1400 272822.8 381951920 382 0.8
Q4 2007 90830 2300 343791.6 790720565 791 1.7 61750 2000 233723.8 467447500 467 1.0
Ql 2008 83950 2400 317750.8 762601800 763 1.7 47780 930 180847.3 !68187989 168 0.4
Q2 2008 62780 2500 237622.3 594055750 594 1.3 44840 1300 169719.4 220635220 221 0.5
Q3 2008 81400 1800 308099.0 554578200 555 1.2 61280 630 231944.8 146125224 146 0.3
Q4 2008 91320 1700 345646.2 587598540 588 1.3 55700 630 210824.5 132819435 133 0.3
Ql 2009 90710 2200 343337.4 755342170 755 1.7 52970 950 200491.5 190466878 190 0.4
Q2 2009 450040 1800 1703401.4 3066122520 3066 6.8 58050 410 219719.3 90084892.5 90 0.2
Q3 2009 90420 2000 342239.7 684479400 684 1.5 57610 850 218053.9 185345773 185 0.4
Q4 2009 322380 1800 1220208.3 2196374940 2196 4.8 61960 1100 234518.6 257970460 258 0.6
QI 2010 68125 1600 257853.1 412565000 413 0.9 61320 780 232096.2 181035036 181 0.4
Q2 2010 84005.33 2100 317960.2 667716366 668 1.5 60500 1900 228992.5 435085750 435 1.0
Q3 2010 79859.l 1900 302266.7 574306718 574 1.3 63850 2200 241672.3 531678950 532 1.2
Q4 2010 90042.2 1500 340809.7 511214591 511 1.1 60180 970 227781.3 220947861 221 0.5
QI 2011 76247.6 1700 288597.2 490615182 491 1.1 55130 450 208667.l 93900172.5 94 0.2
Q2 2011 85849.3 1700 324939.6 552397321 552 1.2 55800.6 1800 211205.3 380169488 380 0.8
Q3 2011 85327.7 1700 322965.3 549041086 549 1.2 65618 720 248364.J 178822174 179 0.4
Q42011 89735.0 1600 339647.0 543435160 543 1.2 50191.3 1800 189974.1 341953327 342 0.8
Ql 2012 90376.4 1500 342074.7 513112011 513 I.I 31440.1 2400 119000.8 285601868 286 0.6
Q2 2012 90916.5 1400 344118.8 481766269 482 1.1 26701.2 3000 101064.l 303192353 303 0.7
Q3 2012 91607.0 1500 346732.5 520098743 520 I. I 25246 3100 95556.l 296223941 296 0.7
Q4 2012 78840.0 1300 298409.4 387932220 388 0.9 30797 1200 116566.6 139879974 140 0.3
QI 2013 62943.7 1670 238241.9 397863981 398 0.9 22650.7 2120 85732.9 181753747 182 0.4
Q2 2013 71187.3 1490 269443.9 401471456 401 0.9 25343.4 4030 95924.8 386576819 387 0.9
Q3 2013 72898.8 1520 275922.0 419401376 419 0.9 25763 2940 97513.0 286688088 287 0.6
Q4 2013 70340.4 1410 266238.4 375396164 375 0.8 24207.6 1410 91625.8 129192330 129 0.3
QI 2014 69833.8 1390 264320.9 367406097 367 0.8 23263.1 1400 88050.8 123271167 123 0.3
Q2 2014 71934.9 1390 272273.6 378460299 378 0.8 23757.5 1960 89922.1 176247390 176 0.4
Q3 2014 74788.2 1490 283073.3 421779272 422 0.9 24062.4 2120 91076.2 193081510 193 0.4
Q4 2014 63093.0 1440 238807.0 343882087 344 0.8 21875.8 2090 82799.9 173051797 173 0.4
QI 2015 76454.3 1400 289379.5 405131336 405 0.9 24004.9 1980 90858.5 179899922 180 0.4
Q2 2015 60714.7 1300 229805.1 298746681 299 0.7 27804.6 1980 105240.4 208376014 208 0.5
Q3 2015 89520.8 1290 338836.2 437098734 437 1.0 21042.0 2350 79644.0 187163330 187 0.4
Q4 2015 99633.4 1200 377112.4 452534903 453 1.0 19355.6 2680 73260.9 196339335 196 0.4
QI 2016 90882.1 1240 343988.7 426546048 427 0.9 19150.8 2650 72485.8 192087312 192 0.4
Q2 2016 96540.5 1580 365405.8 577341152 577 1.3 22105.7 2220 83670.1 185747565 186 0.4
Q3 2016 79786.4 1430 301991.5 431847879 432 1.0 17149.5 3190 64910.9 207065635 207 0.5
Q4 2016 85414.0 1470 323292.0 475239225 475 1.0 18541.6 2510 70180.0 176151690 176 0.4
QI 2017 76642.3 1450 290091.1 420632103 421 0.9 26107.0 1290 98815.0 127471344 127 0.3
Q2 2017 72299.8 1430 273654.7 391326282 391 0.9 25921 .8 2450 98114.0 240379332 240 0.5
Q3 2017 95349.3 1400 360897.1 505255941 505 I.I 27489.9 1230 104049.3 127980604 128 0.3
Q4 2017 106679.8 1320 403783.0 532993617 533 1.2 26445.8 2570 100097.4 257250197 257 0.6
Table G-1
-. -·-·· -· .. --------------
-~ TW~lS (f~rmerl.y ~-W -1:ota1
Pqrp~ 'H>"31 Puiftpejl To_~I Toi!l) Total _Tota!Pwn~ Total To~
~-<&.lW Gpnc Qitefy) Total(ug) ~) :(e<>~ds) Ptim~(gal) {::~-"~-(litef:s) Total (ug) ~') {i>;owl~)
Ql 2018 105060.4 1320 397653.6 524902770 525 1.2 27004.7 1210 102212.8 123677475 124 0.3
Q2 2018 101786.2 1240 385260.8 477723351 478 1.1 26654.7 1870 100888.0 188660634 189 0.4
Q3 2018 95480.5 1300 361393.7 469811800 470 1.0 25536.1 1680 96654.1 162378953 162 0.4
Q4 2018 102884.8 1330 389418.9 517927177 518 1.1 23791.3 1480 90050.1 133274104 133 0.3
Ql 2019 111746.9 1190 422962.0 503324800 503 1.1 26798.5 1110 101432.3 112589878 113 0.2
Q2 2019 94540.7 1300 357836.5 465187514 465 1.0 24050.2 1280 91030.0 116518409 117 0.3
Q3 2019 95517.7 1180 361534.5 426610704 427 0.9 24181.1 1360 91525.5 124474630 124 0.3
Totals 6157755.77 102.1 2789763.5 36.2
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-19 TW4-20 .. --. -
I Total
Pumped Total Pumped Total Total Total Total Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) Pumped (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 6768986 2660 25620612.0 68150827947 68151 150.2 642290 16240 2431067.7 3.9481E+l0 39481 87.0
Q2 2007 605400 8 2291439.0 18331512 18 0.0 163520 1800 618923.2 1114061760 1114 2.5
Q3 2007 316080 llOO 1196362.8 1315999080 1316 2.9 70360 5200 266312.6 1384825520 1385 3.1
Q4 2007 334350 1100 1265514.8 1392066225 1392 3.1 63630 9000 240839.6 2167555950 2168 4.8
Ql 2008 304784 1800 1153607.4 2076493392 2076 4.6 66520 13000 251778.2 3273ll6600 3273 7.2
Q2 2008 380310 1000 1439473.4 1439473350 1439 3.2 39360 30000 148977.6 4469328000 4469 9.9
Q3 2008 529020 3600 2002340.7 7208426520 7208 15.9 53260 21000 201589.1 4233371100 4233 9.3
Q4 2008 589620 4200 2231711.7 9373189140 9373 20.7 50230 1000 190120.6 190120550 190 0.4
QI 2009 469100 llOO 1775543.5 1953097850 1953 4.3 52050 8200 197009.3 1615475850 1615 3.6
Q2 2009 450040 990 1703401.4 1686367386 1686 3.7 49270 6800 186487.0 1268111260 1268 2.8
Q3 2009 200650 6600 759460.3 5012437650 5012 I I.I 51030 13000 193148.6 2510931150 2511 5.5
Q4 2009 454205 4700 1719165.9 8080079848 8080 17.8 208790 15000 790270.2 l.1854E+IO 11854 26.1
Ql 2010 348550 940 1319261.8 1240106045 1240 2.7 14490 3500 54844.7 191956275 192 0.4
Q2 2010 453340 1800 1715891.9 3088605420 3089 6.8 39014.86 18000 147671.2 2658082412 2658 5.9
Q3 2010 116899.2 2000 442463.5 884926944 885 2.0 39098.3 15000 147987.1 2219805983 2220 4.9
Q4 2010 767970.5 1200 2906768.3 3488122011 3488 7.7 36752.5 24000 139108.2 3338597100 3339 7.4
QI 2011 454607.9 3400 1720690.9 5850349065 5850 12.9 37187.5 31000 140754.7 4363395313 4363 9.6
Q2 2011 159238.9 4000 602719.2 2410876946 2411 5.3 67907.7 8100 257030.6 2081948220 2082 4.6
Q32011 141542.6 970 535738.7 519666578.8 520 I.I 72311.2 6800 273697.9 1861145666 1861 4.1
Q42011 147647.2 2200 558844.7 1229458234 1229 2.7 72089.3 7900 272858.0 2155578204 2156 4.8
Ql 2012 148747 650 563007.4 365954806.8 366 0.8 76306 11000 288818.2 3177000310 3177 7.0
Q2 2012 172082.03 460 651330.5 299612022.4 300 0.7 22956.43 36000 86890.1 3128043152 3128 6.9
Q3 2012 171345 950 648540.8 616113783.8 616 1.4 22025 13000 83364.6 1083740125 1084 2.4
Q4 2012 156653 1500 592931.6 889397407.5 889 2.0 20114 19000 76131.5 1446498310 1446 3.2
Ql 2013 210908 4210 798286.8 3360787344 3361 7.4 18177 18500 68799.9 1272798983 1273 2.8
Q2 2013 226224 2070 856257.8 1772453729 1772 3.9 20252.4 26300 76655.3 2016035284 2016 4.4
Q3 2013 329460.l 8100 1247006.5 10100752476 10101 22.3 19731 26800 74681.8 2001473178 2001 4.4
Q4 2013 403974 942 1529041.6 1440357178 1440 3.2 19280.2 15700 72975.6 1145716245 1146 2.5
Ql 2014 304851 586 1153861.0 676162566.5 676 1.5 18781.6 17800 71088.4 1265372737 1265 2.8
Q2 2014 297660.0 810 1126643.1 912580911 913 2.0 18462.4 22100 69880.2 1544352066 1544 3.4
Q3 2014 309742.0 1410 1172373.5 1653046593 1653 3.6 17237.9 12400 65245.5 809043599 809 1.8
Q4 2014 198331.0 4310 750682.8 3235443019 3235 7.1 16341.8 23300 61853.7 1441191513 1441 3.2
Ql 2015 60553.0 4660 229193.1 1068039869 1068 2.4 15744.7 19900 59593.7 1185914421 1186 2.6
Q2 2015 75102.8 1570 284264.1 446294633.9 446 1.0 18754.l 17600 70984.3 1249323126 1249 2.8
Q3 2015 116503.9 7860 440967.3 3466002675 3466 7.6 17657.3 17000 66832.9 1136158969 1136 2.5
Q4 2015 112762.7 7840 426806.8 3346165465 3346 7.4 15547.4 17000 58846.9 1000397453 1000 2.2
Ql 2016 ll6597.0 7780 441319.6 3433466838 3433 7.6 14353.5 21600 54328.0 1173484746 1173 2.6
Q2 2016 123768.0 12600 468461.9 5902619688 5903 13.0 15818.3 33700 59872.3 2017695347 2018 4.4
Q3 2016 103609.0 6040 392160.l 2368646793 2369 5.2 12186.6 23600 46126.3 1088580232 1089 2.4
Q4 2016 104919.4 6640 397119.9 2636876329 2637 5.8 12879.6 21300 48749.3 1038359792 1038 2.3
Ql 2017 110416.7 1240 417927.2 518229739.8 518 I.I 13552.8 23400 51297.3 1200357943 1200 2.6
Q2 2017 109943.0 510 416134.3 212228470.1 212 0.5 12475.3 18100 47219.0 854664090 855 1.9
Q3 2017 112626.4 8840 426290.9 3768411768 3768 8.3 14556.8 27600 55097.5 1520690669 1521 3.4
Q4 2017 108891.2 129 412153.2 53167761.77 53 0.1 14271.0 11600 54015.7 626582526 627 1.4
Table G-1
-~-·. -·---~~•V•• ~• _ ... ..,. . ._..,,... ••• .,._...,,...,. ,.._. . ._. _ _. . ._ ,. ._,,...,._, • ...... , ... ,,,._ ..,., •• ..._,....,, ·• ,..., •• ._..._..
TW4-19 . TW4-20 .. Total
Pumped Total Pumped Total Total Total Total Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) , (pounds) Pumped (gal) Cone (liters) Total (ug) (grams) (pounds)
01 2018 109856.3 2640 415806.1 1097728092 1098 2.4 14258.4 15400 53968.0 831107878 831 1.8
Q2 2018 111271.4 2980 421162.2 1255063502 1255 2.8 13367.6 12000 50596.4 607156392 607 1.3
Q3 2018 105821.8 1910 400535.5 765022829.8 765 1.7 12443.6 10500 47099.0 494539773 495 1.1
Q4 2018 107197.4 5270 405742.2 2138261178 2138 4.7 12841.1 9500 48603.5 461733494 462 1.0
Ql 2019 116132.8 2050 439562.6 901103428.4 901 2.0 14623.9 15600 55351.5 863482799 863 1.9
Q2 2019 100704.0 11500 381164.6 4383393360 4383 9.7 13439.1 13700 50867.0 696877811 697 1.5
Q3 2019 101026.8 6670 382386.4 2550517541 2551 5.6 13787.0 10500 52183.8 547929848 548 1.2
Totals 18930022.03 423.4 2451385.18 289.6
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-4 -TW4-22 .:I:.-·-~..:,.., ·,,~cl.~:.>" ' ·------~ --~ ..
~ Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter _ (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 84513.9 2000 319885.1 639770223 640 1.4 NA NA NA NA NA NA
Q3 2010 76916.8 2100 291130.1 611373184.8 611 1.3 NA NA NA NA NA NA
Q4 2010 86872.1 1700 328810.9 558978527 .5 559 1.2 NA NA NA NA NA NA
QI 2011 73360.0 1800 277667.6 499801680 500 1.1 NA NA NA NA NA NA
Q22011 80334.6 1700 304066.5 516912983.7 517 1.1 NA NA NA NA NA NA
Q3 2011 97535.0 1500 369170.0 553754962.5 554 1.2 NA NA NA NA NA NA
Q4 2011 109043.5 1500 412729.6 619094471.3 619 1.4 NA NA NA NA NA NA
Ql 2012 101616.8 1200 384619.6 461543505.6 462 1.0 NA NA NA NA NA NA
Q2 2012 87759.1 1500 332168.2 498252290.3 498 I.I NA NA NA NA NA NA
Q3 2012 80006.0 1600 302822.7 484516336 485 I.I NA NA NA NA NA NA
Q4 2012 71596 1400 270990.9 379387204 379 0.8 NA NA NA NA NA NA
Ql 2013 58716.8 1460 222243.1 324474908.5 324 0.7 16677.4 10600 63124.0 669113965.4 669.1 1.5
Q2 2013 65603.4 1330 248308.9 330250795.8 330 0.7 25523.2 12500 96605.3 1207566400.0 1207.6 2.7
Q3 2013 63515.4 1380 240405.8 331759988.8 332 0.7 25592.9 9640 96869.1 933818379 .5 933.8 2.1
Q4 2013 60233.6 1360 227984.2 310058479.4 310 0.7 24952.2 13300 94444.1 1256106224.1 1256.1 2.8
QI 2014 58992.9 1260 223288.1 281343039.4 281 0.6 24532.0 12100 92853.6 1123528802.0 1123.5 2.5
Q2 2014 60235.3 1220 227990.6 278148544.8 278 0.6 24193.9 12400 91573.9 1135516502.6 1135.5 2.5
Q3 2014 69229.4 1320 262033.3 345883928.3 346 0.8 24610.9 12400 93152.3 1155087980.6 1155.1 2.5
Q4 2014 64422.6 1130 243839.5 275538681.3 276 0.6 23956.9 12400 90676.9 1124393144.6 1124.4 2.5
Ql 2015 36941.3 1350 139822.8 188760807.7 189 0.4 22046.9 12700 83447.5 l 059783459 .6 1059.8 2.3
Q2 2015 68162.8 1280 257996.2 330235133.4 330 0.7 23191.6 8050 87780.2 706630658.3 706.6 1.6
Q3 2015 64333.0 1220 243500.4 297070494.1 297 0.7 24619.9 7810 93186.3 727785170.9 727.8 1.6
Q4 2015 59235.1 1190 224204.9 266803775.7 267 0.6 23657.6 7530 89544.0 674266440.5 674.3 1.5
Ql 2016 57274.0 1190 216782.1 257970687 .1 258 0.6 24517.8 6070 92799.9 563295229.1 563.3 1.2
Q2 2016 61378.0 1780 232315.7 413521999.4 414 0.9 26506.3 8570 100326.3 859796780.9 859.8 1.9
Q3 2016 50104.2 1380 189644.4 261709267.9 262 0.6 22144.1 5840 83815.4 489482044.0 489.5 1.1
Q4 2016 31656.0 1430 119818.0 171339682.8 171 0.4 23646.8 3370 89503.1 301625575.1 301.6 0.7
Ql 2017 23526.8 1290 89048.9 114873130 115 0.3 24066.2 5320 91090.6 484601816.4 484.6 I.I
Q2 2017 23244.9 1290 87981.9 113496711 113 0.3 23685.0 3670 89647.7 329007150.8 329.0 0.7
Q3 2017 23937.3 1290 90602.7 116877457.8 117 0.3 24583.2 5150 93047.4 479194171.8 479.2 1.1
Q4 2017 22900.6 1120 86678.8 97080223.52 97 0.2 23779.6 4770 90005.8 429327599.2 429.3 0.9
Table G-1
--·--· ... .... ·-·····--··-~·--··-----· ·~·-···--· ........ ._ ................... :rw44 TW4,.22 -----
"Total 'rotal . Total Total
Pumped Pumped Total Total 'Punipecl Puinped To® Tot;il
Quarter (gilt) C@c (literll) Tot;U(ug) (gnms) (po®~) (gal) Cone (litt!ts), 'J:otaJ (ug) ~) (JJ!>unds)
012018 23103.4 1160 87446.4 101437788 101 0.2 23982.8 4530 90774.9 411210287.9 41 l.2 0.9
Q2 2018 18137.0 1050 68648.5 72080972.25 72 0.2 23256.6 3010 88026.2 264958955.3 265.0 0.6
Q3 2018 15366.0 1030 58160.3 59905119.3 60 0.1 21248.7 3600 80426.3 289534786.2 289.5 0.6
Q4 2018 15420.2 1140 58365.5 66536620.98 67 0.1 24171.0 2680 91487.2 245185789.8 245.2 0.5
Ql 2019 16655.0 1050 63039.2 66191133.75 66 0.1 26149.9 4310 98977.4 426592471.2 426.6 0.9
Q2 2019 14311.9 1070 54170.5 57962479.41 58 0.1 23073.1 4690 87331.7 409585595.6 409.6 0.9
Q3 2019 14520.0 989 54958.2 54353659.8 54 0.1 24711.7 3460 93533.8 323626894.4 323.6 0.7
Totals 2090710.7 25.2 643078.2 39.9
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-24 TW4-25
' Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
01 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q22011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q42011 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2013 144842.6 5.7 548229.2 3124906.7 3.1 0.0 99369.9 0.0 376115.1 0.0 0.0 0.0
Q2 2013 187509.3 17.4 709722.7 12349175.0 12.3 0.0 147310.4 0.0 557569.9 0.0 0.0 0.0
Q3 2013 267703.5 21.8 1013257.7 22089018.9 22.1 0.1 145840.9 0.0 552007.8 0.0 0.0 0.0
Q4 2013 260555.3 32.5 986201.8 32051558.8 32.1 0.1 126576.5 0.0 479092.1 0.0 0.0 0.0
QI 2014 229063.9 78.5 867006.9 68060038.6 68.1 0.2 129979.2 0.0 491971.3 0.0 0.0 0.0
Q2 2014 216984.l 62.7 821284.8 51494558.1 51.5 0.1 124829.8 0.0 472480.8 0.0 0.0 0.0
Q3 2014 213652.5 76.3 808674.7 61701880.6 61.7 0.1 119663.9 0.0 452927.9 0.0 0.0 0.0
Q4 2014 178468.7 25.8 675504.0 17428004.0 17.4 0.04 107416.1 0.0 406569.9 0.0 0.0 0.0
QI 2015 92449.3 49.2 349920.6 17216093.5 17.2 0.04 71452.4 0.0 270447.3 0.0 0.0 0.0
Q2 2015 62664.2 4.28 237184.0 1015147.5 1.0 0.002 91985.3 0.0 348164.4 0.0 0.0 0.0
Q3 2015 66313.2 46.9 250995.5 11771687.2 11.8 0.026 124137.1 0.0 469858.9 0.0 0.0 0.0
Q4 2015 107799.1 25.3 408019.6 10322895.7 10.3 0.023 116420.1 0.0 440650.1 0.0 0.0 0.0
QI 2016 100063.2 22.8 378739.2 8635254.0 8.6 0.019 115483.2 0.0 437103.9 0.0 0.0 0.0
Q2 2016 65233.6 69.6 246909.2 17184878.6 17.2 0.038 125606.0 0.0 475418.7 0.0 0.0 0.0
Q3 2016 51765.8 17.8 195933.6 3487617.2 3.5 0.008 104983.6 0.0 397362.9 0.0 0.0 0.0
Q4 2016 99522.5 20.8 376692.7 7835207.4 7.8 0.017 98681.2 0.0 373508.3 0.0 0.0 0.0
QI 2017 99117.4 18.3 375159.4 6865416.3 6.9 0.015 161.2 1.15 610.l 701.7 0.0 0.0
Q22017 52808.7 17.2 199880.9 3437952.0 3.4 0.008 101617.2 0.0 384621.1 0.0 0.0 0.0
Q3 2017 55574.6 17.8 210349.9 3744227.5 3.7 0.008 124138.4 0.0 469863.8 0.0 0.0 0.0
Q4 2017 106021.4 16.0 401291.0 6420656.0 6.4 0.014 116731.9 0.0 441830.2 0.0 0.0 0.0
Table G-1 _ .... _. ~·-·. --·-.................... "'" -···-· .................. -···-.......... . ............. ...,.. ........................ ..__, ....... -........
TW4-~ TW4-25 -
-TgtaJ Tota! 'fotal Total
~ Pumped Total Total fumped Pum~ Tqtal To~J
Quarte.r ~). Cone (liters) Total(ug) (grams) (pounds) (gaJ) Cone (li~) T~tal(ug) ~) .(J>oooils)
01 2018 96900.2 24.9 366767.3 9132504.7 9.1 0.020 116991.7 0.0 442813.6 0.0 0.0 0.0
Q2 2018 53117.9 49.2 201051.3 9891721.6 9.9 0.022 117758.3 0.0 445715.2 0.0 0.0 0.0
Q3 2018 53142.5 35.0 201144.4 7040052.7 7.0 0.016 111657.5 0.0 422623.6 0.0 0.0 0.0
Q4 2018 101606.4 21.0 384580.3 8076185.5 8.1 O.DI8 114458.2 0.0 433224.3 0.0 0.0 0.0
Ql 2019 97701.0 28.1 369798.3 10391331.8 10.4 0.023 90789.5 0.0 343638.3 0.0 0.0 0.0
Q2 2019 53197.3 28.8 201351.8 5798931.3 5.8 0.013 88302.0 0.0 334223.1 0.0 0.0 0.0
Q3 2019 54445.7 31.1 206077.0 6408993.9 6.4 0.014 87609.5 0.0 331602.0 0.0 0.0 0.0
Totals 3168223.9 0.984 2919951.0 0.0
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-01 -. TW4-02 ---~ -Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA ' NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q22011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2015 24569.2 1130 92994.4 105083696.9 105.1 0.23 24156.7 1840 91433.1 168236921.5 168.2 0.37
Q2 2015 23989.9 1260 90801.8 114410232.1 114.4 0.25 22029.9 1650 83383.2 137582233.0 137.6 0.30
Q3 2015 23652.0 1060 89522.8 94894189.2 94.9 0.21 21586.9 1310 81706.4 107035405.6 107.0 0.24
Q4 2015 20764.3 1040 78592.9 81736590.5 81.7 0.18 21769.8 2070 82398.7 170565294.5 170.6 0.38
Ql 2016 19255.6 974 72882.4 70987502.4 71.0 0.16 20944.6 1970 79275.3 156172362.7 156.2 0.34
Q2 2016 19588.2 1140 74141.3 84521124.2 84.5 0.19 20624.0 2070 78061.8 161588008.8 161.6 0.36
Q3 2016 15613.5 1160 59097.1 68552633.1 68.6 0.15 17487.4 1780 66189.8 117817860.0 117.8 0.26
Q4 2016 16756.8 1330 63424.5 84354569.0 84.4 0.19 19740.6 1600 74718.2 119549073.6 119.5 0.26
QI 2017 16931.8 519 64086.9 33261081.9 33.3 0.07 19869.7 1570 75206.8 ll8074698.8 118.1 0.26
Q2 2017 18200.2 977 68887.8 67303338.6 67 .3 0.15 18716.7 1940 70842.7 137434856.4 137.4 0.30
Q3 2017 17413.6 958 65910.5 63142236.0 63 .1 0.14 19338.8 1310 73197.4 95888539.0 95.9 0.21
Q4 2017 14089.8 556 53329.9 29651420.5 29.7 0.07 17327.6 1610 65585.0 105591795.3 105.6 0.23
Table G-1
--·.' -·--·--··-·· --· ····-· -· -· ... ~ ,-···-. --~-·-~ -·-· . -·-···--· ' -·--· ...... --
-------TW4-0:r-TW4;_02' -..
'Totai Total 'T6tal . Total
~~ Pwo_ped TifW To~J ~Pl4 ·J>umpe4 T!,tal 'Tofil
~~t (gaI): Cone Qiter§) Total (ug) (grams) (J,!:iunds) (&JU! Con~ (Ji~) Tota) (ug) .~) (pc)UD'ds)
01 2018 12505.7 70.4 47334.1 3332318.8 3.3 0.01 16232.3 764 61439.3 46939591.2 46.9 0.10
Q2 2018 10814.8 942 40934.0 38559845.0 38.6 0.09 16051.4 949 60754.5 57656067.0 57.7 0.13
Q3 2018 9727.3 1010 36817.8 37186008.8 37.2 0.08 14927.2 980 56499.5 55369463.0 55.4 0.12
Q4 2018 9836.7 752 37231.9 27998395.9 28.0 0.06 15464.1 822 58531.6 48112990.4 48.1 0.11
Ql 2019 10603.6 87.2 40134.6 3499739.4 3.50 O.Ql 16169.9 1040.0 61203.1 63651194.4 63.65 0.14
Q2 2019 9393.9 1040.0 35555.9 36978148.0 36.98 0.08 13893.7 1360.0 52587.7 71519210.1 71.52 0.16
Q3 2019 9734.1 894 36843.6 32938150.2 32.94 0.07 14106.9 797 53394.6 42555509.4 42.56 0.09
Totals 303441.0 2.38 350438.2 4.37
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-ff TW4-21 ~------
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2015 9898.7 2450 37466.6 91793119.8 91.8 0.20 NA NA NA NA NA NA
Q2 2015 5243.3 2710 19845.9 53782363.3 53.8 0.12 30743.7 366 116364.9 42589555.0 42.6 0.09
Q3 2015 3584.4 1120 13567.0 15194988.5 15.2 0.03 125285.4 281 474205.2 133251672.2 133.3 0.29
Q4 2015 4110.3 2730 15557.5 42471935.4 42.5 0.09 134774.9 339 510123.0 172931695.8 172.9 0.38
Ql 2016 3676.2 2660 13914.4 37012349.2 37.0 0.08 125513.3 390 475067.8 185276457.8 185.3 0.41
Q2 2016 3760.4 3340 14233.1 47538600.8 47.5 0.10 132248.7 545 500561.3 272805924.6 272.8 0.60
Q3 2016 2953.8 3200 11180.1 35776425.6 35.8 0.08 110381.9 456 417795.5 190514744.1 190.5 0.42
Q4 2016 3050.2 3180 11545.0 36713122.3 36.7 0.08 130311.3 434 493228.3 214061069 .4 214.1 0.47
Ql 2017 2984.2 3310 11295.2 37387102.1 37.4 0.08 54333.5 598 205652.3 122980073.9 123.0 0.27
Q2 2017 2845.9 3370 10771.7 36300735.2 36.3 0.08 60969.7 224 230770.3 51692550.4 51.7 0.11
Q3 2017 2830.0 3290 10711.6 35240999.5 35.2 0.08 120116.2 537 454639.8 244141581.7 244.1 0.54
Q4 2017 2612.7 2880 9889.1 28480520.2 28.5 0.06 126492.5 466 478774.1 223108736.4 223.1 0.49
Table G-1
----------·-· -. ~ -~ -"" --... ·---. --. -.. -· ----------
TW4-11 TW4-21
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Qparter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
012018 2571.0 3090 9731.2 30069516.2 30.l 0.07 117832.0 421 445994.1 187763524.5 187.8 0.41
Q2 2018 2513.5 2800 9513.6 26638073.0 26.6 0.06 116681.0 532 441637.6 234951195.2 235.0 0.52
Q3 2018 2170.2 3050 8214.2 25053331.4 25.1 0.06 110001.4 476 416355.3 198185122.3 198.2 0.44
Q4 2018 2379.5 2930 9006.4 26388774.0 26.4 0.06 121686.3 585 460582.8 269440914.0 269.4 0.59
Ql 2019 2342.4 2820 8866.0 25002074.9 25.00 0.1 123264 323 466554.6 150697141.8 150.70 0.3
Q2 2019 2195.1 2970 8308.5 24676106.9 24.68 0.1 106893.6 734 404592.3 296970730.6 297.0 0.7
Q3 2019 2046.0 2790 7744.1 21606066.9 21.61 0.0 108132.9 596 409283.0 243932683.8 243.9 0.5
Totals 63767.8 1.49 1955662.4 7.57
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-37 TW4-39
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q22011 NA NA NA NA NA NA NA NA NA NA NA NA
Q32011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2015 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2015 29206.0 30200 110544.7 3338450242.0 3338.5 7.4 NA NA NA NA NA NA
Q3 2015 118063.9 19100 446871.9 8535252554.7 8535.3 18.8 NA NA NA NA NA NA
Q4 2015 111737.5 19500 422926.4 8247065531.3 8247.1 18.2 NA NA NA NA NA NA
QI 2016 111591.0 17500 422371.9 7391508862.5 7391.5 16.3 NA NA NA NA NA NA
Q2 2016 119241.2 16200 451327.9 7311512660.4 7311.5 16.1 NA NA NA NA NA NA
Q3 2016 98377.6 15900 372359 5920511534.4 5920.5 13.1 NA NA NA NA NA NA
Q4 2016 101949.l 16400 385877 6328388433.4 6328.4 14.0 3598.3 2800 13620 38134783.4 38.1 0.1
QI 2017 97071.7 18000 367416 6613494921.0 6613.5 14.6 103117.8 6460 390301 2521343639.6 2521.3 5.56
Q2 2017 93191.3 15800 352729 5573119313.9 5573.] 12.3 41313.0 5560 156370 869415559.8 869.4 1.92
Q3 2017 81749.3 15000 309421 4641316507.5 4641.3 10.2 34546.3 10000 130758 1307577455.0 1307.6 2.9
Q4 2017 87529.6 15500 331300 5135142808.0 5135.1 11.3 68180.2 552 258062 142450255.5 142.5 0.3
Table G-1
--· ·-··. -·-.. ·--·~"""" .... .............................. _.. ---····-.. "" ....... ·-···---· .....................................
TW4-37 TW4-39
Total Total Total Total
Pumped Pumped I Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
012018 84769.3 12900 320852 4138988226.5 4139.0 9.1 59262.2 2870 224307 643762315.5 643.8 1.4
Q2 2018 83653.1 14400 316627 4559428562.4 4559.4 JO.I 34259.8 7160 129673 928461135.9 928.5 2.0
Q3 2018 77457.8 14100 293178 4133806599.3 4133.8 9.1 33473.4 8180 126697 1036379979.4 1036.4 2.3
Q4 2018 76271.4 15200 288687 4388046184.8 4388.0 9.7 37003.6 6520 140059 913182241.5 913.2 2.0
Ql 2019 77591 13300 293683.4 3905989871.7 3906.0 8.6 49117 885 185907.5 164528107.9 164.5 0.4
Q2 2019 64950.1 16200 245836.1 3982545281 .7 3982.5 8.8 34285.7 8640 129771.4 1121224675.7 1121.2 2.5
Q3 2019 67572.0 11900 255760.0 3043544238.0 3043.5 6.7 36976.2 4240 139954.9 593408848.1 593.4 1.3
Totals 1581973.3 214.3 535133.4 22.7
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
-TW4-40 -TW4-41
Total Total Total Total fotal Volum~
Pumped Pumped Total Total Pumped Pumped Total Total Total Pumped
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds) (pounds) (gallons)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA 286.9 9648896.0
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA 4.0 904550.0
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA 9.0 559220.0
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 550560.0
Ql 2008 NA NA NA NA NA NA NA NA NA NA NA NA 13.8 503034.0
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA 14.8 527290.0
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA 26.8 724960.0
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA 22.7 786870.0
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA 10.0 664830.0
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA 13.5 1007400.0
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA 18.5 399710.0
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA 49.4 1047335.0
Ql 2010 NA NA NA NA NA NA NA NA NA NA NA NA 4.5 492485.0
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA 16.5 721374.1
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 376623.4
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA 17.9 1041817.3
Ql 2011 NA NA NA NA NA NA NA NA NA NA NA NA 24.9 696533.0
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA 13.1 449131.1
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA 8.1 462334.5
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA 10.8 468706.3
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 448486.3
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA 10.4 400415.2
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA 6.6 390229.0
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA 7.1 358000.0
Ql 2013 NA NA NA NA NA NA NA NA NA NA NA NA 13.7 634286.l
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA 13.5 768953.4
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA 31.1 950505.6
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA 10.3 990119.8
Ql 2014 NA NA NA NA NA NA NA NA NA NA NA NA 8.6 859297.5
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA 9.9 838057.9
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA 10.2 852987.2
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA 14.6 673905.9
QI 2015 NA NA NA NA NA NA NA NA NA NA NA NA 9.9 458271.4
Q2 2015 NA NA NA NA NA NA NA NA NA NA NA NA 15.3 539592.9
Q3 2015 NA NA NA NA NA NA NA NA NA NA NA NA 33.4 816299.8
Q4 2015 NA NA NA NA NA NA NA NA NA NA NA NA 32.3 847567.8
Ql 2016 NA NA NA NA NA NA NA NA NA NA NA NA 30.6 819302.3
Q2 2016 NA NA NA NA NA NA NA NA NA NA NA NA 39.4 832418.9
Q3 2016 NA NA NA NA NA NA NA NA NA NA NA NA 24.7 686543.4
Q4 2016 NA NA NA NA NA NA NA NA NA NA NA NA 25.6 750667.4
Ql 2017 NA NA NA NA NA NA NA NA NA NA NA NA 27.2 667899.1
Q2 2017 NA NA NA NA NA NA NA NA NA NA NA NA 19.6 657232.5
Q3 2017 NA NA NA NA NA NA NA NA NA NA NA NA 28.5 754250.1
Q4 2017 NA NA NA NA NA NA NA NA NA NA NA NA 16.9 841953.7
Table G-1
-·------·----· --·--. -------------·-----------------.
TW4-40 TW4-41 ---
Total Total I Total Total Total Volume
Pumped Pumped Total Total Pumped Pumped Total Total Total Pumped
Qi!_arter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds) (pounds) (gallons)
01 2018 NA NA NA NA NA NA NA NA NA NA NA NA 18.0 810330.4
Q2 2018 NA NA NA NA NA NA 73711.2 1400 278997 390595648.8 390.6 0.9 20.1 803034.5
Q3 2018 NA NA NA NA NA NA 44981.6 1390 170255 236654734.4 236.7 0.5 17.6 733435.6
Q4 2018 NA NA NA NA NA NA 35431.6 1320 134108 177023110.1 177.0 0.4 20.8 800443.6
QI 2019 NA NA NA NA NA NA 31904 1220 120755.1 147321253.7 147.3 0.3 16.2 811589.4
Q2 2019 81762.7 263 309471.8 81391088.5 81.4 0.18 25146.5 1320 95179.5 125636943.3 125.6 0.3 26.2 750139.6
Q3 2019 116414.2 380 440627.7 167438543.9 167.4 0.37 24045.6 1190 91012.6 108304989.2 108.3 0.2 18.3 794827.4
Totals 198176.9 0.55 235220.0 2.6 1173.3 44176526.5
TableG-2
Chloroform Mass Removal Per Well Per Quarter
TW4-15
MW-4 (MW-26) TW4-19 TW4-20 TW4-4 TW4-22 TW4-24 TW4-25 TW4-01 TW4-02 TW4-11 TW4-21 TW4-37 TW4-39 TW4-40 TW4-41 Quarter
Ooarter* (lbs.) (lbs.) (lbs.) Obs.) Obs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) Obs.) Totals Obs.)
QI 2007 36.8 12.9 150.2 87.0 NA NA NA NA NA NA NA NA NA NA NA NA 286.9
Q2 2007 1.4 0.1 0.0 2.5 NA NA NA NA NA NA NA NA NA NA NA NA 4.0
Q3 2007 2.2 0.8 2.9 3.1 NA NA NA NA NA NA NA NA NA NA NA NA 9.0
042007 1.7 1.0 3.1 4.8 NA NA NA NA NA NA NA NA NA NA NA NA 10.6
QI 2008 1.7 0.4 4.6 7.2 NA NA NA NA NA NA NA NA NA NA NA NA 13.8
Q2 2008 1.3 0.5 3.2 9.9 NA NA NA NA NA NA NA NA NA NA NA NA 14.8
03 2008 1.2 0.3 15.9 9.3 NA NA NA NA NA NA NA NA NA NA NA NA 26.8
Q4 2008 1.3 0.3 20.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 22.7
Ql 2009 1.7 0.4 4.3 3-6 NA NA NA NA NA NA NA NA NA NA NA NA 10.0
Q2 2009 6.8 0.2 3.7 2.8 NA NA NA NA NA NA NA NA NA NA NA NA 13.5
Q3 2009 1.5 0.4 I I.I 5.5 NA NA NA NA NA NA NA NA NA NA NA NA 18.5
Q4 2009 4.8 0.6 17.8 26.l NA NA NA NA NA NA NA NA NA NA NA NA 49.4
QI 2010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 4.5
Q2 2010 1.5 1.0 6.8 5.9 1.4 NA NA NA NA NA NA NA NA NA NA NA 16.5
Q3 2010 l.3 1.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA NA NA NA 10.6
Q42010 I.I 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA NA NA NA 17.9
QI 2011 I.I 0.2 12.9 9.6 I.I NA NA NA NA NA NA NA NA NA NA NA 24.9
02 2011 1.2 0.8 5.3 4.6 I.I NA NA NA NA NA NA NA NA NA NA NA 13.1
Q3 2011 1.2 0.4 I.I 4.1 1.2 NA NA NA NA NA NA NA NA NA NA NA 8.1
Q42011 1.2 0.8 2.7 4.8 1.4 NA NA NA NA NA NA NA NA NA NA NA 10.8
QI 2012 I.I 0.6 0.8 7,0 1.0 NA NA NA NA NA NA NA NA NA NA NA 10.6
Q22012 I.I 0.7 0.7 6.9 1.1 NA NA NA NA NA NA NA NA NA NA NA 10.4
Q3 2012 I.I 0.7 1.4 2.4 1.1 NA NA NA NA NA NA NA NA NA NA NA 6.6
Q4 2012 0.9 0.3 2.0 3.2 0.8 NA NA NA NA NA NA NA NA NA NA NA 7.2
QI 2013 0.9 0.4 7.4 2.8 0.7 l.5 0.0 0.0 NA NA NA NA NA NA NA NA 13.7
Q2 2013 0.9 0.9 3.9 4.4 0.7 2.7 0.0 0.0 NA NA NA NA NA NA NA NA 13.5
03 2013 0.9 0.6 22.3 4.4 0.7 2.1 O.l 0.0 NA NA NA NA NA NA NA NA 31.I
Q4 2013 0.8 0.3 3.2 2.5 0.7 2.8 0.1 0.0 NA NA NA NA NA NA NA NA 10.3
QI 2014 0.8 0.3 1..5 2.8 0.6 2.5 0.2 0.0 NA NA NA NA NA NA NA NA 8.6
Q2 2014 0.8 0.4 2.0 3.4 0.6 2.5 0.1 0.0 NA NA NA NA NA NA NA NA 9.9
Q3 2014 0.9 0.4 3.6 1.8 0.8 2.5 0.1 0.0 NA NA NA NA NA NA NA NA 10.2
Q4 2014 0.8 0.4 7.1 3.2 0.6 2.5 0.04 o.o NA NA NA NA NA NA NA NA 14.6
QI 2015 0.9 0.4 2.4 2.6 0.4 2.3 0.04 0.0 0.23 0.37 0.20 NA NA NA NA NA 9.9
02 2015 0.7 0.5 1.0 2.8 0.7 1.6 0.00 0.0 0.25 0.30 0.12 0.09 7.4 NA NA NA 15.3
Q3 2015 1.0 0.4 7.6 2.5 0.7 1.6 O.D3 0.0 0.21 0.24 0.03 0.29 18.8 NA NA NA 33.4
Q42015 1.0 0.4 7.4 2.2 0.6 1.5 0.02 0.0 0.18 0.38 0.09 0.38 18.2 NA NA NA 32.3
01 2016 0.9 0.4 7.6 2.6 0.6 1.2 0.02 0.0 0.16 0.34 0.08 0.41 16.3 NA NA NA 30.6
Q2 2016 1.3 0.4 13.0 4.4 0.9 1.9 0.04 0.0 0.19 0.36 0.10 0.60 16.1 NA NA NA 39.4
Q3 2016 1.0 0.5 5.2 2.4 0.6 1.1 0.01 0.0 0.15 0.26 0.08 0.42 13.1 NA NA NA 24.7
04 2016 1.0 0.4 5.8 2.3 0.4 0.7 0.017 o.o 0.19 0.26 0.08 0.47 14.0 0.1 NA NA 25.6
QI 2017 0.9 0.3 I.I 2.6 0.3 1. l O.Ql5 0.0 om 0.26 0.08 0.27 14.6 5.6 NA NA 27.2
Q220l7 0.9 0.5 0.5 1.9 0.3 0.7 0.008 0.0 0.15 0.30 0.08 0.11 12.3 1.9 NA NA 19.6
Q3 2017 I. I 0.3 8,3 3.4 0.3 l.l 0.008 0.0 0.14 0.21 0.08 0.54 10.2 2.9 NA NA 28.5
042017 1.2 0.6 0.1 l.4 0.2 0.9 0.014 0.0 0.07 0.23 0.06 0.49 11.3 0.3 NA NA 16.9
QI 2018 1.2 0.3 2.4 1.8 0.2 0.9 0.020 0.0 O.QI 0.10 0.07 0.41 9.l 1.4 NA NA 18.0
02 2018 I. I 0.4 2.8 1.3 0.2 0.6 0.022 0.0 0.09 0.13 0.06 0.52 IO.I 2.0 NA 0.9 20.1
Q3 20!8 1.0 0.4 1.7 1.1 0.1 0.6 0.016 0.0 0.08 0.12 0.06 0.44 9.1 2.3 NA 0.5 17.6
Q4 2018 1.1 0.3 4.7 1.0 0.1 0.5 O.Ql8 0.0 0.06 0.11 0.06 0.59 9.7 2.0 NA 0.4 20.8
QI 2019 1.1 0.2 2.0 1.9 0.1 0.9 0.023 0.0 0.01 0.14 0.06 0.33 8.6 0.4 NA 0.3 16.2
Q22019 1.0 0.3 9.7 1.5 0.1 0.9 0.013 0.0 0.08 0.16 0.05 0.65 8.8 2.5 0.18 0.3 26.2
Q3 2019 0.9 0.3 5.6 1.2 0.1 0.7 0.014 0.0 O.o? 0.09 0.0 0.5 6.7 1.3 0.37 0.2 18.3
Well Totals 102.1 36.2 423.4 289.6 25.2 39.9 0.984 0.0 2.38 4.37 1.49 7.57 214.3 22.7 0.5 2.6 1173.3
* QI 2007 represents the cumulative total prior to and including QI 2007.
Table G-3 Well Pumping Rates and Volumes
Volume of Water Pumped
Pumping Well Name During the Quarter (gals) Average Pump Rate (2:om)
MW-4 95517.7 3.8
MW-26 24181.1 11.3
TW4-19 101026.8 18.0
TW4-20 13787.0 6.4
TW4-4 14520.0 16.6
TWN-2 41377.5 17 .6
TW4-22 24711.7 17.8
TW4-24 54445.7 15.8
TW4-25 87609.5 11.6
TW4-01 9734.1 13.8
TW4-02 14106.9 17.2
TW4-11 2046.0 16.4
TW4-21 108132.9 16.6
TW4-37 67572.0 17.9
TW4-39 36976.2 17.9
TW4-40 116414.2 18.0
TW4-41 24045.6 4.0
-(/) .c ::=,.. ....
Q) t ca ::::,
0
>, .c
"O Q) > 0 E
Q) er:
E ....
0 -e 0
..c: () -0
(/)
(/) ca ~
0 c:i lO (V)
0
0 0 (V)
0 c:i lO C\J
0
0 0 C\J
6 ~OG ~O
8~0G GO
noG£O
9WG170
9 ~OG ~O
9WGG0
17~0G £0
8WG170
£ ~OG ~O
GWGGO
~ ~OG £0 §
N
O~OG 170
OWG ~O
600G GO
800G £0
LOOG 170
LOOG ~O
0 0 0 0 c:i c:i 0 c:i lO 0 lO ,..... ,.....
(spunod) paAowa1:::1 WJO!OJOl4:J -Cl
MW-04 Mass of Chloroform Removed by Quarter {lbs.)
40.0
35.0
30.0
25.0
en 20.0
"O
C :::,
0 a.. -"O 15.0
Q) > 0 E Q) a: 10.0
E ... .E 0 ... 0 5.0 :c (.)
0.0
10
l"-0 0 C\J ..... a
...... . ,... .
l"-0 0 C\J
s::t a
& -& .
<X) 0 0 C\J
Ct) a
A
.JV\~--~ .
O> 0 0 C\J
C\J a
0 ..... 0 C\J ..... a
-.
0 .....
0 C\J
s::t a
-... --
..... ..... 0 C\J
Ct) a
Ql 2007 represents the cumulative total prior to and including Ql 2007.
---
I
.
C\J .....
0 C\J
C\J a
--... -.
Ct) .....
0 C\J ..... a
--. . -.
Ct) .....
0 C\J
s::t a
-. -.
s::t .....
0 C\J
Ct) a
-& ... ...
It) .....
0 C\J
C\J a
-. -.
I
...
co .....
0 C\J ..... a
.... ... . .
co .....
0
C\J
s::t a
. -... --
I"-.....
0 C\J
Ct) a
. --. -
<X) .....
0 C\J
C\J a
-& -. -
O> .....
0 C\J
5
-. -
-en ..c -,._
Q) t:
al :::J
0
>. ..c
"'C Q) > 0 E Q) c:c
E ,._
0 .... e
0
.c (_) .... 0 en en al ~
T"""
0 I
-.::t" ~
0 (')
0
LO C\I
0
0 C\I
0
LO O LO .,.... .,.... 0 o o o (spunod) paAOW8l::::I WJO!OJ0148
6~0G£0
6~0G GO
6WG ~O
B~OG tO
BWG£0
BWGGO
BWG ~0
HOGtO
L~OG £0
HOG GO
HOG ~0
9~0G tO
9~0G £0
9WGG0
9~0G ~0
~HOG tO
S~OG £0
SWGGO
SWG ~O
0 0
0
-(/)
..0 -.... Q)
t m
:::J a
>,
..0
"C
Q) > 0
E Q) a:
E ....
0 -0 ....
.Q
..c
() -0
(/)
(/) m ~
C\I 0 I ~ ~
0 s;f"
c:i
g
0
II)
C\J
0
0 II) 0 II) C\J T"" T"" 0
O(spuno~ paAowe'\:j WJOJd.R>ll..18
0 0
c:i
6~0G £0
6~0G GO
6~0G ~O
8WGV0
B~OG £0
B~OG GO
B~OG ~O
L~OG vO
L~OG £0
UOGGO
UOG ~O
9~0G vO
9~0G £0
9~0G GO
9~0G ~O
SWGvO
S~OG £0
S~OG GO
S~OG ~O
-U) .c -....
Q)
t::: ctl
:::J a
>, .c
"C
Q) > 0 E
Q) a:
E ....
0 -0 ....
0
..c
() -0
U)
U)
ctl ~
T"""
T"""
I -.::t ~ I-
LO C\J 0
0 C\J 0
6~0G £0
6~0G GO
6~0G ~0
B~OG PO
B~OG £0
B~OG GO
B~OG ~0
L~OG PO
HOG£0
L~OG GO
L~OG ~O
9~0G PO
9~0G £0
9~0G GO
9~0G ~0
S~OG PO
S~OG £0
S~OG GO
S~OG ~O
LO 0 LO 0
T"" T"" 0 0
0 (spuna'd) paAowa1:1 !&oJOJOILIO 0
-en ..c -,._
Q)
t:
<ti :::::, a
>, ..c
"'C Q) > 0 E
Q) a:
E ,._
0 ..... 0 ,._
0
..c: 0 ..... 0
en en <ti ~
""'" 0 I
""'" s I-
co
ci
CD
ci
N
ci
(spunod) paAOW9tJ WJO!OJ014:J
0
ci
8~0G 80
HOG VO
L~OG ~O
9~0G GO
!HOG80
v~OG vO
vWGm
8~0G GO
G~OG 80
O~OG lO
-(/) .c -...
Q) t «I
::J 0
>, .c
"O ~ 0 E
Q) er:
E ... 0 -e
0
..c
0 -0
(/)
(/)
«I ~
(0
C\I I ;;:
~
0 0 0 cxi .,....
0 0 0 0 co -,i C\I 0
(spunod) paAOW8l::l WJO!OJ0140
6WG ~O
8~0G GO
noG£0
9~0G PO
9 ~OG ~O
!:HOG GO
P~OG £0
£~0G PO
£ ~OG ~O
G~OG GO
~WG£0
O~OG PO
O~OG ~O
600G GO
800G £0
LOOG PO
LOOG ~O
r--0 0 N
-Cl
TW4-19 Mass of Chloroform Removed by Quarter (lbs.)
160.0 ~--------------------------------------,
140.0 -++-----------------------------------------1
120.0 ~----------------------------------------1
100.0 -l-4-----------------------------------------i
80.0
U)
"'O C: ::::,
0 60.0 a.. --"O Q) > 0 E 40.0 Q) a:
E .... 0 -20.0 0 .... .Q ..c: 0
0.0 I I ,...._ ,...._ 00 0) 0 0 ..... C\I (Y) (Y) v LO co co ,...._ 00 0)
0 0 0 0 ..... ..... ..... ..... ..... ..... ..... ..... ..... ..... ..... ..... .....
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I C\I ..... v (Y) C\I ..... v (Y) C\I ..... v (Y) C\I ..... v (Y) C\I .....
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
Ql 2007 represents the cumulative total prior to and including Ql 2007.
TW4-20 Mass of Chloroform Removed by Quarter (lbs.)
100.0
90.0
80.0
70.0
60.0
-. 50.0 en 'O
C
::l
0 40.0 a.. -'O Q) > 30.0 0 E
Q) er:
E 20.0 ,._
0 -0 ,._
10.0 0
..c (.)
0.0
r-,... r-,... <X> O> 0 0 ..--C\J cry cry -.::I' IJ") co co r-,... <X> O> 0 0 0 0 ..--..--..--..--..--..--..--..--..--..--..--..--..--0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J C\J
..---.::I' cry C\J ..---.::I' cry C\J ..---.::I' cry C\J ..---.::I' cry C\J ..--a a a a a a a a a a a a a a a a a
Ql 2007 represents the cumulative total prior to and including Ql 2007.
Chloroform Removed (Pounds)
!=' 0 0 0
0 ...... i\, w 0 0 0 0
t 02 2015
03 2015
04 2015
01 2016
02 2016
03 2016
04 2016
01 2017
02 2017
03 2017
04 2017
01 2018
02 2018
03 2018
04 2018
01 2019
02 2019
03 2019
0 :,::.
0
!='
01 0
0
i:,,
0
0 ~ 0
~ ~ I I\) ......
s:: Ill CJ)
CJ)
0 -() ::,-
0 -,,
0 -0 -,,
3
:D CD
3 0 oi a.
C" '<
0
C Ill ;::::i.
CD -,, -C" CJ) __.
-(/) .c ::::::, ...
Q)
t ~
::J a
>, .c
,:,
Q) > 0 E
Q) a:
E ... 0 -0 ...
.Q .c.
() -0
(/)
(/)
~ ~
C\I C\I I -.::t" ~
0
Cl)
0
C\I
U? C! I!) ~ T-0
(spunod) pa/\OW8H WJOJOJ014~
0 ci
noGEO
9WGvO
9~0G m
~HOG GO
v~OG 80
-en .0 :::::, ...
Q) t ~ ::J a
>,
.0
"O Q) > 0 E
Q) a:
E ... 0 -e
0
..c
(.) -0
en en ~ ~
'<:I" C\J I '<:I" ~ I-
C\I
ci
.....
ci
.....
ci
.....
ci
..... ...
ci ci 0 ci 0 ci
(spunod) paAowat:1 WJOJOJOl4:::>
0 ci
L~Oc 80
9~0c vO
9WC: ~O
S~OC: C:0
v~Oc 80
Cl) .c ::::::,.. ._
Q) t
ctl
::I a
>, .c
"C g?
0
E Q) a:
E ._
0 -e
0
..c
(.) -0
Cl)
Cl)
ctl ~
I.{)
C\l I -.::t" ~
0
ci
0
ci
T
0
ci
0
ci
0
ci
0
ci
0 ci 0
ci
0
ci
(spunod) pa/\OW8tJ WJOJOJOILIO
0
l~
~
~
•
0
0
0
0
-
'~ '. '. •• -••
••
'. '.
' .
• •
• •
• •
0
0
••
0 ci
..--.
en
..0
,_
Q) t ca
::J a
>,
..0
"C Q) > 0 E
Q) a:
E ,_
0 e
0
..c
()
q
0 C\J
q
(0 .....
0
-,i .....
q
C\J .....
q O O 0
0 CX) (0 ""'"
(spunOd) paAOW0t:1 WJOJOJOILI~
6WG£0
6WGG0
6WG ~0
BWGPO
8~0G £0
8~0G GO
8~0G ~O
L~OG PO
L~OG £0
UOGGO
UOG ~0
9~0G PO
9~0G £0
9~0G GO
9~0G ~O
S~OG PO
S~OG £0
S~OG GO
0 0
C\J c:i
-Cl) .c -"-Q) t:: «s :::::,
0
>, .c
"C Q) > 0 E
Q) a:
E "-0 -0 "-0
.c () -0
Cl)
Cl) «s ~
0)
C")
I
-.;;t"
~
0
(0
0 0 0
C") C\J ,......
(spunod) paAOW9tJ WJOJOJ014~
0 0
6~0c €0
6~0c cO
6Wc ~o
8Wct0
8Wc€0
swcco
awe ~o
LWcvO
L~Oc €0
TW4-40 Mass of Chloroform Removed by Quarter (lbs.)
0.40 -r----------------------------------,
0.35 -1---------------------------------c,,_ __________ ---l
0.30 -t----------------------~~----------------1
0.25 -l-----------------~~---------------------------1
<n
-g0.20 ::I
0 e:..
"C Q)
~0.15 +------------------------------------------------1
E
Q) er:
E 00.10 ;------------------------------------------------1 0 ,_
..Q .c ()
0.05 +-----------------------------------------------1
0.00
CJ) CJ) ,.... ,....
0 0 C\J C\J
C') a C\J a
-Cl) ..c -....
Q) t co
::1 0
>, ..c
"O
Q) > 0 E
Q) a:
E ....
0 -0 ....
0
..c
(.) -0
Cl)
Cl) co ~
T"""
""" I
""" ~ I-
0 CJ)
0
CX)
0
<D LO ,;:t-C') C\J ,-
0 o o o o o
(spunod) paAowa1::::1 WJOJOJOl48
0
0
6~0G £0
6~0G cO
6~0G ~0
B~OG 170
B~OG £0
Volume Pumped by Quarter (gal.}
12000000.0 -,-------------------------------
10000000.0 +-----------------------------------------------
8000000.0 +-Ir---------------------------------------------
6000000.0 -t-1--------------------------------------------
4000000.0 +---a----------------------------------------------
2000000.0 +---+-------------------------------------------
0.0 -1---r--ir--r----r----r----.---,.--..---.----.----.-----,--r---.--.....--.----.----..---r----r---.--.,--r--,----..---r----r---.--.....---r--i----..---.---.----.--.-----r--ir--r----r----r--r--r--,---r--r---r----r----.---,--,
Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3
2007 2007 2008 2008 2009 2009 2010 2010 2011 2011 2012 2012 2013 2013 2014 2014 2015 2015 2016 2016 2017 2017 2018 2018 2019 2019
Ql 2007 represents the cumulative total prior to and including Ql 207.
1400000
' MW-04 Volume Pumped by Quarter (ga l.)
1200000
1000000
800000
600000
400000
200000
J~
....... ~ -{ • •
... --_ _........
..._J ... . . -. ,.... ~---. . ..... -... ---.._.... ... -..... ---... --.... ... ... ....
0 I I I I I ( I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I I , I I I I I
~ ~ t;:,'b t;:,'b t;:,o, t;:,o, ~~ ~~ ~"" ~"" ~'\, ~'\, ~ ~~ ~ ~ ~ ~ ~<o ~<o ~ ~ ~'b ~'b ~ ~ ~~~~~~~~~~~~~~~~~~~~~~~~~~ ~~~~~~~~~~~~~~~~~~~~~~~~~~
Q 1 2007 represents the cumulative total prior to and including Q 1 2007 .
....... ....... N N (JJ
u, 0 u, 0 u, 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 9 0 0 0 0 0 0 0 0
I I I Ql 2015
Q2 2015
Q3 2015
Q4 2015
I I I I II I -t
012016 I I I I f l I ~ .,::a.
I
02 2016 I I I I ~I I 0 ....
03 2016 I I I I~ I I I ~ -C
3
04 2016 I I I I t I I I t1)
"tJ
012011 I I I I \ I I I C
3
"C
02 2011 I I I t I I I t1) a.
CT
03 2011 I I I ~ I I 1 < ,:,
C
04 2011 I I I ,1 I I I OJ
""'l ,...
t1)
012018 I I I # I I I ""'l -OQ
Q2 2018 j V OJ -• -
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
.... .... N N w u, 0 u, 0 u, 0 0 0 0 0 0 0 0 0 0 0 0 0 9 9 0 0 9 0 0
0 0 0 0 0 0 0
I I I Ql 2015
Q2 2015
Q3 2015
Q4 2015
I I I I I I I -t
012016 I I I I I t I I ~ .a:::-I
02 2016 I I I I I> I 0 N
Q3 2016 I I I I < I I ~ -C
04 2016 I I I ~ 3
tD
"tJ
012011 I I I I C
3
"C
02 2017 I I I 1 I I tD a.
C"'
Q3 2011 I I I >I I I <
0 C
04 2011 I I I I I I QJ ... r+ tD
012018 I I I f I I I ... -OQ
Q2 2018 i V QJ -• -
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
.... ....
N .i::,. O'l 00 0 N 0 0 0 0 0 0 0 0 0 0 0 0 0 9 0 0 0 0 0
0 0 0 0 0 0 0
I I I I Ql 2015
Q2 2015
Q3 2015
Q4 2015
I I I I I I -I
012016 I I f l I I I :E ~ I
02 2016 I I >I I I I ~
~
Q3 2016 I I f I I I I ~ -C
Q4 2016 I I t I I I I 3
ti)
-a
012017 I I t I I C
3
"C
02 2017 I I t I I ti)
Q.
C"'
Q3 2017 I I t I I <
0 C
Q4 2017 I t I I I I I OJ
""I ,..
ti)
012018 I t I I I I I ""I -OQ
OJ
Q2 2018 j I -. -
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
.... ....
N -1:> en 00 0 N
0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 9 0 0 0 9 0 0 0 0 0 0 0
+ Q2 2010
Q3 2010
Q4 2010
Ql 2011
Q2 2011
Q3 2011
Q4 2011
Ql 2012 -I Q2 2012 :E Q3 2012 .,:::.
I Q4 2012 C
Ql 2013 .,:::.
Q2 2013 ~ -Q3 2013 C
Q4 2013 3
Ql 2014 tD
-a Q2 2014 C
Q3 2014 3
Q4 2014 "C tD
Ql 2015 C.
Q2 2015 C"' <
Q3 2015 0 Q4 2015 C
Ql 2016 OJ
~
Q2 2016 tD
""I
Q3 2016 -Q4 2016 OQ
OJ -Ql 2017 • -Q2 2017
Q3 2017
Q4 2017
Ql 2018
Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
MW-26 Volume Pumped by Quarter (gal.)
1000000
900000
800000 ~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
700000 +-11~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
600000 +-11--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
500000 -!-----~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
400000 -!--+-~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
300000 -+---+-~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
200000 -+------~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
100000 -+------~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
....
...--------..,-...... ... ....---------...-----.-----,.-
0 ' m w m w m w m w m w m w m w m w m w m w m w m w m w
20072007200820082009200920102010201120112012201220132013201420142015201520162016201720172018201820192019
QI 2007 represents the cumulative total prior to and including QI 2007.
IO ......
N f--' N w .i,. u, a, -.J 00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 -.J 0 0 0 0 0 0 0 0 ..., 0 0 0 0 0 0 0 0 ('D 0 0 0 0 0 0 0 0 'O 0 0 0 0 0 0 0 0 0 ...,
('D "' ('D Ql 2007 ::, .... Q2 2007 "' .... ::r Q3 2007 ('D
0 Q4 2007 r:: [ Ql 2008
Pol Q2 2008 :;:t. < Q3 2008 ('D .... Q42008 0 .... a Ql 2009 'O ..., Q2 2009 s· ..., Q3 2009 .... 0
Pol Q4 2009 -I ::, Ql 2010 0. =E 5· Q2 2010 0 8" Q3 2010 ~ 0. I 5· Q4 2010 ....
()Q \D IO Ql 2011 ...... Q2 2011 ~ N 0 Q3 2011 0 -:--1 Q4 2011 C
Ql 2012 3
Q2 2012 tD .,,
Q3 2012 C Q4 2012 3 Ql 2013 'C Q2 2013 tD
Q3 2013 Q.
Q4 2013 C'"
Ql 2014 <
Q2 2014 0
Q3 2014 C
DJ
Q4 2014 ..,
r+ Ql 2015 tD
Q2 2015 .., -Q3 2015 OQ
Q4 2015 DJ -Ql 2016 . -Q2 2016
Q3 2016
Q4 2016
Ql 2017
Q2 2017
Q3 2017
Q4 2017
Ql 2018
Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
700000
600000
500000
400000
300000
200000
100000
0
TW4-20 Volume Pumped by Quarter (gal.)
. ~
\
\. -. j -...--T --V ----------T -----
I I I I I I
Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3 Ql Q3
2007 2007 2008 2008 2009 2009 2010 2010 201120112012 2012 2013 2013 2014 2014 2015 2015 2016 2016 2017 2017 2018 2018 2019 2019
Ql 2007 represents the cumulative total prior to and including Ql 2007.
I-"' I-"' I-"' I-"'
N .i:,.. en 00 0 N .i:,.. en 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
-1 I I I I I I I I Q2 2015
Q3 2015
Q4 2015
Ql 2016 i I -I :E
02 2016 I I I I I I I >· I I .a:=-I N ....
03 2016 I I I I I I <. I I I ~ -
04 2016 I I I I I I I I C
3 n,
01 2011 I I ~ I I I I I "ti
C
3
02 2011 I I ~ I I I I I "C n, a.
03 2011 I I I I I ~ I C"' <
04 2011 I I I I I I # I I 0 C
QJ ..,
012018 I I I I I I f l I I r+ n, .., -02 2018 I I I I I I I I I I OQ
QJ -• -I I I I I I I I I I Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
I-' I-' N N w V, 0 V, 0 V, 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0
Ql 2013
Q2 2013
Q3 2013
Q4 2013
Ql 2014
Q2 2014
Q3 2014 I I I I I i , I ~ Q4 2014 I I I I I ~ I ~ I
012015 I I I I I < I N
N
02 2015 I I I I I ' I ~ -Q3 2015 I I I I >I I C
3
Q4 2015 1 \j ff) .,,
Ql 2016 C
02 2016 I I I I I 1.-.> 3
"C
ff)
Q3 2016 1 \ C.
C" Q4 2016 <
01 2011 I I I I I t I I /:)
C
OJ
02 2011 I I I I I ~ I I ~ ff)
Q3 2011 I I I I >I I ""I -Q4 2011 I I I I f I (1Q
OJ -.
Ql 2018 ' .. ' ' -
Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
.... .... N N w
1./1 0 1./1 0 1./1 0 0 0 0 0 0 0 0 8 0 0 0 0
0 0 8 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0
Ql 2013
Q2 2013
Q3 2013
Q4 2013
Ql 2014
Q2 2014 I I I I I I I I -1
Q3 2014 I I I I I~ I 1!
I
Q4 2014 I I I I I 1N ~
012015 I I ~ I I I I ~
02 2015 I I ~ I I I I 1c
Q3 2015 I I '-.... I I I I ,3 t1)
Q4 2015 I I N I I I I -g
C
012016 I I ,A I I I 13
"'C
02 2016 I I r I I I I I n>
C.
03 2016 I ~ I I I I I c-<
04 2016 I I ---; I I I I ,o
012011 I I .A I I I I ~ ..,
02 2011 I Ir""" I I I I I r+ t1) ..,
Q3 2011 I I.....__ I I I I 1-OQ
Q4 2011 I I ~ I I I I ~ • --Ql 2018
Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
..... ..... ..... .....
N .i:::,. CTI 00 0 N .i:::,. CTI 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0
Ql 2013
Q2 2013
Q3 2013
Q4 2013 I I I I I I I "I' I I ~ 012014 I I I I I I I , I I
02 2014 I I I I I I 1, I I .,::.
I N
Q3 2014 1 1/1 u,
Q4 2014 ~
012015 I I I I <T I I I I -C
02 2015 I I I I I ~ I I I 3
tD
03 2015 I I I I I I ~ I I '"tJ
Q4 2015 I I I I I I fl I I C
3 012016 I I I I I I ~I I I "'C
02 2016 I I I I I I J> I I tD a.
03 2016 I I I I I I Y I I I c-< 04 2016 I I I I I ~ I I I /:)
Ql 2017 I I I I I I I C
QJ
02 2011 I I I I I ~ I I I mt ~
Q3 2011 I I I I I I i, I I tD
mt
Q4 2011 I I I I I I f l I I ........
CJQ
012018 I I I I I I t i I I
QJ -• ........ -' Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
6Wl £0
6Wl l0
6Wl l0
8Wl vO
8,:0l £0 -• -ns 8Wl l0 bO -~ cu ~ 8Wl l0
ns :, LWl vO a
> .c LWl £0
"'C cu a. LWl lO
E :,
Q. LWl lO
cu
E 9Wl vO :, -~ 9Wl £0
" M I 9Wl l0 '11:t s I-9Wl tO
SWl vO
SWl £0
SWl lO
q q 0 0 0 0 0 0
0 0 0 0 0 c:i c:i c:i 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 -=:t N 0 00 U) -=:t N ..-t ..-t ..-t
61:0ZEO
610ZZ0
610Z "lO
-• 81:0Z 170 -ns bO -... cu ..., 81:0ZEO ... ns ::s
CJ
> 810Z ZO .c
"'C cu a.
E 81:0Z "lO
::s
C.
cu
E LWl 170
::s -0 > en LWlEO
M
I ~ ~ LWllO I-
LWl "lO
9Wl 170
q 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 N 0 00 \D "d" N .-t .-t
6Wl£0 -• -n,
bD -... cu ~ n, :, a
> .a
"'C cu a.
E :,
Q.
cu
E :, -~
0 ~ I 6WllD ~ 3: I-
0 0 0 0 0 0 q 0
0 0 ci ci ci ci 0 ci
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 <::t N 0 00 lO <::t N .-,j .-,j .-,j
-• -ns bO -'-cu ...,
'-ns ::, a
> .a
-c cu
~
E ::,
CL
cu
E ::, -0 > ....
~ I ~ 3: I-
0 ci 0 0 0 00
0 ci 0 0 0 "
q
0 0 0 0 ID
0 ci 0 0 0
LI')
0 ci 0 0 0 <:t
0 ci 0 0 0 rn
q
0 0 0 0 N
0 ci 0 0 0 .-I
0 ci
6Wlfb
6WltD
6Wll:b
8Wlvb
8Wlfb
8Wllb
TabH
Laboratory Analytical Reports
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909134-00SC
Client Sample ID: MW-04_09042019
Collection Date: 9/4/2019 1402h
Contact: Garrin Palmer
Received Date: 9/6/2019 1030h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/6/2019 2054h
Units: µg/L
Compound
Chloroform
Surrogate Units: µg/L
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
CAS Result Amount Spiked %REC
17060-07-0 1,040 1,000 104
460-00-4 1,020 1,000 102
1868-53-7 992 1,000 99.2
2037-26-5 1,000 1,000 100
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1502h Extracted:
Units: µg/L Dilution Factor: Method:
CAS Reporting
Compound Number Limit
Carbon tetrachloride 56-23-5 1.00
Chloromethane 74-87-3 1.00
Methylene chloride 75-09-2 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4 17060-07-0 49.7 50.00 99.3
Surr: 4-Bromofluorobenzene 460-00-4 49.4 50.00 98.7
Surr: Dibromofluoromethane 1868-53-7 49.0 50.00 98.0
Surr: Toluene-d8 2037-26-5 49.2 50.00 98.3
SW8260D
Analytical
Result Qual
1,180
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/20/2019 Page 30 of 48
All annlyses opplicob1c U) 1111~ CWA. SOWA. tutd RC'RA are perfom1ed in accordance to NELAC protocols. rctlmc.nt sampling information is located on the auached COC. Confidential Business Information: This report is pro,·ided for lhe exclttsi,·e use of the
~ddressee. Prhile~es o~sub!tq~enl ~~e of the '!~~u:orthis .cot~pany or rut~· ~mber of its slaff, or reproducli~! ~r1his repo~ in ~o~eclion~ \\·il.11 the a~~·ertise~enl, P~?moiio.n ~r sale or?-1~Y._~rodl~Cl or P~?cess, ~r in ~onm;,c~ion "'!th th~ r~-publicntion or this report
3440 South 700 West
,alt Lake City, UT 84 I 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-008
Client Sample ID: MW-04_09042019
Collection Date: 9/4/2019 1402h
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/16/2019 1819h
9/9/2019 847h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 41.9
E353.2 0.100 4.69 -------
Report Date: 9/20/2019 Page 13 of 48
All an~lyses applicable 10 lhe CW A. SOWA Md RCRA ore perfom1ed in accordnnce to NELAC pro1qcols. l'i:ttlnC'nl sampling informnlion is located on the nil.ached COC. ('onOdi.-::nlial Ou,imm Information: This repon is pro,·ided for the exclusi\·e use of lhe
~ddressee. P1iyi\e~es orsub,.seq~ent ~1~e or the ~~ne or this 1co1~pnny or nny ~':lber of its stnfT, orn:11mdUCtl~ ~~this repo~ in ~on~1ec1ion .. \\ith lhe <"!~·ertise~ent. p~~moli~ ~i't.1le of~!> ~od~ct or P~?cess, ~r in 7onn;c)ion w11h lh? r:.·p~blicution oCthis report
3440 South 700 West
,alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-005C
Client Sample ID: TW4-01_09042019
Collection Date: 9/4/2019 141 lh
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 1956h
Units: µg/L
Compound
Chloroform
1030h
Extracted:
Dilution Factor: 20
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 894
CAS Result Amount Spiked %REC Limits Qual Phone: (80 I) 263-8686 Surrogate ----------Units: µg/L
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,010
986
988
993
--The reporting limits were raised due to high ana/yte concentrations.
Analyzed: 9/6/2019 1403h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 IOI 72-151
1,000 98.6 80-152
1,000 98.8 72-1 35
1,000 99.3 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 50.2 50.00 IOI 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.3 50.00 IOI 80-152
Surr: Dibromofluoromethane 1868-53-7 49.6 50.00 99.1 72-135
Surr: Toluene-dB 2037-26-5 49.6 50.00 99.2 80-124
Report Date: 9/20/2019 Page 27 of 48
All analyses applicable to lhcCWA. SOWA.. Md RCRA are perfom1ed in occordance to NELAC protocols. Pmfn('.nl sampling information is located on the attached COC. Conliden1ial Business Jnformal1on: This reporl is proYided ror the ~,c:lushe 11:U! of the
~ddressee. PriYile~es o,rsu~eq~enl ~,~e of the 1~ru]1u orthis .coi~pany or any ~'!lber of its s!aIT. or reproducli~ ~rthis repo~ in .con~eclion .. "ith the a~~'ertisemenf, P~?moli~n ~r sale of ~!Y. rrod~cl or P~?cess, ~r in ~nn~!ion \\'!lh 1h~ r~-publlct\l.ion t1r1his repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-005
Client Sample ID: TW4-01_09042019
ANALvr1cAL LAeouroA1ra Collection Date: 9/4/2019 141 lh
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/16/2019 l 622h E300.0 1.00 46.0
9/9/2019 843h E353 .2 0.100 1.65 -----
Report Date: 9/20/2019 Page 10 of 48
All an:ilyses e.pplicnble 10 lht CWA. SOW,\, And R('RA are perfom1ed in accordance to NELAC p101ocols. Pcfltncnt samplin!J inform 1100 is located on the a11nc:hed COC. Conlidenliol Business Jnfonnolion: This repon is pro,·ided for lh~ es.clush'('I USO of !he
~ddressc,e. Plivile~es o}'Jub}C"q~ent ~,~e orfha ~!1'.no or lhis .co1~pnny or nny ~mber or its slruf. or l\.1'n>ductlo!! ~~lhis repo~ in ~on~'-'<fion .. ,,ith the n~~·ertise1'!1ent P~?motio.n ~r ~rue of ~!Y. ~rodt~cl or p1:?cess, ~r in ~onn7.c~ion w\lh lh~ r~·p~blicotion or1his repor1
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Ioli Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-0IOC
Client Sample ID: TW4-02_09042019
Collection Date: 9/4/2019 1353h
Received Date: 9/6/2019 1030h
Analytical Results
Extracted:
Contact: Garrin Palmer
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/6/2019 2133h
Units: µg/L Dilution Factor: 20 Method: SW8260D
Compound
Chloroform
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
CAS
Number
67-66-3
Reporting
Limit
20.0
Result Amount Spiked %REC
1,050 1,000 105
1,000 1,000 100
1,010 1,000 101
1,020 1,000 102
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1542h Extracted:
Analytical
Result
797
Limits
Qual
Qual -------
72-151
80-152
72-135
80-124
Units: µg/L Dilution Factor: Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 < 1.00
Chloromethane 74-87-3 1.00 < 1.00
Methylene chloride 75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.4 50.00 IOI 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.7 50.00 99.4 80-152
Surr: Dibromofluoromethane 1868-53-7 48.8 50.00 97.5 72-135
Surr: Toluene-d8 2037-26-5 49.4 50.00 98.8 80-124
Report Date: 9/20/2019 Page 32 of 48
All annl~ ses applicable 10 lhe CWA. SOWA. and RCRA are perrom1ed in accordance 10 NELAC protocols. Pcnintnl sllrnplang information is localed on 1he auached COC. Confidenti.il Bus,neu Jnformalion: This report is pro,·ided for lhe ~c.hsl\·ci use of lhe
~ddressee Pri\ ile~es o: sub .. seq~enl ~~e or the ~~e or I his .co1~pany or any ~mber or ils staff, or reproducll~ ~~1h1s rl!pot! m .con~1ec1ion~ ,,ith the a~~'crtisement, P~?molio.n ~r ~ale of~,, ~rod~ct or P~?Cess, ~r in ~nn~c~io11 w~1h lh~ n;-publ1ca11on of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-010
Client Sample ID: TW4-02_09042019
ANALYTICAL LAeoRAToR1es Collection Date: 9/4/2019 1353h
Received Date: 9/6/2019
Analytical Results
3440 South 700 West Compound Units
,alt Lake City, UT 84119 Chloride
Nitrate/Nitrite (as N)
mg/L
mg/L
1030h
Date
Prepared
Date
Analyzed
9/16/2019 18531!
9/9/2019 849h -------------------------
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Contact: Garrin Palmer
Method
Used
E300.0
E353.2
Reporting
Limit
1.00
0.100
Analytical
Result
40.8
4.79
Qual
----------------------
Report Date: 9/20/2019 Page 15 of 48
All analyses applicable 10 tlus CW A. SOW A. Md RCRA are l)erformed in accordance lo NELAC protocols. Pe11ln~nt sampling i11for111:111cxt is locnled on the allached COC. ConOd~ntiol Ou~nc-ss lnformolion: This report is pro"ided for the e"(CIU!iYe use of the
~cldress~e. P1frile~es of 1u~1cq~enl ~1~e of 1he '!~~1u. or1his _co1~pcmy or any 1~mber of its stRff, or reproduc1ie~ ~f this repo~ in ~o~ccuon. with the ~~·er1ise1~ent. p~~moli~1 or :sctlc of !1' ... I)'_ ~rodl~Cl or p1:?Cess, ~r in 7°1m1;_c~io11 w(lh lh~ r~-pubJicolion of I his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l909320-002C
Client Sample ID: TW4-03_09112019
ANAL rn c AL L AooR AToR, Es Collection Date: 9/11/2019 715h
3440 South 700 West
;alt Lake City, UT 84 I I 9
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2009h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: I ,2-Dichloroelhane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
54.7 50.00 109 72-151
49.4 50.00 98.7 80-152
52.1 50.00 104 72-135
50.4 50.00 101 80-124
Report Date: 10/23/2019 Page 41 of 80
All onalyses applicable 10 1he CWA. SDWA. :ultl RCRA are performed in accordance lo NELAC protocols. Ptnlncnt sampling infonnallou is located on lhe atrnched COC. Confidenlia/ Business Informal ion: This report is prm1ided for the r.'(C'lush-c use of lhe
~ddressee. Pridle~es o. ~u~q~enl ~1~e of ihe ~:"!,c(lrthis .co1~pml) or .my ~mber of iLs staff. 01 rcproduch°'! ~1his rq)()t! i11 ~01~«t1on .. \\ith the ;:i~~·ertise~eill, P~?molio.n ~r sale or~!Y. ~rodl~ct or P~?cess, ~r in ~onn:_c!ion w!th th~ r:_-rJUhhtndoo Qr this report
INORGANIC ANALYTICAL REPORT
3440 South 700 West
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-002
Client Sample ID: TW4-03_09112019
Collection Date: 9/11/2019 715h
Received Date:
Analytical Results
Compound
9/13/2019 1025h
Units
Date
Prepared
,alt Lake City, UT 84119 Chloride mg/L
mg/L
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Nitrate/Nitrite (as N) ----------------
Date
Analyzed
9/19/2019 012h
9/13/2019 1327h
Contact: Tanner Holliday
Method
Used
E300.0
E353.2
Reporting
Limit
1.00
0.100
Analytical
Result
26.0
5.12
Qual
Report Date: 9/30/2019 Page 9 of 80
All analyses applicable lo lhe CWA. SOWA. and RCRA nre perfom1ed in accordance lo NELAC protocols. Per1,,1cnl sampling information is locnLed on the auached COC. Confidentinl Business lnfornu1IIQfl~ This repor1 is prOl·ided for the c~tht:ihc use of lhe
~ddressee. P1frile~es or su~seq~tenl ~·~e of 1he ~~ne of 1his .cm~pany or nny 1~mber of its stalT, or reproducll~ ~~ this repo~ in ~OL~teclio~ \\ilh the a~~·ertiser~enl. P~?motio.n ~r ~ale of ~~Y. ~rodl~Cl ar p~, ~r in ~onm;_c~ion w!th th~ r~-p~bhttdlonor this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mai I: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-00lC
Client Sample ID: TW4-03R_09102019
Collection Date: 9/10/2019 627h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2115h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method:
CAS Reporting
Number Limit
56-23-5 1.00
67-66-3 1.00
74-87-3 1.00
75-09-2 1.00
SW8260D
Analytical
Result
< 1.00
17.6
< 1.00
< 1.00
Qual
$
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual -------
Surr: l ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-dB 2037-26-5
$ -This compound exceeded (low) the control limit for the CCV
54.3 50.00
50.6 50.00
51.7 50.00
51.5 50.00
---
109
IOI
103
103
72-151
80-152
72-135
80-124
Report Date: 10/23/2019 Page 40 of 80
All analyses applicable 10 lhe CWA. SOWA. and RCRA are performed in accordance to NE LAC 11ro1ocols. il'('mm:nt sampling inform.ntion is located on the otlached COC. Coofhkn1ial Bwltlcss Jnform:uion: This rtporl is pro,·ided for 1he exclusi\·e use of 1he
~ddressee. Pri,·ile~es o,r sub~seq~enl ~1;e of 1he ~~1e of this .can_ipany or any 1~mber of its stnJT, or r1.1uoducth~~ ~f lhis repo~ in ~on~1cc1lo1~ ,vith the u~~·ertisement. P~?motio." ~r :snlc of ~1!~-~rod1~cl or P~?Cess, ~r in ~onn~c~ion w!th th~ r~-publication or this repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-001
Client Sample ID: TW4-03R_09102019
Collection Date: 9/10/2019 627h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/19/2019 120h E300.0 1.00 < 1.00
9/13/2019 1326h E353.2 0.100 < 0.100 -----
Report Date: 9/30/2019 Page 8 of 80
All analyses applicable: to the" CWA. SDWA and RCRA rue perfom1ed in accordance 10 NELAC flfQ1ocols. Peninent sampling h1(omQ11oa1 is localed on the attached COC. Con11dentiol Business lnfornuuion: This report is provided for lhe exch1Si,·e use of the
~ddressee. Pririle~es or,su~l!q~nl ~e of lhc ~-t 6( this .co•~pany or any ~mber of its slaff. or rcpNducli~ ~r1his repo~ in ~4!('11()11. \\ilh lhe u~:ertise~enl, P~?moli~n ~r ~aJe of :112): rrodl~l Qr 1>•.~ess, ~r in 7onm;.c!im1 \\'~lh th~ T~-publication or this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909134-006C
Client Sample ID: TW4-04_09042019
Collection Date: 9/4/2019 1425h
Received Date: 9/6/2019
Analytical Results
1030h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/6/2019 2015h
Units: µg/L
Compound
Chlorofonn
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
CAS Result Amount Spiked %REC
17060-07-0 1,040 1,000 104
460-00-4 995 1,000 99.5
I 868-53-7 988 1,000 98.8
2037-26-5 998 1,000 99.8
--The reporting limits were raised due to high ana/yte concentrations.
