DRC-2020-010062 - 0901a06880c89842

Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.encrgy rue I s.com ENERGY FUELS
P RC- 2020 -0 10062_
May 13, 2020
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
Re: Transmittal of 1st Quarter 2020 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Mr. Howard:
Div of Waste Management
and Radiation Control
ItilAY 1 8 2020
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 1st Quarter of
2020 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,
aay 1
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Paul Goranson
Logan Shumway
Scott Bakken
Terry Slade
May 13, 2020
Sent VIA OVERNIGHT DELIVERY
Mr. Ty L. Howard
Director
Di vision 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
Re: Transmittal of 1st Quarter 2020 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 1st Quarter of
2020 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,
i1Zkf 5v~
. I
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
1st Quarter
(January through March)
2020
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
May 13, 2020
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 QA/QC 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 QA/QC Evaluation for Sample Duplicates ............................................... 10
3.4.9 Rinsate Sample Check .............................................................................. 10
3.4.10 Other Laboratory QA/QC ......................................................................... 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 Hydro graphs .............................................................................................. 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
1
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 ....................................................... 31
5.6 Inspections ........................................................................................................ 31
5.7 Conditions That May Affect Water Levels in Piezometers .............................. 32
6.0 CORRECTIVE ACTION REPORT ................................................................. 32
6.1 Assessment of Previous Quarter's Corrective Actions ..................................... 32
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. ................................................................. 33
7.4 Compliance Well Performance ......................................................................... 33
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 Wells 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 QA/QC 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 QA/QC 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 first quarter of 2020 as required
under the SCO. This report also includes the Operations Report for MW-04, TW4-01, 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, TW4-11, 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 wells. These wells are sampled throughout the
sampling event and are not sampled in the order of contamination. This practice does not affect
the samples for this reason: the pumping wells have dedicated pumps and there will be no cross-
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 is collected at a frequency
of one rinsate sample per 20 field samples. Well depth measurements are taken and the one
casing volume is calculated for those wells which do not have a dedicated pump as described 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 samples 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 H of this Report. Also included under Tab H are 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 AWAL 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 SOPs
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 QA/QC evaluation, a holding time check, a receipt
temperature check, an analytical method check, a reporting limit evaluation, a trip blank check, a
QA/QC 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 Volume with Stable Field Parameters (within 10% RPO)
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% RPO.
Purging a Well to Dryne s and Stability of a Limited List 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% RPO under the QAP. The QAP
requirements for stabilization were met.
Continuously 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 TW4-9, TW4-16, MW-32, TW4-18, TW4-21, TW4-23, TW4-32, and TW4-38 exceeded
the QAP's 5 NTU goal. EFRI's letter to DWMRC of March 26, 2010 discusses further 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
than the increased detection limit.
9
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 11.3 ug/L. TW4-3 was
nondetect for chloroform. Rinsate blank sample TW 4-9R had a reported chloroform detection of
12.3 ug/L. TW4-9 had a chloroform detection of 48.9 ug/L. Both rinsate blank results were
outside of acceptance limits for the rinsate blank results.
TW4-3R was collected after decontamination and prior to the pump being used to collect any Ql
2020 chloroform samples. Because the pump was not used prior to the rinsate sample collection,
the detection is not the result of cross contamination. TW 4-9R was collected after the
decontamination was completed after purging well TW4-30 and prior to sampling TW4-9.
TW 4-9 had a chloroform detection of 48.9 ug /L. The chloroform detection of 48.9 ug/L in
TW4-9 is within the historic range of detections and is not likely the result of cross
contamination.
10
Prior to the Ql 2020 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 TW4-3 and TW4-9 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 as
indicated in Tab I.
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
from the Laboratory QA/QC Summary Reports indicates that the surrogate recoveries for the
quarterly chloroform samples were within acceptable laboratory limits for the surrogate
11
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 QNQC 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 QNQC Summary Reports indicates that there was a high
Continuing Calibration Verification ("CCV") recovery for chloromethane. The CCV recovery
affected samples MW-04, TW4-1, TW4-2, TW4-4, TW4-11, MW-26, TW4-20, TW4-22, TW4-
37, TW4-39, and TW4-41. 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 the high CCV
recovery is indicative of a high bias to the sample results. A high bias results in a more
conservative data application. EFRI does not believe the data quality has been affected.
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 north-northwesterly 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 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.
12
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:
1) Reduced dilution -the mixing of low constituent concentration pond recharge into
existing perched groundwater will be reduced over time.
13
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. Impacts were also expected to occur over time at wells subsequently added to the
chloroform pumping network: TW4-1, TW4-2, TW4-11, 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
TW4-4, and 2) historical relatively low water levels at adjacent well TW4-14.
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.