Analyzed: 9/6/2019 1423h Extracted:
Units: µg/L Dilution Factor: Method:
CAS Reporting
Compound Number Limit
Carbon tetrachloride 56-23-5 1.00
Chloromethane 74-87-3 1.00
Methylene chloride 75-09-2 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.4 50.00 IOI
Surr: 4-Bromofluorobenzene 460-00-4 50.6 50.00 IOI
Surr: Dibromofluoromethane 1868-53-7 50.3 50.00 IOI
Surr: Toluene-d8 2037-26-5 50.6 50.00 IOI
SW8260D
Analytical
Result Qual
989
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/20/2019 Page 28 of 48
All analyses applicable lo lhe CWA. SOW A. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent snmpl111K information is located on the auached COC. Confiden1ial Business Information: This repor1 is pro,·ided ro1 1ht, e.xch~i,·c u:sc of 1he
~ddressee Pri, i\e~es o.r sub..5eq~en1 ~,~e or lhe ~:11,'le or 1his .co1~pany or any 1~mber or ils slalT, or reproducLio~ ~r I his ~?Ol! in ~o~eclion .. \\ith Lhe a~,·ertisemenl. P~?motio.n ~r sale of ?1!~. ~rodt~cl or P~?Cess, ~r in ~onn~c~ion w!th Ill~ r~·puhllc11tl011 or1his report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-006
Client Sample ID: TW4-04_09042019
ANALvT1cAL LAB0RAT0R1es Collection Date: 9/4/2019 1425h
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/16/2019 1639h
9/9/2019 844h ----
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 39.8
E353.2 0.100 6.32
Report Date: 9/20/2019 Page 11 of 48
All nnnlyses opplic.1l>le to lhe CW A. SOWA. and RCRA me performed in f\Ccordance 10 NELAC protocols. Penini:nt stunpHng_ infotm!Jtion is locoted on the nttnched COC. ("onfidcnlinl Busines5 Information: This ri,por1 is prodded for lhe exclusire use of lhe
~ddressee. P1frile~es o,C sub..5e<1~enl ~1~e of the ~~1e of I his .cm~pnny or any ~7mber of its stnrT. or re11roduc11°!? ~\his ft:J>Q'! in ~0t1!~1I°'! \\ilh the n~~·efliser~..ent p~moti~ ~ n le of ~!Y. ~rodl~CI or P~?c~ss, ~r in ~nn!c~ion \\'!th th~ r~·pu1Jlica1ion of I his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
:-mail : [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laborat01y Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-0 l 7C
Client Sample ID: TW4-05_09112019
Collection Date: 9/11/2019 1000h
Received Date: 9/l 3/2019 I 025h
Analytical Results
Analyzed: 9/14/2019 208h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 14.6
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
54.6
48.4
50.8
50.5
-----
50.00 109 72-151
50.00 96.7 80-152
50.00 102 72-135
50.00 IOI 80-124
Report Date: I 0/23/2019 Page 56 of 80
All analyses applicnble to the CWA. SDW A. and RCRA w·e perfom1ed in accordance to NE LAC protocols Pertinent sampling infommlion is located on the au ached COC Confidential Business Information: This report is proYided for the t..~ch~uC' use of the
~ddressee Pri, ile~es o~ sub~seq~enl ~·~e of lhe ~~1e of 1his.co1~pru1y or any ~mber of its staff, or reproducli~ ~f lhis repm~ in .con)1ec1ion~ \\ith the a~, ertiseme11t. P~?motio.n or saJe of~!) ~rodt~cl or P~?cess, ~r in ~nn~c~ion w!th lh~ r:_-pubhclllion of I his report
American West
ANALYTICAL LABOAATOAIF.6
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web : www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-017
Client Sample ID: TW4-05_09112019
Collection Date: 9/11/2019 l OOOh
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2132h
9/13/2019 1400h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 46.1
E353.2 0.100 7.02
Report Date: 9/30/2019 Page 24 of80
All analyses applico1ble 10 lhe CWA. SOWA. ru1d RCRA are perfom1ed m accordance to NELAC protocols. l1e.(11m.!nl sampling infornv.ulon is localed on the altached COC. Conliden1ial Business lnronnalion: This report is provided for \hr c:xchu \~C use of1he
~ddressee. P1iyile~es o_f sub~seq~enl ~·~e of the ~~e of this .co1~pa11y or an~ ~mber of its staIT. or reproducuo1~ ~r1his repo~ in ~on!tetHOO~ \,ith the a~,·ertisement, P~?moli~ or saJe of :1'!~~ ~rodl!'l or p~ocess, ~r in ~nn~c!ion w!d, 1~ r~ .. publimuion of 1his reporl
3440 South 700 West
~alt Lake City, UT 84 I 19
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-0lSC
Client Sample ID: TW4-06_09112019
Collection Date: 9/11/2019 1010h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 227h
Units: µg/L
Extracted:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Dilution Factor:
------
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW82600
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 l.00 15.8
74-87-3 1.00 < l.00 $
75-09-2 1.00 < l.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limitfor the CCV.
55.5
50.8
51.5
50.3
50.00 111 72-151
50.00 102 80-152
50.00 103 72-135
50.00 101 80-124
Report Date: l 0/23/2019 Page 57 of 80
All analyses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC prolocols Pertinenl sampling information is located on the altached COC Confidenlial Business lnformalion: This repor1 is prO\ided for the exclushe use of1he
~cldressee. P1i\ ile~es o.r sub .. seq~1ent ~,~e of the ~~1e of lhis .co1~pan~ or an) ~mbe1 of its slaff, or reproduclio~ ~~ lhis repo~ in ~on~1ection .. \\ilh I.he a~~ ertise~enl. P~?molio,n ~r sale of ?1!) ~roch~cl or P~?cess, ~r in ~nn!c~ion \\'!th lh~ ':publicalion of !his repon
American West
ANALYTICAL LAOORATORIES
3440 South 700 West
,alt Lake City, UT 84 I 19
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-018
Client Sample ID: TW4-06_09112019
Collection Date: 9/11/2019 1010h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2149h
9/13/2019 1401b
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 39.7
E353.2 0.100 0.412
Report Date: 9/30/2019 Page 25 of 80
All analyses applicable to the CW A. SDWA. and RCRA a, e perfom1ed in accordance lo NELAC p101ocols. Perhm:nl sampling i11fomwion is located on the atlached COC. C"onOtknti11113usiness Jnfonnalion: This repor1 is provided for the ~ch~h e U5C of 1he
~ddressee. P1 i, ile~es o.r sub ... seq~ent ~,~e oft he ~~e or I his .co1~pany or nny ~mber of its Slaff, or u:11rotluctl~~ ~! this repo~ in ~1i.:c.t1on .. \\ith the a~,·ertisemenl. P~?moti~ or 53Je ~f !"!~ .~rodl'.Cl or P~?Cess, ~r in ~onn~c~ion w(1h lh~ r~-p~bliccufon of 1his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: I 909320-027C
ClientSampleID: TW4-07_09122019
Collection Date: 9/12/2019 808h
Contact: Tanner Holliday
Received Date:
Analytical Results
9/13/2019 1025h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/18/2019 1639h
Units: µg/L
Compound
Chloroform
Surrogate Units: µg/L ----
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
CAS Result Amount Spiked %REC
17060-07-0 1,000 1,000 100
460-00-4 1,040 1,000 104
1868-53-7 978 1,000 97.8
2037-26-5 1,040 1,000 104
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/18/2019 2139h Extracted:
Units: µg/L Dilution Factor: Method:
CAS Reporting
Compound Number Limit
Carbon tetrachloride 56-23-5 1.00
Chloromethane 74-87-3 1.00
Methylene chloride 75-09-2 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: 1,2-Dichloroethane-d4 I 7060-07-0 49.9 50.00 99.8
Surr: 4-Bromofluorobenzene 460-00-4 50.7 50.00 IOI
Surr: Dibromofluoromethane 1868-53-7 48.4 50.00 96.8
Surr: Toluene-d8 2037-26-5 51.1 50.00 102
SW82600
Analytical
Result Qual
801
Limits Qual
72-151
80-152
72-135
80-124
SW82600
Analytical
Result Qua)
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/30/2019 Page 66 of 80
All analyses applicable 10 the CWA. SDWA. Md RCRA are perfom1ed in Accordance to NELAC protocols. Pertinenl sampling information is localed on tJ,e aUnched COC Confidential Business lnformalion: This report is proyided for lhe exclusi, e use of lhe
~ddressee Pri, ile~es o~ su~seq~enl ~~e of lhe ~~le of this .coi~tpany or an., ~'!1ber of its slruT. or reproductio~ ~f lhis repo~ in _con~eclion~ ,dth the a~~ ertisemenl. p~~molio_n or saJe of~;). ~rc><iL~cl or p~ocess, ~r in c_:onn:c!ion '''!lh th~ r:-publiculion or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-027
Client Sample ID: TW4-07_09122019
A NA L v r 1 c AL LAD o RAToR, Es Collection Date: 9/12/2019 808h
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/21/2019 126h E300.0 1.00 39.7
9/13/2019 1434h E353.2 0.100 3.76
Report Date: 9/30/2019 Page 34 of 80
AJI analyses applicable lo lhe CWA. SOWA. and RCRA are perfom1cd in accordance lo NELAC protocols Pertinent sampling information is locoted on the a.Ltache<I COC. Conlidenlial Business Information: This report is pro,•ided for lhe exc\usi\ e use or lhe
~ddressee Pri\'ile~es o~ sub~seq~enl ~?e of the ~?1:"e of I his .coi~pnny or ony ~'!1ber of its stnJT, or reproduclio~ ~~ this repo~ in .con~eclion .. \\ilh lhe a~, ertisemenl, p~omotio.n or sale or ?1!~ ~rodl~cl or P~?ccss, ~r in ~onn:c~ion w~lh th~ r:-publication or I his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-023C
Client Sample ID: TW4-08_09122019
A NA L vr, c AL LAB oR AToR" s Collection Date: 9/12/2019 717h
3440 South 700 West
,alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1839h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENJOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 75.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
----
50.4 50.00 IOI 72-151
53.0 50.00 106 80-152
48.7 50.00 97.3 72-135
52.4 50.00 105 80-124
Report Date: 9/30/2019 Page 62 of 80
All an.llyses applicable 10 the CW A. SD\V A. and RCRA are performed in nccordance to NELAC pro1occ,I$. Pertinenl snmpling infom111hon is locoted on 1he atlnched COC. Confidenlial OUiincss Information: This report is pro,·ided for 1hci exclusiYe use of the
~ddressee Pri, ile~es of sub__seq~enl ~,~e of the ~~e or this .co1~pwiy or any ~t;mber of its staff orn:1,rCMHlc:1io~ ~f this repo~ in ~on!1ccU~ wil.h the a~,·ertisement, P~?moti°:° ~r ~ale of~· ~rod,~t or p~~ess, ~r in ?>""~Jion '''!lh II~ r~ublicotion of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-023
Client Sample ID: TW4-08_09122019
Collection Date: 9/12/2019 717h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 019h
9/13/2019 1417h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 52.0
E353.2 0.100 0.999
Report Date: 9/30/2019 Page 30 of 80
All anal~ ses upplic:tble 10 lhe CWA. SOWA. Md RCRA are perfom1ed in accordance lo NELAC p1otocols. Pe11inenl sampling infonnation is localed on the attached COC Conf1denlial Business Information: This report is pro,•ided for lhe exclusi\"e use of lhe
~ddressee P,i, ile~es o~ sub,.seq~enl ~,~e of !he ~!1'?1e of this .co1~pan~ or an~· ,~mber of its Slaff, or reproduclio~ ~f this repo~ in ~on?eclion,, \\ilh the a~, ertiseme.nl. P~?moli~ ~r sale of ~r. ~rodl~Ct or p~ocess, ~r in ~onn~c!ion w!lh lh~ r~-publicalion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-021C
Client Sample ID: TW4-09 _09112019
ANALvr1cAL LABoRATo R 1r-s Collection Date: 9/11/2019 1045h
3440 South 700 West
,alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1759h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 66.0
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0 50.6
460-00-4 53.0
1868-53-7 49.4
2037-26-5 52.5
---
50.00 IOI 72-151
50.00 106 80-152
50.00 98.7 72-135
50.00 105 80-124
Report Date: 9/30/2019 Page 60 of 80
All nnnlyses applicable 10 1hc CWA. SDW ,\. tu•d RCRA are rierfom1ed in accordance to NELAC pmlocolJ P~runcnl samphny information is localed on the auached COC. Confrdenlial 13UJtntss lnformalion: This repon is pro,·ided for lhe c:-.,clu:J,·e use of lhe
~ddressee. Pri\·ile~es o:,u~tq~enl ~·~e oflbt.1 ~~!'1e brlhis .co1~pany or any 1~ml>er or its slafT, or rquoduct ~ ~f\his rq)O(! in ~on~ect1on~ \\ith lhe a~~'e11ise1~e111. P~?molio.n ~r saJe of ~J.J?-Odl~cl or P~?cess, ~r in ';O""t;.c!ion w!lh 1h~ H:-pubho:uiw of 1his repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-021
Client Sample ID: TW4-09_09112019
A NA L vr, c A 1. 1 ABoR AroR, Es Collection Date: 9/11/2019 1045h
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratmy Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/20/2019 2346h E300.0 1.00 35.2
9/13/2019 1407h E353.2 0.100 0.904
Report Date: 9/30/2019 Page 28 of 80
All anal~ ses applicable lo the CW A. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infonnntion is located on lhe allached COC Confidential Business Information: This report is prm•ided for the exclusi, e use of the
~ddressee P1frile~es o! sub~seq~enl ~~e or the ~~1e of lhis .c01~pm1y or ony ~mber of iLs sill.ff, or reproduclio~ ~r this repo~ in ~011~1eclion~ \\"ith the a~, ertisement, p~omotio.n 01 sa1e of ?1!~. ~rod1~cl or P~?cess, ~r in :onn:c~ion "~th th~ r~-publication or I his repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-026C
Client Sample ID: TW4-I0_09122019
ANALYTICAL LA00RAT0R1es Collection Date: 9/12/2019 754h
Contact: Tanner Holliday
Received Date: 9/13/2019 1025h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
~alt Lake City, UT 841 19
Analyzed: 9/18/2019 1619h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
----------------
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,010
1,040
994
1,030
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 9/18/2019 2119h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
1,000 IOI
1,000 104
1,000 99.4
1,000 103
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: 1,2-Dichloroethane-d4 17060-07-0 49.4 50.00 98.7
Surr: 4-Bromofluorobenzene 460-00-4 52.3 50.00 105
Surr: Dibromofluoromethane 1868-53-7 48.2 50.00 96.5
Surr: Toluene-d8 2037-26-5 52.3 50.00 105
SW8260D
Analytical
Result Qual
734
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qua!
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/30/2019 Page 65 of80
All annl~ ses applicable 10 lhe CWA. SDWA. ru1d RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is localed on the auache<l COC Confidentinl Business lnfonnnlion: This report is pro, ided for the exclusi, e use of the
~ddressee Pri\·ile~es o~ sub.:,;eq~ent ~,~e of the ~~1e of I his .co1~pany or rm~ 1~1!1ber of its stafT, or reproductio~ ~f this repo1; in .con~1~c1ion .. \Vith lhe n~, ertisemenL, P~?motio.n or sale of~~~ ~rochict or p1.ocess, ~r in :-°nn:c~ion w!th th~ r:-publication of this repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-026
Client Sample ID: TW4-I0_09122019
Collection Date: 9/12/2019 754h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 109h
9/13/2019 1433h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 55.8
E353.2 0.100 7.79
Report Date: 9/30/2019 Page 33 of 80
All anal~ ses applicable to the CWA. SDW A. and RCRA ure perfom1ed in accordance lo NELAC prolocols Pertinent sampling infomtation is locnled on the auached COC Confidenlinl Business Information: This repor1 is provided for the exclusive use of the
~ddressee Pri, ile~es o.f sub_,seq~enl ~;e of the ~~le of lhis .co1~pany or an~ ~mber of its sla/T. or reproduclio~ ~f lhis tepo~ in ~on?ection ... l\ith !he 3<!,et1isemenl, P~?moti~n 01 sale of~~~. ~rodl~CI or p~ocess, ~r in ~nn~c!ion \\'!lh 1h~ r~-publical.ion of this report
3440 South 700 West
~alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-01 lC
Client Sample ID: TW4-11_09042019
Collection Date: 9/4/2019 1345h
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 2153h
Units: µg/L
Compound
Chloroform
1030h
Extracted:
Dilution Factor: 20
CAS
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 2,790
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
-------------------
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,060
1,010
1,010
1,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1601h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
---
1,000 106 72-151
1,000 101 80-152
1,000 101 72-135
1,000 IOI 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual ---
Surr: 1,2-Dichloroethane-d4 17060-07-0 51.2 50.00 103 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.4 50.00 101 80-152
Surr: Dibromofluoromethane 1868-53-7 50.2 50.00 100 72-135
Surr: Toluene-d8 2037-26-5 50.3 50.00 IOI 80-124
Report Date: 9/20/2019 Page 33 of 48
All analyses applicable lo 1he CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pe11inenl sampling information is localed on lhe allached COC. Confidential Business lnformalion: This repon is provided ror lhe exclushe use or the
~ddressee Pri\ ile~es o: sub,,seq~ent ~e of !he ~~e or I his .c01,:1pnny or nn) ~mber of its siaJT. or reproductio~ ~rt his repo~ in _co~eclion,. ,,ilh the a~,·ertisemenl. P~?motio.n or saJe of~!~ rrodl~ct or p~ocess, ~r in ~onm;c~ion \\'!th 1h~ r1;:-publicaLion or rhis repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909134-011
Client Sample ID: TW4-l 1_09042019
Collection Date: 9/4/2019 1345h
Received Date: 9/6/2019 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/201 9 1909h E300.0 1.00 48.8
Nitrate/Nitrite (as N) mg/L 9/9/2019 850h E353.2 0.100 7.15
Report Date: 9/20/2019 Page 16 of 48
All anal~ ses applicable lo lhe CWA. SOWA. and RCRA i:ue perfom1ed in accordance to NELAC prolocols. Peninenl sampling information is localed on the attached COC Confidential Business lnformolion: This report is proYided for 1he exclusive use of1he
~ddressee P1i\·ile~es of' sub .. seq~ent ~~e or 1he ~~e or lhis .con,ipony or nny ~'!'be1 of its slnff. or reproduclio~ ~f this repm; in .con~eclion ... ,,,ith the a~,·ertisemenl, P~?molio.n 01·sale of ~!Y ~rodl~Cl or p~ocess, ~r in ~onn~c~ion w/th th? r:-p~blicotion of this 1eport
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l909320-005C
Client Sample ID: TW4-12_09112019
Collection Date: 9/11/2019 755h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2213h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual ---------
Surr: l,2-Dichloroethane-d4 17060-07-0 54.2 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.0 50.00 97.9 80-152
Surr: Dibromofluoromethane 1868-53-7 50.7 50.00 IOI 72-135
Surr: Toluene-d8 2037-26-5 49.9 50.00 99.8 80-124
$ -This compound exceeded (low) the control limit for the CCV.
Report Date: I 0/23/2019 Page 44 of 80
All nn:ilyses applicable 10 lhe CWA. SOWA. and RCRA are perfomled in acco,dance lo NELAC ruo1ocols.. P<'.11mmt sampling inform:mon is located on lhe attached COC. Confidenlial Business lnfonnalion: This report is pro,·ided forthe exchtsiw use of the
~ddressee. Pri,·ile~es o_f sub~seq~ent .u~e of the ~~1e of this .co1~pany or any 1~mber or its stafT, or r1.:1uQduc11or, ~r1his repo~ in ~011~u.-c11onr \\ilh lhe a~Yertisement, p~~moli<>_n ~r ~ale of ?-1~Y. ~roclL~l or P~?Cess, ~r in ~nn:c.Lion w!lh 1h~ r!·publication oflhis report
3440 South 700 West
;alt Lake City, UT 84 J 19
Phone: (80 J) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-005
Client Sample ID: TW4-12_09112019
Collection Date: 9/11/2019 755h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 229h
9/13/2019 1341h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 52.6
E353.2 0.100 8.88
Report Date: 9/30/2019 Page 12 of80
All analyses applicable 10 lheCWA. SOWA. and RCRA aie perfom1ed in accordance 10 NELAC protocols Pertinent sampling infomuu.ion is located on the ellnched COC Confidenlinl Business lnformarion: This repon is pro\'ided for the exclushe use oflhe
addressee Pri, iteges of subsequent use of the name or1his company or an, member of its staff. or reproduclion of I.his report in co1U1eclion \\ilh the adYertisemenl. promotion or sale of nn~ p1 oducl or process, or in conn~tion with the re-publico.tion of lhis repor\
.. • • ~ • •• ..!. • • --··· • • • ,.. ,. •• • • • ,.. '' • •• • • ~' ' • ,.
American West
ANALYTICAL I ABORATORlfS
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-006C
Client Sample ID: TW4-13_09112019
Collection Date: 9/11/2019 804h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2233h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 55.2 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.8 50.00 99.6 80-152
Surr: Dibromofluoromethane 1868-53-7 52.0 50.00 104 72-135
Surr: Toluene-d8 2037-26-5 50.0 50.00 100 80-124
$ -This compound exceeded (low) the control limit for the CCV
Report Date: I 0/23/2019 Page 45 of 80
All anal~ ses applicable to the CWA. SDWA. and RCRA rue perfom1ed in accordance lo NELAC prolocols_ Pertinent sampling infonnotion is localed on the attached COC Confirlentio\ Business Information: This reporl is pro\'ided for lhe e~clusi, e use of the
~ddressee Prl\"ile~es o: su~seg~1enl ~·~e of the ~'.11:"e of I his .co~pany or an~· 1~mber of its slnIT. or reproduclio~ ~r U1is repo~ in ~0~1ec11on .. \\iU1 the a~vertisemenL P~?motio.n ~r sale of~~). ~rodl)CI or P~?cess, ~r in 7onn:_c~ion w!th th~ n;-publicotion of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-006
Client Sample ID: TW4-13_09112019
ANALvr,cAL LAooRAroR1Es Collection Date: 9/11/2019 804h
3440 South 700 West
;alt Lake City, UT 84 I 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/19/20 J 9 246h E300.0 1.00 65.3
9/13/2019 1342h E353.2 0.100 5.19
Report Date: 9/30/2019 Page 13 of80
All anal) ses applicable 10 the CWA. SOWA, and RCRA ore perfom1ed in accordance to NELAC protocols Pertinent sampling infom1alion is localed on the attached COC Confidential Business Information: This repon is pro,·ided for the exclusi\'e use of the
~ddressee, Pri, ile~es o!' sub~seg~enl ~~e or the ~~1e of this .co1~pan~ or an~ r~_:mbcr or its stafT, or reproduclio~ ~f this repo~ in ~on~1eclion~ ,,ith lhe a~vertisement p~omotio.n or saJe or :11!~ ~rodt~ct or p~ocess, ~r in 7onn!c~ion ,,·!th th! r:-publication or I his repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-015C
Client Sample ID: TW4-l4_09l 12019
ANALYTICAL LAB0RAT0R1Es Collection Date: 9/11/2019 940h
3440 South 700 West
;aJt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 129h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 6.08
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Phone: (80 I) 263-8686
Toll Free: [phone]
fax: (80 I) 263-8687
!-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV
55.4 50.00 1 ll 72-151
50.0 50.00 100 80-152
50.6 50.00 101 72-135
SO.I 50.00 100 80-124
Report Date: I 0/23/2019 Page 54 of 80
All .analyses applicable lo 1hc \ A. SDWA. and RCRA ore perrom1ed in R.Ccordance lo NELAC protocols Pe11inen1 sampling information is located oi1 tJ1e altached COC Conlidential Business Information: This report is pr°' ided ror lhe exclusi\e use or1he
~ddressee. Pri,·ile~es o~~u~~K'nl ~~e of the ~~e of this .co,~pany or any '~'!'ber of its slaff, or reproduclio~ ~f this repo~ in ~01~1ection .. \\ith lhe a~vertisement, p~~moli~ or sale of~!~· rrod1~c1 or p~ocess, ~r in ~nn:_c~ion \\'~lh th? r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-015
Client Sample ID: TW4-14_09112019
Collection Date: 9/ 11/2019 940h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2059h
9/13/2019 1358h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 45.4
E353.2 0.100 4.77
Report Date: 9/30/2019 Page 22 of 80
All analyses applicable lo lhe CWA. SOW A. and RCRA are perfom1ed in occordance lo NELAC protocols. Pertinenl sampling information is located on lhe auached COC C'onridential Business Jnfo11nat1on: This repor1 is pro,·ided for lhe exclusi\e use of lhe
~ddressee Pri, ile~es or su~seq~tenl ~1~e of lhe ~~le of I his .co1~pttny or nny ~mbe1 of its slruf, or reproductio~ ~f this repo~ in ~on~1eclion .. \\ilh lhe a~;ertise1'!1ent P~?moli~n ~1 sale of?'!~. ~rodt)Ct or p~ocess, ~r in ~nne;:~ion "!th th~ r~-publicaLion of lhis reporl
Client:
Project:
Lab Sample ID:
ORGANIC ANALYTICAL REPORT
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
l 909 l 34-007C
Contact: Garrin Palmer
American West Client Sample ID: MW-26 09042019
ANALYTICAL LAaoRAToR1es Collection Date: 9/4/2019 1330h
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C Analytical Results
Analyzed: 9/6/2019 2035h Extracted:
Units: µg/L Dilution Factor: 20 Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 20.0 1,360
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 1,050 1,000 105 72-151
Surr: 4-Bromofluorobenzene 460-00-4 1,010 1,000 101 80-152
Surr: Dibromofluoromethane 1868-53-7 1,000 1,000 100 72-135
Surr: Toluene-d8 2037-26-5 1,010 1,000 101 80-124
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1443h Extracted:
Units: µg/L Dilution Factor: Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 < 1.00
Chloromethane 74-87-3 1.00 < 1.00
Methylene chloride 75-09-2 1.00 1.93
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 50.6 50.00 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.8 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 49.9 50.00 99.7 72-135
Surr: Toluene-d8 2037-26-5 50.4 50.00 101 80-124
Report Date: 9/20/2019 Page 29 of 48
All anal) ses apµlicnble lo the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on Lhe attached COC Confidenlial Business lnformat1on: This report is provided for lhe exclusi\e use of1he
~ddressee Pri,·ile~es o.f su~seq~enl ~1~e of the ~?1,11e or lhis
1
co1~pany or any ~mber or its slaIT, or reproduclio~ .~f this repo~ in ~on~eclion .. Wilh the a~vertisemenl. P~?moti~n ~1 sale of~!~ ~rodl~Cl or p1
1
ocess, ~r in ~onrn;.c!ion w~lh th~ r~-publication or this report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-007
Client Sample ID: MW-26_09042019
Collection Date: 9/4/2019 1330h
Received Date: 9/6/2019 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/2019 1729h E300.0 1.00 76.2
Nitrate/Nitrite (as N) mg/L 9/9/2019 845h E353.2 0.100 3.08
Report Date: 9/20/2019 Page 12 of 48
All armt, ses applicable lo the CWA. SOWA, and RCRA me performed in accordMce to NE LAC prolocols Pe11inent sampling information is located Oil the ottnched COC C'onfidenlinl Business Information: This rnpor1 is prol'ided for the e;\;clusi,'e use of lhe
~ddressee Pri,·ile~es o,f sub..5eq~ent ~1~e of 1he ~~1e of this .cm~pnny or cu1y ~mbe1 of its stnfT. or rel)roductio~ ~f 1his repo1; in fOn~1t:ic1ion .. with the o~~·ertisement. p~omoli~ ~r sale of~!~. ~1 och~ct or P~?Cess, ~1 in ~nn~c!ion w!lh th~ r:-p~blico.tion or this 1eport
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-022C
Client Sample ID: TW4-16_09122019
ANALYTICAL LAB0RAT0A1Es Collection Date: 9/12/2019 708h
3440 South 700 West
;alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1819h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 99.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
49.5 50.00 99.0 72-151
52.0 50.00 104 80-152
47.9 50.00 95.8 72-135
51.3 50.00 103 80-124
Report Date: 9/30/2019 Page 61 of80
All annl) ses applicable 10 lhe CWA. SDWA. and RCRA rue perfom\ed in f\CCOrdance 10 NELAC protocols Pertinent sampling information is located on the altached COC Confatential Business Jn[ormation: This report is prodded for the exclnsi, e use of1he
~ddressee Pai, ile~es of sub .. seq~enl ~·~e of the ~~1e of this
0
co1~pany or ilrl~ ~mber or its stafT, or reµroduclio~ ~f this repo~ in ~0~1ection,. with the a~yertisement, P~?motio.n or saJe of~~) ~rodl~ct or p~ocess, ~r in :onm;_c~ion \\~th th~ 1:_-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-022
Client Sample ID: TW4-16_09122019
Collection Date: 9/12/2019 708h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 003h
9/13/2019 1416h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 72.9
E353.2 0.100 3.55
Report Date: 9/30/2019 Page 29 of 80
All amd) ses applicable lo the CWA. SOWA. and RCRA are perfom1ed in nccorclnnce to NELAC protocols. Pertinent sampling information is located on the altached COC Confldenlial Business lnfonnalion: This report is provided for 1he e.xclusi, e use of the
~ddressee Prl\ ile~es o~ sub~seq~t ~e of the ~~e of this .co1~pru1y or any ~mber of ils slaff, or repmduclio~ ~f lhis repo~ in ~on~eclion,.. ,,ith the n~,er1isement, p~omotio.n or sale of~!) ~1odl~l or p~ocess, ~r in ~1m~!ion ''!th th~ r:_-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-029C
Client Sample ID: TW4-l6R_09112019
Collection Date: 9/11/2019 11 lOh
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1919h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 19.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
49.8
50.l
48.7
51.0
50.00 99.5 72-151
50.00 100 80-152
50.00 97.3 72-135
50.00 102 80-124
Report Date: 9/30/2019 Page 68 of 80
All an.ii~ ses opplic.1ble to the CWA. SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols Pertinenl sampling information is localed on the allached COC Conlidenlia/ Business lnformalion: This repor1 is pro\ ided for lhe exclush·e use of the
~ddressee Pri, ile~es o_f sub~seq~1ent ~e orlhe ~~ne or this .con:ipany or an) ~mber ori1s stn(T, or reproduclio~ ~r this repo~ in ~on~echon~ with the a~, ertisemenl, p~omo1io.n ~r saJe or~!) ~rod~cl or p~ocess, ~r in ?'nn~c!ion \\~th th~ rt;·publica.tion of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-029
Client Sample ID: TW4-16R_09112019
Collection Date: 9/11/2019 11 lOh
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 200h
9/13/2019 I 444h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 9/30/2019 Page 36 of 80
All anal) ses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordMce to NELAC protocols. Peninenl sampling information is located on 1he attached COC Conndential Business Information; This report is prO\ ided for the exclusi\ e use or1he
~ddressee, P1i\'ile~es a; sub~seq~enl ~,~e of 1he ~~1e or lhis .co1~pan~ or nn~ 1~mber of its staff or reproduclio~ ~f this repo~ in ~ofl;lection~ \\ith Lhe u~: er1iseme111 p~omotio.n ~1 sa1e of '.11!)~ ~rodl~cl or p~ocess, ~r in ~nn!c~ion w~lh 1h: r~-publication of !his repon
American West ANALYTICAi. LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-0BC
Client Sample ID: MW-32_09112019
Collection Date: 9/11/2019 1435h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 050h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55.5 50.00 Ill 72-151
49.6 50.00 99.2 80-152
52.5 50.00 105 72-135
50.7 50.00 101 80-124
Report Date: I0/23/2019 Page 52 of 80
All anal~ ses applicable lo the CWA. SOW A. and RCRA are pcrfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the altached COC. Conftden1ial Business Information: This report is pro,·ided for lhe exclush e use of the
~ddressee Pri, ile~es o~ sub .. seq~1ent ~~e of the ~~1e of lhis .co,~pany or any ~mber of its s1:uf, or reproducli~ ~f this repo~ in ~11!1eclionr ,,ith 1he a~\ertise~enl. P~?motio.n ~r snJe of~!~ ~1odi~cl or p~ocess, ~r in 7°"":.C!ion \\'!th lh~ r:_·publicalion of 1his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-013
Client Sample ID: MW-32_09112019
Collection Date: 9/11/2019 1435h
Received Date: 9/13/2019 I025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9no12019 2026h
9/13/2019 1424h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
EJOO.O l.00 33.7
E353.2 0.100 < 0.100
Report Date: 9/30/2019 Page 20 of 80
AIJ .analyses applicable lo the CW A. SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols Pertinenl sampling information is located on lhe Bllached COC. Confidentinl Business Jnfonnolion: This repon is pro, ided for lhe exclush e use of lhe
~ddressee Pri, ile~es o_f sub~seq~enl ~e of lhe ~~e of this .co1~pany or an~ ~mber of its staff. or reproduc1io~ ~fl.his repo~ in ~on~ieclion .. "ilh the a~Yertisemenl, P~?moli~n ~r sale of ~!Y, ~rodl~ct or p~ocess, ~r in ~onn~c!ion '''!lh 1h~ r~-publication of I his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: I909320-020C
Client Sample ID: TW4-I8_09112019
Collection Date: 9/11/2019 1035h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 306h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 56.2
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit f or the CCV.
55.6
50.6
52.4
51.9
50.00 Ill 72-151
50.00 IOI 80-152
50.00 105 72-135
50.00 104 80-124
Report Date: 10/23/2019 Page 59 of80
All anal~ ses applicable to !he CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on tJ1e altnched COC Confidential Business Information: This report is pro\•ided for the e:'\:clush e use orthe
~ddressee Pririle~es o:sub .. seq~nt ~1~e of lhe ~~1e of this .con:1pru1y or nny 1~7mber of ils staJT, or reproductio~ ~f lhis repo~ in .co1~1~ction,. \\ilh lhe a~vertisemenl.,. P~?molio.n ~· saJe of~!~ ~rod1~cl or p~ocess, ~r in ~nn:c!ion \\!lh lh~ r:_-publication or this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-020
Client Sample ID: TW4-18_09112019
Collection Date: 9/11/2019 1035h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2256h
9/13/2019 1404h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 36.8
E353.2 0.100 3.25
Report Date: 9/30/2019 Page 27 of80
All anal)ses applicable to the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the auached COC Conlidential Business lnfol'lnalion: This repor1 is provided for the exclusi, e use or1he
~ddressee Pri, ile~es o~ sub ... seq~enl ~~e of the ~?1:',e of this .co1~pan> or an) 1~mber of ils staJT, or reproduclio~ ~r this repo~ in 0Con'.1ection ... \\ilh the a~: ertise~enl, P~?motio.n ':r ~ale of~!). ~1odL~Cl or P•.?cess, ~r in :onn:c!ion \\'!th lh~ n;_-p~blication or this 1eport
Client:
Project:
Lab Sample ID:
ORGANIC ANALYTICAL REPORT
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909134-014C
Contact: Garrin Palmer
Client Sample ID: TW4-19 09042019
Collection Date: 9/4/2019
Received Date: 9/6/2019
Analytical Results
1445h
1030h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 9/6/2019 2251h
Units: µg/L
Compound
Chloroform
Phone: [phone] Surrogate Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 100 Method:
CAS Reporting
Number Limit
67-66-3 100
CAS Result Amount Spiked %REC
17060-07-0 5,240 5,000 105
460-00-4 4,930 5,000 98.5
1868-53-7 5,010 5,000 100
2037-26-5 5,020 5,000 101
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 9/7/2019 049h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor: Method:
CAS Reporting
Number Limit
56-23-5 1.00
74-87-3 1.00
75-09-2 1.00
CAS Result Amount Spiked %REC
17060-07-0 52.0 50.00 104
460-00-4 50.2 50.00 100
1868-53-7 49.9 50.00 99.8
2037-26-5 49.6 50.00 99.2
SW8260D
Analytical
Result Qual
6,670
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
10.1
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/20/2019 Page 36 of 48
All anal~ses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Per1inent sampling information is located on the allached COC. Confidential Business Information: This report is provided for lhe exclusive use of the
~ddressee Pri,·ile~es o_f sub,,seq~enl ~1~e of the ~~e of this .crn~pany or an) ~mber of its slaff, or reproduclio~ ~fth1s repo~ in ,co~eclion ... ,vilh Lhe a~:er1isement. p~omotio.n o,·sale of ?1!) frod1ict or p~ocess, ~r in ~nn~c!ion w~th lh~ r~-p~blicalion of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-014
Client Sample ID: TW4-19 _09042019
Collection Date: 9/4/2019 1445h
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/16/2019 1959h
9/9/2019 854h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
£300.0 5.00 153
£353.2 0.100 0.332
Report Date: 9/20/2019 Page 19 of 48
All onal~ ses applicoble to the CWA. SDWA, and RCRA nre perfom1ed in accordance to NELAC p1olocols Pertinenl sampling i11fornuuion is located oi1 the attached COC. Conliden1ial Business Information: This repon is proyided for 1he exclusiYe use of lhe
~ddressee Pri\ ile~es o.r sub,.seq~ent ~~e of the ~~1e of this .cm~pany or nn) •~l_!lber of its slruT. or reproduclio_~ ~r this repo11 in .co~eclion,, \\ilh the a~,·ertisemenl, P~?motio.n ~r sale of ?1!~, ~rod~cl or p~ocess, ~r in :°nn~~ion w!lh 1h7 r:_·publicotion of lhis repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-015C
Client Sample ID: TW4-20_09042019
Collection Date: 9/4/2019 1314h
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 2311h
Units: µg/L
Compound
Chloroform
1030h
Extracted:
Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 10,500
Phone: (80 J) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
-------------
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,220
4,980
5,020
5,000
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/7/2019 109h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
5,000 104 72-151
5,000 99.6 80-152
5,000 100 72-135
5,000 100 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 8.39
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Surr: l ,2-Dichloroethane-d4 17060-07-0 48.5 50.00 97.1 72-151
Surr: 4-Bromofluorobenzene 460-00-4 47.1 50.00 94.2 80-152
Surr: Dibromofluoromethane 1868-53-7 45.0 50.00 90.0 72-135
Surr: Toluene-d8 2037-26-5 47.4 50.00 94.7 80-124
Report Date: 9/20/2019 Page 3 7 of 48
All annlyses applicable lo the CWA. SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols Pertinent sampling information is located on the allached COC. Confidential Business Jnformation: This repon is prO\ idcd for lhe exclushe use of the
~ddressee Pri, ile~es o!' sub .. seq~enl ~~e of the ~~1e or this .co1~pnny or an~ 1~mber or its sta!T. or reproduclim~ ~f this repo~ in .co11~1eclion .. \\illl 1he il~~ertisemenl. P~?molio.n ~r saJe of '.11!~ ~rod1~cl or p~ocess, ~r in ~onm~c~ion 11·~th lh~ r~-publication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-015
Client Sample ID: TW4-20_09042019
ANALvncAL LAeoRAToR1Ea Collection Date: 9/4/2019 1314h
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/1 6/2019 2050h E300.0 5.00 286
9/9/2019 900h E353.2 0.100 10.2
Report Date: 9/20/2019 Page 20 of 48
All anal) ses epplicnble lo the CW A. SOWA. and RCRA are perfomted in accordance 10 NELAC protocols Pertinenl sampling information is located on lhe auached COC Confidenlial Business lnformalion: This repon is prO\ ided for the exclusive use of !he
~ddressee P1ivile~es o,r sub,_seq~enl ~~e or1he ~~e of this .co1~pany or nny 1~mbe1' of its staJT. or reproduclio~ ~r this repo~ in ~on?ection .. with the a~~·ertisemenl P~?moli~ ':r sale of ?1!). ~rod~ct or P~?cess, ~r in ~onn~c!ion w!th th~ r~-publication of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-004C
Client Sample ID: TW4-21_09042019
ANALvT,cAL LAB0RAT0R1E11 Collection Date: 9/4/2019 1228h
3440 South 700 West
,alt Lake City, UT 84119
Received Date: 9/6/2019 1030h
Analytical Results
Analyzed: 9/6/2019 1936h
Units: µg /L
Compound
Chloroform
Extracted:
Dilution Factor: 20
CAS
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 596
CAS Result Amount Spiked %REC Limits Qual Phone: (80 l) 263-8686 Surrogate -------------------Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,050
1,030
1,000
1,030
--The reporling limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1344h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 105 72-151
1,000 103 80-152
1,000 100 72-135
1,000 103 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.5 50.00 JOI 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.0 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 49.2 50.00 98.5 72-135
Surr: Toluene-dB 2037-26-5 50.3 50.00 101 80-124
Report Date: 9/20/2019 Page 26 of 48
All anal) ses applicable 10 lhe CWA. SOWA, and RCRA are perfom1ed in accordance to NELAC protocols Pe1tinent sampling i11formalion is localed on the auached COC Conlidenlinl Business lnformnt1on: This repor1 is provided for the exclusi, e use or the
~ddressee Pri, ile~es o.rsub ... seq~enl ~1~e of the ~~1e or this .con_ipan~ or rm) 1~mbe1 or its stnff, or reproduclio~ ~f lhis repo~ in .co~eclion~ \\ilh lhe ~Yertisemenl. P~?moti~n or sale or:11!Y ~rod~cl or p~ocess, ~r in ~onn:_c!ion ,,,~th th~ n:-publicalion or this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-004
Client Sample ID: TW4-21_09042019
Collection Date: 9/4/2019 1228h
Received Date: 9/6/2019 l 030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/2019 1606h E300.0 5.00 478
Nitrate/Nitrite (as N) mg/L 9/9/2019 837h E353.2 0.100 14.7
Report Date: 9/20/2019 Page 9 of 48
All onnl~ses applicnble to the CWA. SDWA. and RCRA ore perfom1ed in accordance to NELAC protocols. Pe1tinen1 sampling information is localed on the nllnched COC Conlidenlial Business Information: This repon is p1'0\'ided for lhe es.clush·e use of the
~ddressee P1i, ile~es o,f sub,.seq~enl ~1~e of 1he ~?':m' of this .co1~pany or ;my 1~mbel' of its slaff. or reproduclio~ ~f lhis repo1! in fO~tection,, with the n~,·ertisemenl, P~?molio.n ~1 saJe of~!~. ~rodl!ct or p1,ocess, ~r in ~onn!c~ion w!lh lh? ri;:-p~l>licolio1l of this 1"port
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-012C
Client Sample ID: TW4-22_09042019
ANALYTICAL LAeoRAToR1Es Collection Date: 9/4/2019 1258h
Received Date: 9/6/2019
Analytical Results
1030h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 9/6/2019 2212h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 100 Method:
CAS Reporting
Number Limit
67-66-3 100
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: awal @awal-labs.com
-----------------
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,180
4,980
5,000
4,960
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 9/7/2019 010h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
5,000 104
5,000 99.7
5,000 100
5,000 99.2
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
52.6
49.1
50.2
49.6
50.00 105
50.00 98.2
50.00 100
50.00 99.3
SW8260D
Analytical
Result Qual
3,460
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/20/2019 Page 34 of 48
All an.ibses applicable to the CWA. SOWA. and RCRA are performed in accordance to NELAC protocols, Pertinent sampling information is located on Lhe attached COC Conride11t111I Business Information: This report is provided for the exclusi, e use o(lhe
~ddressee P1i, ile~es o.f sub,.seq~enl ~~e of the ~?-':'e of this .cm~pany or any ~mbe1 of its slaIT, or reproduclio~ ~f this repo~ in ~o~eclion,. \\·ilh lhe ™!"ertisemenl, P~?motio.n ~r sale of~!~~ ~rodt~cl or p~ocess, ~r in ~onn~c~io11 w!lh lh~ r!-publicaLion or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909134-012
Client Sample ID: TW4-22_09042019
11u1<Lvr,c11L L11 eo~1oron 1n Collection Date: 9/4/2019 1258h
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: awal @awal-labs.com
, web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/16/2019 1926h E300.0 10.0 588
9/9/2019 953h E353.2 1.00 72.5
Report Date: 9/20/2019 Page 17 of48
All analyses applicable to lhe CWA. SDWA. and RCRA :1re performed in accordance to NELAC protocols Pertinent sampling infonmll1on is located on the aunched COC Conridentio\ Business lnfonnotion: This repon is pro,·ided for lhe exclush e use or the
~ctdressee Privile~es o[ sub .. seq~1ent ~1~e of lhe ~~e of I his .co1~pw,y or an~ 1~mberof its slaIT, or reproductio~ ~f this repo~ in 0C011~l~ction .. \\ilh lhe o~Ye1tisemenl, p~omotio.n DI ~nle of~!> ~roch~ct or p1.ocess, ?r in ~onn;_c~ion w!th 1h? r~·publicntion of this 1'tport
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-012C
Client Sample ID: TW4-23_09112019
Collection Date: 9/11/2019 902h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 030h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
55.3
50.6
51.4
50.7
50.00 111 72-151
50.00 101 80-152
50.00 103 72-135
50.00 101 80-124
Report Date: I 0/23/2019 Page 51 of 80
All onnl) ses applicable lo lhe CWA. SOWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Conlidenlial Business Information: This repor1 is provided for the exclusi, e use of the
~ddressee Pri, ile~es o_f su~seq~enl ~~e or the ~~1e o[this .co1~pai1) or art) ~mber ori1s stnrf, or reproduclio~ ~r this repo~ in .co1~1ection~ \\ilh the o~~'ertisemenl. p~omolio.n m sale of :ii~~. ~rodL~cL or P~?Cess, ~r in ~nn:c~ion. w!lh lh~ r:-publication of this report
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320-012
TW4-23 09112019
ANALvT1cAL LAB0RAT0R1£s Collection Date: 9/11/2019 902h
3440 South 700 West
;;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qua)
9/20/2019 1902h E300.0 1.00 47.9
9/13/2019 1349h E353.2 0.100 < 0.100
Report Date: 9/30/2019 Page 19 of80
All anal) ses applicable 10 the CWA. SOWA. and RCRA are perfom,ed in accordance to NELAC prolocols Pertinent sampling infom1alion is locoled on the auached COC Confidenlinl Business lnformalion: This report is pro,·ided for 1he e~clusfre use of 1he
~ddressee Pri, ile~es o.r sub~seq~t ?~e or the ~:ii:ne of this .co,~pany or any ,~mber of its slaff, or reproduclio~ ~f this repo~ in ~rn~1ec1ion~ "i~1 the ~,ertisemenL p~~moli°:° ~r sale of~!). ~,och~t or p,.ocess, ~r in ~onn~c!ion w(th lh~ r~-publicnlion of this reporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-002C
Client Sample ID: TW4-24_09042019
Collection Date: 9/4/2019 1248h
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 1305h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
1030h
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 31.1
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
50.7 50.00 IOI 72-151
50.9 50.00 102 80-152
49.6 50.00 99.3 72-135
50.2 50.00 100 80-124
Report Date: 9/20/2019 Page 24 of 48
All analyses applicable 10 the CW A. SOWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is locoted on the altached COC Confidential Business Jnformalion: This report is prorided for lhe e.'{clUSi\'e use of the
~ddressee Pri, ile~es o.r sub__seq~enl ~~e of the ~?',11e of this .co1~pany or any ~mbei of its slafT, or reproductio.~ ~: Lhis repo~ in ~0~1ection .. with Lhe D~\'ertisemenl, p~omoti~n or sale of :ii!~ ~rod1:cl or p~ocess, ~r in ~nn:c!ion w/lh lh~ r:-publicalion or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-002
Client Sample ID: TW4-24_09042019
ANALYTICAL LAB0RAT0R 1es Collection Date: 9/4/2019 1248h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/16/2019 1459h E300.0 20.0 1,130
9/9/2019 944h E353.2 1.00 36.4
Report Date: 9/20/2019 Page 7 of48
All nnnlyses applicnb\e to the CWA. SOWA. and RCRA n1e perlbm,ed in accordance to NELAC protocols. Pertinenl sampling i11formotion is localed on the ouached COC Confidenlial Business Information: This repon is provided for 1he exclusiYe use of the
~ddressee. Pii, ile~es o,r sub .. seq~1en1 ~1~e or the ~~e of this
1
co1~pnny or nny 1~~bel' or its slnli, or reproductio~ ~f I his repo~ in 7on~ection,. \\ith the O~\'ertisen;ent. P~?moli~n ~r ~ale of ?1!). ~rodl~cl or p1.ocess, ~r in ~mm1;c~ion w!th th~ r~·p~blicalion of 1his repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-00lC
Client Sample ID: TW4-25_09042019
ANALYTICAL LAB0RAT0R1Es Collection Date: 9/4/2019 1238h
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 1245h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
1030h
Extracted:
Dilution Factor:
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 50.2 50.00 100 72-151
460-00-4 50.5 50.00 101 80-152
1868-53-7 50.2 50.00 JOO 72-135
2037-26-5 51.0 50.00 102 80-124
Report Date: 9/20/2019 Page 23 of 48
All annlyses applicable lo the CWA. SOWA. and RCRA are perfom1ed in accordance 10 NELAC protocols. Pertinent sampling infomlnlion is located on the allached COC Confidential Business Jnfonnation: This report is prol'ided for the exclusi\ e use of the
~ddressee Prl\ ile~es o! su~seq~enl ~1~e of the ~~e of this .co1~pany or an~ ~':1ber of its slaff, or reproduclio.~ ~r this repo~ in ~on~1ecli0t~ \\ilh the a~~enisement. P~?motio_n 01 saJe of~) ~rod1:ct or p~ocess, ~r in ~nn;C~ion \\'!th th~ r~-publication of this repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-001
Client Sample ID: TW4-25_09042019
ANALvr1cAL LAeoRAroR1es Collection Date: 9/4/2019 1238h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/16/2019 1442h E300.0 2.00 58.l
9/9/2019 829h E353.2 0.100 0.548
Report Date: 9/20/2019 Page 6 of 48
All analyses applicable to the CWA. SDWA. and RCRA 01e perfom1ed in accordance to NELAC protocols. Pertinent sampling i11formotio11 is located on the euached COC Conlidenlial Business Information: This report is proYided for the exclusi\"e use of1he
~cldressee. P1i\'ile~es of sub;eq~ent ~1~e or lhe ~~e of this .co1~pony or nny 1~iyaber or its stnff, or reproductio.~ ~~ this repo~ i11 .co11~11:!clion .. \,1th the n~~·ertise1;1ent, p~~motio1n ~r ~ale or ?1!Y. ~rod1~cl or P~?Cess, ~r in 7onn:c~io11 w!lh lh~ r:-publication of this repon
American West
ANALYTICAi, I ABORATORIES
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
l 909320-028C
Client Sample ID: TW4-26_09122019
Collection Date: 9/12/2019 817h
Contact: Tanner Holliday
Received Date: 9/13/2019 1025h
Analytical Results
Test Code: 82600-W-DENlOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 9/18/2019 1659h
Units: µg/L
Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate --------Units: µg/L
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibrornofluorornethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
CAS Result Amount Spiked %REC
17060-07-0 1,000 1,000 100
460-00-4 1,030 1,000 103
1868-53-7 971 1,000 97.l
2037-26-5 1,030 1,000 103
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 9/18/2019 1419h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Brornofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
Method:
Reporting
Limit
1.00
1.00
1.00
CAS Result Amount Spiked %REC
17060-07-0 50.8 50.00 102
460-00-4 53.9 50.00 108
1868-53-7 48.7 50.00 97.4
2037-26-5 52.7 50.00 105
SW8260D
Analytical
Result Qual
877
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/30/2019 Page 67 of80
All anal~ ses applicnble to lhe CW A SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling informati<Hl is located on the allached COC. Confidenlinl Business Information: This repor1 is pro,•ided for lhe exclusi, e use of lhe
~ddressee Pri, ile~es of sub,_seq~enl ~·~e of lhe ~~1e or lhis .co1~pa11y or an~-~mber orils staff, or reproducli~ ~f 1his repo~ in ~n~1eclionr ,,ith the a~\ertisemenl, P~?moli~ or sale or~!~ ~1od,~cl or P~?cess, ~r in ~nn;_c~ion "!'h lh~ r~-publication or this repC\rl
American West
ANALYTICAL l ABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-028
Client Sample ID: TW4-26_09122019
Collection Date: 9/12/2019 817h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 143h
9/13/2019 1435h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 32.0
E353.2 0.100 10.9
Report Date: 9/30/2019 Page 35 of80
All anal) ses applic:1ble to the CWA. SOWA. and RCRA me perfom1ed m accordance lo NELAC protocols Pertinent s11mpling infom1aLion is located on the altnched COC Conlidential Business lnfonnalion: This repon is prorided for the e\'.clusi, e use of the
~ddressee Pri,·ile~es o,Csub__seq~ent ~1~e of the ~~1e of this .cm~pany or nn~ ~mberof its slruT, or reproductio~ ~fthis repo~ in .con?ection .. \\ilh Lhe a<!_~ ertisemenl, p~~moli~ or sale or:ii!~ ~rod~ct or p~ocess, ~r in ~orm~c~ion w~lh 1h~ r~·publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320-0 l 6C
Client Sample ID: TW4-27 09112019
Collection Date: 9/11/2019 947h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 148h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 7.58
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV
55.8
49.9
52.6
50.4
50.00 112 72-151
50.00 99.9 80-152
50.00 105 72-135
50.00 IOI 80-124
Report Date: I 0/23/2019 Page 55 of 80
All nnal)ses applicable to lhe CWA. SDWA. and RCRA are perf'om1ed in accordance lo NELAC protocols~ Pe1tinenl sampling informalion is located on the allached COC Confidential Business Information: This report is proYided f'orthe exclusi\e use of lhe
~ddressee Pri, ile~es o_f sub~seq~ent ~~e of the ~?1,ne of 1his .co1~pany or an~ 1~1;1ber of its staff, or reproduclio~ ~rthis repo~ in .co~1eclion~ \\ith the .i~, ertisernent, p~omoli~n ~r sale of ?1!~ ~rodllCI or p~ocess, ~r in ~onn~c~ion w~1h th~ r~-p~blicalion of this reporl
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-016
Client Sample ID: TW4-27_09112019
Collection Date: 9/11/2019 947h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2116h
9/13/2019 1359h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 25.3
E353.2 0.200 21.2
Report Date: 9/30/2019 Page 23 of 80
All annlyses applicoble lo the CW A. SOWA. and RCRA are perfomred in accordance to NELAC protocols Pertinenl sampling information is localed on the al1ached COC Conridenliol Business Information: This report is prO\ided for lhe e.~clusi, e use or the
~ddressee Pti, ile~es o.r sub__seq~enl ~1~e of the ~~1e of this .cm~pany or rm) 1~mbe1 of its slaif, or reproduc1io~ ~f 1his repo1~ in _con?l!ction_ ,,ilh the a~~·ertisement, p~omolio_n ~r sale of ?-1.f rrodl~L or p~ocess, ~r in <;<>nn:,c!ion "!th lh~ r:·publicnLion of this report
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
l 909320-003C
Client Sample ID: TW4-28 09112019
ANALvT1cAL LAD0AAT0A1Es Collection Date: 9/11/2019 740h
3440 South 700 West
)alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2134h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Ta1U1er Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
:-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
53.3 50.00 107 72-151
48.8 50.00 97.5 80-152
50.4 50.00 IOI 72-135
49.4 50.00 98.8 80-124
Report Date: I 0/23/2019 Page 42 of 80
All analyses applicable lo lhe CW A. SOWA. and RCRA are performed in accordance lo NELAC protocols Pertinent sampling informal ion is located on lhe allached COC Confidential Business lnfonnalion: This reporl is pro, ided for lhe e'.'<clusi\ e use of !he
~ddressee P1i, ile~es o! su~seq~nt ~~e of the ~~1e of this .co1~pany or ,mr ,~mber or ils slalT, or reproduclio~ ~f this repo~ in ~o~eclion~ ,,ith the ::i~,ertisemenl, p~omoli~n or sale of~) ~rodl~ct or p~ocess, ~r in ~~~ion w!th th~ r~-p~blication of Jhis repor1
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-003
Client Sample ID: TW4-28_09112019
Collection Date: 9/11/2019 740h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 103h
9/13/2019 1331h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 49.0
E353.2 0.100 10.2
Report Date: 9/30/2019 Page IO of 80
All rurnl~ses applicrible to the CWA. SOWA. and RCRA rue i,er(omled in accordance to NELAC protocols Pertinenl sampling information is locnted on lhe altadted COC Confidenlinl Business lnfonnalion: This repor1 is pro\'ided for the exclusi,e use or1he
~ddressee Pri, ile~es o~ sub__seq~tenl ~~ or the ~~te or this .co1~pany or any ~mber of its slaJT. or reproductio~ ~f this repo~ in ~1~1eclion~ "ith the a~~ertise~enl. P~?moli~n ~r sale or~~ ~rodl~l or p~ocess, ~r in 1:°nn~~ion w!lh lh~ r~-publicalion or !his reporl
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-025C
Client Sample ID: TW4-29 _09122019
Collection Date: 9/12/2019 742h
Contact: Tanner Holliday
Received Date:
Analytical Results
9/13/2019 1025h Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/18/2019 1519h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,000
1,030
983
1,030
--The reporling limits were raised due to high analyte concentrations.
Analyzed: 9/18/2019 2059h
Units: µg/L
Compound
Extracted:
Dilution Factor: 1
CAS
Number
1,000 100
1,000 103
1,000 98.3
1,000 103
Method:
Reporting
Limit
SW8260D
Analytical
Result Qua!
549
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
Carbon tetrachloride
Jose Rocha Chloromethane
56-23-5
74-87-3
75-09-2
1.00
1.00
< 1.00
< 1.00
QA Officer Methylene chloride 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 49.8 50.00 99.6 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.4 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 48.3 50.00 96.6 72-135
Surr: Toluene-d8 2037-26-5 51.9 50.00 104 80-124
Report Date: 9/30/2019 Page 64 of80
All anal) ses applicnble 10 the CWA. SOW A. and RCRA o.re perfom1ed m accordance to NELAC protocols. Pertinenl sampling information is located on U1e attached COC Confidential Business Information: This report is pro, ided for the exclusi\ e use or the
~dressee Pri, ile~es o:sub~seq~nl ~~e or the ~~1e or this .co1~pany or an~ 1~mber oriLs staff or reproduclio_~ ~rthis repo~ in _con~1ection .. ,,ith lhe o~,·ertisement, 1J~?mo1io.n m sn.Je or~~} ~todL~cl or p1.ocess, ~r in ~onn~c~ion w(lh 1h~ r:-publicotion or this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-025
Client Sample ID: TW4-29 _09122019
Collection Date: 9/12/2019 742h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 053h
9/13/2019 1431h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.0
E353.2 0.100 2.55
Report Date: 9/30/2019 Page 32 of80
All nmd~ ses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Per1inenl sampling i11fonnalion is loc.11Led on lhe aHached COC Confidenliul Business Information: This report is proYided f'or 1he e.,,:clusi,e use of1he
~ddressee P1i, ile~es o_f sub .. seq~enl ~~e of the ~~1e of lhis .co1~pany or any ~mber of its slnfT. or reproduclio~ ~f this repo~ in ~01~1eclion .. ,,ilh the a~, ertisement. P~?moli~ or saJe of ~!Y ~rodL~cl or p~ocess, ~r in ~onm;.c~ion w!th lh? r~-pul>licalion or this reporl
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-019C
Client Sample ID: TW4-30_09112019
Collection Date: 9/11/2019 1022h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 247h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 34.8
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control /imitfor the CCV.
56.3
50.2
53.4
50.0
50.00 113 72-151
50.00 100 80-152
50.00 107 72-135
50.00 99.9 80-124
Report Date: 10/23/2019 Page 58 of 80
All anal~ ses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols. Pertinenl sampling infom1a1ion is located on lhe allached COC Confidenliol Business lnformalion: This report is provided for the exclush e use or the
~ddressee Pri, ile~es o[ sub_seq~1enl ,u!e or the ~~e of I his _cofl;pany or nny ~mber of its staIT, or reproductio~ ~f this repo~ in .con~iection~ \\ilh the a~, ertisemenl P~?molio.n ~r saJe of~~.~· odl~cl or P~?cess, ~r in 7onn1;c!ion w!th th: r:_-publicruion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320-019
Client Sample ID: TW4-30_09112019
Collection Date: 9/11/2019 1022h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2206h
9/13/2019 I402h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 34.5
E353.2 0.100 3.62
Report Date: 9/30/2019 Page 26 of 80
All anal~ ses applicable to lhe CWA. SDWA. and RCRA ore performed in accordance 10 NELAC protocols Pertinent snmpling infom111tion is located on the altnched COC. Conlidentinl Business Information: This report is pro,·ided for lhe exclusi,·e use or1he
~dressee Prh ile~es o! sub .. seq~enl ~~e of the ~~e or this .con:1p:my or an~-~mber or its slalT, or reproduclio~ ~~ this repo~ in .c0t1)1ection .. \\ilh lhe a~, ertisemenl. P~?n101io.n ~r sale of~!~ ~rodt)Cl or p,:ocess, ~r in ~onn:_c!ion \\'!th th~ r~-publicalion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
l 909320-008C
ClientSampleID: TW4-31 09112019
Collection Date: 9/11/2019 820h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2312h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV
54.1
50.3
50.7
49.7
50.00 108 72-151
50.00 101 80-152
50.00 101 72-135
50.00 99.4 80-124
Report Date: 10/23/2019 Page 4 7 of 80
All anal)ses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinenl sampling information is located on the allached COC Confidential Business Information: This report is provided for the exclusi\e use of the
~ddressee Pri\·ile~es of sub.seq~ent .u~e or1he ~~1e of'1his .crn~pany or any 1~mbe1•of its slafr; or reproductio~ ~~this repo~ in .con'.1ection .. \\ilh the ::t~~1ertise1~ent, P~?moli~n ~r ~aJe of !'1!~. rrod1~ct or p~ocess, ~r in ~nn:,c!ion w!th th~ r;-publication or1his report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-008
Client Sample ID: TW4-31_09112019
ANAL vr, cA L L As o RAro R, Es Collection Date: 9/11/2019 820h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 320h
9/13/2019 1344h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 35.8
E353.2 0.100 0.610
Report Date: 9/30/2019 Page 15 of 80
All anab ses applicable to lhe CWA. SOWA. RrJd RCRA are perfom1ed in accordance to NELAC protocols Pe1tinenl sampling informalion is located on the attached COC Conndenlial Business Information: This report is pro, ided for the exclusi, e use of the
~ddressee P1i,·ile~es o.r sub__seq~enl ~~e of the ~~1e or this .co1~p11ny or any J~~mber of its stnfT. or reproductio~ ~~ this repm; in ~rn~eclion .. \\ ith the a~~ ertise1:1enl, P~?molio.n ~r sale of:"!~ ~rodl~CL or p~ocess, ~r in ~onn~c~ion w~lh th7 r~·p~blication of !his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-004C
Client Sample ID: TW4-32_09112019
LAaoRAroR1Es Collection Date: 9/11/2019 748h
3440 South 700 West
;alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2154h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: 1,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
53.1 50.00 106 72-151
47.9 50.00 95.7 80-152
50.3 50.00 101 72-135
49.0 50.00 98.0 80-124
Report Date: 10/23/2019 Page 43 of 80
All analyses applicnble to the CWA. SOWA. and RCRA are perfom1ed in accordance to NE LAC protocols Pertinenl sampling information is localed on the aUached COC Confidenlial Business lnformafion: This report is prO\ ided for the exclusi, e use or the
~dressee P1i, ile~es o_f sub~seq~ent ~1~e of the ~~,e or this .con,-ipany or M) 1~mber of its slafT. or reproduclior~ ~f this repo~ in .coi1?eclion .. "ilh the n~~·ertisemenl, P~?motio.n or sale of~!)~ ~rodl~Ct or p~ocess, ?r in ~onn~c~ion "!th th~ r~-publication of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-004
Client Sample ID: TW4-32_09112019
Collection Date: 9/11/2019 748h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 2llh
9/13/2019 1334h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 55.0
E353.2 0.100 1.84
Report Date: 9/30/2019 Page 11 of 80
All anal~ ses applicable to the CWA, SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols Pertinenl sampling inCormation is located on lhe attached COC Confidenlial Business Information: This reporl is pro, ided for the C:\:clushe use of the
~ddressee Pririle~es o.r sub__seq~ent ~~e of the ~~1e or I his .coi~pw1y or an} 1~mber of its starT, or reproducLio~ ~f this repo~ in ~0~1ection~ \\ilh the a~: ertisemenl. p~omoli~ or sale of !'1!' ~rodl~Cl or p~ocess, ~r in !;O"n~~ion ''!lh th~ r:p~blicalion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-024C
Client Sample ID: TW4-33_09122019
Collection Date: 9/12/2019 732h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1859h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 101
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
50.9 50.00 102 72-151
52.5 50.00 105 80-152
49.1 50.00 98.3 72-135
52.4 50.00 105 80-124
Report Date: 9/30/2019 Page 63 of80
All anal) ses applic::ible to lhe CWA. SDWA. and RCRA are i,erfom1ed in Rccord:ince to NELAC prolocols Pertinent sampling infom1ation is located on lhe attached COC Confirlentiol Business Information: This repor1 is prO\ ided for the e;,.:c\usi, e use of 1he
~ddressee Pri, ile~es o! sub .. seq~enl ~~e of the ~~e of this .con:ipany or rul) ~mber of its staIT. or reproducti~ ~f this repo~ in ~on~eclion .. \\ilh the ~YertisemenL P~?molio.n ~r sale of ~lY ~1odi~cl or p~ocess, ~r in ~onn:c~ion w!th th~ r:,-p~blicotion or this reporl
American West
ANALYTICAL LAOORAT0Rlf6
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Collection Date:
Received Date:
Analytical Results
Compound
Chloride
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320-024
TW4-33 09122019
9/12/2019 732h
9/13/2019 1025h
Date
Units Prepared
mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/2019 036h
9/13/2019 1428h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 41.1
E353.2 0.100 1.61
Report Date: 9/30/2019 Page 31 of80
All analyses applicable lo lhe CWA. SOWA. Md RCRA are perfom1ed in accordance lo NELAC prolocols Pertinenl sampling informalion is located on lhe al\ached COC Conlidential Business Information: This report is pro, ided for the e:...dush e use of the
~ddressee P1i, ile~es o,f su~seq~1enl ~~e of the ~~e or I his .co1~pany or rmy 1~mber or its staff, or reµroductio!~ ~f this repo~ in ~o~iection~ ,,ith the a~~'ertisemenL, P~?molio_n ~r sale of~) r1och~cl or p~ocess, ~r in ~onn:c~ion w!th th7 rE;-publication or this repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-0IOC
Client Sample ID: TW4-34_09112019
Collection Date: 9/11/2019 843h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2351h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit f or the CCV.
1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
54.2 50.00 108 72-151
49.8 50.00 99.6 80-152
50.9 50.00 102 72-135
50.2 50.00 100 80-124
Report Date: 10/23/2019 Page 49 of 80
All annl~ ses applicnble to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pe11inenl sampling information is located on Lhe altached CDC Confidential Business lnrormalion: This repor1 is pro\'ided for the e.xclushe use of the
~ddressee Pri, ile~es of su~seq~1enl ~1:e of the ~~e of this
0
co1~po.n~ or nn~~ 1~mber or ils still, or reproductio~ ~f lhis repo~ in ~on?ection .. ,,i1h Lhe a~, er1isement. P~?moli~ ~r sale of~~~ ~rodi~t or p~ocess, ~r in ~nn~c~ion \\~lh 1h~ r~-publication or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-010
Client Sample ID: TW4-34_09112019
ANALvT1cAL LA00RAT0R 1Es Collection Date: 9/11/2019 843h
3440 South 700 West
:ialt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qua)
9/19/2019 428h E300.0 1.00 17.8
9/1 3/2019 1347h E353.2 0.100 0.934
Report Date: 9/30/2019 Page 17 of 80
All anal~ses ap1>licable to the CWA. SOWA. and RCRA are perfomred in accordance to NELAC protocols. Pertinenl sampling information is located on lhe atl.tched COC Conlidentlal Business lnfonnahon: This repor1 is pro,·ided for lhe exclusiYe use of1he
~ddressee P1frile~es o,r su~seq~tent ~~e of lhe ~~le of I his .co1~pm1y or any ~mber of its stnlT. or reproducrio~ ~f this repo~ in ~on~1eclion~ ,,ith the~~ ertisemenl, p~omolio.n or sale or ~y ~rodl~Ct or p~ocess, ~r in ~~!ion w!th 1h~ r~p~blicnlion of lhis report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320-011 C
Client Sample ID: TW4-35 09112019
Collection Date: 9/11/2019 853h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/14/2019 Ollh
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the control limit for the CCV
55.4
50.6
52.1
50.4
50.00 Ill 72-151
50.00 101 80-152
50.00 104 72-135
50.00 IOI 80-124
Report Date: I 0/23/2019 Page 50 of 80
All annlyses applicable to the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling informalion is located Oil lhe allached COC Confidential Business [nformation: This repon is pro, ided for the exdusiH use of the
~ddressee P1i, ile~es o_f sub,,seq~enl ~~e or lhe ~:31.ne of this .co1~pany or any ~mber of ils slaff, or reproductio~ ~f this repo~ in .con~1ection ... ,,iU1 the ::i~,•ertisemenl P~?molio.n ~r sa1e or~~~ ~rodt~ct or p~ocess, ~r in ~nn:_c.tion w!lh lh~ r~-publication of this repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: awa1 @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-011
Client Sample ID: TW4-35_09112019
Collection Date: 9/11/2019 853h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L ----
Date
Analyzed
9/19/2019 445h
9/13/2019 1348h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 31.7
E353.2 0.100 0.525
Report Date: 9/30/2019 Page 18 of 80
All annl~ ses applicable lo the CWA. SDW A. and RCRA are perfom1ed in accordance to NE LAC polocols. Pcnmc.111 si.m1nlin,g infcirnuuon is located on the aUached COC. Confidenlial Business lnfonnation: This repon is prm·ided for lhe e,chfil,,~ u:Je of the
~ddressee P1i, ile~es o_f su~seq~nl ~1~e of lhe ~~1e of lhis .co1~imny or any ~mber of its slafT, or rcproductt~ ~(lhis repo1~ in ~~lt.'Chon .... ,,iU1 lhe a~,·ertisemenl, P~?moli°:° ~r sale of ~!Y ~rodl~CI or P~?Cess, ~r in ~nn~~ion \\'!th lh~ r;·pubhc:ntio1\ of I his reporl
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-007C
Client Sample ID: TW4-36_09112019
ANALvr,cAL LABORAroR1[s Collection Date: 9/11/2019 812h
3440 South 700 West
;alt Lake City, UT 84119
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2252h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratmy Director
Jose Rocha
QA Officer
Surr: J ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
$ -This compound exceeded (low) the control limit for the CCV.
55.4 50.00 Ill 72-151
48.9 50.00 97.8 80-152
51.8 50.00 104 72-135
50.7 50.00 101 80-124
Report Date: I 0/23/2019 Page 46 of 80
All anal) ses applic::ible to lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Per1inent sampling informalion is located on the attnched COC Confidenlial Business Information: This report is pro, ided for 1he exclusi, e use of lhe
~dressee. Pri, ile~es o.f su~seq~I ~~e of lhe ~~le of this .co1~pan~ or an) ~mber of its slaJT, or reproductio~ ~f this repo~ in ~on~1eclion~ \\ith the n.~:ertisement, P~?motio.n or saJe of~!) ~rod1~ct or p1.ocess, ~r in 7onn:_c!ion \\ !th th~ r~-publication of !his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-007
Client Sample ID: TW4-36_09112019
Collection Date: 9/11/2019 812h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 303h
9/13/2019 1423h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 69.6
E353.2 0.100 < 0.100
Report Date: 9/30/2019 Page 14 of 80
AJI anal) ses applicable lo lhe CWA. SDWA. Md RCRA are pcrfom1ed in accordance to NELAC protocols Pe11inen1 sampling information is located on the allnched COC Conlidenlial Business lnfonmilion: This repor1 is proYided for lhe exchGIH' I.de of the
~ddressee Pri, ile~es o!" sub .. seq~enl ~~e of the ~~1e of !his _coa~~ or any 1~mber of ils slnff. or reproductio~ ~'._this repm~ in ~on~1ection ... "ith then~~ ertisemenL P~?moli~n ~r sale of ?',f -~1odl~CI or p~~ess, ~r in ?>nn~!ion "'!'h lh~ r!-publi :»ion or lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-016C
Client Sample ID: TW4-37_09042019
Collection Date: 9/4/2019 1305h
Received Date: 9/6/2019
Analytical Results
1030h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 9/6/2019 2331h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 100 Method:
CAS Reporting
Number Limit
67-66-3 100
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
------------------
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,180
4,900
5,040
5,080
--The reporting limils were raised due to high analyte concenlralions.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 9/7/2019 128h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
5,000 104
5,000 97.9
5,000 101
5,000 102
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
52.5
50.6
49.6
50.1
50.00 105
50.00 101
50.00 99.3
50.00 100
SW8260D
Analytical
Result Qual
11,900
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
10.7
1.90
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 9/20/2019 Page 38 of 48
All anal~ ses applicable to lhe CWA. SOW A. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the all ached COC Conlidenlial Business lnfonm1lion: This report is pro,·ided for 1he exclusi, e use of lhe
~ddressee. Pri, ile~es o.f sub,,seq~ent ~1~e of the ~~1e of this .co1~pa11y or M) 1~mber of its staff, or reproductim~ ~f Lhis repo~ in ~ot~1ectior: with the a~verlisement. P~?motio.n or sale of :ii!~ f!rodl!ct or p~ocess, ~r in ~onn~c~ion wirh 1h? r:p~blication of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-016
Client Sample ID: TW4-37 _09042019
Collection Date: 9/4/2019 1305h
Received Date: 9/6/2019 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/2019 2 I06h E300.0 5.00 228
Nitrate/Nitrite (as N) mg/L 9/9/2019 90\h E353.2 0.100 25.8
Report Date: 9/20/2019 Page 21 of48
All .innlyses applicable lo the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinenl sampling information is located on lhe altached COC Conl'idenlial Business lnforma1ion: This repor1 is proYided for lhe exclusi,e use of the
~ddressee Pri, ile~es or sub .. seq~enl ~1~e of the ~~e of lhis .con:ipnny or any ~mber of ils slnff, or reproduclio~ ~f this repo~ in .con?ection~ ,,ith the at!"ertisement, P~?moli~n ~r ~ale of ?A!) ~rodl~cl or p~ocess, ~r in 7onn;c~ion w~th th~ r:-publicu.lion or this report
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-014C
Client Sample ID: TW4-38_09112019
Collection Date: 9/11/2019 929h
Received Date: 9/13/2019 I 025h
Analytical Results
Analyzed: 9/14/2019 109h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method:
CAS Reporting
Number Limit
56-23-5 1.00
67-66-3 1.00
74-87-3 1.00
75-09-2 1.00
SW8260D
Analytical
Result
< 1.00
< 1.00
< 1.00
< 1.00
Qual
$
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
$ -This compound exceeded (low) the con/rot limit for the CCV.