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
14
wells immediately south and southeast (downgradient) of TW4-4 resulting from TW4-4 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 TW 4-4 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 Gust prior to the start of TW4-4 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 outside the plume
again this quarter) has also trended downward since the fourth quarter 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 TW 4-14,
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 pumpmg 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 TW 4-4 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 TW 4-4 has been pumping since 2010, the water level at TW 4-14 was
typically lower than the water level at TW4-6 and lower to an even greater extent than the water
level at TW4-4. For the current quarter, as during the previous quarter, the water level at TW4-
14 is higher than water levels at both TW 4-4 and TW 4-6: the water level at TW 4-14
(approximately 5535.3 feet above mean sea level ["ft amsl"]) is 4 feet higher than the water level
at TW4-6 (approximately 5531.3 ft amsl), and nearly 1 foot higher than the water level at TW4-4
(approximately 5534.4 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 TW4-4, TW4-6, and TW4-
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 downgradient of TW4-4, regardless of the
flow direction implied by the relatively low water level at TW4-14. The water level at TW4-26
(5529.7 feet amsl) is, however, lower than water levels at adjacent wells TW4-6 (5531.3 feet
amsl) and TW4-23 (5533.3 ft. amsl), as shown in the detail water level map under Tab C.
Hydraulic tests indicate that the permeability at TW4-27 is an order of magnitude lower than at
TW4-6 and three orders of magnitude lower than at TW4-4 (see Hydro Geo Chem, Inc. [HGC],
September 20, 2010: Hydraulic Testing of TW4-4, TW4-6, and TW4-26, White Mesa 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 (see: HGC, January 23, 2014, Contamination
Investigation Report, TW4-12 and TW4-27 Areas, White Mesa Uranium Mill Near Blanding,
Utah; and HGC, July 1, 2014, Installation and Hydraulic Testing 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 5529.3 ft. amsl) is approximately 6
feet lower than the water level at TW4-14 (5535.3 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
directions including downgradient to the south. The relative hydraulic isolation of TW 4-14 and
16
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 TW 4-14 due to factors that include: closer proximity
to the northern pond seepage source; and a smaller thickness of low permeability materials
separating TW4-14 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 TW4-27 sooner and to a
greater extent than TW4-14, consistent with the lower rate of increase in water levels at TW4-27,
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 transport of chloroform
to these wells (compared to nearby wells). As will be discussed in Section 4.2.3, TW4-14 and
TW 4-27 remain outside the plume with current quarter chloroform concentrations of
approximately 3 µg/L and 8 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 TW4-4 to TW4-
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 TW 4-4 around
the low permeability zone defined by TW4-36, TW4-14, and TW4-27.
Chloroform during the current quarter was detected at approximately 53 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 TW 4-26 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 TW4-30, 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 at TW4-29 and TW4-33 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 at both wells (since about the fourth quarter of
2013); temporarily increased concentrations at TW4-6 subsequent to the first quarter of 2014;
and increased concentrations at TW4-26 since the third quarter of 2016.
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 TW4-26.
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 TW 4-26 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 TW4-6 dropping below 70 µg/L after the second quarter of
2018. Furthermore, 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 TW4-40.
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 (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 fourth quarter of 2019, as submitted with
the Chloroform Monitoring Report for the fourth quarter of 2019, is attached under Tab E. A
comparison of the water table contour maps for the current quarter (first quarter of 2020) to the
water table contour maps for the previous quarter (fourth quarter of 2019) indicates the
following: water level changes at the majority of site wells were small ( < lfoot); 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-ll, 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 TW 4-41 since the second quarter of 2018 and from initiation of
pumping at TW 4-40 during the second quarter of 2019.
The drawdown at chloroform pumping well MW-4 increased by more than 2 feet this quarter.
However drawdowns at chloroform pumping wells MW-26, TW4-1, TW4-4 and TW4-21; and
nitrate pumping wells TW4-22, TW4-24 and TWN-2 decreased by more than 2 feet this quarter.
Water level changes at other nitrate and chloroform pumping wells were 2 feet or less, although
both increases (decreases in drawdown) and decreases (increases in drawdown) occurred. Water
19
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 levels for
chloroform pumping wells TW 4-1, TW 4-2 and TW 4-11 are below the depth of the Brushy Basin
contact this quarter. Although both increase·s 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 TW 4-4, 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 TW4-4 and adjacent pumping well TW4-41
since the initiation of pumping at TW 4-41 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.
The reported water level decreases of up 0.38 feet at Piezometers 1, 2 and 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 0.34 feet at Piezometers 4 and 5 likely resulted primarily from reduced
recharge at the southern wildlife pond. Reported water level decreases of approximately 0.39 and
0.34 feet, respectively, at TWN-1 and TWN-4 are consistent with continuing decay of the
northern groundwater mound.
The reported water levels at MW-20 and MW-37 increased by approximately 2.5 and 7.5 feet,
respectively, compensating for decreases last quarter. Water level variability at these wells
likely results from low permeability and variable intervals between purging/sampling and water
level measurement. The reported water level increase of nearly 4 feet at MW-22 may result from
measurement error.
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 m 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 rapidly as is practical.
The original pumping wells up gradient of TW 4-4 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 further 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
TW4-20 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 TW 4-4 became operational in 2010, the draw down
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 TW 4-
21
2, TW4-11, TW4-19, TW4-20, TW4-37, TW4-39, TW4-40 and TW4-41; and nitrate pumping
well TW 4-25 were less than two feet. Water level decreases occurred in chloroform pumping
wells MW-4 (nearly 8 feet); TW4-19 (approximately 0.2 feet); TW4-37 (nearly 2 feet); TW4-39
(approximately 1.6 feet); and TW4-40 (approximately 0.9 feet). Water level increases occurred
in chloroform pumping wells MW-26 (approximately 3.2 feet); TW4-1 (approximately 2.3 feet);
TW4-2 (approximately 1 foot); TW4-4 (approximately 6 feet); TW4-11 (approximately 1 foot);
TW4-20 (approximately 1.3 feet); TW4-21 (approximately 5 feet); and TW4-41 (nearly 2 feet);
and in nitrate pumping wells TW4-22 (approximately 13 feet); TW4-24 (approximately 9 feet);
TW4-25 (approximately 0.1 feet); and TWN-2 (nearly 10 feet). The overall apparent combined
capture area of the nitrate and chloroform pumping systems is smaller than last quarter, with
capture decreasing within the central and northern portion of the pumping system due to
decreased drawdowns at MW-26, TW4-21, TW4-22, TW4-24 and TWN-2.
The capture associated with nitrate pumping wells and chloroform pumping wells added since
the beginning of 2015 is expected to generally 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 since the third quarter of 2014 have been noted 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 (717,160 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.
22
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
pumping wells are attributable to westward migration of chloroform from the vicinity of TW 4-20
toward these wells. The increase in concentration at TW4-8 from non-detect to 100 µg/L in the
first quarter of 2014 is likely related to reduced dilution. The concentration at TW4-8 remained
above 70 ug/L as of last quarter but has dropped below 70 µg/L this quarter. In addition,
although the chloroform concentration in TW 4-6 generally decreased between the first quarter of
2015 and the current quarter (and remains outside the plume), concentrations at TW4-6 increased
from approximately 6 µg/L in the first quarter of 2014 to 1,180 µg/L in the first quarter of 2015
before dropping to approximately 7 µg/L this quarter. The increase between the first quarter of
2014 and the first quarter of 2015 was 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 2010; 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 and TW4-41) 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 TW4-4 was
implemented during the first quarter of 2010 to improve capture downgradient of TW 4-4 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 quarter 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, TW4-11
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
23
pumping system has expanded since initiation of pumping at wells TW4-1, TW4-2, TW4-11
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
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 116 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 TW 4-33 were likely higher prior to initiation of TW 4-4 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 turn
24
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 quarter of 2016 to 1,090
µg/L this quarter).
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 ofTW4-29 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 111.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: TW4-2, TW4-7, TW4-19, TW4-20 and TW4-24;
25
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: MW-26, TW4-8, TW4-14, and TW4-39;
c) Chloroform concentrations have remained within 20% in the following wells compared
to last quarter: MW-4, TW4-1, TW4-4, TW4-5, TW4-6, TW4-9, TW4-10, TW4-11,
TW4-16, TW4-18, TW4-21, TW4-22, TW4-26, TW4-27, TW4-29, TW4-30, TW4-33,
TW4-37, TW4-40 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 MW-26, TW4-2,
TW4-7, TW4-8, TW4-14, TW4-19, TW4-20, TW4-24 and TW4-39 had changes in
concentration greater than 20%. Of these, MW-26, TW4-2, TW4-19, TW4-20 and TW4-39 are
chloroform pumping wells; and TW4-24 is a nitrate pumping well. TW4-7 and TW4-8 are
located adjacent to chloroform pumping well MW-4; and TW4-14 is located adjacent to
chloroform pumping wells TW 4-4 and TW 4-41. 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 and TW4-24 are located just outside the plume boundary. Fluctuations in
concentrations at these wells are expected based on their locations near the plume margins.