55.1
50.5
51.7
50.9
50.00
50.00
50.00
50.00
IIO
IOI
103
102
72-151
80-152
72-135
80-124
Report Date: 10/23/2019 Page 53 of 80
All ::malyses applic..1ble to the CWA. SOWA. and RCRA are perfom-ied in accordance lo NELAC protocols Pe1tinenl sampling informalion is located on the auached COC Conf1den1ia[ Business lnforma1ion: This reµon is pro,ided for the e:,;clusi,e use of the
~dressee P,frile~es o.f sub~seq~en\ ~·~e of the ~~e of this .co1~pm1y or an) ~mber of its sln!T. or reproduclio~ ~fthis repo~ in ~on~teclion~ \\ilh the n~vertise1~enl. P~?moti~ ~r sale of~!) ~rodtict or p~ocess, ~r in 7onn:_c~ion "!th th~ r:-publicnlion of this report
American West
ANAlVTICAl lABORATOR IES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-014
Client Sample ID: TW4-38_09112019
Collection Date: 9/11/2019 929h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/20/2019 2042h
9/13/2019 1351h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 31.6
E353.2 0.100 7.61
Report Date: 9/30/2019 Page 21 of80
All annl~ses applicable 10 lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC prolocols. Pertinent sampling infomialion is located on lhe auached COC Confidenlial Business Information: This repon is pro\'ided for the exclusirn use of the
~ddressee Pri,·ile~es orsub,.5eq~en1 ~~e oflhe ~~,:ne of lhis .cOJ~pany or.m~· ~'!1ber ofilS stnff or reproduclio~ ~~this rep01; in .c~1eclion ... \\ith the a~vertise':1ent, p~omolio.n m sale of?'!~ ~rodL~ct or p~ocess, ~r in ~nn~c!ion "ilh th~ r~-p~blication of this repor1
3440 South 700 West
,alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-013C
Client Sample ID: TW4-39_09042019
Collection Date: 9/4/2019 1322h
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 2232h
Units: µg/L
Compound
Chloroform
1030h
Extracted:
Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 4,240
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,260
5,090
5,020
5,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/7/2019 029h Extracted:
Units: µg/L Dilution Factor: 1
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
5,000 105 72-151
5,000 102 80-152
5,000 JOO 72-135
5,000 JOO 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 5.71
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 51.2 50.00 103 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.3 50.00 96.7 80-152
Surr: Dibromofluoromethane 1868-53-7 48.6 50.00 97.3 72-135
Surr: Toluene-d8 2037-26-5 49.5 50.00 99.1 80-124
Report Date: 9/20/2019 Page 35 of 48
All analyses applicable lo lhe CWA. SOWA. and RCRA are pcrfom1ed in accordance lo NELAC profocols Pertinenl sampling infomuition is localed on the allached COC Confidential Business Information: This repor1 is pro\'ided for lhe exclush e use of 1he
~ddressee Pri, ile~es o!' sub,,seq~nt ~~e of the ~~e or this .cm~pany or an~ ~mber of its slafT, or reproducli~ ~f this repo~ in .con~eclion ... \\ilh the a~~·ertisemenl, P~?moti°:11 o} sale of :11!~ ~roch~ct or p,.ocess, ~r in ~nn~~ion \\'!th th~ r~-p~blicalion of this report
INORGANIC ANALYTICAL REPORT
A merican West
ANALYTICAL LABORATORIES
3440 South 700 West
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-013
Client Sample ID: TW4-39_09042019
Collection Date: 9/4/2019 1322h
Received Date: 9/6/2019
Analytical Results
Compound Units
1030h
Date
Prepared
;alt Lake City, UT 84119 Chloride mg/L
mg/L
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Nitrate/Nitrite (as N)
Date
Analyzed
9/16/2019 1943h
9/9/2019 853h
Contact:
Method
Used
EJOO.O
E353.2
Garrin Palmer
Reporting
Limit
2.00
0.100
Analytical
Result
48.2
1.75
Qual
Report Date: 9/20/2019 Page 18 of 48
All anal) ses applicnble to lhe CW A. SDWA. Md RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on the attached COC. ConOdenlial Business lnfonnalion: This report is pro"ided for the exclusi\'e use of the
~ddressee. Pri, ile~es o~ sub .. seq~I ~1~e of lhe ~~1e of I his .cm~pnny or any ~7mbe1 or its stnJT. or reproduclio!~ ~f this repo~ in .co11~1ection .. wilh lhe r.a~\·e11ise~enl, P~?molio.n ~1 ~ale of~!~: ~rod~cl or p1:?Cess, ~r in ~xmn:c~ion w!th lh~ r~-publicolion of I his 1eport
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Gan-in Palmer
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-003C
Client Sample ID: TW4-40_09042019
Collection Date: 9/4/2019 1433h
Received Date: 9/6/2019 1030h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 9/6/2019 1837h
Units: µg/L
Compound
Chloroform
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d&
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
CAS Result Amount Spiked %REC
17060-07-0 1,040 1,000 104
460-00-4 1,010 1,000 101
1868-53-7 1,010 1,000 IOI
2037-26-5 1,020 1,000 102
SW8260D
Analytical
Result Qual
380
Limits Qual
72-151
80-152
72-135
80-124
--The reporling limils were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1324h Extracted:
Units: µg/L Dilution Factor: Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 < 1.00
Chloromethane 74-87-3 1.00 < 1.00
Methylene chloride 75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 50.0 50.00 100 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.3 50.00 103 80-152
Surr: Dibromofluoromethane 1868-53-7 49.9 50.00 99.8 72-135
Surr: Toluene-dB 2037-26-5 50.0 50.00 100 80-124
Report Date: 9/20/2019 Page 25 of 48
All annlyses applicable 10 the CWA. SDWA. and RCRA are perfom1ed in accordnnce to NELAC protocols Pertinent sampling informalion is located on the altached COC Confidential Business lnformotion: This report is pro\'ided for the e:\'.clushe use of lhe
~ddressee Pri, ile~es o:sub .. seri~ient ~J~e of the ~~e of this .co1~pany or nn~ ~mber of its slalT. or reproduclio~ ~f this repo~ in ~on!leclion ... \\ilh Lhe D~\'ertisemenl, P~?moli~ ~r ~aJe of :11!~ ~rod1~l or p~ocess, ~r in ';°nn~~ion ,,·!th th~ r1;_·publication of this 1eporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909134-003
Client Sample ID: TW4-40_09042019
Collection Date: 9/4/2019 1433h
Received Date: 9/6/2019 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/2019 1516h E300.0 1.00 35.9
Nitrate/Nitrite (as N) mg/L 9/9/2019 836h E353.2 0.100 3.39
Report Date: 9/20/2019 Page 8 of 48
All analyses npplicnble 10 tht.' C'WA. SOWA. ru1d RCRA are i)erfom1ed in nccordnnce to NELAC protocols, Pertinent sampling i11rormation is located on the aunched COC Confidential Business lnfmma1ion: This repon is pro,·ided for the exclusi, e use or the
~ddr~see Pri,·ile~es o,r su~seq~enl ~1~e or lhe ~~10 of this .co1~pnny or any ~'!)bet of its stnff, or reproducliOO, ?,f this repo~ in .coi,~ection,, with lhe n~Yertisemenl, P~?motio.n or saJe of ?J!Y. ~1 odl~ct or p11ocess, ~r in 7°nn~~ion w!th th? r~·publication or this report
3440 South 700 West
~alt Lake City, UT 84 I I 9
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-009C
Client Sample ID: TW4-41_09042019
Collection Date: 9/4/2019 1418h
Received Date: 9/6/2019 l 030h
Analytical Results
Analyzed: 9/6/2019 2114h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20
CAS
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 1,190
CAS Result Amount Spiked %REC Limits Qua! Phone: (80 I) 263-8686 Surrogate ------------Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,050
1,020
1,010
1,000
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 9/6/2019 1522h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 105 72-151
1,000 102 80-152
1,000 IOI 72-135
1,000 100 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Surr: l ,2-Dichloroethane-d4 17060-07-0 51.1 50.00 102 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.7 50.00 101 80-152
Surr: Dibromofluoromethane 1868-53-7 49.4 50.00 98.8 72-135
Surr: Toluene-dB 2037-26-5 49.9 50.00 99.9 80-124
Report Date: 9/20/2019 Page 31 of 48
All analyses applicable lo lhe CWA, SDWA. and RCRA ore perfom1ed in accordance to NELAC protocols. Pertinent sampling informalion is located on the all ached COC Confldenlial Business Information: This report is pro\'ided for lhe C..'<clw:i\e use of lhe
~ddressee Pri,-ile~es o:sub3eq~1ent ~e or the ~~ne of this .crn~pnny or M) ~mber of its slatT. or reproduclio~ ~f this repo~ in ~on~eclior~ with the a~venisement. P~?molio.n ~r safe of ~!Y. ~rod~cl or p~~ess, ~r in ~nn~c!ion w(lh lh~ r~-publicalion af this repon
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909134-009
Client Sample ID: TW4-41_09042019
Collection Date: 9/4/2019 1418h
Received Date: 9/6/2019 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/16/2019 1836h E300.0 1.00 39.4
9/9/2019 848h E353.2 0.100 6.22
Report Date: 9/20/2019 Page 14 of 48
All c:mnb ses o.pplicnble 10 the CW A. SDWA. and RCRA 01 e perfom1ed in RCcordance to NE LAC protocols. Pertinent sampliny informntion is localed on 1he attached COC. Conliden1i11I Business Jnfonmilion: This repor1 is proYided for the exclusi\ e use of the
~ddressee Pri\ i\e~es o,r su~seq~1ent ~1~e or the~~.., or this .co,~pony or nny 1~1;1b~r of its strut, or reproduc1io~ ~~ this rtpo~ in .co~1ec1ion,, with lhe °'!'.·er1isement, P~?motio.n or sale of :1l!Y ~1od~ct or p1.ocess, ~r in ~onn~c~ion w!1h lh~ r:-publiclUion of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-009C
Client Sample ID: TW4-42_09112019
Collection Date: 9/11/2019 833h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/13/2019 2331h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00 $
75-09-2 1.00 < 1.00
Surrogate Units: µg,'L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4 17060-07-0 52.6 50.00 105 72-151
Surr: 4-Bromofluorobenzene 460-00-4 47.9 50.00 95.8 80-152
Surr: Dibromofluoromethane 1868-53-7 49.5 50.00 98.9 72-135
Surr: Toluene-d8 2037-26-5 49.4 50.00 98.8 80-124
$ -This compound exceeded (low) the control limit for the CCV
Report Date: 10/23/2019 Page 48 of 80
All anal)ses applicable lo the CWA. SOWA. Md RCRA are performed in accordance lo NELAC protocols, Pe1tinenl sampling in(ormatlon is localed on I.he aU.iched COC Confidential Business lnformnlion; This repor1 is provided for the exclusi,e ~e of the
~ddressee P1i, ile~es o_f su~seq~enl ~~e of the ~~1e of lhis .crn~pany or any ~mber orils slarf, or reproduclio~ ~f lhis repo~ in ~01~1ection ... \\ilh the o.~vertisemenl. p~omolio.n or sale of ?1!' ~rod1~cl or p~ocess, ~r in ~nn~c~ion w~lh lh~ r~-publicalion of this repor1
American West
ANALYTICAL LAOORATORlfS
3440 South 700 West
;aJt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-009
Client Sample ID: TW4-42_09l l20I9
Collection Date: 9/11/2019 833h
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/19/2019 33 7h
9/13/2019 1345h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 20.6
E353.2 0.100 2.75
Report Date: 9/30/2019 Page 16 of80
All analyses applicable lo the CWA. SOWA. and RCRA o.re perfomted in accordance to NELAC protocols. Pe11inent sampling in(omumon is locnled on the attnched COC. Confidenlial Business Information: This report is pro"ided for the exclusi,·e use of the
~rldressee. Pri,·ile~es o,rsu~seq~ent ~1~e of the ~~1e of this .cm~pnny or any 1~mber of its struT, or reproduclio~ ~rlhis repm1 in ~~t<.'<!lh:M~ ,,ith the ~Yertisemenl. P~?motio.n or sale of ?1!Y ~rodl~cl or p1:ocess, ~r in ~1m:_c!ion w!lh 1h~ n;_-publicaLion or lhis repon
3440 South 700 West
,alt Lake City, UT 841 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909134-017C
Client Sample ID: TW4-60_09042019
Collection Date: 9/4/2019 1500h
Received Date: 9/6/2019
Analytical Results
Analyzed: 9/6/2019 2350h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
1030h
Extracted:
Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua(
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
52.5
50.7
49.9
50.5
50.00 105 72-151
50.00 IOI 80-152
50.00 99.8 72.135
50.00 IOI 80-124
Report Date: 9/20/2019 Page 39 of 48
All analyses applicable to the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Per1inenl sampling i11formatio11 is localed on the auached COC Confidenliol Business Information: This report is provided for the e.'iclusi, e use or the
~cldressee Pri, ile~es of sub~seq~enl ~~e of lhe ~~e or lhis .co1~pany or Dn) ~1;1ber of its stnIT, or reproduclio~ ~rthis repo~ in ~on~ection,.. ,vilh lhe a~vertisemenl, P~?molio.n ~r sale of~!)_ ~rod~cl or P~?cess, ~r in 7onn~c!io11 w!th lh~ r:-p~blicalion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chlorofonn 2019
LabSampleID: 1909134-017
Client Sample ID: TW4-60_09042019
Collection Date: 9/4/2019 1500h
Received Date: 9/6/2019 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 9/16/2019 2123h E300.0 1.00 < 1.00
Nitrate/Nitrite (as N) mg/L 9/9/2019 902h E353.2 0.100 < 0.100
Report Date: 9/20/2019 Page 22 of 48
All nnal~ ses api,licnble to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is localed on the al111ched COC. Conridenlial Business lnformalion: This report is proYided for the e:xclusi, e use of the
~ddressee Pri, ile~es o_r sub,,seq~enl ~,~e of the ~~e of this
0
C01~pany or any ~~mber of its slaff, or reproducti~ ~f Lhis repo~ in _con!1~ction ... ,,ith the .i~vertisemenl. P~?moti°:'1 01 sale of :ii!), ~rodL~I or P~?cess, ~r in ~nn:c~ion w!lh lh~ r~-publicaiion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-030C
Client Sample ID: TW4-65_09112019
Collection Date: 9/11/2019 715h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1939h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
50.3 50.00 JOI 72-151
51.6 50.00 103 80-152
49.0 50.00 98.1 72-135
52.3 50.00 105 80-124
Report Date: 9/30/2019 Page 69 of 80
All annl~ ses applic:i.ble lo the CWA. SDW A. ruid RCRA are performed in accordance 10 NELAC protocols Pertinent sampling i11formalion is located on the altached COC Confidenlial Business lnformalion: This report is pro\ ided for the exclush e use of the
~ddressee Pri\ile~es o_f sub .. seq~enl ~~e of the ~~1e of this .co1~p<my or an~ ~mber or its staff, or reproductio~ ~r Lhis repo~ in ~on~,eclion ... \\ilh the a~~ertisemenl, P~?motio.n ~r sale or?1!). rrod1~cl or p~ocess, ~r in 7onn1;_c~ion w~lh th~ r1;·publico1io11 or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-030
Client Sample ID: TW4-65_09112019
ANAL vr, cA L LAB oR Aro R, Es Collection Date: 9/11/2019 715h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/21/2019 216h E300.0 1.00 22.1
9/13/2019 1437h E353.2 0.100 5.76
Report Date: 9/30/2019 Page 37 of80
All annl~ ses applicable lo the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling infonnation is localed on tJ1e allached COC Conlidenlinl Business lnfonm:ilion: This report is pr°' ided for the exclusi, e use of the
~ddressee P1frile~es o_f sub .. seq!1enl ~~e of 1he ~~1e of lhis .co1~pon~ or nny ,~mber of its slaff, or reproductio~ ~f I his repm~ in ~01~1ection .. \\ilh the a~, ertisemenl, P~?moti~n or saJe of~~ ~rodl'.Ct or p~ocess, ~r in ~nn:c!ion w(lh lh~ r:_-publicalion of I his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2019
Lab Sample ID: 1909320-031C
Client Sample ID: TW4-70_09112019
ANALvr1cAL I AD0RAr0R1Es Collection Date: 9/11/2019 1000h
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 1959h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
I 7060-07-0
460-00-4
I 868-53-7
2037-26-5
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 13.6
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
49.9 50.00 99.7 72-151
53.8 50.00 108 80-152
48.1 50.00 96.1 72-135
52.6 50.00 105 80-124
Report Date: 9/30/2019 Page 70 of 80
All anal~ ses applic.i.ble to the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Per1inent sampling inrorma1ion is located on tJ1e auached COC Conlidenlial Business Jnformation: This repor1 is prO\·ided ror the esclnsi,-e use of the
~ddressee Pri\ ile~es o.r sob .. seq~ent ~~e of the ~~1e of this _co1~pany or an~ 1~mber or ils slnff or reproduclio~ ~f this repor.! in ~on~ection .. ,\ilh the a~~ ertisemenl. P~?molio.n ~· sn.le of~!~ ~rodl~CI or p~ocess, ~r in ~onn:c~ion '''!th th~ r:_·p~blication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: l 909320-031
Client Sample ID: TW4-70_09112019
A NA I vr1 c A 1. 1.AooA Aro A IE s Collection Date: 9/11/2019 1000h
Received Date: 9/13/2019 1025h
Analytical Results
Date
3440 South 700 West Compound Units Prepared
,alt Lake City, UT 84119 Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
9/21/201 9 306h
9/13/2019 1438h -----------
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 45.8
E353.2 0.100 6.89
Report Date: 9/30/2019 Page 38 of80
All annl~ ses applicuble 10 lhe CWA. SOWA. and RCRA are perfom1ed in accordilJlce to NELAC protocols, Pertinent sampling information is located on the au ached COC Confidential Business Information: This report is prorided for the c-.~clu1h·c-use of the
~cldressee. PriYile~es o.r sub,,5eq~1ent ~1~e of the ~~1e of lhis .co,~pany or ru,y ~mller of its staff, or reproduclio~ ~f this repm~ in ~~11::clion,. \\ith lhe ~~ertisemenL p~~molio.n or sale of ?'~Y ~rodl'.ct or p~ocess, ~r in ~nn~!ion \\~lh lh~ r~-p~btkadon of 1his report
American West
ANALYTICAL LAOORATORIE6
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-032C
Client Sample ID: TW4-75_09122019
Collection Date: 9/12/2019 717h
Received Date: 9/13/2019 1025h
Analytical Results
Analyzed: 9/18/2019 2019h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 75.6
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 50.6 50.00 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.0 50.00 104 80-152
Surr: Dibromotluoromethane 1868-53-7 48.5 50.00 96.9 72-135
Surr: Toluene-d8 2037-26-5 52.4 50.00 105 80-124
Report Date: 9/30/2019 Page 71 of 80
All analyses applicable to the CWA. SOWA. Md RCRA are perfom1ed in accordonce to NELAC protocols. Pertinent S!lmpling infom1&tion is located on the attached COC Conlidential Business Information: This report is provided for1he exclusi\ e use or1he
~ddressee P1frile~es orsub,,seq~enl ~~e of the ~~1e of this .c01~pru1y or an~ ~mber of ils slnfT, or reproductio~ ~flhis repoi; in _cOl~lection .. \,ith the ~vertisement, p~omotio_n 01 sale of ?1~). ~1odlic1 or p~ocess, ~1 in ~nn:_c~ion w!th th~ r:_·public~tion of this repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2019
Lab Sample ID: 1909320-032
Client Sample ID: TW4-75_09122019
ANAL vr, c AL L Aeo RAro R, es Collection Date: 9/12/2019 717h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 9/13/2019 1025h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
9/21/2019 323h E300.0 1.00 52.5
9/13/2019 1442h E353 .2 0.100 1.03
Report Date: 9/30/2019 Page 39 of 80
All analyses applicable 10 lhe CWA. SDWA. and RCRA a1e performed in accordance to NELAC protocols Pertinent sampling infommlion is located on the altached COC Confidential Business Information: This repon is proYided for the c:-:du~n'C' me of the
~ddressee. P,i, ile~es of su~seq~enl ~~e of the ~~ne of lhis .co1~pw1y or any ~mber of its slalT, or reproductio~ ~f lhis repo~ in .con~eclion~ \\ith I.he a~,,er1ise1~ent, P~?molio.n ~r ~aJe of ~~Y._~rodt~l or P~?cess, ~r in ~nn:c~ion \\·!th th~ r;:-p~bJicotiot, of1his reporl
ANALYTICAL LABORATOn lES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
l 909320-033A
Client Sample ID: Trip Blank
Collection Date: 9/10/2019
Received Date: 9/13/2019
Analytical Results
Analyzed: 9/18/2019 2039h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
627h
1025h
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 l.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < l.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual --
Surr: 1,2-Dichloroethane-d4 17060-07-0 49.4 50.00 98.9 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.7 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 47.8 50.00 95.6 72-135
Surr: Toluene-dB 2037-26-5 51.9 50.00 104 80-124
Report Date: 9/30/2019 Page 72 of 80
All analyses applicable h) the 'WA. SDWA. Md RCRA are performed in accordMce to NELAC protocols. Penmen! s~11n1>lm,g.infornm11on is located on lhe aWtched COC. Conr.ctenlial Business lnfonnalion: This repor1 is pro\'ided for the C'(Ch1sn-o u,:.:e of1he
~ddressee. Pri,·i\e~eso_tSu~l~I ~:'e oflhe ~~1c orlhis .co1~pany or any ~mber of its stnIT. or reproduct1~ ~flhis rq101~ ill ~011~1ect10'!. \\ilh the :i~~1ertise~enl, P~?molio.n ~r sa.le of ~!Y. ~rodl~cl or P~?cess, ~r in ~onn~c~ion w~Lh th~ r1;-p~bllcn11onor lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84 I I 9
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909134-018A
Client Sample ID: Trip Blank
Collection Date: 9/4/2019 1228h
Received Date: 9/6/2019 1030h
Analytical Results
Analyzed: 9/6/2019 1226h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
50.5 50.00
51.2 50.00
50.2 50.00
51.4 50.00
IOI 72-151
102 80-152
IOI 72-135
103 80-124
Report Date: 9/20/2019 Page 40 of 48
All ilm1I~ ses applicable to the CWA, SOWA. and RCRA are perfonned in accordance to NELAC protocols, Pertinent sampling information is localed 011 the allached COC Confidenliol Business Information: This repor1 is provided for lhe exclusi, e use of the
~ddressee, Pri, ile~es o:sub ... seq~ent ~1~e of1he ~:tr_ne of this .co1~pany or nny ~mbe1 of ils slnff, or reproduclio!~ ~f this repo~ in .co1~eclion,, ,\ith the ~\·ertisemenl, p~~motio.n or sale of~!) rrod~cl or P~?cess, ~r in ~onn:_c!ion w!th th~ r:_-p~blication of lhis repon
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Garrin Palmer
Energy Fuels Resources, Inc.
6425 S. Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 3rd Quarter Chloroform 2019
Dear Garrin Palmer: Lab Set ID: 1909134
American West Analytical Laboratories received sample( s) on 9/6/2019 for the analyses
presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
Thank You,
Digitally signed by Jose G.
JO Se G ~~~~~=Jose G. Rocha,
• o=American West Analytical
Laboratories, ou, Rocha ~:~tjose@awal-labscom.
Date: 2019,09,20 16:24:15 Approved by: -os·oo·
Laboratory Director or designee
Report Date: 9/20/2019 Page I of 48
All anal~·ses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols. Pertinent sampling information is located on Lhe attached COC Con(idenlinl Business Information: This report is provided for the exclusi\·e use oFthe
~ddressee Prl\ ile~es o_f su~seq~1enl ~~e of lhe ~~e of lhis .co~pan) or anr 1~mber of ils slafi, or reproducl10~ ~f this repo~ in ~~eel ion,. \\ilh the ~vertisemenl. P~?moti~n ~r sale of :U!~ ~rodL~cl or p~~ess, ?r in ~onn:c!ion w!lh th~ n:-publicaLion of 1his report
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
ANALYTICAL LABORATORIES Project: 3rd Quarter Chloroform 2019
Lab Set ID: 1909134
Date Received: 9/6/2019 1030h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1909134-00lA TW4-25 09042019 9/4/2019 1238h Aqueous Anions, E300.0
;alt Lake City, UT 841 I 9 1909134-00IB TW4-25 09042019 9/4/2019 1238h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-001 C TW4-25 09042019 9/4/2019 1238h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: (80 I) 263-8686 l 909 l 34-002A TW4-24 09042019 9/4/2019 1248h Aqueous Anions, E300.0
l 909 l 34-002B TW4-24 09042019 9/4/2019 1248h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] l 909 l 34-002C TW4-24 09042019 9/4/2019 1248h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260D/5030C
!-mail: [e-mail] l 909134-003A TW4-40 09042019 9/4/2019 1433h Aqueous Anions, E300.0
l 909134-003 B TW4-40 09042019 9/4/2019 1433h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1909134-003C TW4-40 09042019 9/4/2019 1433h Aqueous VOA by GC/MS Method
8260D/5030C
l 909 l 34-004A TW4-21 09042019 9/4/2019 1228h Aqueous Anions, E300.0
Kyle F. Gross 1909134-004B TW4-21 09042019 9/4/2019 1228h Aqueous Nitrite/Nitrate (as N), E353.2
l 909 l 34-004C TW4-21 09042019 9/4/2019 1228h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
1909134-00SA TW4-0l 09042019 9/4/2019 1411h Aqueous Anions, E300.0
Jose Rocha 1909134-00SB TW4-0l 09042019 9/4/2019 141 lh Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1909134-00SC TW4-0l 09042019 9/4/2019 141 lh Aqueous VOA by GC/MS Method
8260D/5030C
l 909 l 34-006A TW4-04 09042019 9/4/2019 1425h Aqueous Anions, E300.0
l 909134-006B TW4-04 09042019 9/4/2019 1425h Aqueous Nitrite/Nitrate (as N), E353.2
l 909 l 34-006C TW4-04 09042019 9/4/2019 1425h Aqueous VOA by GC/MS Method
8260D/5030C
1909134-007 A MW-26 09042019 9/4/2019 1330h Aqueous Anions, E300.0
l 909 l 34-007B MW-26 09042019 9/4/2019 1330h Aqueous Nitrite/Nitrate (as N), E353.2
l 909 l 34-007C MW-26 09042019 9/4/2019 1330h Aqueous VOA by GC/MS Method
8260D/5030C
l 909134-008A MW-04 09042019 9/4/2019 1402h Aqueous Anions, E300.0
1909134-008B MW-04 09042019 9/4/2019 1402h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-00SC MW-04 09042019 9/4/2019 1402h Aqueous VOA by GC/MS Method
8260D/5030C
1909134-009 A TW4-41 09042019 9/4/2019 1418h Aqueous Anions, E300.0
1909134-009B TW4-41 09042019 9/4/2019 1418h Aqueous Nitrite/Nitrate (as N), E353.2
l 909134-009C TW4-41 09042019 9/4/2019 1418h Aqueous VOA by GC/MS Method
8260D/5030C
1909134-0 IOA TW4-02 09042019 9/4/2019 1353h Aqueous Anions, E300.0
Report Date: 9/20/2019 Page 2 of 48
All anal~ ses applic.:ible Lo the CWA. SDWA, and RCRA are µerfom1ed in accordance lo NELAC protocols Pertinent sampling information is localed on lhe allached COC Confidential Business lnformalion: This report is provided for the exclusi, e U5e of the
~ddressee Prl\'ile~es o.r sub ... seq~ienl ~1~e of lhe ~~e of lhis .con,ipany or an~ ~mber of its s1aff, or reµroduclio~ ~~ this repo~ in 70~1eclion~ with lhe a~, ertise1:1enl, p~~moli~n ~· sale of~~~ ~rodt~t or p~ocess, ~r in ~onn~c~ion w~1h th~ r~-publication of this 1eporl
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2019
American West Lab Set ID: 1909134
ANALYTICAL LABORATORIES Date Received: 9/6/2019 1030h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
1909134-0 lOB TW4-02 09042019 9/4/2019 1353h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 1909134-0 IOC TW4-02 09042019 9/4/2019 1353h Aqueous VOA by GC/MS Method
8260D/5030C
~alt Lake City, UT 84119 1909134-01 lA TW4-ll 09042019 9/4/2019 1345h Aqueous Anions, E300.0
1909134-0 l IB TW4-ll 09042019 9/4/2019 1345h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-01 lC TW4-ll 09042019 9/4/2019 1345h Aqueous VOA by GC/MS Method
Phone:[phone]D/5030C
1909134-012A TW4-22 09042019 9/4/2019 1258h Aqueous Anions, E300.0
Toll Free: [phone] 1909134-012B TW 4-22_09042019 9/4/2019 1258h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 1909134-0 l 2C TW4-22 09042019 9/4/2019 1258h Aqueous VOA by GC/MS Method
~-mail: [e-mail] 8260D/5030C
1909134-013A TW4-39 09042019 9/4/2019 1322h Aqueous Anions, E300.0
web: www.awal-labs.com l 909134-0l 3B TW4-39 09042019 9/4/2019 1322h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-0 l 3C TW4-39 09042019 9/4/2019 1322h Aqueous VOA by GC/MS Method
8260D/5030C
Kyle F. Gross 1909134-014A TW4-19 09042019 9/4/2019 1445h Aqueous Anions, E300.0
1909134-014B TW4-19_09042019 9/4/2019 1445h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 1909134-014C TW4-19_09042019 9/4/2019 1445h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 1909134-0lSA TW4-20 09042019 9/4/2019 1314h Aqueous Anions, E300.0
QA Officer 1909134-015B TW4-20 09042019 9/4/2019 1314h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-0lSC TW4-20 09042019 9/4/2019 1314h Aqueous VOA by GC/MS Method
8260D/5030C
l 909134-016A TW4-37 09042019 9/4/2019 1305h Aqueous Anions, E300.0
1909134-016B TW4-37 09042019 9/4/2019 1305h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-016C TW4-37 09042019 9/4/2019 1305h Aqueous VOA by GC/MS Method
8260D/5030C
1909134-0l 7A TW4-60 09042019 9/4/2019 1500h Aqueous Anions, E300.0
1909134-0l 7B TW4-60 09042019 9/4/2019 1500h Aqueous Nitrite/Nitrate (as N), E353.2
1909134-0l 7C TW4-60 09042019 9/4/2019 1500h Aqueous VOA by GC/MS Method
8260D/5030C
1909134-018A Trip Blank 9/4/2019 1228h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 9/20/2019 Page 3 of 48
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols, Pertinent sampling information is localed on the attached COC Conliclenlial Business lnformnlion: This report is provided for lhe e.xclusire u<.e of the
~ddressee, Pri\ ile~es o! su~seq~nt .~e of lhe ·~:11_l1e of this .c01~pnn~ or nn~ ~mber of ils slaff. or reproduclio~ ~r this repm; in .co~eclion ... "ith the a~:ertisemenl, P~?molio.n or sale of ?-1!~ ~rodl~l or p1.ocess, ~r in '?°nn~c~ion w!th 1h~ r:-p~blico.tion or this repon
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
3rd Quarter Chloroform 2019
1909134
9/6/2019
9/4/2019
Intact
None
Holding Time and Preservation Requirements: The analysis and preparation of all
samples were performed within the method holding times. All samples were properly
preserved.
Preparation and Analysis Requirements: The samples were analyzed following the
methods stated on the analytical reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD:
Method Blanks (MB): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Samples (LCS): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicates (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, indicating no
apparent matrix interferences.
Corrective Action: None required.
Report Date: 9/20/2019 Page 4 of 48
All analyses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Per1inenl sampling information is localed on Lhe allached COC. Conridentinl Business Information: This repor1 is proYided for lhe exclusi,·e use of the
~ddressee Pri\'ile~es o_f sub__seq~enl ~~e of the ~?1.'1-e of this .co1~pa11y or rul) ~'!lber of its slaIT. or reproductio~ ~fthis repo~ in ~o~ection .. ,vith the a~vertisemenl, P~?molio.n or snle of~!) ~rod~cl or p1.?cess, ~r in ~nn~c)ion w!lh lh~ r~-publication oflhis 1eport
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
3rd Quarter Chloroform 2019
1909134
9/6/2019
9/4/2019
Intact
None
SW-846 8260D/5030C
Tetrahydrofuran
General Set Comments: Multiple target analytes were observed above reporting limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicate (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, indicating no
apparent matrix interferences.
Surrogates: All surrogate recoveries were within established limits.
Corrective Action: None required.
Report Date: 9/20/2019 Page 5 of 48
All an.1lyses applicnble 10 lhe CWA. SDWA. and RCRA are perfom1ed in accordimce to NELAC protocols Pe1tinenl sempliny information is located on the nttnched COC. Conlidenrinl Business lnrormolion: This report is prol'ided for 1he es:clusi, e use of lhe
~ddressee P1i, ile~es o:' sub .. seq~enl ~·~e of the ~~e of lhis .co1~pany or nnr ~mbe1· of its staIT, or reproductio~ ~f this repo~ in ~on~1ec1ion .. with the o~Yenisement, p~~moli~ or sale or ?Jf. ~1 od~t or p1;ocess, ?r in ~onn:_c!ion 11·!1h 1h7 r~·p~blication or I his report
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: WC
Method MDL
Reporting
Limit
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS-RI30362 Date Analyzed: 09/16/2019 1425h
Test Code: 300.0-W
Chloride 5.01 mg/L E300.0 0.0386 0.100 5.000 0 100
Lab Sample ID: LCS-Rl29962 Date Analyzed: 09/09/2019 827h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.03 mg/L E353.2 0.00363 0.0100 1.000 0 103
Limits
90-110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt % RPO Limit Qual
Report Date: 9/20/2019 Page 41 of 48
analyses applicable to the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COC Confidential Business lnformation: This repon is provided for the exclusive use of the addressee Privileges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte Result
Lab Sample ID: MB-R130362 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-R129962 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: WC
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
09/16/2019 1409h
mg/L E300_0 0.0386 0.100
09/09/2019 826h
mg/L E353.2 0.00363 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 9/20/2019 Page 42 of 48
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Jnfonnation: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contacL This
ANALYTICAL
3440 South 700 West
Salt Lake City, UT 84 I 19
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte
Lab Sample ID: 1909134-00JAMS
Test Code: 300.0-W
Chloride
Lab Sample ID: 1909134-007 AMS
Test Code:
Chloride
Lab Sample ID:
Test Code:
300.0-W
1909134-001 BMS
N02/N03-W-353.2
Nitrate/Nitrite ( as N)
Lab Sample ID: I909134-002BMS
Test Code: N02/N03-W-353.2
Nitrate/Nitrite ( as N)
Result Units Method
Date Analyzed: 09/16/2019 1532h
138 mg/L E300.0
Date Analyzed: 09/16/2019 1746h
177 mg/L E300.0
Date Analyzed: 09/09/2019 830h
11.0 mg/L E353,2
Date Analyzed: 09/09/2019 950h
144 mg/L E353.2
MDL
0.772
0.772
0.0363
0.363
Reporting
Limit
2.00
2.00
0.100
1.00
Dept: WC
QC Type: MS
Amount
Spiked
100.0
100.0
10.00
100.0
Spike Ref.
Amount
35.9
76.2
0.548
36.4
%REC
102
101
105
107
Limits
90 -110
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 9/20/2019 Page 43 of 48
analyses applicable to the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax: [phone] Laboratory Director
e-mail: awal@ awal-labs.com, web: www.awal-Iabs.com
Jose Rocha
QA Officer
American West QC SUMMARY REPORT ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1909134 Dept: WC
Project: 3rd Quarter Chloroform 2019 QC Type: MSD
-----
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1909134-00JAMSD Date Analyzed: 09/16/2019 1549h
Test Code: 300.0-W
Chloride 137 mg/L E300.0 0.772 2.00 100.0 35.9 101 90 -110 138 0.621 20
Lab Sample ID: 1909134-007 AMSD Date Analyzed: 09/16/2019 1802h
Test Code: 300.0-W
Chloride 175 mg/L E300.0 0.772 2.00 100.0 76.2 98.4 90 -110 177 1.27 20
Lab Sample ID: 1909134-00IBMSD Date Analyzed: 09/09/2019 831 h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.3 mg/L E353.2 0.0363 0.100 10.00 0.548 108 90 -110 11 2.86 10 -Lab Sample ID: I909134-002BMSD Date Analyzed: 09/09/2019 952h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 144 mg/L E353 2 0.363 1.00 100.0 36.4 108 90 -110 144 0.278 10
Report Date: 9/20/2019 Page 44 of 48
analyses applicable to the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tt-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re•publication of this report for any purpose other than for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-3 090619A Date Analyzed: 09/06/2019 743h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-3 0906198
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.2 µg/L SW8260D
19.2 µg/L SW8260D
14.7 µg/L SW8260D
19.3 µg/L SW8260D
49.4 µg/L SW8260D
50.6 µg/L SW8260D
50.7 µg/L SW8260D
50.6 µg/L SW8260D
Date Analyzed: 09/06/2019 1758h
22.9 µg/L SW8260D
23.l µg/L SW8260D
14.5 µg/L SW8260D
23.6 µg/L SW8260D
50.5 µg/L SW8260D
49.3 µg/L SW8260D
50.3 µg/L SW8260D
48.8 µg/L SW8260D
0.262 1.00 20.00 0 96.0
0.166 1.00 20.00 0 95.9
0.832 1.00 20.00 0 73.3
0.448 1.00 20.00 0 96.3
50.00 98.8
50.00 101
50.00 IOI
50.00 101
0.262 1.00 20.00 0 115
0.166 1.00 20.00 0 116
0.832 1.00 20.00 0 72.6
0.448 1.00 20.00 0 118
50.00 101
50.00 98.6
50.00 101
50.00 97.7
Limits
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 9/20/2019 Page 45 of 48
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC, Confidential Business Jnformation: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tl-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Garrin Palmer
MSVOA
MBLK
Spike Ref.
Amount %REC
Lab Sample ID: MB VOC-3 090619A Date Analyzed: 09/06/2019 803h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-3 090619B
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
49.3
49.2
48.3
49.7
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
51.5
50.9
49.4
50.5
µg/L SW8260D 0.262 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.832 1.00
µg/L SW8260D 0.448 1.00
µg/L SW8260D 50.00 98.6
µg/L SW8260D 50.00 98.4
µg/L SW8260D 50.00 96.7
µg/L SW8260D 50.00 99.5
09/06/2019 1818h
µg/L SW8260D 0.262 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.832 1.00
µg/L SW8260D 0.448 1.00
µg/L SW8260D 50.00 103
µg/L SW8260D 50.00 102
µg/L SW8260D 50.00 98.8
µg/L SW8260D 50.00 101
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt % RPO Limit Qual
Report Date: 9/20/2019 Page 46 of 48
analyses applicable to the CWA. SOWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is prov1ded for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909134
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: MS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1909107-00UMS Date Analyzed: 09/06/2019 842h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 1909134-00JCMS
Test Code: 8260D-W-DEN I 00
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
197 µg/L SW8260D
201 µg/L SW8260D
141 µg/L SW8260D
189 µg/L SW8260D
491 µg/L SW8260D
499 µg/L SW8260D
503 µg/L SW8260D
502 µg/L SW8260D
Date Analyzed: 09/06/2019 1857h
415 µg/L SW8260D
781 µg/L SW8260D
269 µg/L SW8260D
411 µg/L SW8260D
999 µg/L SW8260D
992 µg/L SW8260D
991 µg/L SW8260D
973 µg/L SW8260D
2.62 10.0 200.0 0 98.4
1.66 10.0 200.0 0 IOI
8.32 10.0 200.0 0 70.4
4.48 10.0 200.0 0 94.5
500.0 98.2
500.0 99.7
500.0 IOI
500.0 100
5.24 20.0 400.0 0 104
3.32 20.0 400.0 380 100
16.6 20.0 400.0 0 67.2
8.96 20.0 400.0 0 103
1,000 99.9
1,000 99.2
1,000 99.1
1,000 97.3
Limits
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPO Limit Qua]
Report Date: 9/20/2019 Page 4 7 of 48
analyses applicabJe to the CW A. SDW A, and RCRA are perfonned in accordance to N ELAC protocols Pertinent samphng infom1ation is located on the attached COC. Confidential Business Information: l11is report is provided for the exclusive use of the addressee. Privlleges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1909134 Dept: MSVOA
Project: 3rd Quarter Chloroform 2019 QC Type: MSD
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1909107-00 l IMSD Date Analyzed: 09/06/2019 902h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 202 µg/L SW8260D 2.62 10.0 200.0 0 101 77 -143 197 2.66 35
Chloroform 208 µg/L SW8260D 1.66 10.0 200.0 0 104 85 -124 201 3.23 35
Chloromethane 150 µg/L SW8260D 8.32 10.0 200.0 0 75.l 30 -149 141 6.46 35
Methylene chloride 194 µg/L SW8260D 4.48 10.0 200.0 0 97.2 65 -I 54 189. 2.87 35
Surr: I ,2-Dichloroethane-d4 488 µg/L SW8260D 500.0 97.6 80 -136
Surr: 4-Bromofluorobenzene 495 µg/L SW8260D 500.0 99.0 85 -121
Surr: Dibromofluoromethane 499 µg/L SW8260D 500.0 99.8 78 -132
Surr: Toluene-d8 503 µg/L SW8260D 500.0 101 81 -123
Lab Sample ID: 1909134-00JCMSD Date Analyzed: 09/06/2019 1916h
Test Code: 8260D-W-DENlOO
Carbon tetrachloride 417 µg/L SW8260D 5.24 20.0 400.0 0 104 77 -143 415 0.577 35
Chloroform 763 µg/L SW8260D 3.32 20.0 400.0 380 95.7 85 -124 781 2.31 35
Chloromethane 285 µg/L SW8260D 16.6 20.0 400.0 0 71.3 30 -149 269 5.99 35
Methylene chloride 410 µg/L SW8260D 8.96 20.0 400.0 0 103 65 -I 54 41 l 0.341 35
Surr: I ,2-Dichloroethane-d4 993 µg/L SW8260D l,000 99.3 80 -136
Surr: 4-Bromofluorobenzene 964 µg/L SW8260D l,000 96.4 85 -121
Surr: Dibromofluoromethane 990 µg/L SW8260D l,000 99.0 78 -132
Surr: Toluene-d8 978 µg/L SW8260D 1,000 97.8 81 -123
Report Date: 9/20/2019 Page 48 of 48
analyses applicable to the CWA. SDWA, 3Tld RCRA are performed in accordance to NE LAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business rnfonnation: This report is provided fort.he exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West Analytical Laboratories Rpt Emailed:
WORK ORDER Summary
Client:
Client ID:
Project:
Energy Fuels Resources, Inc.
ENE300
3rd Quarter Chloroform 2019
Contact: Garrin Palmer
QC Level: III
Work Order: 1909134
Due Date: 9/20/2019
WO Type: Project
Comments: QC 3 (no chromatograms). EDD-Denison. CC [e-mail].& [e-mail]. Do not use "*R_" samples as MS/MSD.;
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1909134-00lA TW4-25_09042019 9/4/2019 1238h 9/6/2019 1030h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1909134-001B N02/N03-W-353.2 elf. no2/no3
1 SEL AnaZ.JJ_tes: N03N02N
1909134-00lC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEN 100; # of A11a/ytes: 4 I # of Surr: 4
l 909 l34-002A TW4-24_09042019 9/4/2019 1248h 9/6/2019 1030h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1909134-002B N02/N03-W-353.2 elf-no2/no3
1 SEL AnaiJJ_tes: N03N02N
1909134-002C 8260D-W-DEN100 VOCFridge
-Test Group: 8260D-W-DENJOO; # oLAnalytes: 4 I # oJ_Sull: 4
1909l34-003A TW4-40_09042019 9/4/2019 1433h 9/6/2019 1030h 300.0-W Aqueous df-we
1 SEL Analytes: CL
1909134-003B N02/N03-W-353.2 elf-no2/no3
I SEL Analytes: N03N02N
1909134-003C 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEN100; # of Analytes: 4 I #_()f S11rr: 4
1909l34-004A TW4-21_09042019 9/4/2019 1228h 9/6/2019 1030h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1909134-004B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1909l34-004C 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of AnalJl_tes: 4 /# ofSull: 4
1909134-00SA TW4-01_09042019 9/4/2019 1411h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1909134-00SB N02/N03-W-353.2 df-no2/no3
1 SEL AnalJ>tes: N03N02N
1909134-00SC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of A11alytes: 4 I # of Surr: 4
UL
Denison
Page 1 of 4
~
3
3
3
3
Printed: 09/10/19 17:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK___ HOK __ _ HOK___ COC Emailed ____ _
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
1909134-006A TW4-04_09042019
1909134-006B
1909134-006C
1909134-00?A MW-26_09042019
1909134-00?B
1909134-00?C
1909134-00SA MW-04_09042019
1909134-00SB
1909134-00SC
1909134-009A TW4-41_09042019
1909134-009B
1909134-009C
1909134-0lOA TW4-02_09042019
1909134-0lOB
1909134-01 oc
1909134-0llA TW4-11_09042019
1909134-0llB
1909134-01 lC
Work Order: 1909134
Due Date: 9/20/2019
Collected Date Received Date Test Code Matrix Set Storage
9/4/2019 1425h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anal}'_tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENIOO; # of Analytes:_ 41 # of Surr: 4
9/4/2019 1330h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of An.dlytes: 4/# of Surr: 4
9/4/2019 1402h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Anal}'les: CL
N02/N03-W-353.2 df-no2/no3
1 SEL AnaQ!les: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENI00; # of Analytes: 41 # of Surr: 4
9/4/2019 1418h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENI00; # of Analytes: 4 1 # of Surr: 4
9/4/2019 1353h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Ana/ytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana1l_tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJOO; # of Analytes: 4/# ofSurr: 4
9/4/2019 1345h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Analy tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 1 # of Surr: 4
Page2 of4
3
3
3
3
3
Printed: 09/10/19 17:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed,_ ___ _
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
1909134-012A TW4-22_09042019
1909134-012B
1909134-012C
1909134-0lJA TW 4-39 _ 09042019
1909134-013B
1909134-0 BC
1909134-014A TW4-19_09042019
1909134-014B
1909134-014C
1909134-0lSA TW4-20_09042019
1909134-0ISB
1909134-0lSC
1909134-016A TW4-37_09042019
1909134-016B
1909134-016C
1909134-017A TW4-60_09042019
1909134-017B
Work Order: 1909134
Due Date: 9/20/2019
Collected Date Received Date Test Code Matrix Sel Storage
9/4/2019 1258h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: §_260D-W-DENIOO; # of Analyti!£ 4 I# of Su": 4
9/4/2019 1322h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# of Surr: 4
9/4/2019 1445h 9/6/2019 1030h 300.0-W Aqueous df-wc
1 SELAnafxtes: CL
N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260JJ-W-DENJOO; # of Analytes: 4 I# of Su": 4
9/4/2019 1314h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Ana/ytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I# of Surr: 4
9/4/2019 1305h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENIOO; # of Analytes: 4 I# of Su": 4
9/4/2019 1500h 9/6/2019 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
Page3 of4
3
3
3
Printed: 09/10/19 I 7:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK_~-HOK __ _ HOK___ COC Emailed ____ _
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID Collected Date
1909134-0l?C T\V~0_09042019 9/4/2019 1500h
1909134-0lSA Trip Blank 9/4/2019 1228h
Received Date
9/6/2019 1030h
9/6/2019 1030h
Test Code Matrix
8260D-W-DEN100 Aqueous
Work Order: 1909134
Due Date: 9/20/2019
Sel Storage
VOCFridge
Test Grou2_: 8260D-W-DENJOO; # of Analytes: 4/# ofSurr: 4
8260D-W-DEN100 Aqueous VOCFridge
Test Group: 8260D-W-DEN100; # of Analytes: 4 I # ofSurr: 4
Page4of4
3
3
Printed: 09/10/19 17:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK_· __ HOK __ _ HOK___ COC Emailed. ____ _
4
8
8
American West
Analytical Laboratories
463W.3600S. Saltl.akeCity,UT 84115
Phone# [phone] Too Free# [phone]
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact; Ganin Palmer
Phone#: [phone] Gel#:
[e-mail], KWeinel@energyt\lels.com;
Emal; dtmllraleneri:z:!!!els.com
Project Name: 3rd Quarter Chloroform 2019
Project#;
PO#:
Sampler Name; Tanner Holliday
Date
Samele ID: Sameled
'l'W4-25_09042019 9/4/2019
TW4-24_09042019 9/4/2019
TW~_09042019 9/4/2019
TW4-21_09042019 9/4/2019
TW4-01_09042019 9,l4/2019
TW4-04_09042019 9/4/2019
MW-26_09042019 9/4/2019
MW-04_09042019 9/4/2019
TW~1_09042019 9/4/2019
I TW4-02_09042019 10
11
9/4/2019
1 TW4-11_09042019 9/4/2019
12 t TW4-22_09042019 9/4/2019
13 I TW4-39_09042019 9/4/2019
a.to:
I
=.:""by:..:--\~ d ~ ~,,. µj / / IV!f/2011
V ;1rne:
PrintNomo: Tonnar""'""-113'
!wllnqu!,i,od by: Dato:
51onmm,
1•m"' _,N.emo:
RDl!nqui&l,od by: Clabo: Sinn-Tlrno:
PrinlNamn:
Rolinqu!l!hod by: ~
lsi..naJun,
Time.:
PJ1ntNBmo:
Time
Sameled
1238
1248
1433
1228
1411
1425
1330
1402
1418
1353
1345
1258
1322
Received by:
S1anal!JJ8
PrtnlName:
CHAIN OF CUSTODY
All anaJysls wil be oonductod using NElAP accradited methods aoo el data wil be reported using AWM.'s standard analyle K61s and n,porting
rrn1ts (PQL) unles .. pec:lflcally reqt-iod oUlerwi9e on this C!1aJn of CU6tody end/or attached documentation.
QC Level: Tum Around Time: Unless other arrangements have been made,
signed reports wlll be emailed by 5:00 pm on
3 Standard the day they are due.
X Include EDD;
LOCUS UPLOAD
ZXCEL
Field Filtered For:
For Compllance With:
D NELAP
D RCRA
0 CWA
tJ SDWA
0 ELAP/A21.A
a' 0 NLI.AP ~ <:) D Non-Compliance
Ci Cl "CT' D Other:
~ "1 I'! >< ... 0 " 0 IC C :s l'l Cl C'i1 ~ "' g ::;; ~ ~ Known Hazards 0 ., ..... ~ • (.) ci C'I u & 't; E 0 tl g "' Samele Comments .. "' tll
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X .X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
Date: Special Instructions:
Time:
l °LP9Btr
AWAL Lab Sample Set II
Page 1 al 2
Due Date:
°' U> lC,
Laboratory Use Only
Samples Wen,: • l.9-.rS
~~ 2AinbloJ,I ·11oc1
3 Temperatura U ·c
4 Received Brok""'1..eelcing ~mpropettf st,
~P-ed N ·-N
.e RO<l!Mld WllNn C)Tlmoo N
'°""T!lf>GWas:
,~ono ~orP~ y N Q,
2(!'.jkon onO~erP ~ -~;fl y N ,
3 Present on Sample
y N NI\
4 Unbroken on Sample
y N NA
isaepancles Be~n Sample
y N abels and COCR~
Received by: Date: See the Analytical Scope of Work for Reporting Limits and voe
Signature analyte list.
rnme:
PrtntName:
Rece.ived by: Date:
ISlonatura
Tlme:
Prtr!IName; ..... ,., I • -Received by: ~\()Al a"s\Cr..Y-k_1"..:> Pate: q ln I\ c; Slonature J
~~.~.llAY'\ Time: rf'I ·l~) Print Name;
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, lJT 84115
Phone# [phone] Toll Free# [phone] L~ Fax# [phone] Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: GarriD. Palmer
Phone#: [phone] Cell#: gpalmez@eiieri:,faela.com.; KWeme:@)e.,:,.....,-fDela.com.;
Email: dtm~cinfitela.com.
Project Name: 3rd Quarter Chloroform 2019
Project#:
PO#:
Sampler Name: Tanner Hofilday
Date
Sample.ID: Sampled
TW4-19_09042019 9/4/2019
TW4-20_09042019 9/4/2019
• TW4-37_09042019 9/4/2019
TW4-60_09042019 9/4/2019
TRIP BLANK 9/4/2019
'
I
I
~
1
2
3
RlolJnq.-by: :::I jf,,_/L/ Datte
''""""'"'" • Jt.J1{ l'<... , -:_ IIIS/2011
/ '"'""' PrlnlNamo! T..-Hol"""" ''"' Rol~by: Dllto: ,~--,,.,,.,
PrintNane;
RollllQWl)ocf by: Oatw.
ISlanahn
TJm,r.
Plin!Nano:
Roll~by: Dido:
$'""-'•~
Timr.
Prln!NM,o:
I
Time
Sampled
1445
1314
1305
1500
1228
Received by:
Sklnebre
1Pr1ntNeme:
CHAIN OF CUSTODY
'
All analysis wli be conducted using NELAP a=edlted -hods and ell data will be 181)0rt8d using AWPu.'s stand&fd analyte llsls and reporting
limits (POL) unless specifically requested otherwise on this Chain of Custody and/or attached documentation.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed roports win be emaned by 5:00 pm on
3 Standard the day Uiey are due~
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
D NELAP
D RCRA
D CWA
D SDWA
D ELAP/A2LA
c' D NLLAP & <:i D Non-Compliance &i 0 G' D Other. "l I!! >( ,2. ... 0 CD 0 IO C :.s I') :e ~ O · 0 ~
C I!: 5l ~ Known Hazards 0 .. .... ::t. • 0 1i ('II 0 & '5 E 0 a g ., I!: Sample Comments "" <fl
5 w X X X
5 w X X X
5 w X X X
5 w X X X
3 w X
Date: Special Instructions:
rnme:
Page 2 of 2
Due Date: 20J l 9 ~ ,
Laboratory Use Only
SamplesW""": ~
1~delivered
2 -~
3 Temperature ~ ·c
4 Received Broken/Leaking
(Improperly s""Z, y . N
5~Preserved y N ... al bench
y N
6 .Received Within rJrTimes N
COCTapeWes. tYntoo~e,7!/tt-
t7~:-·~
3 Present on Sample
y N N.\
4 .Unbroken on Semple A
Y N NA ~--~ Ll!bola and coc Record
y N
Received by: Dale: Sec the Analytical Scope of Work for Reporting Limits and voe
~1nnah.Jre analyte list.
Time:
:)rint Name:
~eceived by: Date:
Slanature
Time: ' PrintName: ""-,.,
::::by:x 10 M , 1\ c ri.~b ~Ap.) Oate: Lt lol l ci
PrintName: ,\)e..v\\~~n J..\JJ\ inm&: ,.e t-:S'O
Analysis
Ammonia
COD
Cyanide
Metals
N02&
N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s ,H amp1e ~et .ll.xtensmu auo p
Preservative -mt -002--003 -o~ --oos -t>O~
pH<2H2S04
pH<2H2S04
pH>12NaOH
pH<2HN03
pH<2H2S04 \}e,S ,JeS ye0 ye,s ·ye..s lyes
pH<ZHCL .
pH<2H2S04
pH>9NaOH,
Zn Acetate
pH<2H2S04
pH<2H2S04
Pour a small amount of sample in the sample lid
Pour sample from lid gently over wide range pH paper
Do Not dip the pH paper in the sample bottle or lid
...-Dt)T -00~ -061
ye.-s Hes ye5
-OltJ -on
yes l'fes
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
•
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH> due to the samole matrix interference.
-()12
y~S
Lab Set ID:
pH Lot#:
-013 -DILi
ye5 yes
1qo91nt\
(a[ff{5
-Dls -0/b -DJ?
yes y.~ ~~
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
American West Blanding, UT 84511
ANAlVTICAl LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
TEL: [phone]
RE: 3rd Quarter Chloroform 2019
Dear Tanner Holliday: Lab Set ID: 1909320
American West Analytical Laboratories received sample(s) on 9/13/2019 for the analyses
presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL ). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
This is a revision to a report originally issued 9/30/2019. Information herein supersedes
that of the previously issued reports. Pages 1 and 40-59 have been revised. The footnotes
have been updated.
Thank You,
Digitally signed by Jose G.
JO Se G ~~~~~=Jose G. Rocha,
• o=American West Analytical
Laboratories, ou=UT00031, RO Ch a ~::[e-mail],
Date: 2019.10.23 13:40:24 Approved by: -os·oo·
Laboratory Director or designee
Report Date: I 0/23/2019 Page I of 80
All anal~ ses applicable lo lhe CWA. SDWA. and RCRA are perfomled in accordance lo NELAC protocols Pertinent s.>mpling informal ion is localed on the aUached COC Conlidential Business lnformalion: This report is provided for lhe exclush e use of lhe
~ddresscc Pri, ile~es o_f su~seq~ent ~~e of the ~~le of this .corr:1pany or an~ t~mber of its slnIT, or reproducli0t~ ~(this repo~ in ~on~1ec1ion~ wilh the a~,ertisement, p~~moli°:° or sale or ?'!Y ~rodL'.cl or p~ocess, ~r in ~onn~!ion "(lh 1h~ r~-publicaJion of lhis report
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANALYTICAL LABORATORIES Project: 3rd Quarter Chloroform 2019
Lab Set ID: 1909320
Date Received: 9/13/2019 1025h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1909320-00 l A TW4-03R 09102019 9/10/2019 627h Aqueous Anions, E300.0
,alt Lake City, UT 84119 1909320-001 B TW4-03R 09102019 9/10/2019 627h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-001 C TW4-03R 09102019 9/10/2019 627h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: (80 I) 263-8686 1909320-002A TW4-03_09112019 9/11/2019 715h Aqueous Anions, E300.0
1909320-0028 TW4-03 09112019 9/11/2019 715h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1909320-002C TW4-03 09112019 9/11/2019 715h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260D/5030C
!-mail: [e-mail] 1909320-003A TW4-28 09112019 9/11/2019 740h Aqueous Anions, E300.0
l 909320-003B TW4-28 09112019 9/11/2019 740h Aqueous Nitrite/Nitrate (as N), E353 .2
web: www.awal-labs.com l 909320-003C TW4-28 09112019 9/11/2019 740h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-004A TW4-32 09112019 9/11/2019 748h Aqueous Anions, E300.0
Kyle F. Gross 1909320-0048 TW4-32_09112019 9/11/2019 748h Aqueous Nitrite/Nitrate (as N), E353.2
l 909320-004C TW4-32 09112019 9/11/2019 748h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
1909320-00SA TW4-12 09112019 9/11/2019 755h Aqueous Anions, E300.0
Jose Rocha 1909320-00SB TW4-12 09112019 9/11/2019 755h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1909320-00SC TW4-12 09112019 9/11/2019 755h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-006A TW4-13 09112019 9/11/2019 804h Aqueous Anions, E300.0
1909320-0068 TW4-13 09112019 9/11/2019 804h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-006C TW4-13 09112019 9/11/2019 804h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-007 A TW4-36 09112019 9/11/2019 812h Aqueous Anions, E300.0
1909320-0078 TW4-36 09112019 9/11/2019 812h Aqueous Nitrite/Nitrate (as N), E353.2
l 909320-007C TW4-36 09112019 9/11/2019 812h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-008A TW4-31 09112019 9/11/2019 820h Aqueous Anions, E300.0
1909320-0088 TW4-31 09112019 9/11/2019 820h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-008C TW4-31 09112019 9/11/2019 820h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-009A TW4-42 09112019 9/11/2019 833h Aqueous Anions, E300.0
1909320-0098 TW4-42 09112019 9/11/2019 833h Aqueous Nitrite/Nitrate (as N), E353 .2
1909320-009C TW4-42 09112019 9/11/2019 833h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-0lOA TW4-34 09112019 9/11/2019 843h Aqueous Anions, E300.0
Report Date: 9/30/2019 Page 2 of 80
All anal) ses applicable to lhe CWA. SOWA. and RCRA ::ire performed in accordance to NELAC protocols Pe1tinenl sampling i11rormatio11 is located 011 the attached COC Confidentiol Business lnrormalion: This repor1 is provided for 1he exclusi, e use of the
~ddressee Pri, ile~es o_f sub,..5eq~1enl ~~e of the ~~1e of this
0
co1~pany or ru,~· ~1:nbe1 of its slafT. or reproduclio~ ~fthis repo~ in ~0~1ccl1on .. \\ith then~, ertisement p~~motio.n or saJe of~~~ ~ro<h~cl or p~ocess, ~r in ~nn~c~irn1 w~th th~ n;_·publication of this report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 3rd Quarter Chloroform 2019
American West Lab Set ID: 1909320
ANALYTICAL LABORATORIES Date Received: 9/13/2019 1025h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
1909320-0 I OB TW4-34 09112019 9/11/2019 843h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 1909320-0 I OC TW4-34 09112019 9/11/2019 843h Aqueous VOA by GC/MS Method
8260D/5030C
;alt Lake City, UT 84119 1909320-01 lA TW4-35 09112019 9/11/2019 853h Aqueous Anions, E300.0
1909320-01 lB TW4-35 09112019 9/11/2019 853h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-011 C TW4-35 09112019 9/11/2019 853h Aqueous VOA by GC/MS Method
Phone: [phone]D/5030C
1909320-012A TW4-23 09112019 9/11/2019 902h Aqueous Anions, E300.0
Toll Free: [phone] 1909320-012B TW4-23 09112019 9/11/2019 902h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 1909320-012C TW4-23 09112019 9/11/2019 902h Aqueous VOA by GC/MS Method
!-mail: [e-mail] 8260D/5030C
1909320-013A MW-32_09112019 9/11/2019 1435h Aqueous Anions, E300.0
web: www.awal-labs.com 1909320-013B MW-32 09112019 9/11/2019 1435h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-013C MW-32 09112019 9/11/2019 1435h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-014A TW4-38 09112019 9/11/2019 929h Aqueous Anions, E300.0 Kyle F. Gross 1909320-014B TW4-38 09112019 9/11/2019 929h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 1909320-014C TW4-38 09112019 9/11/2019 929h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 1909320-015A TW4-14 09112019 9/11/2019 940h Aqueous Anions, E300.0
QA Officer 1909320-0lSB TW4-14_09112019 9/11/2019 940h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-0 l 5C TW4-14 09112019 9/11/2019 940h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-016A TW4-27 09112019 9/11/2019 947h Aqueous Anions, E300.0
1909320-016B TW4-27 09112019 9/11/2019 947h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-016C TW4-27 09112019 9/11/2019 947h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-017 A TW4-05 09112019 9/11/2019 1000h Aqueous Anions, E300.0
1909320-017B TW4-05 09112019 9/11/2019 1000h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-017C TW4-05 09112019 9/11/2019 1000h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-018A TW4-06 09112019 9/11/2019 1010h Aqueous Anions, E300.0
1909320-018B TW4-06 09112019 9/11/2019 1010h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-0 l 8C TW4-06 09112019 9/11/2019 1010h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-019A TW4-30 09112019 9/11/2019 1022h Aqueous Anions, E300.0
1909320-019B TW4-30 09112019 9/11/2019 1022h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-019C TW4-30 09112019 9/11/2019 1022h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 9/30/2019 Page 3 of80
All anal) ses applicable Lo the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinenl sampling information is locc1Led on the attached COC Confidential Business Information: This report is pro,·ided for the exclusi, e use or1he
~ctdressee, Pti, ile~es o: sub~seq~ent ~,~e or the ~~1e or this .con;,pan~ or M) 1~~be1 or its staff, or reproduclio~ ~f this repo~ in ~01~1ection ... ,vilh lhe a~\'ertisemenL P~?molio.n or sale of ?1!~ ~rodl~cl or p~ocess, ~r in ';°""~c!ion w!lh th~ r~-p~blication of this repon
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 3rd Quarter Chloroform 20 I 9
American West Lab Set ID: 1909320
ANALYTICAL LABORATORIES Date Received: 9/13/2019 1025h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
l 909320-020A TW4-18 09112019 9/11/2019 1035h Aqueous Anions, E300.0
3440 South 700 West l 909320-020B TW4-18 09112019 9/11/2019 1035h Aqueous Nitrite/Nitrate (as N), E353.2
;alt Lake City, UT 84119 l 909320-020C TW4-18 09112019 9/11/2019 1035h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-02 lA TW4-09 09112019 9/11/2019 1045h Aqueous Anions, E300.0
1909320-02 lB TW4-09 09112019 9/11/2019 1045h Aqueous Nitrite/Nitrate (as N), E353.2
Phone: [phone] 1909320-021 C TW4-09 09112019 9/11/2019 1045h Aqueous VOA by GC/MS Method
8260D/5030C Toll Free: [phone] 1909320-022A TW4-16 09122019 9/12/2019 708h Aqueous Anions, E300.0
Fax: [phone] l 909320-022B TW4-16 09122019 9/12/2019 708h Aqueous Nitrite/Nitrate (as N), E353.2
!-mail: [e-mail] l 909320-022C TW4-16 09122019 9/12/2019 708h Aqueous VOA by GC/MS Method
8260D/5030C
web: www.awal-labs.com l 909320-023A TW4-08 09122019 9/12/2019 717h Aqueous Anions, E300.0
1909320-023B TW4-08 09122019 9/12/2019 717h Aqueous Nitrite/Nitrate (as N), E353.2
l 909320-023C TW4-08 09122019 9/12/2019 717h Aqueous VOA by GC/MS Method
Kyle F. Gross 8260D/5030C
l 909320-024A TW4-33 09122019 9/12/2019 732h Aqueous Anions, E300.0
Laboratory Director 1909320-024B TW4-33 09122019 9/12/2019 732h Aqueous Nitrite/Nitrate (as N), E353.2
l 909320-024C TW4-33 09122019 9/12/2019 732h Aqueous VOA by GC/MS Method
Jose Rocha 8260D/5030C
QA Officer l 909320-025A TW4-29 09122019 9/12/2019 742h Aqueous Anions, E300.0
1909320-025B TW4-29 09122019 9/12/2019 742h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-025C TW4-29 09122019 9/12/2019 742h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-026A TW4-10 09122019 9/12/2019 754h Aqueous Anions, E300.0
l 909320-026B TW4-10 09122019 9/12/2019 754h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-026C TW4-10 09122019 9/12/2019 754h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-027 A TW4-07 09122019 9/12/2019 808h Aqueous Anions, E300.0
1909320-027B TW4-07 09122019 9/12/2019 808h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-027C TW4-07 09122019 9/12/2019 808h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-028A TW4-26 09122019 9/12/2019 817h Aqueous Anions, E300.0
l 909320-028B TW4-26 09122019 9/12/2019 817h Aqueous Nitrite/Nitrate (as N), E353.2
1909320-028C TW4-26 09122019 9/12/2019 817h Aqueous VOA by GC/MS Method
8260D/5030C
1909320-029A TW4-16R 09112019 9/11/2019 11 lOh Aqueous Anions, E300.0
1909320-029B TW4-16R 09112019 9/11/2019 1110h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 9/30/2019 Page 4 of 80
All an.tl)Ses applicable lo lhe CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling information is localed on lhe al1ached COC Confidential Business Information: This report is pro,·ided for the exclusi\e use or the
!ddressee P1i\'iie~es o:sub~seq~ent ~~e or1he ~~ne of lhis .crn~pany or an) ~mber of its slaff, or reproduclio~ ~fthis repo~ in ~on~1eclion~ "ilh Lhe ll~vertisemenl, p~~molio.n or saJe of~!). ~rod~cl or P~?cess, ~r in i;onn~~ion w!lh th~ r~·publication of this report
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client:
Project:
Lab Set ID:
Date Received:
Lab Sample ID
1909320-029C
l 909320-030A
l 909320-030B
1909320-030C
1909320-03 lA
1909320-03 lB
1909320-031 C
1909320-032A
1909320-032B
l 909320-032C
1909320-033A
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2019
1909320
9/13/2019 1025h
Client Sample ID
TW4-16R 09112019
TW4-65 09112019
TW4-65 09112019
TW4-65_09l 12019
TW4-70 09112019
TW4-70 09112019
TW4-70 09112019
TW4-75 09122019
TW4-75 09122019
TW4-75 09122019
Trip Blank
Contact: Tanner Holliday
Date Collected Matrix Analysis
9/11/2019 1110h Aqueous VOA by GC/MS Method
8260D/5030C
9/11/2019 715h Aqueous Anions, E300.0
9/11/2019 715h Aqueous Nitrite/Nitrate (as N), E353.2
9/11/2019 715h Aqueous VOA by GC/MS Method
8260D/5030C
9/11/2019 1000h Aqueous Anions, E300.0
9/11/2019 1000h Aqueous Nitrite/Nitrate (as N), E353.2
9/11/2019 1000h Aqueous VOA by GC/MS Method
8260D/5030C
9/12/2019 717h Aqueous Anions, E300.0
9/12/2019 717h Aqueous Nitrite/Nitrate (as N), E353.2
9/12/2019 717h Aqueous VOA by GC/MS Method
8260D/5030C
9/10/2019 627h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 9/30/2019 Page 5 of80
All anal~ ses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance Lo NELAC prolocols, Pertinent sampling information is located on the allached COC Confidential Business [nformalion: This reporl is p1m·ided for lhe exclusi, e use or1he
~ddressee. P1i\ ile~es o.f sub~seq~enl ~~e of the ~:u:i1e of this .crn~pan~ or an~ 1~mber of its staJT. or reproduclio~ ~f this repo~ in ~01~1ection ... \\ilh the u~,. ertisemenl P~?motio.n ~· snJe of ?1!~ ~ro<h~cl or p~ocess, ~1 in ~nm;.c~ion w!th th~ r:-publicalion of I his repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
3rd Quarter Chloroform 2019
1909320
9/13/2019
9/10-9/12/2019
Intact
None
Holding Time and Preservation Requirements: The analysis and preparation of all
samples were performed within the method holding times. All samples were properly
preserved.
Preparation and Analysis Requirements: The samples were analyzed following the
methods stated on the analytical reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD:
Method Blanks (MB): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Samples (LCS): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicates (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, indicating no
apparent matrix interferences.
Corrective Action: None required.
Report Date: 9/30/2019 Page 6 of 80
All analyses applicable 10 the CWA. SOWA. and RCRA aie perfom1ed in accordance lo NELAC protocols Pertinent sampling inrommlion is locnted on lhe allached COC Confidential Business lnformnlion: ll1is report is pro,•ided for lhe exclusi\ e use of 1he
~ddressee Pri,·ile~es o.f sub~sec:1~tcnl ~1;e or1he ~~ne of this .co,~pnny or an) ,~mber of its Slaff, or reproduclio~ ~f this repo~ in ~~eclion~ \\"ith the n~n:rtise~ent. p~~mloli~n ~r sale of?'!~ ~1od1~ct or p~ocess, ~r in 7onn~c~ion w!lh lh~ r~-publicntion of 1his 1eport
ANALYTICAL LAB0RATOR1£8
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
3rd Quarter Chloroform 2019
1909320
9/13/2019
9/10-9/12/2019
Intact
None
SW-846 8260D/5030C
Tetrahydrofuran
General Set Comments: Multiple target analytes were observed above reporting limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met, with CCV exceptions noted on the reports. All internal standard
recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPO, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicate (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, indicating no
apparent matrix interferences.
Surrogates: All surrogate recoveries were within established limits.
Corrective Action: None required.
Report Date: 9/30/2019 Page 7 of 80
All ,m::il) ses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance lo NELAC protocols. Pe11inent sampling infomialion is located on the auached COC Conlidentinl Business lnfornwtion: This report is provided for the exchlSi\e use of the
~ddressee, P1i, ile~es o_f subnseq~enl ~~e of lhe ~?1!1e of lhis .cm~pany or an~· ~~ber of iLs stnfT, or reproduclio~ ~f Lhis repo~ in ~on~1eclion .. \\ilh then~~ ertisemenl, p~omotio.n ~r sale of :U~~ ~1odL~CL or p~ocess, ~r in ~nn:_c~ion w~lh th~ r:_-publicalion of this repon
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909320
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Tanner Holliday
WC
LCS
Spike Ref.
Amount %REC
Lab Sample ID: LCS-R130409 Date Analyzed: 09/18/2019 1939h
Test Code: 300.0-W
Chloride 4.81 mg/L E300.0 0.0386 0.100 5.000 0 96.1
Lab Sample ID: LCS-Rl30447 Date Analyzed: 09/20/2019 1041h
Test Code: 300.0-W
Chloride 4.67 mg/L E300.0 0.0386 0.100 5.000 0 93.5
Lab Sample ID: LCS-R130509 Date Analyzed: 09/20/2019 1846h
Test Code: 300.0-W
Chloride 4.68 mg/L E300.0 0.0386 0.100 5.000 0 93.5
Lab Sample ID: LCS-Rl30180 Date Analyzed: 09/13/2019 1325h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.00 mg/L E353.2 0.00363 0.0100 1.000 0 100
Lab Sample ID: LCS-RI30181 Date Analyzed: 09/13/2019 1406h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.998 mg/L E353.2 0.00363 0.0100 1.000 0 99.8
Limits
90 -110
90 -110
90 -110
90 -110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 9/30/2019 Page 73 of80
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tl-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909320
Project: 3rd Quarter Chloroform 2019
Analyte Result
Lab Sample ID: MB-Rl30409 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-Rl30447 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-Rl30509 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-Rl30180 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-Rl30181 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. fa'X: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount
Units Method MDL Limit Spiked
09/18/2019 1922h
mg/L E300.0 0.0386 0.100
09/20/2019 1025h
mg/L E300,0 0.0386 0.100
09/20/2019 1829h
mg/L E300.0 0.0386 0.100
09/13/2019 1324h
mg/L E353.2 0.00363 0.0100
09/13/2019 1405h
mg/L E353.2 0.00363 0.0100
Tanner Holliday
WC
MBLK
Spike Ref.
Amount %REC Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 9/30/2019 Page 74 of80
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on the attached COC_ Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
3440 South 700 West
Salt Lake City, UT 84 l l 9 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
American West QC SUMMARY REPORT ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 1909320 Dept: WC
Project: 3rd Quarter Chloroform 2019 QC Type: MS
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: 1909320-00JAMS Date Analyzed: 09/19/2019 029h
Test Code: 300.0-W
Chloride 149 mg/L E300 0 0.772 2.00 100.0 49 100 90 -110
Lab Sample ID: 1909320-009AMS Date Analyzed: 09/19/2019 354h
Test Code: 300.0-W
Chloride 70.l mg/L E300.0 0.386 1.00 50.00 20.6 99.0 90 -110
Lab Sample ID: 1909320-012AMS Date Analyzed: 09/20/2019 1919h
Test Code: 300.0-W
Chloride 143 mg/L E300.0 0.772 2.00 100.0 47.9 95.3 90 -110
Lab Sample ID: 1909320-019AMS Date Analyzed: 09/20/2019 2223h
Test Code: 300.0-W
Chloride 130 mg/L E300.0 0.772 2.00 100.0 34.5 95.3 90-110
Lab Sample ID: 1909320-00JBMS Date Analyzed: 09/13/2019 1418h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 32.0 mg/L E353.2 0.0726 0.200 20.00 10.2 109 90 -110
Lab Sample ID: 1909320-004BMS Date Analyzed: 09/13/2019 1421h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) l l.5 mg/L E353.2 0.0363 0.100 10.00 l.84 97.0 90 -110
Lab Sample ID: 1909320-02IBMS Date Analyzed: 09/13/2019 1408h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) l l.4 mg/L E353.2 0.0363 0.100 10.00 0.904 105 90 -110
Lab Sample ID: 1909320-024BMS Date Analyzed: 09/13/2019 1429h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) l l.8 mg/L E353.2 0.0363 0.100 10.00 l.61 102 90 -110
Report Date: 9/30/2019 Page 75 of 80
analyses applicable to the CWA. SOWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the e;(clusive use of the addressee Privileges of subsequent use of tl-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
American West QC SUMMARY REPORT ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 1909320 Dept: WC
Project: 3rd Quarter Chloroform 2019 QC Type: MSD
Reporting Amount Spike Ref. RPDRef. RPO
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1909320-00JAMSD Date Analyzed: 09/19/2019 046h
Test Code: 300.0-W
Chloride 147 mg/L E300 0 0.772 2.00 100.0 49 98.1 90-110 149 1.60 20
Lab Sample ID: 1909320-009AMSD Date Analyzed: 09/19/2019 41 lh
Test Code: 300.0-W
Chloride 70.6 mg/L E300.0 0.386 1.00 50.00 20.6 99.9 90 -110 70.1 0.655 20
Lab Sample ID: 1909320-0llAMSD Date Analyzed: 09/20/2019 1936h
Test Code: 300.0-W
Chloride 142 mg/L E300.0 0.772 2.00 100.0 47.9 94.4 90 -110 143 0.607 20
Lab Sample ID: 1909320-019AMSD Date Analyzed: 09/20/2019 2239h
Test Code: 300.0-W
Chloride 130 mg/L E300.0 0.772 2.00 100.0 34.5 95.8 90 -110 130 0.386 20
Lab Sample ID: 1909320-00JBMSD Date Analyzed: 09/13/2019 1419h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite ( as N) 31.6 mg/L E353.2 0.0726 0.200 20.00 10.2 107 90 -110 32 1.29 10
Lab Sample ID: 1909320-004BMSD Date Analyzed: 09/13/2019 1422h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.7 mg/L E353 ,2 0.0363 0.100 10.00 1.84 98.3 90 -110 11.5 1.12 10
Lab Sample ID: 1909320-0llBMSD Date Analyzed: 09/13/2019 1415h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.2 mg/L E353,2 0.0363 0.100 10.00 0.904 103 90 -110 11.4 I.SO 10
Lab Sample ID: 1909320-024BMSD Date Analyzed: 09/13/2019 1443h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.6 mg/L E353.2 0.0363 0.100 10.00 1.61 99.9 90 -110 11.8 1.96 JO
Report Date: 9/30/2019 Page 76 of80
analyses applicable to the CW A. S DW A, and RCRA are perfomied in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business lnfom1ation: This report is provided for the exclusive use of the addressee, Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909320
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail : [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Tanner Holliday
MSVOA
LCS
Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-3 091319A Date Analyzed: 09/13/2019 1930h
Test Code: 8260D-W-DENlOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-2 091819A
Test Code: 8260D-W-DENlOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
20.2 µg/L SW8260D
20.2 µg/L SW8260D
12.6 µg/L SW8260D
21.2 µg/L SW8260D
52.3 µg/L SW8260D
49.3 µg/L SW8260D
51.6 µg/L SW8260D
49.8 µg/L SW8260D
Date Analyzed: 09/18/2019 l l36h
21.4 µg/L SW8260D
21.l µg/L SW8260D
17.7 µg/L SW8260D
21.8 µg/L SW8260D
50.8 µg/L SW8260D
50.6 µg/L SW8260D
50.5 µg/L SW8260D
51.l µg/L SW8260D
0.262 LOO 20.00 0 101
0.166 l.00 20.00 0 101
0.832 l.00 20.00 0 63.0
0.448 l.00 20.00 0 106
50.00 105
50.00 98.6
50.00 103
50.00 99.5
0.262 1.00 20.00 0 107
0.166 l.00 20.00 0 105
0.832 l.00 20.00 0 88.4
0.448 l.00 20.00 0 109
50.00 102
50.00 101
50.00 IOI
50.00 102
Limits
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 9/30/2019 Page 77 of 80
analyses applicable to the CWA. SOWA, and RCRA are perfonned in accordance to NE LAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: TI1is report is provided for the e:"'(clusive use of the addressee Privileges of subsequent use oft}
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909320
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fa": [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Tanner Holliday
MSVOA
MBLK
Spike Ref.
Amount %REC
Lab Sample ID: MB VOC-3 091319A Date Analyzed: 09/13/2019 1950h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-2 091819A
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< l.00
< 1.00
< 1.00
53.3
49.2
50.5
49.8
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
50.3
51.8
49.6
51.2
µg/L SW8260D 0.262 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.832 1.00
µg/L SW8260D 0.448 1.00
µg/L SW8260D 50.00 107
µg/L SW8260D 50.00 98.5
µg/L SW8260D 50.00 IOI
µg/L SW8260D 50.00 99.5
09/18/2019 1155h
µg/L SW8260D 0.262 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.832 1.00
µg/L SW8260D 0.448 1.00
µg/L SW8260D 50.00 101
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 99.2
µg/L SW8260D 50.00 102
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt % RPD Limit Qual
Report Date: 9/30/2019 Page 78 of80
analyses applicable to the C'WA. SOWA, and RCRA are perfom1ed in acco1dance to NELAC protocols Pertinent samphng information is located on the attached COC. Confidential Business Information: TI1is report is provided for the exclusive use of the addressee Privileges of subsequent use of tJ-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1909320
Project: 3rd Quarter Chloroform 2019
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 841 I 9
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
Lab Sample ID: I909320-002CMS Date Analyzed: 09/13/2019 2035h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: I909320-025CMS
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.6 µg/L SW8260D
19.5 µg/L SW8260D
13.4 µg/L SW8260D
20.4 µg/L SW8260D
51.4 µg/L SW8260D
47.8 µg/L SW8260D
51.0 µg/L SW8260D
49.6 µg/L SW8260D
Date Analyzed: 09/18/2019 1539h
412 µg/L SW8260D
952 µg/L SW8260D
324 µg/L SW8260D
417 µg/L SW8260D
999 µg/L SW8260D
1,020 µg/L SW8260D
998 µg/L SW8260D
1,010 µg/L SW8260D
0.262 1.00 20.00 0 98.2
0.166 1.00 20.00 0 97.3
0.832 1.00 20.00 0 66.8
0.448 1.00 20.00 0 102
50.00 103
50.00 95.7
50.00 102
50.00 99.3
5.24 20.0 400.0 0 103
3.32 20.0 400.0 549 101
16.6 20.0 400.0 0 81.0
8.96 20.0 400.0 0 104
1,000 99.9
1,000 102
1,000 99.8
1,000 101
Limits
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt % RPO Limit Qual
Report Date: 9/30/2019 Page 79 of 80
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tr
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
ANALYTICAL LABORATORIES _, C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 1909320 Dept: MSVOA
Project: 3rd Quarter Chloroform 2019 QC Type: MSD
-
Reporting Amount Spike Ref. RPO Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: 1909320-002CMSD Date Analyzed: 09/13/2019 2055h
Test Code: 8260D-W-DEN100
Carbon tetrachloride 21.0 µg/L SW8260D 0.262 1.00 20.00 0 105 77 -143 19.7 6.78 35
Chloroform 20.5 µg/L SW8260D 0.166 1.00 20.00 0 102 85 -124 19.5 5.11 35
Chloromethane 13.5 µg/L SW8260D 0.832 1.00 20.00 0 67.6 30 -149 13.4 1.19 35
Methylene chloride 21.2 µg/L SW8260D 0.448 1.00 20.00 0 106 65 -154 20.4 4.33 35
Surr: I ,2-Dichloroethane-d4 52.2 µg/L SW8260D 50.00 104 80 -136
Surr: 4-Bromofluorobenzene 48.6 µg/L SW8260D 50.00 97.3 85 -121
Surr: Dibromofluoromethane 51.0 µg/L SW8260D 50.00 102 78 -132
Surr: Toluene-d8 49.9 µg/L SW8260D 50.00 99.8 81 -123
Lab Sample ID: 1909320-025CMSD Date Analyzed: 09/18/2019 1559h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 423 µg/L SW8260D 5.24 20.0 400.0 0 106 77 -143 412 2.64 35
Chloroform 954 µg/L SW8260D 3.32 20.0 400.0 549 101 85 -124 952 0.210 35
Chloromethane 322 µg/L SW8260D 16.6 20.0 400.0 0 80.4 30 -149 324 0.681 35
Methylene chloride 434 µg/L SW8260D 8.96 20.0 400.0 0 108 65 -154 417 4.09 35
Surr: I ,2-Dichloroethane-d4 992 µg/L SW8260D 1,000 99.2 80 -136
Surr: 4-Bromofluorobenzene 1,020 µg/L SW8260D 1,000 102 85 -121
Surr: Dibromofluoromethane 988 µg/L SW8260D 1,000 98.8 78 -132
Surr: Toluene-d8 1,020 µg/L SW8260D 1,000 102 81 -123
Report Date: 9/30/2019 Page 80 of80
analyses applicable to the CWA. SDWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infom1ation is located on the attached COC Confidential Business [nfonnation: This report is provided for the e:xclusive use of the addressee Privileges of subsequent use of ti
ne of this company or any member of its staff, or reproduction of thls report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West Analytical Laboratories Rpt Emailed:
WORK ORDER Summary
Client:
Client ID:
Project:
Energy Fuels Resources, Inc.
ENE300
3rd Quarter Chloroform 2019
Contact: Garrin Palmer
QC Level: III
Work Order: 1909320
Due Date: 9/27/2019
WO Type: Project
Comments: QC 3 (no chromatograms). EDD-Denison. CC [e-mail]; Do not use "*R_" samples as MS/MSD.;
Sample ID Client Sample ID
1909320-001 A TW4-03R_09102019
1909320-0018
1909320-00lC
l 909320-002A TW4-03_09112019
1909320-0028
I 909320-002C
1909320-003A TW4-28_09112019
---
1909320-0038
1909320-003C
1909320-004A TW4-32_09112019
·--··
1909320-0048
l 909320-004C
··-
1909320-00SA TW4-12_09112019
1909320-0058
1909320-00SC
-Collected Date Received Date Test Code
9/10/2019 0627h 9/13/20191025h 300.0-W
_ 1 SELAnalytes: Cl
N02/N03-W-353.2
I SELAnal1tes: N03!v02N
8260D-W-DEN100
Matrix
Aqueous
7:est_Group: 8260£!:lf:DENIOO; _# ..5Jf Ana/ytes: 4 /# ofSurr: 4
9/11/2019 0715h 9/13/2019 1025h 300.0-W
I SEL Analytes: Cl
N02/N03-W-353.2
I SEL Analrtes: N03N02N
82600-W-DENIOO
Aqueous
Sel Storage
~ df-wc
--~ df-no2/no3
~ VOCFridge
~ df-wc
~ df -no2/no3
VOCFridge
Te~t qroup: 8260D:'!_-DENJOq;_~_of Analytes: f/# of Surr: 4
9/11/2019 0740h 9/13/2019 1025h 300.0-W
I SEL Ana/ytes: C~-
N02/N03-W-353.2
I SELAnalyt~s: N03N02N_ __
8260D-W-DEN100
Aqueous
______ Test Gro11p:_8~0D:.11:.:~E_NWO,~# of Ana/ytes: 4 I_# o.[_Surr: 4
9/11/2019 0748h 9/13/2019 1025h 300.0-W
___ ·-------. I SEL Ana/ytes: Cl __
N02/N03-W-353.2
I SEL Analyt:s·: No_3N02N.
82600-W-DENIOO
Aqueous
~ df-wc
~ df -no2/no3
~ VOCFridge
~ df-wc
~
~
df-no2/no3
VOCFridge
_Test Group: 82lj0D-W-DENJOqi_# of Analytes:_4 /# ofSurr: 4
9/11/2019 0755h 9/13/2019 1025h 300.0-W Aqueous ~ df-wc
----· -···-I SEL Analytes: _CL -------. ---
N02/N03-W-353.2 ~ df-no2/no3 __ .,. -···--·-----I SEL Ana/y~~s: NOJN02N _ ..
8260D-W-DEN100 ~ VOCFridge
·--·-----Test Group: 8260D-°i!':.P£;!:!JOO; # of An<;lytes: 4 /# ofSurr_:_ 4
UL
Denison
Page I of6
Z!/~~
3
3
3
3
3
Printed: 09/16/19 15:41 LABORATORY CHECK: %M I .I RT I CN 11 TAT L.I QC LJ LUO [J HOK ___ HOK __ _ HOK___ COG Emailed~----
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
1909320-006A TW4-13_09112019
1909320-006B
l 909320-006C
1909320-007 A TW4-36_09112019
1909320-007B
1909320-007C
1909320-00&A TW4-31_09112019
1909320-00SB
1909320-00BC
1909320-009A TW4-42_09112019
1909320-009B
1909320-009C
1909320-01 OA TW4-34_09112019
1909320-0lOB
1909320-0lOC
1909320-01 lA TW4-35_09112019
1909320-01 lB
1909320-01 lC
Work Order: 1909320
Due Date: 9/27/2019
Collected Date Received Date Test Code Matrix Sel Storage
9/11/2019 0804h 9/13/2019 1025h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENIOO; # of Analytes: 4 j# ofSurr: 4
9/11/2019 0812h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL AnaIJ1_tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
9/11/2019 0820h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
NOl/NOJ-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENI 00; # of Ana/),!_~: 4 I# of Surr: 4
9/11/2019 0833h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL AnalJlles: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENI 00; # of Analytes: 4 I# of Surr: 4
9/11/2019 0843h 9/13/2019 1025h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJOO; # of Analytes: 4 I#_ of Surr: 4
9/11/2019 0853h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEN100; # of Analytes: 4/# ofSurr: 4
Page2 of6
3
3
3
3
3
3
Printed: 09/13/19 12:26 LABORATORY CHECK: %M D RT O CN O TAT O QC D LUO D HOK ___ HOK __ _ HOK___ COC Emailed. ____ _
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
1909320-012A T\V4-23_09112019
19093.20-0 l2B
1909320-012C
1909320-0BA MW-32_09112019
1909320-013B
1909320-0 BC
1909320-014A T\V4-38_09112019
1909320-014B
1909320-014C
1909320-0lSA T\V4-14_09112019
1909320-0lSB
1909320-0lSC
1909320-016A T\V4-27_09112019
1909320-016B
1909320-016C
1909320-017 A T\V4-05_09112019
1909320-01 ?B
Work Order: 1909320
Due Date: 9/27/2019
Collected Date Received Date Test Code Matrix Sel Storage
9/11/2019 0902h 9/13/2019 1025h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Surr: 4
9/11/2019 1435h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Anal:;_tes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Surr: 4
9/11/2019 0929h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test GrouE_: 8260D-W-DENIOO; # of Analytes: 41 # ofSurr: 4
9/11/2019 0940h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Surr: 4
9/11/2019 0947h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W0DENIOO; # of Analytes: 41 # o/Surr: 4
9/11/2019 1000h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anolytes: N03N02N
Page3 of6
3
3
Printed: 09/13/19 12:26 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COG Emailed. ____ _
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
1909320-017C TW4-05_09I12019
1909320-0lSA TW4-06_09112019
1909320-018B
1909320-0lSC
1909320-019A TW4-30_09112019
1909320-019B
1909320-019C
1909320-020A TW4-18_09112019
1909320-020B
1909320--020C
1909320-021A TW 4-09 _ 09112019
1909320-021B
1909320-021 C
1909320-022A TW4-16_09122019
1909320-022B
1909320-022C
1909320-023A TW4-08_09122019
Work Order: 1909320
Due Date: 9/27/2019
Collected Date Received Date Test Code Matrix Sel Storage
9/11/2019 1000h 9/13/20191025h 8260D-W-DEN100 Aqueous VOCFridge
TestGrouJJ_: 8260D-W-DENIOO; # of Analytes: 4/# ofSu":.4
9/11/2019 1010h 9/13/2019 1025h 300.0-W Aqueous elf-we
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENI 00; # of Analytes: 4 I# of Su": 4
9/11/2019 1022h 9/13/2019 1025h 300.0-W Aqueous elf-we
I SEL AnalJ'(es: CL
N02/N03-W-353.2 elf -no2/no3
I SELAnalytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJ 00; # of_ Analytes: 4 I # of Surr: 4
9/ll/2019 1035h 9/13/2019 1025h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anal),tes: N03N02N
8260D-W-DENIOO VOCFridgc
Test Group_: 8260D-W-DENIOO; # of Ana[ytes: 4 I# ofSurr: 4
9/11/2019 1045h 9/13/2019 1025h 300.0-W Aqueous elf-we
I SEL Anal),tes: CL
N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DENIOO VOCFridge
Test Group_: 8260D-W-DENIOO; # of Analytes: 4 !# ofSurr: 4
9/12/2019 0708h 9/13/2019 1025h 300.0-W Aqueous elf-we
1 SELAna1l'_tes: CL
N02/N03-W-353.2 elf-no2/no3
1 SELAnalyJes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJ 00; # of Analytes: 4 ( # o[ Surr: 4
9/12/2019 0717h 9/13/2019 1025h 300.0-W Aqueous df -we
1 SEL Analytes: CL
Page 4 of6
3
3
3
3
3
3
Printed: 09/13/19 12:26 LABORATORY CHECK: %M O RT D CN O TAT O QC O LUO 0 HOK_~-HOK __ _ HOK___ COC Emailed ____ _
WORK ORDER Summary WorkOrder: 1909320 Page 5 of6
Client: Energy Fuels Resources, Inc. Due Date: 9/27/2019
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1909320-023B T\V4-08_09122019 9/12/2019 0717h 9/13/2019 1025h N02/N03-W-353.2 Aqueous df-no2/no3
1 SEL Analytes: N03N02N
1909320-023C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Ana{ytes: 4 I# of Surr: 4
1909320-024A T\V4-33_09122019 9/12/2019 0732h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Ana{ytes: CL
1909320-024B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1909320-024C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENJOO; # o[Aruzl)i_tes: 41 # ofSurr: 4
1909320-025A T\V4-29_09122019 9/12/2019 0742h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1909320-025B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1909320-025C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
1909320-026A T\V4-10_09122019 9/12/2019 0754h 9/13/2019 1025h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1909320-026B N02/N03-W-353.2 df-no2/no3
1 SEL Ana{ytes: N03N02N
1909320-026C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Ana{ytes: 4 I# of Su": 4
1909320-027A T\V4-07_09122019 9/12/2019 0808h 9/13/2019 1025h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1909320-027B N02/N03-W-353.2 elf-no2/no3
1 SEL Ana{ytes: N03N02N
1909320-027C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Ana{ytes: 4 I # of Su": 4
1909320-028A T\V4-26_09122019 9/12/2019 0817h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1909320-028B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1909320-028C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# ofSurr: 4
Printed: 09/13/19 12:26 LABORATORY CHECK: %M O RT O CN O TAT O QC D LUO 0 HOK~~ HOK~~ HOK___ COC Emailed ____ _
WORK ORDER Summary Work Order: 1909320 Page6 of6
Client: Energy Fuels Resources, Inc. Due Date: 9/27/2019
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1909320-029A TW4-16R_09112019 9/11/2019 111 Oh 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1909320-029B N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
1909320-029C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Su": 4
1909320-030A TW4-65_09112019 9/11/2019 0715h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
l 909320-030B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
l 909320-030C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Su": 4
1909320-03 lA TW4-70_09112019 9/11/2019 1000h 9/13/2019 1025h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1909320-03 lB N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
1909320-031C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 #_ of SW?': 4
1909320-032A TW4-75_09122019 9/12/2019 0717h 9/13/2019 1025h 300.0-W Aqueous df-wc
I SEL Analytes: CL
1909320-032B N02/N03-W-353.2 df-no2/no3
I SEL Analyte-s: N03N02N
1909320-032C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Su": 4
1909320-033A Trip Blank 9/10/2019 0627h 9/13/2019 1025h 8260D-W-DEN100 Aqueous VOCFridge 3
Test Group_: 8260D-W-DENJOO; # of Analytes: 41 # of SW?': 4
Printed: 09/13/19 12:26 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed ____ _
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City. UT 84115
Phone# (801) 26~6 Toll Free# [phone]
1
-··-··--
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Ganin Palmer
Phone#: [phone] CeU#:
gpalmer@,lmciri,fudi.c-mn; KWelnel@ene:rc,f11eli:com;
Email: dtmll(ii!enm)Dfuols..c-mn
Projecl Name: 3rd Quarter Chloroform 2019
Project#:
PO#:
Sampler Name: Tanner Holliday
TW4-03R_09102019
TW4-03_09112019
3 , TW4-28_09112019
TW4-32_09112019
, TW4-12_09112019
I TW4-13_09112019
' TW4-36_09112019
1 TW4-31_09112019
TW4-42_09112019
1 TW4-34_09112019 10
11 TW4-35_09112019
12 I TW4-23_09112019
13 I MW-32_09112019
Samele ID:
Rolinqu!Shad by'_J lJ.-o-t l j Sic-..tA'lJ\.trC.-. • . •. •
?rwf: Narno:, Tannor Hollldnv I
Rell""""'od by, --rt, ,k I J-. ls.n,iawn, r ... ,.,._ ./.,, .-•
PJrtNamo: --r-7-. ·~ -i~ ·ph,
/(ellnqu"-by: I " ,Sional\Jno
P,ttName:
~ellnqulshad by:
ISionattm,
IPr:i.otNeme:
Date
Sampled
9/10/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
9/11/2019
ate:
Q/12/2018
Time:
1130
0'1-/3-/'r
T.!m,' ;)_ s
Date:
mmo:
Dato:.
tnme:
I
Time
Sameled
627
715
740
748
755
804
812
820
833
843
853
902
1435
Rocolvm by:
Skt-..,. J
CHAIN OF CUSTODY
Al analysis will be a,nducled using NEI..AP acaedited methods and all data wiU be reported using AW/>L's standard analyte ll&ls and reporting
Umlls (PQL) unless specifically roquesled olhelwse on lhi• Chain of CUstody and/or attached docunemation.
QC Level: I Turn Around Time: Unless other arrangementr. have been made,
signed reports will be emailed by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For.
For Compllance With:
D NELAP
D RCRA
0 CWA
0 SOWA
0 ELAP/A2LA
a' 0 NLLAP
C'l' ci D Non-Compliance ~ Cl G' D other:
'2. ('J
f? .. 0 " ~ (') C) IC C: 0 C'l ]i ! 0 Cl ~ 6 IZ; lt) Known Hazards a, ...... • u i5. N :!:. 0 & 'o E 0 El g Ill .. rJ} IZ; Samele Comments
6 w X X X
5 w X X X
5 w X X X
5 w X X X
5 1w X X X
5 w X X X
5 w X X X
5 ~ X X X
6 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X -
L -LI!;;: M r _,;y Data: GI /1z/2.ol'I Special Instructions:
Prlnt Nama:--1h ll\ Lln e }.lr,/f :Time: \1-z,6
L 9a7 ;>2.J~
AWAL lab Sample Set#
Page 1 of 3 r~ .... I
Laboratory Use Only
Samples Were:
1 Shlppodo~
2 Ambiont"@?
3 Tam~ _.!:Q_ •c
4 Received Brok8fll1..oeldng
(lmproperty~ y N
~Preserved N
od at bench
y N
6 Received Within (!J"Tows N
lcoCTapeWe,,;
1 Praoenton OLtorP~
Y N NA
2 Unbroken on 01.tar Pa~
Y N NA
3 Present on Sample E)
Y N NA
4 Unbroken on Sample ~
Y N NI>;.
lscrepancies Between Sample
y N Labels and coc ~
Rscollled b'(! '? --Sktno!ure fl ( 117. rrJ ~e .;; t . ? /:;> /Cf
See the Analytical Scope of Work for Reporting Limits and VOC
PJln!N01T1<1: ~ lc1--.-1.lJJ ~I ._ I
analytc list.
Tlme: /OL5
Ree&lved by: I ...--, Date:
Si~nalura
nme:
PrlntName:
Received by: Date:
I.Slonahn
tnme:
Print Name:
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone # [phone] Toll Free# [phone]
1
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact Garrin Palmer
Phone#: [phone] Cell#:
[e-mail]; [e-mail];
Email: dtmlrftiltmer.&l'.!!!els.com
Project Name: 3rd Quarter Chloroform 2019
Project#:
PO#:
Sampler Name: Tanner HoWday
Date
Sample ID: Sampled
TW4-38_09112019 9/11/2019
TW4-14_09112019 9/11/2019
TW4-27_09112019 9/11/2019
TW4-05_09112019 9/11/2019
TW4-06_09112019 9/11/2019
TW4-30_09112019 9/11/2019
TW4-18_09112019 9/11/2019
TW4-09_09112019 9/11/2019
TW4-16_09122019 9/12/2019
TW4-08_09122019 9/12/2019
TW4-33_09122019 9/12/2019
TW4-29_09122019 9/12/2019
TW4-10_09122019 9/12/2019
Relinquished by: -A•M~ <fl.// D / Date:
Slaneture ~ 9/12/2010
nme:
'nntName: Tanner.HolUdev 1130
~ellnqutshed by: ___,.-,.,,_G'-i I.~ ~ f~/.l )"'! J.3-Jf"f Signabm,
PrlntName; t -L-·~ llob TI~: •..3.~ 0, L
Rellnquiehed by: / IOate:
lslanature
rnme:
Prtn!Name:
Relinquished by: !Date:
Slgoalure
rnme:
Print Na.me:
CHAIN OF CUSTODY
All analysis wlll be conducted uslng NELAP accredited methods and eD data wlll be reported using AWAL's standard analyte lists and reporting
limits {PQL) unless speclftcally requested otherwise on this Chain of Custody and/or attached documentation.
I QC Level: I Tum Around Time: Unless other arrangements have been made,
signed "'ports wtll be emailed by 5:00 pm on
3 Standard Hie day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For.
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAPIA2LA
o' D NLLAP ~ ci D Non-Compliance
1;j C D' D Other:
~ "1 I!! X ... C " 0 IO C ·c (') ]! ai 0 C C'l ::;; C ~ Known Hazards C Iii; lt) 0 " ..... ~ .. Time u C. N t.l & 0 E g u g Sampled .. Sample Comments .. "'
929 5 w X X X
940 5 w X X X
947 5 w X X X
1000 5 w X X X
1010 5 w X X X
1022 5 w X X X
1035 5 w X X X
1045 5 w X X X
708 5 w X X X
717 5 w X X X
732 5 w X X X
742 5 w X X X
754 5 w X X X
-odby.~f, 1,/r, _./(SJ
~ Date: q/ 1z./zo19 Special Instructions: ~1'18l\l"U .... '--"' ~
Prinl Name,-11,ll ;-,t!. !CJ+ II Time: 11~0
/ '="J0 1 3"Ld
AWAL Lab Sample Set#
Page 2 of 3 r~-, I
Laboratory Use Only
Samples Were:
1 Shippedo~
2 Arnblon!~ .
3 Tempomluro L.Q__ ·c
4 Received Broken/Leaking
(lmpn,porty &>olv y N
5 ~Preserved y N
at bench
y N
e Received Within &·~ N
COC Tape Was:
1 Present on O!AarP~
Y N NA
2 Unbroken on Outer Pa~
Y N NA
3 Present on Sample 0 y N
4 Unbroken on sample G'
Y N NA
Discrepancies Between Sampfe
Lebelsand CDC~ y N
-~ed. Y. ![·' 1.--. fr, // / D.we: 97; '3, j/ ~ See the Analytical Scope of Work for Reporting Limits and voe . analyte list.
2//A -iL v,,~~., frime:
Print Name: IO '2-')
Received by: I I Date:
Sk:mature
Time:
Print Name:
Received by: Date:
lsianature
mme:
Print Name:
-··-··
Address:
Contact:
Phone#:
Email:
Project Name:
Project#:
PO#:
Sampler Name:
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Toll Free# [phone]
6425 S. Hwy. 191
Blanding,UT 84511
Garrin Palmer
[phone] Cell#:
iii,aim.e%@)energyfue1s.com.; [e-mail];
4t:urk@enerQ!!els,com
3rd Quarter Chloroform 2019
Tanner Holliday
Date
$ample ID: Sampled
,
TW4-07 _09122019 9/12/2019
TW4-26_09122019 9/12/2019
TW4-16R_09112019 9/11/2019
TW4-65_09112019 9/11/2019
~ TW4-70_09112019 9/11/2019
~ TW4-75_09122019 9/12/2019
TRIP BLANK 9/10/2019
'
1
Roflr)q\Jilhodby; _-\,, .Jl_/// , Dal.a:
1-..a -,,~,,,, , / ~12/2019
/ Time;
Prirll Namo: T-Ho!ll<!ov 11!!1
Rel,nqwllllodby; -rn (H,,/,LL-/./o. { b-°'f-1>-A lslonal.m,
Priol-/ L --rl rr7~; ~s
[R~by: I IOate:
l"""""'ro
rnme:
""nl tla-
Ro/lnqlJlshcd by: lf)ate:
l!ainl)O!ura
liime: --
CHAIN OF CUSTODY
All analysis will be conducted u&lng NELAP acaedlted methods and all data wlll be reported using AWAL's standard analyle lists and reporting
llmils (POL) unless specifically rvquasted otherwise on this Chain of Custody and/or attached documentaHon.
I QC Level: I Tum Around Time: Unless other arrangements have been made,
signed reports will be emailed by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCJ!:L
Field Filtered For:
For Compliance With:
D NELAP
D RCRA
D CWA
D SOWA
D ELAP/A2LA
& D NUAP ~ c:i D Non-Compliance ~ 0 G' D other.
~ "l ; .. 0
C -~ (') 0 IO
' ! Ii 0 ~ 0 ~ Known Hazards 8 .. Lt) .... ~ ..
Time a. ('ii t) & 'l5 E 0 a g Sampled ., .. rn ,; Sample Comments
808 5 w X X X
817 5 w X X X
1110 5 w X X X
715 5 w X X X
1000 5 w X X X
717 5 w X X X
627 3 w X
Rocalvcd by: -f
"'""'"·-l -~ b r.,,;z,/,J.._.. Pete: llf /JZ/Z.0/(l Special Instructions:
Prl•I Namo: --rha..i~ ia.. l.Jo H Timo: 11~0
I '1 G 9 3 2-.(j
AWAI.. Lab Sample Set#
Page 3 of 3
I"""""'' I
Laboratory Use Only
tsamples Were: ·-tfj? 2 Ambient hlUod
3 Temperature ~ 'C
4 Rocolved Brokonn.eeklng
y N
{lmproporiy Seaic)
S~fffler;edN
et bench
y N
6 -Received Within
DTimos N
COCTapeWe:s:
1 Present on Outer P~
Y N NA
2 Unbroken on Outer~
Y N NA
I
3 Present on Sample r;;> y N
4 Unbroken on Sample G:)
Y N NA
Oiscrepenctes8-1Sample
label• and coc w
y N
R-odby-~ f ,. Data: '7 ~2.-h S,
See the Analytical Scope of Work for Reporting Limits and voe 1............. ,_ I r~ 1. L analyte list. ?:/~,.,. ,=t.. \I ./.7 ITirne: '
'"rinlNam.o· , , . /oz...,
R8C81Ved by: / / JOate:
L~1nnetl68
ITlme:
Print Nome:
Received by: Date:
I.signature
!Time:
PrtnlName:
Analysis
Ammonia
COD
Cvanide
Metals
N02&
N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s le Set Ext
Preservative ·-DOI -CO?... -003 -OOI -001:S -WG,
pH<2H2S04
pH <2H2S04
pH>12NaOH
pH<2HN03
pH<2H2S04 ~ ~ ~ ~ ~ ~
t>H<2HCL
pH<2H2S04
pH>9NaOH,
Zn Acetate
pH<2H2S04
t>H<2H2S04
Pour a small amount of sample in the sample lid
Pour sample from lid gently over wide range pH paper
Do Not dip the pH paper in the sample bottle or lid
-009-
w-6
dvH
~008 l-011
~ ~
-0/0 -0(1
~ ~
I)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+ ..
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference .
-Oil-
~
Lab Set ID: l qcq;w
pH Lot#: lQOpS
r~. l of1.
-/)13 1--{)Jc..f I}/~ -0/b -Of?-
~ ~ 'AW ~ W,x1
-018
~
Analysis
Ammonia
COD
Cvanide
Metals
N02&
N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
:samole :set Extens10n amt r>H
Preservative -o,q -rrw -en, -07,.'Z -oi-; -OV,/
0H<2H2S04
pH <2 H2S04
pH>l2NaOH
0H<2HN03
pH<2H2S04 ~ .~ ~ ~ ~ ~
pH<2HCL
0H<2H2S04
pH>9NaOH,
Zn Acetate
1>H<2H2S04
1>H<2H2S04
Pour a small amount of sample in the sample lid
Pour sample from lid gently over wide range pH paper
Do Not dip the pH paper in the sample bottle or lid
-(Jlc; -OULJ -oz.._~
~ ~ ~
-075? -02,4
~ ~
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
A
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference .
-030
I~
Lab Set ID:
pH Lot#:
\qog310
bOJ>S
fV 2 or 2
.,, tR-'1 JI ?/1'"1
-031 -032.. nJ55 ,
~ ~
Tab I
Quality Assurance and Data Validation Tables
1-1 · Field QA/QC Evaluation
1 x Casing 2x Casing Dissolved
Location Volume Volume Pumped Volume Volume Check Conductivity RPD Temperature RPD Redox RPD Turbidity RPD Oxygen RPD RPD pH
NC 6.86 MW-04 NA Continuously Pumped well --1790 NC 17.89 NC 271 NC 1.5 NC 31.5 NC
NA Continuously Pumped well --3277 NC 18.49 NC 399 NC 10.9 NC 12.9 NC NC 6.62
0.06 6.36 6.35 MW-32 32.74 67.27 65.48 okay 3466 3464 0.16 15.34 15.30 0.26 280 278 0.72 36.9 37.0 0.27 O O O
NC 6.87 TW4-01 NA Continuously Pumped well --2201 NC 19.16 NC 329 NC 5.6 NC 85.2 NC
NC 6.74 TW4-02 NA Continuously Pumped well --3590 NC 22.11 NC 403 NC O NC 81 .5 NC
'1• -~ •• , .. -J ~Kl',,AB r~ -1Dt:a:a '11 :-Pum-·~ .. ·:·:• -_ 1tilfli' :,1.'-_ 1.695.-.. 'Oilb-I J5~12 ~l~7 ::f5.:l!7°_ .... -..JII~.-· ... >~ •• •-:NM .;-,'~ 11:· • .1 ... '\,!-~ 1,1.~t-:"~""-1..-:::-0 "_1.1N&:: _.;-·,e2.•-:-~ .. .---,~ I',' O!A7 ~ ~.a:as:~ ::'. 6,a.J.,.._
NC 6.79 TW4-04 NA Continuously Pumped well -· 2198 NC 17.75 NC 348 NC 2.1 NC 111 .5 NC
0.50 6.89 6.89
0.06. ~ '.6:ie· 'I ; 6~f9(-
0:U.7. -;cr-98 I ·, 1.p2
TW4-05 34.08 88.00 68.16 okay 1398 1391 0.00 15.49 15.49 0.00 330 340 2.99 6.2. 6.1 1.63 54.0 52 .0 3.77
~ ... -~·'"~ -,rn._...,, -~."-.,.· .29:98' ~UfflliHKl lJQl. ·~·36114~';..__., '1 36121 .... • 11 .0:UD ... 15~~· ~ 15.25, ,--l1i2t');.::·..:.i. :..NM~~~, -.. ~,,,.~., 1~""2 ,_, 1'·'.-":.NG:" -~.1"'\..-1.·--~·;,
~T •-~ '·" ·, 1:::>L:z 5'., ~ .S1'.52! ON-.•' ~J.--,~-~430. ~0:57' •'f31801 -.l~ , V.1::.18'1 ~, ..... ,_NM!~-~ -,,·iur!' ·-1~·~ 1,,.-.~ 'Nri,·-.1 -a :. • ...,.,.,,.,._._-:_:.:,
0.04 6.65 6.65 TW4-08 27.09 66.00 54.18 okay 4631 4629 0.00 15.12 15.12 0.00 130 134 3.03 1.9 1.9 0.00 O O O
TW4-09 34.23 88.00 68.46 okay 2317 2317 0.00 6.75 6.70 0.74 15.09 15.07 0.13 127 130 2.33 25.0 25.0 0.00 O O O
'•:fW4\lCL" ~.30.03 " ~ .A1:,2!r .•. ,.---.--;ao~06.,__,;,-P.umoei:t'()ry·_ 1,_ 255.6 ...:-1 _2570 0(55 _ ~a..sai. 1 6.60 .,1, 0.30 .. i:. 13.80 , i 1Gl85 . 01315 · .~ .NIii~ -..... -· !'NQi:. ::..., !.~1 .... -. r:N<l.. ·. ' \!'i ll~' ... .-,_~
TW4-11 NA Continuously Pumped well --3463 NC 6.73 NC 20.82 NC 307 NC O NC 89.1 NC
;· ~12 .... ·, _32~22 ,, J -• • ~~--s4:q ; 11· P.umNM N -:: _ t 3081 JI 1-·:..1SQ8;, 1 O;llo .. , , ,2a 1 7.22. .0.14._ 14:61l'-·.,, .1~M;;"= ~ ~1 •• j,....·.-,-.• --NM·.,;:: =-T ~-Js u• .~-.. -.'..."U:.NMr-:" -.;. -"'1 1,..~: 1 ··--~
TW§-13 .... "32~-. --_ · ~~ -_ ....-, lS!'ii'.Bfl --eumr-rv-_ 19821' L' 19_3J -· .r .~o· · .2-1• · 71-20:. ,_ "1>!1.~ ...• :]B' .. ~. 1 .._ :t!,tst,r ~ .uu ::1. 1 .~ .,. _ ~-;:. ·-, ~m :,.,: ":._-~ •• a.: _ i' I•~ u .!:' -~ -i
·-TW+rl~~ ,~ ·11~4t .· ~ ~ ~ ~-·~ .~tHr'" --~ ~ _,z-..s2 .. ~, PutnDel 1' tY " !,,I! ... ~~mr I I'. 4872 ,. O:OIJr ..:1 .2'4 -! ."6.23•. I 11 o.16 ~,s.sor ,-1 "1 5135:" ' ·~ r·._ ~---·"M = -. rN ,--": ~,-q:Nr ~~ ~. ; :. -~''r; ,.,_921 ~ .i', ' ~ ~
TW4-16 49.48 121.00 98.96 3380 3360 0.59 6.75 6.72 0.45 14.92 14.92 0.00 210 208 0.96 11.2 11.5 2.64 0 0 0 okay
okay 1594 1563 1.96 6.63 6.60 0.45 15.46 15.46 0.00 180 183 1.65 13.7 13.5 1.47 18.0 18.5 2.74
y Pumped well 2745 NC 6.77 NC 18.90 NC 227 NC 10.2 NC 33.3 NC --
y Pumped well 3934 NC 6.35 NC 18. 76 NC 400 NC 1.5 NC 45.0 NC --
y Pumped well 3124 NC 6.65 NC 18.25 NC 393 NC O NC 47.4 NC --
y Pumped well 5161 NC 7.14 NC 18.10 NC 248 NC 5.1 NC 104.3 NC --
TW4-23 28.00 88.00 56 3307 3288 0.58 6.89 6.83 0.87 14.45 14.50 0.35 200 204 1.98 20.5 21.1 2.88 91.0 92.0 1.09 okay
TW4-24 NA Continuously Pumped well --8219 NC 6.71 NC 17.65 NC 337 NC O NC 29.2 NC
TW 4-25 NA Continuously Pumped well --2256 NC 6.91 NC 17 .60 NC 368 NC 1.8 NC 31. 7 NC
.. m ~2ar •. 110:az-:.; r_. __ _._:trt~ ..... _" ~-;.: ~-• .£'~~-· -~ 11>, '" 1;....._M cg;·.··· IL 4A61 ,. o ... 09 . s:wr · ~--a.BBL . ...,, .:0.14.. ,.1'4 .. 111-'", 'i 1~rrs:---\0. .J 11 .-=.:...-i: N~-L .-~dL...__··--~~ L '·-· .. -1 · '~-
iC: I"!"'• ....... j L' 'Tlfl_4'--: 1" ~--.-=trti;WEI_ ~ -~--i2e::-"' :, ... ·pymlfe Dr ~_r~I• . j 6581".-.... -4e54--I· .• 0.0 I 6.5~~·· J 6.53. -::.-. ,-.o.ts . 1 ~u &.1r1~ 1,1 -~115.19 -:;10. ~ -. ~ J #r'-=~·· .,..,, ; 1-Ou ·-=::.., --.-C ... I ~= --... ;-,
,_ r~,:-. IF' I•, '4Qt2a1 ' -··--: -·-=_-C -• .5Sl -.·-Fri moe ur -1'::: .. 1 4851_~.1•• -1429 1·· . .'.0~:ii :-."Y.1'11:l I II 7112'.'"' :0:-2.8 1-~·1~---,11V.41-6-OJi ~ __ -,_., -~J-··t, ... c-:.'.-._ --• .:;;;.~ ~'".. .LJ•
11_ '<f' 9 ~ ~ ·1-1 ;63°._ J ""· .. ,m-=_~_=,:--f ~ _ , ,. -...... l~U~ 1,:., i7R"o& -.• .'.-~, D~ ,ll I• 1 -'l!OO J' • 6~~8 ,. 0,29.' \\ 1W.07.-, , , -1 10· .1 -111 :-:-c;., .--, NM' --i;: -N r~.: :.r:= 1 -·~..,_-., _. -It ~ _..
·-..:: _12125!:. -l -!Mitl '~ ~:Sf-"1 ,~ i-oum,....-.,u,,.,,--4':ltfil . 1:u-~1 a.:...... : •:o 'J. -,i ~-! L 5.59}1 • 0.1 8 ,· 1S:03 ., ''·· .IU 1 .:::...o:: 1: I j;:" r~ NM:.: -_, ~-: FN ·-~, j r . .-.N ··. --,, -..;a .
I~ v~ Ll ~ ... zu.1.a: . ~-:· '= .. -~Jlv n.:'",. r _:; = . & .... g __ , . "'Ulll . .:387,f' •J Ii 38 3 . r.o _6;1M . ;, J -6i~ 0:00 .•. f4.98 .. : • ·1 • n,,· ' Q!I .. F• ,r ·r :N11111 • "."j',;-,_I --IN • ;:::.:. .. NI I,".'~~. L ·-1 -..... :10:.:--~..::~~ll!:!·s.:.~
0 TW4-32 39.05 88.00 78.1 okay 6095 6099 0.07 4.33 4.32 0.23 14.85 14.85 0.00 331 330 0.30 16.0 16.0 0.00 O 0
i,y.4-33-11 -.a:_tffj_ ' , ·:: -s.oo; .,_ -1-:-··_ _ --~--~ ~ ~-eilmDB1 llli) 7-'ii. ,~ ....3.956i~ ,l 39t0, I~ 0.1.0" . ,_ -,7,30 . ,. ' 7.28 1 .;. 0:27 -, .c 14.8,1} ':, .• 1 'f4.82::-, O;g7._ 'Ii,,_., _,-.NIVH 1 1 • 1 .N(b J l'"' .... H ....... N• r ........ 11!'""=~~F'.~,-,,,~.z;,;··:=s_ia"~--::;.::"'!":'"11'illl"'.;:-.o:;:!I
,VV.!!r.:~; ~-1 .its-~:" ·---16~58 ~~..: .0 ~"2:z.~,·: --,-· li)j ,!-1, __ 3272L __ 1 _32~lJ-·_ ,. 0.12 ..... 1:,c._e. ~ ..:"· -6~ -~oz :• f.ol~94 I,: ·~(98!, '°'2 ·-, --~'NM.1 ' _..:::i;: _NG----~ -I NMr., ,· · ... l -· .... -~ 1·~~
1, ~4-31> .•. ,ns ,' -! T.33_-& •. -~-~-_., ... , ~-·PJ!!!J)E 1,1:2 , 4lr.lR lw 4U'l:U r ~o..'1 0::"1:c 6~~ _.1 6.~>i,.',1'-"',Q.1iC8"c-.~ 114.~; :-.-1J;l00:-.. 11 1lo,1 I I-· .ruvi•,,. ... ,f' e. • ....... .,;JiE -~ ~ :.C! ~1i 0 ~ ... ...1 """·
..... 4-.:M>. •1, i!:Z!UU ['·--. ;:5;:I~ -. ~ _c .55.2 ,._ . n!!!Jit 1•1,1 ,,, _,_ ~7.:,·· ',._ 227.5 -u.w 1, -~-~ . ' 6.95 0.00 I -14.99 -,,... 15.00" I •• O!o ~ I \ NM r.. ... .. ... "',:---Rir.'.',, __ . .,... '-~ -= I;' -·
TW4-37 NA Continuously Pumped well --3512 NC 6.64 NC 17.60 NC 339 NC O NC 82.6 NC
TW4-38 36.65 77.00 73.3 okay 1644 1718 4.40 6.83 6.87 0.58 14.70 14.70 0.00 243 248 2.04 22.9 22.5 1.76 64.0 63.5 0.78
TW4-39 NA Continuously Pumped well --2189 NC 6.71 NC 17.79 NC 312 NC 4.9 NC 91.7 NC
TW4-40 NA Continuously Pumped well --3667 NC 6.35 NC 17.00 NC 345 NC 14.9 NC 83.1 NC
TW4-41 NA Continuously Pumped well --2581 NC 6.95 NC 19.20 NC 341 NC 15.0 NC 109.1 NC
MW-04, MW-26, TW4-01, TW4-02, TW4-04, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41 are continually pumped wells.
rFW~-@"§';~l'iw.~-015,;,;ili:XIXl~-Qi7,:.(liM'W4:;'i1lb'\ ;Ji,IJ,\/,:,i~.~f21'.irlW14!-1l3\..~~14, l!WBh26t:i!iWj ffii'f'iW~:Ml .. ~~1illWM:-3Q,,c·lJ:IJ,IJ,ij,.3}1.,:r'liWl:la~aa;flWV,<t~3~TW~35 1iW4-36, JW4-42 were pl.imoed'd6i~and samored after reeoverv.i
NM= Not Measured. The OAP does not require the measurement of redox potential or turbidity in wells that were purged to dryness.
RPO = Relative Percent Difference
The OAP states that turbidity should be less than 5 Nephelometric Turbidity Units ("NTU") prior to sampling unless the well is characterized by water that has a higher turbidity. The OAP does not require that turbidity measurements be less than 5 NTU prior to
sampling. As such, the noted observations regarding turbidity measurements less than 5 NTU are included for information purposes only.
~ ... --._I tl'Vi~ -~ -,J
..
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Anal¥sis Date (Days) Time (Davs) Check
Trip Blank Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
Trip Blank Chloroform 9/4/2019 9/6/2019 2 14 OK
Trip Blank Chloromethane 9/4/2019 9/6/2019 2 14 OK
Trip Blank Methylene chloride 9/4/2019 9/6/2019 2 14 OK
Trip Blank Carbon tetrachloride 9/10/2019 9/18/2019 8 14 OK
Trip Blank Chloroform 9/I0/2019 9/18/2019 8 14 OK
Trip Blank Chloromethane 9/10/2019 9/18/2019 8 14 OK
Trip Blank Methylene chloride 9/10/2019 9/18/2019 8 14 OK
MW-04 Chloride 9/4/2019 9/16/2019 12 28 OK
MW-04 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
MW-04 Chloroform 9/4/2019 9/6/2019 2 14 OK
MW-04 Chloromethane 9/4/2019 9/6/2019 2 14 OK
MW-04 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
MW-04 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
MW-26 Chloride 9/4/2019 9/16/2019 12 28 OK
MW-26 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
MW-26 Chloroform 9/4/2019 9/6/2019 2 14 OK
MW-26 Chloromethane 9/4/2019 9/6/2019 2 14 OK
MW-26 Methvlene chloride 9/4/2019 9/6/2019 2 14 OK
MW-26 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
MW-32 Chloride 9/11/2019 9/20/2019 9 28 OK
MW-32 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
MW-32 Chloroform 9/11/2019 9/14/2019 3 14 OK
MW-32 Chloromethane 9/11/2019 9/14/2019 3 14 OK
MW-32 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
MW-32 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-01 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-01 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-01 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-0l Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-0J Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-0l Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-02 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-02 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-02 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-02 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-02 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-02 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-03 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-03 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-03 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-03 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-03 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-03 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-03R Chloride 9/10/2019 9/19/2019 9 28 OK
TW4-03R Carbon tetrachloride 9/I0/2019 9/13/2019 3 14 OK
TW4-03R Chloroform 9/10/2019 9/13/2019 3 14 OK
TW4-03R Chloromethane 9/10/2019 9/13/2019 3 14 OK
TW4-03R Methylene chloride 9/10/2019 9/13/2019 3 14 OK
TW4-03R Nitrate/Nitrite (as N) 9/10/2019 9/13/2019 3 28 OK
TW4-04 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-04 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-04 Chloroform 9/4/2019 9/6/2019 2 14 OK
I-2: Holding Time Evaluation
'jj ,\.
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-04 Chlorornethane 9/4/2019 9/6/2019 2 14 OK
TW4-04 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-04 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-05 Chloride 9/l l/2019 9/20/2019 9 28 OK
TW4-05 Carbon tetrachloride 9/l l/2019 9/14/2019 3 14 OK
TW4-05 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-05 Chloromethane 9/l l/2019 9/14/2019 3 14 OK
TW4-05 Methylene chloride 9/l 1/2019 9/l4/20I9 3 14 OK
TW4-05 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-06 Chloride 9/l l/2019 9/20/2019 9 28 OK
TW4-06 Carbon tetrachloride 9/l 1/2019 9/l4/2019 3 14 OK
TW4-06 Chloroform 9/l 1/2019 9/14/2019 3 14 OK
TW4-06 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-06 Methylene chloride 9/l l/2019 9/14/2019 3 14 OK
TW4-06 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-07 Chloride 9/12/2019 9/2l/2019 9 28 OK
TW4-07 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-07 Chloroform 9/12/2019 9/l8/2019 6 14 OK
TW4-07 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-07 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-07 Nitrate/Nitrite (as N) 9/l2/2019 9/13/2019 1 28 OK
TW4-08 Chloride 9/l2/2019 9/2l/2019 9 28 OK
TW4-08 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-08 Chloroform 9/l2/2019 9/18/2019 6 14 OK
TW4-08 Chloromethane 9/l2/2019 9/18/2019 6 14 OK
TW4-08 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-08 Nitrate/Nitrite (as N) 9/12/2019 9/l3/2019 1 28 OK
TW4-09 Chloride 9/l 1/2019 9/20/2019 9 28 OK
TW4-09 Carbon tetrachloride 9/l 1/2019 9/18/2019 7 14 OK
TW4-09 Chloroform 9/l 1/2019 9/18/2019 7 14 OK
TW4-09 Chloromethane 9/l 1/2019 9/l8/20I9 7 14 OK
TW4-09 Methylene chloride 9/l l/2019 9/l8/2019 7 14 OK
TW4-09 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-10 Chloride 9/l2/2019 9/21/2019 9 28 OK
TW4-10 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-10 Chloroform 9/l2/2019 9/18/2019 6 14 OK
TW4-10 Chloromethane 9/l2/2019 9/18/2019 6 14 OK
TW4-10 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-10 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
TW4-11 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-l l Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-ll Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-ll Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-11 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-11 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-12 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-12 Carbon tetrachloride 9/l l/2019 9/13/2019 2 14 OK
TW4-12 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-12 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-12 Methylene chloride 9/l l/2019 9/13/2019 2 14 OK
TW4-12 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-13 Chloride 9/1 l/2019 9/19/2019 8 28 OK
TW4-13 Carbon tetrachloride 9/l 1/2019 9/13/2019 2 14 OK
I-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-13 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-13 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-13 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-13 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-14 Chloride 9/11/2019 9/20/2019 9 28 OK
TW4-14 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-14 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-14 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-14 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-14 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-16 Chloride 9/12/2019 9/21/2019 9 28 OK
TW4-16 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-16 Chloroform 9/12/2019 9/18/2019 6 14 OK
TW4-16 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-16 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-16 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
TW4-16R Chloride 9/11/2019 9/21/2019 10 28 OK
TW4-16R Carbon tetrachloride 9/11/2019 9/18/2019 7 14 OK
TW4-16R Chloroform 9/11/2019 9/18/2019 7 14 OK
TW4-16R Chloromethane 9/11/2019 9/18/2019 7 14 OK
TW4-16R Methylene chloride 9/11/2019 9/18/2019 7 14 OK
TW4-16R Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-18 Chloride 9/11/2019 9/20/2019 9 28 OK
TW4-18 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-18 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-18 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-18 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-18 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-19 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-19 Carbon tetrachloride 9/4/2019 9/7/2019 3 14 OK
TW4-19 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-19 Chloromethane 9/4/2019 9/7/2019 3 14 OK
TW4-19 Methylene chloride 9/4/2019 9/7/2019 3 14 OK
TW4-19 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-20 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-20 Carbon tetrachloride 9/4/2019 9/7/2019 3 14 OK
TW4-20 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-20 Chloromethane 9/4/2019 9/7/2019 3 14 OK
TW4-20 Methylene chloride 9/4/2019 9/7/2019 3 14 OK
TW4-20 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-21 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-21 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-21 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-21 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-21 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-21 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-22 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-22 Carbon tetrachloride 9/4/2019 9/7/2019 3 14 OK
TW4-22 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-22 Chloromethane 9/4/2019 9/7/2019 3 14 OK
TW4-22 Methylene chloride 9/4/2019 9/7/2019 3 14 OK
TW4-22 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-23 Chloride 9/11/2019 9/20/2019 9 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-23 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-23 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-23 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-23 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-23 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-24 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-24 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-24 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-24 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-24 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-24 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-25 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-25 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-25 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-25 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-25 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-25 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-26 Chloride 9/12/2019 9/21/2019 9 28 OK
TW4-26 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-26 Chloroform 9/12/2019 9/18/2019 6 14 OK
TW4-26 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-26 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-26 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
TW4-27 Chloride 9/11/2019 9/20/2019 9 28 OK
TW4-27 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-27 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-27 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-27 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-27 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-28 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-28 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-28 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-28 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-28 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-28 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-29 Chloride 9/12/2019 9/21/2019 9 28 OK
TW4-29 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-29 Chloroform 9/12/2019 9/18/2019 6 14 OK
TW4-29 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-29 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-29 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
TW4-30 Chloride 9/11/2019 9/20/2019 9 28 OK
TW4-30 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-30 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-30 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-30 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-30 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-31 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-31 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-31 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-31 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-31 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-31 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
I-2: Holding Time Evaluation
~
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-32 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-32 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-32 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-32 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-32 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-32 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-33 Chloride 9/12/2019 9/21/2019 9 28 OK
TW4-33 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-33 Chloroform 9/12/2019 9/18/2019 6 14 OK
TW4-33 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-33 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-33 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
TW4-34 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-34 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-34 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-34 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-34 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-34 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-35 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-35 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-35 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-35 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-35 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-35 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-36 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-36 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-36 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-36 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-36 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-36 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-37 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-37 Carbon tetrachloride 9/4/2019 9/7/2019 3 14 OK
TW4-37 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-37 Chloromethane 9/4/2019 9/7/2019 3 14 OK
TW4-37 Methylene chloride 9/4/2019 9/7/2019 3 14 OK
TW4-37 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-38 Chloride 9/11/2019 9/20/2019 9 28 OK
TW4-38 Carbon tetrachloride 9/11/2019 9/14/2019 3 14 OK
TW4-38 Chloroform 9/11/2019 9/14/2019 3 14 OK
TW4-38 Chloromethane 9/11/2019 9/14/2019 3 14 OK
TW4-38 Methylene chloride 9/11/2019 9/14/2019 3 14 OK
TW4-38 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-39 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-39 Carbon tetrachloride 9/4/2019 9/7/2019 3 14 OK
TW4-39 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-39 Chloromethane 9/4/2019 9/7/2019 3 14 OK
TW4-39 Methylene chloride 9/4/2019 9/7/2019 3 14 OK
TW4-39 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-40 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-40 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-40 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-40 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-40 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Davs) Check
TW4-40 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-41 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-41 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-41 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-41 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-41 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-41 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-42 Chloride 9/11/2019 9/19/2019 8 28 OK
TW4-42 Carbon tetrachloride 9/11/2019 9/13/2019 2 14 OK
TW4-42 Chloroform 9/11/2019 9/13/2019 2 14 OK
TW4-42 Chloromethane 9/11/2019 9/13/2019 2 14 OK
TW4-42 Methylene chloride 9/11/2019 9/13/2019 2 14 OK
TW4-42 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-60 Chloride 9/4/2019 9/16/2019 12 28 OK
TW4-60 Carbon tetrachloride 9/4/2019 9/6/2019 2 14 OK
TW4-60 Chloroform 9/4/2019 9/6/2019 2 14 OK
TW4-60 Chloromethane 9/4/2019 9/6/2019 2 14 OK
TW4-60 Methylene chloride 9/4/2019 9/6/2019 2 14 OK
TW4-60 Nitrate/Nitrite (as N) 9/4/2019 9/9/2019 5 28 OK
TW4-65 Chloride 9/11/2019 9/21/2019 10 28 OK
TW4-65 Carbon tetrachloride 9/11/2019 9/18/2019 7 14 OK
TW4-65 Chloroform 9/11/2019 9/18/2019 7 14 OK
TW4-65 Chloromethane 9/11/2019 9/18/2019 7 14 OK
TW4-65 Methylene chloride 9/11/2019 9/18/2019 7 14 OK
TW4-65 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-70 Chloride 9/11/2019 9/21/2019 10 28 OK
TW4-70 Carbon tetrachloride 9/11/2019 9/18/2019 7 14 OK
TW4-70 Chloroform 9/11/2019 9/18/2019 7 14 OK
TW4-70 Chloromethane 9/11/2019 9/18/2019 7 14 OK
TW4-70 Methylene chloride 9/11/2019 9/18/2019 7 14 OK
TW4-70 Nitrate/Nitrite (as N) 9/11/2019 9/13/2019 2 28 OK
TW4-75 Chloride 9/12/2019 9/21/2019 9 28 OK
TW4-75 Carbon tetrachloride 9/12/2019 9/18/2019 6 14 OK
TW4-75 Chloroform 9/12/2019 9/18/2019 6 14 OK
TW4-75 Chloromethane 9/12/2019 9/18/2019 6 14 OK
TW4-75 Methylene chloride 9/12/2019 9/18/2019 6 14 OK
TW4-75 Nitrate/Nitrite (as N) 9/12/2019 9/13/2019 1 28 OK
Table I-3 Recipt Temperature Check
Sample Batch Wells in Batch Temperature
1909134 MW-04, TW4-0l, TW4-02, TW4-04, TW4-ll, MW-26, TW4-19, TW4-20, TW4-21, TW4-22, o.rc TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41, TW4-60, Trip Blank
TW4-03, TW4-03R, TW4-05, TW4-06, TW4-07, TW4-08, TW4-09, TW4-IO, TW4-12, TW4-13,
1909320 TW4-14, TW4-16, TW4-16R, MW-32, TW4-18, TW4-23, TW4-26, TW4-27, TW4-28, TW4-29, 1.o·c TW4-30, TW4-31, TW4-32, TW4-33. TW4-34, TW4-35, TW4-36, TW4-38, TW4-42, TW4-65,
TW4-70, TW4-75, Trip Blank
I-4 Analytical Method Check
Parameter Method Method Used by Lab
SW8260B,
Carbon Tetrachloride SW8260C or SW8260D
SW8260D
A4500-Cl B or
Chloride A4500-Cl E or E300.0
E300.0
SW8260B,
Chloroform SW8260C or SW8260D
SW8260D
SW8260B,
Chloromethane SW8260C or SW8260D
SW8260D
SW8260B ,
Methylene chloride SW8260C or SW8260D
SW8260D
Nitrogen E353.1 or E353.2 E353.2
All parameters were analyzed using the reporting method specificied in the QAP
I R L .. Ch k -5 eportmg 1m1t ec
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
Trip Blank Carbon tetrachloride 1 ug/L u I 1 OK
Trip Blank Chloroform 1 ug/L u I 1 OK
Trip Blank Chloromethane 1 ug/L u I 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
Trip Blank Carbon tetrachloride I ug/L u 1 1 OK
Trip Blank Chloroform I ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u I 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
MW-04 Chloride I mg/L IO I OK
MW-04 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-04 Chloroform 20 ug/L 20 1 OK
MW-04 Chloromethane 1 ug/L u I I OK
MW-04 Methylene chloride 1 ug/L u 1 1 OK
MW-04 Nitrate/Nitrite (as N) 0. I mg/L IO 0.1 OK
MW-26 Chloride 1 mg/L IO 1 OK
MW-26 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-26 Chloroform 20 ug/L 20 1 OK
MW-26 Chloromethane 1 ug/L u 1 1 OK
MW-26 Methylene chloride 1 ug/L I I OK
MW-26 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
MW-32 Chloride 1 mg/L 10 1 OK
MW-32 Carbon tetrachloride 1 ug/L u l 1 OK
MW-32 Chloroform 1 ug/L u I 1 OK
MW-32 Chloromethane 1 ug/L u 1 1 OK
MW-32 Methylene chloride 1 UJ.J;/L u 1 1 OK
MW-32 Nitrate/Nitrite (as N) 0.1 mg/L u I 0.1 OK
TW4-0I Chloride 1 mg/L 10 1 OK
TW4-01 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-01 Chloroform 20 ug/L 20 1 OK
TW4-01 Chloromethane 1 ug/L u I 1 OK
TW4-01 Methylene chloride 1 ug/L u 1 1 OK
TW4-01 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-02 Chloride 1 mg/L IO 1 OK
TW4-02 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-02 Chloroform 20 ug/L 20 1 OK
TW4-02 Chloromethane 1 ug/L u 1 1 OK
TW4-02 Methylene chloride 1 ug/L u 1 1 OK
TW4-02 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-03 Chloride 1 mg/L IO 1 OK
TW4-03 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-03 Chloroform 1 ug/L u 1 1 OK
TW4-03 Chloromethane 1 ug/L u 1 1 OK
TW4-03 Methylene chloride 1 ug/L u 1 1 OK
TW4-03 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-03R Chloride 1 mg/L u 1 1 OK
TW4-03R Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-03R Chloroform 1 ug/L 1 1 OK
TW4-03R Chloromethane 1 ug/L u 1 1 OK
TW4-03R Methylene chloride 1 ug/L u 1 1 OK
TW4-03R Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-04 Chloride 1 mg/L 10 1 OK
TW4-04 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-04 Chloroform 20 ug/L 20 1 OK
TW4-04 Chloromethane 1 ug/L u I 1 OK
I 5 R L .. C k -eporung 1m1t hec
Lab Required
II Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-04 Methylene chloride 1 ug/L u 1 1 OK
TW4-04 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-05 Chloride 1 mg/L 10 1 OK
TW4-05 Carbon tetrachloride 1 ug/L u l 1 OK
TW4-05 Chloroform 1 ug/L l l OK
TW4-05 Chloromethane 1 ug/L u 1 l OK
TW4-05 Methylene chloride l ug/L u 1 1 OK
TW4-05 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-06 Chloride 1 mg/L 10 1 OK
TW4-06 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-06 Chloroform l ug/L 1 1 OK
TW4-06 Chloromethane I ug/L u l 1 OK
TW4-06 MeLhylene chloride 1 ug/L u l 1 OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-07 Chloride 1 mg/L 10 1 OK
TW4-07 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-07 Chloroform 20 ug/L 20 1 OK
TW4-07 Chloromethane 1 ug/L u 1 I OK
TW4-07 Methylene chloride 1 ug/L u 1 1 OK
TW4-07 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-08 Chloride 1 mg/L 10 1 OK
TW4-08 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-08 Chloroform 1 ug/L 1 1 OK
TW4-08 Chloromethane 1 ug/L u 1 1 OK
TW4-08 Methylene chloride 1 ug/L u 1 1 OK
TW4-08 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-09 Chloride 1 mg/L 10 I OK
TW4-09 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-09 Chloroform 1 ug/L 1 1 OK
TW4-09 Chloromethane 1 ug/L u I 1 OK
TW4-09 Methylene chloride 1 ug/L u 1 1 OK
TW4-09 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-10 Chloride 1 mg/L 10 1 OK
TW4-10 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-10 Chloroform 20 ug/L 20 1 OK
TW4-10 Chloromethane 1 ug/L u 1 1 OK
TW4-10 Methylene chloride 1 ug/L u 1 1 OK
TW4-10 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-11 Chloride 1 mg/L 10 1 OK
TW4-11 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-l l Chloroform 20 ug/L 20 1 OK
TW4-11 Chloromethane 1 ug/L u 1 1 OK
TW4-11 Methylene chloride 1 ug/L u 1 1 OK
TW4-ll Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-I2 Chloride 1 mg/L 10 1 OK
TW4-12 Carbon tetrachloride 1 u_g/L u 1 1 OK
TW4-12 Chloroform 1 ug/L u 1 1 OK
TW4-12 Chloromethane 1 ug/L u 1 1 OK
TW4-12 Methylene chloride 1 ug/L u 1 I OK
TW4-12 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-13 Chloride 1 mg/L 10 1 OK
TW4-13 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-I3 Chloroform l ug/L u 1 1 OK
TW4-13 Chloromethane 1 ug/L u 1 1 OK
-eporung Jilli ec I 5 R L' 't Ch k
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-13 Methylene chloride 1 ug/L u 1 1 OK
TW4-13 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-14 Chloride 1 mg/L 10 1 OK
TW4-14 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-14 Chloroform 1 ug/L 1 1 OK
TW4-14 Chloromethane 1 ug/L u 1 1 OK
TW4-14 Methylene chloride 1 ug/L u 1 1 OK
TW4-14 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-16 Chloride 1 mg/L 10 1 OK
TW4-16 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-16 Chloroform 1 ug/L 1 1 OK
TW4-16 Chloromethane 1 ug/L u 1 1 OK
TW4-16 Methylene chloride 1 ug/L u 1 1 OK
TW4-16 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-16R Chloride 1 mg/L u 1 1 OK
TW4-16R Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-16R Chloroform 1 ug/L 1 1 OK
TW4-16R Chloromethane 1 ug/L u 1 1 OK
TW4-16R Methylene chloride 1 ug/L u 1 1 OK
TW4-16R Nitrate/Nitrite (as N) 0.1 mg/L u I 0.1 OK
TW4-18 Chloride 1 mg/L 10 1 OK
TW4-18 Carbon tetrachloride 1 ug/L u I 1 OK
TW4-18 Chloroform 1 ug/L 1 1 OK
TW4-18 Chloromethane 1 ug/L u 1 1 OK
TW4-18 Methylene chloride 1 ug/L u 1 1 OK
TW4-18 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-19 Chloride 5 mg/L 50 1 OK
TW4-19 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-19 Chloroform 100 ug/L 100 1 OK
TW4-19 Ch loromethane I ug/L u 1 1 OK
TW4-19 Methylene chloride l ug/L u 1 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-20 Chloride 5 mg/L 50 1 OK
TW4-20 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-20 Chloroform 100 ug/L 100 1 OK
TW4-20 Chloromethane 1 ug/L u 1 1 OK
TW4-20 Methylene chloride 1 ug/L u 1 1 OK
TW4-20 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-21 Chloride 5 mg/L 50 1 OK
TW4-21 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-21 Chloroform 20 ug/L 20 1 OK
TW4-21 Chloromethane 1 ug/L u 1 1 OK
TW4-21 Methylene chloride 1 ug/L u 1 1 OK
TW4-21 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-22 Chloride 10 mg/L 100 1 OK
TW4-22 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-22 Chloroform 100 ug/L 100 1 OK
TW4-22 Chloromethane 1 ug/L u 1 1 OK
TW4-22 Methylene chloride 1 ug/L u 1 1 OK
TW4-22 Nitrate/Nitrite (as N) 1 mg/L 100 0.1 OK
TW4-23 Chloride 1 mg/L 10 1 OK
TW4-23 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-23 Chloroform 1 ug/L u 1 1 OK
TW4-23 Chloromethane 1 ug/L u 1 1 OK
1-5 R eportmg Limit Check
Lab Required
Reporting Dilution Reporting
Location Analvte Limit Units Qualifier Factor Limit RLCheck
TW4-23 Methylene chloride 1 ug/L u 1 1 OK
TW4-23 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-24 Chloride 20 mg/L 200 1 OK
TW4-24 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-24 Chloroform 1 ug/L 1 1 OK
TW4-24 Chloromethane 1 ug/L u 1 1 OK
TW4-24 Methylene chloride I ug/L u 1 1 OK
TW4-24 Nitrate/Nitrite (as N) 1 mg/L 100 0.1 OK
TW4-25 Chloride 2 mg/L 20 1 OK
TW4-25 Carbon tetrachloride l ug/L u 1 1 OK
TW4-25 Chloroform 1 ug/L u 1 1 OK
TW4-25 Chloromethane 1 ug/L u 1 1 OK
TW4-25 Methylene chloride 1 ug/L u 1 1 OK
TW4-25 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-26 Chloride 1 mg/L 10 1 OK
TW4-26 Carbon tetrachloride 1 ug/L u 1 l OK
TW4-26 Chloroform 20 ug/L 20 1 OK
TW4-26 Chloromethane 1 ug/L u 1 1 OK
TW4-26 Methylene chloride 1 ug/L u 1 1 OK
TW4-26 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-27 Chloride 1 mg/L 10 1 OK
TW4-27 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-27 Chloroform 1 ug/L 1 1 OK
TW4-27 Chloromethane 1 ug/L u 1 1 OK
TW4-27 Methylene chloride 1 ug/L u 1 1 OK
TW4-27 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-28 Chloride 1 mg/L 10 1 OK
TW4-28 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-28 Chloroform 1 ug/L u 1 1 OK
TW4-28 Chloromethane 1 ug/L u 1 1 OK
TW4-28 Methylene chloride 1 ug/L u 1 1 OK
TW4-28 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-29 Chloride I mg/L 10 1 OK
TW4-29 Carbon tetrachloride I ug/L u I 1 OK
TW4-29 Chloroform 20 ug/L 20 1 OK
TW4-29 Chloromethane 1 ug/L u 1 1 OK
TW4-29 Methylene chloride 1 ug/L u 1 l OK
TW4-29 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-30 Chloride I mg/L 10 1 OK
TW4-30 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-30 Chloroform I ug/L 1 I OK
TW4-30 Chloromethane 1 ug/L u I 1 OK
TW4-30 Methylene chloride 1 ug/L u 1 1 OK
TW4-30 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-31 Chloride 1 mg/L 10 1 OK
TW4-31 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-31 Chloroform 1 ug/L u 1 1 OK
TW4-31 Chloromethane 1 ug/L u 1 1 OK
TW4-31 Methylene chloride I ug/L u 1 1 OK
TW4-31 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-32 Chloride 1 mg/L 10 1 OK
TW4-32 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-32 Chloroform 1 ug/L u 1 1 OK
TW4-32 Chloromethane 1 ug/L u 1 1 OK
-eporung 1m1t ec I 5 R L .. Ch k
II Lab Required
II' Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-32 Methylene chloride 1 ug/L u 1 1 OK
TW4-32 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-33 Chloride 1 mg/L IO 1 OK
TW4-33 Carbon tetrachloride I ug/L u 1 1 OK
TW4-33 Chloroform 1 ug/L 1 1 OK
TW4-33 Chloromethane 1 ug/L u 1 1 OK
TW4-33 Methylene chloride 1 ug/L u 1 1 OK
TW4-33 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-34 Chloride 1 mg/L IO 1 OK
TW4-34 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-34 Chlorofonn 1 ug/L u 1 1 OK
TW4-34 Chloromethane I ug/L u 1 1 OK
TW4-34 Methylene chloride 1 ug/L u 1 1 OK
TW4-34 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-35 Chloride 1 mg/L IO 1 OK
TW4-35 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-35 Chloroform 1 ug/L u 1 1 OK
TW4-35 Chloromethane 1 ug/L u 1 1 OK
TW4-35 Methylene chloride 1 ug/L u 1 1 OK
TW4-35 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-36 Chloride 1 mg/L IO 1 OK
TW4-36 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-36 Chloroform 1 ug/L u 1 1 OK
TW4-36 Chloromethane 1 ug/L u 1 1 OK
TW4-36 Methylene chloride 1 ug/L u 1 1 OK
TW4-36 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-37 Chloride 5 mg/L 50 1 OK
TW4-37 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-37 Chloroform 100 ug/L 100 1 OK
TW4-37 Ch loromethane 1 ug/L 1 1 OK
TW4-37 Methylene chloride 1 ug/L u 1 1 OK
TW4-37 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-38 Chloride 1 mg/L IO 1 OK
TW4-38 Carbon tetrachloride I ug/L u 1 1 OK
TW4-38 Chloroform 1 ug/L u 1 1 OK
TW4-38 Chloromethane 1 ug/L u 1 1 OK
TW4-38 Methylene chloride 1 ug/L u 1 1 OK
TW4-38 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-39 Chloride 2 mg/L 20 1 OK
TW4-39 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-39 Chloroform 100 ug/L 100 1 OK
TW4-39 Chloromethane 1 ug/L u 1 1 OK
TW4-39 Methylene chloride 1 ug/L u 1 1 OK
TW4-39 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-40 Chloride 1 mg/L IO 1 OK
TW4-40 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-40 Chloroform 20 ug/L 20 1 OK
TW4-40 Chloromethane 1 ug/L u 1 1 OK
TW4-40 Methylene chloride 1 ug/L u 1 1 OK
TW4-40 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-41 Chloride 1 mg/L IO 1 OK
TW4-41 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-41 Chloroform 20 ug/L 20 1 OK
TW4-4I Chloromethane 1 ug/L u 1 1 OK
I 5 R L .. Ch k -eportrnP.. 1m1t ec
Lab Required
Reporting Dilution Reporting
Location Analvte Limit Units Qualifier Factor Limit RLCheck
TW4-41 Methylene chloride 1 ug/L u 1 1 OK
TW4-41 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-42 Chloride 1 mg/L 10 1 OK
TW4-42 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-42 Chloroform 1 ug/L u 1 1 OK
TW4-42 Chloromethane 1 ug/L u 1 1 OK
TW4-42 Methylene chloride 1 ug/L u 1 1 OK
TW4-42 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-60 Chloride 1 mg/L u 1 1 OK
TW4-60 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-60 Chloroform 1 ug/L u 1 1 OK
TW4-60 Chloromethane 1 ug/L u 1 1 OK
TW4-60 Methylene chloride 1 ug/L u 1 1 OK
TW4-60 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-65 Chloride 1 m_g/L 10 1 OK
TW4-65 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-65 Chloroform 1 ug/L u 1 1 OK
TW4-65 Chloromethane 1 ug/L u 1 1 OK
TW4-65 Methylene chloride 1 ug/L u 1 1 OK
TW4-65 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-70 Chloride 1 mg/L 10 1 OK
TW4-70 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-70 Chloroform 1 ug/L 1 1 OK
TW4-70 Chloromethane 1 ug/L u 1 l OK
TW4-70 Methylene chloride 1 ug/L u 1 1 OK
TW4-70 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-75 Chloride 1 mg/L 10 1 OK
TW4-75 Carbon tetrachloride I ug/L u 1 1 OK
TW4-75 Chloroform 1 ug/L 1 1 OK
TW4-75 Chloromethane I ug/L u 1 1 OK
TW4-75 Methylene chloride 1 ug/L u 1 1 OK
TW4-75 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
I-6 Trip Blank Evaluation
Lab Report Constituent Result
Carbon tetrachloride ND ug/L
1909134 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
1909320 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
I-7 QA/QC Evaluation for Sample Duplicates
Constituent
Chloride (m_g/L)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
Constituent
Chloride (mg/L)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
Constituent
Chloride (mg/I...)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
RPD = Relative Percent Difference
ND = The analyte was not detected
TW4-03
26.0
5.12
ND
ND
ND
ND
TW4-05
46.1
7.02
ND
14.6
ND
ND
TW4-08,
52.0
0.999
ND
75.4
ND
ND
TW4-65 ' %RPD
22.10 16.2
5.76 11.8
ND NC
ND NC
ND NC
ND NC
TW4-70 %RPO
45.8 0.7
6.89 1.9
ND NC
13.6 7.1
ND NC
ND NC
TW4-15 %RPO
52.5 1.0
1.03 3.1
ND NC
75.6 0.3
ND NC
ND NC
I-8 QC Control Limits for Analysis and Blanks
Method Blank Detections
All Method Blank (MB) for the quarter were nondetect.
Matrix Spike % Recovery Comparison
All Matrix Spike % Recoveries for the quarter were within acceptance limits.
Laboratory Control Sample
All LCS recoveries for the quarter were within acceptance limits.
Surrogate % Recovery
All Surrogate recoveries were within acceptance limits for the quarter.
1-9 Rinsate Evaluation
~.
R.illl\'&ate $ample Pa~11meter (ugfq I ne\>li llliJS Yi'-fullli .@'ffl;lI)lte~t
TW4-03R Chloroform 17.6 NA
TW4-16R Chloroform 19.4 TW4-09 (66.0 ugfL)
NA = This rinsate sample was collected prior to the first use of the pump.
TabJ
Kriged Current Quarter Chloroform Isoconcentration Map
EXPLANATION
NS = not sampled; ND = not detected;
ND 20 = not detected during second quarter
........... 70
TW4-42
¢ND
TW4-40
.. 380
MW-38
-<,ND
MW-32
e ND
TW4-7
0 801
TWN-1
~NS
PIEZ-1
~NS
kriged chlorofonn isocon and label
temporary perched monitoring well
installed April, 201 9 showing
concentration in µg/L
temporary perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well showing
concentration in µg/L
temporary perched monitoring well
showing concentration in µg/L
temporary perched nitrate monitoring
well (not sampled)
perched piezometer (not sampled)
NOTES: MW-4, MW-26, TW4-1 , TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21 , TW4-37, TW4-39, TW4-40 and TW4-41 are
chloroform pumping wells; TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells
HYDRO
GEO
KRIGED 3rd QUARTER, 2019 CHLOROFORM (µg/L)
WHITE MESA SITE
CHEM, INC. APPROVED DATE REFERENCE
H:/718000/nov19/chlorofonn/Uchl0919.srf
FIGURE
J-1
NS= not sampled; ND= not detected;
ND 20 = not detected during second quarter
....._ 70
TW4-42
¢ND
TW4-40
... 380
MW-32
e ND
TW4-7
0 801
PIEZ-2
Q NS
kriged chloroform isocon and label
temporary perched monitoring well
installed April, 2019 showing
concentration in µg/L
temporary perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well showing
concentration (µg/L)
temporary perched monitoring well
showing concentration (µg/L)
perched piezometer (not sampled)
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are
chloroform pumping wells; TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells
HYDRO
GEO
CHEM,INC.
KRIGED 3rd QUARTER, 2019 CHLOROFORM (µg/L)
WHITE MESA SITE
APPROVED DATE
(detail map)
REFERENCE H:1718000/nov19/
chloroform/Uchl0919det.srf
FIGURE
J-2
NS= not sampled; ND= not detected;
ND 20 = not detected during second quarter
'-70
1W4-42
¢ND
TW4-40
.. 380
MW-32
e ND
1W4-7
0 801
PIEZ-2
'-' NS
kriged chlorofonn isocon and label
temporary perched monitoring well
installed April, 2019 showing
concentration in µg/L
temporary perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well showing
concentration (µg/L)
temporary perched monitoring well
showing concentration (µg/L)
perched piezometer (not sampled)
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are
chloroform pumping wells; TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells
HYDRO
GEO
CHEM,INC.
3rd QUARTER, 2019 CHLOROFORM
GREATER THAN OR EQUAL TO 70 µg/L GRID
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/nov19/
chloroform/Uchl0919GE70.srf
FIGURE
J-3
TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
1•1 '·Jitw. Chloroform C mm Clwremeth 4\&tb Nitrate Chloride ['/ ~ Te ac Ide 11 (ug/1) (ligt) Chleride (ugll) (mwl) (ing:ll~ I _I (uir/1,)
28-Sep-99 6200
28-Sep-99 5820
28-Sep-99 6020
15-Mar-OO 5520
15-Mar-OO 5430
2-Sep-00 5420 9.63
30-Nov-OO 6470 9.37
29-Mar-Ol 4360 8.77
22-Jun-01 6300 9.02
20-Sep-01 5300 9.45
8-Nov-01 5200 8
26-Mar-02 4700 8.19
22-May-02 4300 8.21
12-Sep-02 6000 8.45 .
24-Nov-02 2500 8.1
28-Mar-03 2000 8.3
30-Apr-03 3300 NA
30-May-03 3400 8.2
23-Jun-03 4300 8.2
30-Jul-03 3600 8.1
29-Aug-03 4100 8.4
12-Sep-03 3500 8.5
15-0ct-03 3800 8.1
8-Nov-03 3800 8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 3300 6.71
17-Nov-04 4300 7.5
16-Mar-05 2900 6.3
25-May-05 3170 NA NA NA 7.1 NA
31-Aug-05 3500 <10 <10 <10 7.0 NA
1-Dec-05 3000 <50 <50 <50 7.0 NA
9-Mar-06 3100 <50 <50 50 6 49
14-Jun-06 3000 <50 <50 50 6 49
20-Jul-06 2820 <50 <50 <50 1.2 48
9-Nov-06 2830 2.1 1.4 <1 6.4 50
28-Feb-07 2300 1.6 <l <1 6.3 47
27-Jun-07 2000 1.8 <l <1 7 45
15-Aug-07 2600 1.9 <l <1 6.2 47
10-0ct-07 2300 1.7 <1 <1 6.2 45
26-Mar-08 2400 1.7 <1 <1 5.8 42
25-Jun-08 2500 1.6 <1 <1 6.09 42
10-Sep-08 1800 1.8 <1 <1 6.36 35
15-0ct-08 2100 1.7 <1 <1 5.86 45
4-Mar-09 2200 1.5 <l <1 5.7 37
23-Jun-09 1800 1.3 <1 <1 5.2 34
14-Sep-09 2000 1.4 <l <l 5.3 43
Chlorofo.rm Carbon Chloromethane ylene ltrate Chloride MW-4 Tetraehbide (ug/J) {llf!M) (II~ Chloride {agffl; (ing/1) (mg/I)
14-Dec-09 1800 1.6 ND ND 5.8 44
17-Feb-10 1600 1.2 ND ND 4 45
14-Jun-10 2100 1.2 ND ND 5.1 41
16-Aug-10 1900 1.5 ND ND 4.8 38
11-0ct-10 1500 1.4 ND ND 4.9 41
23-Feb-11 1700 1.5 ND ND 4.6 40
l-Jun-11 1700 1.4 ND ND 4.9 35
17-Aug-11 1700 1.1 ND ND 4.9 41
16-Nov-11 1600 1.3 ND ND 5.1 40
23-Jan-12 1500 1 ND ND 4.8 41
6-Jun-12 1400 1.2 ND ND 4.9 39
4-Sep-12 1500 1.5 ND ND 5 41
4-0ct-12 1300 1 ND ND 4.8 42
11-Feb-13 1670 1.49 ND ND 4.78 37.8
5-Jun-13 1490 1.31 ND ND 4.22 44
3-Sep-13 1520 1.13 ND ND 4.89 41.4
29-0ct-13 1410 5.58 ND ND 5.25 40.1
27-Jan-14 1390 4.15 ND ND 4.7 38.5
19-May-14 1390 5.21 ND ND 4.08 39.9
24-Aug-14 1490 ND 7.6 ND 3.7 41
21-0ct-14 1440 ND ND ND 5.07 41.5
9-Mar-15 1400 1.26 ND ND 5.75 40.7
8-Jun-15 1300 ND ND ND 2.53 43 .1
31-Aug-15 1290 ND ND ND 4.79 44.3
19-0ct-15 1200 ND ND ND 4.43 40.8
9-Mar-16 1240 ND ND ND 5.15 42.2
23-May-16 1580 1.44 ND ND 4.54 43.7
25-Jul-16 1430 ND ND ND 4.95 42.5
12-0ct-16 1470 1.24 ND ND 4.88 44.8
8-Mar-17 1450 1.22 ND ND 4.99 43.3
13-Jun-17 1430 1.15 ND ND 4.88 44.0
26-Jul-17 1400 1.15 ND ND 4.59 43.8
ll-Oct-17 1320 ND ND ND 5.25 43.8
12-Mar-18 1320 1.07 ND ND 4.47 46.2
8-Jun-18 1240 ND ND ND 4.64 43.5
22-Aug-18 1300 ND ND ND 4.55 48.5
28-Nov-18 1330 ND ND ND 4.44 43.1
8-Mar-19 1190 ND ND ND 5.05 41.5
5-Jun-19 1300 ND ND ND 5.16 40.6
4-Sep-19 1180 ND ND ND 4.69 41.9
Sep-99
Mar-00
Sep-00
Mar-01
Sep-01
Mar-02
Sep-02
Mar-03
Sep-03
Mar-04
Sep-04
Mar-05
Sep-05
Mar-06
Sep-06
Mar-07
Sep-07
Mar-08
Sep-08
Mar-09
Sep-09
Mar-10
Sep-10
Mar-11
Sep-11
Mar-12
Sep-12
Mar-13
Sep-13
Mar-14
Sep-14
Mar-15
Sep-15
Mar-16
Sep-16
Mar-17
Sep-17
Mar-18
Sep-18
Mar-19
......
0 0 0 0
l\:l 0 0 0
(ug/L)
(.,.)
0 0 0
""" 0 0 0
01 0 0 0
0)
0 0 0
-..J 0 0 0
~ ~ ~ I ()
:::r
0 a -0
3
~
C:
CD (J)
Chlorof Ol'lll Cabon Cblenm MetbJI e Nitrate atloride TW4 .. 1 , Tewaclllioride ne €hlor,i II (ug/1) (ug/1) (mg/I) (mg/I) 11 (ugt,I) I (ugAI} ,j
28-Jun-99 1700 7.2
10-Nov-99 5.8
15-Mar-OO 1100
10-Apr-OO 1490
6-Jun-00 1530
2-Sep-00 2320 5.58
30-Nov-00 3440 7.79
29-Mar-01 2340 7.15
22-Jun-01 6000 8.81
20-Sep-01 12.8
8-Nov-01 3200 12.4
26-Mar-02 3200 13.1
22-May-02 2800 12.7
12-Sep-02 3300 12.8
24-Nov-02 3500 13.6
28-Mar-03 3000 12.4
23-Jun-03 3600 12.5
12-Sep-03 2700 12.5
8-Nov-03 3400 11.8
29-Mar-04 3200 11
22-Jun-04 3100 8.78
17-Sep-04 2800 10.8
17-Nov-04 3000 11.1
16-Mar-05 2700 9.1
25-May-05 3080 NA NA NA 10.6 NA
31-Aug-05 2900 <10 <10 <10 9.8 NA
1-Dec-05 2400 <50 <50 <50 9.7 NA
9-Mar-06 2700 <50 <50 <50 9.4 49
14-Jun-06 2200 <50 <50 <50 9.8 48
20-Jul-06 2840 <50 <50 <50 9.7 51
8-Nov-06 2260 1.4 <1 <1 9.4 47
28-Feb-07 1900 1.2 <1 <1 8.9 47
27-Jun-07 1900 1.4 <1 <1 9 45
15-Aug-07 2300 1.3 <1 <1 8.4 43
10-0ct-07 2000 1.3 <1 <l 7.8 43
26-Mar-08 2000 1.3 <1 <1 7.6 39
25-Jun-08 1900 1.1 <I <1 8.68 39
10-Sep-08 1700 1.3 <1 <l 8.15 35
15-0ct-08 1700 1.3 <1 <1 9.3 41
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Te.trachloride (ug/1) C.hloride (mg/I) (mg/I) (µg/1) (Ug/1) I
ll-Mar-09 1700 1.1 <1 <1 7.5 37
24-Jun-09 1500 1 <l <1 6.9 37
15-Sep-09 1700 <l <1 <l 7.3 36
29-Dec-09 1400 <l <1 <l 6.8 41
3-Mar-10 1300 <1 <l <l 7.1 35
15-Jun-10 1600 1.2 <1 <l 6.8 40
24-Aug-10 1500 <1 <1 <1 6.8 35
14-0ct-10 1500 <l <l <1 6.6 40
24-Feb-l l 1300 ND ND ND 6.6 41
l-Jun-11 1200 ND ND ND 7 35
18-Aug-ll 1300 ND ND ND 6.8 36
29-Nov-ll 1300 ND ND ND 6.6 37
19-Jan-12 1300 ND ND ND 6.8 38
14-Jun-12 1000 ND ND ND 7.1 42
13-Sep-12 1000 ND ND ND 5 39
4-0ct-12 1100 ND ND ND 6.5 40
13-Feb-13 1320 3.66 ND ND 6.99 37.6
19-Jun-13 1100 ND ND ND 6.87 39.1
12-Sep-13 1150 ND ND ND 7.12 37.6
14-Nov-13 1280 ND ND ND 7.08 36.5
5-Feb-14 1090 5.47 ND ND 7.74 38.9
23-May-14 1020 4.77 ND ND 6.93 37.4
27-Aug-14 845 ND 1.4 ND 4.8 38
29-0ct-14 1140 ND ND ND 6.31 38.7
9-Mar-15 1130 ND ND ND 7.06 38.3
8-Jun-15 1260 ND ND ND 6.07 40.3
31-Aug-15 1060 ND ND ND 6.28 45.9
19-0ct-15 1040 ND ND ND 1.55 38.5
9-Mar-16 974 ND ND ND 0.148 41.7
23-May-16 1140 ND ND ND 0.138 44.4
25-Jul-16 1160 ND ND ND 5.49 44.7
13-0ct-16 1330 ND ND ND 0.746 44.2
8-Mar-17 519 ND ND ND 4.44 41.5
13-Jun-17 977 ND ND ND 5.74 41.8
26-Jul-17 958 ND ND ND 5.04 42.8
ll-Oct-17 556 ND ND ND 5.78 38.5
12-Mar-18 70.4 ND ND ND 4.84 45 .8
8-Jun-18 942 ND ND ND 4.38 42.0
22-Aug-18 1010 ND ND ND 4.30 47.3
Chloroform ca~bon Chloromethane Methylene Nitrate Ohloride TW4-1 (ugll) Tet,,ra~hloride· (ug/1) Chloride (mg/I) (mg/I~ (ug/1) I (ug/1)
22-0ct-18 752 ND ND ND 4.57 43.2
8-Mar-19 87.2 ND ND ND 4.51 40.9
5-Jun-19 1040 ND ND ND 1.43 44.8
4-Sep-19 894 ND ND ND 1.65 46.0
0
.....
0 0 0
I\)
0 0 0
(ug/L)
w 0 0 0
.i,,.. 0 0 0
0, 0 0 0
0) 0 0 0
-...J 0 0 0
28-Jun-99 +----+-===-e-+----t----1----t-----t------1
28-Dec-99
28-Jun-OO
28-Dec-OO
2B-Jun-01 ~ I I a--=: I • I I t
28-Dec-01
28-Jun-02
28-Dec-02
28-Jun-03
28-Dec-03
28-Jun-04
28-Dec-04
28-Jun-05
28-Dec-05
28-Jun-06
28-Dec-06
28-Jun-07
28-Dec-07
28-Jun-08
28-Dec-08
28-Jun-09
28-Dec-09
28-Jun-10
28-Dec-10
28-Jun-11
28-Dec-11
28-Jun-12
28-Dec-12
28-Jun-13
28-Dec-13
28-Jun-14
28-Dec-14
28-Jun-15
28-Dec-15
28-Jun-16
28-Dec-16
28-Jun-17
28-Dec-17
28-Jun-18
28-Dec-18
~
28-Jun-19 ~~ I I I I I I
-4 i I ....
0 :::r
0 ""(
2. 0 ""(
3
~ C C1)
0
1 ,ChlQrofomi carbon CliloroJnetltane Metl\ylene Nitrate Chloride TW4*2 Tetraclilorlde Chloride Cu~I) ''rullln (ug/1) (us/I) 1: (mgll) (mg/I) ·,
10-Nov-99 2510
2-Sep-00 5220
28-Nov-OO 4220 10.7
29-Mar-01 3890 10.2
22-Jun-01 5500 9.67
20-Sep-01 4900 11.4
8-Nov-01 5300 10.1
26-Mar-02 5100 9.98
23-May-02 4700 9.78
12-Sep-02 6000 9.44
24-Nov-02 5400 10.4
28-Mar-03 4700 9.5
23-Jun-03 5100 9.6
12-Sep-03 3200 8.6
8-Nov-03 4700 9.7
29-Mar-04 4200 9.14
22-Jun-04 4300 8.22
17-Sep-04 4100 8.4
17-Nov-04 4500 8.6
16-Mar-05 3700 7.7
25-May-05 3750 8.6
31-Aug-05 3900 <10 <10 <10 8 NA
l-Dec-05 3500 <50 <50 <50 7.8 NA
9-Mar-06 3800 <50 <50 <50 7.5 56
14-Jun-06 3200 <50 <50 <50 7.1 56
20-Jul-06 4120 <50 <50 <50 7.4 54
8-Nov-06 3420 2.3 <1 <1 7.6 55
28-Feb-07 2900 1.8 <1 <1 7.3 54
27-Jun-07 3000 2.5 <1 <1 7.8 50
15-Aug-07 340 2.2 <1 <1 7.3 49
10-0ct-07 3200 2.1 <1 <1 6.9 51
26-Mar-08 3300 2.3 <1 <1 6.9 48
25-Jun-08 3100 2.2 <1 <1 7.44 46
10-Sep-08 2800 2.4 <1 <1 7.1 42
15-0ct-08 3200 2.4 <2 <2 7.99 47
ll-Mar-09 3100 2.2 <1 <1 6.5 46
24-Jun-09 2800 2 <1 <1 6.4 44
15-Sep-09 3000 2 <1 <1 6.6 43
29-Dec-09 1600 2 <1 <1 6.4 46
',. 1-·. Carbon Methylene
TW+2 1 Ghio oform Tet.-ac.ldMiu Chloromethane Chloride Nitrate Cblorlde
1·. (ug/0 (wtJ11 (ug/1) (usr/i) (mfll) (mg/I) '•
3-Mar-10 2600 2 <1 <1 6.8 42
15-Jun-10 3300 2.6 <1 <1 6.7 43
16-Aug-10 3300 2.5 <l <l 6.6 43
14-0ct-10 3000 2.1 <1 <l 6.5 41
24-Feb-11 3100 2.4 ND ND 7 46
2-Jun-11 3000 2.2 ND ND 6.8 42
17-Aug-11 2400 1.6 ND ND 6 48
29-Nov-11 3900 2.8 ND ND 7 49
24-Jan-12 2500 2 ND ND 7.1 49
14-Jun-12 2500 2.1 ND ND 7.7 52
13-Sep-12 2900 1.8 ND ND 4 76
4-0ct-12 3100 2 ND ND 7.6 49
13-Feb-13 3580 5.17 ND ND 8.1 46
19-Jun-13 3110 2.65 ND ND 7.51 46.9
12-Sep-13 3480 2.41 ND ND 9.3 44.9
14-Nov-13 3740 3.15 ND ND 8.39 43.9
6-Feb-14 3180 7.1 ND ND 7.87 45.9
23-May-14 2930 6.05 ND ND 9.11 45.4
27-Aug-14 3170 1.4 3.6 ND 6.2 45
30-0ct-14 3580 2.6 ND ND 8.45 45.5
9-Mar-15 1840 1.44 ND ND 5.32 44.9
8-Jun-15 1650 ND ND ND 4.3 48.1
31-Aug-15 1310 ND ND ND 3.76 50.0
19-0ct-15 2070 ND ND ND 5.18 41.9
9-Mar-16 1970 1.20 ND ND 5.30 43.4
23-May-16 2070 1.49 ND ND 5.67 43.8
25-Jul-16 1780 ND ND ND 4.07 42.9
12-0ct-16 1600 ND ND ND 6.07 44.3
8-Mar-17 1570 ND ND ND 4.74 43.1
13-Jun-17 1940 ND ND ND 4.90 43.6
26-Jul-17 1310 ND ND ND 5.08 43.2
l l-Oct-17 1610 ND ND ND 3.28 43.5
12-Mar-18 764 ND ND ND 2.94 44.4
8-Jun-18 949 ND ND ND 3.50 41.3
22-Aug-18 980 ND ND ND 4.83 44.3
28-Nov-18 822 ND ND ND 3.52 41.7
8-Mar-19 1040 ND ND ND 3.92 40.4
5-Jun-19 1360 ND ND ND 4.38 39.8
4-Sep-19 797 ND ND ND 4.79 40.8
0
......
0 0 0
I\)
0 0 0
(ug/L)
c,.:,
0 0 0
~ 0 0 0
u,
0 0 0
0)
0 0 0
.....,
0 0 0
1 O-Nov-99 -t-----+---+--...._=-+----+---+-----1-------1
10-May-OO
10-Nov-OO
10-May-01
10-Nov-01
10-May-02
10-Nov-02
10-May-03
10-Nov-03
10-May-04
10-Nov-04
10-May-05
10-Nov-05
10-May-06
10-Nov-06
10-May-07
10-Nov-07
10-May-08
10-Nov-08
10-May-09
10-Nov-09
10-May-10
10-Nov-10
10-May-11
10-Nov-11
10-May-12
10-Nov-12
10-May-13
10-Nov-13
10-May-14
10-Nov-14
10-May-15
10-Nov-15
1 O-May-16
10-Nov-16
10-May-17
1 O-Nov-1·7
10-May-18
10-Nov-18
10-May-19 -
~ii>~o o c:0-(1)-D) ~Q«D> 6i
gac:8"-o _ o:::,-. o
Cl) .-:! a. a -·
C) '<; (I) 0 ;:t O~CO'<-, .......... en (I) oQ::::t.ro~ -3 en (I) ...... :::, Cl) C: en
0 2. ..... ;::::;-(I) • (I) en ::, C) C. . ..... g C.-1~
!!1. ~ (1)-:::J" C) C. 0 CD,....<~ ~-0 Cl) (I) :::, -en co C: "O ..... (I) 0 ffi cii" ~ en
-f i ~
0 :::T
0 .. ~ ..