Chloroform pumping wells TW4-2 (1,880); TW4-11 (2,990 µg/L); TW4-19 (8,720 µg/L), TW4-
20 (14,300 µg/L) and TW4-37 (12,000 µg/L); and nitrate pumping well TW4-22 (3,910 µg/L),
had the highest detected chloroform concentrations. Since last quarter, the chloroform
concentrations in TW4-2 increased from 934 to 1,880 µg/L; TW4-11 decreased from 3,250 to
2,990 µg/L; TW4-19 increased from 551 to 8,720 µg/L; TW4-20 increased from 8,790 µg/L to
14,300 µg/L; and TW4-37 decreased from 13,100 µg/L to 12,000 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 increased from 794 to 844 µg/L;
the concentration in nitrate pumping well TW4-22 increased from 3,820 to 3,910 µg/L; and the
concentration in nitrate pumping well TW4-24 increased from 43.3 to 61.7 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 84.4 µg/L to 55 µg/L, taking it again outside the plume. TW4-8
is located immediately east of chloroform pumping well MW-4, where chloroform was detected
at a concentration of 1,230 µg/L. Although the plume boundary remained between MW-4 and
TW4-8 from the first quarter of 2005 through the fourth quarter of 2013, TW4-8 was re-
incorporated into the plume between the first quarter of 2014 and last quarter. The occurrence of
elevated chloroform at TW 4-8 is likely related to its location along the eastern plume boundary
26
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 TW 4-8 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 (3 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 from 630 µg/L to 652 µg/L, and chloroform at TW4-
30, located immediately cross-to downgradient of TW4-29, increased from approximately 45
µg/L to approximately 53 µg/L. Chloroform at TW4-14 decreased from 3.8 µg/L to 3 µg/L and
chloroform at TW4-27 remained at approximately 8 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 (approximately 8 µg/L), to
the east by TW4-30 (approximately 53 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 7 µg/L) and
TW4-23 (non-detect). As discussed in Section 4.1.1, 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 117 µg/L to 94 µg/L. Chloroform at TW4-33 is bounded to
the north by TW4-14 (3 µg/L), to the east by TW4-27 (approximately 8 µg/L), and to the west by
TW4-6 (approximately 7 µg/L) and TW4-23 (non-detect). Recent increases in concentration at
TW 4-26 have widened the southeast extremity of the plume which historically was narrow
compared to more upgradient locations.
The chloroform concentration in TW4-6 remained approximately 7 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 v1c1mty 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 TW 4-4. Concentrations at TW 4-4 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
27
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
that occurred after initiation of TW 4-4 pumping, chloroform concentrations at both TW 4-29 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 TW4-24 and a slight contraction near TW4-33. The chloroform concentration
increase at TW4-24, from approximately 43 µg/L to 62 µg/L, shifted the plume boundary to the
west toward TW4-24. The concentration decrease at TW4-33 from approximately 117 µg/L to
94 µg/L, and relatively low concentration at adjacent well TW4-6, caused the kriging algorithm
to 'pinch off the southern extremity of the plume for the first time.
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). Subsequent to the first quarter of 2014, generally
higher concentrations at TW4-6 and TW4-16 (both of which were within the chloroform plume
in the past) caused the plume boundary to migrate to the southwest and temporarily re-
incorporate both wells. This increase was 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.
TW 4-6 has remained outside the plume since the third quarter of 2018 due to the general
decrease in chloroform concentrations since the third quarter of 2015, while (as discussed in
Section 4.1.5) TW4-16 has been both within and outside the plume. This quarter, although TW4-
6 remains outside the plume, TW4-16 remains just inside the plume.
The decreasing trend in chloroform 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. This behavior is consistent with the apparent 'pinching-off of the southern
extremity of the plume this quarter. Regardless, pumping at TW 4-41, located adjacent to TW 4-4,
and pumping at TW4-40, located just south (downgradient) of TW4-26, is expected to reduce or
halt plume expansion to the south.
28
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 of TW4-1, TW4-2, and
TW4-11 pumping during 2015. Maintaining reduced concentrations at TW4-6 is anticipated to
result from pumping at TW 4-41.
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 long
term pumping of TW 4-41. Beginning in May 2019 EFRI began long term pumping of TW 4-40.
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.
29
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
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 TW 4-1, TW 4-2, TW 4-11, TW 4-21, TW 4-22,
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.
30
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 18.9 lb., which is approximately 45% larger than the approximately
13 lb. removed last quarter. The larger rate of mass removal is attributable primarily to the
increased concentrations at TW4-19 and TW4-20.
The residual mass of chloroform within the plume is estimated as 1,106 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 336 lb. larger than last quarter's estimate of 770 lb. As per Part
III.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.l. Since the third quarter of 2015 the trend is downward;
the current quarter's estimate of 1,106 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 Part 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, 2018 and 2019 ranged from
approximately 84% to 99%. The approximate proportion of the mass of the plume under capture
this quarter is 99%, about the same as last quarter's.
5.6 Inspections
All of the required inspections were completed and the inspection forms are included in Tab C.
31
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.
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 7 µg/L), TW4-
23 (non-detect), and TW4-24 (approximately 62 µg/L); to the east by TW4-3 (non-detect), TW4-
5 (approximately 15 µg/L), TW4-9 (approximately 49 µg/L), TW4-13 (non-detect), TW4-14
(approximately 3 µg/L), TW4-18 (approximately 57 µg/L), TW4-27 (approximately 8 µg/L),
TW4-30 (approximately 53 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.
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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.
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 1,106 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 336 lb. larger than last quarter's estimate of 770 lb. The mass of
chloroform removed from the plume this quarter is approximately 18.9 lb., which is
approximately 45% larger than the approximately 13 lb. removed last quarter. The larger rate of
mass removal is attributable primarily to the increased chloroform concentrations at TW4-19 and
TW4-20.
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 7 µg/L), TW4-
23 (non-detect), and TW4-24 (approximately 62 µg/L); to the east by TW4-3 (non-detect), TW4-
5 (approximately 15 µg/L), TW4-9 (approximately 49 µg/L), TW4-13 (non-detect), TW4-14
(approximately 3 µg/L), TW4-18 (approximately 57 µg/L), TW4-27 (approximately 8 µg/L),
TW4-30 (approximately 53 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
33
(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 fourth 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 TW 4-
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
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 TW 4-4 until the third quarter of 2018. Increased draw downs
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 TW4-14 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, with capture decreasing within the central and northern
portions of the pumping system due to decreased drawdowns at MW-26, TW4-21, TW4-22,
TW4-24 and TWN-2.
'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
34
typical for sampling and analytical error. Wells MW-26, TW4-2, TW4-7, TW4-8, TW4-14,
TW4-19, TW4-20, TW4-24 and TW4-39 had changes in concentration greater than 20%. Of
these, MW-26, TW4-2, TW4-19, TW4-20 and TW4-39 are chloroform pumping wells; and
TW4-24 is a nitrate pumping well. TW4-7 and TW4-8 are located adjacent to chloroform
pumping well MW-4; and TW4-14 is located adjacent to chloroform pumping wells TW4-4 and
TW4-41.
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 and TW4-
24 are located just outside 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 continued operation of nitrate
pumping wells as the capture associated with nitrate pumping expands and flow directions
change locally.
Chloroform pumping wells TW4-2 (1,880); TW4-1 l (2,990 µg/L); TW4-19 (8,720 µg/L), TW4-
20 (14,300 µg/L) and TW4-37 (12,000 µg/L); and nitrate pumping well TW4-22 (3,910 µg/L),
had the highest detected chloroform concentrations. Since last quarter, the chloroform
concentrations in TW4-2 increased from 934 to 1,880 µg/L; TW4-11 decreased from 3,250 to
2,990 µg/L; TW4-19 increased from 551 to 8,720 µg/L; TW4-20 increased from 8,790 µg/L to
14,300 µg/L; and TW4-37 decreased from 13,100 µg/L to 12,000 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 increased from 794 to 844 µg/L;
the concentration in nitrate pumping well TW4-22 increased from 3,820 to 3,910 µg/L; and the
concentration in nitrate pumping well TW4-24 increased from 43.3 to 61.7 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 84.4 µg/L to 55 µg/L, taking it again outside the plume. TW4-8
is located immediately east of chloroform pumping well MW-4, where chloroform was detected
at a concentration of 1,230 µg/L. Although the plume boundary remained between MW-4 and
TW4-8 from the first quarter of 2005 through the fourth quarter of 2013, TW4-8 was re-
incorporated into the plume between the first quarter of 2014 and last quarter. 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 TW 4-8 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 (3 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 decreased
from approximately 3.8 µg/L to 3 µg/L and chloroform at TW4-27 remained at approximately 8
35
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 from 630 µg/L to 652 µg/L, and
chloroform at TW4-30, located immediately cross-to downgradient of TW4-29, increased from
approximately 45 µg/L to approximately 53 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 (approximately 8 µg/L), to
the east by TW4-30 (approximately 53 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 7 µg/L) and
TW4-23 (non-detect). In addition, general increases in concentrations at TW4-26 since the third
quarter of 2016 are 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 117 µg/L to 94 µg/L. Chloroform at TW4-33 is bounded to
the north by TW4-14 (3 µg/), to the east by TW4-27 (approximately 8 µg/L), and to the west by
TW4-6 (approximately 7 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 TW4-24 and a slight contraction near TW4-6. Chloroform concentrations at
TW4-24 increased from approximately 43 µg/L to 62 µg/L shifting the plume boundary toward
TW4-24. The relatively low concentration at TW4-6 (7 µg/L) and decrease at TW4-33 (from
approximately 117 µg/L to 94 µg/L), caused the kriging function to 'pinch off' the southern
extremity of the plume for the first time.
TW 4-9 remained outside the plume this quarter. Chloroform concentrations at TW 4-9 decreased
from approximately 55 µg/L to 49 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 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). Subsequent to the first quarter of 2014, generally
increased concentrations at TW 4-6 and TW 4-16 (both of which were within the chloroform
36
plume in the past), caused the plume boundary to migrate to the southwest and temporarily re-
incorporate both wells. Increased concentrations at these wells subsequent to 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
TW 4-6 may be influenced by reduced recharge at the southern wildlife pond and the decay of the
associated groundwater mound.
Since 2014, TW4-16 has been both within and outside the plume; whereas a decreasing trend in
chloroform concentrations at TW4-6 (since the third quarter of 2015) has once again taken TW4-
6 outside the plume. This quarter, TW4-16 and TW4-6 remain within and outside the plume,
respectively.