3
~
i: C'D en
I ~~"'-
,a1· ·, ·r. 11. Carbon Methyle.ne ·, .. Ci! oro onn Chlorometbane Nitrate Chloride )~\f4· J~,IJ) Titl'2'~::rld~ (ug/1~ Chloride (mg/I) (mg/I)
,·~ . (il . (u2ll)
28-Jun-99 3500 7.6
29-Nov-99 702
15-Mar-OO 834
2-Sep-00 836 1.56
29-Nov-OO 836 1.97
27-Mar-01 347 1.85
21-Jun-01 390 2.61
20-Sep-01 300 3.06
7-Nov-01 170 3.6
26-Mar-02 11 3.87
21-May-02 204 4.34
12-Sep-02 203 4.32
24-Nov-02 102 4.9
28-Mar-03 0 4.6
23-Jun-03 0 4.8
12-Sep-03 0 4.3
8-Nov-03 0 4.8
29-Mar-04 0 4.48
22-Jun-04 0 3.68
17-Sep-04 0 3.88
17-Nov-04 0 4.1
16-Mar-05 0 3.5
25-May-05 <l NA NA NA 3.7 NA
31-Aug-05 <1 <1 6.4 <1 3.5 NA
1-Dec-05 <1 <1 2.3 <1 3.3 NA
9-Mar-06 <1 <l 2.2 <I 3.3 26
14-Jun-06 <1 <l <1 <I 3.2 26
20-Jul-06 <1 <1 1.6 <l 2.9 26
8-Nov-06 <1 <1 <1 <1 1.5 23
28-Feb-07 <1 <1 <1 <1 3.1 22
27-Jun-07 <1 <1 <1 <1 3.3 23
15-Aug-07 <l <1 <1 <l 3.1 24
10-0ct-07 <1 <1 <1 <l 2.8 27
26-Mar-08 <l <l <1 <1 2.8 21
25-Jun-08 <1 <1 <1 <1 2.85 19
10-Sep-08 <1 <1 <1 <l 2.66 19
15-0ct-08 <1 <1 <1 <l 2.63 22
4-Mar-09 <1 <1 <1 <1 2.5 21
24-Jun-09 <1 <l <1 <1 2.9 20
15-Sep-09 <1 <l <1 <1 2.8 21
16-Dec-09 <1 <l <1 <1 2.5 22
23-Feb-10 <1 <l <1 <1 2.8 23
s -1,: ," rf.'-C.Qrbon Metjtylen 1
' CJtlo~.tonn Chlo o e~ane itrate Chloride TW4--3 1, l"g!))
: Tetracbloride (uW. Chl'ottiile (Dig/I) (mgll) I-' -,~) (uldl}
8-Jun-10 <1 <1 <1 <1 3 24
10-Aug-10 <1 <1 <1 <1 3.1 22
5-0ct-10 <1 <1 <1 <1 3.3 26
15-Feb-11 ND ND ND ND 3.5 23
25-May-11 ND ND ND ND 3.7 23
16-Aug-11 ND ND ND ND 4 23
15-Nov-1 I ND ND ND ND 4.4 23
17-Jan-12 ND ND ND ND 4.3 21
31-May-12 ND ND ND ND 4.4 24
29-Aug-12 ND ND ND ND 4.9 25
3-0ct-12 ND ND ND ND 4.8 25
7-Feb-13 ND ND ND ND 5.05 23.7
29-May-13 ND ND ND ND 5.83 23.8
29-Aug-13 ND ND ND ND 6.26 24.0
6-Nov-13 ND ND ND ND 5.89 24.1
22-Jan-14 ND ND ND ND 6.66 24.9
19-May-14 ND ND ND ND 6.01 24.4
13-Aug-14 ND ND ND ND 5.3 26
23-0ct-14 ND ND ND ND 6.07 26.7
ll-Mar-15 ND ND ND ND 6.64 26.2
10-Jun-15 ND ND ND ND 5.71 27.5
2-Sep-15 ND ND ND ND 3.88 27.4
21-0ct-15 ND ND ND ND 5.37 25.6
15-Mar-16 ND ND ND ND 5.83 32.8
25-May-16 ND ND ND ND 5.65 27.9
27-Jul-16 ND ND ND ND 6.10 26.5
19-0ct-16 ND ND ND ND 6.00 29.5
14-Mar-17 ND ND ND ND 6.18 28.1
14-Jun-17 ND ND ND ND 6.36 28.7
27-Jul-17 ND ND ND ND 6.36 28.5
10-0ct-17 ND ND ND ND 6.32 25.9
14-Mar-18 ND ND ND ND 6.46 29.8
12-Jun-18 ND ND ND ND 6.52 26.1
29-Aug-18 ND ND ND ND 5.53 31.0
30-Nov-18 ND ND ND ND 5.85 27.4
13-Mar-19 ND ND ND ND 5.82 25.5
13-Jun-19 ND ND ND ND 6.68 27.4
11-Sep-19 ND ND ND ND 5.12 26.0
Jun-99
Dec-99
Jun-00
Dec-00
Jun-01
Dec-01
Jun-02
Dec-02
Jun-03
Dec-03
Jun-04
Dec-04
Jun-05
Dec-05
Jun-06
Dec-06
Jun-07
Dec-07
Jun-08
Dec-08
Jun-09
Dec-09
Jun-10
Dec-10
Jun-11
Dec-11
Jun-12
Dec-12
Jun-13
Dec-13
Jun-14
Dec-14
Jun-15
Dec-15
Jun-16
Dec-16
Jun-17
Dec-17
Jun-18
Dec-18
Jun-19
0 0
...... u, 0 0 0 0 0 0 0
(ug/L)
...... I\) I\) u, 0 u,
0 0 0 0 0 0 0 0 0
w 0 0 0 0
3~ -· .a::. r1' I u, w -· ::::s ::r n DJ tD u, s a-
DJ tD ... tD n ::, ::r_
N tD co ~ .. .... N ::r 0 DJ 0 ::, w ....
::r
tD
Q.
tD ....
tD n .... -· 0 ::::s
w .i:,.. u, 0 0 0 0 0 0 0
i I w
0 :::r
0 .. 2. 0 .. 3
< m
C
(D en
Chlorofonn ! Carbon Chlo ometban Methylene Nitrate 1' .OhJoride II TW4·· Tetracliloride C.llJonde
II (ug/J) ·.(ue'/1) (ug(I) (ul?II> ~mg/I (mg/I)
6-Jun-00 0
2-Sep-00 0
28-Nov-OO 3.9
28-Mar-01 2260 1.02
20-Jun-01 3100 14.5
20-Sep-Ol 3200 14
8-Nov-01 2900 14.8
26-Mar-02 3400 15
22-May-02 3200 13.2
12-Sep-02 4000 13.4
24-Nov-02 3800 12.6
28-Mar-03 3300 13.4
23-Jun-03 3600 12.8
12-Sep-03 2900 12.3
8-Nov-03 3500 12.3
29-Mar-04 3200 12.2
22-Jun-04 3500 12.1
17-Sep-04 3100 11.1
17-Nov-04 3600 10.8
16-Mar-05 3100 11.6
25-May-05 2400 NA NA NA 11.3 NA
31-Aug-05 3200 <10 <10 <10 9.9 NA
l-Dec-05 2800 <50 <50 <50 10.2 NA
9-Mar-06 2900 <50 <50 <50 9.5 51
14-Jun-06 2600 <50 <50 <50 8.6 48
20-Jul-06 2850 <50 <50 <50 9.7 50
8-Nov-06 2670 1.7 <1 <l 10.1 49
28-Feb-07 2200 1.5 <1 <1 9 49
27-Jun-07 2400 1.7 <1 <1 9.4 47
15-Aug-07 2700 1.5 <1 <1 9.5 45
10-0ct-07 2500 1.5 <1 <1 9.5 47
26-Mar-08 2800 1.6 <l <1 9.2 43
25-Jun-08 2500 1.5 <1 <1 10.8 42
10-Sep-08 2200 1.4 <l <1 8.83 39
15-0ct-08 2500 2 <2 <2 IO.I 44
4-Mar-09 2200 1.2 <l <1 10.2 37
24-Jun-09 1800 1.2 <l <1 8.2 34
15-Sep-09 2000 1.1 <1 <1 8.4 39
29-Dec-09 950 1.1 <1 <1 7.6 41
,... -"" ... ,cc, ea,bo~ Methylene ~· Chloro omi Chloromethane Nitrate Chloride' ~~ M (ug/1) Tetrachloride (ug/lj Chloride (_mg/I) (mg/I) (il2'}~ -(ueA~ 1, '> '•
17-Feb-IO 1700 1 <1 <1 6.6 48
IO-Jun-IO 2000 1.2 <1 <1 7.6 35
16-Aug-10 2100 1.3 <l <1 7.3 36
l 1-0ct-10 1700 1.3 <1 <l 7.1 38
23-Feb-1 l 1800 1.4 ND ND 7 41
1-Jun-11 1700 1.2 ND ND 7 35
17-Aug-ll 1500 ND ND ND 6.6 40
16-Nov-1 l 1500 1 ND ND 7 39
23-Jan-12 1200 ND ND ND 7.1 38
6-Jun-12 1500 ND ND ND 7.1 43
4-Sep-12 1600 1.2 ND ND 7.1 39
3-0ct-12 1400 1 ND ND 7 38
ll-Feb-13 1460 1.12 ND ND 7.36 39
5-Jun-13 1330 ND ND ND 6.3 39.6
3-Sep-13 1380 ND ND ND 7.22 38.8
29-0ct-13 1360 5.3 ND ND 7.84 43.9
27-Jan-14 1260 3.88 ND ND 7.28 37.4
19-May-14 1220 5 ND ND 5.91 47.5
l l-Aug-14 1320 ND 7 ND 5.30 40.0
21-0ct-14 1130 ND ND ND 7.02 40.0
9-Mar-15 1350 1 ND ND 7.70 37.6
8-Jun-15 1280 ND ND ND 6.33 41.3
31-Aug-15 1220 ND ND ND 6.45 45.8
19-0ct-15 1190 ND ND ND 6.27 38.5
9-Mar-16 1190 ND ND ND 6.71 39.7
23-May-16 1780 1 ND ND 6.56 41.9
26-Jul-16 1380 ND ND ND 7.22 40.2
13-0ct-16 1430 ND ND ND 6.77 42.3
8-Mar-17 1290 ND ND ND 6.87 41.7
13-Jun-17 1290 ND ND ND 7.06 40.7
26-Jul-17 1290 ND ND ND 6.47 40.5
l 1-0ct-17 1290 ND ND ND 6.90 40.7
12-Mar-18 1160 ND ND ND 6.12 42.2
8-Jun-18 1050 ND ND ND 6.34 39.0
22-Aug-18 1030 ND ND ND 6.34 39.0
28-Nov-18 1140 ND ND ND 6.02 41.4
8-Mar-19 1050 ND ND ND 7.26 38.3
5-Jun-19 1070 ND ND ND 10.40 38.5
4-Sep-19 989 ND ND ND 6.32 39.8
u,
Cl) :::::,
ca >
E ...
0 -0 ...
.2 .c 0
-=:t' I -=:t'
3r: I-
0 0 I{)
"""
0 0 0
"""
0 0 I{)
C')
0 0 0 C')
0 0 I{)
C\I
0 0 0 C\I
(1J6n)
0 0 IO .....
0 0 0 .....
0 0 IO
oc-unr-B~
L~-das-cc
v~-oaa-a
c ~ -JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
0
ChlorofQn;n Carb'Gn Chloremethan Methylene Nltr fe Chloride TW4•5 (ug/1) Te,.rorkle {ug/l) €hlo e (mg/I) (mgll) ul?lil burlJ)
20-Dec-99 29.5
15-Mar-OO 49.0
2-Sep-00 124
29-Nov-OO 255
28-Mar-01 236
20-Jun-01 240
20-Sep-Ol 240
7-Nov-01 260
26-Mar-02 260
22-May-02 300
12-Sep-02 330
24-Nov-02 260
28-Mar-03 240
23-Jun-03 290
12-Sep-03 200
8-Nov-03 240
29-Mar-04 210
22-Jun-04 200
17-Sep-04 150
17-Nov-04 180
16-Mar-05 120
25-May-05 113 NA NA NA 3.7 NA
31-Aug-05 82.0 <2.5 5.8 <2.5 6 NA
1-Dec-05 63.0 <2.5 2.5 <2.5 6 NA
9-Mar-06 66.0 <2.5 3.1 <2.5 6 52
14-Jun-06 51.0 <1 <2.5 <2.5 5.9 51
20-Jul-06 53.7 <1 <1 <l 6.7 54
8-Nov-06 47.1 <1 <1 <l 2.9 55
28-Feb-07 33.0 <1 <1 <1 7.8 57
27-Jun-07 26.0 <1 <l <1 7 45
15-Aug-07 9.2 <1 <l <1 7.7 38
10-0ct-07 9.4 <l <l <1 8.2 39
26-Mar-08 11.0 <1 <1 <1 7.4 36
25-Jun-08 9.3 <1 <1 <1 8.7 37
10-Sep-08 11.0 <1 <1 <1 7.91 34
15-0ct-08 10.0 <1 <1 <1 9.3 37
4-Mar-09 12.0 <1 <1 <1 7.9 34
24-Jun-09 13.0 <1 <1 <1 7.5 37
15-Sep-09 12.0 <I <1 <I 8.3 48
Chloroform Ca,bon Chloromethan·e Methylene Nitrate Chlollide TW~-5 (ullll) Temtchlorlde (ugll) Chloride (mg/I) (mgll) (uldil (ue/))
22-Dec-09 8.5 <l <1 <1 7.5 41
25-Feb-10 13.0 <1 <l <1 6.8 43
9-Jun-10 12.0 <1 <1 <I 7.1 28
1 l-Aug-10 12.0 <1 <1 <1 7 38
13-0ct-10 11.0 <l <1 <1 7.2 41
22-Feb-11 10.0 ND ND ND 7 34
26-May-11 9.0 ND ND ND 7.2 35
17-Aug-ll 10.0 ND ND ND 7.5 37
7-Dec-11 7.9 ND ND ND 6 30
18-Jan-12 7.6 ND ND ND 5.8 22
6-Jun-12 8.4 ND ND ND 8 39
11-Sep-12 12.0 ND ND ND 8.1 37
3-0ct-12 8.0 ND ND ND 7.7 38
13-Feb-13 10.8 ND ND ND 8.24 34.3
13-Jun-13 11.2 ND ND ND 10.7 36.5
5-Sep-13 11.6 ND ND ND 7.79 39.1
13-Nov-13 14.4 ND ND ND 7.75 41.1
30-Jan-14 12.5 ND ND ND 9.16 40.5
22-May-14 13.4 ND ND ND 7.78 51.4
14-Aug-14 12.0 ND ND ND 7.2 44
28-0ct-14 14.6 ND ND ND 8.31 45.1
12-Mar-15 13.8 ND ND ND 9.32 45.1
10-Jun-15 13.3 ND 1.07 ND 7.08 47.3
3-Sep-15 12.9 ND ND ND 8.1 52.2
28-0ct-15 11.0 ND ND ND 8.03 43.6
17-Mar-16 11.0 ND ND ND 10.2 44.7
26-May-16 13.6 ND ND ND 8.98 45.9
25-Jul-16 10.8 ND ND ND 8.49 44.6
26-0ct-16 10.8 ND ND ND 8.32 47.8
15-Mar-17 12.6 ND ND ND 8.49 44.7
15-Jun-17 14.6 ND ND ND 8.52 47.3
2-Aug-17 14.6 ND ND ND 8.52 48.6
10-0ct-17 13.8 ND ND ND 8.57 42.5
15-Mar-18 15.2 ND ND ND 8.36 51.2
13-Jun-18 13.9 ND ND ND 9.24 47.4
30-Aug-18 15.4 ND ND ND 7.34 54.7
12-Dec-18 15.6 ND ND ND 7.67 49.8
16-Mar-19 14.1 ND ND ND 7.38 47.6
13-Jun-19 15.8 ND ND ND 7.62 49.3
TW4·5
Carl.ron Chloromethane
Tetrachloride (ugtl)
J l -Sep-19 14.6 ND
Methylene
Chloride
u )
ND
Nitrate Chloride
(mg/1) (mg/I)
7.02 46.1
0 01 0
......
0 0
(ug/L)
......
01 0
I\)
0 0
I\)
01 0
c,.:,
0 0
c,.:,
01 0
24-Jul-98 +----....----1--------1-----+----+------1------1
19-Apr-01
14-Jan-04
10-0ct-06 ~ I I / I I I I I
6-Jul-09 ~ ~ I I I I I I I I
1-Apr-12 ~ l /I I I I I I I
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 _.__ ___ ......_ __ __J'------'----'------'------'---------'
-I
== .1:1,,
I c.n
(")
~ 0 ... 0 -0 ... 3
< !!. C
(I)
(/)
Cbloro~orm Ca'llbO Claloromethane Methylene itrate Chloride TW-4-6 etncblmid Cbllinde . (ugll) tuafl) (ugff) (02/1~ (mg/)) (Digtl)
6-Jun-00 0
2-Sep-00 0
28-Nov-OO 0 ND
26-Mar-01 0 0.13
20-Jun-01 0 ND
20-Sep-01 4 ND
7-Nov-01 1 ND
26-Mar-02 0 ND
21-May-02 0 ND
12-Sep-02 0 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 0 ND
12-Sep-03 0 ND
8-Nov-03 0 ND
29-Mar-04 0 ND
22-Jun-04 0 ND
17-Sep-04 0 ND
17-Nov-04 0 ND
16-Mar-05 0 0.2
25-May-05 2.5 NA NA NA 0.4 NA
31-Aug-05 10.0 <1 2.8 <1 0.8 NA
l-Dec-05 17.0 <l 1.3 <1 0.9 NA
9-Mar-06 31.0 <1 <l <1 1.2 31
14-Jun-06 19.0 <1 <1 <1 1 30
20-Jul-06 11.0 <1 <1 <1 0.6 37
8-Nov-06 42.8 <1 <1 <1 1.4 65
28-Feb-07 46.0 <l <1 <1 1.5 32
27-Jun-07 11.0 <1 <l <l 0.6 38
15-Aug-07 18.0 <l <1 <1 0.7 36
10-0ct-07 18.0 <1 <1 <1 0.8 38
26-Mar-08 52.0 <1 <1 <l 1.1 33
25-Jun-08 24.0 <1 <1 <1 0.9 35
10-Sep-08 39.0 <1 <1 <1 1.14 35
15-0ct-08 37.0 <1 <1 <1 1.01 33
11-Mar-09 81.0 <1 <1 <1 2.2 35
24-Jun-09 120 <1 <1 <l 2.7 37
15-Sep-09 280 <1 <1 <1 5.0 37
22-Dec-09 250 <l <1 <l 6.1 41
25-Feb-10 1000 <1 <1 <1 1.6 45
10-Jun-10 590 <1 <l <1 2.5 33
12-Aug-10 630 <1 <1 <1 3.9 31
13-0ct-10 420 <1 <l <1 4.3 41
:.!3-Feb-11 47 ND ND ND 0.7 40
l·:~i"'ill'·W 1_ CIIIOTOIOl'lb C rb'en ChloJ.10medlane
1
' Metliyle~e Nitrate r • Chlorille ~ . !
I (ug(J) I• TetraehloriclJ (llg/1), Ct.Jo.ride (mg/I) t~) .. ~~~la:"" . ' (liir/1) (uS!lll
26-May-l I lU NU NU ND 0.3 42
17-Aug-l 1 16 ND ND ND 0.3 39
7-Dec-11 21 ND ND ND 0.8 36
18-Jan-12 38 ND ND ND 0.7 38
13-Jun-12 4.7 ND ND ND 0.2 40
lI-Sep-12 6.9 ND ND ND 0.1 21
3-0ct-12 9.0 ND ND ND 0.2 41
13-Feb-13 6.9 ND ND ND 0.154 40.4
13-Jun-13 4.9 ND ND ND 0.155 37.9
5-Sep-13 5.9 ND ND ND 0.157 40.6
13-Nov-13 5.5 ND ND ND 1.52 40.2
29-Jan-14 5.7 ND ND ND 0.184 40.6
22-May-14 10.3 ND ND ND 0.312 37
14-Aug-14 202 ND ND ND 4.2 40
24-Sep-14 260 ND ND ND NIA NIA
29-0ct-14 723 ND ND ND 6.92 41.1
18-Mar-15 1180 ND ND ND 5.25 41.2
ll-Jun-15 1040 ND ND ND 5.87 41.6
10-Sep-15 1040 ND ND ND 6.75 47.0
29-0ct-15 843 ND ND ND 5.61 40.2
22-Mar-16 834 ND ND ND 6.79 42.0
8-Jun-16 486 ND ND ND 3.19 44.1
4-Aug-16 433 ND ND ND 3.85 42.2
26-0ct-16 301 ND ND ND 3.74 46.1
16-Mar-17 288 ND ND ND 3.15 42.1
21-Jun-17 239 ND ND ND 2.42 42.6
3-Aug-17 129 ND ND ND 1.71 42.9
11-0ct-17 121 ND ND ND 1.71 37.6
20-Mar-18 159 ND ND ND 1.96 43.1
14-Jun-18 74.9 ND ND ND 1.48 40.2
5-Sep-18 53.2 ND ND ND 1.18 44.0
12-Dec-18 37.0 ND ND ND 0.900 20.0
19-Mar-19 23.2 ND ND ND 0.755 41.0
13-Jun-19 15.8 ND ND ND 0.484 38.1
ll-Sep-19 15.8 ND ND ND 0.412 39.7
U)
Cl)
:::s -a; >
E ..
0 -0 .. .2 .c (.)
U)
I ~ 3: I-
0 0 "<:f" ,....
0 0 (\J ,....
0 0 0 ,....
0 0 co
(1J6n)
0 0 CD
0 0 "<:f"
0 0 (\J
0
oc::-unr-a~
L~-das-c::,
C::~-JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
"' . Cal!bo Methylene Chloroform Oblorom~thane Nit.rate C11loride
l ·4-7 (ug/1) ·TerrachJori(),e (ug/.1) Chloride (JQgll) (mgll) ~ ~iii-(ue/fi· (ue/1) .. · ..
29-Nov-99 256
15-Mar-OO 616
2-Sep-00 698
29-Nov-OO 684 1.99
28-Mar-01 747 2.46
20-Jun-01 llOO 2.65
20-Sep-Ol 1200 3.38
8-Nov-01 llOO 2.5
26-Mar-02 1500 3.76
23-May-02 1600 3.89
12-Sep-02 1500 3.18
24-Nov-02 2300 4.6
28-Mar-03 1800 4.8
23-Jun-03 5200 7.6
12-Sep-03 3600 7.6
8-Nov-03 4500 7.1
29-Mar-04 2500 4.63
22-Jun-04 2900 4.83
17-Sep-04 3100 5.59
17-Nov-04 3800 6
16-Mar-05 3100 5.2
25-May-05 2700 NA NA NA 5.4 NA
31-Aug-05 3100 <10 <10 <10 5.2 NA
l-Dec-05 2500 <50 <50 <50 5.3 NA
9-Mar-06 1900 <50 <50 <50 1 48
14-Jun-06 2200 <50 <50 <50 4.5 47
20-Jul-06 2140 <50 <50 <50 4.7 51
8-Nov-06 2160 1.5 <1 <1 4.6 49
28-Feb-07 1800 1.1 <1 <1 5 47
27-Jun-07 2600 1.5 <1 <1 5.1 45
14-Aug-07 2300 1.4 <1 <1 4.7 44
10-0ct-07 1900 1.2 <1 <l 4.7 45
26-Mar-08 2200 1.3 <1 <1 4.2 43
25-Jun-08 1800 1.3 <1 <1 4.8 43
10-Sep-08 1600 1.4 <1 <1 4.16 35
15-0ct-08 1900 <2 <2 <2 4.01 40
11-Mar-09 1800 1.2 <1 <1 3.7 35
24-Jun-09 1400 <1 <l <l 3.8 37
15-Sep-09 1500 1.0 <1 <1 4.1 37
Cbloroform Carbon Chloromethane Methylene itrate Chlonde ffl4-7. Tetrachloride Chloride (ug/1} (ue:11) (ug/1) Cueli) (mg/I) (mg()}
29-Dec-09 1300 <1 <1 <1 4.2 37
3-Mar-10 1200 <1 <1 <1 3.8 36
10-Jun-10 1100 <1 <1 <1 3.9 31
18-Aug-10 1500 1.1 <l <1 3.9 36
13-0ct-10 1100 1.1 <1 <1 4 38
23-Feb-1 l 1300 ND ND ND 3.60 45
1-Jun-11 1200 ND ND ND 4.00 35
18-Aug-11 1200 ND ND ND 4.10 37
29-Nov-11 1000 ND ND ND 3.80 37
19-Jan-12 1000 ND ND ND 3.90 37
14-Jun-12 790 ND ND ND 4.00 41
l 3-Sep-12 870 ND ND ND 3.80 40
4-0ct-12 940 ND ND ND 3.80 41
13-Feb-13 1080 3.51 ND ND 3.90 37.7
18-Jun-13 953 ND ND ND 4.04 39.3
12-Sep-13 1040 ND ND ND 4.17 36.4
14-Nov-13 1050 ND ND ND 4.13 37.2
5-Feb-14 946 5.41 ND ND 4.24 38.2
23-May-14 847 4.78 ND ND 4.19 37.7
27-Aug-14 857 ND 1.5 ND 2.90 39
30-0ct-14 926 ND ND ND 3.68 40.2
18-Mar-15 942 ND ND ND 4.25 40.4
ll-Jun-15 950 ND ND ND 2.62 42.1
10-Sep-15 897 ND ND ND 4.72 46.7
29-0ct-15 847 ND ND ND 3.49 40.6
22-Mar-16 834 ND ND ND 4.43 42.4
8-Jun-16 909 ND ND ND 3.75 44.1
4-Aug-16 1000 ND ND ND 4.21 42.3
27-0ct-16 886 ND ND ND 4.33 45.8
21-Mar-17 986 ND ND ND 3.87 40.5
21-Jun-17 968 ND ND ND 4.15 43.3
4-Aug-17 1070 ND ND ND 4.20 44.7
11-0ct-17 884 ND ND ND 4.35 43.7
21-Mar-18 721 ND ND ND 3.96 44.5
14-Jun-18 751 ND ND ND 4.45 41.5
5-Sep-18 781 ND ND ND 4.34 48.5
13-Dec-18 838 ND ND ND 3.98 42.8
20-Mar-19 736 ND ND ND 4.01 41.3
19-Jun-19 862 ND ND ND 4.19 43.0
l2-Sep-l9
Cat~on
Chlorofol'JJI Tetrachlotide
(ugtl)
801
Chloromethane Methylene
(ug/1) Chloride
ND
Nitrate Chloride
(mg/l) (mgll)
3.76 39.7
0
~
0 0 0
I\)
0 0 0
(ug/L)
w 0 0 0
.i:,.
0 0 0
01 0 0 0
0)
0 0 0
24-Jul-98 -1------+-----if------1-----t-----,-------,
19-Apr-01
14-Jan-04
10-0ct-06 , ,.-
6-Jul-09 ~ I ~ I I I I I
1-Apr-12 ~ M"'i I I I I I
~7-Dec-14
~2-Sep-17
18-Jun-20
15-Mar-23 -'-------l------l...------'-----'-----~---~
.....
=E .,::.. I .......
0 :::r
0 ""I 0 -0 ""I
3
< !.
C CD 0
Chlorofo Carbon · -Ohl~remefliane Methylene Nitrate €hloride I TW4--8 (Ilg/I) Tetrachloride Chlorid~
tW?JAl (ug(l) (udl) {mgfA) {Plg/1)
29-Nov-99 0
15-Mar-00 21.8
2-Sep-00 102
29-Nov-00 107 ND
26-Mar-01 116 ND
20-Jun-01 180 ND
20-Sep-01 180 0.35
7-Nov-01 180 ND
26-Mar-02 190 0.62
22-May-02 210 0.77
12-Sep-02 300 ND
24-Nov-02 450 ND
28-Mar-03 320 0.8
23-Jun-03 420 ND
12-Sep-03 66.0 ND
8-Nov-03 21.0 0.1
29-Mar-04 24.0 0.65
22-Jun-04 110 0.52
17-Sep-04 120 ND
17-Nov-04 120 ND
16-Mar-05 10.0 ND
25-May-05 <1 NA NA NA 0.2 NA
31-Aug-05 1.1 <1 1.7 <1 <0.1 NA
30-Nov-05 <l <1 <1 <1 <0.1 NA
9-Mar-06 1.3 <1 2.1 <1 0.3 39
14-Jun-06 1.0 <l 1.8 <l <0.1 37
20-Jul-06 <1 <1 <1 <1 0.1 39
8-Nov-06 <1 <1 <1 <1 <0.1 40
28-Feb-07 2.5 <1 <1 <1 0.7 39
27-Jun-07 2.5 <1 <1 <1 0.2 42
15-Aug-07 1.5 <1 <1 <1 <0.1 42
10-0ct-07 3.5 <1 <1 <1 0.5 43
26-Mar-08 <1 <1 <1 <1 0.1 46
25-Jun-08 <1 <1 <1 <1 <0.05 45
10-Sep-08 <1 <1 <1 <1 <0.05 39
15-0ct-08 <1 <1 <1 <l <0.05 44
4-Mar-09 <1 <1 <1 <l <0.1 42
24-Jun-09 <1 <l <1 <1 <0.1 44
15-Sep-09 <1 <1 <1 <1 <l 44
I~ ·. :, : Carbon Methylene ... Ct;lorolorm • · Chlo ometbane Nitrate Ohloride 'f,W+ 'Tetrachloride Chloride :i . ug/1) (ua:/1) (ug/1) Cue/I~ (mg/I, entgm
'
17-Dec-09 <1 <1 <1 <l <0.1 51
24-Feb-10 <1 <1 <1 <l <0.1 57
9-Jun-10 <1 <1 <l <l <0.1 42
1 l-Aug-10 <1 <l <1 <1 <0.1 45
5-0ct-10 <1 <l <1 <1 <0.1 46
16-Feb-11 ND ND ND ND ND 52
25-May-1 l ND ND ND ND 0.1 45
16-Aug-11 ND ND ND ND 0.1 46
7-Dec-11 ND ND ND ND 0.2 45
18-Jan-12 ND ND ND ND 0.3 45
31-May-12 ND ND ND ND 0.2 44
29-Aug-12 ND ND ND ND 0.1 48
3-0ct-12 ND ND ND ND ND 47
7-Feb-13 ND ND ND ND 0.411 46.6
30-May-13 ND ND ND ND ND 45.5
5-Sep-13 ND ND ND ND ND 47.5
7-Nov-13 ND ND ND ND ND 46.1
23-Jan-14 63.8 ND ND ND 0.166 48.5
6-Feb-14 100 ND ND ND 0.165 46.6
22-May-14 122 ND ND ND 0.538 53
27-Aug-14 107 ND ND ND 0.6 47
29-0ct-14 191 ND ND ND 0.914 46.7
12-Mar-15 961 ND ND ND 2.34 49.6
ll-Jun-15 981 ND ND ND 1.88 53
10-Sep-15 747 ND ND ND 1.96 59.6
29-0ct-15 770 ND ND ND 2.20 52.0
17-Mar-16 634 ND ND ND 2.48 54.2
8-Jun-16 595 ND ND ND 2.14 58.7
4-Aug-16 522 ND ND ND 2.10 56.9
27-0ct-16 472 ND ND ND 2.16 60.1
21-Mar-l 7 359 ND ND ND 2.06 57.4
21-Jun-17 256 ND ND ND 1.97 58.8
4-Aug-17 223 ND ND ND 1.64 61.2
11-0ct-17 214 ND ND ND 1.97 52.2
21-Mar-18 220 ND ND ND 1.36 60.8
14-Jun-18 155 ND ND ND 1.31 53.8
5-Sep-18 137 ND ND ND 1.40 63.2
13-Dec-18 93.8 ND ND ND 0.123 65.8
19-Mar-19 103 ND ND ND 1.23 54.3
Cbloromethane Metby.lene Nitrate Chloride
(ug/1) C.hlo,ide Ong{)) (mg/I)
19-Jun-19 96.0 ND 1.10 56.5
12-Sep-l 9 75.4 ND ND ND 0.999 52.0
tn G)
::l -; >
E ... 0 -0 ...
.2 .c 0
co I ~ 3: I-
0 0 C\J ,....
0 0 0 ,....
0 0 <X)
0 0 <D
(1J6n)
0 0
""'"
0 0 C\J
oi-unr-B~
L~-daS-ll
l ~ -JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
0
Chloroform1 earbon Cblorom thane Methyl~ Nitrate Chloride
' TW~9 (ug/J) Tetrachloride (ug(l> 0 e (mg/I) (mg/I) (ua/1) (tQ!/.1)
20-Dec-99 4.2
15-Mar-OO 1.9
2-Sep-00 14.2
29-Nov-00 39.4 ND
27-Mar-01 43.6 ND
20-Jun-01 59.0 0.15
20-Sep-01 19.0 0.4
7-Nov-01 49.0 0.1
26-Mar-02 41.0 0.5
22-May-02 38.0 0.65
12-Sep-02 49.0 0.2
24-Nov-02 51.0 0.6
28-Mar-03 34.0 0.6
23-Jun-03 33.0 0.8
12-Sep-03 32.0 1.1
8-Nov-03 46.0 1.1
29-Mar-04 48.0 0.82
22-Jun-04 48.0 0.75
17-Sep-04 39.0 0.81
17-Nov-04 26.0 1.2
16-Mar-05 3.8 1.3
25-May-05 1.2 NA NA NA 1.3 NA
31-Aug-05 <1 <1 2.9 <1 1.3 NA
1-Dec-05 <1 <1 <1 <1 1.3 NA
9-Mar-06 <1 <1 2.6 <1 1.5 38
14-Jun-06 <1 <1 2.7 <1 1.5 39
20-Jul-06 <1 <1 <1 <1 0.9 41
8-Nov-06 <1 <1 <1 <l 0.7 44
28-Feb-07 <1 <1 <1 <1 0.6 44
27-Jun-07 21 <1 <1 <1 1.3 42
15-Aug-07 9.5 <1 <1 <l 1.8 38
10-0ct-07 8.7 <1 <l <1 2 40
26-Mar-08 1.3 <1 <l <1 2.1 35
25-Jun-08 1.0 <1 <l <1 2.3 35
10-Sep-08 <l <l <l <1 2.79 28
15-0ct-08 <1 <1 <l <l 1.99 58
4-Mar-09 <1 <l <l <l 2.5 30
24-Jun-09 <1 <l <1 <l 2.3 30
15-Sep-09 <1 <l <l <l 2.5 30
-€8l'bO M-ylene Chloroform -·· Nitrate Chloride I e rw4 .. 9 :, 'tetrachlotid .. -Chlo (ug/0 iuelfl f gJI) (ualil (mg/I) (mg/J)
17-Dec-09 <l <l <I <1 1.7 37
23-Feb-10 <l <1 <1 <l 1.7 47
9-Jun-10 <1 <1 <1 <1 1.5 33
11-Aug-10 <1 <1 <1 <1 1.2 40
6-0ct-10 <1 <1 <l <1 1.8 34
17-Feb-11 ND ND ND ND 1.3 41
25-May-l l ND ND ND ND 3.4 38
16-Aug-ll ND ND ND ND 4 21
7-Dec-11 ND ND ND ND 2.3 38
18-Jan-12 ND ND ND ND 2.3 28
31-May-12 ND ND ND ND 4 23
30-Aug-12 ND ND ND ND 3.9 22
3-0ct-12 ND ND ND ND 3.8 21
7-Feb-13 ND ND ND ND 4.12 20.6
30-May-13 ND ND ND ND 4.49 21.4
5-Sep-13 ND ND ND ND 4.03 22.7
7-Nov-13 ND ND ND ND 4.87 23.6
29-Jan-14 ND ND ND ND 4.36 22
21-May-14 6.9 ND ND ND 3.44 24
14-Aug-14 46.9 ND ND ND 2.7 27
29-0ct-14 101 ND ND ND 4.27 25
12-Mar-15 53.5 ND ND ND 3.28 29.5
11-Jun-15 35.1 ND ND ND 1.83 35.3
3-Sep-15 48.2 ND ND ND 1.44 39.5
28-0ct-15 68.4 ND ND ND 2.89 29.2
17-Mar-16 74.3 ND ND ND 2.51 33.6
8-Jun-16 76.2 ND ND ND 2.16 35.1
3-Aug-16 76.8 ND ND ND 2.11 33.6
26-0ct-16 76 ND ND ND 2.24 37.4
16-Mar-17 113 ND ND ND 2.18 34.5
21-Jun-17 113 ND ND ND 1.92 35.9
3-Aug-17 118 ND ND ND 1.90 37.0
11-0ct-l 7 132 ND ND ND 2.18 32.3
21-Mar-18 159 ND ND ND 1.85 38.3
14-Jun-18 134 ND ND ND 1.85 35.7
5-Sep-18 94.2 ND ND ND 1.04 43.4
13-Dec-18 109 ND ND ND 1.23 36.3
19-Mar-19 86.4 ND ND ND 1.09 36.9
19-Jun-19 68.1 ND ND ND 0.785 38.3
ll-Sep-19
Carbon
Qh.oroform Tetrachloride
{ug/l)
66.0
Chloromethane
(ug/1}
ND
Methylene Nitrate Chloride
Chloride (mg/)) (mgll)
0.904 35.2
u,
Cl) :::s
c,s >
E ...
0 -0 ...
.2 .c 0
a,
I "d' 3: I-
0 co ..--
0 co 0 s;f" ..--
0 C\J 0 0
(1J6n)
0 co 0 co 0 C\J 0
oi-unr-B~
L~-das-cc:
p~-oaa-a
c ~ -Jd\f-~
60-1nr-9
go-ioo-o~
po-uer-P~
~Q-Jd\f-6 ~
Chloroform Carben CJillormnethue Ueth,t~ Nitl'ate Chloride TW4-10 11arachlmide n· ;.
(ug/1) ( -.-.,.~~. (mg/I) glf)) (ile/.t\ (u,vl)'
21-Jan-02 14
26-Mar-02 16 0.14
21-May-02 17 0.11
12-Sep-02 6 ND
24-Nov-02 14 ND
28-Mar-03 29 0.2
23-Jun-03 110 0.4
12-Sep-03 74 0.4
8-Nov-03 75 0.3
29-Mar-04 22 0.1
22-Jun-04 32 ND
17-Sep-04 63 0.46
17-Nov-04 120 0.4
16-Mar-05 140 1.6
25-May-05 62.4 NA NA NA 0.8 NA
31-Aug-05 110 <2.5 6.2 <2.5 1.1 NA
l-Dec-05 300 <2.5 <2.5 <2.5 3.3 NA
9-Mar-06 190 <5 <50 <50 2.4 50
14-Jun-06 300 <5 <50 <50 3.5 54
20-Jul-06 504 <5 <50 <50 6.8 61
8-Nov-06 452 <l 1.6 1 5.7 58
28-Feb-07 500 <l <l 1 7.6 62
27-Jun-07 350 <1 <l 1 5.1 54
15-Aug-07 660 <1 <l 1 7.3 59
10-0ct-07 470 <1 <l 1 6.7 59
26-Mar-08 620 <1 <l 1 7.3 55
25-Jun-08 720 <1 <1 1 9.91 58
10-Sep-08 680 <l <1 1 9.23 51
15-0ct-08 1200 <2 <2 2 10.5 61
11-Mar-09 1100 <l <l 1 11.6 64
24-Jun-09 1200 <1 <1 1 9.8 62
15-Sep-09 910 <1 <1 1 8.1 51
22-Dec-09 300 <1 <1 <l 3.5 51
3-Mar-10 460 <1 <1 <l 5 49
10-Jun-10 220 <l <1 <l 1.6 42
12-Aug-10 100 <1 <1 <l 0.8 38
13-0ct-10 1100 <l <1 <1 11 52
23-Feb-11 620 ND ND ND 9 62
l-Jun-11 280 ND ND ND 3.3 42
.. earb• Meth,teu. Cldor.ofomt ~ Nitrate
1
,Ch1oride
'I TW~lO (~ Tetnltdderide {Ufdl) Cldonde (mg/I)) (~g/1) II (udj 'ismll ' -
17-Aug-11 180 ND ND ND 1.9 41
16-Nov-11 110 ND ND ND 1.1 45
19-Jan-12 76 ND ND ND 0.9 40
13-Jun-12 79 ND ND ND 0.8 46
12-Sep-12 130 ND ND ND 1.0 44
3-0ct-12 140 ND ND ND 1.6 45
13-Feb-13 154 ND ND ND 1.2 49.l
13-Jun-13 486 ND ND ND 5.6 51.5
12-Sep-13 1160 ND ND ND 13.0 67.9
14-Nov-13 1380 ND ND ND 16.0 70.9
5-Feb-14 1260 5.16 ND ND 16.8 73
23-May-14 1110 ND ND ND 13.9 77.3
27-Aug-14 1060 ND 1.5 ND 9.8 74
30-0ct-14 1220 ND ND ND 13.2 75.2
18-Mar-15 1210 ND ND ND 15.0 78.6
ll-Jun-15 1240 ND ND ND 11.4 75
10-Sep-15 1280 ND ND ND 14.0 89.5
29-0ct-15 1350 ND ND ND 13.5 79.9
22-Mar-16 1430 ND ND ND 17.3 84.1
8-Jun-16 1510 ND ND ND 14.9 89.5
4-Aug-16 1500 ND ND ND 14.9 85.3
27-0ct-16 1290 ND ND ND 14.8 84.4
21-Mar-17 1260 ND ND ND 13.0 74.6
21-Jun-17 1140 ND .ND ND 13.0 73.1
4-Aug-17 1320 ND ND ND 13.4 77.0
11-0ct-17 1150 ND ND ND 12.9 70.0
21-Mar-18 1240 ND ND ND 11.1 72.7
14-Jun-18 914 ND ND ND 11.2 64.5
5-Sep-18 911 ND ND ND 10.1 73.5
13-Dec-18 1070 ND ND ND 10.6 63.5
20-Mar-19 869 ND ND ND 9.34 59.3
19-Jun-19 799 ND ND ND 8.86 58.7
12-Sep-19 734 ND ND ND 7.79 55.8
u,
Cl) :::, m >
E ...
0 -0 ...
.2 .c
0
0 ,....
I o:::t 3: I-
0 0 (0 ....
0 0 ,;f" ....
0 0 C\J ....
0 0 0 ....
0 0 co
0 0 (0
(1J6n)
0 0 C\I
oz-unr-e~
L~-das-zz
C::kJdV-~
50-1nr-9
90-PO-O~
vo-uer-v~
0
~ ,,~ -~, , .. ,II; C81'bon ·~ 1 • Qilorp orm Cblol'Omethaqe Methylene Nitrate ChloPide g ~~11 ·" T~r ~· ~ ,,, ( g/1) (ugll) €hloride (ug/1) (mg/I) (mg/I)
lh"-.
21-Jan-02 4700
26-Mar-02 4900 9.6
22-May-02 5200 9.07
12-Sep-02 6200 8.84
24-Nov-02 5800 9.7
28-Mar-03 5100 9.7
23-Jun-03 5700 9.4
12-Sep-03 4600 9.9
8-Nov-03 5200 9.3
29-Mar-04 5300 9.07
22-Jun-04 5700 8.74
17-Sep-04 4800 8.75
17-Nov-04 5800 9.7
16-Mar-05 4400 8.7
25-May-05 3590 NA NA NA 10.3 NA
31-Aug-05 4400 <10 <10 <10 9.4 NA
l-Dec-05 4400 <100 <100 <100 9.4 NA
9-Mar-06 4400 <50 <50 <50 9.2 56
14-Jun-06 4300 <50 <50 <50 10 56
20-Jul-06 4080 <50 <50 <50 10 55
8-Nov-06 3660 1.7 2.7 1.3 10 55
28-Feb-07 3500 1.3 <l 1.6 10.1 54
27-Jun-07 3800 1.6 <l 1.1 10.6 53
15-Aug-07 4500 1.7 <l 1.1 10.2 53
10-0ct-07 4400 1.6 <l 1.2 9.8 53
26-Mar-08 340 <l <l <1 7.7 63
25-Jun-08 640 <l <l <l 7.28 46
10-Sep-08 900 <l <1 <l 7.93 42
15-0ct-08 1000 <2 <2 <2 9.46 47
ll-Mar-09 1100 <l <1 <l 7.3 49
24-Jun-09 980 <l <1 <l 6.8 44
15-Sep-09 1000 <l <1 <l 7 49
29-Dec-09 860 <l <1 <l 6.6 46
3-Mar-10 820 <l <1 <l 6.8 42
10-Jun-10 820 <l <1 <1 6.9 40
12-Aug-10 800 <1 <1 <1 6.7 43
13-0ct-10 720 <1 <l <l 6.4 49
23-Feb-11 1000 ND ND ND 6.5 46
I-Jun-11 930 ND ND ND 7.3 49
Ir Chlo ofonn Car,bGn Chmr-·· ···-~-£ eth I Nittate Chloride TW4. Tetr chtoride •.
Ii ~ug/1~ fue'Jn (ugil~ cw . title ( ti) (mg/)) (mg/I)
17-Aug-11 820 ND ND ND 7.1 48
16-Nov-11 1500 ND ND ND 7.1 46
24-Jan-12 610 ND ND ND 6.8 43
13-Jun-12 660 ND ND ND 6.7 52
13-Sep-12 740 ND ND ND 3 49
4-0ct-12 730 ND ND ND 7 50
13-Feb-13 867 3.23 ND ND 6.83 47.3
18-Jun-13 788 ND ND ND 7.42 49.7
12-Sep-13 865 ND ND ND 7.8 46.6
13-Nov-13 874 ND ND ND 8.01 46.7
5-Feb-14 785 5.19 ND ND 8.47 48.5
23-May-14 751 ND ND ND 6.92 51.6
27-Aug-14 719 ND 1.2 ND 5.4 48
29-0ct-14 803 ND ND ND 7.33 56.4
9-Mar-15 2450 1.24 ND ND 8.72 49.8
8-Jun-15 2710 ND ND ND 8.48 62.2
31-Aug-15 1120 ND 1.62 ND 9.61 73.1
19-0ct-15 2730 ND ND ND 7.5 55.3
9-Mar-16 2660 1.2 ND ND 7.13 55.5
23-May-16 3340 2.19 ND ND 7.81 56.4
25-Jul-16 3200 ND ND ND 8.83 55.3
12-0ct-16 3180 1.58 ND ND 8.92 57.2
8-Mar-17 3310 1.71 ND ND 8.12 49.8
13-Jun-17 3370 1.83 ND ND 7.92 51.4
26-Jul-17 3290 1.81 ND ND 7.78 51.0
11-0ct-17 2880 1.48 ND ND 7.79 49.7
12-Mar-18 3090 1.82 ND ND 7.89 54.0
8-Jun-18 2800 1.34 ND ND 7.51 52.6
22-Aug-18 3050 1.47 ND ND 7.15 53.3
28-Nov-18 2930 1.33 ND ND 6.85 45.4
8-Mar-19 2820 1.48 ND ND 7.50 46.8
5-Jun-19 2970 1.52 1.40 ND 8.30 45.3
4-Sep-19 2790 ND ND ND 7.15 48.8
u,
G) :::,
"i >
E ...
0 -0 ... ,g
.c 0 ... ... I oi:t' 3: I-
0 0 0 I'--
0 0 0 co
0 0 0 lO
0 0 0 'q"
0 0 0 ct)
(1J6n)
0 0 0 C\J
0 0 0 ,-
0
oc-unr-a~
L~-das-cc
v~-oaa-a
G ~ -JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
,t €blorofOl'Jll Carbon Chloromethane Methy,~ Nitrate Chloride I~ TW~12 (ug/1) Tetrachlo Ide (ug/1) Ohl&rlde (mg/I) (mg/l) (uf?/1): :(111!/1)
12-Sep-02 2 2.54
24-Nov-02 0 2.2
28-Mar-03 0 1.9
23-Jun-03 0 1.8
12-Sep-03 0 1.8
9-Nov-03 0 1.6
29-Mar-04 0 1.58
22-Jun-04 0 1.4
17-Sep-04 0 1.24
17-Nov-04 0 1.5
16-Mar-05 0 1.4
25-May-05 <1 NA NA NA 1.6 NA
31-Aug-05 <1 <1 5.8 <1 1.5 NA
1-Dec-05 <l <l 1.9 <2 1.4 NA
9-Mar-06 <1 <l 2.6 <1 1.3 19
14-Jun-06 <1 <1 1.4 <l 1.4 16
20-Jul-06 <1 <1 <1 <l 1.4 16
8-Nov-06 <1 <1 <1 <1 1.4 16
28-Feb-07 <1 <1 <1 <1 1.5 16
27-Jun-07 <l <l <1 <l I,5 18
15-Aug-07 <l <l <1 <1 I.4 29
10-0ct-07 <1 <1 <1 <1 I.4 16
26-Mar-08 <1 <1 <1 <1 1.6 16
25-Jun-08 <1 <l <1 <l 2.69 19
10-Sep-08 <1 <1 <l <1 2.65 18
15-0ct-08 <1 <l <1 <1 2.47 22
4-Mar-09 <1 <1 <1 <1 2.4 23
24-Jun-09 <1 <l <l <l 3.8 22
15-Sep-09 <l <1 <1 <l 5.1 22
16-Dec-09 <1 <l <1 <1 3.6 23
23-Feb-10 <1 <1 <1 <1 4 22
8-Jun-10 <1 <1 <1 <1 11 29
10-Aug-IO <1 <1 <1 <1 9 35
5-0ct-10 <1 <1 <1 <1 8 31
15-Feb-ll ND ND ND ND 6.5 31
25-May-11 ND ND ND ND 7 32
16-Aug-11 ND ND ND ND 6.8 31
15-Nov-11 ND ND ND ND 8 30
17-Jan-12 ND ND ND ND 7.7 28
Chloroform Cad>&n Cbmromethaae ~eae N~ale CMo~ TW4• 2 T~ ChlOl'i. (ug4) ~ (qf/1) (q/1} (rnd)) (mgi&)
1,
31-May-12 ND ND ND ND 10 34
29-Aug-12 ND ND ND ND 13 39
3-0ct-12 ND ND ND ND 13 39
7-Feb-13 ND ND ND ND 12.6 36.7
29-May-13 ND ND ND ND 14.2 38.6
29-Aug-13 ND ND ND ND 17.4 41.7
6-Nov-13 ND ND ND ND 16.4 41.4
22-Jan-14 ND ND ND ND 18.4 41.6
21-May-14 ND ND ND ND 17 40.2
27-Aug-14 ND ND ND ND 13 47
23-0ct-14 ND ND ND ND 16.1 50.2
ll-Mar-15 ND ND ND ND 19.2 50.6
10-Jun-15 ND ND ND ND 18.8 56
2-Sep-15 ND ND ND ND 16.4 60.2
21-0ct-15 ND ND ND ND 18 51.0
15-Mar-16 ND ND ND ND 34.8 56.2
25-May-16 ND ND ND ND 30.7 66.4
27-Jul-16 ND ND ND ND 37.7 67.5
19-0ct-16 ND ND ND ND 25.8 72.6
14-Mar-17 ND ND ND ND 25.9 62.6
14-Jun-17 1.25 ND ND ND 29.9 67.2
2-Aug-17 1.20 ND ND ND 25.1 65.3
10-0ct-17 ND ND ND ND 26.9 56.2
14-Mar-18 ND ND ND ND 19.8 59.5
12-Jun-18 ND ND ND ND 18.4 53.6
29-Aug-18 ND ND ND ND 13.6 59.9
30-Nov-18 ND ND ND ND 10.4 56.1
16-Mar-19 ND ND ND ND 10.1 50.8
13-Jun-19 ND ND ND ND 8.31 55.3
ll-Sep-19 ND ND ND ND 8.88 52.6
19-Apr-01
14-Jan-04
10-0ct-06
6-Jul-09
1-Apr-12
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23
0 0
t •
• • ll
1
i
II
i
'
•
'
'
•• IS
•• •
' •• :
••
:
•• ' . • •• •
0 01
(ug/L)
0
.....
01
-
I\)
0
-4 ! I -I\)
0 :r 0 ... ~ ... 3
~ c Cl en
ehlorofonn c~ Chloro .. Mdhyten i ~ te Chloride W4-13 Nraehtorid.e €Jileride (ug/1) Jud) (ugln j(lfflA1'.), (mg/I) (mg/I~ ~-
12-Sep-02 ND ND
24-Nov-02 ND ND
28-Mar-03 ND 0.20
23-Jun-03 ND 0.20
12-Sep-03 ND ND
9-Nov-03 ND 0.90
29-Mar-04 ND 0.12
22-Jun-04 ND 0.17
17-Sep-04 ND 4.43
17-Nov-04 ND 4.70
16-Mar-05 ND 4.20
25-May-05 <l NA NA NA 4.30 NA
31-Aug-05 <1 <l 3.1 <l 4.60 NA
l-Dec-05 <l <l <l <l 4.30 NA
9-Mar-06 <l <l 1.7 <l 4.20 67.0
14-Jun-06 <I <l 1.4 <l 4.90 66.0
20-Jul-06 <1 <I <l <l 4.30 65.0
8-Nov-06 <l <I <l <I 0.80 33.0
28-Feb-07 <l <l <I <1 4.00 59.0
27-Jun-07 <1 <l <l <1 4.60 59.0
15-Aug-07 <1 <1 <1 <1 4.40 58.0
IO-Oct-07 <1 <1 <1 <1 4.10 58.0
26-Mar-08 <1 <1 <I <1 3.80 54.0
25-Jun-08 <1 <1 <l <1 4.24 58.0
IO-Sep-08 <1 <1 <l <l 4.26 50.0
15-0ct-08 <l <1 <l <l 4.63 58.0
4-Mar-09 <l <1 <l <l 3.70 58.0
24-Jun-09 <l <1 <l <1 1.20 57.0
15-Sep-09 <l <l <l <1 4.70 63.0
16-Dec-09 <l <1 <1 <1 4.10 60.0
24-Feb-10 <l <1 <l <l 4.30 53.0
8-Jun-10 <I <l <l <l 5.20 52.0
IO-Aug-10 <l <l <l <l 5.60 55.0
5-0ct-10 <l <l <I <l 5.80 55.0
15-Feb-11 ND ND ND ND 5.50 60.0
25-May-ll ND ND ND ND 5.40 56.0
16-Aug-ll ND ND ND ND 5.20 60.0
15-Nov-11 ND ND ND ND 5.90 54.0
17-Jan-12 ND ND ND ND 5.50 55.0
31-May-12 ND ND ND ND 6.00 59.0
29-Aug-12 ND ND ND ND 6.20 60.0
3-0ct-12 ND ND ND ND 5.90 60.0
11 O.hlo1.1ofoprp 1
Carbon Ch10Pomet1l11ne Methylene Nitrate ChloJ!itl~ 111 TW4-13 Teti11a hloride ·· Chloride
,I.
(ug/.1 .(ue/1) (ug/1) (ue/1) (~) C gtI>
7-Feb-13 ND ND ND ND 6.31 59.3
29-May-13 ND ND ND ND 6.84 56
29-Aug-13 ND ND ND ND 7.16 63.5
6-Nov-13 ND ND ND ND 6.48 58.5
22-Jan-14 ND ND ND ND 7.09 63.1
21-May-14 ND ND ND ND 5.99 56.1
13-Aug-14 ND ND ND ND 4.80 62
23-0ct-14 ND ND ND ND 6.28 66.1
l l-Mar-15 ND ND ND ND 7.09 66.4
10-Jun-15 ND ND ND ND 6.32 70.3
2-Sep-15 ND ND ND ND 5.70 76.5
21-0ct-15 ND ND ND ND 5.78 65.5
16-Mar-16 ND ND ND ND 7.97 69.4
25-May-16 ND ND ND ND 5.87 71.8
28-Jul-16 ND ND ND ND 6.14 69.3
19-0ct-16 ND ND ND ND 6.20 70.9
15-Mar-17 ND ND ND ND 6.05 66.0
15-Jun-17 ND ND ND ND 6.49 70.4
2-Aug-17 ND ND ND ND 6.15 70.5
10-0ct-17 ND ND ND ND 6.17 60.9
14-Mar-18 ND ND ND ND 5.76 71.0
12-Jun-18 ND ND ND ND 6.24 65.0
29-Aug-18 ND ND ND ND 5.13 73.7
30-Nov-18 ND ND ND ND 5.29 64.5
16-Mar-19 ND ND ND ND 5.74 61.6
13-Jun-19 ND ND ND ND 6.56 65.4
13-Sep-19 ND ND ND ND 5.19 65.3
Sep-02
Dec-02
Mar-03
Jun-03
Sep-03
Dec-03
Mar-04
Jun-04
Sep-04
Dec-04
Mar-05
Jun-05
Sep-05
Dec-05
Mar-06
Jun-06
Sep-06
Dec-06
Mar-07
Jun-07
Sep-07
Dec-07
Mar-08
Jun-08
Sep-08
Dec-08
Mar-09
Jun-09
Sep-09
Dec-09
Mar-10
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
Sep-16
Dec-16
Mar-17
Jun-17
Sep-17
Dec-17
Mar-18
Jun-18
Sep-18
Dec-18
Mar-19
Jun-19
Sep-19
0
'
!J
!J ,, ,,
' ' ' ' '
t ' j
-· •J ••
l
' '
' '
•J •• u
•• ••
tJ
' j
t
j
•
•J •• ••
'
••
'
••
•J
••
' • j. j. ..
•• '. a '. ' • •• '. ' ' ..
•• •• H
'~ '. ..
9 _. 0 i\, 9 w 0 :is,.
(ug/L)
9 u,
0
~
0
"""I 0 -0
"""I 3
~
Q) en
:::::s
0 -O"'
CD CD
:::::s
a.
CD -CD (') -CD a.
:::::s
-I ~ ~ I ......
vJ
9 0) 9 -...J 9 CX) 9 co
-I ! I ..
~
(") ::r
0 ~ ... 3
~
2" CD tn
-· 'T~:=-Metllyle ' er: .. ' 1· ...... -.. ·-TW4-. ~ • , .. orm Cblwoni Cfiloffll te Cbmride > -.... ;'
(, ~-:, (ll&'l) GndAO (,ng(t) (-0 (mgl)) (mg!.
8-Nov-06 <l <l <l <l 2.40 37.0
28-Feb-07 <l <l <l <l 2.30 38.0
27-Jun-07 <1 <l <l <1 1.40 38.0
15-Aug-07 <1 <1 <1 <l 1.10 36.0
IO-Oct-07 <l <1 <1 <1 0.80 36.0
26-Mar-08 <1 <1 <1 <l 0.04 57.0
25-Jun-08 <1 <1 <1 <l 1.56 35.0
10-Sep-08 <1 <l <1 <l 1.34 34.0
15-0ct-08 <1 <l <1 <1 0.76 40.0
4-Mar-09 <1 <1 <1 <1 1.60 35.0
24-Jun-09 <1 <1 <1 <l 1.40 36.0
15-Sep-09 <1 <1 <1 <1 1.50 38.0
16-Dec-09 <1 <1 <1 <l 1.40 34.0
3-Mar-10 <l <1 <l <1 2.50 33.0
8-Jun-10 <1 <1 <1 <1 2.90 49.0
10-Aug-10 <1 <1 <1 <l 2.80 35.0
6-0ct-10 <1 <1 <1 <l 2.90 29.0
15-Feb-11 ND ND ND ND 1.80 25.0
16-Aug-l l ND ND ND ND 2.60 33.0
15-Nov-11 ND ND ND ND 1.70 15.0
17-Jan-12 ND ND ND ND 1.90 20.0
31-May-12 ND ND ND ND 3.30 35.0
29-Aug-12 ND ND ND ND 3.90 37.0
3-0ct-12 ND ND ND ND 4.20 37.0
7-Feb-13 ND ND ND ND 4.63 35.2
30-May-13 ND ND ND ND 4.37 38.6
29-Aug-13 ND ND ND ND 4.51 37.6
6-Nov-13 ND ND ND ND 4.81 36.5
22-Jan-14 ND ND ND ND 5.92 35.5
21-May-14 ND ND ND ND 4.87 32.5
13-Aug-14 ND ND ND ND 4.10 38.0
23-0ct-14 1.68 ND ND ND 5.22 38.9
12-Mar-15 1.71 ND ND ND 5.22 40.1
10-Jun-15 1.82 ND ND ND 3.55 41.8
3-Sep-15 ND ND ND ND 2.77 42.4
21-0ct-15 1.46 ND ND ND 2.45 40.6
16-Mar-16 4.49 ND ND 2.18 2.94 42.4
26-May-16 6.15 ND ND 3.18 2.45 43.6
28-Jul-16 5.00 ND ND 1.80 2.88 42.4
--,_ .411•·-. ; Car.bQn Methilene
'] \f4.; 4 Chlotoform Tefra:wrlde ChJol!omethane Chloride Nitraf Chloride'
>' (Ug/1) (ug/1) (mg/I) (mg/I) ~ ~ Cu (uflll)
20-0ct-16 7.02 ND ND 1.59 2.86 45.6
15-Mar-17 6.45 ND ND ND 4.36 45.4
15-Jun-17 6.85 ND ND ND 5.12 46.9
2-Aug-17 6.14 ND ND ND 4.84 46.4
10-0ct-17 6.13 ND ND ND 4.73 42.5
15-Mar-18 5.80 ND ND ND 5.67 51.5
13-Jun-18 5.12 ND ND ND 6.36 46.9
30-Aug-18 4.76 ND ND ND 5.34 54.1
12-Dec-18 4.41 ND ND ND 5.85 48.7
16-Mar-19 4.08 ND ND ND 6.16 48.7
13-Jun-19 4.18 ND ND ND 5.86 48.3
ll-Sep-19 6.08 ND ND ND 4.77 45.4
fl) a,
:::::s
~
E lo, ~ ..2 .c 0
q' ,-
1 ;
I-
0 0
cri
...
V V
b!
0 0 r-..:
-
0 0 co
0 0
1/)
-
0 0
.,f
(1J6n)
0 0
cvj
0 0
C\i
-
1
T
~
•• • .. •• •• •
'J
••
• •
• •
••
•• 0 •• • ... '. a
•• ••
0
•t
0 0
ci
OG-unr-B~
L~-daS-GG
v~-oaa-a
60-1nr-9
90-JOQ-O~
vo-uer-v~
--Carb~n Melatle e ,\ , Cblor.oform c~•-Nilrate Cldbride W-2 Tetradilodde &rid (ug/1) '(uwf}, Cugll~ {ull) (mg/I~ (aqjl)
12-Sep-02 3 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 7800 14.5
15-Aug-03 7400 16.8
12-Sep-03 2500 2.7
25-Sep-03 2600 2.5
29-0ct-03 3100 3.1
8-Nov-03 3000 2.8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 1400 0.53
17-Nov-04 300 0.2
16-Mar-05 310 0.3
30-Mar-05 230 0.2
25-May-05 442 NA NA NA 0.2 NA
31-Aug-05 960 <5 5.4 <5 0.2 NA
l-Dec-05 1000 <50 <50 <50 0.3 NA
9-Mar-06 IlOO <50 <50 <50 0.2 52
14-Jun-06 830 <50 <50 <50 0.2 52
20-Jul-06 2170 <50 <50 <50 1.4 65
8-Nov-06 282 <l <1 2.8 0.3 54
28-Feb-07 570 <1 <1 5.5 0.5 56
27-Jun-07 300 <1 <1 13 0.4 49
15-Aug-07 1400 <1 <1 36 1 57
10-0ct-07 2000 <1 <1 14 0.6 57
26-Mar-08 930 <1 <1 40 0.1 49
25-Jun-08 1300 <1 <1 53 0.56 57
10-Sep-08 630 <1 <1 24 0.24 44
15-0ct-08 1700 <1 <1 100 0.65 64
4-Mar-09 950 <1 <1 51 0.4 49
24-Jun-09 410 <1 <1 12 0.2 48
15-Sep-09 850 <1 <1 30 0.1 46
14-Dec-09 1100 <1 <1 40 2.3 60
17-Feb-10 780 <1 <1 19 0.2 57
9-Jun-10 1900 <1 <1 28 1.1 58
16-Aug-10 2200 <1 <1 21 0.6 49
ll-Oct-10 970 <1 <1 6.5 0.7 65
23-Feb-11 450 ND ND 3.6 0.5 57
Clil&ro orm Carhon CW01'o · ...... Metil e ttrate Chloride MW-26 Tetr cklo Ide , e CM«t4e ' (uwf) :Cumh (ug{ij' (lll!A} (mgA) (mg/I)
31-May-11 1800 ND ND 1.3 0.4 88
17-Aug-l l 720 ND ND 7.2 0.9 58
5-Dec-11 1800 ND ND 2.9 2 69
7-Feb-12 2400 ND ND 16 1.7 98
6-Jun-12 3000 ND ND 21 2.5 73
4-Sep-12 3100 ND ND 31 2.6 73
4-0ct-12 1200 ND ND 4 1.8 68
ll-Feb-13 2120 ND ND 9.34 2.27 81.9
5-Jun-13 4030 ND ND 52.4 2.11 77.9
3-Sep-13 2940 ND ND 33.2 1.18 60.5
29-0ct-13 1410 ND ND 4.03 1.38 72.3
27-Jan-14 1400 ND ND 13.8 0.549 59.4
19-May-14 1960 ND ND 15.4 0.928 53.4
11-Aug-14 2120 ND 8.7 26 0.7 59
21-0ct-14 2090 ND ND 23.2 0.934 60.1
9-Mar-15 1980 ND ND 27.4 0.732 56.5
8-Jun-15 1980 ND ND 11.2 0.419 62
31-Aug-15 2350 ND 4.05 11.6 0.684 69.6
19-0ct-15 2680 ND 1.32 8.28 0.991 62.6
9-Mar-16 2650 ND 1.32 4.66 1.45 68.3
23-May-16 2220 ND ND 4.57 1.12 66.2
25-Jul-16 3190 ND ND 7.81 1.57 66.4
12-0ct-16 2510 ND ND 4.31 1.18 66.2
8-Mar-17 1290 ND ND 7.65 0.768 58.4
13-Jun-17 2450 ND ND 7.59 0.922 64.3
26-Jul-17 1230 ND ND 5.26 1.56 61.4
11-0ct-l 7 2570 ND ND 7.83 1.18 62.2
12-Mar-18 1210 ND ND 2.14 1.57 60.3
8-Jun-18 1870 ND ND 9.19 0.901 58.7
22-Aug-18 1680 ND ND ND 2.80 91.4
28-Nov-18 1480 ND ND ND 1.96 85.5
8-Mar-19 1110 ND ND 2.20 1.85 69.9
5-Jun-19 1280 ND ND 1.19 2.83 80.7
4-Sep-19 1360 ND ND 1.93 3.08 76.2
L~-das-cc
v~-oao-a
G ~ -Jd'v'-~ ,,,
Cl) :,
'ii >
E ..
0 -0 .. 60-1nr-9 .2 .c
0
co C\I 3:
:E
90-PO-O~
vo-uer-v~
~Q-Jd'v'-6 ~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 LO 0 LO 0 LO 0 LO 0 LO s:t" s:t" C') C') C\J C\J .... ....
(1J6n)
Chloroform Carbon Chlorometh ne M tbylene I• Nitrate Cblorldei II TW4•16 Tetracbh,rlde Cbteri 11 (ug/1) fwd!} (ugtl) (utdl) (mg/I) (mgll)
12-Sep-02 140 ND
24-Nov-02 200 ND
28-Mar-03 260 ND
23-Jun-03 370 ND
12-Sep-03 350 ND
8-Nov-03 400 ND
29-Mar-04 430 ND
22-Jun-04 530 ND
17-Sep-04 400 ND
17-Nov-04 350 ND
16-Mar-05 240 ND
25-May-05 212 NA NA NA <0.1 NA
31-Aug-05 85 <l 3.2 43 <0.1 NA
l-Dec-05 14 <2.5 2.6 5.9 1.4 NA
9-Mar-06 39 <1 1.1 21 3 60
14-Jun-06 13 <1 2.4 8.9 1.9 55
20-Jul-06 5.2 <1 <1 2.7 2.7 60
8-Nov-06 13.6 <1 <1 9.2 5.6 62
28-Feb-07 8.7 <1 <1 6.5 12.3 79
27-Jun-07 2.6 <1 <1 1.8 9.9 75
15-Aug-07 7.1 <1 <1 5.1 5.4 66
10-0ct-07 1.4 <1 <1 <1 4.4 69
26-Mar-08 11 <1 <l 26 ND 52
25-Jun-08 <1 <l <1 <1 1.46 58
10-Sep-08 10 <1 <1 14 10.5 71
15-0ct-08 3.9 <1 <1 6.6 9.82 89
4-Mar-09 <l <l <l <1 9.6 78
24-Jun-09 <l <1 <l <l 8.9 76
15-Sep-09 <1 <l <l <l 8.8 79
17-Dec-09 <1 <l <l <l 5.2 76
24-Feb-10 <1 <1 <1 <l 4.2 77
9-Jun-10 2.1 <l <l <l 4.7 64
24-Aug-10 4.3 <l <l <1 4.6 72
6-0ct-10 3 <l <l <l 3.3 72
22-Feb-ll 15 ND ND ND 7 86
26-May-ll 16 ND ND ND 5 81
17-Aug-11 9.2 ND ND ND 1.7 63
16-Nov-ll ND ND ND 1.4 0.4 38
18-Jan-12 ND ND ND 1.7 0.1 48
Chloroform Carbon Chlol'ometbane Methylene itrat €hloride TW4-16 (ug/l) T trachlorid (ug,'1) Chlorid (mg/I) (mg/I) (uS?ll) (ul?/1)
31-May-12 ND ND ND ND ND 53
30-Aug-12 ND ND ND ND ND 59
3-0ct-12 ND ND ND 3 ND 53
7-Feb-13 ND ND ND 3 ND 58 .1
30-May-13 ND ND ND 4.21 ND 49.8
5-Sep-13 ND ND ND ND ND 54.4
7-Nov-13 13.4 ND ND ND 1.37 56.6
29-Jan-14 6.9 ND ND ND 3.16 66.8
22-May-14 14.6 ND ND ND 4.94 80.7
14-Aug-14 229 ND ND ND 5.1 80
24-Sep-14 371 ND ND ND NIA NIA
29-0ct-14 387 ND ND ND 8.40 92.1
12-Mar-15 153 ND ND ND 4.30 65.3
11-Jun-15 65.3 ND ND ND 1.06 61
3-Sep-15 82 ND ND ND 1.18 65.8
28-0ct-15 112 ND ND ND 1.69 58.3
17-Mar-16 45.9 ND ND ND 1.63 56.5
26-May-16 93.4 ND ND ND 1.89 61.3
3-Aug-16 49 ND ND ND 2.20 60
26-0ct-16 92.9 ND ND ND 2.78 66.7
8-Mar-17 19.1 ND ND ND 2.75 62.2
20-Jun-17 64.3 ND ND ND 1.81 60.6
3-Aug-17 143 ND ND ND 2.63 67.1
ll-Oct-17 97.8 ND ND ND 2.12 54.2
20-Mar-18 170 ND ND ND 4.55 85.1
14-Jun-18 54.5 ND ND ND 2.83 62.5
30-Aug-18 54.5 ND ND ND 2.53 73.0
12-Dec-18 52.0 ND ND ND 2.88 68.8
19-Mar-19 60.6 ND ND ND 3.36 66.3
19-Jun-19 76.2 ND ND ND 2.43 71.5
12-Sep-19 99.8 ND ND ND 3.55 72.9
u,
CL)
:::s 'i >
E ...
0 -0 ...
.2 .c
0
co ,-
I
"1::1' 3: I-
0 0 (0
0 0 LO
0 0 (")
(1J6n)
0 0 C\I
0 0 .... 0
oi-unr-B~
L~-das-cc
v~-oaa-a
c ~ -JdV-~
60-1nr-9
go-ioo-o~
vo-uer-v~
,! ,., Cabon ~le 1
" Chloroform Ohloro ·;· .. itrate Chloride MWi-32 Tek ,oride eh! t·, (ug/1) tugM) (mg/I) (m,vl,
I {u,wl), €ue/ilt)
12-Sep-02 1.6 ND
24-Nov-02 ND ND
28-Mar-03 ND ND
23-Jun-03 ND ND
12-Sep-03 ND ND
8-Nov-03 ND ND
29-Mar-04 ND ND
22-Jun-04 ND ND
17-Sep-04 ND ND
17-Nov-04 ND ND
16-Mar-05 ND ND
30-Mar-05 ND ND
25-May-05 <1 NA NA NA <0.1 NA
31-Aug-05 <1 <1 3.2 <1 <0.1 NA
l-Dec-05 <1 <1 <l <1 <0.1 NA
9-Mar-06 <1 <1 <1 <1 <0.1 32
14-Jun-06 <1 <1 3.5 <1 <0.1 30
20-Jul-06 <1 <1 1.8 <1 <0.1 32
8-Nov-06 <1 <1 1.5 <1 <0.1 31
28-Feb-07 <1 <1 <1 <1 <0.1 32
27-Jun-07 <l <1 <l <1 <0.1 32
15-Aug-07 <1 <1 <1 <1 <0.1 31
10-0ct-07 <1 <1 <1 <1 <0.1 32
26-Mar-08 <1 <1 <1 <1 <0.1 31
25-Jun-08 <1 <1 <1 <1 <0.05 29
10-Sep-08 <1 <1 <1 <1 <0.05 30
15-0ct-08 <1 <1 <1 <1 <0.05 26
4-Mar-09 <1 <1 <1 <1 <0.1 30
24-Jun-09 <1 <1 <1 <1 <0.1 31
15-Sep-09 <1 <1 <1 <1 <0.1 33
16-Dec-09 <1 <1 <1 <1 <0.1 34
17-Feb-10 <1 <1 <1 <1 <0.1 38
14-Jun-10 <1 <1 <1 <1 <0.1 32
16-Aug-10 <1 <1 <1 <1 <0.1 28
6-0ct-10 <1 <1 <1 <1 <0.1 24
23-Feb-11 ND ND ND ND ND 40
25-May-11 ND ND ND ND ND 31
16-Aug-11 ND ND ND ND ND 33
6-Dec-11 ND ND ND ND ND 32
··'.r.JI .. i -Carbon Methylene 1
• :D !~· Chloroform Cbloromethane Nit te Chloride ~32 '&: 1:--(ug/1) Tetrachloride (ugll), Chlo11ide (mg/I) (mg{(~
D;,. ! (Ue/1) '(tie/I)
18-Jan-12 ND ND ND ND ND 21
4-Jun-12 ND ND ND ND ND 32
5-Sep-12 ND ND ND ND ND 33
10-0ct-12 ND ND ND ND ND 35
13-Feb-13 ND ND ND ND ND 34.3
18-Jun-13 ND ND ND ND ND 34.9
4-Sep-13 ND ND ND ND ND 33
29-0ct-13 ND ND ND ND ND 35.7
29-Jan-14 ND ND ND ND ND 34
23-May-14 ND ND ND ND ND 39.7
26-Aug-14 ND ND ND ND ND 34
29-0ct-14 ND ND ND ND ND 34.9
17-Mar-15 ND ND ND ND ND 36.3
ll-Jun-15 ND ND ND ND ND 35.8
9-Sep-15 ND ND ND ND ND 37.7
28-0ct-15 ND ND ND ND ND 34.7
22-Mar-16 ND ND ND ND ND 36.7
8-Jun-16 ND ND ND ND ND 37.2
17-Aug-16 ND ND ND ND ND 37.5
31-0ct-16 ND ND ND ND ND 36.9
21-Mar-17 ND ND ND ND ND 33.7
21-Jun-17 ND ND ND ND ND 37.2
4-Aug;-17 ND ND ND ND ND 38.1
12-0ct-17 ND ND ND ND ND 32.6
15-Mar-18 ND ND ND ND ND 39.4
14-Jun-18 ND ND ND ND ND 34.4
5-Sep-18 ND ND ND ND ND 41.2
29-0ct-18 ND ND ND ND ND 32.9
19-Mar-19 ND ND ND ND ND 35.3
18-Jun-19 ND ND ND ND ND 36.5
ll-Sep-19 ND ND ND ND ND 33.7
,-
(1J6n)
co
ci
co
ci
C\J
ci
oi-unr-B~
' ' ..
: ' . •
I • L~-das-cc
•
• • •
: .. •
•• •• :
••
I~ ••
•
•
'
' • 60-1nr-9
••
I .
'
• t
• • ••
'
' ' ... . .
~Q-Jd'v'-6 ~
0
l 'J ·. I Carbon Meth~lene
· 4 .. 1~ Chloro orm '', Tettaddoiide Cbl~romethane Chkmde Nftnte Chlo de
, _n.:,,"f (ug/1) 't~l ~ug/1) (uwi) (mg/I) (mg/I)
II
12-Sep-02 440 1.49
24-Nov-02 240 13.3
28-Mar-03 160 13.1
23-Jun-03 110 19
12-Sep-03 68.0 19.9
9-Nov-03 84.0 20.7
29-Mar-04 90.0 14
22-Jun-04 82.0 12.2
17-Sep-04 38.0 14.5
17-Nov-04 51.0 17.3
16-Mar-05 38.0 14.1
25-May-05 29.8 NA NA NA 12.9 NA
31-Aug-05 39 <1 2.8 <l 13.3 NA
1-Dec-05 14 <l 1.1 <l 7.3 NA
9-Mar-06 12.0 <l 1.1 <1 5.9 5.9
14-Jun-06 12.0 <l 1.6 <1 4.7 35
20-Jul-06 10.8 <l 2.7 <1 6.1 35
8-Nov-06 139 <1 <1 <1 8.7 34
28-Feb-07 9.2 <l <1 <1 5.1 30
27-Jun-07 8.0 <1 <1 <l 4.9 28
15-Aug-07 8.9 <1 <1 <1 5 32
10-0ct-07 7.4 <l <1 <l 4.4 27
26-Mar-08 6.4 <l <l <1 0.7 23
25-Jun-08 5.7 <l <l <1 4.55 23
10-Sep-08 8.0 <l <1 <l 4.68 26
15-0ct-08 9.4 <l <1 <1 5,15 30
4-Mar-09 11.0 <l <1 <l 5.2 29
24-Jun-09 16.0 <l <l <l 6.2 30
15-Sep-09 13.0 <l <1 <l 5.9 26
22-Dec-09 8.2 <1 <1 <l 5.4 30
24-Feb-10 69.0 <1 <l <l 5.1 41
9-Jun-10 29.0 <1 <1 <l 9 35
12-Aug-10 29.0 <1 <1 <l 9 37
13-0ct-10 30.0 <1 <l <1 10 50
22-Feb-l l 39.0 ND ND ND 10 52
26-May-ll 26.0 ND ND ND 9 36
17-Aug-ll 29.0 ND ND ND 4.6 23
7-Dec-11 28.0 ND ND ND 6.3 23
19-Jan-12 25.0 ND ND ND 4.4 18
. C~bon Meth1lene Chloroform l•L C.blnromet,bane· Nfttate Chloride TW4l8 1, Tetraebloride Chloride (ug/1) ,,. . (tiiflli (ug/1) '(uil/1) (lng/1) {mg/I)
13-Jun-12 24.0 ND ND ND 6.6 30
ll-Sep-12 38.0 ND ND ND 6.6 26
3-0ct-12 30.0 ND ND ND 6 27
13-Feb-13 34.9 ND ND ND 5.58 23.1
13-Jun-13 37.9 ND ND ND 8.86 22.9
5-Sep-13 41.0 ND ND ND 12.1 36.2
13-Nov-13 44.3 ND ND ND 14.2 37.1
30-Jan-14 38.9 ND ND ND 12.8 40.9
22-May-14 34.8 ND ND ND 12.2 47
14-Aug-14 32.8 ND ND ND 9.8 49
28-0ct-14 33.0 ND ND ND 11.1 40.8
12-Mar-15 32.0 ND ND ND 11.7 41.6
11-Jun-15 30.5 ND ND ND 9.69 43.5
3-Sep-15 28.7 ND ND ND 15.7 47.6
28-0ct-15 52.9 ND ND ND 6.24 39.4
17-Mar-16 56.6 ND ND ND 5.96 40.7
8-Jun-16 60.0 ND ND ND 5.43 43.8
3-Aug-16 56.3 ND ND ND 5.79 40.7
26-0ct-16 60.1 ND ND ND 5.24 43.9
16-Mar-17 62.0 ND ND ND 4.47 39.4
20-Jun-17 63.8 ND ND ND 4.5 41.6
3-Aug-17 62.8 ND ND ND 4.24 40.4
10-0ct-17 62.9 ND ND ND 4.43 37.1
15-Mar-18 62.3 ND ND ND 4.32 44.3
13-Jun-18 59.9 ND ND ND 4.09 39.5
30-Aug-18 56.2 ND ND ND 3.51 45.6
13-Dec-18 57.6 ND ND ND 3.60 38.2
19-Mar-19 52.8 ND ND ND 3.85 37.6
19-Jun-19 54.2 ND ND ND 4.01 39.5
11-Sep-19 56.2 ND ND ND 3.25 36.8
m :s ~
E "-~ .. ..2 .c 0
co ... I !
0 0 I!)
0 I!) s:t
-T
0 0 s:t
0 I!) ('I')
0 0 ('I')
0 I!) C\J
-
~
} .~ .
1
~ .
~ .
I,,. • • ~
.._.
\ ~
-;,
~ ••
'
' t ,
-
~
~ ~ {~
L--+-i--•
L--+' ~
0 0 C\J
(1J6n)
0 I!) .... 0 0 .... 0 I!) 0
oi-unr-B~
L~-das-cc
v~-oaa-a
50-1nr-9
90-PO-O~
vo-uer-v~
W-JdV-6 ~
,I Camo M , ...
Chloroform ro-.. . Nitl'ate Chloride 'I TW.4-19 T Id "de (rug/I~ Cblmiide (mg{.t)
I (~g/1) ~) ,(.llflil;) (lng/1)
12-Sep-02 7700 47.6
24-Nov-02 5400 42
28-Mar-03 4200 61.4
15-May-03 4700 NA
23-Jun-03 4500 11.4
15-Jul-03 2400 6.8
15-Aug-03 2600 4
12-Sep-03 2500 5.7
25-Sep-03 4600 9.2
29-0ct-03 4600 7.7
9-Nov-03 2600 4.8
29-Mar-04 NA NA
22-Jun-04 NA NA
16-Aug-04 7100 9.91
17-Sep-04 2600 4.5
17-Nov-04 1800 3.6
16-Mar-05 2200 5.3
25-May-05 1200 5.7
31-Aug-05 1400 <5 <5 <5 4.6 NA
1-Dec-05 2800 <50 <50 <50 <0.1 NA
9-Mar-06 1200 <50 <50 <50 4 86
14-Jun-06 1100 <50 <50 <50 5.2 116
20-Jul-06 1120 <50 <50 <50 4.3 123
8-Nov-06 1050 1.6 2.6 <1 4.6 134
28-Feb-07 1200 1.3 <1 <1 4 133
27-Jun-07 1800 2.3
15-Aug-07 1100 1.9 <1 <1 4.1 129
10-0ct-07 1100 1.9 <1 <1 4 132
26-Mar-08 1800 2.9 <1 <1 2.2 131
25-Jun-08 1000 1 <1 <1 2.81 128
10-Sep-08 3600 8.6 <1 <1 36.2 113
15-0ct-08 4200 12 <1 <1 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <1 2.4 132
15-Sep-09 6600 15 <1 <l 0.1 43
14-Dec-09 4700 16 <1 <l 26.7 124
17-Feb-10 940 1.3 <1 <l 2 144
9-Jun-10 1800 4.2 <l <1 4.4 132
16-Aug-10 2000 4.9 <l <I 5.9 142
Cblol'ofbrm Carbon Chl~romethane Methrlene NitraUt Chlo11ide "rW4-l9 Tetrachloride Ohlorlde
;, (ug/1) (ue/1) (ug/l) (ue/lJ (mg/I~ (m"1)
11-0ct-10 1200 1.3 <1 <l 2.7 146
17-Feb-ll 3400 17 ND ND 17 135
7-Jun-11 4000 8.3 ND ND 12 148
17-Aug-11 970 2.1 ND ND 3 148
5-Dec-11 2200 5.4 ND ND 5 148
23-Jan-12 650 1.5 ND ND 0.6 138
6-Jun-12 460 1.1 ND ND 2.4 149
5-Sep-12 950 3.5 ND ND 2.5 149
3-0ct-12 1500 4 ND ND 4.1 150
11-Feb-13 4210 5.15 ND ND 7.99 164
5-Jun-13 2070 5.15 ND ND 2.95 148
3-Sep-13 8100 20.7 ND ND 17.6 179
29-0ct-13 942 6.42 ND ND 4.7 134
27-Jan-14 586 4.05 ND ND 1.62 134
19-May-14 810 5.51 ND ND 1.34 152
11-Aug-14 1410 1.9 8.3 ND 1.6 140
21-0ct-14 4310 4.8 ND ND 4.72 130
9-Mar-15 4660 8.92 ND ND 8.56 238
8-Jun-15 1570 2.62 ND ND 0.916 180
4-Sep-15 7860 7.78 ND ND 11.6 326
19-0ct-15 7840 12.2 5.46 ND 10.6 252
9-Mar-16 7780 13.5 1.40 ND 15 .7 276
23-May-16 12600 23.1 ND ND 1.27 204
25-Jul-16 6040 9.89 ND ND 10.5 214
25-Jul-16 6040 9.89 ND ND 10.5 214
13-0ct-16 6640 10.8 ND ND 10.0 200
8-Mar-17 1240 3.06 ND ND 11.1 461
13-Jun-17 510 1.35 ND ND 0.243 135
26-Jul-17 8840 13.0 ND ND 1.12 218
l 1-0ct-17 129 ND ND ND 0.377 139
12-Mar-18 2640 1.36 ND ND 8.61 193
8-Jun-18 2980 3.45 ND ND 0.494 138
22-Aug-18 1910 2.03 ND ND 2.55 166
28-Nov-18 5270 6.18 ND ND 0.233 140
8-Mar-19 2050 2.43 ND ND 6.58 197
5-Jun-19 11500 15.90 ND ND 8.96 160
4-Sep-19 6670 10.10 ND ND 0.332 153
oi-unr-B~
vkoaa-a
U) c ~ -Jdy-~ CD :::s cii >
E ...
0 -0 ...
0 ::2 60-1nr-9
0
0) .,...
I oi::t' 3: t-
90-PO·O~
vo-uer-v~
~Q-JdV-6 ~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 '<I" C\J 0 co <D '<I" C\J ,.... ,.... ,....
(1J6n)
.. · ~ .11 . Carbon Methylene
TW.t:. 0
1 'Ciblorofonn TetrachlorJd ClliJoromethane C.hloride Nitrate €hloride
'ISi It
ug/1) (ue/1) ~ug/1~ (ue/ll (mg/l) ~mg/l) -25-May-05 39000 NA NA NA 10.1 NA
31-Aug-05 3800 <10 <10 <10 2.9 NA
l-Dec-05 19000 <250 <250 <250 1.8 NA
9-Mar-06 9200 <500 <500 <500 3.8 120
14-Jun-06 61000 <500 <500 <500 9.4 235
20-Jul-06 5300 <1000 <1000 <1000 2.9 134
8-Nov-06 11000 7.1 1.9 2.2 3.5 124
28-Feb-07 4400 3.1 <l 1.1 4.2 124
27-Jun-07 1800 2.2 <1 <1 2.3 112
15-Aug-07 5200 3.5 <1 1.8 2.1 117
10-0ct-07 9000 6.8 <1 1.9 5.6 170
26-Mar-08 13000 9 <1 1.5 0.9 132
25-Jun-08 30000 13 <1 1.2 7.96 191
10-Sep-08 21000 15 <1 3.7 4.44 156
15-0ct-08 NA NA NA NA 5.51 166
4-Mar-09 8200 5.7 <1 5.2 5.1 164
24-Jun-09 6800 4.9 <2 4.2 2.9 164
15-Sep-09 13000 8.4 <2 4.4 3.3 153
14-Dec-09 15000 14 <l 3 5.3 187
17-Feb-10 3500 2.7 <1 3.2 2 179
14-Jun-10 18000 11 <1 3.7 5.6 200
16-Aug-10 15000 12 <1 2.2 5.3 196
11-0ct-10 24000 20 <1 5.5 4.6 203
23-Feb-l 1 31000 27 ND 19 4.4 220
1-Jun-11 8100 10 ND 2.1 4.8 177
17-Aug-ll 6800 7.3 ND 3.1 6.5 207
16-Nov-11 7900 7.2 ND 2.5 4.2 186
23-Jan-12 11000 10 ND 1.3 7.9 207
6-Jun-12 36000 33 ND ND 11 262
4-Sep-12 13000 26 ND ND 10.8 289
3-0ct-12 19000 22 ND ND 11 302
11-Feb-13 18500 19.6 ND 1.21 9.07 252
5-Jun-13 26300 32.5 ND 1.13 9.76 250
3-Sep-13 26800 25.7 ND 2.14 8.65 260
29-0ct-13 15700 17.3 ND 1.37 9.64 272
27-Jan-14 17800 18.4 ND 2.04 7.56 254
19-May-14 22100 22.1 2.31 3.98 5.95 269
ll-Aug-14 12400 14.1 55.2 2.2 4.3 299
21-0ct-14 23300 18.5 4.04 2.38 7.67 292
.. .... Carbon Methylene r 'Cblol'Oform Chlorometbane itrate Chloride ~20 (ug/1) Tetrachloride (ug/1) Chloride ·(mg/l) (mg/I) ' Ill! (Uldl) ,(u24)
9-Mar-15 19900 20.8 4.85 1.38 9.8 290
8-Jun-15 17600 16.2 13.4 1.73 5.76 296
31-Aug-15 17000 15.1 12.3 ND 9.27 365
19-0ct-15 17000 14.5 10.8 1 6.23 293
9-Mar-16 21600 20.2 4.09 1.16 10.3 293
23-May-16 33700 40.6 ND ND 11.2 318
25-Jul-16 23600 26.6 ND ND 11.3 307
12-0ct-16 21300 24.4 ND ND 11.4 301
8-Mar-17 23400 23.5 ND ND 12 290
13-Jun-17 18100 23.4 ND ND 9.76 281
26-Jul-17 27600 25.0 ND ND 10.8 292
12-0ct-17 11600 11.2 2.34 ND 8.91 293
12-Mar-18 15400 15.9 1.77 2.36 9.5 289
14-Jun-18 12000 ND ND 7.77 10.4 258
22-Aug-18 10500 9.85 4.98 ND 8.14 282
28-Nov-18 9500 8.32 15.6 ND 9.72 295
8-Mar-19 15600 15.40 ND ND 6.70 272
5-Jun-19 13700 10.10 ND ND 9.59 279
4-Sep-19 10500 8.39 ND ND 10.2 286
v~-oaa-a
U) a, ::::,
«I >
E c ~ -Jd'v'-~ ... 0 -0 ... 0 ::c 0
0 N I
3: 60-1nr-9 ...
90-PO-O~
vo-uer-v~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 J'-. co U") '<:f" C") C\l
(1/6n)
Chloro.form C b Chf(ffi)lltethan • Meth tene Nitrate Chloride TW+-2 ~ Oitodde (ug/1) <H'fii (uglt) (mdli\ (mg/I) (mg/I}
25-May-05 192 NA NA NA 14.6 NA
31-Aug-05 78 <5 <5 <5 10.1 NA
l-Dec-05 86 <l 1.0 <l 9.6 NA
9-Mar-06 120 <2.5 <2.5 <2.5 8.5 347
14-Jun-06 130 <2.5 <2.5 <2.5 10.2 318
20-Jul-06 106 <2.5 <2.5 <2.5 8.9 357
8-Nov-06 139 2 <l <l 8.7 296
28-Feb-07 160 1.8 <l <l 8.7 306
27-Jun-07 300 5.8 <l <l 8.6 327
15-Aug-07 140 <l <1 <l 8.6 300
10-0ct-07 120 <l <1 <1 8.3 288
26-Mar-08 380 7 <1 <1 14.3 331
25-Jun-08 160 1.7 <1 <1 8.81 271
10-Sep-08 120 1.6 <1 <1 7.57 244
15-0ct-08 170 2 <l <2 8.00 284
11-Mar-09 180 <1 <1 <1 8.3 279
24-Jun-09 200 <1 <1 <l 8.1 291
15-Sep-09 140 <1 <1 <1 9.2 281
22-Dec-09 160 <1 <l <1 8.4 256
25-Feb-10 170 <l <1 <1 8.4 228
10-Jun-10 210 1.2 <1 <1 12 266
12-Aug-10 390 9.2 <1 <1 14 278
13-0ct-10 200 1.2 <1 <1 7 210
22-Feb-l l 230 1.2 ND ND 9 303
28-Jun-11 290 4.8 ND ND 12 290
17-Aug-11 460 6.3 ND ND 14 287
7-Dec-11 390 6.7 ND ND 13 276
19-Jan-12 420 6.4 ND ND 15 228
13-Jun-12 400 5.4 ND ND 11 285
13-Sep-12 410 6 ND ND 13 142
4-0ct-12 390 7 ND ND 14 270
13-Jan-13 282 5.25 ND ND 11.8 221
18-Jun-13 328 3.49 ND ND 13.8 243
12-Sep-13 244 2.13 ND ND 10.3 207
13-Nov-13 204 ND ND ND 9 206
5-Feb-14 220 6.23 ND ND 11.4 200
22-May-14 240 4.73 ND ND 11.5 243
27-Aug-14 204 ND ND ND 7.1 230
29-0ct-14 229 1.04 ND ND 10 252
€.hloroform Ca~bon ChlQromethane Methrle Nitrate Chlorld TW4·2 (ug'll) TetrachlorJde (ugtl) Chlo hi (mg/J) (mg/I) (ul!/D (ul!/1)
12-Mar-15 292 1.75 ND ND 10.9 255
8-Jun-15 366 1.92 ND ND 13.1 494
31-Aug-15 281 ND ND ND 14.7 499
19-0ct-15 339 ND ND ND 14.3 413
9-Mar-16 390 ND ND ND 14.6 452
23-May-16 545 ND ND ND 13.1 425
25-Jul-16 456 ND ND ND 16.5 457
12-0ct-16 434 ND ND ND 11.4 301
12-0ct-16 434 ND ND ND 11.4 301
8-Mar-17 598 2.36 ND ND 12.0 290
13-Jun-17 224 1.16 ND ND 9.53 309
26-Jul-17 537 1.05 ND ND 18.2 447
11-0ct-17 466 ND ND ND 16.9 378
12-Mar-18 421 ND ND ND 15.8 447
8-Jun-18 532 ND ND ND 14.1 387
22-Aug-18 476 ND ND ND 0.236 182
22-0ct-18 585 ND ND ND 15.2 392
8-Mar-19 323 ND ND ND 8.99 180
5-Jun-19 734 ND ND ND 17.5 456
4-Sep-19 596 ND ND ND 14.7 478
u,
Cl)
::::s
ca >
E ...
0 -0 ...
.2 .c
0 ,....
N I "'=t' 3:: I-
0 0 co
0 0 <O
0 0 LO
0 0 "<t"
(1J6n)
0 0 C".)
0 0 C\J
0 0
L~-das-cc
v~-oaa-a
G ~ -Jd'v'-~
60-1nr-9
90-PO·O~
0
C b --&. le 1'Ch10.ride <tlenn· ....., . --Nitrate • -ilL ... •'-TW4-'.22 ~ radii • . ' Qglj) (~ -----(mg/I) ~mgll) {,-IJ) (utrJI)
25-May-05 340 NA NA NA 18.2 NA
31-Aug-05 290 <5 <5 <5 15.7 NA
l-Dec-05 320 <5 <5 <5 15.1 NA
9-Mar-06 390 <10 <10 <10 15.3 236
14-Jun-06 280 <10 <10 <10 14.3 221
20-Jul-06 864 <10 <10 <10 14.5 221
8-Nov-06 350 <1 1.6 <l 15.9 236
28-Feb-07 440 <1 <l <l 20.9 347
27-Jun-07 740 <1 <l <l 19.3 273
15-Aug-07 530 <1 <l <l 19.3 259
10-0ct-07 440 <1 <1 <1 18.8 238
26-Mar-08 1400 <I <l <l 39.1 519
25-Jun-08 1200 <l <1 <1 41.9 271
IO-Sep-08 6300 1.3 <l <I 38.7 524
15-0ct-08 630 <2 <2 <2 36.3 539
11-Mar-09 390 <1 <l <I 20.7 177
24-Jun-09 730 <1 <I <1 20.6 177
15-Sep-09 2300 <1 <1 <1 40.3 391
29-Dec-09 380 <I <I <1 17.8 175
3-Mar-10 2200 <1 <I <1 36.6 427
15-Jun-10 540 <1 <1 <1 19 134
24-Aug-10 340 <l <l <I 15 130
13-0ct-10 340 <1 <l <1 16 134
23-Feb-11 1300 ND ND ND 18 114
1-Jun-11 210 ND ND ND 17 138
17-Aug-11 450 ND ND ND 15 120
7-Dec-11 400 ND ND ND 19 174
19-Jan-12 200 ND ND ND 14 36
13-Jun-12 120 ND ND ND 12.8 35
12-Sep-12 940 ND ND ND 7 121
4-0ct-12 330 ND ND ND 14 130
11-Feb-13 10600 3.24 ND ND 58 635
5-Jun-13 12500 3.35 ND ND 50.2 586
3-Sep-13 9640 3.25 ND ND 29.7 487
29-0ct-13 13300 8.09 ND ND 45.2 501
27-Jan-14 12100 6.06 ND 2.83 54.6 598
19-May-14 12400 6.65 ND ND 47.2 614
11-Aug-14 12400 1.9 40 ND 41.5 540
21-0ct-14 12400 3.32 1.61 ND 54.9 596
C o oform C rbi;m Chloromethane Methylene Nitrat <Chloride TW4-,,22 (ugll) Tetraehlorid (ug/J) Chloride (mg!l) (mg/I) (u2'1) ,112'1)
9-Mar-15 12700 3.77 4.31 ND 69.2 675
8-Jun-15 8050 2.42 3.42 ND 47.1 390
31-Aug-15 7810 ND 5.47 ND 64.7 557
19-0ct-15 7530 ND 5.1 ND 56.1 567
9-Mar-16 6070 ND ND ND 31.1 583
23-May-16 8570 2.64 ND ND 58.4 598
25-Jul-16 5840 ND ND ND 61.3 619
12-0ct-16 3370 1.08 ND ND 61.5 588
8-Mar-17 5320 1.56 ND ND 69.8 566
13-Jun-17 3670 1.21 ND ND 70.8 572
26-Jul-17 5150 ND ND ND 66.1 391
ll-Oct-17 4770 ND ND ND 80.1 600
12-Mar-18 4530 ND ND ND 62.3 607
8-Jun-18 3010 ND ND ND 72.5 580
22-Aug-18 3600 ND ND ND 55.4 613
28-Nov-18 2680 ND ND ND 75.7 567
8-Mar-19 4310 1.02 ND ND 71.9 528
5-Jun-19 4690 ND 1.13 ND 83.9 662
4-Sep-19 3460 ND ND ND 72.5 588
L~-das-c::c::
v~-oaa-a
ti)
G) :::,
«I >
E ..
2: ~ -Jd'v'-~ 0 -0 ..
0 ::c
0
N N I
111::1'
== I-
60-1nr-9
90-lOQ-O~
vo-uer-v~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
""" C\J 0 00 co """ C\J ..... .....
(1J6n)
' Carboo Mflhyfae I'-Chlo pfoJ'JII Chlarometbane Nitrate Oi(9ride
II :'l'.W¢-23 (ug/il) 1"~-(u~) Chloride (mwo {mg/I~
' .,llf!A) tmrill),
27-Jun-07 <1 <1 <1 <1 <0.1 47
15-Aug-07 <1 <1 <1 <1 <0.1 46
10-0ct-07 <1 <1 <1 <1 <0.1 43
26-Mar-08 <1 <1 <1 <1 <0.1 41
25-Jun-08 <1 <1 <1 <1 <0.05 41
10-Sep-08 <1 <1 <1 <1 <0.05 35
15-0ct-08 <2 <2 <2 <2 <0.05 51
4-Mar-09 <1 <1 <1 <1 <0.1 41
24-Jun-09 <1 <1 <1 <1 <0.1 43
15-Sep-09 <1 <1 <1 <1 <0.1 43
16-Dec-09 <1 <1 <1 <1 <0.1 37
24-Feb-IO <1 <1 <1 <1 <0.1 45
8-Jun-IO <1 <1 <1 <1 <0.1 40
IO-Aug-IO <1 <1 <1 <1 <0.1 40
5-0ct-IO <1 <1 <1 <1 <0.1 34
16-Feb-11 ND ND ND ND ND 44
25-May-11 ND ND ND ND ND 44
16-Aug-ll ND ND ND ND ND 41
15-Nov-11 ND ND ND ND ND 43
17-Jan-12 ND ND ND ND ND 40
31-May-12 ND ND ND ND ND 44
29-Aug-12 ND ND ND ND ND 46
3-0ct-12 ND ND ND ND ND 45
7-Feb-13 ND ND ND ND ND 43.6
30-May-13 ND ND ND ND 0.116 44.7
5-Sep-13 ND ND ND ND ND 48.0
7-Nov-13 ND ND ND ND ND 43.0
23-Jan-14 ND ND ND ND ND 44.6
21-May-14 ND ND ND ND ND 42.3
13-Aug-14 ND ND ND ND ND 46.0
28-0ct-14 ND ND ND ND ND 46.8
12-Mar-15 ND ND ND ND ND 47.3
IO-Jun-15 ND ND ND ND ND 48.4
3-Sep-15 ND ND ND ND ND 54.1
28-0ct-15 ND ND ND ND ND 46.4
16-Mar-16 ND ND ND ND ND 49.1
26-May-16 ND ND ND ND ND 50.4
3-Aug-16 ND ND ND ND ND 49.6
20-0ct-16 ND ND ND ND ND 52.1
Chlo11oform C rbon Chlo~omethane Methylene Nitrate Chloride TW4-23 (ugll~ Tetrachlorlde uw'I) Chloride {~g/1) (mgll) <wun (oil.II~
15-Mar-17 ND ND ND ND ND 47.7
15-Jun-17 ND ND ND ND ND 51.5
2-Aug-17 ND ND ND ND ND 51.8
10-0ct-17 ND ND ND ND ND 44.7
14-Mar-18 ND ND ND ND ND 53.8
13-Jun-18 ND ND ND ND ND 47.6
30-Aug-18 ND ND ND ND ND 56.0
12-Dec-18 ND ND ND ND ND 54.9
16-Mar-19 ND ND ND ND ND 48.9
13-Jun-19 ND ND ND ND ND 50.2
11-Sep-19 ND ND ND ND ND 47.9
Jun-07
Sep-07
Dec-07
Mar-OB
Jun-OB
Sep-OB
Dec-OB
Mar-09
Jun-09
Sep-09
Dec-09
Mar-10
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
Sep-16
Dec-16
Mar-17
Jun-17
Sep-17
Dec-17
Mar-1B
Jun-1B
Sep-1B
Dec-1B
Mar-19
Jun-19
Sep-19
0
.i
0
I
l
' ' .
I
1
1
1
l •
H
j.
4
j.
j
•
.i
.i. 4.
.i•
l •
1
0
0
.i. .i. i•
' .
' .
1 •
1• .i.
i• ••
'
I .i. i•
,.
••
l
H ~• 1• .
0 0 0 0
(ug/L)
0 =r
0
"""' 0 -0
"""' 3
=r
Sl)
(/)
::J
0 -O" CD
CD
::J
0..
CD -CD (') -CD
0..
::J
-I :E ~ I
I\) w
...... ......
~ ~ ~ w
0 ::T o ..
0 0 .. 3
~ c CD rn
ChlorefonQ Carbo Othwometbarne Methylene Nitrate -· -···-
TW4-24 1 l'aeklolide Chloride '1.JIIUI .._ ..
I (ug/1) (u,g/1) (mg/I) (mgj)
1, (~) (uwl)
27-Jun-07 2.6 <1 <1 <1 26.1 770
15-Aug-07 2.2 <1 <1 <1 29 791
10-0ct-07 1.5 <1 <1 <1 24.7 692
26-Mar-08 1.5 <l <l <1 24.4 740
25-Jun-08 1.4 <l <1 <1 45.3 834
10-Sep-08 2.9 <1 <l <l 38.4 1180
15-0ct-08 <2 <2 <2 <2 44.6 1130
4-Mar-09 1.4 <1 <1 <l 30.5 1010
24-Jun-09 1.5 <1 <l <1 30.4 759
15-Sep-09 1.4 <1 <1 <1 30.7 618
17-Dec-09 1.2 <1 <1 <1 28.3 1080
25-Feb-10 1.3 <l <l <1 33.1 896
9-Jun-10 1.7 <1 <1 <1 30 639
24-Aug-10 1.8 <l <l <1 31 587
6-0ct-10 1.4 <1 <1 <1 31 522
17-Feb-ll 1.8 ND ND ND 31 1100
26-May-l l 1.1 ND ND ND 35 1110
17-Aug-11 1.7 ND ND ND 34 967
7-Dec-11 1.2 ND ND ND 35 608
18-Jan-12 ND ND ND ND 37 373
6-Jun-12 ND ND ND ND 37 355
30-Aug-12 1.1 ND ND ND 37 489
3-0ct-12 1.0 ND ND ND 38 405
ll-Feb-13 5.7 ND ND ND 35.9 1260
5-Jun-13 17.4 ND ND ND 23.7 916
3-Sep-13 21.8 ND ND ND 32.6 998
29-0ct-13 32.5 ND ND ND 34.6 1030
27-Jan-14 78.5 ND ND 1.18 31.6 809
19-May-14 62.7 ND ND ND 35 1020
l l-Aug-14 76.3 ND ND ND 31.5 1150
21-0ct-14 25.8 ND ND ND 35.7 1050
9-Mar-15 49.2 ND ND ND 34.6 944
8-Jun-15 4.3 ND ND ND 31.8 1290
31-Aug-15 46.9 ND ND ND 25.3 788
19-0ct-15 25.3 ND ND ND 29.6 909
9-Mar-16 22.8 ND ND ND 29.1 989
23-May-16 69.6 ND ND ND 24.2 771
25-Jul-16 17.8 ND ND ND 34.4 1180
12-0ct-16 20.8 ND ND ND 31.9 1010
'" Carbon Methylene I Ohloroor,m Chlo.rometbane Nitrate Chloride TW4•24 Tetrachloride €hlo~ide (Ug/1) fiue/1) (ug/1) (ue/1) (mg/I) (mg/I)
I ' 8-Mar-17 18.3 ND ND ND 41.3 1090
13-Jun-17 17.2 ND ND ND 39.9 1080
26-Jul-17 17 .8 ND ND ND 40.0 1230
l l-Oct-17 16.0 ND ND ND 31.7 895
12-Mar-18 24.9 ND ND ND 44.9 1320
14-Jun-18 49.2 ND ND ND 33.6 792
22-Aug-18 35.0 ND ND ND 33.8 996
28-Nov-18 21.0 ND ND ND 38.4 1100
8-Mar-19 28.1 ND ND ND 39.3 1040
5-Jun-19 28.8 ND ND ND 33.2 1020
4-Sep-19 31.1 ND ND ND 36.4 1130
(ug/L)
I-" N OJ .i,. V, Cl ......, 00 I.Cl 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0
10-0ct-06
22-Feb-08
6-Jul-09
18-Nov-10
~f ~ I I I I I I I I ~ .,::a.
1-Apr-12 i I \ I I I I I I I N .,::a.
n ~
0 ..,
0 -0
14-Aug-13 1 I \'h-___ I I I I I I I ..,
3
< I» c tD Ill 1 I I \ +«=l::: I I I 1 ~ I I 27-Dec-14
10-May-16
22-Sep-17
4-Feb-19
18-Jun-20 -'-----'------'----.1..-----'---_1----L----...1..._----1..--_1
·-· Carbo MdlJlen Chlorofonn Chle o ethane Nitrate Chloride TW4-15 (ug/1) Tetraclll ride (ugm ChlGrid (mg/I) (mg/I) ..a (.uell) (ud)
27-Jun-07 <1 <1 <1 <1 17.1 395
15-Aug-07 <1 <1 <1 <1 16.7 382
10-0ct-07 <I <1 <1 <1 17 356
26-Mar-08 <I <1 <1 <1 18.7 374
25-Jun-08 <I <1 <1 <1 22.1 344
10-Sep-08 <I <1 <1 <1 18.8 333
I5-0ct-08 <2 <2 <2 <2 21.3 366
4-Mar-09 <1 <1 <1 <1 15.3 332
24-Jun-09 <1 <1 <1 <1 15.3 328
15-Sep-09 <1 <1 <1 <1 3.3 328
16-Dec-09 <l <1 <1 <l 14.2 371
23-Feb-10 <l <1 <1 <l 14.4 296
8-Jun-10 <1 <l <1 <l 16 306
10-Aug-10 <1 <1 <l <1 14 250
5-0ct-10 <1 <1 <1 <1 15 312
16-Feb-ll ND ND ND ND 15 315
25-May-11 ND ND ND ND 16 321
16-Aug-ll ND ND ND ND 16 276
15-Nov-l l ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 ND ND ND ND 16 287
ll-Sep-12 ND ND ND ND 17 334
3-0ct-12 ND ND ND ND 17 338
ll-Feb-13 ND ND ND ND 9.04 190
5-Jun-13 ND ND ND ND 5.24 136
3-Sep-13 ND ND ND ND 5.69 119
29-0ct-13 ND ND ND ND 6.1 88.6
27-Jan-14 ND ND ND ND 2.16 85.7
19-May-14 ND ND ND ND 1.21 51.1
1 l-Aug-14 ND ND ND ND 1.6 67
21-0ct-14 ND ND ND ND 1.03 58.1
9-Mar-15 ND ND ND ND 14.4 310
8-Jun-15 ND ND ND ND 1.14 58.3
31-Aug-15 ND ND ND ND 1.63 69.2
21-0ct-15 ND ND ND ND 1.78 93.7
9-Mar-16 ND ND ND ND 0.837 62.7
23-May-16 ND ND ND ND 0.959 75.5
25-Jul-16 ND ND ND ND 1.78 74.1
12-0ct-16 ND ND ND ND 1.24 59.8
!J: T Chloi,oform Carbon Chloromethane Methylene Nitrate Chloride 4-ZS (ug/1) TetraeJ(lorlde (ug/1) Ohlorlde (mg/I) (mgll) \\ -{'u!/1) (uS!'/1)
8-Mar-17 1 ND ND ND 17 285
13-Jun-17 ND ND ND ND 0.976 69.8
26-Jul-17 ND ND ND ND 1.23 70.1
ll-Oct-17 ND ND ND ND 1.29 68.0
12-Mar-18 ND ND ND ND 2.23 70.5
14-Jun-18 ND ND ND ND 1.14 60.3
22-Aug-18 ND ND ND ND 0.810 69.1
28-Nov-18 ND ND ND ND 0.634 59.7
8-Mar-19 ND ND ND ND 0.639 65.0
5-Jun-19 ND ND ND ND 0.821 59.0
4-Sep-19 ND ND ND ND 0.548 58.1
Jun-07
Sep-07
Dec-07
Mar-08
Jun-08
Sep-08
Dec-08
Mar-09
Jun-09
Sep-09
Dec-09
Mar-10
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
Sep-16
Dec-16
Mar-17
Jun-17
Sep-17
Dec-17
Mar-18
Jun-18
Sep-18
Dec-18
Mar-19
Jun-19
Sep-19
0
l • • ,. ~.
11
I
,.
l
' .
l •
_j. ·~ i• •
.i.
.i. j.
i• ••
_j.
1 •
j ~
••
l
• j.
i• ••
••
•• j.
••
••
l~ ••
.
••
1• 1• i• i•
••
••
l
(ug/L)
0 0 ......
0
::J"'
0 ~ 0 -h 0
~
3
::J"'
!l)
(/)
:::J
0 -C'"
CD
CD
:::J
a.
CD -CD ("') -CD a.
:::J
--1 ~ ~ I
I\)
CJ1
-
~ ~ I N UI
0 :::r
0 ""I 0 -0 ""I 3
< !!.
C (D en
Chi efoffll C ho Ohlor. .. l'lethykme Nitrate Chlorld TW4-26 Te cblo · e ChJor.ide (ug/1) {W!R) (u ) (usr/U (mg/I) (mgl,li)
15-Jun-10 13 <1 <l <1 7.9 33
1 l-Aug-10 5 <1 <l <1 9 17
6-0ct-10 5.4 <l <1 <1 9.6 22
22-Feb-11 2.0 ND ND ND 10 30
26-May-11 2.9 ND ND ND 10 15
17-Aug-1 l 2.8 ND ND ND 11 19
7-Dec-11 5.2 ND ND ND 10 26
18-Jan-12 7.0 ND ND ND 11 17
6-Jun-12 4.1 ND ND ND 12 19
11-Sep-12 4.9 ND ND ND 9 19
3-0ct-12 6.0 ND ND ND 12 19
7-Feb-13 5.0 ND ND ND 12.5 16.6
13-Jun-13 2.1 ND ND ND 13.6 14.5
5-Sep-13 2.8 ND ND ND 11.7 17.6
7-Nov-13 3.4 ND ND ND 15.9 15.9
29-Jan-14 1.4 ND ND ND 14.2 16.9
21-May-14 4.2 ND ND ND 12.5 15.4
ll-Aug-14 1.3 ND ND ND 10.8 15
28-0ct-14 2.45 ND ND ND 12.3 14.6
12-Mar-15 2.37 ND ND ND 14.4 14.4
10-Jun-15 6.12 ND 1.17 ND 11.3 14.4
3-Sep-15 4.77 ND ND ND 14.2 14.0
28-0ct-15 3.45 ND ND ND 13.9 13.3
16-Mar-16 1.80 ND ND ND 16.9 13.7
26-May-16 8.23 ND ND ND 15.2 13.9
3-Aug-16 4.42 ND ND ND 17.9 13.9
20-0ct-16 19.9 ND ND ND 15.0 14.2
16-Mar-17 46.1 ND ND ND 15.8 16.2
20-Jun-17 244 ND ND ND 15.2 19.0
3-Aug-17 419 ND ND ND 15.2 25.8
11-0ct-17 608 ND ND ND 10.0 27.3
21-Mar-18 1050 ND ND ND 12.2 35.5
14-Jun-18 960 ND ND ND 13.2 33.5
5-Sep-18 916 ND ND ND 13.5 38.9
13-Dec-18 1050 ND ND ND 11.8 33.4
20-Mar-19 963 ND ND ND 12.2 32.9
19-Jun-19 1070 ND ND ND 12.6 35.8
12-Sep-19 877 ND ND ND 10.9 32.0
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
Sep-16
Dec-16
Mar-17
Jun-17
Sep-17
Dec-17
Mar-18
Jun-18
Sep-18
Dec-18
Mar-19
Jun-19
N 0 0 0
.i,. 0 0
(ug/1)
0)
0 0
00 0 0
....
0 0 0
....
N 0 0
i ~ I N en n :::r 0 ...
a-...
3
< OJ
C: 11)
Ill
Chloroform Cartio O .. _-~uDe M-e.$)1 1trate Chloride TW4-27 Tew--'-"--'d (,ug/1) (utilll (uwl) Chlm"i (og:AI) (mg/I) (mg/I)
24-Jan-12 9 ND ND ND 24 11
13-Jun-12 ND ND ND ND 41 17
30-Aug-12 ND ND ND ND 37 21
3-0ct-12 ND ND ND ND 36 18
7-Feb-13 ND ND ND ND 31.2 18.8
30-May-13 ND ND ND ND 29.4 20.3
29-Aug-13 ND ND ND ND 27.2 19
6-Nov-13 ND ND ND ND 29.8 21.8
23-Jan-14 ND ND ND ND 31.3 21.8
21-May-14 ND ND ND ND 31.1 20.6
13-Aug-14 ND ND ND ND 27.0 23
23-0ct-14 ND ND ND ND 28.2 24.4
ll-Mar-15 ND ND ND ND 26.5 26.2
10-Jun-15 ND ND ND ND 24.0 26.8
2-Sep-15 1.30 ND ND ND 20.9 26.8
28-0ct-15 1.60 ND ND ND 23.5 26.2
16-Mar-16 2.11 ND ND ND 25.0 28.0
26-May-16 3.16 ND ND ND 21.2 28.7
3-Aug-16 2.78 ND ND ND 21.8 27.1
20-0ct-16 3.80 ND ND ND 19.3 29.4
15-Mar-17 4.33 ND ND ND 22.2 28.3
15-Jun-17 5.65 ND ND ND 23.8 27.9
2-Aug-17 6.05 ND ND ND 20.0 29.5
10-0ct-17 5.91 ND ND ND 21.5 26.3
14-Mar-18 6.95 ND ND ND 19.5 30.3
13-Jun-18 5.95 ND ND ND 22.0 28.3
30-Aug-18 7.32 ND ND ND 18.1 31.4
12-Dec-18 7.70 ND ND ND 20.8 28.2
16-Mar-19 6.54 ND ND ND 21.5 26.2
13-Jun-19 8.24 ND ND ND 22.3 28.6
11-Sep-19 7.58 ND ND ND 21.2 25.3
Ill a,
:l
"' >
E ...
.2 0 ... ..2 .t:. u
" N I ~ ~
(1/Sn)
Chloroform Ca fum Chlo om.ethane Methylene Nitrate C oride TW4-28 (Ug/1) Tetrachloride (ug,'Q Chloride (mg/I} (DWI) (uelt) (u2/t)
19-Jun-13 ND ND ND ND 14.9 44.6
29-Aug-13 ND ND ND ND 17.3 45.3
6-Nov-13 ND ND ND ND 16.2 45.2
22-Jan-14 ND ND ND ND 16.9 47.8
21-May-14 ND ND ND ND 16.5 45.7
13-Aug-14 ND ND ND ND 14.2 50
23-0ct-14 ND ND ND ND 16.5 52.1
l 1-Mar-15 ND ND ND ND 19 52.2
10-Jun-15 ND ND ND ND 19 56.4
2-Sep-15 ND ND ND ND 17.8 61.4
21-0ct-15 ND ND ND ND 18.7 52.7
15-Mar-16 ND ND ND ND 34.0 61.6
25-May-16 ND ND ND ND 29.0 67.1
27-Jul-16 ND ND ND ND 31.3 70.1
19-0ct-16 ND ND ND ND 25.5 70.9
14-Mar-17 ND ND ND ND 24.4 64.2
14-Jun-17 ND ND ND ND 26.0 68.6
27-Jul-17 ND ND ND ND 24.8 67.1
10-0ct-17 ND ND ND ND 24.8 57.4
14-Mar-18 ND ND ND ND 17.2 65.0
12-Jun-18 ND ND ND ND 19.0 55.7
29-Aug-18 ND ND ND ND 16.0 63.8
30-Nov-18 ND ND ND ND 17.7 52.4
16-Mar-19 ND ND ND ND 17.2 51.7
13-Jun-19 ND ND ND ND 15.0 51.8
11-Sep-19 ND ND ND ND 10.2 49.0
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
Sep-16
Dec-16
Mar-17
Jun-17
Sep-17
Dec-17
Mar-18
Jun-18
Sep-18
Dec-18
Mar-19
Jun-19
Sep-19
0
0
0
0
0
i•
•
•
•
• •
• • •
••
't
•• ••
0
0
0
0 ..
0
'~
0
(ug/L)
0 0 0 0
()
~ -0 ~ 0 ......
0
~ 3
~
Sl)
CJ)
:::::,
0 ,-+
C"'
CD
CD :::::,
a.
CD ,-+
CD (")
,-+
CD a.
:::::,
-i ~ .i::..
I
I\)
CX>
...... ......
i I N Q)
0 =r
0 ""I ~ ""I 3
~
C:
(I) u,
Chloroform Cariacm Chloromethane Methylene ~itrate Chloride TW4-l9 'f.e'tracbleride Chloride (ug11) (ue/.1}, (ug/1) (utlll, (mg/I) (mg/I)
19-Jun-13 242 ND ND ND 4.63 44.8
ll-Jul-13 262 ND ND ND 3.52 37.7
26-Sep-13 246 ND ND ND 4.18 41.4
13-Nov-13 260 ND ND ND 4.11 42.5
5-Feb-14 258 ND ND ND 4.63 41.9
22-May-14 262 ND ND ND 3.52 38.2
27-Aug-14 242 ND ND ND 3.4 41
29-0ct-14 290 ND ND ND 3.64 41
12-Mar-15 299 ND ND ND 4.14 40.5
11-Jun-15 329 ND ND ND 2.95 42.5
3-Sep-15 276 ND ND ND 2.19 47.3
29-0ct-15 631 ND ND ND 2.74 39.8
17-Mar-16 335 ND ND ND 2.92 40.3
8-Jun-16 366 ND ND ND 2.51 42.9
4-Aug-16 401 ND ND ND 2.44 40.6
26-0ct-16 392 ND ND ND 2.4 44.2
16-Mar-17 446 ND ND ND 2.24 41.5
21-Jun-17 420 ND ND ND 2.26 42.0
4-Aug-17 466 ND ND ND 2.35 42.9
l l-Oct-17 466 ND ND ND 2.45 37.7
21-Mar-18 533 ND ND ND 2.44 43.1
14-Jun-18 474 ND ND ND 2.67 40.1
5-Sep-18 454 ND ND ND 2.52 45.9
13-Dec-18 521 ND ND ND 2.50 40.9
20-Mar-19 507 ND ND ND 2.67 39.9
19-Jun-19 537 ND ND ND 2.56 39.4
12-Sep-19 549 ND ND ND 2.55 38.0
Jun-13 Jul-13 Aug-13 SeP.-13 Oct-13 Nov-13 Dec-13 Jan-14 Feb-14 Mar-14
Apr-14.
Ma~-14 Ju -14 Ju -14 Aug-14 Sep-14 Oct-14 Nov-14 Dec-14 Jan-15 Feb-15 Mar-15 Apr-15
Ma~-15 Ju -15 Ju -15
Au~-15 Se -15 0 -15 Nov-15 Dec-15 Jan-16 Feb-16 Mar-16 Apr-16
Ma~-16 Ju -16 Ju -16 Aug-16 SeP.-16 Oct-16 Nov-16 Dec-16 Jan-17 Feb-17 Mar-17 Apr-17 May-17 Jun-17 Jul-17 Aug-17 SeP.-17 Oct-17 Nov-17 Dec-17 Jan-18 Feb-18 Mar-18 Apr-18
Ma~·-18 Ju -18 Ju -18 Aug-18 SeP.-18 Oct-18 Nov-18 Dec-18 Jan-19 Feb-19 Mar-19 Apr-19 May-19 Jun-19 Jul-19 Aug-19 Sep-19
0
..... 0 0
N 0 0
w 0 0
(ug/1) .,.
0 0
l/1 0 0
en 0 0
-.J 0 0
i .i::. I N ID n ::J"
0 ... 0 o' ...
3
< QI c ID Ill
" .. Car.bon Methylene Ch1oroform Chloromethane Nitrate Chloride TW 30 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) ~mgll) (mun (ullll)
19-Jun-13 ND ND ND ND 0.948 36
29-Aug-13 ND ND ND ND 0.952 36.3
7-Nov-13 ND ND ND ND 1.24 35.9
23-Jan-14 ND ND ND ND 1.36 36
21-May-14 ND ND ND ND 1.44 31.99
13-Aug-14 ND ND ND ND 1.5 38
23-0ct-14 ND ND ND ND 1.84 37.1
11-Mar-15 1.65 ND ND ND 2.15 38.3
10-Jun-15 2.25 ND ND ND 1.75 40.3
3-Sep-15 3.27 ND ND ND 1.75 44.2
28-0ct-15 3.48 ND ND ND 1.86 37.8
17-Mar-16 5.16 ND ND ND 2.74 39.6
26-May-16 7.38 ND ND ND 2.04 40.2
3-Aug-16 6.79 ND ND ND 2.32 38.6
20-0ct-16 8.69 ND ND ND 2.51 41.3
15-Mar-17 13.6 ND ND ND 2.7 37.7
15-Jun-17 15.2 ND ND ND 2.95 37.8
3-Aug-17 15.7 ND ND ND 3.11 39.8
10-0ct-17 13.4 ND ND ND 2.58 34.9
15-Mar-18 16.4 ND ND ND 3.63 41.0
13-Jun-18 16.9 ND ND ND 3.93 37.4
30-Aug-18 19.8 ND ND ND 3.79 44.1
12-Dec-18 23.9 ND ND ND 3.70 35.5
16-Mar-19 25.3 ND ND ND 4.08 35.9
13-Jun-19 31.5 ND ND ND 4.13 27.2
11-Sep-19 34.8 ND ND ND 3.62 34.5
0
Cl
Jun-13
Aug-13
Oct-13
Dec-13
Feb-14
Apr-14
Jun-14
Aug-14
Oct-14
Dec-14
Feb-15
Apr-15
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
Oct-16
Dec-16
Feb-17
Apr-17
Jun-17
Aug-17
Oct-17
Dec-17
Feb-18
Apr-18
Jun-18
Aug-18
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
01
Cl
......
0 Cl
(ug/L)
......
01
Cl
I\)
0 Cl
I\)
01 Cl
w 0 Cl
w 01 Cl
.i::,. 0 Cl
i I w 0
0 =r
0 ... 0 -0 ...
3
< !. C: (I) en
Chloroform C r.llon Cid (i)ffletha e Metbyl}e Nitrate Chloride TW4•31 (ug/1) Tetr chwllkle (ug/1) Ch orkle (mg/I) (mg/.)) (111Uli) (hwf.}
19-Jun-13 ND ND ND ND 1.26 28.4
5-Sep-13 ND ND ND ND 1.1 29.4
7-Nov-13 ND ND ND ND 1.33 28
23-Jan-14 ND ND ND ND 1.32 28.5
21-May-14 ND ND ND ND 1.22 26.3
13-Aug-14 ND ND ND ND 1.1 30
28-0ct-14 ND ND ND ND 1.23 30
1 l-Mar-15 ND ND ND ND 1.33 30.6
10-Jun-15 ND ND ND ND 1.19 31.1
2-Sep-15 ND ND ND ND 0.916 30.4
21-0ct-15 ND ND ND ND 0.953 29.1
16-Mar-16 ND ND ND ND 1.84 31.5
25-May-16 ND ND ND ND 1.36 32.5
28-Jul-16 ND ND ND ND 1.41 30.6
20-0ct-16 ND ND ND ND 1.14 34.0
15-Mar-17 ND ND ND ND 1.19 31.3
15-Jun-17 ND ND ND ND 1.21 33.4
2-Aug-17 ND ND ND ND 1.11 33.0
10-0ct-17 ND ND ND ND 1.04 30.9
14-Mar-18 ND ND ND ND 0.916 38.8
12-Jun-18 ND ND ND ND 0.948 34.4
29-Aug-18 ND ND ND ND 0.710 40.3
12-Dec-18 ND ND ND ND 0.766 35.2
16-Mar-19 ND ND ND ND 0.754 35.0
13-Jun-19 ND ND ND ND 0.713 36.9
1 l-Sep-19 ND ND ND ND 0 .610 35.8
Jun-13
Aug-13
Oct-13
Dec-13
Feb-14
Apr-14
Jun-14
Aug-14
Oct-14
Dec-14
Feb-15
Apr-15
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
Oct-16
Dec-16
Feb-17
Apr-17
Jun-17
Aug-17
Oct-17
Dec-17
Feb-18
Apr-18
Jun-18
Aug-18
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
0
••
••
0
'.
0
0
0
0
0
0
0
0
j
0
0
~
i•
i•
~
•
•
••
••
•
•
•
(ug/L)
0 0 0 0
0
:::J"'
0
"""I: 0 ...... 0 """I: 3
:::J"'
Q) en
::::I
0 -C'"
CD
CD ::::I
a.
CD -CD
(') -CD a.
::::I
-f :E ~ I (,J ......
-4 ! I w .....
0 :::r
0 "'I 0 0 "'I 3
< D)
C (1) en
Chloroform Ca11bon Ohloromethane Methylene Nitrate Ohloride TW4-32 Tetrachloride I
(ug/1) (.ue/l) (Ug/1~ Chloride (og/1) (mg/l) ,mg/1~ II I
14-Nov-13 ND ND ND ND 4.26 52.1
22-Jan-14 ND ND ND ND 5.11 54.5
21-May-14 ND ND ND ND 5.63 54.9
13-Aug-14 ND ND ND ND 4.2 64
23-0ct-14 ND ND ND ND 2.14 62.6
l l-Mar-15 ND ND ND ND 2.46 64.2
10-Jun-15 ND ND ND ND 1.21 62.7
2-Sep-15 ND ND ND ND 5.09 59.6
21-0ct-15 ND ND ND ND 1.19 55.1
15-Mar-16 ND ND ND ND 4.48 64.2
25-May-16 ND ND ND ND 3.16 71.8
28-Jul-16 ND ND ND ND 3.44 64.4
19-0ct-16 ND ND ND ND 2.87 66.0
14-Mar-17 ND ND ND ND 2.82 62.8
15-Jun-17 ND ND ND ND 2.37 53.5
2-Aug-17 ND ND ND ND 2.47 65.8
10-0ct-17 ND ND ND ND 2.54 58.3
14-Mar-18 ND ND ND ND 2.94 65.4
12-Jun-18 ND ND ND ND 2.51 59.2
29-Aug-18 ND ND ND ND 2.56 68.1
30-Nov-18 ND ND ND ND 2.50 57.5
16-Mar-19 ND ND ND ND 2.15 57.5
13-Jun-19 ND ND ND ND 2.18 60.1
ll-Sep-19 ND ND ND ND 1.84 55.0
Nov-1
Jan-1
Mar-1
May-1
Jul-1
Sep-1
Nov-1
Jan-1
Mar-1
May-1
Jul-1
Sep-1
Nov-1
Jan-1
Mar-16
May-16
Jul-16
Sep-16
Nov-16
Jan-17
Mar-17
May-17
Jul-17
Sep-17
Nov-17
Jan-18
Mar-18
May-18
Jul-18
Sep-18
Nov-18
Jan-19
Mar-19
May-19
Jul-19
Sep-19
0
0
0
••
0
0
0
0
•• • •
••
0
••
0
••
••
••
0
0
0
••
••
0
0
0
(ug/L)
0 0 0 0 ......
0
~
0 ...... 0 .......
0 ......
3
~
PJ
(/)
::J
0 -C"' (t)
(t)
::J
C.
(t) -(t)
0 -(t)
C.
::J
~ :E ~ I
(,.)
I\)
-4 :E ~ I c,.)
N
C') :::r
0 ~ a 0 ~ 3
< m
C C1)
0
··1 Carbon
TW'4-33 • Chlo11of-01llll Tetrachloride Ohlo110JDethane Methylene Nitrate Chloride
(ug/1) (ul!II~ (ug/1) Chlodcle (ugll) (mg/)) (mg/I)
I
14-Nov-13 126 ND ND ND 1.82 47.2
30-Jan-14 124 ND ND ND 2.56 43.5
22-May-14 121 ND ND ND 1.63 46.8
27-Aug-14 104 ND ND ND 1.5 43
29-0ct-14 124 ND ND ND 2.22 44.2
12-Mar-15 134 ND ND ND 1.91 44.2
11-Jun-15 127 ND ND ND 1.62 46.4
3-Sep-15 123 ND ND ND 1.64 53.4
29-0ct-15 129 ND ND ND 1.92 44.5
17-Mar-16 122 ND ND ND 2.13 46.2
8-Jun-16 96 ND ND ND 2.06 49.7
4-Aug-16 121 ND ND ND 2.32 48.5
26-0ct-16 I09 ND ND ND 2.36 52.4
16-Mar-17 91 ND ND ND 2.11 49.0
20-Jun-17 103 ND ND ND 2.34 49.2
3-Aug-17 127 ND ND ND 2.04 46.9
11-0ct-17 97.1 ND ND ND 2.09 42.5
15-Mar-18 128 ND ND ND 1.94 49.2
13-Jun-18 88 ND ND ND 2.13 44.0
5-Sep-18 113 ND ND ND 1.82 50.0
13-Dec-18 141 ND ND ND 2.01 43.2
20-Mar-19 86.2 ND ND ND 2.00 47.2
19-Jun-19 121 ND ND ND 2.16 43.4
12-Sep-19 101 ND ND ND 1.61 41.1
I\)
0 0
I -'-Nov-13
Jan-14
Mar-14
May-14
Jul-14
Sep-14
Nov-14
Jan-15
Mar-15
May-15
Jul-15
Sep-15
Nov-15
Jan-16
Mar-16
May-16
Jul-16
Sep-16
Nov-16
Jan-17
Mar-17
May-17
Jul-17
Sep-17
Nov-17
Jan-18
Mar-18
May-18
Jul-18
Sep-18
Nov-18
Jan-19
Mar-19
May-19
Jul-19
Sep-19
.j::,,.
0
0)
0
(ug/L)
co 0
......
0 0
......
I\)
0
.j::,,.
0
......
0)
0
-t :e ~ I w w
0 :r 0 ...
9. 0 ...
3
< m c (1)
0
Chloroform Carl> Cbloromethane Metb;vleoe 'Fat Oh..,ide, TW4·34 Tetrachloride Chloride (ug/1) (ue./lJ) (u~) (iudl,) (mgrt) (mg/I)
14-Nov-13 ND ND ND ND 1.64 19.2
23-Jan-14 ND ND ND ND 1.94 20.4
21-May-14 ND ND ND ND 1.69 17.9
13-Aug-14 ND ND ND ND 1.1 18
28-0ct-14 ND ND ND ND 1.16 17.5
ll-Mar-15 ND ND ND ND 1.21 17.7
10-Jun-15 ND ND ND ND 0.868 17.4
3-Sep-15 ND ND ND ND 0.458 15.1
21-0ct-15 ND ND ND ND 0.368 15.8
16-Mar-16 ND ND ND ND 0.925 17.3
26-May-16 ND ND ND ND 0.605 18
26-May-16 ND ND ND ND 0.605 18
3-Aug-16 ND ND ND ND 0.726 17.2
20-0ct-16 ND ND ND ND 0.612 19.0
15-Mar-17 ND ND ND ND 0.674 18.0
15-Jun-17 ND ND ND ND 0.727 15.7
2-Aug-17 ND ND ND ND 0.733 19.8
10-0ct-17 ND ND ND ND 0.774 18.5
14-Mar-18 ND ND ND ND 0.737 19.1
13-Jun-18 ND ND ND ND 0.877 19.5
29-Aug-18 ND ND ND ND 0.736 23.8
12-Dec-18 ND ND ND ND 0.889 18.5
16-Mar-19 ND ND ND ND 0.859 17.9
13-Jun-l 9 ND ND ND ND 0.994 20.1
l 1-Sep-19 ND ND ND ND 0.934 17.8
Nov-1
Jan-1
Mar-1
May-1
Jul-1
Sep-1
Nov-1
Jan-1
Mar-1
May-1
Jul-1
Sep-1
Nov-1
Jan-1
Mar-1
May-1
Jul-16
Sep-16
Nov-16
Jan-17
Mar-17
May-17
Jul-17
Sep-17
Nov-17
Jan-18
Mar-18
May-18
Jul-18
Sep-18
Nov-18
Jan-19
Mar-19
May-19
Jul-19
Sep-19
0 0 0 0 0
0
••
••
0
••
0
0
0
0
0
0
0
0
0
0
0
0
j
i•
•
i•
·~
·~
(ug/L)
0
:Y'
0 -0 -0 -3
:Y'
tu (J)
:J
0 r-+
er
CD
CD :J
0..
CD r-+ CD
C") r-+
CD 0..
:J
-I ~ ~ I w ~
....
i I w .,::,.
0 :::r
0 ""I a 0 ""I 3
< !. C Cl) u,
ChJotoform Carbon Cklotrometlhane Methylene Nitrate Qhloride TW~-35 (ugll) Tetr QrmFide (11,glt) O.hloride (mgll): (mw'l) I i11utO (oo/l), I
27-Aug-14 ND ND ND ND 0,2 34
28-0ct-14 ND ND ND ND 0.351 34.1
11-Mar-15 ND ND ND ND 0.436 34.9
10-Jun-15 ND ND ND ND 0.452 35.2
3-Sep-15 ND ND ND ND 0.304 35.9
28-0ct-15 ND ND ND ND 0.419 33.4
16-Mar-16 ND ND ND ND 0.521 35.4
26-May-16 ND ND ND ND 0.631 35.4
3-Aug-16 ND ND ND ND 0.723 34.8
20-0ct-16 ND ND ND ND 0.626 37.1
15-Mar-17 ND ND ND ND 0.673 33.7
15-Jun-l 7 ND ND ND ND 0.699 34.8
2-Aug-17 ND ND ND ND 0.670 36.3
10-0ct-17 ND ND ND ND 0.651 31.7
14-Mar-18 ND ND ND ND 0.740 37.4
13-Jun-18 ND ND ND ND 0.662 33.7
30-Aug-18 ND ND ND ND 0.527 39.3
12-Dec-18 ND ND ND ND 0.559 43.0
16-Mar-19 ND ND ND ND 0.574 33.5
13-Jun-19 ND ND ND ND 0.670 35.5
11-Sep-19 ND ND ND ND 0.525 31.7
Aug-14
Oct-14
Dec-14
Feb-15
Apr-15
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
Oct-16
Dec-16
Feb-17
Apr-17
Jun-17
Aug-17
Oct-17
Dec-17
Feb-18
Apr-18
Jun-18
Aug-18
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
0 .~
•
••
•
•• ·~
0
0
0
••
..
.. .. ..
..
0
•
0
0
•
0
(ug/L)
0 0 0 0
0 :::::r
0
~ 0 -0
~ 3
:::::r
DJ en
:::J
0 ,-+
C"' CD CD
:::J
a.
CD ,-+
CD
(")
,-+
CD a.
:::J
-I :E ~ I
u)
01
.....
i I w U1
0 :::r
0
0 -0 ""I
3
< !. C CD en
Chlor~!omn Carlton Chl•r~e Methylene Pfflnte €hloride 'TW~-36 (ug/1) Tmaclllorlcle (Rill Olderide (mgA) .(mg/I~ fffl!lt), {W!'lt)
27-Aug-14 ND ND ND ND ND 65
23-0ct-14 ND ND ND ND ND 67.3
ll-Mar-15 ND ND ND ND ND 67.2
10-Jun-15 ND ND ND ND ND 69.3
3-Sep-15 ND ND ND ND ND 76.4
21-0ct-15 ND ND ND ND ND 64.5
16-Mar-16 ND ND ND ND ND 67.1
25-May-16 ND ND ND ND ND 72.3
27-Jul-16 ND ND ND ND ND 69.4
20-0ct-16 ND ND ND ND ND 73.8
15-Mar-17 ND ND ND ND ND 60.2
15-Jun-l 7 ND ND ND ND ND 71.3
2-Aug-17 ND ND ND ND ND 69.6
10-0ct-17 ND ND ND ND 0.104 62.9
14-Mar-18 ND ND ND ND ND 73.8
12-Jun-18 ND ND ND ND ND 64.3
29-Aug-18 ND ND ND ND ND 76.4
12-Dec-18 ND ND ND ND 0.123 65.8
16-Mar-19 ND ND ND ND 0.116 65.0
13-Jun-19 ND ND ND ND ND 71.5
11-Sep-19 ND ND ND ND ND 69.6
Aug-14
Oct-14
Dec-14
Feb-15
Apr-15
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
Oct-16
Dec-16
Feb-17
Apr-17
Jun-17
Aug-17
Oct-17
Dec-17
Feb-18
Apr-18
Jun-18
Aug-18
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
0
0
0
j
~~
0
0
0
0
"
0
0
0
0
0
0
0
"
0
. ~
. ~
. ~
(ug/L)
0 0 0 0
0 ::::;
0
~ 0 -+. 0
~
3
::::; p.:, en
::::,
0 -O"'
ct>
ct> ::::,
c..
ct> -ct>
0 -ct> c..
::::,
-;
~ ~
I w O')
-t ! I <,.)
0)
0 :::T
0 2. 0 ..,
3
< !!!. C (I) rn
,~ Carbon M~lene loroform Chloromethan itrate Chi ride TW4 .. 37 (ug/1) Tetraebloride (ug/lJ Cbl()rlde (mg/I, (naglt) (112'.ll) tuml)
8-Jun-15 30200 18 16 2 35 345
31-Aug-15 19100 17 14 1.04 32 374
19-0ct-15 19500 13 9 1.17 35 399
9-Mar-16 17500 16 4 1.34 28.4 332
23-May-16 16200 14 ND 1.17 27.9 389
25-Jul-16 15900 17 ND ND 33.4 294
12-0ct-16 16400 16 ND ND 26.1 304
8-Mar-17 18000 15 ND ND 32.3 305
13-Jun-17 15800 16 ND ND 31.2 281
26-Jul-17 15000 15.1 ND ND 30.5 277
11-0ct-17 15500 12.6 2.47 ND 30.6 255
12-Mar-18 12900 12.8 1.14 ND 30.0 263
8-Jun-18 14400 10.6 ND ND 28.6 275
22-Aug-18 14100 12.1 6.20 ND 25.4 387
28-Nov-18 15200 11.3 19.8 ND 27.3 264
8-Mar-19 13300 13.8 1.2 ND 30.1 209
5-Jun-19 16200 14.6 ND ND 31.2 250
4-Sep-19 11900 10.7 1.90 ND 25.8 228
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
Oct-16
Dec-16
Feb-17
Apr-17
Jun-17
Aug-17
Oct-17
Dec-17
Feb-18
Apr-18
Jun-18
Aug-18
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
0
-l-
01 0 0 0
......
0 0 0 0
@ (ug/L)
8
I\) 0 0 0 0
I\)
01 0 0 0
c,.:, 0 0 0 0
c,.:,
01 0 0 0
i
I w
""" 0 :::r
0 ... 0 -0 ...
3
< I» c CD tn
Chloroform
1
Carbon ChloFomethane Methywae ffi(Jfate C.liloride TW4 .. J8 Titra hlorlde Chloride (ug/1) (uem (fllg/1) (Uf?/1) (mg/I~ (mg/I)
10-Nov-16 ND ND ND ND 11.2 40.0
15-Mar-17 ND ND ND ND 10.6 35.7
15-Jun-17 ND ND ND ND 10.8 36.2
2-Aug-17 ND ND ND ND 10.1 36.9
10-0ct-17 ND ND ND ND 10.3 31.3
14-Mar-18 ND ND ND ND 9.34 36.5
13-Jun-18 ND ND ND ND 9.48 33.1
30-Aug-18 ND ND ND ND 7.77 39.2
12-Dec-18 ND ND ND ND 8.48 35.0
16-Mar-19 ND ND ND ND 8.96 33.5
13-Jun-19 ND ND ND ND 8.53 33.7
11-Sep-19 ND ND ND ND 7.61 31.6
(ug/L)
0 0 0 0 0 ...... ...... ......
Nov-16 -----1---r----+----t---+---+---t----i----i-----i
Feb-17 l
May-17
Aug-17
Nov-17
Feb-18 ~
•
May-18 -i
Aug-18
Nov-18
Feb-19
•
I
~
May-19 t
Aug-19
I I I
I I I
I I I
I I I
I I I
I I I
I I I I
'
I
'
I I I I I I I
I I I I I I I
I I I I I I I
I I I I I
I I I I I I I
-t :e ~ I w QC)
0
:::J"
0 ..,
0 -0 ..,
3
< D)
C (D en
Chloroform Carbon Chloromethane MetbJlene Nitrate Chloride TW·4-39 (ug/.1) Tet.rachloride {Ilg/I) Chl~ride (mg/I) (m_g/J) (m!IB fue/n
10-Nov-16 2800 ND ND ND 20.7 68.9
8-Mar-17 6460 8.15 ND 1.35 6.44 130
13-Jun-17 5560 8.20 ND 1.31 6.25 120
26-Jul-17 10000 14.40 ND 1.50 7.74 132
l l-Oct-17 552 ND ND ND 2.65 73.5
12-Mar-18 2870 3.10 ND ND 3.33 118
8-Jun-18 7160 7.94 ND ND 4.84 107
22-Aug-18 8180 12.50 2.33 ND 6.05 110
28-Nov-18 6520 6.08 ND ND 6.39 123
8-Mar-19 885 1.20 ND ND 2.08 49.0
5-Jun-19 8640 11.60 ND ND 8.45 114.0
4-Sep-19 4240 5.71 ND ND 1.75 48.2
6 ~ -onv
6~-qa.:1
8~-AON
"' s ~ -onv
Cl) :, m >
8 ~-AEIIJ E ... 0 0 ...
..2 .c 0 8 ~-qa.:1
0)
C") I ; ...
L~-AON
L ~ -Bnv
9~-AON 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 C\f 0 GO co s::t C\f ~ ~
(110n)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-40 (ug/1) Tetrachlot!icle ~ug/1} Chloride (mg/l) (mg/)) '1.s~:/1) hu,m
21-Mar-18 248 ND ND ND 3.08 35.7
14-Jun-18 131 ND ND ND 3.33 31.6
5-Sep-18 116 ND ND ND 3.22 37.6
13-Dec-18 118 ND ND ND 3.54 29.9
20-Mar-19 111 ND ND ND 3.18 30.9
5-Jun-19 263 ND ND ND 3.55 35.6
4-Sep-19 380 ND ND ND 3.39 35.9
U)
CD :J 'i >
E lo,
0 -0 lo,
.2 .c 0
0 oi::t' I ;
I-
0 0 "'"
0 LI)
C')
0 0 C')
0 LI)
C\I
0 0 C\I
(1J6n)
0 LI) ,-
0 0 ,-
0 LI)
6~-onv-£c
6 ~-qa:i-v
8~-lOQ-LG
s~-1nr-6~
0
Chloroform Carbon Chloromt,thane Methylene Chloride TW4-41 (ug/1) Tetncblodde (ug/1) ehl'oride Nitra.te (m:gt)) (mg/I) ~u1!/I) ~llfz/1) I
9-May-18 1400 ND ND ND 6.54 42.8
22-Aug-18 1390 ND ND ND 6.13 45.5
28-Nov-18 1320 ND ND ND 6.02 41.4
8-Mar-19 1220 ND ND ND 6.71 39.1
5-Jun-19 1320 ND ND ND 6.00 38.9
4-Sep-19 1190 ND ND ND 6.22 39.4
ti)
Cl)
~ ca >
E I.,
0 -0 I.,
.2 .c 0
T""
111:f' I ;
I-
0 LO -.:I" ....
0 0 -.:I" ....
0 LO Ct) ....
0 0 Ct) .....
(1J6n)
0 LO C\J ....
0 0 C\J .....
0 LO .... ....
6 ~ -5nv-Ec
6 ~ -A'BV\1-9 ~
6~-qa.:1-v
8~-PO-LG
~ Carbon Metb~lene Chloroform Obloromethane Nifr,ate Chlijrlde 1WY4·42 (og/J) Tetrachloride {ug/1) Chloride {jng/J) (mg/I)
' (ue/U (utz/J}
19-Jun-1 9 ND ND ND ND 2.57 23.3
11-Sep-19 ND ND ND ND 2.75 20.6
Ohloroform Carbon Chlol'.omethane Methylene Nitrate Chloride TW4•42 (Ug/1) Tetrachloride (iJg/1) Chloride (mg/I) (mgll} Cul!/D (ugll}
l 9-Jun-1 9 ND ND ND ND 2.57 23.3
1 I-Sep-19 ND ND ND ND 2.75 20.6
UJ a, ::, m >
E ..
0 0 ..
.2 .c 0
~ t-
..... ..... ..... 0
(1J6n)
..
6 ~-Bnv-8 ~
6~-Bnv-8
6 ~-unr-vz
0
6~-unr-v~
0 0 0 0
TabL
Contour Map Based Chloroform Plume Mass Calculations and Data over Time
CHLOROFORM RESIDUAL MASS ESTIMATE DETAILS:
Chloroform Data File: CHL_Surferlnput_Q3_19.xls
Gridding details:
1) kriging parameters: SURFER™ default parameters (point kriging, linear
variogram, slope= 1, no anisotropy [anisotropy= 1], no search constraints [all data
used])
2) min x, max x (UTME[m]): 631900, 633043
3) min y, may y (UTMN[m]): 4154240, 4155550.64
4) grid spacing in x, y (m): 15.24, 15.24
5) artificial or pseudo-data: none
6) Q2, 2019 (previous quarter) data used at wells: MW-1, MW-2, MW-3A, MW-5,
MW-12, MW-15, MW-17 through MW-20, MW-22 through MW-24, MW-27
through MW-29 (all non-detect).
Chloroform residual mass estimate kriged grid files (ascii format):
Ucm3Q19wl.grd: third quarter, 2019 Water Level Grid (ft amsl)
Ucm3Q19bb.grd: third quarter, 2019 Aquifer Base Grid (ft amsl)
Ucm3Q19sat.grd: third quarter, 2019 Saturated Thickness Grid (ft)
Ucm3Q191ogchl.grd: third quarter, 2019 log of chloroform grid (log of ug/L)
Ucm3Q19chl.grd: third quarter, 2019 Chloroform Concentration Grid (ug/L)
Ucm3Q19ge70.grd: third quarter, 2019 Chloroform Concentration GE 70 Grid (ug/L)
Ucm3Q19volm3.grd: third quarter, 2019 Groundwater Volume Grid (m3)
Ucm3Q19masslb.grd: third quarter, 2019 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format):
Ucm3Q19wl.dat: third quarter, 2019 Water Level Grid XYZ file (ft amsl)
Ucm3Ql9bb.dat: third quarter, 2019 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm3Q19sat.dat: third quarter, 2019 Saturated Thickness Grid XYZ file (ft)
Ucm3Q19logchl.dat: third quarter, 2019 log of chloroform grid XYZ file (log of ug/L)
Ucm3Q19chl.dat: third quarter, 2019 Chloroform Concentration Grid XYZ file (ug/L)
Ucm3Q19ge70.dat: third quarter, 2019 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm3Q19volm3.dat: third quarter, 2019 Groundwater Volume Grid XYZ file (m3)
Ucm3Q19masslb.dat: third quarter, 2019 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate file: Ucm3Q19result.xls
2400
2200
2000
1800
:a-=-1600 GI .. "' E = IA.I
Ill Ill "' :E
E ... .E 0 ... 0 ::c u
iii ::::,
'a ·;;;
GI a:
1400
1200
1000
800
600
400
200
0
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ()?~ 0-°'~ ()>~ o.1-~ ()?~ 0-°'~ ()>~ o.1-~ ()?~ 0-°'~ ()>~ o.1-~ ()?~ 0-°'~ ()>~ o.1-~ ()?~
~ mass estimate
--Linear (mass estimate)
H:\718000\nov19\chloroform\masscalc\FL.1_resid_chl_mass_3019.xls: FL.1 Resid CHL Mass
HYDRO
GEO
CHEM, INC.
TIME SERIES OF RESIDUAL CHLOROFORM MASS
ESTIMATES
Approved I Date
SJS
Author I Date
SJS
File Name !Figure .......,,-..........,. L.1
TABLE L.1
Chloroform Plume Residual Mass
Since Third Quarter 2015
Residual
Plume Mass
Quarter (lbs)
0315 1712
0415 1869
01 16 1946
0216 2261
0316 1718
0416 1711
0117 1271
0217 1372
0317 1948
0417 884
01 18 1271
0218 1271
0318 1208
0418 1107
01 19 833
0219 1408
0319 1050
Notes:
lbs= pounds
H:\718000\novl9\chloroform\masscalc\FL.l_resid_chl_mass_3Q19.xls: Table L.l
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Tuesday, November 5, 2019 8:55 AM
Phillip Goble
Dean Henderson; David Frydenlund; Terry Slade; Scott Bakken; Logan Shumway; Paul
Goranson
Transmittal of CSV Files White Mesa Mill 2019 Q3 Chloroform Monitoring
1909134-report-EDD.csv; 1909320-report-EDD.csv; DTWS -EIM All Programs.csv; Q3
2019 Chloroform Field Data.csv
Attached to this e-mail is an electronic copy of laboratory results for chloroform monitoring conducted at the White
Mesa Mill during the third quarter of 2019, in Comma Separated Value (CSV) format.
Other electronic files required by the Corrective Action Plan are included on the CDs included with the hard copy
reports.
Please contact me at 303-389-4134 if you have any questions on this transmittal.
Yours Truly
Kathy Weinel
1° ---1Energy Fuels Resources (USA) Inc.
Kathy Weinel
Quality Assurance Manager
t: 303.389.4134 I t: 303.389.4125
225 Union Blvd., Suite 600
Lakewood, CO 80228
http://www.energyfuels.com
This e-mail is intended for the exclusive use of person(s) mentioned as the recipient(s). This message and any attached files with it are confidential and may
contain privileged or proprietary information. If you are not the intended recipient(s) please delete this message and notify the sender. You may not use, distribute
print or copy this message if you are not the intended recipient(s).
1
TabN
Exceedance Notices for the Reporting Period
This attachment has been deliberately left blank.