The 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 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
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,
TW4-40 and TW4-41 since the beginning of 2015 is expected to have a beneficial impact.
Generally reduced concentrations at TW 4-6 ( since the first quarter of 2015) and TW 4-16 ( since
the fourth quarter of 2014) after previous increases are likely the result of initiation of TW4-1,
TW 4-2, and TW 4-11 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 TW 4-4, 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
quarter 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
(augmented by TW4-41) pumping. Continued operation of TW4-1, TW4-2, TW4-11, TW4-21,
TW4-37, TW4-39, TW4-40 and TW4-41 is also recommended because pumping these wells has
increased overall capture and improved chloroform mass removal.
37
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 TW4-33 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.
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 Bakken Digitally signed by Scott Bakken
Date: 2020.05.13 19:10:33 -06'00'
Scott A. Bakken Date
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.
Digitally signed by Scott Bakken Scott Bakken Date:2020.05.1319:11:15
·06'00'
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
40
Tables
Table 1: Summary of Well Sampling for the Period
Well SamoleDate Date of Lab Reoort
MW-04 2/19/2020 3/9/2020
TW4-0l 2/19/2020 3/9/2020
TW4-02 2/19/2020 3/9/2020
TW4-03 3/17/2020 3/31/2020
TW4-03R 3/16/2020 3/31/2020
TW4-04 2/19/2020 3/9/2020
TW4-05 3/17/2020 3/31/2020
TW4-06 3/17/2020 3/31/2020
TW4-07 3/18/2020 3/31/2020
TW4-08 3/18/2020 3/31/2020
TW4-09 3/18/2020 3/31/2020
TW4-09R 3/17/2020 3/31/2020
TW4-10 3/18/2020 3/31/2020
TW4-ll 2/19/2020 3/9/2020
TW4-12 3/17/2020 3/31/2020
TW4-13 3/17/2020 3/31/2020
TW4-14 3/17/2020 3/31/2020
MW-26 2/19/2020 3/9/2020
TW4-16 3/18/2020 3/31/2020
MW-32 3/18/2020 3/31/2020
TW4-18 3/18/2020 3/31/2020
TW4-19 2/19/2020 3/9/2020
TW4-20 2/19/2020 3/9/2020
TW4-21 2/19/2020 3/9/2020
TW4-22 2/19/2020 3/9/2020
TW4-23 3/17/2020 3/31/2020
TW4-24 2/19/2020 3/9/2020
TW4-25 2/19/2020 3/9/2020
TW4-26 3/18/2020 3/31/2020
TW4-27 3/17/2020 3/31/2020
TW4-28 3/17/2020 3/31/2020
TW4-29 3/18/2020 3/31/2020
TW4-30 3/17/2020 3/31/2020
TW4-31 3/17/2020 3/31/2020
TW4-32 3/17/2020 3/31/2020
TW4-33 3/18/2020 3/31/2020
TW4-34 3/17/2020 3/31/2020
TW4-35 3/17/2020 3/31/2020
TW4-36 3/17/2020 3/31/2020
TW4-37 2/19/2020 3/9/2020
TW4-38 3/17/2020 3/31/2020
TW4-39 2/19/2020 3/9/2020
TW4-40 2/19/2020 3/9/2020
TW4-41 2/19/2020 3/9/2020
TW4-42 3/17/2020 3/31/2020
TW4-60 2/19/2020 3/9/2020
TW4-65 3/17/2020 3/31/2020
TW4-70 3/17/2020 3/31/2020
TW4-75 3/18/2020 3/31/2020
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 ofMW-32.
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 QA/QC 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
1-7 QA/QC 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
MW-24A perched monitoring well installed • December 2019
TW4-42
¢ temporary perched monitoring well
installed April 2019
TW4-40 perched chlorofonn 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 -1
RUIN SPRING
b seep or spring
HYDRO
GEO
CHEM, INC.