ID UTM NAD83 E UTM NAD83 N Q3 chl log chl
MW-01 632048.762 4156277.343 0.5 -0.69315
MW-02 631111.458 4155147.645 0.5 -0.69315
MW-3A 631188 4153701 0.5 -0.69315
MW-04 632528.239 4154843.595 1180 7.07327
MW-05 631487.143 4154685.998 0.5 -0.69315
MW-11 631884.320 4154613.567 0.5 -0.69315
MW-12 631227.666 4154732.958 0.5 -0.69315
MW-14 631683.028 4154278.148 0.5 -0.69315
MW-15 631500.674 4154305.536 0.5 -0.69315
MW-17 631911.605 4154068.619 0.5 -0.69315
MW-18 632293.435 4156108.350 0.5 -0.69315
MW-19 632687.427 4155914.140 0.5 -0.69315
MW-20 631080.558 4153163.859 0.5 -0.69315
MW-22 632550.351 4152699.061 0.5 -0.69315
MW-23 631055.742 4154775.143 0.5 -0.69315
MW-24 631278.659 4155179.519 0.5 -0.69315
MW-25 632162.900 4154565.810 0.5 -0.69315
MW-27 632058.974 4155531.958 0.5 -0.69315
MW-28 631668.123 4155173.235 0.5 -0.69315
MW-29 631508.577 4154977.313 0.5 -0.69315
MW-30 631814.639 4154904.086 0.5 -0.69315
MW-31 632096.041 4154832.451 0.5 -0.69315
MW-33 631066.637 4154384.754
MW-34 631289.321 4154343.279
MW-35 631066.446 4154577.601 0.5 -0.69315
MW-36 631052.558 4154496.563 0.5 -0.69315
MW-37 631395.246 4154320.793 0.5 -0.69315
MW-38 631855.323 4153140.006 0.5 -0.69315
MW-39 632220.670 4153395.504 0.5 -0.69315
MW-40 632565.648 4153638.305 0.5 -0.69315
TW4-01 632520.433 4154799.077 894 6.795706
TW4-02 632528.370 4154876.070 797 6.680855
TW4-03 632529.958 4155043.522 0.5 -0.69315
TW4-04 632536.308 4154716.526 989 6.896694
TW4-05 632510.114 4155144.358 14.6 2.681022
TW4-06 632522.020 4154641.120 15.8 2.76001
TW4-07 632514.876 4154837.177 801 6.685861
TW4-08 632563.295 4154833.208 75.4 4.322807
TW4-09 632514.876 4155095.960 66 4.189655
TW4-10 632447.407 4155045.933 734 6.598509
TW4-11 632452.964 4154913.377 2790 7.933797
TW4-12 632677.595 4155051.490 0.5 -0.69315
TW4-13 632653.783 4154905.439 0.5 -0.69315
TW4-14 632658.545 4154695.889 6.08 1.805005
MW-26 632333.661 4155062.031 1360 7.21524
TW4-16 632313.263 4154921.314 99.8 4.603168
MW-32 632310.150 4154786.287 0.5 -0.69315
TW4-18 632486.301 4155193.571 56.2 4.028917
TW4-19 632348.982 4155189.602 6670 8.805375
TW4-20 632306.120 4155155.471 10500 9.259131
TW4-21 632354.538 4155286.440 596 6.390241
TW4-22 632198.963 4155172.934 3460 8.149024
TW4-23 632383.895 4154586.902 0.5 -0.69315
TW4-24 632116.844 4155166.850 31.1 3.437208
TW4-25 632359.142 4155402.627 0.5 -0.69315
TW4-26 632518.845 4154554.601 877 6.776507
TW4-27 632674.000 4154604.000 7.58 2.025513
TW4-28 632742.000 4155021.000 0.5 -0.69315
TW4-29 632668.000 4154547.000 549 6.308098
TW4-30 632715.000 4154561.000 34.8 3.549617
TW4-31 632734.000 4154601.000 0.5 -0.69315
TW4-32 632808.000 4154983.000 0.5 -0.69315
TW4-33 632609.000 4154617.000 101 4.615121
TW4-34 632667.000 4154471.000 0.5 -0.69315
TW4-35 632714.000 4154505.000 0.5 -0.69315
TW4-36 632674.000 4154828.000 0.5 -0.69315
TW4-37 632256.000 4155157.000 11900 9.384294
TW4-38 632584.643 4155087.571 0.5 -0.69315
TW4-39 632397.658 4155145.602 4240 8.352319
TW4-40 632513.410 4154480.872 380 5.940171
TW4-41 632553.968 4154729.708 1190 7.081709
TW4-42 632524.19 4154418.44 0.5 -0.69315
632326.7 4155170 9.681323
632311.5 4155170 9.672083
632265.8 4155154 9.669513
632296.2 4155170 9.607466
632281 4155170 9.582492
632281 4155154 9.520519
632265.8 4155170 9.448361
632296.2 4155154 9.360982
632342 4155170 9.31479
632311.5 4155154 9.279922
632326.7 4155154 9.216443
632326.7 4155185 9.113431
632342 4155185 9.035717
632311.5 4155185 8.967889
632250.5 4155154 8.884871
632342 4155154 8.822681
632296.2 4155185 8.726782
632250.5 4155170 8.583165
632281 4155185 8.408573
632296.2 4155139 8.238659
632281 4155139 8.232676
632357.2 4155170 8.208973
632311.5 4155139 8.180512
632326.7 4155139 8.055041
632357.2 4155154 8.008668
632265.8 4155139 7.970026
632265.8 4155185 7.900282
632342 4155139 7.746329
632357.2 4155185 7.734212
632326.7 4155200 7.481529
632311.5 4155200 7.358442
632342 4155200 7.252909
632357.2 4155139 7.196879
632296.2 4155200 7.049498
632250.5 4155139 7.039086
632250.5 4155185 7.02575
632235.3 4155170 6.976615
632372.4 4155154 6.868959
632235.3 4155154 6.803952
632311.5 4155124 6.620907
632296.2 4155124 6.612852
632281 4155200 6.598289
632372.4 4155170 6.588964
632326.7 4155124 6.53019
632281 4155124 6.449
632372.4 4155139 6.420347
632342 4155124 6.332668
632357.2 4155200 6.139507
632265.8 4155124 6.004195
632265.8 4155200 5.985526
632357.2 4155124 5.984722
632235.3 4155185 5.854551
632372.4 4155185 5.756834
632387.7 4155154 5.567448
632220 4155170 5.514563
632235.3 4155139 5.507474
632326.7 4155215 5.494844
632387.7 4155139 5.458085
632311.5 4155215 5.446479
632372.4 4155124 5.425678
632250.5 4155200 5.187914
632250.5 4155124 5.172798
632342 4155215 5.168536
632296.2 4155215 5.165318
632220 4155154 5.044258
632311.5 4155109 5.005642
632296.2 4155109 4.963664
632326.7 4155109 4.96193
632387.7 4155170 4.895708
632342 4155109 4.871491
632281 4155109 4.762803
632281 4155215 4.732633
632357.2 4155109 4.699289
632220 4155185 4.64856
632387.7 4155124 4.578177
632372.4 4155200 4.54639
632357.2 4155215 4.371413
632372.4 4155109 4.351099
632265.8 4155109 4.33842
632204.8 4155170 4.304211
632235.3 4155200 4.249278
632265.8 4155215 4.18313
632235.3 4155124 4.051664
632387.7 4155185 4.045857
632402.9 4155139 3.967661
632220 4155139 3.944734
632402.9 4155154 3.886772
632326.7 4155231 3.781391
632387.7 4155109 3.743838
632311.5 4155231 3.737097
632250.5 4155109 3.682093
632311.5 4155093 3.611844
632296.2 4155093 3.581964
632326.7 4155093 3.580869
632342 4155093 3.574498
632357.2 4155093 3.565456
632342 4155231 3.548277
632250.5 4155215 3.538458
632296.2 4155231 3.505101
632372.4 4155093 3.427012
632204.8 4155154 3.416418
632281 4155093 3.412311
632204.8 4155185 3.404396
632402.9 4155124 3.394881
632372.4 4155215 3.312522
632402.9 4155170 3.266741
632220 4155200 3.247952
632281 4155231 3.158794
632387.7 4155200 3.145666
632265.8 4155093 3.073366
632387.7 4155093 3.068758
632357.2 4155231 3.014951
632402.9 4155109 2.896032
632220 4155124 2.887912
632235.3 4155109 2.878012
632235.3 4155215 2.832582
632265.8 4155231 2.741117
632372.4 4155078 2.708936
632357.2 4155078 2.679462
632402.9 4155185 2.642247
632250.5 4155093 2.587895
632296.2 4155078 2.555555
632311.5 4155078 2.555366
632204.8 4155139 2.544651
632387.7 4155078 2.544166
632342 4155078 2.539449
632402.9 4155093 2.498975
632326.7 4155246 2.490714
632326.7 4155078 2.490513
632281 4155078 2.426913
632311.5 4155246 2.420191
632342 4155246 2.377253
632387.7 4155215 2.309437
632372.4 4155231 2.308123
632418.2 4155139 2.29521
632250.5 4155231 2.279547
632296.2 4155246 2.235908
632189.6 4155170 2.224083
632204.8 4155200 2.222633
632418.2 4155154 2.215274
632372.4 4155063 2.191421
632402.9 4155078 2.186557
632265.8 4155078 2.169862
632418.2 4155124 2.166156
632387.7 4155063 2.141478
632220 4155215 2.111627
632357.2 4155063 2.077141
632220 4155109 2.06519
632402.9 4155200 2.04593
632357.2 4155246 2.041999
632235.3 4155093 2.024261
632281 4155246 1.988408
632418.2 4155109 1.984844
632418.2 4155170 1.937339
632402.9 4155063 1.928657
632204.8 4155124 1.866446
632311.5 4155063 1.85755
632296.2 4155063 1.856615
632189.6 4155185 1.85266
632189.6 4155154 1.848243
632372.4 4155048 1.833676
632342 4155063 1.833126
632387.7 4155048 1.826131
632418.2 4155093 1.823623
632250.5 4155078 1.818282
632235.3 4155231 1.800421
632326.7 4155063 1.747757
632281 4155063 1.74606
632357.2 4155048 1.724153
632265.8 4155246 1.706582
632418.2 4155078 1.69711
632402.9 4155048 1.689702
632387.7 4155231 1.619469
632418.2 4155185 1.598032
632418.2 4155063 1.589574
632372.4 4155032 1.574517
632326.7 4155261 1.572334
632387.7 4155032 1.569275
632372.4 4155246 1.563477
632342 4155261 1.559541
632342 4155048 1.555976
632265.8 4155063 1.545185
632402.9 4155215 1.511256
632357.2 4155032 1.493566
632311.5 4155261 1.484659
632220 4155093 1.469051
632326.7 4155048 1.463742
632402.9 4155032 1.455719
632311.5 4155048 1.451278
632418.2 4155048 1.447448
632204.8 4155215 1.430929
632189.6 4155139 1.425706
632235.3 4155078 1.425529
632250.5 4155246 1.408687
632296.2 4155048 1.399627
632342 4155032 1.374861
632372.4 4155017 1.368715
632357.2 4155261 1.367711
632204.8 4155109 1.361444
632387.7 4155017 1.357404
632296.2 4155261 1.349207
632220 4155231 1.334518
632357.2 4155017 1.304945
632250.5 4155063 1.286988
632281 4155048 1.284081
632189.6 4155200 1.279803
632326.7 4155032 1.270492
632418.2 4155200 1.256621
632402.9 4155017 1.247048
632433.4 4155124 1.24359
632433.4 4155139 1.239705
632418.2 4155032 1.239506
632433.4 4155109 1.217144
632342 4155017 1.201557
632372.4 4155002 1.19611
632281 4155261 1.189923
632387.7 4155002 1.186295
632311.5 4155032 1.185247
632433.4 4155093 1.184111
632433.4 4155154 1.180268
632433.4 4155063 1.171149
632433.4 4155078 1.164352
632433.4 4155048 1.14495
632357.2 4155002 1.136336
632265.8 4155048 1.116655
632235.3 4155246 1.110827
632387.7 4155246 1.092049
632189.6 4155124 1.088998
632326.7 4155017 1.088215
632296.2 4155032 1.088015
632402.9 4155002 1.084708
632402.9 4155231 1.066208
632433.4 4155170 1.063965
632387.7 4154987 1.049961
632372.4 4154987 1.047392
632220 4155078 1.047078
632342 4155002 1.035837
632418.2 4155017 1.035272
632372.4 4155261 1.030437
632265.8 4155261 1.018509
632235.3 4155063 1.010206
632204.8 4155093 0.992315
632342 4155276 0.984296
632357.2 4154987 0.982387
632311.5 4155017 0.974667
632402.9 4154987 0.968851
632281 4155032 0.964034
632418.2 4155215 0.941434
632433.4 4155032 0.941349
632387.7 4154972 0.93732
632326.7 4155276 0.93066
632250.5 4155048 0.920754
632326.7 4155002 0.91806
632204.8 4155231 0.917019
632372.4 4154972 0.914181
632433.4 4155185 0.910285
632357.2 4155276 0.909252
632418.2 4155002 0.890006
632402.9 4154972 0.885967
632174.3 4155170 0.884802
632342 4154987 0.880604
632189.6 4155215 0.865307
632296.2 4155017 0.856822
632311.5 4155276 0.854258
632250.5 4155261 0.842836
632357.2 4154972 0.839356
632387.7 4154956 0.834174
632220 4155246 0.830333
632189.6 4155109 0.828919
632174.3 4155154 0.826019
632265.8 4155032 0.818589
632402.9 4154956 0.817777
632418.2 4154987 0.802386
632174.3 4155185 0.801623
632311.5 4155002 0.795832
632372.4 4154956 0.787093
632448.6 4155048 0.779763
632296.2 4155276 0.76956
632326.7 4154987 0.762658
632418.2 4154972 0.753132
632220 4155063 0.749682
632402.9 4154941 0.745635
632433.4 4155017 0.744757
632433.4 4155200 0.738043
632342 4154972 0.736465
632281 4155017 0.732372
632387.7 4154941 0.726876
632204.8 4155078 0.724032
632235.3 4155048 0.721447
632418.2 4154956 0.720621
632402.9 4155246 0.718854
632174.3 4155139 0.70513
632387.7 4155261 0.704789
632357.2 4154956 0.702569
632448.6 4155063 0.701337
632448.6 4155093 0.68472
632418.2 4154941 0.683014
632448.6 4155078 0.682301
632448.6 4155109 0.680393
632281 4155276 0.679627
632296.2 4155002 0.674483
632418.2 4155231 0.671829
632235.3 4155261 0.670661
632250.5 4155032 0.665366
632448.6 4155124 0.66048
632372.4 4154941 0.658062
632402.9 4154926 0.655508
632372.4 4155276 0.64451
632311.5 4154987 0.641886
632174.3 4155200 0.635066
632433.4 4155002 0.632959
632448.6 4155139 0.630682
632189.6 4155093 0.62892
632418.2 4154926 0.623587
632326.7 4154972 0.622849
632387.7 4154926 0.607523
632265.8 4155017 0.605551
632342 4154956 0.602048
632448.6 4155154 0.59654
632265.8 4155276 0.586077
632204.8 4155246 0.58489
632174.3 4155124 0.582619
632189.6 4155231 0.58148
632433.4 4154987 0.580894
632357.2 4154941 0.567943
632433.4 4155215 0.565913
632448.6 4155032 0.565039
632433.4 4154972 0.562669
632281 4155002 0.557504
632448.6 4155170 0.555356
632433.4 4154956 0.554613
632509.6 4154804 0.546742
632402.9 4154911 0.545179
632418.2 4154911 0.542902
632220 4155048 0.539205
632342 4155292 0.530914
632204.8 4155063 0.528926
632433.4 4154941 0.528407
632296.2 4154987 0.526487
632372.4 4154926 0.524664
632235.3 4155032 0.518605
632220 4155261 0.510536
632357.2 4155292 0.510145
632311.5 4154972 0.509739
632509.6 4154789 0.508168
632524.8 4154804 0.506251
632448.6 4155185 0.498601
632326.7 4154956 0.498138
632326.7 4155292 0.493695
632250.5 4155276 0.491092
632524.8 4154789 0.488915
632509.6 4154819 0.487812
632250.5 4155017 0.483807
632387.7 4154911 0.478997
632189.6 4155078 0.475364
632342 4154941 0.475067
632174.3 4155215 0.474255
632174.3 4155109 0.473399
632402.9 4155261 0.460916
632433.4 4154926 0.458458
632524.8 4154850 0.457781
632524.8 4154834 0.457069
632418.2 4155246 0.456678
632311.5 4155292 0.454593
632418.2 4154895 0.454061
632494.4 4154804 0.453292
632494.4 4154819 0.452383
632265.8 4155002 0.448807
632357.2 4154926 0.435336
632448.6 4155017 0.432855
632524.8 4154819 0.431669
632494.4 4154834 0.426398
632524.8 4154773 0.426394
632402.9 4154895 0.426311
632387.7 4155276 0.426084
632281 4154987 0.421778
632448.6 4155200 0.42147
632509.6 4154773 0.418351
632509.6 4154834 0.418049
632296.2 4155292 0.414258
632433.4 4155231 0.4112
632494.4 4154789 0.408645
632296.2 4154972 0.405225
632509.6 4154850 0.401001
632235.3 4155276 0.397938
632311.5 4154956 0.39723
632372.4 4154911 0.393229
632220 4155032 0.388986
632189.6 4155246 0.388334
632479.1 4154834 0.387509
632326.7 4154941 0.387114
632204.8 4155048 0.386552
632433.4 4154911 0.385418
632494.4 4154850 0.381689
632479.1 4154819 0.379837
632174.3 4155093 0.379393
632448.6 4155002 0.376282
632524.8 4154758 0.375445
632235.3 4155017 0.374048
632433.4 4154895 0.373926
632281 4155292 0.371786
632204.8 4155261 0.370785
632448.6 4154956 0.369671
632448.6 4154972 0.365673
632418.2 4154880 0.364669
632479.1 4154850 0.363497
632463.9 4155093 0.361462
632448.6 4154987 0.360682
632433.4 4154880 0.358882
632189.6 4155063 0.357705
632463.9 4155109 0.356621
632387.7 4154895 0.354109
632159.1 4155170 0.354
632342 4154926 0.35399
632250.5 4155002 0.352032
632372.4 4155292 0.350341
632479.1 4154804 0.349831
632159.1 4155154 0.348634
632174.3 4155231 0.344418
632540.1 4154758 0.343848
632463.9 4155078 0.33977
632463.9 4154850 0.339018
632509.6 4154758 0.337205
632540.1 4154773 0.336462
632159.1 4155185 0.336124
632494.4 4154773 0.336089
632540.1 4154743 0.333449
632448.6 4154941 0.332991
632448.6 4155215 0.332567
632265.8 4154987 0.330853
632463.9 4154834 0.330768
632463.9 4155124 0.328779
632159.1 4155139 0.327351
632265.8 4155292 0.326843
632540.1 4154789 0.321945
632448.6 4154865 0.321136
632433.4 4154865 0.317562
632402.9 4154880 0.315482
632281 4154972 0.314921
632524.8 4154743 0.312161
632357.2 4154911 0.311694
632220 4155276 0.310708
632463.9 4155063 0.310253
632448.6 4154850 0.307082
632524.8 4154545 0.30635
632296.2 4154956 0.30585
632463.9 4154865 0.304048
632311.5 4154941 0.302591
632479.1 4154789 0.30075
632174.3 4155078 0.300095
632463.9 4155139 0.299449
632463.9 4154819 0.299347
632159.1 4155200 0.296703
632159.1 4155124 0.296566
632418.2 4155261 0.295074
632479.1 4154865 0.288575
632540.1 4154804 0.287829
632448.6 4154880 0.286566
632326.7 4154926 0.285703
632433.4 4155246 0.284064
632463.9 4155154 0.282875
632204.8 4155032 0.282183
632555.3 4154743 0.281244
632418.2 4154865 0.281082
632220 4155017 0.2807
632250.5 4155292 0.280038
632494.4 4154865 0.279569
632463.9 4155048 0.278426
632402.9 4155276 0.277917
632463.9 4155170 0.276613
632372.4 4154895 0.275878
632555.3 4154728 0.275455
632448.6 4154834 0.26974
632235.3 4155002 0.269509
632189.6 4155048 0.26778
632509.6 4154865 0.267312
632463.9 4155185 0.266909
632433.4 4154850 0.263388
632524.8 4154560 0.263246
632494.4 4154758 0.26197
632524.8 4154530 0.260525
632159.1 4155109 0.260425
632509.6 4154743 0.258549
632189.6 4155261 0.257385
632463.9 4154804 0.256973
632250.5 4154987 0.254767
632509.6 4154545 0.252618
632540.1 4154728 0.250097
632555.3 4154758 0.248562
632540.1 4154819 0.248145
632540.1 4154834 0.24744
632448.6 4155231 0.247047
632387.7 4154880 0.246941
632159.1 4155215 0.246635
632174.3 4155246 0.245415
632342 4154911 0.243339
632479.1 4154773 0.242404
632265.8 4154972 0.240893
632540.1 4154545 0.240477
632463.9 4155200 0.238063
632174.3 4155063 0.234403
632387.7 4155292 0.233563
632204.8 4155276 0.233479
632326.7 4155307 0.232985
632235.3 4155292 0.23289
632342 4155307 0.232691
632281 4154956 0.230371
632540.1 4154850 0.229493
632463.9 4155032 0.229325
632509.6 4154530 0.228874
632524.8 4154865 0.228566
632448.6 4154819 0.224988
632296.2 4154941 0.224509
632311.5 4155307 0.224303
632311.5 4154926 0.224133
632402.9 4154865 0.223812
632159.1 4155093 0.222343
632463.9 4154956 0.221539
632524.8 4154728 0.219215
632540.1 4154530 0.218231
632524.8 4154514 0.215428
632555.3 4154773 0.214278
632296.2 4155307 0.211729
632463.9 4154789 0.210357
632418.2 4154850 0.20954
632463.9 4154972 0.209519
632433.4 4154834 0.209111
632357.2 4155307 0.208738
632509.6 4154560 0.208708
632357.2 4154895 0.208037
632463.9 4154880 0.206504
632204.8 4155017 0.205333
632540.1 4154560 0.205029
632509.6 4154514 0.201935
632220 4155002 0.201925
632189.6 4155032 0.199245
632281 4155307 0.196193
632159.1 4155231 0.195976
632463.9 4155017 0.194537
632463.9 4154941 0.19431
632494.4 4154743 0.193965
632235.3 4154987 0.193036
632463.9 4155215 0.19284
632463.9 4154987 0.192369
632326.7 4154911 0.188931
632220 4155292 0.187519
632433.4 4155261 0.186877
632479.1 4155093 0.186009
632479.1 4154758 0.18555
632159.1 4155078 0.185132
632463.9 4155002 0.184609
632479.1 4155109 0.184077
632372.4 4154880 0.182394
632250.5 4154972 0.182249
632448.6 4154804 0.181005
632174.3 4155048 0.180892
632418.2 4155276 0.180527
632509.6 4154728 0.180163
632509.6 4154499 0.178687
632555.3 4154789 0.178281
632265.8 4155307 0.177879
632555.3 4154545 0.175604
632448.6 4155246 0.174449
632448.6 4154926 0.173839
632174.3 4155261 0.172111
632524.8 4154499 0.172087
632265.8 4154956 0.17197
632540.1 4154514 0.171355
632479.1 4154880 0.169569
632189.6 4155276 0.169229
632448.6 4154895 0.167198
632662 4154545 0.166368
632463.9 4154773 0.164774
632387.7 4154865 0.164683
632281 4154941 0.163478
632433.4 4154819 0.161389
632372.4 4155307 0.161105
632570.6 4154743 0.158997
632555.3 4154530 0.158522
632250.5 4155307 0.157205
632296.2 4154926 0.156956
632555.3 4154560 0.156664
632402.9 4155292 0.155925
632479.1 4155124 0.155402
632494.4 4154880 0.155379
632342 4154895 0.154672
632402.9 4154850 0.154394
632479.1 4155078 0.153493
632418.2 4154834 0.152757
632509.6 4154484 0.151203
632143.8 4155139 0.150998
632159.1 4155063 0.150772
632159.1 4155246 0.15043
632143.8 4155124 0.150173
632204.8 4155002 0.148565
632189.6 4155017 0.147176
632494.4 4154530 0.14663
632143.8 4155154 0.14663
632463.9 4155231 0.146475
632540.1 4154865 0.146203
632204.8 4155292 0.146132
632220 4154987 0.144259
632570.6 4154728 0.143457
632143.8 4155170 0.143183
632494.4 4154545 0.143101
632143.8 4155185 0.143062
632143.8 4155109 0.142593
632570.6 4154758 0.142558
632311.5 4154911 0.14244
632448.6 4154789 0.141359
632479.1 4155185 0.140696
632555.3 4154804 0.139636
632524.8 4154575 0.139602
632143.8 4155200 0.139265
632174.3 4155032 0.137961
632235.3 4154972 0.136759
632479.1 4154743 0.135567
632494.4 4154514 0.135398
632235.3 4155307 0.135032
632555.3 4154712 0.134825
632479.1 4155200 0.134569
632494.4 4154728 0.134516
632509.6 4154880 0.13447
632540.1 4154575 0.132695
632357.2 4154880 0.130736
632570.6 4154545 0.130289
632479.1 4155139 0.130149
632524.8 4154712 0.130119
632479.1 4155170 0.130008
632143.8 4155093 0.129678
632540.1 4154712 0.128344
632250.5 4154956 0.128071
632143.8 4155215 0.127907
632479.1 4154956 0.126639
632479.1 4154941 0.124425
632463.9 4154758 0.124126
632479.1 4155154 0.122947
632570.6 4154560 0.12258
632433.4 4154804 0.122281
632159.1 4155048 0.120399
632174.3 4155276 0.119057
632555.3 4154514 0.118481
632448.6 4155261 0.117694
632570.6 4154773 0.117573
632540.1 4154499 0.117183
632433.4 4155276 0.117155
632387.7 4155307 0.115766
632372.4 4154865 0.115176
632479.1 4155063 0.114737
632555.3 4154575 0.114349
632494.4 4154560 0.114296
632509.6 4154575 0.114265
632494.4 4154499 0.113961
632524.8 4154484 0.113869
632143.8 4155078 0.113645
632509.6 4154712 0.113416
632662 4154560 0.112967
632570.6 4154530 0.112801
632220 4155307 0.112565
632159.1 4155261 0.112352
632143.8 4155231 0.110855
632189.6 4155292 0.110474
632418.2 4154819 0.110063
632479.1 4154972 0.10965
632189.6 4155002 0.107775
632448.6 4154773 0.107501
632646.8 4154545 0.106751
632387.7 4154850 0.10675
632311.5 4155322 0.105265
632402.9 4154834 0.104992
632296.2 4155322 0.104444
632418.2 4155292 0.104432
632174.3 4155017 0.103988
632494.4 4155093 0.103376
632326.7 4155322 0.103196
632555.3 4154819 0.102433
632585.8 4154545 0.101716
632281 4155322 0.101119
632494.4 4155109 0.10034
632585.8 4154560 0.100058
632524.8 4154880 0.098584
632646.8 4154560 0.098138
632342 4155322 0.097033
632143.8 4155063 0.096522
632570.6 4154575 0.096474
632570.6 4154712 0.095824
632265.8 4155322 0.09541
632479.1 4154728 0.094415
632143.8 4155246 0.091557
632570.6 4154789 0.091523
632433.4 4154789 0.091456
632204.8 4155307 0.091102
632479.1 4154987 0.090811
632463.9 4154743 0.09024
632479.1 4155048 0.087917
632250.5 4155322 0.087552
632540.1 4154880 0.087427
632494.4 4154712 0.08713
632601 4154560 0.086743
632601 4154545 0.085658
632509.6 4154895 0.085207
632677.2 4154545 0.084913
632631.5 4154545 0.084641
632631.5 4154560 0.084582
632585.8 4154530 0.083405
632494.4 4154941 0.082791
632159.1 4155276 0.082098
632585.8 4154575 0.081791
632494.4 4154895 0.081547
632616.3 4154560 0.081447
632174.3 4155292 0.081435
632479.1 4154926 0.080373
632494.4 4154926 0.080348
632128.6 4155109 0.080328
632570.6 4154514 0.07991
632448.6 4154758 0.079797
632616.3 4154545 0.079745
632555.3 4154850 0.079693
632540.1 4154697 0.079683
632128.6 4155124 0.079207
632418.2 4154804 0.079049
632555.3 4154834 0.078861
632479.1 4154530 0.078343
632585.8 4154743 0.077709
632479.1 4155002 0.077112
632524.8 4154895 0.076793
632524.8 4154697 0.076788
632540.1 4154591 0.076045
632494.4 4154484 0.076041
632555.3 4154697 0.075276
632479.1 4155032 0.073998
632555.3 4154591 0.073917
632555.3 4154499 0.073741
632494.4 4154575 0.07362
632479.1 4154514 0.073528
632479.1 4154545 0.073369
632128.6 4155139 0.073235
632509.6 4154911 0.072963
632143.8 4155261 0.072784
632585.8 4154728 0.071691
632585.8 4154758 0.071691
632524.8 4154591 0.071653
632402.9 4154819 0.071278
632494.4 4154956 0.071253
632479.1 4155017 0.070985
632601 4154575 0.070743
632677.2 4154560 0.070419
632555.3 4154865 0.069075
632494.4 4154911 0.068675
632387.7 4154834 0.068378
632433.4 4154773 0.067702
632570.6 4154591 0.067665
632570.6 4154804 0.066903
632509.6 4154697 0.066901
632601 4154530 0.06594
632509.6 4154926 0.065208
632463.9 4154728 0.063475
632616.3 4154575 0.063016
632540.1 4154484 0.062888
632479.1 4154712 0.062884
632463.9 4154926 0.062437
632524.8 4154911 0.06105
632540.1 4154895 0.060584
632570.6 4154697 0.059967
632479.1 4154499 0.059691
632509.6 4154591 0.059552
632479.1 4154560 0.059523
632585.8 4154773 0.059457
632585.8 4154591 0.059199
632448.6 4154743 0.057935
632479.1 4154895 0.057803
632631.5 4154575 0.057474
632418.2 4154789 0.056925
632616.3 4154530 0.056649
632585.8 4154712 0.056
632585.8 4154514 0.055485
632494.4 4154972 0.054797
632509.6 4154941 0.053684
632494.4 4154697 0.05365
632646.8 4154530 0.053623
632631.5 4154530 0.053283
632555.3 4154880 0.052294
632646.8 4154575 0.051661
632601 4154591 0.050127
632662 4154530 0.048551
632570.6 4154499 0.046924
632540.1 4154682 0.046885
632524.8 4154926 0.046672
632555.3 4154606 0.046394
632555.3 4154682 0.046331
632585.8 4154789 0.045948
632570.6 4154606 0.045916
632570.6 4154819 0.045608
632509.6 4154469 0.045535
632463.9 4154712 0.043475
632494.4 4154591 0.043437
632540.1 4154911 0.043435
632463.9 4154895 0.043343
632524.8 4154682 0.04328
632540.1 4154606 0.042786
632479.1 4154575 0.042516
632662 4154575 0.041492
632616.3 4154591 0.041418
632585.8 4154606 0.041188
632479.1 4154697 0.040696
632585.8 4154697 0.040686
632601 4154514 0.040377
632570.6 4154682 0.040173
632509.6 4154956 0.039938
632479.1 4154484 0.039049
632509.6 4154682 0.038101
632555.3 4154895 0.037876
632524.8 4154469 0.037748
632601 4154743 0.037344
632524.8 4154606 0.037262
632555.3 4154484 0.037105
632601 4154728 0.035674
632601 4154606 0.033784
632524.8 4154941 0.03359
632570.6 4154621 0.032807
632631.5 4154591 0.032655
632555.3 4154667 0.031211
632555.3 4154621 0.030917
632585.8 4154499 0.030826
632616.3 4154514 0.030743
632601 4154712 0.030597
632585.8 4154682 0.030423
632540.1 4154926 0.030407
632585.8 4154621 0.030014
632692.5 4154560 0.030008
632570.6 4154667 0.029965
632540.1 4154667 0.02822
632570.6 4154636 0.026644
632616.3 4154606 0.026183
632570.6 4154651 0.025837
632479.1 4154911 0.02576
632601 4154697 0.024897
632585.8 4154667 0.024854
632585.8 4154636 0.024475
632601 4154621 0.023992
632646.8 4154591 0.023147
632585.8 4154651 0.022971
632601 4154682 0.020591
632601 4154636 0.019527
632616.3 4154621 0.017857
631900 4154240 0
631915.2 4154240 0
631930.5 4154240 0
631945.7 4154240 0
631961 4154240 0
631976.2 4154240 0
631991.4 4154240 0
632006.7 4154240 0
632021.9 4154240 0
632037.2 4154240 0
632052.4 4154240 0
632067.6 4154240 0
632082.9 4154240 0
632098.1 4154240 0
632113.4 4154240 0
632128.6 4154240 0
632143.8 4154240 0
632159.1 4154240 0
632174.3 4154240 0
632189.6 4154240 0
632204.8 4154240 0
632220 4154240 0
632235.3 4154240 0
632250.5 4154240 0
632265.8 4154240 0
632281 4154240 0
632296.2 4154240 0
632311.5 4154240 0
632326.7 4154240 0
632342 4154240 0
632357.2 4154240 0
632372.4 4154240 0
632387.7 4154240 0
632402.9 4154240 0
632418.2 4154240 0
632433.4 4154240 0
632448.6 4154240 0
632463.9 4154240 0
632479.1 4154240 0
632494.4 4154240 0
632509.6 4154240 0
632524.8 4154240 0
632540.1 4154240 0
632555.3 4154240 0
632570.6 4154240 0
632585.8 4154240 0
632601 4154240 0
632616.3 4154240 0
632631.5 4154240 0
632646.8 4154240 0
632662 4154240 0
632677.2 4154240 0
632692.5 4154240 0
632707.7 4154240 0
632723 4154240 0
632738.2 4154240 0
632753.4 4154240 0
632768.7 4154240 0
632783.9 4154240 0
632799.2 4154240 0
632814.4 4154240 0
632829.6 4154240 0
632844.9 4154240 0
632860.1 4154240 0
632875.4 4154240 0
632890.6 4154240 0
632905.8 4154240 0
632921.1 4154240 0
632936.3 4154240 0
632951.6 4154240 0
632966.8 4154240 0
632982 4154240 0
632997.3 4154240 0
633012.5 4154240 0
633027.8 4154240 0
633043 4154240 0
631900 4154255 0
631915.2 4154255 0
631930.5 4154255 0
631945.7 4154255 0
631961 4154255 0
631976.2 4154255 0
631991.4 4154255 0
632006.7 4154255 0
632021.9 4154255 0
632037.2 4154255 0
632052.4 4154255 0
632067.6 4154255 0
632082.9 4154255 0
632098.1 4154255 0
632113.4 4154255 0
632128.6 4154255 0
632143.8 4154255 0
632159.1 4154255 0
632174.3 4154255 0
632189.6 4154255 0
632204.8 4154255 0
632220 4154255 0
632235.3 4154255 0
632250.5 4154255 0
632265.8 4154255 0
632281 4154255 0
632296.2 4154255 0
632311.5 4154255 0
632326.7 4154255 0
632342 4154255 0
632357.2 4154255 0
632372.4 4154255 0
632387.7 4154255 0
632402.9 4154255 0
632418.2 4154255 0
632433.4 4154255 0
632448.6 4154255 0
632463.9 4154255 0
632479.1 4154255 0
632494.4 4154255 0
632509.6 4154255 0
632524.8 4154255 0
632540.1 4154255 0
632555.3 4154255 0
632570.6 4154255 0
632585.8 4154255 0
632601 4154255 0
632616.3 4154255 0
632631.5 4154255 0
632646.8 4154255 0
632662 4154255 0
632677.2 4154255 0
632692.5 4154255 0
632707.7 4154255 0
632723 4154255 0
632738.2 4154255 0
632753.4 4154255 0
632768.7 4154255 0
632783.9 4154255 0
632799.2 4154255 0
632814.4 4154255 0
632829.6 4154255 0
632844.9 4154255 0
632860.1 4154255 0
632875.4 4154255 0
632890.6 4154255 0
632905.8 4154255 0
632921.1 4154255 0
632936.3 4154255 0
632951.6 4154255 0
632966.8 4154255 0
632982 4154255 0
632997.3 4154255 0
633012.5 4154255 0
633027.8 4154255 0
633043 4154255 0
631900 4154270 0
631915.2 4154270 0
631930.5 4154270 0
631945.7 4154270 0
631961 4154270 0
631976.2 4154270 0
631991.4 4154270 0
632006.7 4154270 0
632021.9 4154270 0
632037.2 4154270 0
632052.4 4154270 0
632067.6 4154270 0
632082.9 4154270 0
632098.1 4154270 0
632113.4 4154270 0
632128.6 4154270 0
632143.8 4154270 0
632159.1 4154270 0
632174.3 4154270 0
632189.6 4154270 0
632204.8 4154270 0
632220 4154270 0
632235.3 4154270 0
632250.5 4154270 0
632265.8 4154270 0
632281 4154270 0
632296.2 4154270 0
632311.5 4154270 0
632326.7 4154270 0
632342 4154270 0
632357.2 4154270 0
632372.4 4154270 0
632387.7 4154270 0
632402.9 4154270 0
632418.2 4154270 0
632433.4 4154270 0
632448.6 4154270 0
632463.9 4154270 0
632479.1 4154270 0
632494.4 4154270 0
632509.6 4154270 0
632524.8 4154270 0
632540.1 4154270 0
632555.3 4154270 0
632570.6 4154270 0
632585.8 4154270 0
632601 4154270 0
632616.3 4154270 0
632631.5 4154270 0
632646.8 4154270 0
632662 4154270 0
632677.2 4154270 0
632692.5 4154270 0
632707.7 4154270 0
632723 4154270 0
632738.2 4154270 0
632753.4 4154270 0
632768.7 4154270 0
632783.9 4154270 0
632799.2 4154270 0
632814.4 4154270 0
632829.6 4154270 0
632844.9 4154270 0
632860.1 4154270 0
632875.4 4154270 0
632890.6 4154270 0
632905.8 4154270 0
632921.1 4154270 0
632936.3 4154270 0
632951.6 4154270 0
632966.8 4154270 0
632982 4154270 0
632997.3 4154270 0
633012.5 4154270 0
633027.8 4154270 0
633043 4154270 0
631900 4154286 0
631915.2 4154286 0
631930.5 4154286 0
631945.7 4154286 0
631961 4154286 0
631976.2 4154286 0
631991.4 4154286 0
632006.7 4154286 0
632021.9 4154286 0
632037.2 4154286 0
632052.4 4154286 0
632067.6 4154286 0
632082.9 4154286 0
632098.1 4154286 0
632113.4 4154286 0
632128.6 4154286 0
632143.8 4154286 0
632159.1 4154286 0
632174.3 4154286 0
632189.6 4154286 0
632204.8 4154286 0
632220 4154286 0
632235.3 4154286 0
632250.5 4154286 0
632265.8 4154286 0
632281 4154286 0
632296.2 4154286 0
632311.5 4154286 0
632326.7 4154286 0
632342 4154286 0
632357.2 4154286 0
632372.4 4154286 0
632387.7 4154286 0
632402.9 4154286 0
632418.2 4154286 0
632433.4 4154286 0
632448.6 4154286 0
632463.9 4154286 0
632479.1 4154286 0
632494.4 4154286 0
632509.6 4154286 0
632524.8 4154286 0
632540.1 4154286 0
632555.3 4154286 0
632570.6 4154286 0
632585.8 4154286 0
632601 4154286 0
632616.3 4154286 0
632631.5 4154286 0
632646.8 4154286 0
632662 4154286 0
632677.2 4154286 0
632692.5 4154286 0
632707.7 4154286 0
632723 4154286 0
632738.2 4154286 0
632753.4 4154286 0
632768.7 4154286 0
632783.9 4154286 0
632799.2 4154286 0
632814.4 4154286 0
632829.6 4154286 0
632844.9 4154286 0
632860.1 4154286 0
632875.4 4154286 0
632890.6 4154286 0
632905.8 4154286 0
632921.1 4154286 0
632936.3 4154286 0
632951.6 4154286 0
632966.8 4154286 0
632982 4154286 0
632997.3 4154286 0
633012.5 4154286 0
633027.8 4154286 0
633043 4154286 0
631900 4154301 0
631915.2 4154301 0
631930.5 4154301 0
631945.7 4154301 0
631961 4154301 0
631976.2 4154301 0
631991.4 4154301 0
632006.7 4154301 0
632021.9 4154301 0
632037.2 4154301 0
632052.4 4154301 0
632067.6 4154301 0
632082.9 4154301 0
632098.1 4154301 0
632113.4 4154301 0
632128.6 4154301 0
632143.8 4154301 0
632159.1 4154301 0
632174.3 4154301 0
632189.6 4154301 0
632204.8 4154301 0
632220 4154301 0
632235.3 4154301 0
632250.5 4154301 0
632265.8 4154301 0
632281 4154301 0
632296.2 4154301 0
632311.5 4154301 0
632326.7 4154301 0
632342 4154301 0
632357.2 4154301 0
632372.4 4154301 0
632387.7 4154301 0
632402.9 4154301 0
632418.2 4154301 0
632433.4 4154301 0
632448.6 4154301 0
632463.9 4154301 0
632479.1 4154301 0
632494.4 4154301 0
632509.6 4154301 0
632524.8 4154301 0
632540.1 4154301 0
632555.3 4154301 0
632570.6 4154301 0
632585.8 4154301 0
632601 4154301 0
632616.3 4154301 0
632631.5 4154301 0
632646.8 4154301 0
632662 4154301 0
632677.2 4154301 0
632692.5 4154301 0
632707.7 4154301 0
632723 4154301 0
632738.2 4154301 0
632753.4 4154301 0
632768.7 4154301 0
632783.9 4154301 0
632799.2 4154301 0
632814.4 4154301 0
632829.6 4154301 0
632844.9 4154301 0
632860.1 4154301 0
632875.4 4154301 0
632890.6 4154301 0
632905.8 4154301 0
632921.1 4154301 0
632936.3 4154301 0
632951.6 4154301 0
632966.8 4154301 0
632982 4154301 0
632997.3 4154301 0
633012.5 4154301 0
633027.8 4154301 0
633043 4154301 0
631900 4154316 0
631915.2 4154316 0
631930.5 4154316 0
631945.7 4154316 0
631961 4154316 0
631976.2 4154316 0
631991.4 4154316 0
632006.7 4154316 0
632021.9 4154316 0
632037.2 4154316 0
632052.4 4154316 0
632067.6 4154316 0
632082.9 4154316 0
632098.1 4154316 0
632113.4 4154316 0
632128.6 4154316 0
632143.8 4154316 0
632159.1 4154316 0
632174.3 4154316 0
632189.6 4154316 0
632204.8 4154316 0
632220 4154316 0
632235.3 4154316 0
632250.5 4154316 0
632265.8 4154316 0
632281 4154316 0
632296.2 4154316 0
632311.5 4154316 0
632326.7 4154316 0
632342 4154316 0
632357.2 4154316 0
632372.4 4154316 0
632387.7 4154316 0
632402.9 4154316 0
632418.2 4154316 0
632433.4 4154316 0
632448.6 4154316 0
632463.9 4154316 0
632479.1 4154316 0
632494.4 4154316 0
632509.6 4154316 0
632524.8 4154316 0
632540.1 4154316 0
632555.3 4154316 0
632570.6 4154316 0
632585.8 4154316 0
632601 4154316 0
632616.3 4154316 0
632631.5 4154316 0
632646.8 4154316 0
632662 4154316 0
632677.2 4154316 0
632692.5 4154316 0
632707.7 4154316 0
632723 4154316 0
632738.2 4154316 0
632753.4 4154316 0
632768.7 4154316 0
632783.9 4154316 0
632799.2 4154316 0
632814.4 4154316 0
632829.6 4154316 0
632844.9 4154316 0
632860.1 4154316 0
632875.4 4154316 0
632890.6 4154316 0
632905.8 4154316 0
632921.1 4154316 0
632936.3 4154316 0
632951.6 4154316 0
632966.8 4154316 0
632982 4154316 0
632997.3 4154316 0
633012.5 4154316 0
633027.8 4154316 0
633043 4154316 0
631900 4154331 0
631915.2 4154331 0
631930.5 4154331 0
631945.7 4154331 0
631961 4154331 0
631976.2 4154331 0
631991.4 4154331 0
632006.7 4154331 0
632021.9 4154331 0
632037.2 4154331 0
632052.4 4154331 0
632067.6 4154331 0
632082.9 4154331 0
632098.1 4154331 0
632113.4 4154331 0
632128.6 4154331 0
632143.8 4154331 0
632159.1 4154331 0
632174.3 4154331 0
632189.6 4154331 0
632204.8 4154331 0
632220 4154331 0
632235.3 4154331 0
632250.5 4154331 0
632265.8 4154331 0
632281 4154331 0
632296.2 4154331 0
632311.5 4154331 0
632326.7 4154331 0
632342 4154331 0
632357.2 4154331 0
632372.4 4154331 0
632387.7 4154331 0
632402.9 4154331 0
632418.2 4154331 0
632433.4 4154331 0
632448.6 4154331 0
632463.9 4154331 0
632479.1 4154331 0
632494.4 4154331 0
632509.6 4154331 0
632524.8 4154331 0
632540.1 4154331 0
632555.3 4154331 0
632570.6 4154331 0
632585.8 4154331 0
632601 4154331 0
632616.3 4154331 0
632631.5 4154331 0
632646.8 4154331 0
632662 4154331 0
632677.2 4154331 0
632692.5 4154331 0
632707.7 4154331 0
632723 4154331 0
632738.2 4154331 0
632753.4 4154331 0
632768.7 4154331 0
632783.9 4154331 0
632799.2 4154331 0
632814.4 4154331 0
632829.6 4154331 0
632844.9 4154331 0
632860.1 4154331 0
632875.4 4154331 0
632890.6 4154331 0
632905.8 4154331 0
632921.1 4154331 0
632936.3 4154331 0
632951.6 4154331 0
632966.8 4154331 0
632982 4154331 0
632997.3 4154331 0
633012.5 4154331 0
633027.8 4154331 0
633043 4154331 0
631900 4154347 0
631915.2 4154347 0
631930.5 4154347 0
631945.7 4154347 0
631961 4154347 0
631976.2 4154347 0
631991.4 4154347 0
632006.7 4154347 0
632021.9 4154347 0
632037.2 4154347 0
632052.4 4154347 0
632067.6 4154347 0
632082.9 4154347 0
632098.1 4154347 0
632113.4 4154347 0
632128.6 4154347 0
632143.8 4154347 0
632159.1 4154347 0
632174.3 4154347 0
632189.6 4154347 0
632204.8 4154347 0
632220 4154347 0
632235.3 4154347 0
632250.5 4154347 0
632265.8 4154347 0
632281 4154347 0
632296.2 4154347 0
632311.5 4154347 0
632326.7 4154347 0
632342 4154347 0
632357.2 4154347 0
632372.4 4154347 0
632387.7 4154347 0
632402.9 4154347 0
632418.2 4154347 0
632433.4 4154347 0
632448.6 4154347 0
632463.9 4154347 0
632479.1 4154347 0
632494.4 4154347 0
632509.6 4154347 0
632524.8 4154347 0
632540.1 4154347 0
632555.3 4154347 0
632570.6 4154347 0
632585.8 4154347 0
632601 4154347 0
632616.3 4154347 0
632631.5 4154347 0
632646.8 4154347 0
632662 4154347 0
632677.2 4154347 0
632692.5 4154347 0
632707.7 4154347 0
632723 4154347 0
632738.2 4154347 0
632753.4 4154347 0
632768.7 4154347 0
632783.9 4154347 0
632799.2 4154347 0
632814.4 4154347 0
632829.6 4154347 0
632844.9 4154347 0
632860.1 4154347 0
632875.4 4154347 0
632890.6 4154347 0
632905.8 4154347 0
632921.1 4154347 0
632936.3 4154347 0
632951.6 4154347 0
632966.8 4154347 0
632982 4154347 0
632997.3 4154347 0
633012.5 4154347 0
633027.8 4154347 0
633043 4154347 0
631900 4154362 0
631915.2 4154362 0
631930.5 4154362 0
631945.7 4154362 0
631961 4154362 0
631976.2 4154362 0
631991.4 4154362 0
632006.7 4154362 0
632021.9 4154362 0
632037.2 4154362 0
632052.4 4154362 0
632067.6 4154362 0
632082.9 4154362 0
632098.1 4154362 0
632113.4 4154362 0
632128.6 4154362 0
632143.8 4154362 0
632159.1 4154362 0
632174.3 4154362 0
632189.6 4154362 0
632204.8 4154362 0
632220 4154362 0
632235.3 4154362 0
632250.5 4154362 0
632265.8 4154362 0
632281 4154362 0
632296.2 4154362 0
632311.5 4154362 0
632326.7 4154362 0
632342 4154362 0
632357.2 4154362 0
632372.4 4154362 0
632387.7 4154362 0
632402.9 4154362 0
632418.2 4154362 0
632433.4 4154362 0
632448.6 4154362 0
632463.9 4154362 0
632479.1 4154362 0
632494.4 4154362 0
632509.6 4154362 0
632524.8 4154362 0
632540.1 4154362 0
632555.3 4154362 0
632570.6 4154362 0
632585.8 4154362 0
632601 4154362 0
632616.3 4154362 0
632631.5 4154362 0
632646.8 4154362 0
632662 4154362 0
632677.2 4154362 0
632692.5 4154362 0
632707.7 4154362 0
632723 4154362 0
632738.2 4154362 0
632753.4 4154362 0
632768.7 4154362 0
632783.9 4154362 0
632799.2 4154362 0
632814.4 4154362 0
632829.6 4154362 0
632844.9 4154362 0
632860.1 4154362 0
632875.4 4154362 0
632890.6 4154362 0
632905.8 4154362 0
632921.1 4154362 0
632936.3 4154362 0
632951.6 4154362 0
632966.8 4154362 0
632982 4154362 0
632997.3 4154362 0
633012.5 4154362 0
633027.8 4154362 0
633043 4154362 0
631900 4154377 0
631915.2 4154377 0
631930.5 4154377 0
631945.7 4154377 0
631961 4154377 0
631976.2 4154377 0
631991.4 4154377 0
632006.7 4154377 0
632021.9 4154377 0
632037.2 4154377 0
632052.4 4154377 0
632067.6 4154377 0
632082.9 4154377 0
632098.1 4154377 0
632113.4 4154377 0
632128.6 4154377 0
632143.8 4154377 0
632159.1 4154377 0
632174.3 4154377 0
632189.6 4154377 0
632204.8 4154377 0
632220 4154377 0
632235.3 4154377 0
632250.5 4154377 0
632265.8 4154377 0
632281 4154377 0
632296.2 4154377 0
632311.5 4154377 0
632326.7 4154377 0
632342 4154377 0
632357.2 4154377 0
632372.4 4154377 0
632387.7 4154377 0
632402.9 4154377 0
632418.2 4154377 0
632433.4 4154377 0
632448.6 4154377 0
632463.9 4154377 0
632479.1 4154377 0
632494.4 4154377 0
632509.6 4154377 0
632524.8 4154377 0
632540.1 4154377 0
632555.3 4154377 0
632570.6 4154377 0
632585.8 4154377 0
632601 4154377 0
632616.3 4154377 0
632631.5 4154377 0
632646.8 4154377 0
632662 4154377 0
632677.2 4154377 0
632692.5 4154377 0
632707.7 4154377 0
632723 4154377 0
632738.2 4154377 0
632753.4 4154377 0
632768.7 4154377 0
632783.9 4154377 0
632799.2 4154377 0
632814.4 4154377 0
632829.6 4154377 0
632844.9 4154377 0
632860.1 4154377 0
632875.4 4154377 0
632890.6 4154377 0
632905.8 4154377 0
632921.1 4154377 0
632936.3 4154377 0
632951.6 4154377 0
632966.8 4154377 0
632982 4154377 0
632997.3 4154377 0
633012.5 4154377 0
633027.8 4154377 0
633043 4154377 0
631900 4154392 0
631915.2 4154392 0
631930.5 4154392 0
631945.7 4154392 0
631961 4154392 0
631976.2 4154392 0
631991.4 4154392 0
632006.7 4154392 0
632021.9 4154392 0
632037.2 4154392 0
632052.4 4154392 0
632067.6 4154392 0
632082.9 4154392 0
632098.1 4154392 0
632113.4 4154392 0
632128.6 4154392 0
632143.8 4154392 0
632159.1 4154392 0
632174.3 4154392 0
632189.6 4154392 0
632204.8 4154392 0
632220 4154392 0
632235.3 4154392 0
632250.5 4154392 0
632265.8 4154392 0
632281 4154392 0
632296.2 4154392 0
632311.5 4154392 0
632326.7 4154392 0
632342 4154392 0
632357.2 4154392 0
632372.4 4154392 0
632387.7 4154392 0
632402.9 4154392 0
632418.2 4154392 0
632433.4 4154392 0
632448.6 4154392 0
632463.9 4154392 0
632479.1 4154392 0
632494.4 4154392 0
632509.6 4154392 0
632524.8 4154392 0
632540.1 4154392 0
632555.3 4154392 0
632570.6 4154392 0
632585.8 4154392 0
632601 4154392 0
632616.3 4154392 0
632631.5 4154392 0
632646.8 4154392 0
632662 4154392 0
632677.2 4154392 0
632692.5 4154392 0
632707.7 4154392 0
632723 4154392 0
632738.2 4154392 0
632753.4 4154392 0
632768.7 4154392 0
632783.9 4154392 0
632799.2 4154392 0
632814.4 4154392 0
632829.6 4154392 0
632844.9 4154392 0
632860.1 4154392 0
632875.4 4154392 0
632890.6 4154392 0
632905.8 4154392 0
632921.1 4154392 0
632936.3 4154392 0
632951.6 4154392 0
632966.8 4154392 0
632982 4154392 0
632997.3 4154392 0
633012.5 4154392 0
633027.8 4154392 0
633043 4154392 0
631900 4154408 0
631915.2 4154408 0
631930.5 4154408 0
631945.7 4154408 0
631961 4154408 0
631976.2 4154408 0
631991.4 4154408 0
632006.7 4154408 0
632021.9 4154408 0
632037.2 4154408 0
632052.4 4154408 0
632067.6 4154408 0
632082.9 4154408 0
632098.1 4154408 0
632113.4 4154408 0
632128.6 4154408 0
632143.8 4154408 0
632159.1 4154408 0
632174.3 4154408 0
632189.6 4154408 0
632204.8 4154408 0
632220 4154408 0
632235.3 4154408 0
632250.5 4154408 0
632265.8 4154408 0
632281 4154408 0
632296.2 4154408 0
632311.5 4154408 0
632326.7 4154408 0
632342 4154408 0
632357.2 4154408 0
632372.4 4154408 0
632387.7 4154408 0
632402.9 4154408 0
632418.2 4154408 0
632433.4 4154408 0
632448.6 4154408 0
632463.9 4154408 0
632479.1 4154408 0
632494.4 4154408 0
632509.6 4154408 0
632524.8 4154408 0
632540.1 4154408 0
632555.3 4154408 0
632570.6 4154408 0
632585.8 4154408 0
632601 4154408 0
632616.3 4154408 0
632631.5 4154408 0
632646.8 4154408 0
632662 4154408 0
632677.2 4154408 0
632692.5 4154408 0
632707.7 4154408 0
632723 4154408 0
632738.2 4154408 0
632753.4 4154408 0
632768.7 4154408 0
632783.9 4154408 0
632799.2 4154408 0
632814.4 4154408 0
632829.6 4154408 0
632844.9 4154408 0
632860.1 4154408 0
632875.4 4154408 0
632890.6 4154408 0
632905.8 4154408 0
632921.1 4154408 0
632936.3 4154408 0
632951.6 4154408 0
632966.8 4154408 0
632982 4154408 0
632997.3 4154408 0
633012.5 4154408 0
633027.8 4154408 0
633043 4154408 0
631900 4154423 0
631915.2 4154423 0
631930.5 4154423 0
631945.7 4154423 0
631961 4154423 0
631976.2 4154423 0
631991.4 4154423 0
632006.7 4154423 0
632021.9 4154423 0
632037.2 4154423 0
632052.4 4154423 0
632067.6 4154423 0
632082.9 4154423 0
632098.1 4154423 0
632113.4 4154423 0
632128.6 4154423 0
632143.8 4154423 0
632159.1 4154423 0
632174.3 4154423 0
632189.6 4154423 0
632204.8 4154423 0
632220 4154423 0
632235.3 4154423 0
632250.5 4154423 0
632265.8 4154423 0
632281 4154423 0
632296.2 4154423 0
632311.5 4154423 0
632326.7 4154423 0
632342 4154423 0
632357.2 4154423 0
632372.4 4154423 0
632387.7 4154423 0
632402.9 4154423 0
632418.2 4154423 0
632433.4 4154423 0
632448.6 4154423 0
632463.9 4154423 0
632479.1 4154423 0
632494.4 4154423 0
632509.6 4154423 0
632524.8 4154423 0
632540.1 4154423 0
632555.3 4154423 0
632570.6 4154423 0
632585.8 4154423 0
632601 4154423 0
632616.3 4154423 0
632631.5 4154423 0
632646.8 4154423 0
632662 4154423 0
632677.2 4154423 0
632692.5 4154423 0
632707.7 4154423 0
632723 4154423 0
632738.2 4154423 0
632753.4 4154423 0
632768.7 4154423 0
632783.9 4154423 0
632799.2 4154423 0
632814.4 4154423 0
632829.6 4154423 0
632844.9 4154423 0
632860.1 4154423 0
632875.4 4154423 0
632890.6 4154423 0
632905.8 4154423 0
632921.1 4154423 0
632936.3 4154423 0
632951.6 4154423 0
632966.8 4154423 0
632982 4154423 0
632997.3 4154423 0
633012.5 4154423 0
633027.8 4154423 0
633043 4154423 0
631900 4154438 0
631915.2 4154438 0
631930.5 4154438 0
631945.7 4154438 0
631961 4154438 0
631976.2 4154438 0
631991.4 4154438 0
632006.7 4154438 0
632021.9 4154438 0
632037.2 4154438 0
632052.4 4154438 0
632067.6 4154438 0
632082.9 4154438 0
632098.1 4154438 0
632113.4 4154438 0
632128.6 4154438 0
632143.8 4154438 0
632159.1 4154438 0
632174.3 4154438 0
632189.6 4154438 0
632204.8 4154438 0
632220 4154438 0
632235.3 4154438 0
632250.5 4154438 0
632265.8 4154438 0
632281 4154438 0
632296.2 4154438 0
632311.5 4154438 0
632326.7 4154438 0
632342 4154438 0
632357.2 4154438 0
632372.4 4154438 0
632387.7 4154438 0
632402.9 4154438 0
632418.2 4154438 0
632433.4 4154438 0
632448.6 4154438 0
632463.9 4154438 0
632479.1 4154438 0
632494.4 4154438 0
632509.6 4154438 0
632524.8 4154438 0
632540.1 4154438 0
632555.3 4154438 0
632570.6 4154438 0
632585.8 4154438 0
632601 4154438 0
632616.3 4154438 0
632631.5 4154438 0
632646.8 4154438 0
632662 4154438 0
632677.2 4154438 0
632692.5 4154438 0
632707.7 4154438 0
632723 4154438 0
632738.2 4154438 0
632753.4 4154438 0
632768.7 4154438 0
632783.9 4154438 0
632799.2 4154438 0
632814.4 4154438 0
632829.6 4154438 0
632844.9 4154438 0
632860.1 4154438 0
632875.4 4154438 0
632890.6 4154438 0
632905.8 4154438 0
632921.1 4154438 0
632936.3 4154438 0
632951.6 4154438 0
632966.8 4154438 0
632982 4154438 0
632997.3 4154438 0
633012.5 4154438 0
633027.8 4154438 0
633043 4154438 0
631900 4154453 0
631915.2 4154453 0
631930.5 4154453 0
631945.7 4154453 0
631961 4154453 0
631976.2 4154453 0
631991.4 4154453 0
632006.7 4154453 0
632021.9 4154453 0
632037.2 4154453 0
632052.4 4154453 0
632067.6 4154453 0
632082.9 4154453 0
632098.1 4154453 0
632113.4 4154453 0
632128.6 4154453 0
632143.8 4154453 0
632159.1 4154453 0
632174.3 4154453 0
632189.6 4154453 0
632204.8 4154453 0
632220 4154453 0
632235.3 4154453 0
632250.5 4154453 0
632265.8 4154453 0
632281 4154453 0
632296.2 4154453 0
632311.5 4154453 0
632326.7 4154453 0
632342 4154453 0
632357.2 4154453 0
632372.4 4154453 0
632387.7 4154453 0
632402.9 4154453 0
632418.2 4154453 0
632433.4 4154453 0
632448.6 4154453 0
632463.9 4154453 0
632479.1 4154453 0
632494.4 4154453 0
632509.6 4154453 0
632524.8 4154453 0
632540.1 4154453 0
632555.3 4154453 0
632570.6 4154453 0
632585.8 4154453 0
632601 4154453 0
632616.3 4154453 0
632631.5 4154453 0
632646.8 4154453 0
632662 4154453 0
632677.2 4154453 0
632692.5 4154453 0
632707.7 4154453 0
632723 4154453 0
632738.2 4154453 0
632753.4 4154453 0
632768.7 4154453 0
632783.9 4154453 0
632799.2 4154453 0
632814.4 4154453 0
632829.6 4154453 0
632844.9 4154453 0
632860.1 4154453 0
632875.4 4154453 0
632890.6 4154453 0
632905.8 4154453 0
632921.1 4154453 0
632936.3 4154453 0
632951.6 4154453 0
632966.8 4154453 0
632982 4154453 0
632997.3 4154453 0
633012.5 4154453 0
633027.8 4154453 0
633043 4154453 0
631900 4154469 0
631915.2 4154469 0
631930.5 4154469 0
631945.7 4154469 0
631961 4154469 0
631976.2 4154469 0
631991.4 4154469 0
632006.7 4154469 0
632021.9 4154469 0
632037.2 4154469 0
632052.4 4154469 0
632067.6 4154469 0
632082.9 4154469 0
632098.1 4154469 0
632113.4 4154469 0
632128.6 4154469 0
632143.8 4154469 0
632159.1 4154469 0
632174.3 4154469 0
632189.6 4154469 0
632204.8 4154469 0
632220 4154469 0
632235.3 4154469 0
632250.5 4154469 0
632265.8 4154469 0
632281 4154469 0
632296.2 4154469 0
632311.5 4154469 0
632326.7 4154469 0
632342 4154469 0
632357.2 4154469 0
632372.4 4154469 0
632387.7 4154469 0
632402.9 4154469 0
632418.2 4154469 0
632433.4 4154469 0
632448.6 4154469 0
632463.9 4154469 0
632479.1 4154469 0
632494.4 4154469 0
632540.1 4154469 0
632555.3 4154469 0
632570.6 4154469 0
632585.8 4154469 0
632601 4154469 0
632616.3 4154469 0
632631.5 4154469 0
632646.8 4154469 0
632662 4154469 0
632677.2 4154469 0
632692.5 4154469 0
632707.7 4154469 0
632723 4154469 0
632738.2 4154469 0
632753.4 4154469 0
632768.7 4154469 0
632783.9 4154469 0
632799.2 4154469 0
632814.4 4154469 0
632829.6 4154469 0
632844.9 4154469 0
632860.1 4154469 0
632875.4 4154469 0
632890.6 4154469 0
632905.8 4154469 0
632921.1 4154469 0
632936.3 4154469 0
632951.6 4154469 0
632966.8 4154469 0
632982 4154469 0
632997.3 4154469 0
633012.5 4154469 0
633027.8 4154469 0
633043 4154469 0
631900 4154484 0
631915.2 4154484 0
631930.5 4154484 0
631945.7 4154484 0
631961 4154484 0
631976.2 4154484 0
631991.4 4154484 0
632006.7 4154484 0
632021.9 4154484 0
632037.2 4154484 0
632052.4 4154484 0
632067.6 4154484 0
632082.9 4154484 0
632098.1 4154484 0
632113.4 4154484 0
632128.6 4154484 0
632143.8 4154484 0
632159.1 4154484 0
632174.3 4154484 0
632189.6 4154484 0
632204.8 4154484 0
632220 4154484 0
632235.3 4154484 0
632250.5 4154484 0
632265.8 4154484 0
632281 4154484 0
632296.2 4154484 0
632311.5 4154484 0
632326.7 4154484 0
632342 4154484 0
632357.2 4154484 0
632372.4 4154484 0
632387.7 4154484 0
632402.9 4154484 0
632418.2 4154484 0
632433.4 4154484 0
632448.6 4154484 0
632463.9 4154484 0
632570.6 4154484 0
632585.8 4154484 0
632601 4154484 0
632616.3 4154484 0
632631.5 4154484 0
632646.8 4154484 0
632662 4154484 0
632677.2 4154484 0
632692.5 4154484 0
632707.7 4154484 0
632723 4154484 0
632738.2 4154484 0
632753.4 4154484 0
632768.7 4154484 0
632783.9 4154484 0
632799.2 4154484 0
632814.4 4154484 0
632829.6 4154484 0
632844.9 4154484 0
632860.1 4154484 0
632875.4 4154484 0
632890.6 4154484 0
632905.8 4154484 0
632921.1 4154484 0
632936.3 4154484 0
632951.6 4154484 0
632966.8 4154484 0
632982 4154484 0
632997.3 4154484 0
633012.5 4154484 0
633027.8 4154484 0
633043 4154484 0
631900 4154499 0
631915.2 4154499 0
631930.5 4154499 0
631945.7 4154499 0
631961 4154499 0
631976.2 4154499 0
631991.4 4154499 0
632006.7 4154499 0
632021.9 4154499 0
632037.2 4154499 0
632052.4 4154499 0
632067.6 4154499 0
632082.9 4154499 0
632098.1 4154499 0
632113.4 4154499 0
632128.6 4154499 0
632143.8 4154499 0
632159.1 4154499 0
632174.3 4154499 0
632189.6 4154499 0
632204.8 4154499 0
632220 4154499 0
632235.3 4154499 0
632250.5 4154499 0
632265.8 4154499 0
632281 4154499 0
632296.2 4154499 0
632311.5 4154499 0
632326.7 4154499 0
632342 4154499 0
632357.2 4154499 0
632372.4 4154499 0
632387.7 4154499 0
632402.9 4154499 0
632418.2 4154499 0
632433.4 4154499 0
632448.6 4154499 0
632463.9 4154499 0
632601 4154499 0
632616.3 4154499 0
632631.5 4154499 0
632646.8 4154499 0
632662 4154499 0
632677.2 4154499 0
632692.5 4154499 0
632707.7 4154499 0
632723 4154499 0
632738.2 4154499 0
632753.4 4154499 0
632768.7 4154499 0
632783.9 4154499 0
632799.2 4154499 0
632814.4 4154499 0
632829.6 4154499 0
632844.9 4154499 0
632860.1 4154499 0
632875.4 4154499 0
632890.6 4154499 0
632905.8 4154499 0
632921.1 4154499 0
632936.3 4154499 0
632951.6 4154499 0
632966.8 4154499 0
632982 4154499 0
632997.3 4154499 0
633012.5 4154499 0
633027.8 4154499 0
633043 4154499 0
631900 4154514 0
631915.2 4154514 0
631930.5 4154514 0
631945.7 4154514 0
631961 4154514 0
631976.2 4154514 0
631991.4 4154514 0
632006.7 4154514 0
632021.9 4154514 0
632037.2 4154514 0
632052.4 4154514 0
632067.6 4154514 0
632082.9 4154514 0
632098.1 4154514 0
632113.4 4154514 0
632128.6 4154514 0
632143.8 4154514 0
632159.1 4154514 0
632174.3 4154514 0
632189.6 4154514 0
632204.8 4154514 0
632220 4154514 0
632235.3 4154514 0
632250.5 4154514 0
632265.8 4154514 0
632281 4154514 0
632296.2 4154514 0
632311.5 4154514 0
632326.7 4154514 0
632342 4154514 0
632357.2 4154514 0
632372.4 4154514 0
632387.7 4154514 0
632402.9 4154514 0
632418.2 4154514 0
632433.4 4154514 0
632448.6 4154514 0
632463.9 4154514 0
632631.5 4154514 0
632646.8 4154514 0
632662 4154514 0
632677.2 4154514 0
632692.5 4154514 0
632707.7 4154514 0
632723 4154514 0
632738.2 4154514 0
632753.4 4154514 0
632768.7 4154514 0
632783.9 4154514 0
632799.2 4154514 0
632814.4 4154514 0
632829.6 4154514 0
632844.9 4154514 0
632860.1 4154514 0
632875.4 4154514 0
632890.6 4154514 0
632905.8 4154514 0
632921.1 4154514 0
632936.3 4154514 0
632951.6 4154514 0
632966.8 4154514 0
632982 4154514 0
632997.3 4154514 0
633012.5 4154514 0
633027.8 4154514 0
633043 4154514 0
631900 4154530 0
631915.2 4154530 0
631930.5 4154530 0
631945.7 4154530 0
631961 4154530 0
631976.2 4154530 0
631991.4 4154530 0
632006.7 4154530 0
632021.9 4154530 0
632037.2 4154530 0
632052.4 4154530 0
632067.6 4154530 0
632082.9 4154530 0
632098.1 4154530 0
632113.4 4154530 0
632128.6 4154530 0
632143.8 4154530 0
632159.1 4154530 0
632174.3 4154530 0
632189.6 4154530 0
632204.8 4154530 0
632220 4154530 0
632235.3 4154530 0
632250.5 4154530 0
632265.8 4154530 0
632281 4154530 0
632296.2 4154530 0
632311.5 4154530 0
632326.7 4154530 0
632342 4154530 0
632357.2 4154530 0
632372.4 4154530 0
632387.7 4154530 0
632402.9 4154530 0
632418.2 4154530 0
632433.4 4154530 0
632448.6 4154530 0
632463.9 4154530 0
632677.2 4154530 0
632692.5 4154530 0
632707.7 4154530 0
632723 4154530 0
632738.2 4154530 0
632753.4 4154530 0
632768.7 4154530 0
632783.9 4154530 0
632799.2 4154530 0
632814.4 4154530 0
632829.6 4154530 0
632844.9 4154530 0
632860.1 4154530 0
632875.4 4154530 0
632890.6 4154530 0
632905.8 4154530 0
632921.1 4154530 0
632936.3 4154530 0
632951.6 4154530 0
632966.8 4154530 0
632982 4154530 0
632997.3 4154530 0
633012.5 4154530 0
633027.8 4154530 0
633043 4154530 0
631900 4154545 0
631915.2 4154545 0
631930.5 4154545 0
631945.7 4154545 0
631961 4154545 0
631976.2 4154545 0
631991.4 4154545 0
632006.7 4154545 0
632021.9 4154545 0
632037.2 4154545 0
632052.4 4154545 0
632067.6 4154545 0
632082.9 4154545 0
632098.1 4154545 0
632113.4 4154545 0
632128.6 4154545 0
632143.8 4154545 0
632159.1 4154545 0
632174.3 4154545 0
632189.6 4154545 0
632204.8 4154545 0
632220 4154545 0
632235.3 4154545 0
632250.5 4154545 0
632265.8 4154545 0
632281 4154545 0
632296.2 4154545 0
632311.5 4154545 0
632326.7 4154545 0
632342 4154545 0
632357.2 4154545 0
632372.4 4154545 0
632387.7 4154545 0
632402.9 4154545 0
632418.2 4154545 0
632433.4 4154545 0
632448.6 4154545 0
632463.9 4154545 0
632692.5 4154545 0
632707.7 4154545 0
632723 4154545 0
632738.2 4154545 0
632753.4 4154545 0
632768.7 4154545 0
632783.9 4154545 0
632799.2 4154545 0
632814.4 4154545 0
632829.6 4154545 0
632844.9 4154545 0
632860.1 4154545 0
632875.4 4154545 0
632890.6 4154545 0
632905.8 4154545 0
632921.1 4154545 0
632936.3 4154545 0
632951.6 4154545 0
632966.8 4154545 0
632982 4154545 0
632997.3 4154545 0
633012.5 4154545 0
633027.8 4154545 0
633043 4154545 0
631900 4154560 0
631915.2 4154560 0
631930.5 4154560 0
631945.7 4154560 0
631961 4154560 0
631976.2 4154560 0
631991.4 4154560 0
632006.7 4154560 0
632021.9 4154560 0
632037.2 4154560 0
632052.4 4154560 0
632067.6 4154560 0
632082.9 4154560 0
632098.1 4154560 0
632113.4 4154560 0
632128.6 4154560 0
632143.8 4154560 0
632159.1 4154560 0
632174.3 4154560 0
632189.6 4154560 0
632204.8 4154560 0
632220 4154560 0
632235.3 4154560 0
632250.5 4154560 0
632265.8 4154560 0
632281 4154560 0
632296.2 4154560 0
632311.5 4154560 0
632326.7 4154560 0
632342 4154560 0
632357.2 4154560 0
632372.4 4154560 0
632387.7 4154560 0
632402.9 4154560 0
632418.2 4154560 0
632433.4 4154560 0
632448.6 4154560 0
632463.9 4154560 0
632707.7 4154560 0
632723 4154560 0
632738.2 4154560 0
632753.4 4154560 0
632768.7 4154560 0
632783.9 4154560 0
632799.2 4154560 0
632814.4 4154560 0
632829.6 4154560 0
632844.9 4154560 0
632860.1 4154560 0
632875.4 4154560 0
632890.6 4154560 0
632905.8 4154560 0
632921.1 4154560 0
632936.3 4154560 0
632951.6 4154560 0
632966.8 4154560 0
632982 4154560 0
632997.3 4154560 0
633012.5 4154560 0
633027.8 4154560 0
633043 4154560 0
631900 4154575 0
631915.2 4154575 0
631930.5 4154575 0
631945.7 4154575 0
631961 4154575 0
631976.2 4154575 0
631991.4 4154575 0
632006.7 4154575 0
632021.9 4154575 0
632037.2 4154575 0
632052.4 4154575 0
632067.6 4154575 0
632082.9 4154575 0
632098.1 4154575 0
632113.4 4154575 0
632128.6 4154575 0
632143.8 4154575 0
632159.1 4154575 0
632174.3 4154575 0
632189.6 4154575 0
632204.8 4154575 0
632220 4154575 0
632235.3 4154575 0
632250.5 4154575 0
632265.8 4154575 0
632281 4154575 0
632296.2 4154575 0
632311.5 4154575 0
632326.7 4154575 0
632342 4154575 0
632357.2 4154575 0
632372.4 4154575 0
632387.7 4154575 0
632402.9 4154575 0
632418.2 4154575 0
632433.4 4154575 0
632448.6 4154575 0
632463.9 4154575 0
632677.2 4154575 0
632692.5 4154575 0
632707.7 4154575 0
632723 4154575 0
632738.2 4154575 0
632753.4 4154575 0
632768.7 4154575 0
632783.9 4154575 0
632799.2 4154575 0
632814.4 4154575 0
632829.6 4154575 0
632844.9 4154575 0
632860.1 4154575 0
632875.4 4154575 0
632890.6 4154575 0
632905.8 4154575 0
632921.1 4154575 0
632936.3 4154575 0
632951.6 4154575 0
632966.8 4154575 0
632982 4154575 0
632997.3 4154575 0
633012.5 4154575 0
633027.8 4154575 0
633043 4154575 0
631900 4154591 0
631915.2 4154591 0
631930.5 4154591 0
631945.7 4154591 0
631961 4154591 0
631976.2 4154591 0
631991.4 4154591 0
632006.7 4154591 0
632021.9 4154591 0
632037.2 4154591 0
632052.4 4154591 0
632067.6 4154591 0
632082.9 4154591 0
632098.1 4154591 0
632113.4 4154591 0
632128.6 4154591 0
632143.8 4154591 0
632159.1 4154591 0
632174.3 4154591 0
632189.6 4154591 0
632204.8 4154591 0
632220 4154591 0
632235.3 4154591 0
632250.5 4154591 0
632265.8 4154591 0
632281 4154591 0
632296.2 4154591 0
632311.5 4154591 0
632326.7 4154591 0
632342 4154591 0
632357.2 4154591 0
632372.4 4154591 0
632387.7 4154591 0
632402.9 4154591 0
632418.2 4154591 0
632433.4 4154591 0
632448.6 4154591 0
632463.9 4154591 0
632479.1 4154591 0
632662 4154591 0
632677.2 4154591 0
632692.5 4154591 0
632707.7 4154591 0
632723 4154591 0
632738.2 4154591 0
632753.4 4154591 0
632768.7 4154591 0
632783.9 4154591 0
632799.2 4154591 0
632814.4 4154591 0
632829.6 4154591 0
632844.9 4154591 0
632860.1 4154591 0
632875.4 4154591 0
632890.6 4154591 0
632905.8 4154591 0
632921.1 4154591 0
632936.3 4154591 0
632951.6 4154591 0
632966.8 4154591 0
632982 4154591 0
632997.3 4154591 0
633012.5 4154591 0
633027.8 4154591 0
633043 4154591 0
631900 4154606 0
631915.2 4154606 0
631930.5 4154606 0
631945.7 4154606 0
631961 4154606 0
631976.2 4154606 0
631991.4 4154606 0
632006.7 4154606 0
632021.9 4154606 0
632037.2 4154606 0
632052.4 4154606 0
632067.6 4154606 0
632082.9 4154606 0
632098.1 4154606 0
632113.4 4154606 0
632128.6 4154606 0
632143.8 4154606 0
632159.1 4154606 0
632174.3 4154606 0
632189.6 4154606 0
632204.8 4154606 0
632220 4154606 0
632235.3 4154606 0
632250.5 4154606 0
632265.8 4154606 0
632281 4154606 0
632296.2 4154606 0
632311.5 4154606 0
632326.7 4154606 0
632342 4154606 0
632357.2 4154606 0
632372.4 4154606 0
632387.7 4154606 0
632402.9 4154606 0
632418.2 4154606 0
632433.4 4154606 0
632448.6 4154606 0
632463.9 4154606 0
632479.1 4154606 0
632494.4 4154606 0
632509.6 4154606 0
632631.5 4154606 0
632646.8 4154606 0
632662 4154606 0
632677.2 4154606 0
632692.5 4154606 0
632707.7 4154606 0
632723 4154606 0
632738.2 4154606 0
632753.4 4154606 0
632768.7 4154606 0
632783.9 4154606 0
632799.2 4154606 0
632814.4 4154606 0
632829.6 4154606 0
632844.9 4154606 0
632860.1 4154606 0
632875.4 4154606 0
632890.6 4154606 0
632905.8 4154606 0
632921.1 4154606 0
632936.3 4154606 0
632951.6 4154606 0
632966.8 4154606 0
632982 4154606 0
632997.3 4154606 0
633012.5 4154606 0
633027.8 4154606 0
633043 4154606 0
631900 4154621 0
631915.2 4154621 0
631930.5 4154621 0
631945.7 4154621 0
631961 4154621 0
631976.2 4154621 0
631991.4 4154621 0
632006.7 4154621 0
632021.9 4154621 0
632037.2 4154621 0
632052.4 4154621 0
632067.6 4154621 0
632082.9 4154621 0
632098.1 4154621 0
632113.4 4154621 0
632128.6 4154621 0
632143.8 4154621 0
632159.1 4154621 0
632174.3 4154621 0
632189.6 4154621 0
632204.8 4154621 0
632220 4154621 0
632235.3 4154621 0
632250.5 4154621 0
632265.8 4154621 0
632281 4154621 0
632296.2 4154621 0
632311.5 4154621 0
632326.7 4154621 0
632342 4154621 0
632357.2 4154621 0
632372.4 4154621 0
632387.7 4154621 0
632402.9 4154621 0
632418.2 4154621 0
632433.4 4154621 0
632448.6 4154621 0
632463.9 4154621 0
632479.1 4154621 0
632494.4 4154621 0
632509.6 4154621 0
632524.8 4154621 0
632540.1 4154621 0
632631.5 4154621 0
632646.8 4154621 0
632662 4154621 0
632677.2 4154621 0
632692.5 4154621 0
632707.7 4154621 0
632723 4154621 0
632738.2 4154621 0
632753.4 4154621 0
632768.7 4154621 0
632783.9 4154621 0
632799.2 4154621 0
632814.4 4154621 0
632829.6 4154621 0
632844.9 4154621 0
632860.1 4154621 0
632875.4 4154621 0
632890.6 4154621 0
632905.8 4154621 0
632921.1 4154621 0
632936.3 4154621 0
632951.6 4154621 0
632966.8 4154621 0
632982 4154621 0
632997.3 4154621 0
633012.5 4154621 0
633027.8 4154621 0
633043 4154621 0
631900 4154636 0
631915.2 4154636 0
631930.5 4154636 0
631945.7 4154636 0
631961 4154636 0
631976.2 4154636 0
631991.4 4154636 0
632006.7 4154636 0
632021.9 4154636 0
632037.2 4154636 0
632052.4 4154636 0
632067.6 4154636 0
632082.9 4154636 0
632098.1 4154636 0
632113.4 4154636 0
632128.6 4154636 0
632143.8 4154636 0
632159.1 4154636 0
632174.3 4154636 0
632189.6 4154636 0
632204.8 4154636 0
632220 4154636 0
632235.3 4154636 0
632250.5 4154636 0
632265.8 4154636 0
632281 4154636 0
632296.2 4154636 0
632311.5 4154636 0
632326.7 4154636 0
632342 4154636 0
632357.2 4154636 0
632372.4 4154636 0
632387.7 4154636 0
632402.9 4154636 0
632418.2 4154636 0
632433.4 4154636 0
632448.6 4154636 0
632463.9 4154636 0
632479.1 4154636 0
632494.4 4154636 0
632509.6 4154636 0
632524.8 4154636 0
632540.1 4154636 0
632555.3 4154636 0
632616.3 4154636 0
632631.5 4154636 0
632646.8 4154636 0
632662 4154636 0
632677.2 4154636 0
632692.5 4154636 0
632707.7 4154636 0
632723 4154636 0
632738.2 4154636 0
632753.4 4154636 0
632768.7 4154636 0
632783.9 4154636 0
632799.2 4154636 0
632814.4 4154636 0
632829.6 4154636 0
632844.9 4154636 0
632860.1 4154636 0
632875.4 4154636 0
632890.6 4154636 0
632905.8 4154636 0
632921.1 4154636 0
632936.3 4154636 0
632951.6 4154636 0
632966.8 4154636 0
632982 4154636 0
632997.3 4154636 0
633012.5 4154636 0
633027.8 4154636 0
633043 4154636 0
631900 4154651 0
631915.2 4154651 0
631930.5 4154651 0
631945.7 4154651 0
631961 4154651 0
631976.2 4154651 0
631991.4 4154651 0
632006.7 4154651 0
632021.9 4154651 0
632037.2 4154651 0
632052.4 4154651 0
632067.6 4154651 0
632082.9 4154651 0
632098.1 4154651 0
632113.4 4154651 0
632128.6 4154651 0
632143.8 4154651 0
632159.1 4154651 0
632174.3 4154651 0
632189.6 4154651 0
632204.8 4154651 0
632220 4154651 0
632235.3 4154651 0
632250.5 4154651 0
632265.8 4154651 0
632281 4154651 0
632296.2 4154651 0
632311.5 4154651 0
632326.7 4154651 0
632342 4154651 0
632357.2 4154651 0
632372.4 4154651 0
632387.7 4154651 0
632402.9 4154651 0
632418.2 4154651 0
632433.4 4154651 0
632448.6 4154651 0
632463.9 4154651 0
632479.1 4154651 0
632494.4 4154651 0
632509.6 4154651 0
632524.8 4154651 0
632540.1 4154651 0
632555.3 4154651 0
632601 4154651 0
632616.3 4154651 0
632631.5 4154651 0
632646.8 4154651 0
632662 4154651 0
632677.2 4154651 0
632692.5 4154651 0
632707.7 4154651 0
632723 4154651 0
632738.2 4154651 0
632753.4 4154651 0
632768.7 4154651 0
632783.9 4154651 0
632799.2 4154651 0
632814.4 4154651 0
632829.6 4154651 0
632844.9 4154651 0
632860.1 4154651 0
632875.4 4154651 0
632890.6 4154651 0
632905.8 4154651 0
632921.1 4154651 0
632936.3 4154651 0
632951.6 4154651 0
632966.8 4154651 0
632982 4154651 0
632997.3 4154651 0
633012.5 4154651 0
633027.8 4154651 0
633043 4154651 0
631900 4154667 0
631915.2 4154667 0
631930.5 4154667 0
631945.7 4154667 0
631961 4154667 0
631976.2 4154667 0
631991.4 4154667 0
632006.7 4154667 0
632021.9 4154667 0
632037.2 4154667 0
632052.4 4154667 0
632067.6 4154667 0
632082.9 4154667 0
632098.1 4154667 0
632113.4 4154667 0
632128.6 4154667 0
632143.8 4154667 0
632159.1 4154667 0
632174.3 4154667 0
632189.6 4154667 0
632204.8 4154667 0
632220 4154667 0
632235.3 4154667 0
632250.5 4154667 0
632265.8 4154667 0
632281 4154667 0
632296.2 4154667 0
632311.5 4154667 0
632326.7 4154667 0
632342 4154667 0
632357.2 4154667 0
632372.4 4154667 0
632387.7 4154667 0
632402.9 4154667 0
632418.2 4154667 0
632433.4 4154667 0
632448.6 4154667 0
632463.9 4154667 0
632479.1 4154667 0
632494.4 4154667 0
632509.6 4154667 0
632524.8 4154667 0
632601 4154667 0
632616.3 4154667 0
632631.5 4154667 0
632646.8 4154667 0
632662 4154667 0
632677.2 4154667 0
632692.5 4154667 0
632707.7 4154667 0
632723 4154667 0
632738.2 4154667 0
632753.4 4154667 0
632768.7 4154667 0
632783.9 4154667 0
632799.2 4154667 0
632814.4 4154667 0
632829.6 4154667 0
632844.9 4154667 0
632860.1 4154667 0
632875.4 4154667 0
632890.6 4154667 0
632905.8 4154667 0
632921.1 4154667 0
632936.3 4154667 0
632951.6 4154667 0
632966.8 4154667 0
632982 4154667 0
632997.3 4154667 0
633012.5 4154667 0
633027.8 4154667 0
633043 4154667 0
631900 4154682 0
631915.2 4154682 0
631930.5 4154682 0
631945.7 4154682 0
631961 4154682 0
631976.2 4154682 0
631991.4 4154682 0
632006.7 4154682 0
632021.9 4154682 0
632037.2 4154682 0
632052.4 4154682 0
632067.6 4154682 0
632082.9 4154682 0
632098.1 4154682 0
632113.4 4154682 0
632128.6 4154682 0
632143.8 4154682 0
632159.1 4154682 0
632174.3 4154682 0
632189.6 4154682 0
632204.8 4154682 0
632220 4154682 0
632235.3 4154682 0
632250.5 4154682 0
632265.8 4154682 0
632281 4154682 0
632296.2 4154682 0
632311.5 4154682 0
632326.7 4154682 0
632342 4154682 0
632357.2 4154682 0
632372.4 4154682 0
632387.7 4154682 0
632402.9 4154682 0
632418.2 4154682 0
632433.4 4154682 0
632448.6 4154682 0
632463.9 4154682 0
632479.1 4154682 0
632494.4 4154682 0
632616.3 4154682 0
632631.5 4154682 0
632646.8 4154682 0
632662 4154682 0
632677.2 4154682 0
632692.5 4154682 0
632707.7 4154682 0
632723 4154682 0
632738.2 4154682 0
632753.4 4154682 0
632768.7 4154682 0
632783.9 4154682 0
632799.2 4154682 0
632814.4 4154682 0
632829.6 4154682 0
632844.9 4154682 0
632860.1 4154682 0
632875.4 4154682 0
632890.6 4154682 0
632905.8 4154682 0
632921.1 4154682 0
632936.3 4154682 0
632951.6 4154682 0
632966.8 4154682 0
632982 4154682 0
632997.3 4154682 0
633012.5 4154682 0
633027.8 4154682 0
633043 4154682 0
631900 4154697 0
631915.2 4154697 0
631930.5 4154697 0
631945.7 4154697 0
631961 4154697 0
631976.2 4154697 0
631991.4 4154697 0
632006.7 4154697 0
632021.9 4154697 0
632037.2 4154697 0
632052.4 4154697 0
632067.6 4154697 0
632082.9 4154697 0
632098.1 4154697 0
632113.4 4154697 0
632128.6 4154697 0
632143.8 4154697 0
632159.1 4154697 0
632174.3 4154697 0
632189.6 4154697 0
632204.8 4154697 0
632220 4154697 0
632235.3 4154697 0
632250.5 4154697 0
632265.8 4154697 0
632281 4154697 0
632296.2 4154697 0
632311.5 4154697 0
632326.7 4154697 0
632342 4154697 0
632357.2 4154697 0
632372.4 4154697 0
632387.7 4154697 0
632402.9 4154697 0
632418.2 4154697 0
632433.4 4154697 0
632448.6 4154697 0
632463.9 4154697 0
632616.3 4154697 0
632631.5 4154697 0
632646.8 4154697 0
632662 4154697 0
632677.2 4154697 0
632692.5 4154697 0
632707.7 4154697 0
632723 4154697 0
632738.2 4154697 0
632753.4 4154697 0
632768.7 4154697 0
632783.9 4154697 0
632799.2 4154697 0
632814.4 4154697 0
632829.6 4154697 0
632844.9 4154697 0
632860.1 4154697 0
632875.4 4154697 0
632890.6 4154697 0
632905.8 4154697 0
632921.1 4154697 0
632936.3 4154697 0
632951.6 4154697 0
632966.8 4154697 0
632982 4154697 0
632997.3 4154697 0
633012.5 4154697 0
633027.8 4154697 0
633043 4154697 0
631900 4154712 0
631915.2 4154712 0
631930.5 4154712 0
631945.7 4154712 0
631961 4154712 0
631976.2 4154712 0
631991.4 4154712 0
632006.7 4154712 0
632021.9 4154712 0
632037.2 4154712 0
632052.4 4154712 0
632067.6 4154712 0
632082.9 4154712 0
632098.1 4154712 0
632113.4 4154712 0
632128.6 4154712 0
632143.8 4154712 0
632159.1 4154712 0
632174.3 4154712 0
632189.6 4154712 0
632204.8 4154712 0
632220 4154712 0
632235.3 4154712 0
632250.5 4154712 0
632265.8 4154712 0
632281 4154712 0
632296.2 4154712 0
632311.5 4154712 0
632326.7 4154712 0
632342 4154712 0
632357.2 4154712 0
632372.4 4154712 0
632387.7 4154712 0
632402.9 4154712 0
632418.2 4154712 0
632433.4 4154712 0
632448.6 4154712 0
632616.3 4154712 0
632631.5 4154712 0
632646.8 4154712 0
632662 4154712 0
632677.2 4154712 0
632692.5 4154712 0
632707.7 4154712 0
632723 4154712 0
632738.2 4154712 0
632753.4 4154712 0
632768.7 4154712 0
632783.9 4154712 0
632799.2 4154712 0
632814.4 4154712 0
632829.6 4154712 0
632844.9 4154712 0
632860.1 4154712 0
632875.4 4154712 0
632890.6 4154712 0
632905.8 4154712 0
632921.1 4154712 0
632936.3 4154712 0
632951.6 4154712 0
632966.8 4154712 0
632982 4154712 0
632997.3 4154712 0
633012.5 4154712 0
633027.8 4154712 0
633043 4154712 0
631900 4154728 0
631915.2 4154728 0
631930.5 4154728 0
631945.7 4154728 0
631961 4154728 0
631976.2 4154728 0
631991.4 4154728 0
632006.7 4154728 0
632021.9 4154728 0
632037.2 4154728 0
632052.4 4154728 0
632067.6 4154728 0
632082.9 4154728 0
632098.1 4154728 0
632113.4 4154728 0
632128.6 4154728 0
632143.8 4154728 0
632159.1 4154728 0
632174.3 4154728 0
632189.6 4154728 0
632204.8 4154728 0
632220 4154728 0
632235.3 4154728 0
632250.5 4154728 0
632265.8 4154728 0
632281 4154728 0
632296.2 4154728 0
632311.5 4154728 0
632326.7 4154728 0
632342 4154728 0
632357.2 4154728 0
632372.4 4154728 0
632387.7 4154728 0
632402.9 4154728 0
632418.2 4154728 0
632433.4 4154728 0
632448.6 4154728 0
632616.3 4154728 0
632631.5 4154728 0
632646.8 4154728 0
632662 4154728 0
632677.2 4154728 0
632692.5 4154728 0
632707.7 4154728 0
632723 4154728 0
632738.2 4154728 0
632753.4 4154728 0
632768.7 4154728 0
632783.9 4154728 0
632799.2 4154728 0
632814.4 4154728 0
632829.6 4154728 0
632844.9 4154728 0
632860.1 4154728 0
632875.4 4154728 0
632890.6 4154728 0
632905.8 4154728 0
632921.1 4154728 0
632936.3 4154728 0
632951.6 4154728 0
632966.8 4154728 0
632982 4154728 0
632997.3 4154728 0
633012.5 4154728 0
633027.8 4154728 0
633043 4154728 0
631900 4154743 0
631915.2 4154743 0
631930.5 4154743 0
631945.7 4154743 0
631961 4154743 0
631976.2 4154743 0
631991.4 4154743 0
632006.7 4154743 0
632021.9 4154743 0
632037.2 4154743 0
632052.4 4154743 0
632067.6 4154743 0
632082.9 4154743 0
632098.1 4154743 0
632113.4 4154743 0
632128.6 4154743 0
632143.8 4154743 0
632159.1 4154743 0
632174.3 4154743 0
632189.6 4154743 0
632204.8 4154743 0
632220 4154743 0
632235.3 4154743 0
632250.5 4154743 0
632265.8 4154743 0
632281 4154743 0
632296.2 4154743 0
632311.5 4154743 0
632326.7 4154743 0
632342 4154743 0
632357.2 4154743 0
632372.4 4154743 0
632387.7 4154743 0
632402.9 4154743 0
632418.2 4154743 0
632433.4 4154743 0
632616.3 4154743 0
632631.5 4154743 0
632646.8 4154743 0
632662 4154743 0
632677.2 4154743 0
632692.5 4154743 0
632707.7 4154743 0
632723 4154743 0
632738.2 4154743 0
632753.4 4154743 0
632768.7 4154743 0
632783.9 4154743 0
632799.2 4154743 0
632814.4 4154743 0
632829.6 4154743 0
632844.9 4154743 0
632860.1 4154743 0
632875.4 4154743 0
632890.6 4154743 0
632905.8 4154743 0
632921.1 4154743 0
632936.3 4154743 0
632951.6 4154743 0
632966.8 4154743 0
632982 4154743 0
632997.3 4154743 0
633012.5 4154743 0
633027.8 4154743 0
633043 4154743 0
631900 4154758 0
631915.2 4154758 0
631930.5 4154758 0
631945.7 4154758 0
631961 4154758 0
631976.2 4154758 0
631991.4 4154758 0
632006.7 4154758 0
632021.9 4154758 0
632037.2 4154758 0
632052.4 4154758 0
632067.6 4154758 0
632082.9 4154758 0
632098.1 4154758 0
632113.4 4154758 0
632128.6 4154758 0
632143.8 4154758 0
632159.1 4154758 0
632174.3 4154758 0
632189.6 4154758 0
632204.8 4154758 0
632220 4154758 0
632235.3 4154758 0
632250.5 4154758 0
632265.8 4154758 0
632281 4154758 0
632296.2 4154758 0
632311.5 4154758 0
632326.7 4154758 0
632342 4154758 0
632357.2 4154758 0
632372.4 4154758 0
632387.7 4154758 0
632402.9 4154758 0
632418.2 4154758 0
632433.4 4154758 0
632601 4154758 0
632616.3 4154758 0
632631.5 4154758 0
632646.8 4154758 0
632662 4154758 0
632677.2 4154758 0
632692.5 4154758 0
632707.7 4154758 0
632723 4154758 0
632738.2 4154758 0
632753.4 4154758 0
632768.7 4154758 0
632783.9 4154758 0
632799.2 4154758 0
632814.4 4154758 0
632829.6 4154758 0
632844.9 4154758 0
632860.1 4154758 0
632875.4 4154758 0
632890.6 4154758 0
632905.8 4154758 0
632921.1 4154758 0
632936.3 4154758 0
632951.6 4154758 0
632966.8 4154758 0
632982 4154758 0
632997.3 4154758 0
633012.5 4154758 0
633027.8 4154758 0
633043 4154758 0
631900 4154773 0
631915.2 4154773 0
631930.5 4154773 0
631945.7 4154773 0
631961 4154773 0
631976.2 4154773 0
631991.4 4154773 0
632006.7 4154773 0
632021.9 4154773 0
632037.2 4154773 0
632052.4 4154773 0
632067.6 4154773 0
632082.9 4154773 0
632098.1 4154773 0
632113.4 4154773 0
632128.6 4154773 0
632143.8 4154773 0
632159.1 4154773 0
632174.3 4154773 0
632189.6 4154773 0
632204.8 4154773 0
632220 4154773 0
632235.3 4154773 0
632250.5 4154773 0
632265.8 4154773 0
632281 4154773 0
632296.2 4154773 0
632311.5 4154773 0
632326.7 4154773 0
632342 4154773 0
632357.2 4154773 0
632372.4 4154773 0
632387.7 4154773 0
632402.9 4154773 0
632418.2 4154773 0
632601 4154773 0
632616.3 4154773 0
632631.5 4154773 0
632646.8 4154773 0
632662 4154773 0
632677.2 4154773 0
632692.5 4154773 0
632707.7 4154773 0
632723 4154773 0
632738.2 4154773 0
632753.4 4154773 0
632768.7 4154773 0
632783.9 4154773 0
632799.2 4154773 0
632814.4 4154773 0
632829.6 4154773 0
632844.9 4154773 0
632860.1 4154773 0
632875.4 4154773 0
632890.6 4154773 0
632905.8 4154773 0
632921.1 4154773 0
632936.3 4154773 0
632951.6 4154773 0
632966.8 4154773 0
632982 4154773 0
632997.3 4154773 0
633012.5 4154773 0
633027.8 4154773 0
633043 4154773 0
631900 4154789 0
631915.2 4154789 0
631930.5 4154789 0
631945.7 4154789 0
631961 4154789 0
631976.2 4154789 0
631991.4 4154789 0
632006.7 4154789 0
632021.9 4154789 0
632037.2 4154789 0
632052.4 4154789 0
632067.6 4154789 0
632082.9 4154789 0
632098.1 4154789 0
632113.4 4154789 0
632128.6 4154789 0
632143.8 4154789 0
632159.1 4154789 0
632174.3 4154789 0
632189.6 4154789 0
632204.8 4154789 0
632220 4154789 0
632235.3 4154789 0
632250.5 4154789 0
632265.8 4154789 0
632281 4154789 0
632296.2 4154789 0
632311.5 4154789 0
632326.7 4154789 0
632342 4154789 0
632357.2 4154789 0
632372.4 4154789 0
632387.7 4154789 0
632402.9 4154789 0
632601 4154789 0
632616.3 4154789 0
632631.5 4154789 0
632646.8 4154789 0
632662 4154789 0
632677.2 4154789 0
632692.5 4154789 0
632707.7 4154789 0
632723 4154789 0
632738.2 4154789 0
632753.4 4154789 0
632768.7 4154789 0
632783.9 4154789 0
632799.2 4154789 0
632814.4 4154789 0
632829.6 4154789 0
632844.9 4154789 0
632860.1 4154789 0
632875.4 4154789 0
632890.6 4154789 0
632905.8 4154789 0
632921.1 4154789 0
632936.3 4154789 0
632951.6 4154789 0
632966.8 4154789 0
632982 4154789 0
632997.3 4154789 0
633012.5 4154789 0
633027.8 4154789 0
633043 4154789 0
631900 4154804 0
631915.2 4154804 0
631930.5 4154804 0
631945.7 4154804 0
631961 4154804 0
631976.2 4154804 0
631991.4 4154804 0
632006.7 4154804 0
632021.9 4154804 0
632037.2 4154804 0
632052.4 4154804 0
632067.6 4154804 0
632082.9 4154804 0
632098.1 4154804 0
632113.4 4154804 0
632128.6 4154804 0
632143.8 4154804 0
632159.1 4154804 0
632174.3 4154804 0
632189.6 4154804 0
632204.8 4154804 0
632220 4154804 0
632235.3 4154804 0
632250.5 4154804 0
632265.8 4154804 0
632281 4154804 0
632296.2 4154804 0
632311.5 4154804 0
632326.7 4154804 0
632342 4154804 0
632357.2 4154804 0
632372.4 4154804 0
632387.7 4154804 0
632402.9 4154804 0
632585.8 4154804 0
632601 4154804 0
632616.3 4154804 0
632631.5 4154804 0
632646.8 4154804 0
632662 4154804 0
632677.2 4154804 0
632692.5 4154804 0
632707.7 4154804 0
632723 4154804 0
632738.2 4154804 0
632753.4 4154804 0
632768.7 4154804 0
632783.9 4154804 0
632799.2 4154804 0
632814.4 4154804 0
632829.6 4154804 0
632844.9 4154804 0
632860.1 4154804 0
632875.4 4154804 0
632890.6 4154804 0
632905.8 4154804 0
632921.1 4154804 0
632936.3 4154804 0
632951.6 4154804 0
632966.8 4154804 0
632982 4154804 0
632997.3 4154804 0
633012.5 4154804 0
633027.8 4154804 0
633043 4154804 0
631900 4154819 0
631915.2 4154819 0
631930.5 4154819 0
631945.7 4154819 0
631961 4154819 0
631976.2 4154819 0
631991.4 4154819 0
632006.7 4154819 0
632021.9 4154819 0
632037.2 4154819 0
632052.4 4154819 0
632067.6 4154819 0
632082.9 4154819 0
632098.1 4154819 0
632113.4 4154819 0
632128.6 4154819 0
632143.8 4154819 0
632159.1 4154819 0
632174.3 4154819 0
632189.6 4154819 0
632204.8 4154819 0
632220 4154819 0
632235.3 4154819 0
632250.5 4154819 0
632265.8 4154819 0
632281 4154819 0
632296.2 4154819 0
632311.5 4154819 0
632326.7 4154819 0
632342 4154819 0
632357.2 4154819 0
632372.4 4154819 0
632387.7 4154819 0
632585.8 4154819 0
632601 4154819 0
632616.3 4154819 0
632631.5 4154819 0
632646.8 4154819 0
632662 4154819 0
632677.2 4154819 0
632692.5 4154819 0
632707.7 4154819 0
632723 4154819 0
632738.2 4154819 0
632753.4 4154819 0
632768.7 4154819 0
632783.9 4154819 0
632799.2 4154819 0
632814.4 4154819 0
632829.6 4154819 0
632844.9 4154819 0
632860.1 4154819 0
632875.4 4154819 0
632890.6 4154819 0
632905.8 4154819 0
632921.1 4154819 0
632936.3 4154819 0
632951.6 4154819 0
632966.8 4154819 0
632982 4154819 0
632997.3 4154819 0
633012.5 4154819 0
633027.8 4154819 0
633043 4154819 0
631900 4154834 0
631915.2 4154834 0
631930.5 4154834 0
631945.7 4154834 0
631961 4154834 0
631976.2 4154834 0
631991.4 4154834 0
632006.7 4154834 0
632021.9 4154834 0
632037.2 4154834 0
632052.4 4154834 0
632067.6 4154834 0
632082.9 4154834 0
632098.1 4154834 0
632113.4 4154834 0
632128.6 4154834 0
632143.8 4154834 0
632159.1 4154834 0
632174.3 4154834 0
632189.6 4154834 0
632204.8 4154834 0
632220 4154834 0
632235.3 4154834 0
632250.5 4154834 0
632265.8 4154834 0
632281 4154834 0
632296.2 4154834 0
632311.5 4154834 0
632326.7 4154834 0
632342 4154834 0
632357.2 4154834 0
632372.4 4154834 0
632570.6 4154834 0
632585.8 4154834 0
632601 4154834 0
632616.3 4154834 0
632631.5 4154834 0
632646.8 4154834 0
632662 4154834 0
632677.2 4154834 0
632692.5 4154834 0
632707.7 4154834 0
632723 4154834 0
632738.2 4154834 0
632753.4 4154834 0
632768.7 4154834 0
632783.9 4154834 0
632799.2 4154834 0
632814.4 4154834 0
632829.6 4154834 0
632844.9 4154834 0
632860.1 4154834 0
632875.4 4154834 0
632890.6 4154834 0
632905.8 4154834 0
632921.1 4154834 0
632936.3 4154834 0
632951.6 4154834 0
632966.8 4154834 0
632982 4154834 0
632997.3 4154834 0
633012.5 4154834 0
633027.8 4154834 0
633043 4154834 0
631900 4154850 0
631915.2 4154850 0
631930.5 4154850 0
631945.7 4154850 0
631961 4154850 0
631976.2 4154850 0
631991.4 4154850 0
632006.7 4154850 0
632021.9 4154850 0
632037.2 4154850 0
632052.4 4154850 0
632067.6 4154850 0
632082.9 4154850 0
632098.1 4154850 0
632113.4 4154850 0
632128.6 4154850 0
632143.8 4154850 0
632159.1 4154850 0
632174.3 4154850 0
632189.6 4154850 0
632204.8 4154850 0
632220 4154850 0
632235.3 4154850 0
632250.5 4154850 0
632265.8 4154850 0
632281 4154850 0
632296.2 4154850 0
632311.5 4154850 0
632326.7 4154850 0
632342 4154850 0
632357.2 4154850 0
632372.4 4154850 0
632570.6 4154850 0
632585.8 4154850 0
632601 4154850 0
632616.3 4154850 0
632631.5 4154850 0
632646.8 4154850 0
632662 4154850 0
632677.2 4154850 0
632692.5 4154850 0
632707.7 4154850 0
632723 4154850 0
632738.2 4154850 0
632753.4 4154850 0
632768.7 4154850 0
632783.9 4154850 0
632799.2 4154850 0
632814.4 4154850 0
632829.6 4154850 0
632844.9 4154850 0
632860.1 4154850 0
632875.4 4154850 0
632890.6 4154850 0
632905.8 4154850 0
632921.1 4154850 0
632936.3 4154850 0
632951.6 4154850 0
632966.8 4154850 0
632982 4154850 0
632997.3 4154850 0
633012.5 4154850 0
633027.8 4154850 0
633043 4154850 0
631900 4154865 0
631915.2 4154865 0
631930.5 4154865 0
631945.7 4154865 0
631961 4154865 0
631976.2 4154865 0
631991.4 4154865 0
632006.7 4154865 0
632021.9 4154865 0
632037.2 4154865 0
632052.4 4154865 0
632067.6 4154865 0
632082.9 4154865 0
632098.1 4154865 0
632113.4 4154865 0
632128.6 4154865 0
632143.8 4154865 0
632159.1 4154865 0
632174.3 4154865 0
632189.6 4154865 0
632204.8 4154865 0
632220 4154865 0
632235.3 4154865 0
632250.5 4154865 0
632265.8 4154865 0
632281 4154865 0
632296.2 4154865 0
632311.5 4154865 0
632326.7 4154865 0
632342 4154865 0
632357.2 4154865 0
632570.6 4154865 0
632585.8 4154865 0
632601 4154865 0
632616.3 4154865 0
632631.5 4154865 0
632646.8 4154865 0
632662 4154865 0
632677.2 4154865 0
632692.5 4154865 0
632707.7 4154865 0
632723 4154865 0
632738.2 4154865 0
632753.4 4154865 0
632768.7 4154865 0
632783.9 4154865 0
632799.2 4154865 0
632814.4 4154865 0
632829.6 4154865 0
632844.9 4154865 0
632860.1 4154865 0
632875.4 4154865 0
632890.6 4154865 0
632905.8 4154865 0
632921.1 4154865 0
632936.3 4154865 0
632951.6 4154865 0
632966.8 4154865 0
632982 4154865 0
632997.3 4154865 0
633012.5 4154865 0
633027.8 4154865 0
633043 4154865 0
631900 4154880 0
631915.2 4154880 0
631930.5 4154880 0
631945.7 4154880 0
631961 4154880 0
631976.2 4154880 0
631991.4 4154880 0
632006.7 4154880 0
632021.9 4154880 0
632037.2 4154880 0
632052.4 4154880 0
632067.6 4154880 0
632082.9 4154880 0
632098.1 4154880 0
632113.4 4154880 0
632128.6 4154880 0
632143.8 4154880 0
632159.1 4154880 0
632174.3 4154880 0
632189.6 4154880 0
632204.8 4154880 0
632220 4154880 0
632235.3 4154880 0
632250.5 4154880 0
632265.8 4154880 0
632281 4154880 0
632296.2 4154880 0
632311.5 4154880 0
632326.7 4154880 0
632342 4154880 0
632570.6 4154880 0
632585.8 4154880 0
632601 4154880 0
632616.3 4154880 0
632631.5 4154880 0
632646.8 4154880 0
632662 4154880 0
632677.2 4154880 0
632692.5 4154880 0
632707.7 4154880 0
632723 4154880 0
632738.2 4154880 0
632753.4 4154880 0
632768.7 4154880 0
632783.9 4154880 0
632799.2 4154880 0
632814.4 4154880 0
632829.6 4154880 0
632844.9 4154880 0
632860.1 4154880 0
632875.4 4154880 0
632890.6 4154880 0
632905.8 4154880 0
632921.1 4154880 0
632936.3 4154880 0
632951.6 4154880 0
632966.8 4154880 0
632982 4154880 0
632997.3 4154880 0
633012.5 4154880 0
633027.8 4154880 0
633043 4154880 0
631900 4154895 0
631915.2 4154895 0
631930.5 4154895 0
631945.7 4154895 0
631961 4154895 0
631976.2 4154895 0
631991.4 4154895 0
632006.7 4154895 0
632021.9 4154895 0
632037.2 4154895 0
632052.4 4154895 0
632067.6 4154895 0
632082.9 4154895 0
632098.1 4154895 0
632113.4 4154895 0
632128.6 4154895 0
632143.8 4154895 0
632159.1 4154895 0
632174.3 4154895 0
632189.6 4154895 0
632204.8 4154895 0
632220 4154895 0
632235.3 4154895 0
632250.5 4154895 0
632265.8 4154895 0
632281 4154895 0
632296.2 4154895 0
632311.5 4154895 0
632326.7 4154895 0
632570.6 4154895 0
632585.8 4154895 0
632601 4154895 0
632616.3 4154895 0
632631.5 4154895 0
632646.8 4154895 0
632662 4154895 0
632677.2 4154895 0
632692.5 4154895 0
632707.7 4154895 0
632723 4154895 0
632738.2 4154895 0
632753.4 4154895 0
632768.7 4154895 0
632783.9 4154895 0
632799.2 4154895 0
632814.4 4154895 0
632829.6 4154895 0
632844.9 4154895 0
632860.1 4154895 0
632875.4 4154895 0
632890.6 4154895 0
632905.8 4154895 0
632921.1 4154895 0
632936.3 4154895 0
632951.6 4154895 0
632966.8 4154895 0
632982 4154895 0
632997.3 4154895 0
633012.5 4154895 0
633027.8 4154895 0
633043 4154895 0
631900 4154911 0
631915.2 4154911 0
631930.5 4154911 0
631945.7 4154911 0
631961 4154911 0
631976.2 4154911 0
631991.4 4154911 0
632006.7 4154911 0
632021.9 4154911 0
632037.2 4154911 0
632052.4 4154911 0
632067.6 4154911 0
632082.9 4154911 0
632098.1 4154911 0
632113.4 4154911 0
632128.6 4154911 0
632143.8 4154911 0
632159.1 4154911 0
632174.3 4154911 0
632189.6 4154911 0
632204.8 4154911 0
632220 4154911 0
632235.3 4154911 0
632250.5 4154911 0
632265.8 4154911 0
632281 4154911 0
632296.2 4154911 0
632555.3 4154911 0
632570.6 4154911 0
632585.8 4154911 0
632601 4154911 0
632616.3 4154911 0
632631.5 4154911 0
632646.8 4154911 0
632662 4154911 0
632677.2 4154911 0
632692.5 4154911 0
632707.7 4154911 0
632723 4154911 0
632738.2 4154911 0
632753.4 4154911 0
632768.7 4154911 0
632783.9 4154911 0
632799.2 4154911 0
632814.4 4154911 0
632829.6 4154911 0
632844.9 4154911 0
632860.1 4154911 0
632875.4 4154911 0
632890.6 4154911 0
632905.8 4154911 0
632921.1 4154911 0
632936.3 4154911 0
632951.6 4154911 0
632966.8 4154911 0
632982 4154911 0
632997.3 4154911 0
633012.5 4154911 0
633027.8 4154911 0
633043 4154911 0
631900 4154926 0
631915.2 4154926 0
631930.5 4154926 0
631945.7 4154926 0
631961 4154926 0
631976.2 4154926 0
631991.4 4154926 0
632006.7 4154926 0
632021.9 4154926 0
632037.2 4154926 0
632052.4 4154926 0
632067.6 4154926 0
632082.9 4154926 0
632098.1 4154926 0
632113.4 4154926 0
632128.6 4154926 0
632143.8 4154926 0
632159.1 4154926 0
632174.3 4154926 0
632189.6 4154926 0
632204.8 4154926 0
632220 4154926 0
632235.3 4154926 0
632250.5 4154926 0
632265.8 4154926 0
632281 4154926 0
632555.3 4154926 0
632570.6 4154926 0
632585.8 4154926 0
632601 4154926 0
632616.3 4154926 0
632631.5 4154926 0
632646.8 4154926 0
632662 4154926 0
632677.2 4154926 0
632692.5 4154926 0
632707.7 4154926 0
632723 4154926 0
632738.2 4154926 0
632753.4 4154926 0
632768.7 4154926 0
632783.9 4154926 0
632799.2 4154926 0
632814.4 4154926 0
632829.6 4154926 0
632844.9 4154926 0
632860.1 4154926 0
632875.4 4154926 0
632890.6 4154926 0
632905.8 4154926 0
632921.1 4154926 0
632936.3 4154926 0
632951.6 4154926 0
632966.8 4154926 0
632982 4154926 0
632997.3 4154926 0
633012.5 4154926 0
633027.8 4154926 0
633043 4154926 0
631900 4154941 0
631915.2 4154941 0
631930.5 4154941 0
631945.7 4154941 0
631961 4154941 0
631976.2 4154941 0
631991.4 4154941 0
632006.7 4154941 0
632021.9 4154941 0
632037.2 4154941 0
632052.4 4154941 0
632067.6 4154941 0
632082.9 4154941 0
632098.1 4154941 0
632113.4 4154941 0
632128.6 4154941 0
632143.8 4154941 0
632159.1 4154941 0
632174.3 4154941 0
632189.6 4154941 0
632204.8 4154941 0
632220 4154941 0
632235.3 4154941 0
632250.5 4154941 0
632265.8 4154941 0
632540.1 4154941 0
632555.3 4154941 0
632570.6 4154941 0
632585.8 4154941 0
632601 4154941 0
632616.3 4154941 0
632631.5 4154941 0
632646.8 4154941 0
632662 4154941 0
632677.2 4154941 0
632692.5 4154941 0
632707.7 4154941 0
632723 4154941 0
632738.2 4154941 0
632753.4 4154941 0
632768.7 4154941 0
632783.9 4154941 0
632799.2 4154941 0
632814.4 4154941 0
632829.6 4154941 0
632844.9 4154941 0
632860.1 4154941 0
632875.4 4154941 0
632890.6 4154941 0
632905.8 4154941 0
632921.1 4154941 0
632936.3 4154941 0
632951.6 4154941 0
632966.8 4154941 0
632982 4154941 0
632997.3 4154941 0
633012.5 4154941 0
633027.8 4154941 0
633043 4154941 0
631900 4154956 0
631915.2 4154956 0
631930.5 4154956 0
631945.7 4154956 0
631961 4154956 0
631976.2 4154956 0
631991.4 4154956 0
632006.7 4154956 0
632021.9 4154956 0
632037.2 4154956 0
632052.4 4154956 0
632067.6 4154956 0
632082.9 4154956 0
632098.1 4154956 0
632113.4 4154956 0
632128.6 4154956 0
632143.8 4154956 0
632159.1 4154956 0
632174.3 4154956 0
632189.6 4154956 0
632204.8 4154956 0
632220 4154956 0
632235.3 4154956 0
632524.8 4154956 0
632540.1 4154956 0
632555.3 4154956 0
632570.6 4154956 0
632585.8 4154956 0
632601 4154956 0
632616.3 4154956 0
632631.5 4154956 0
632646.8 4154956 0
632662 4154956 0
632677.2 4154956 0
632692.5 4154956 0
632707.7 4154956 0
632723 4154956 0
632738.2 4154956 0
632753.4 4154956 0
632768.7 4154956 0
632783.9 4154956 0
632799.2 4154956 0
632814.4 4154956 0
632829.6 4154956 0
632844.9 4154956 0
632860.1 4154956 0
632875.4 4154956 0
632890.6 4154956 0
632905.8 4154956 0
632921.1 4154956 0
632936.3 4154956 0
632951.6 4154956 0
632966.8 4154956 0
632982 4154956 0
632997.3 4154956 0
633012.5 4154956 0
633027.8 4154956 0
633043 4154956 0
631900 4154972 0
631915.2 4154972 0
631930.5 4154972 0
631945.7 4154972 0
631961 4154972 0
631976.2 4154972 0
631991.4 4154972 0
632006.7 4154972 0
632021.9 4154972 0
632037.2 4154972 0
632052.4 4154972 0
632067.6 4154972 0
632082.9 4154972 0
632098.1 4154972 0
632113.4 4154972 0
632128.6 4154972 0
632143.8 4154972 0
632159.1 4154972 0
632174.3 4154972 0
632189.6 4154972 0
632204.8 4154972 0
632220 4154972 0
632509.6 4154972 0
632524.8 4154972 0
632540.1 4154972 0
632555.3 4154972 0
632570.6 4154972 0
632585.8 4154972 0
632601 4154972 0
632616.3 4154972 0
632631.5 4154972 0
632646.8 4154972 0
632662 4154972 0
632677.2 4154972 0
632692.5 4154972 0
632707.7 4154972 0
632723 4154972 0
632738.2 4154972 0
632753.4 4154972 0
632768.7 4154972 0
632783.9 4154972 0
632799.2 4154972 0
632814.4 4154972 0
632829.6 4154972 0
632844.9 4154972 0
632860.1 4154972 0
632875.4 4154972 0
632890.6 4154972 0
632905.8 4154972 0
632921.1 4154972 0
632936.3 4154972 0
632951.6 4154972 0
632966.8 4154972 0
632982 4154972 0
632997.3 4154972 0
633012.5 4154972 0
633027.8 4154972 0
633043 4154972 0
631900 4154987 0
631915.2 4154987 0
631930.5 4154987 0
631945.7 4154987 0
631961 4154987 0
631976.2 4154987 0
631991.4 4154987 0
632006.7 4154987 0
632021.9 4154987 0
632037.2 4154987 0
632052.4 4154987 0
632067.6 4154987 0
632082.9 4154987 0
632098.1 4154987 0
632113.4 4154987 0
632128.6 4154987 0
632143.8 4154987 0
632159.1 4154987 0
632174.3 4154987 0
632189.6 4154987 0
632204.8 4154987 0
632494.4 4154987 0
632509.6 4154987 0
632524.8 4154987 0
632540.1 4154987 0
632555.3 4154987 0
632570.6 4154987 0
632585.8 4154987 0
632601 4154987 0
632616.3 4154987 0
632631.5 4154987 0
632646.8 4154987 0
632662 4154987 0
632677.2 4154987 0
632692.5 4154987 0
632707.7 4154987 0
632723 4154987 0
632738.2 4154987 0
632753.4 4154987 0
632768.7 4154987 0
632783.9 4154987 0
632799.2 4154987 0
632814.4 4154987 0
632829.6 4154987 0
632844.9 4154987 0
632860.1 4154987 0
632875.4 4154987 0
632890.6 4154987 0
632905.8 4154987 0
632921.1 4154987 0
632936.3 4154987 0
632951.6 4154987 0
632966.8 4154987 0
632982 4154987 0
632997.3 4154987 0
633012.5 4154987 0
633027.8 4154987 0
633043 4154987 0
631900 4155002 0
631915.2 4155002 0
631930.5 4155002 0
631945.7 4155002 0
631961 4155002 0
631976.2 4155002 0
631991.4 4155002 0
632006.7 4155002 0
632021.9 4155002 0
632037.2 4155002 0
632052.4 4155002 0
632067.6 4155002 0
632082.9 4155002 0
632098.1 4155002 0
632113.4 4155002 0
632128.6 4155002 0
632143.8 4155002 0
632159.1 4155002 0
632174.3 4155002 0
632494.4 4155002 0
632509.6 4155002 0
632524.8 4155002 0
632540.1 4155002 0
632555.3 4155002 0
632570.6 4155002 0
632585.8 4155002 0
632601 4155002 0
632616.3 4155002 0
632631.5 4155002 0
632646.8 4155002 0
632662 4155002 0
632677.2 4155002 0
632692.5 4155002 0
632707.7 4155002 0
632723 4155002 0
632738.2 4155002 0
632753.4 4155002 0
632768.7 4155002 0
632783.9 4155002 0
632799.2 4155002 0
632814.4 4155002 0
632829.6 4155002 0
632844.9 4155002 0
632860.1 4155002 0
632875.4 4155002 0
632890.6 4155002 0
632905.8 4155002 0
632921.1 4155002 0
632936.3 4155002 0
632951.6 4155002 0
632966.8 4155002 0
632982 4155002 0
632997.3 4155002 0
633012.5 4155002 0
633027.8 4155002 0
633043 4155002 0
631900 4155017 0
631915.2 4155017 0
631930.5 4155017 0
631945.7 4155017 0
631961 4155017 0
631976.2 4155017 0
631991.4 4155017 0
632006.7 4155017 0
632021.9 4155017 0
632037.2 4155017 0
632052.4 4155017 0
632067.6 4155017 0
632082.9 4155017 0
632098.1 4155017 0
632113.4 4155017 0
632128.6 4155017 0
632143.8 4155017 0
632159.1 4155017 0
632494.4 4155017 0
632509.6 4155017 0
632524.8 4155017 0
632540.1 4155017 0
632555.3 4155017 0
632570.6 4155017 0
632585.8 4155017 0
632601 4155017 0
632616.3 4155017 0
632631.5 4155017 0
632646.8 4155017 0
632662 4155017 0
632677.2 4155017 0
632692.5 4155017 0
632707.7 4155017 0
632723 4155017 0
632738.2 4155017 0
632753.4 4155017 0
632768.7 4155017 0
632783.9 4155017 0
632799.2 4155017 0
632814.4 4155017 0
632829.6 4155017 0
632844.9 4155017 0
632860.1 4155017 0
632875.4 4155017 0
632890.6 4155017 0
632905.8 4155017 0
632921.1 4155017 0
632936.3 4155017 0
632951.6 4155017 0
632966.8 4155017 0
632982 4155017 0
632997.3 4155017 0
633012.5 4155017 0
633027.8 4155017 0
633043 4155017 0
631900 4155032 0
631915.2 4155032 0
631930.5 4155032 0
631945.7 4155032 0
631961 4155032 0
631976.2 4155032 0
631991.4 4155032 0
632006.7 4155032 0
632021.9 4155032 0
632037.2 4155032 0
632052.4 4155032 0
632067.6 4155032 0
632082.9 4155032 0
632098.1 4155032 0
632113.4 4155032 0
632128.6 4155032 0
632143.8 4155032 0
632159.1 4155032 0
632494.4 4155032 0
632509.6 4155032 0
632524.8 4155032 0
632540.1 4155032 0
632555.3 4155032 0
632570.6 4155032 0
632585.8 4155032 0
632601 4155032 0
632616.3 4155032 0
632631.5 4155032 0
632646.8 4155032 0
632662 4155032 0
632677.2 4155032 0
632692.5 4155032 0
632707.7 4155032 0
632723 4155032 0
632738.2 4155032 0
632753.4 4155032 0
632768.7 4155032 0
632783.9 4155032 0
632799.2 4155032 0
632814.4 4155032 0
632829.6 4155032 0
632844.9 4155032 0
632860.1 4155032 0
632875.4 4155032 0
632890.6 4155032 0
632905.8 4155032 0
632921.1 4155032 0
632936.3 4155032 0
632951.6 4155032 0
632966.8 4155032 0
632982 4155032 0
632997.3 4155032 0
633012.5 4155032 0
633027.8 4155032 0
633043 4155032 0
631900 4155048 0
631915.2 4155048 0
631930.5 4155048 0
631945.7 4155048 0
631961 4155048 0
631976.2 4155048 0
631991.4 4155048 0
632006.7 4155048 0
632021.9 4155048 0
632037.2 4155048 0
632052.4 4155048 0
632067.6 4155048 0
632082.9 4155048 0
632098.1 4155048 0
632113.4 4155048 0
632128.6 4155048 0
632143.8 4155048 0
632494.4 4155048 0
632509.6 4155048 0
632524.8 4155048 0
632540.1 4155048 0
632555.3 4155048 0
632570.6 4155048 0
632585.8 4155048 0
632601 4155048 0
632616.3 4155048 0
632631.5 4155048 0
632646.8 4155048 0
632662 4155048 0
632677.2 4155048 0
632692.5 4155048 0
632707.7 4155048 0
632723 4155048 0
632738.2 4155048 0
632753.4 4155048 0
632768.7 4155048 0
632783.9 4155048 0
632799.2 4155048 0
632814.4 4155048 0
632829.6 4155048 0
632844.9 4155048 0
632860.1 4155048 0
632875.4 4155048 0
632890.6 4155048 0
632905.8 4155048 0
632921.1 4155048 0
632936.3 4155048 0
632951.6 4155048 0
632966.8 4155048 0
632982 4155048 0
632997.3 4155048 0
633012.5 4155048 0
633027.8 4155048 0
633043 4155048 0
631900 4155063 0
631915.2 4155063 0
631930.5 4155063 0
631945.7 4155063 0
631961 4155063 0
631976.2 4155063 0
631991.4 4155063 0
632006.7 4155063 0
632021.9 4155063 0
632037.2 4155063 0
632052.4 4155063 0
632067.6 4155063 0
632082.9 4155063 0
632098.1 4155063 0
632113.4 4155063 0
632128.6 4155063 0
632494.4 4155063 0
632509.6 4155063 0
632524.8 4155063 0
632540.1 4155063 0
632555.3 4155063 0
632570.6 4155063 0
632585.8 4155063 0
632601 4155063 0
632616.3 4155063 0
632631.5 4155063 0
632646.8 4155063 0
632662 4155063 0
632677.2 4155063 0
632692.5 4155063 0
632707.7 4155063 0
632723 4155063 0
632738.2 4155063 0
632753.4 4155063 0
632768.7 4155063 0
632783.9 4155063 0
632799.2 4155063 0
632814.4 4155063 0
632829.6 4155063 0
632844.9 4155063 0
632860.1 4155063 0
632875.4 4155063 0
632890.6 4155063 0
632905.8 4155063 0
632921.1 4155063 0
632936.3 4155063 0
632951.6 4155063 0
632966.8 4155063 0
632982 4155063 0
632997.3 4155063 0
633012.5 4155063 0
633027.8 4155063 0
633043 4155063 0
631900 4155078 0
631915.2 4155078 0
631930.5 4155078 0
631945.7 4155078 0
631961 4155078 0
631976.2 4155078 0
631991.4 4155078 0
632006.7 4155078 0
632021.9 4155078 0
632037.2 4155078 0
632052.4 4155078 0
632067.6 4155078 0
632082.9 4155078 0
632098.1 4155078 0
632113.4 4155078 0
632128.6 4155078 0
632494.4 4155078 0
632509.6 4155078 0
632524.8 4155078 0
632540.1 4155078 0
632555.3 4155078 0
632570.6 4155078 0
632585.8 4155078 0
632601 4155078 0
632616.3 4155078 0
632631.5 4155078 0
632646.8 4155078 0
632662 4155078 0
632677.2 4155078 0
632692.5 4155078 0
632707.7 4155078 0
632723 4155078 0
632738.2 4155078 0
632753.4 4155078 0
632768.7 4155078 0
632783.9 4155078 0
632799.2 4155078 0
632814.4 4155078 0
632829.6 4155078 0
632844.9 4155078 0
632860.1 4155078 0
632875.4 4155078 0
632890.6 4155078 0
632905.8 4155078 0
632921.1 4155078 0
632936.3 4155078 0
632951.6 4155078 0
632966.8 4155078 0
632982 4155078 0
632997.3 4155078 0
633012.5 4155078 0
633027.8 4155078 0
633043 4155078 0
631900 4155093 0
631915.2 4155093 0
631930.5 4155093 0
631945.7 4155093 0
631961 4155093 0
631976.2 4155093 0
631991.4 4155093 0
632006.7 4155093 0
632021.9 4155093 0
632037.2 4155093 0
632052.4 4155093 0
632067.6 4155093 0
632082.9 4155093 0
632098.1 4155093 0
632113.4 4155093 0
632128.6 4155093 0
632509.6 4155093 0
632524.8 4155093 0
632540.1 4155093 0
632555.3 4155093 0
632570.6 4155093 0
632585.8 4155093 0
632601 4155093 0
632616.3 4155093 0
632631.5 4155093 0
632646.8 4155093 0
632662 4155093 0
632677.2 4155093 0
632692.5 4155093 0
632707.7 4155093 0
632723 4155093 0
632738.2 4155093 0
632753.4 4155093 0
632768.7 4155093 0
632783.9 4155093 0
632799.2 4155093 0
632814.4 4155093 0
632829.6 4155093 0
632844.9 4155093 0
632860.1 4155093 0
632875.4 4155093 0
632890.6 4155093 0
632905.8 4155093 0
632921.1 4155093 0
632936.3 4155093 0
632951.6 4155093 0
632966.8 4155093 0
632982 4155093 0
632997.3 4155093 0
633012.5 4155093 0
633027.8 4155093 0
633043 4155093 0
631900 4155109 0
631915.2 4155109 0
631930.5 4155109 0
631945.7 4155109 0
631961 4155109 0
631976.2 4155109 0
631991.4 4155109 0
632006.7 4155109 0
632021.9 4155109 0
632037.2 4155109 0
632052.4 4155109 0
632067.6 4155109 0
632082.9 4155109 0
632098.1 4155109 0
632113.4 4155109 0
632509.6 4155109 0
632524.8 4155109 0
632540.1 4155109 0
632555.3 4155109 0
632570.6 4155109 0
632585.8 4155109 0
632601 4155109 0
632616.3 4155109 0
632631.5 4155109 0
632646.8 4155109 0
632662 4155109 0
632677.2 4155109 0
632692.5 4155109 0
632707.7 4155109 0
632723 4155109 0
632738.2 4155109 0
632753.4 4155109 0
632768.7 4155109 0
632783.9 4155109 0
632799.2 4155109 0
632814.4 4155109 0
632829.6 4155109 0
632844.9 4155109 0
632860.1 4155109 0
632875.4 4155109 0
632890.6 4155109 0
632905.8 4155109 0
632921.1 4155109 0
632936.3 4155109 0
632951.6 4155109 0
632966.8 4155109 0
632982 4155109 0
632997.3 4155109 0
633012.5 4155109 0
633027.8 4155109 0
633043 4155109 0
631900 4155124 0
631915.2 4155124 0
631930.5 4155124 0
631945.7 4155124 0
631961 4155124 0
631976.2 4155124 0
631991.4 4155124 0
632006.7 4155124 0
632021.9 4155124 0
632037.2 4155124 0
632052.4 4155124 0
632067.6 4155124 0
632082.9 4155124 0
632098.1 4155124 0
632113.4 4155124 0
632494.4 4155124 0
632509.6 4155124 0
632524.8 4155124 0
632540.1 4155124 0
632555.3 4155124 0
632570.6 4155124 0
632585.8 4155124 0
632601 4155124 0
632616.3 4155124 0
632631.5 4155124 0
632646.8 4155124 0
632662 4155124 0
632677.2 4155124 0
632692.5 4155124 0
632707.7 4155124 0
632723 4155124 0
632738.2 4155124 0
632753.4 4155124 0
632768.7 4155124 0
632783.9 4155124 0
632799.2 4155124 0
632814.4 4155124 0
632829.6 4155124 0
632844.9 4155124 0
632860.1 4155124 0
632875.4 4155124 0
632890.6 4155124 0
632905.8 4155124 0
632921.1 4155124 0
632936.3 4155124 0
632951.6 4155124 0
632966.8 4155124 0
632982 4155124 0
632997.3 4155124 0
633012.5 4155124 0
633027.8 4155124 0
633043 4155124 0
631900 4155139 0
631915.2 4155139 0
631930.5 4155139 0
631945.7 4155139 0
631961 4155139 0
631976.2 4155139 0
631991.4 4155139 0
632006.7 4155139 0
632021.9 4155139 0
632037.2 4155139 0
632052.4 4155139 0
632067.6 4155139 0
632082.9 4155139 0
632098.1 4155139 0
632113.4 4155139 0
632494.4 4155139 0
632509.6 4155139 0
632524.8 4155139 0
632540.1 4155139 0
632555.3 4155139 0
632570.6 4155139 0
632585.8 4155139 0
632601 4155139 0
632616.3 4155139 0
632631.5 4155139 0
632646.8 4155139 0
632662 4155139 0
632677.2 4155139 0
632692.5 4155139 0
632707.7 4155139 0
632723 4155139 0
632738.2 4155139 0
632753.4 4155139 0
632768.7 4155139 0
632783.9 4155139 0
632799.2 4155139 0
632814.4 4155139 0
632829.6 4155139 0
632844.9 4155139 0
632860.1 4155139 0
632875.4 4155139 0
632890.6 4155139 0
632905.8 4155139 0
632921.1 4155139 0
632936.3 4155139 0
632951.6 4155139 0
632966.8 4155139 0
632982 4155139 0
632997.3 4155139 0
633012.5 4155139 0
633027.8 4155139 0
633043 4155139 0
631900 4155154 0
631915.2 4155154 0
631930.5 4155154 0
631945.7 4155154 0
631961 4155154 0
631976.2 4155154 0
631991.4 4155154 0
632006.7 4155154 0
632021.9 4155154 0
632037.2 4155154 0
632052.4 4155154 0
632067.6 4155154 0
632082.9 4155154 0
632098.1 4155154 0
632113.4 4155154 0
632128.6 4155154 0
632494.4 4155154 0
632509.6 4155154 0
632524.8 4155154 0
632540.1 4155154 0
632555.3 4155154 0
632570.6 4155154 0
632585.8 4155154 0
632601 4155154 0
632616.3 4155154 0
632631.5 4155154 0
632646.8 4155154 0
632662 4155154 0
632677.2 4155154 0
632692.5 4155154 0
632707.7 4155154 0
632723 4155154 0
632738.2 4155154 0
632753.4 4155154 0
632768.7 4155154 0
632783.9 4155154 0
632799.2 4155154 0
632814.4 4155154 0
632829.6 4155154 0
632844.9 4155154 0
632860.1 4155154 0
632875.4 4155154 0
632890.6 4155154 0
632905.8 4155154 0
632921.1 4155154 0
632936.3 4155154 0
632951.6 4155154 0
632966.8 4155154 0
632982 4155154 0
632997.3 4155154 0
633012.5 4155154 0
633027.8 4155154 0
633043 4155154 0
631900 4155170 0
631915.2 4155170 0
631930.5 4155170 0
631945.7 4155170 0
631961 4155170 0
631976.2 4155170 0
631991.4 4155170 0
632006.7 4155170 0
632021.9 4155170 0
632037.2 4155170 0
632052.4 4155170 0
632067.6 4155170 0
632082.9 4155170 0
632098.1 4155170 0
632113.4 4155170 0
632128.6 4155170 0
632494.4 4155170 0
632509.6 4155170 0
632524.8 4155170 0
632540.1 4155170 0
632555.3 4155170 0
632570.6 4155170 0
632585.8 4155170 0
632601 4155170 0
632616.3 4155170 0
632631.5 4155170 0
632646.8 4155170 0
632662 4155170 0
632677.2 4155170 0
632692.5 4155170 0
632707.7 4155170 0
632723 4155170 0
632738.2 4155170 0
632753.4 4155170 0
632768.7 4155170 0
632783.9 4155170 0
632799.2 4155170 0
632814.4 4155170 0
632829.6 4155170 0
632844.9 4155170 0
632860.1 4155170 0
632875.4 4155170 0
632890.6 4155170 0
632905.8 4155170 0
632921.1 4155170 0
632936.3 4155170 0
632951.6 4155170 0
632966.8 4155170 0
632982 4155170 0
632997.3 4155170 0
633012.5 4155170 0
633027.8 4155170 0
633043 4155170 0
631900 4155185 0
631915.2 4155185 0
631930.5 4155185 0
631945.7 4155185 0
631961 4155185 0
631976.2 4155185 0
631991.4 4155185 0
632006.7 4155185 0
632021.9 4155185 0
632037.2 4155185 0
632052.4 4155185 0
632067.6 4155185 0
632082.9 4155185 0
632098.1 4155185 0
632113.4 4155185 0
632128.6 4155185 0
632494.4 4155185 0
632509.6 4155185 0
632524.8 4155185 0
632540.1 4155185 0
632555.3 4155185 0
632570.6 4155185 0
632585.8 4155185 0
632601 4155185 0
632616.3 4155185 0
632631.5 4155185 0
632646.8 4155185 0
632662 4155185 0
632677.2 4155185 0
632692.5 4155185 0
632707.7 4155185 0
632723 4155185 0
632738.2 4155185 0
632753.4 4155185 0
632768.7 4155185 0
632783.9 4155185 0
632799.2 4155185 0
632814.4 4155185 0
632829.6 4155185 0
632844.9 4155185 0
632860.1 4155185 0
632875.4 4155185 0
632890.6 4155185 0
632905.8 4155185 0
632921.1 4155185 0
632936.3 4155185 0
632951.6 4155185 0
632966.8 4155185 0
632982 4155185 0
632997.3 4155185 0
633012.5 4155185 0
633027.8 4155185 0
633043 4155185 0
631900 4155200 0
631915.2 4155200 0
631930.5 4155200 0
631945.7 4155200 0
631961 4155200 0
631976.2 4155200 0
631991.4 4155200 0
632006.7 4155200 0
632021.9 4155200 0
632037.2 4155200 0
632052.4 4155200 0
632067.6 4155200 0
632082.9 4155200 0
632098.1 4155200 0
632113.4 4155200 0
632128.6 4155200 0
632494.4 4155200 0
632509.6 4155200 0
632524.8 4155200 0
632540.1 4155200 0
632555.3 4155200 0
632570.6 4155200 0
632585.8 4155200 0
632601 4155200 0
632616.3 4155200 0
632631.5 4155200 0
632646.8 4155200 0
632662 4155200 0
632677.2 4155200 0
632692.5 4155200 0
632707.7 4155200 0
632723 4155200 0
632738.2 4155200 0
632753.4 4155200 0
632768.7 4155200 0
632783.9 4155200 0
632799.2 4155200 0
632814.4 4155200 0
632829.6 4155200 0
632844.9 4155200 0
632860.1 4155200 0
632875.4 4155200 0
632890.6 4155200 0
632905.8 4155200 0
632921.1 4155200 0
632936.3 4155200 0
632951.6 4155200 0
632966.8 4155200 0
632982 4155200 0
632997.3 4155200 0
633012.5 4155200 0
633027.8 4155200 0
633043 4155200 0
631900 4155215 0
631915.2 4155215 0
631930.5 4155215 0
631945.7 4155215 0
631961 4155215 0
631976.2 4155215 0
631991.4 4155215 0
632006.7 4155215 0
632021.9 4155215 0
632037.2 4155215 0
632052.4 4155215 0
632067.6 4155215 0
632082.9 4155215 0
632098.1 4155215 0
632113.4 4155215 0
632128.6 4155215 0
632479.1 4155215 0
632494.4 4155215 0
632509.6 4155215 0
632524.8 4155215 0
632540.1 4155215 0
632555.3 4155215 0
632570.6 4155215 0
632585.8 4155215 0
632601 4155215 0
632616.3 4155215 0
632631.5 4155215 0
632646.8 4155215 0
632662 4155215 0
632677.2 4155215 0
632692.5 4155215 0
632707.7 4155215 0
632723 4155215 0
632738.2 4155215 0
632753.4 4155215 0
632768.7 4155215 0
632783.9 4155215 0
632799.2 4155215 0
632814.4 4155215 0
632829.6 4155215 0
632844.9 4155215 0
632860.1 4155215 0
632875.4 4155215 0
632890.6 4155215 0
632905.8 4155215 0
632921.1 4155215 0
632936.3 4155215 0
632951.6 4155215 0
632966.8 4155215 0
632982 4155215 0
632997.3 4155215 0
633012.5 4155215 0
633027.8 4155215 0
633043 4155215 0
631900 4155231 0
631915.2 4155231 0
631930.5 4155231 0
631945.7 4155231 0
631961 4155231 0
631976.2 4155231 0
631991.4 4155231 0
632006.7 4155231 0
632021.9 4155231 0
632037.2 4155231 0
632052.4 4155231 0
632067.6 4155231 0
632082.9 4155231 0
632098.1 4155231 0
632113.4 4155231 0
632128.6 4155231 0
632479.1 4155231 0
632494.4 4155231 0
632509.6 4155231 0
632524.8 4155231 0
632540.1 4155231 0
632555.3 4155231 0
632570.6 4155231 0
632585.8 4155231 0
632601 4155231 0
632616.3 4155231 0
632631.5 4155231 0
632646.8 4155231 0
632662 4155231 0
632677.2 4155231 0
632692.5 4155231 0
632707.7 4155231 0
632723 4155231 0
632738.2 4155231 0
632753.4 4155231 0
632768.7 4155231 0
632783.9 4155231 0
632799.2 4155231 0
632814.4 4155231 0
632829.6 4155231 0
632844.9 4155231 0
632860.1 4155231 0
632875.4 4155231 0
632890.6 4155231 0
632905.8 4155231 0
632921.1 4155231 0
632936.3 4155231 0
632951.6 4155231 0
632966.8 4155231 0
632982 4155231 0
632997.3 4155231 0
633012.5 4155231 0
633027.8 4155231 0
633043 4155231 0
631900 4155246 0
631915.2 4155246 0
631930.5 4155246 0
631945.7 4155246 0
631961 4155246 0
631976.2 4155246 0
631991.4 4155246 0
632006.7 4155246 0
632021.9 4155246 0
632037.2 4155246 0
632052.4 4155246 0
632067.6 4155246 0
632082.9 4155246 0
632098.1 4155246 0
632113.4 4155246 0
632128.6 4155246 0
632463.9 4155246 0
632479.1 4155246 0
632494.4 4155246 0
632509.6 4155246 0
632524.8 4155246 0
632540.1 4155246 0
632555.3 4155246 0
632570.6 4155246 0
632585.8 4155246 0
632601 4155246 0
632616.3 4155246 0
632631.5 4155246 0
632646.8 4155246 0
632662 4155246 0
632677.2 4155246 0
632692.5 4155246 0
632707.7 4155246 0
632723 4155246 0
632738.2 4155246 0
632753.4 4155246 0
632768.7 4155246 0
632783.9 4155246 0
632799.2 4155246 0
632814.4 4155246 0
632829.6 4155246 0
632844.9 4155246 0
632860.1 4155246 0
632875.4 4155246 0
632890.6 4155246 0
632905.8 4155246 0
632921.1 4155246 0
632936.3 4155246 0
632951.6 4155246 0
632966.8 4155246 0
632982 4155246 0
632997.3 4155246 0
633012.5 4155246 0
633027.8 4155246 0
633043 4155246 0
631900 4155261 0
631915.2 4155261 0
631930.5 4155261 0
631945.7 4155261 0
631961 4155261 0
631976.2 4155261 0
631991.4 4155261 0
632006.7 4155261 0
632021.9 4155261 0
632037.2 4155261 0
632052.4 4155261 0
632067.6 4155261 0
632082.9 4155261 0
632098.1 4155261 0
632113.4 4155261 0
632128.6 4155261 0
632463.9 4155261 0
632479.1 4155261 0
632494.4 4155261 0
632509.6 4155261 0
632524.8 4155261 0
632540.1 4155261 0
632555.3 4155261 0
632570.6 4155261 0
632585.8 4155261 0
632601 4155261 0
632616.3 4155261 0
632631.5 4155261 0
632646.8 4155261 0
632662 4155261 0
632677.2 4155261 0
632692.5 4155261 0
632707.7 4155261 0
632723 4155261 0
632738.2 4155261 0
632753.4 4155261 0
632768.7 4155261 0
632783.9 4155261 0
632799.2 4155261 0
632814.4 4155261 0
632829.6 4155261 0
632844.9 4155261 0
632860.1 4155261 0
632875.4 4155261 0
632890.6 4155261 0
632905.8 4155261 0
632921.1 4155261 0
632936.3 4155261 0
632951.6 4155261 0
632966.8 4155261 0
632982 4155261 0
632997.3 4155261 0
633012.5 4155261 0
633027.8 4155261 0
633043 4155261 0
631900 4155276 0
631915.2 4155276 0
631930.5 4155276 0
631945.7 4155276 0
631961 4155276 0
631976.2 4155276 0
631991.4 4155276 0
632006.7 4155276 0
632021.9 4155276 0
632037.2 4155276 0
632052.4 4155276 0
632067.6 4155276 0
632082.9 4155276 0
632098.1 4155276 0
632113.4 4155276 0
632128.6 4155276 0
632143.8 4155276 0
632448.6 4155276 0
632463.9 4155276 0
632479.1 4155276 0
632494.4 4155276 0
632509.6 4155276 0
632524.8 4155276 0
632540.1 4155276 0
632555.3 4155276 0
632570.6 4155276 0
632585.8 4155276 0
632601 4155276 0
632616.3 4155276 0
632631.5 4155276 0
632646.8 4155276 0
632662 4155276 0
632677.2 4155276 0
632692.5 4155276 0
632707.7 4155276 0
632723 4155276 0
632738.2 4155276 0
632753.4 4155276 0
632768.7 4155276 0
632783.9 4155276 0
632799.2 4155276 0
632814.4 4155276 0
632829.6 4155276 0
632844.9 4155276 0
632860.1 4155276 0
632875.4 4155276 0
632890.6 4155276 0
632905.8 4155276 0
632921.1 4155276 0
632936.3 4155276 0
632951.6 4155276 0
632966.8 4155276 0
632982 4155276 0
632997.3 4155276 0
633012.5 4155276 0
633027.8 4155276 0
633043 4155276 0
631900 4155292 0
631915.2 4155292 0
631930.5 4155292 0
631945.7 4155292 0
631961 4155292 0
631976.2 4155292 0
631991.4 4155292 0
632006.7 4155292 0
632021.9 4155292 0
632037.2 4155292 0
632052.4 4155292 0
632067.6 4155292 0
632082.9 4155292 0
632098.1 4155292 0
632113.4 4155292 0
632128.6 4155292 0
632143.8 4155292 0
632159.1 4155292 0
632433.4 4155292 0
632448.6 4155292 0
632463.9 4155292 0
632479.1 4155292 0
632494.4 4155292 0
632509.6 4155292 0
632524.8 4155292 0
632540.1 4155292 0
632555.3 4155292 0
632570.6 4155292 0
632585.8 4155292 0
632601 4155292 0
632616.3 4155292 0
632631.5 4155292 0
632646.8 4155292 0
632662 4155292 0
632677.2 4155292 0
632692.5 4155292 0
632707.7 4155292 0
632723 4155292 0
632738.2 4155292 0
632753.4 4155292 0
632768.7 4155292 0
632783.9 4155292 0
632799.2 4155292 0
632814.4 4155292 0
632829.6 4155292 0
632844.9 4155292 0
632860.1 4155292 0
632875.4 4155292 0
632890.6 4155292 0
632905.8 4155292 0
632921.1 4155292 0
632936.3 4155292 0
632951.6 4155292 0
632966.8 4155292 0
632982 4155292 0
632997.3 4155292 0
633012.5 4155292 0
633027.8 4155292 0
633043 4155292 0
631900 4155307 0
631915.2 4155307 0
631930.5 4155307 0
631945.7 4155307 0
631961 4155307 0
631976.2 4155307 0
631991.4 4155307 0
632006.7 4155307 0
632021.9 4155307 0
632037.2 4155307 0
632052.4 4155307 0
632067.6 4155307 0
632082.9 4155307 0
632098.1 4155307 0
632113.4 4155307 0
632128.6 4155307 0
632143.8 4155307 0
632159.1 4155307 0
632174.3 4155307 0
632189.6 4155307 0
632402.9 4155307 0
632418.2 4155307 0
632433.4 4155307 0
632448.6 4155307 0
632463.9 4155307 0
632479.1 4155307 0
632494.4 4155307 0
632509.6 4155307 0
632524.8 4155307 0
632540.1 4155307 0
632555.3 4155307 0
632570.6 4155307 0
632585.8 4155307 0
632601 4155307 0
632616.3 4155307 0
632631.5 4155307 0
632646.8 4155307 0
632662 4155307 0
632677.2 4155307 0
632692.5 4155307 0
632707.7 4155307 0
632723 4155307 0
632738.2 4155307 0
632753.4 4155307 0
632768.7 4155307 0
632783.9 4155307 0
632799.2 4155307 0
632814.4 4155307 0
632829.6 4155307 0
632844.9 4155307 0
632860.1 4155307 0
632875.4 4155307 0
632890.6 4155307 0
632905.8 4155307 0
632921.1 4155307 0
632936.3 4155307 0
632951.6 4155307 0
632966.8 4155307 0
632982 4155307 0
632997.3 4155307 0
633012.5 4155307 0
633027.8 4155307 0
633043 4155307 0
631900 4155322 0
631915.2 4155322 0
631930.5 4155322 0
631945.7 4155322 0
631961 4155322 0
631976.2 4155322 0
631991.4 4155322 0
632006.7 4155322 0
632021.9 4155322 0
632037.2 4155322 0
632052.4 4155322 0
632067.6 4155322 0
632082.9 4155322 0
632098.1 4155322 0
632113.4 4155322 0
632128.6 4155322 0
632143.8 4155322 0
632159.1 4155322 0
632174.3 4155322 0
632189.6 4155322 0
632204.8 4155322 0
632220 4155322 0
632235.3 4155322 0
632357.2 4155322 0
632372.4 4155322 0
632387.7 4155322 0
632402.9 4155322 0
632418.2 4155322 0
632433.4 4155322 0
632448.6 4155322 0
632463.9 4155322 0
632479.1 4155322 0
632494.4 4155322 0
632509.6 4155322 0
632524.8 4155322 0
632540.1 4155322 0
632555.3 4155322 0
632570.6 4155322 0
632585.8 4155322 0
632601 4155322 0
632616.3 4155322 0
632631.5 4155322 0
632646.8 4155322 0
632662 4155322 0
632677.2 4155322 0
632692.5 4155322 0
632707.7 4155322 0
632723 4155322 0
632738.2 4155322 0
632753.4 4155322 0
632768.7 4155322 0
632783.9 4155322 0
632799.2 4155322 0
632814.4 4155322 0
632829.6 4155322 0
632844.9 4155322 0
632860.1 4155322 0
632875.4 4155322 0
632890.6 4155322 0
632905.8 4155322 0
632921.1 4155322 0
632936.3 4155322 0
632951.6 4155322 0
632966.8 4155322 0
632982 4155322 0
632997.3 4155322 0
633012.5 4155322 0
633027.8 4155322 0
633043 4155322 0
631900 4155337 0
631915.2 4155337 0
631930.5 4155337 0
631945.7 4155337 0
631961 4155337 0
631976.2 4155337 0
631991.4 4155337 0
632006.7 4155337 0
632021.9 4155337 0
632037.2 4155337 0
632052.4 4155337 0
632067.6 4155337 0
632082.9 4155337 0
632098.1 4155337 0
632113.4 4155337 0
632128.6 4155337 0
632143.8 4155337 0
632159.1 4155337 0
632174.3 4155337 0
632189.6 4155337 0
632204.8 4155337 0
632220 4155337 0
632235.3 4155337 0
632250.5 4155337 0
632265.8 4155337 0
632281 4155337 0
632296.2 4155337 0
632311.5 4155337 0
632326.7 4155337 0
632342 4155337 0
632357.2 4155337 0
632372.4 4155337 0
632387.7 4155337 0
632402.9 4155337 0
632418.2 4155337 0
632433.4 4155337 0
632448.6 4155337 0
632463.9 4155337 0
632479.1 4155337 0
632494.4 4155337 0
632509.6 4155337 0
632524.8 4155337 0
632540.1 4155337 0
632555.3 4155337 0
632570.6 4155337 0
632585.8 4155337 0
632601 4155337 0
632616.3 4155337 0
632631.5 4155337 0
632646.8 4155337 0
632662 4155337 0
632677.2 4155337 0
632692.5 4155337 0
632707.7 4155337 0
632723 4155337 0
632738.2 4155337 0
632753.4 4155337 0
632768.7 4155337 0
632783.9 4155337 0
632799.2 4155337 0
632814.4 4155337 0
632829.6 4155337 0
632844.9 4155337 0
632860.1 4155337 0
632875.4 4155337 0
632890.6 4155337 0
632905.8 4155337 0
632921.1 4155337 0
632936.3 4155337 0
632951.6 4155337 0
632966.8 4155337 0
632982 4155337 0
632997.3 4155337 0
633012.5 4155337 0
633027.8 4155337 0
633043 4155337 0
631900 4155353 0
631915.2 4155353 0
631930.5 4155353 0
631945.7 4155353 0
631961 4155353 0
631976.2 4155353 0
631991.4 4155353 0
632006.7 4155353 0
632021.9 4155353 0
632037.2 4155353 0
632052.4 4155353 0
632067.6 4155353 0
632082.9 4155353 0
632098.1 4155353 0
632113.4 4155353 0
632128.6 4155353 0
632143.8 4155353 0
632159.1 4155353 0
632174.3 4155353 0
632189.6 4155353 0
632204.8 4155353 0
632220 4155353 0
632235.3 4155353 0
632250.5 4155353 0
632265.8 4155353 0
632281 4155353 0
632296.2 4155353 0
632311.5 4155353 0
632326.7 4155353 0
632342 4155353 0
632357.2 4155353 0
632372.4 4155353 0
632387.7 4155353 0
632402.9 4155353 0
632418.2 4155353 0
632433.4 4155353 0
632448.6 4155353 0
632463.9 4155353 0
632479.1 4155353 0
632494.4 4155353 0
632509.6 4155353 0
632524.8 4155353 0
632540.1 4155353 0
632555.3 4155353 0
632570.6 4155353 0
632585.8 4155353 0
632601 4155353 0
632616.3 4155353 0
632631.5 4155353 0
632646.8 4155353 0
632662 4155353 0
632677.2 4155353 0
632692.5 4155353 0
632707.7 4155353 0
632723 4155353 0
632738.2 4155353 0
632753.4 4155353 0
632768.7 4155353 0
632783.9 4155353 0
632799.2 4155353 0
632814.4 4155353 0
632829.6 4155353 0
632844.9 4155353 0
632860.1 4155353 0
632875.4 4155353 0
632890.6 4155353 0
632905.8 4155353 0
632921.1 4155353 0
632936.3 4155353 0
632951.6 4155353 0
632966.8 4155353 0
632982 4155353 0
632997.3 4155353 0
633012.5 4155353 0
633027.8 4155353 0
633043 4155353 0
631900 4155368 0
631915.2 4155368 0
631930.5 4155368 0
631945.7 4155368 0
631961 4155368 0
631976.2 4155368 0
631991.4 4155368 0
632006.7 4155368 0
632021.9 4155368 0
632037.2 4155368 0
632052.4 4155368 0
632067.6 4155368 0
632082.9 4155368 0
632098.1 4155368 0
632113.4 4155368 0
632128.6 4155368 0
632143.8 4155368 0
632159.1 4155368 0
632174.3 4155368 0
632189.6 4155368 0
632204.8 4155368 0
632220 4155368 0
632235.3 4155368 0
632250.5 4155368 0
632265.8 4155368 0
632281 4155368 0
632296.2 4155368 0
632311.5 4155368 0
632326.7 4155368 0
632342 4155368 0
632357.2 4155368 0
632372.4 4155368 0
632387.7 4155368 0
632402.9 4155368 0
632418.2 4155368 0
632433.4 4155368 0
632448.6 4155368 0
632463.9 4155368 0
632479.1 4155368 0
632494.4 4155368 0
632509.6 4155368 0
632524.8 4155368 0
632540.1 4155368 0
632555.3 4155368 0
632570.6 4155368 0
632585.8 4155368 0
632601 4155368 0
632616.3 4155368 0
632631.5 4155368 0
632646.8 4155368 0
632662 4155368 0
632677.2 4155368 0
632692.5 4155368 0
632707.7 4155368 0
632723 4155368 0
632738.2 4155368 0
632753.4 4155368 0
632768.7 4155368 0
632783.9 4155368 0
632799.2 4155368 0
632814.4 4155368 0
632829.6 4155368 0
632844.9 4155368 0
632860.1 4155368 0
632875.4 4155368 0
632890.6 4155368 0
632905.8 4155368 0
632921.1 4155368 0
632936.3 4155368 0
632951.6 4155368 0
632966.8 4155368 0
632982 4155368 0
632997.3 4155368 0
633012.5 4155368 0
633027.8 4155368 0
633043 4155368 0
631900 4155383 0
631915.2 4155383 0
631930.5 4155383 0
631945.7 4155383 0
631961 4155383 0
631976.2 4155383 0
631991.4 4155383 0
632006.7 4155383 0
632021.9 4155383 0
632037.2 4155383 0
632052.4 4155383 0
632067.6 4155383 0
632082.9 4155383 0
632098.1 4155383 0
632113.4 4155383 0
632128.6 4155383 0
632143.8 4155383 0
632159.1 4155383 0
632174.3 4155383 0
632189.6 4155383 0
632204.8 4155383 0
632220 4155383 0
632235.3 4155383 0
632250.5 4155383 0
632265.8 4155383 0
632281 4155383 0
632296.2 4155383 0
632311.5 4155383 0
632326.7 4155383 0
632342 4155383 0
632357.2 4155383 0
632372.4 4155383 0
632387.7 4155383 0
632402.9 4155383 0
632418.2 4155383 0
632433.4 4155383 0
632448.6 4155383 0
632463.9 4155383 0
632479.1 4155383 0
632494.4 4155383 0
632509.6 4155383 0
632524.8 4155383 0
632540.1 4155383 0
632555.3 4155383 0
632570.6 4155383 0
632585.8 4155383 0
632601 4155383 0
632616.3 4155383 0
632631.5 4155383 0
632646.8 4155383 0
632662 4155383 0
632677.2 4155383 0
632692.5 4155383 0
632707.7 4155383 0
632723 4155383 0
632738.2 4155383 0
632753.4 4155383 0
632768.7 4155383 0
632783.9 4155383 0
632799.2 4155383 0
632814.4 4155383 0
632829.6 4155383 0
632844.9 4155383 0
632860.1 4155383 0
632875.4 4155383 0
632890.6 4155383 0
632905.8 4155383 0
632921.1 4155383 0
632936.3 4155383 0
632951.6 4155383 0
632966.8 4155383 0
632982 4155383 0
632997.3 4155383 0
633012.5 4155383 0
633027.8 4155383 0
633043 4155383 0
631900 4155398 0
631915.2 4155398 0
631930.5 4155398 0
631945.7 4155398 0
631961 4155398 0
631976.2 4155398 0
631991.4 4155398 0
632006.7 4155398 0
632021.9 4155398 0
632037.2 4155398 0
632052.4 4155398 0
632067.6 4155398 0
632082.9 4155398 0
632098.1 4155398 0
632113.4 4155398 0
632128.6 4155398 0
632143.8 4155398 0
632159.1 4155398 0
632174.3 4155398 0
632189.6 4155398 0
632204.8 4155398 0
632220 4155398 0
632235.3 4155398 0
632250.5 4155398 0
632265.8 4155398 0
632281 4155398 0
632296.2 4155398 0
632311.5 4155398 0
632326.7 4155398 0
632342 4155398 0
632357.2 4155398 0
632372.4 4155398 0
632387.7 4155398 0
632402.9 4155398 0
632418.2 4155398 0
632433.4 4155398 0
632448.6 4155398 0
632463.9 4155398 0
632479.1 4155398 0
632494.4 4155398 0
632509.6 4155398 0
632524.8 4155398 0
632540.1 4155398 0
632555.3 4155398 0
632570.6 4155398 0
632585.8 4155398 0
632601 4155398 0
632616.3 4155398 0
632631.5 4155398 0
632646.8 4155398 0
632662 4155398 0
632677.2 4155398 0
632692.5 4155398 0
632707.7 4155398 0
632723 4155398 0
632738.2 4155398 0
632753.4 4155398 0
632768.7 4155398 0
632783.9 4155398 0
632799.2 4155398 0
632814.4 4155398 0
632829.6 4155398 0
632844.9 4155398 0
632860.1 4155398 0
632875.4 4155398 0
632890.6 4155398 0
632905.8 4155398 0
632921.1 4155398 0
632936.3 4155398 0
632951.6 4155398 0
632966.8 4155398 0
632982 4155398 0
632997.3 4155398 0
633012.5 4155398 0
633027.8 4155398 0
633043 4155398 0
631900 4155413 0
631915.2 4155413 0
631930.5 4155413 0
631945.7 4155413 0
631961 4155413 0
631976.2 4155413 0
631991.4 4155413 0
632006.7 4155413 0
632021.9 4155413 0
632037.2 4155413 0
632052.4 4155413 0
632067.6 4155413 0
632082.9 4155413 0
632098.1 4155413 0
632113.4 4155413 0
632128.6 4155413 0
632143.8 4155413 0
632159.1 4155413 0
632174.3 4155413 0
632189.6 4155413 0
632204.8 4155413 0
632220 4155413 0
632235.3 4155413 0
632250.5 4155413 0
632265.8 4155413 0
632281 4155413 0
632296.2 4155413 0
632311.5 4155413 0
632326.7 4155413 0
632342 4155413 0
632357.2 4155413 0
632372.4 4155413 0
632387.7 4155413 0
632402.9 4155413 0
632418.2 4155413 0
632433.4 4155413 0
632448.6 4155413 0
632463.9 4155413 0
632479.1 4155413 0
632494.4 4155413 0
632509.6 4155413 0
632524.8 4155413 0
632540.1 4155413 0
632555.3 4155413 0
632570.6 4155413 0
632585.8 4155413 0
632601 4155413 0
632616.3 4155413 0
632631.5 4155413 0
632646.8 4155413 0
632662 4155413 0
632677.2 4155413 0
632692.5 4155413 0
632707.7 4155413 0
632723 4155413 0
632738.2 4155413 0
632753.4 4155413 0
632768.7 4155413 0
632783.9 4155413 0
632799.2 4155413 0
632814.4 4155413 0
632829.6 4155413 0
632844.9 4155413 0
632860.1 4155413 0
632875.4 4155413 0
632890.6 4155413 0
632905.8 4155413 0
632921.1 4155413 0
632936.3 4155413 0
632951.6 4155413 0
632966.8 4155413 0
632982 4155413 0
632997.3 4155413 0
633012.5 4155413 0
633027.8 4155413 0
633043 4155413 0
631900 4155429 0
631915.2 4155429 0
631930.5 4155429 0
631945.7 4155429 0
631961 4155429 0
631976.2 4155429 0
631991.4 4155429 0
632006.7 4155429 0
632021.9 4155429 0
632037.2 4155429 0
632052.4 4155429 0
632067.6 4155429 0
632082.9 4155429 0
632098.1 4155429 0
632113.4 4155429 0
632128.6 4155429 0
632143.8 4155429 0
632159.1 4155429 0
632174.3 4155429 0
632189.6 4155429 0
632204.8 4155429 0
632220 4155429 0
632235.3 4155429 0
632250.5 4155429 0
632265.8 4155429 0
632281 4155429 0
632296.2 4155429 0
632311.5 4155429 0
632326.7 4155429 0
632342 4155429 0
632357.2 4155429 0
632372.4 4155429 0
632387.7 4155429 0
632402.9 4155429 0
632418.2 4155429 0
632433.4 4155429 0
632448.6 4155429 0
632463.9 4155429 0
632479.1 4155429 0
632494.4 4155429 0
632509.6 4155429 0
632524.8 4155429 0
632540.1 4155429 0
632555.3 4155429 0
632570.6 4155429 0
632585.8 4155429 0
632601 4155429 0
632616.3 4155429 0
632631.5 4155429 0
632646.8 4155429 0
632662 4155429 0
632677.2 4155429 0
632692.5 4155429 0
632707.7 4155429 0
632723 4155429 0
632738.2 4155429 0
632753.4 4155429 0
632768.7 4155429 0
632783.9 4155429 0
632799.2 4155429 0
632814.4 4155429 0
632829.6 4155429 0
632844.9 4155429 0
632860.1 4155429 0
632875.4 4155429 0
632890.6 4155429 0
632905.8 4155429 0
632921.1 4155429 0
632936.3 4155429 0
632951.6 4155429 0
632966.8 4155429 0
632982 4155429 0
632997.3 4155429 0
633012.5 4155429 0
633027.8 4155429 0
633043 4155429 0
631900 4155444 0
631915.2 4155444 0
631930.5 4155444 0
631945.7 4155444 0
631961 4155444 0
631976.2 4155444 0
631991.4 4155444 0
632006.7 4155444 0
632021.9 4155444 0
632037.2 4155444 0
632052.4 4155444 0
632067.6 4155444 0
632082.9 4155444 0
632098.1 4155444 0
632113.4 4155444 0
632128.6 4155444 0
632143.8 4155444 0
632159.1 4155444 0
632174.3 4155444 0
632189.6 4155444 0
632204.8 4155444 0
632220 4155444 0
632235.3 4155444 0
632250.5 4155444 0
632265.8 4155444 0
632281 4155444 0
632296.2 4155444 0
632311.5 4155444 0
632326.7 4155444 0
632342 4155444 0
632357.2 4155444 0
632372.4 4155444 0
632387.7 4155444 0
632402.9 4155444 0
632418.2 4155444 0
632433.4 4155444 0
632448.6 4155444 0
632463.9 4155444 0
632479.1 4155444 0
632494.4 4155444 0
632509.6 4155444 0
632524.8 4155444 0
632540.1 4155444 0
632555.3 4155444 0
632570.6 4155444 0
632585.8 4155444 0
632601 4155444 0
632616.3 4155444 0
632631.5 4155444 0
632646.8 4155444 0
632662 4155444 0
632677.2 4155444 0
632692.5 4155444 0
632707.7 4155444 0
632723 4155444 0
632738.2 4155444 0
632753.4 4155444 0
632768.7 4155444 0
632783.9 4155444 0
632799.2 4155444 0
632814.4 4155444 0
632829.6 4155444 0
632844.9 4155444 0
632860.1 4155444 0
632875.4 4155444 0
632890.6 4155444 0
632905.8 4155444 0
632921.1 4155444 0
632936.3 4155444 0
632951.6 4155444 0
632966.8 4155444 0
632982 4155444 0
632997.3 4155444 0
633012.5 4155444 0
633027.8 4155444 0
633043 4155444 0
631900 4155459 0
631915.2 4155459 0
631930.5 4155459 0
631945.7 4155459 0
631961 4155459 0
631976.2 4155459 0
631991.4 4155459 0
632006.7 4155459 0
632021.9 4155459 0
632037.2 4155459 0
632052.4 4155459 0
632067.6 4155459 0
632082.9 4155459 0
632098.1 4155459 0
632113.4 4155459 0
632128.6 4155459 0
632143.8 4155459 0
632159.1 4155459 0
632174.3 4155459 0
632189.6 4155459 0
632204.8 4155459 0
632220 4155459 0
632235.3 4155459 0
632250.5 4155459 0
632265.8 4155459 0
632281 4155459 0
632296.2 4155459 0
632311.5 4155459 0
632326.7 4155459 0
632342 4155459 0
632357.2 4155459 0
632372.4 4155459 0
632387.7 4155459 0
632402.9 4155459 0
632418.2 4155459 0
632433.4 4155459 0
632448.6 4155459 0
632463.9 4155459 0
632479.1 4155459 0
632494.4 4155459 0
632509.6 4155459 0
632524.8 4155459 0
632540.1 4155459 0
632555.3 4155459 0
632570.6 4155459 0
632585.8 4155459 0
632601 4155459 0
632616.3 4155459 0
632631.5 4155459 0
632646.8 4155459 0
632662 4155459 0
632677.2 4155459 0
632692.5 4155459 0
632707.7 4155459 0
632723 4155459 0
632738.2 4155459 0
632753.4 4155459 0
632768.7 4155459 0
632783.9 4155459 0
632799.2 4155459 0
632814.4 4155459 0
632829.6 4155459 0
632844.9 4155459 0
632860.1 4155459 0
632875.4 4155459 0
632890.6 4155459 0
632905.8 4155459 0
632921.1 4155459 0
632936.3 4155459 0
632951.6 4155459 0
632966.8 4155459 0
632982 4155459 0
632997.3 4155459 0
633012.5 4155459 0
633027.8 4155459 0
633043 4155459 0
631900 4155474 0
631915.2 4155474 0
631930.5 4155474 0
631945.7 4155474 0
631961 4155474 0
631976.2 4155474 0
631991.4 4155474 0
632006.7 4155474 0
632021.9 4155474 0
632037.2 4155474 0
632052.4 4155474 0
632067.6 4155474 0
632082.9 4155474 0
632098.1 4155474 0
632113.4 4155474 0
632128.6 4155474 0
632143.8 4155474 0
632159.1 4155474 0
632174.3 4155474 0
632189.6 4155474 0
632204.8 4155474 0
632220 4155474 0
632235.3 4155474 0
632250.5 4155474 0
632265.8 4155474 0
632281 4155474 0
632296.2 4155474 0
632311.5 4155474 0
632326.7 4155474 0
632342 4155474 0
632357.2 4155474 0
632372.4 4155474 0
632387.7 4155474 0
632402.9 4155474 0
632418.2 4155474 0
632433.4 4155474 0
632448.6 4155474 0
632463.9 4155474 0
632479.1 4155474 0
632494.4 4155474 0
632509.6 4155474 0
632524.8 4155474 0
632540.1 4155474 0
632555.3 4155474 0
632570.6 4155474 0
632585.8 4155474 0
632601 4155474 0
632616.3 4155474 0
632631.5 4155474 0
632646.8 4155474 0
632662 4155474 0
632677.2 4155474 0
632692.5 4155474 0
632707.7 4155474 0
632723 4155474 0
632738.2 4155474 0
632753.4 4155474 0
632768.7 4155474 0
632783.9 4155474 0
632799.2 4155474 0
632814.4 4155474 0
632829.6 4155474 0
632844.9 4155474 0
632860.1 4155474 0
632875.4 4155474 0
632890.6 4155474 0
632905.8 4155474 0
632921.1 4155474 0
632936.3 4155474 0
632951.6 4155474 0
632966.8 4155474 0
632982 4155474 0
632997.3 4155474 0
633012.5 4155474 0
633027.8 4155474 0
633043 4155474 0
631900 4155490 0
631915.2 4155490 0
631930.5 4155490 0
631945.7 4155490 0
631961 4155490 0
631976.2 4155490 0
631991.4 4155490 0
632006.7 4155490 0
632021.9 4155490 0
632037.2 4155490 0
632052.4 4155490 0
632067.6 4155490 0
632082.9 4155490 0
632098.1 4155490 0
632113.4 4155490 0
632128.6 4155490 0
632143.8 4155490 0
632159.1 4155490 0
632174.3 4155490 0
632189.6 4155490 0
632204.8 4155490 0
632220 4155490 0
632235.3 4155490 0
632250.5 4155490 0
632265.8 4155490 0
632281 4155490 0
632296.2 4155490 0
632311.5 4155490 0
632326.7 4155490 0
632342 4155490 0
632357.2 4155490 0
632372.4 4155490 0
632387.7 4155490 0
632402.9 4155490 0
632418.2 4155490 0
632433.4 4155490 0
632448.6 4155490 0
632463.9 4155490 0
632479.1 4155490 0
632494.4 4155490 0
632509.6 4155490 0
632524.8 4155490 0
632540.1 4155490 0
632555.3 4155490 0
632570.6 4155490 0
632585.8 4155490 0
632601 4155490 0
632616.3 4155490 0
632631.5 4155490 0
632646.8 4155490 0
632662 4155490 0
632677.2 4155490 0
632692.5 4155490 0
632707.7 4155490 0
632723 4155490 0
632738.2 4155490 0
632753.4 4155490 0
632768.7 4155490 0
632783.9 4155490 0
632799.2 4155490 0
632814.4 4155490 0
632829.6 4155490 0
632844.9 4155490 0
632860.1 4155490 0
632875.4 4155490 0
632890.6 4155490 0
632905.8 4155490 0
632921.1 4155490 0
632936.3 4155490 0
632951.6 4155490 0
632966.8 4155490 0
632982 4155490 0
632997.3 4155490 0
633012.5 4155490 0
633027.8 4155490 0
633043 4155490 0
631900 4155505 0
631915.2 4155505 0
631930.5 4155505 0
631945.7 4155505 0
631961 4155505 0
631976.2 4155505 0
631991.4 4155505 0
632006.7 4155505 0
632021.9 4155505 0
632037.2 4155505 0
632052.4 4155505 0
632067.6 4155505 0
632082.9 4155505 0
632098.1 4155505 0
632113.4 4155505 0
632128.6 4155505 0
632143.8 4155505 0
632159.1 4155505 0
632174.3 4155505 0
632189.6 4155505 0
632204.8 4155505 0
632220 4155505 0
632235.3 4155505 0
632250.5 4155505 0
632265.8 4155505 0
632281 4155505 0
632296.2 4155505 0
632311.5 4155505 0
632326.7 4155505 0
632342 4155505 0
632357.2 4155505 0
632372.4 4155505 0
632387.7 4155505 0
632402.9 4155505 0
632418.2 4155505 0
632433.4 4155505 0
632448.6 4155505 0
632463.9 4155505 0
632479.1 4155505 0
632494.4 4155505 0
632509.6 4155505 0
632524.8 4155505 0
632540.1 4155505 0
632555.3 4155505 0
632570.6 4155505 0
632585.8 4155505 0
632601 4155505 0
632616.3 4155505 0
632631.5 4155505 0
632646.8 4155505 0
632662 4155505 0
632677.2 4155505 0
632692.5 4155505 0
632707.7 4155505 0
632723 4155505 0
632738.2 4155505 0
632753.4 4155505 0
632768.7 4155505 0
632783.9 4155505 0
632799.2 4155505 0
632814.4 4155505 0
632829.6 4155505 0
632844.9 4155505 0
632860.1 4155505 0
632875.4 4155505 0
632890.6 4155505 0
632905.8 4155505 0
632921.1 4155505 0
632936.3 4155505 0
632951.6 4155505 0
632966.8 4155505 0
632982 4155505 0
632997.3 4155505 0
633012.5 4155505 0
633027.8 4155505 0
633043 4155505 0
631900 4155520 0
631915.2 4155520 0
631930.5 4155520 0
631945.7 4155520 0
631961 4155520 0
631976.2 4155520 0
631991.4 4155520 0
632006.7 4155520 0
632021.9 4155520 0
632037.2 4155520 0
632052.4 4155520 0
632067.6 4155520 0
632082.9 4155520 0
632098.1 4155520 0
632113.4 4155520 0
632128.6 4155520 0
632143.8 4155520 0
632159.1 4155520 0
632174.3 4155520 0
632189.6 4155520 0
632204.8 4155520 0
632220 4155520 0
632235.3 4155520 0
632250.5 4155520 0
632265.8 4155520 0
632281 4155520 0
632296.2 4155520 0
632311.5 4155520 0
632326.7 4155520 0
632342 4155520 0
632357.2 4155520 0
632372.4 4155520 0
632387.7 4155520 0
632402.9 4155520 0
632418.2 4155520 0
632433.4 4155520 0
632448.6 4155520 0
632463.9 4155520 0
632479.1 4155520 0
632494.4 4155520 0
632509.6 4155520 0
632524.8 4155520 0
632540.1 4155520 0
632555.3 4155520 0
632570.6 4155520 0
632585.8 4155520 0
632601 4155520 0
632616.3 4155520 0
632631.5 4155520 0
632646.8 4155520 0
632662 4155520 0
632677.2 4155520 0
632692.5 4155520 0
632707.7 4155520 0
632723 4155520 0
632738.2 4155520 0
632753.4 4155520 0
632768.7 4155520 0
632783.9 4155520 0
632799.2 4155520 0
632814.4 4155520 0
632829.6 4155520 0
632844.9 4155520 0
632860.1 4155520 0
632875.4 4155520 0
632890.6 4155520 0
632905.8 4155520 0
632921.1 4155520 0
632936.3 4155520 0
632951.6 4155520 0
632966.8 4155520 0
632982 4155520 0
632997.3 4155520 0
633012.5 4155520 0
633027.8 4155520 0
633043 4155520 0
631900 4155535 0
631915.2 4155535 0
631930.5 4155535 0
631945.7 4155535 0
631961 4155535 0
631976.2 4155535 0
631991.4 4155535 0
632006.7 4155535 0
632021.9 4155535 0
632037.2 4155535 0
632052.4 4155535 0
632067.6 4155535 0
632082.9 4155535 0
632098.1 4155535 0
632113.4 4155535 0
632128.6 4155535 0
632143.8 4155535 0
632159.1 4155535 0
632174.3 4155535 0
632189.6 4155535 0
632204.8 4155535 0
632220 4155535 0
632235.3 4155535 0
632250.5 4155535 0
632265.8 4155535 0
632281 4155535 0
632296.2 4155535 0
632311.5 4155535 0
632326.7 4155535 0
632342 4155535 0
632357.2 4155535 0
632372.4 4155535 0
632387.7 4155535 0
632402.9 4155535 0
632418.2 4155535 0
632433.4 4155535 0
632448.6 4155535 0
632463.9 4155535 0
632479.1 4155535 0
632494.4 4155535 0
632509.6 4155535 0
632524.8 4155535 0
632540.1 4155535 0
632555.3 4155535 0
632570.6 4155535 0
632585.8 4155535 0
632601 4155535 0
632616.3 4155535 0
632631.5 4155535 0
632646.8 4155535 0
632662 4155535 0
632677.2 4155535 0
632692.5 4155535 0
632707.7 4155535 0
632723 4155535 0
632738.2 4155535 0
632753.4 4155535 0
632768.7 4155535 0
632783.9 4155535 0
632799.2 4155535 0
632814.4 4155535 0
632829.6 4155535 0
632844.9 4155535 0
632860.1 4155535 0
632875.4 4155535 0
632890.6 4155535 0
632905.8 4155535 0
632921.1 4155535 0
632936.3 4155535 0
632951.6 4155535 0
632966.8 4155535 0
632982 4155535 0
632997.3 4155535 0
633012.5 4155535 0
633027.8 4155535 0
633043 4155535 0
631900 4155551 0
631915.2 4155551 0
631930.5 4155551 0
631945.7 4155551 0
631961 4155551 0
631976.2 4155551 0
631991.4 4155551 0
632006.7 4155551 0
632021.9 4155551 0
632037.2 4155551 0
632052.4 4155551 0
632067.6 4155551 0
632082.9 4155551 0
632098.1 4155551 0
632113.4 4155551 0
632128.6 4155551 0
632143.8 4155551 0
632159.1 4155551 0
632174.3 4155551 0
632189.6 4155551 0
632204.8 4155551 0
632220 4155551 0
632235.3 4155551 0
632250.5 4155551 0
632265.8 4155551 0
632281 4155551 0
632296.2 4155551 0
632311.5 4155551 0
632326.7 4155551 0
632342 4155551 0
632357.2 4155551 0
632372.4 4155551 0
632387.7 4155551 0
632402.9 4155551 0
632418.2 4155551 0
632433.4 4155551 0
632448.6 4155551 0
632463.9 4155551 0
632479.1 4155551 0
632494.4 4155551 0
632509.6 4155551 0
632524.8 4155551 0
632540.1 4155551 0
632555.3 4155551 0
632570.6 4155551 0
632585.8 4155551 0
632601 4155551 0
632616.3 4155551 0
632631.5 4155551 0
632646.8 4155551 0
632662 4155551 0
632677.2 4155551 0
632692.5 4155551 0
632707.7 4155551 0
632723 4155551 0
632738.2 4155551 0
632753.4 4155551 0
632768.7 4155551 0
632783.9 4155551 0
632799.2 4155551 0
632814.4 4155551 0
632829.6 4155551 0
632844.9 4155551 0
632860.1 4155551 0
632875.4 4155551 0
632890.6 4155551 0
632905.8 4155551 0
632921.1 4155551 0
632936.3 4155551 0
632951.6 4155551 0
632966.8 4155551 0
632982 4155551 0
632997.3 4155551 0
633012.5 4155551 0
633027.8 4155551 0
633043 4155551 0
632448.6 4154911 -0.05213
632463.9 4154911 -0.09581
total 1050.461