WHITE MESA SITE PLAN SHOWING LOCATIONS OF
PERCHED WELLS AND PIEZOMETERS
APPROVED DATE REFERENCE FIGURE
H:/718000/aug 19/Uwelloc1219.srf A-1
TabB
Order of Sampling and Field Data Worksheets
Order of Contamination for 1st Quarter 2020 Chlorofonn Purging Event
ChlorofollO
Well Sample time Levels Rlnsate date/time
TW4-03 3.h'1 /'ZQ 0~5 ND
TW4-42 3/)l/.10 t'.>$~ ND
TW4-28 :\1)"1(:2,0 08,~ ND
TW4-32.'}/i"1/.:.D O?l:J<f ND
TW4-12 ;~1g:g, ¢3:l.S ND
TW4-13 ~ _/ _0&91 ND
Tw4-3otrm.o oqos ND
TW4-3l ~fllz0 ~Z. ND
TW4-34 _ tJ:µ) _ U) ND
TW4-35 :!,})1/:J.D ffl:l.8 ND
TW4-23 3/l'z(AA 0,3( ND
MW-32!>/Ul/.:tO IDO'!l ND
TW4-38 :2,,J l1h.o oSi.f.5 ND
rw4.25 2. 119120 oim. ND
TW4-14 V r,/Z,O 1)955 3.83
TW4--06 )111/ti.0 J<'>0,5 7.4
TW4-27 ,l. /r, J:l.D JC>\"{ 7.97
TW4--05 .,Jr1/'IB 102.Y 15.7
TW4-24 :L/1'1 ?.o )ZOO 43.3
TW4-30 ;,/!7/'Z.O 11)38 44.9
rw4-o9 311gpo 0scs s4.8
TW4-183/JM;ap ,).."j~ 62
TW4--08 ~/12,/2.0 OS:?,:l. 84.4
TW4-16 ?,M/.:tO ()!:MO 94.3
TW4-33 -V:f-i> i!!:>O 117 TW4-40'1./_U> _ S:::.0314
TW4--07 3/1~/tO Of):;O 546
TW4-19 Z./l IW d':J 15 551
TW4-29 3/ISIAA _E:.\Z. 630
TW4-I o :,/ UVAA ,)(.c)S 768
TW4-2 t 211'1 lW O'l.3C 794
TW4-027,.9 q r,-;, \~QS 934
TW4-26 .} jg ~ .)~1070
TW4-01.z./11/io !?>2'i t070
TW4-04 U!'j/?.O f3'i0 1140
MW-04 '2./14/w 12>1.5 1370
MW-26 --z./ )'! {1,b j'2.Lf0 1390
TW4-41 2.fl'l {'l.l> l;}m 1410
TW4-39'2.mZ.3l,16S0
TW4-J 1 20 '2.!>0 3250
TW4-22 2. lf> J.?.O(i 3820
TW4-202-/l'l/t O tZ-2.S 8790
TW4-37')../'(i/zl> 12. lb 13100
TW4-60 D.I. Blank ~11/'Z-0
TW4-65 Duplicate ·:Mnl:io
TW4-70 Duplicate 3h7 IM
TW4-7S Duplicate 31/~/'.2 O
Comments:
Water
level
Well
Depth
141
86
107
115.1
101.5
102.5
99
106
97.2
87.5
114
130.6 Bladder pump
112.75
134.8 Cont. Pumping
93
97.5
96
120
112.5 Cont. Pumping
92.5
120 ·'(w'-l • oq R_ o3 nzoz.D i 100
137.5
125
146.3
87.9
86 Cont. Pumping
120
125 Cont. Pumpins
93.5
Ill
121 Cont. Pumping
120 Cont. Pumplns
86
110 Cont. Pumping
112 Cont. Pumping
124 Cont. Pumping
122.5 Cont. Pumping
97. 75 Cont. Pumping
120 Cont. Pumping
100 Cont. Pumping
113.5 Cont. Pumping
I 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 Monitoring
Field Sample ID MW-04 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:14
Sample Date & Time 2/19/2020 13:15 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled TW4-02
Casing Volume (gal) 14.40
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) 84.34
Date/Time Gallons Purg_ed (umhos/cm} pH (pH Units)! Temp (deg C) Redox (mV) Turbidity (NTU) Ox}'_g_en (%) I Before/After
2/19/2020 13:14 1886 7.39 I 14.22 255 0 41.50
Pumping Rate Calculations
jvolume of water purged Q Flow Rate (Q = S/60) (gal/min) 4.00
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 88.90 Number of casing Volumes
Volume, if well evacuated to dryness O 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 1311. Samples collected at 1315. Water was clear. Left site at 1317.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~~
-~~~A=RGY,llq..9FP'S
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-01 Sampling Program Chloroform Monitoring
Field Sample ID TW4-01 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:23
Sample Date & Time 2/19/2020 13:24 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled MW-04
Casing Volume (gal) 19.06
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) 82.10
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 13:23 2414 7.25 14.15 338 0 72.5
Pumping Rate Calculations
~lu_me ~f water purged_() Flow Rate (Q = S/60) (gal/min) 13.00
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 105.56 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Anal~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 1320. Samples collected at 1324. Water was clear. Left site at 1326.
Signature of Field Technician
~c.u~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-02 Sampli_rl_g_Program Chloroform Monitoring
Field Sample ID TW4-02 02192020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:04
Sample Date & Time 2/19/2020 13:05 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 8
Purging Method 2 Casings Previous Well Sampled TW4-11
Casing Volume (gal) 21.82
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) 87.48
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/19/2020 13:04 3798 7.24 14.40 263 0 79.6
lv_511ume of water purged ()
Pumpin9 Rate Calculations
Flow Rate (Q = S/60) (gal/min) 17.00
Time to evacuate 2 Casing Volumes () I Final Deeth to Water (feet) 113.68 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sa'!l_eles 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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 1301. Samples collected at 1305. Water was clear. Left site at 1308.
Signature of Field Technician
~~ ~ . <='
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~·'F-::1 '~ . R: -. ~ ... ,,····---~· .-~~s ' ._____ ~--· ,,• -----.,./ 4 A
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03 Sampling Program Chloroform Monitoring
Field Sample ID TW4-03 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 8:05
Sample Date & Time 3/17/2020 8:05 [~ampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 3
Purging Method 2 Casings Previous Well Sampled TW4-03R
Casing Volume (gal) 50.48
Calculated Casing Volumes Purge Duration (min) 9.17
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) 62.98
Conductivity Dissolved
Dateffime Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen{%) Before/ After
3/16/2020 8:11 71.50 1818 6.84 14.57 481 5.8 76.7
3/17/2020 8:04 1794 6.88 13.16 Before
3/17/2020 8:07 1795 6.90 13.21 After
Pumping Rate Calculations
l'!'o~ume of water eurged (gals) 71.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 6.50
[Final Depth to Water (feet) 137.89 Number of casing Volumes 1.41
Volume, if well evacuated to dryness (gals) 71.SO
Name of Certified Analytical l..aboratory
AWSL
Analytical Same_les 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 0802. Purge began at 0805. Purged well for a total of 6 minutes and 30 seconds. Purged well dry. Purge ended at 0811. Water was clear. Left site at 0814. Arrived on site at
0800. Dep_th to water was 63.05. Samples bailed and collected at 0805. Left site at 0808.
Signature of Field Technician
~u~4~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03R Samefing Program
Field Sample ID T\N4-03R 03162020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/16/2020 7:45 [sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sam_eled
Casing Volume O
Calculated Casing Volumes Purge Duration O
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing_pJamete~_{)
Specific Conductance () Depth to Water Before Purging (ft)
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 7:43 133.00 1.3 7.68 13.46 477 0 31.5
Pumping Rate Calculations
[Volume of water purged () Flow Rate {Q = S/60) ()
[Final Depth to Water (feet)
Time to evacuate 2 Casing_ Volumes ()
Number of casin_g_ Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory
A\NSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
Chloride y \NATER 1 500-ml Poly u None N
VOCs-Chloroform y \NATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Nitrate/nitrite as N y \NATER 1 250-ml HOPE u H2504 (pH<2), 4 Deg C y
Comments:
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-04 Sampling Program Chloroform Monitoring
Field Sample ID TW4-04 02192020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:39
Sample Date & Time 2/19/2020 13:40 !!:>ampler TH/OL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled TW4-41
Casing Volume (gal) 24.55
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) 76.89
Date/Time Gallons Purged (um hos/cm) pH (pH Units} Temp(de_g_ C) Redox (mV) Turbidity (NTU) Oxygel'l_l~ I Before/After
2/19/2020 13:39 2362 7.27 14.85 286 0 128.5
Pumping Rate Calculations
~lume o!__ water pu_rged O Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 107.65 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laborat5>__1)'
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 a11337. Samples collected at 1340. Water was clear. Left site at 1342.
Signature of Field Technician
..::;=~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan --~-~· _. .· ~ ..... .,. ,'.· . ~ _. ( . -, . ,· --~ /~y~
I -~.;~-_,
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-05 Samplin_g Program Chloroform Monitoring
Field Sample ID TW4-05 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 16:04
Sample Date & Time 3/17/2020 10:24 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 14
Purging Method 2 Casings Previous Well Sampled TW4-27
Casing Volume (gal) 33.70
Calculated Casing Volumes Purge Duration (min) 6.12
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) 70.23
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 16:09 55.00 1515 6.80 15.44 447 3.0 61.0
3/16/2020 16:10 66.00 1506 6.83 15.45 441 2.9 59.0
3/16/2020 16:11 77.00 1495 6.87 15.44 436 3.0 57.0
3/16/2020 16:12 88.00 1488 6.91 15.44 432 3.0 56.4
Pumping Rate Calculations
['!'_olume of water i,urged (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) 73.89 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Anal~cal 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 I y
Comments:
Arrived on site at 1600. Purge began at 1604. Purged well for a total of 8 minutes. Purge ended at 1612. Water was clear. Left site at 1615. Arrived on site at 1020. Depth to water was 72.50.
Samples bailed and collected at 1024. Left site at 1027.
Signature of Field Technician
..:3c.v~/ (,"L,£,>'""'!:::"t
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 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 15:06
Sample Date & Time 3/17/2020 10:05 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 15
Purging Method 2 Casings Previous Well Sampled TW4-14
Casing Volume (gal) 14.36
Calculated Casing Volumes Purge Duration (min) 2.61
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) 77.60
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 15:08 16.50 3852 6.65 15.40 423 24.0 5.0
3/17/2020 10:04 3961 6.76 13.48 Before
3/17/2020 10:06 3960 6.75 13.50 After
[Ve>lume o_! water purge<!_(gals) 16.50
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.50
[f:inal Depth to Water (feet) 97.02 Number of casing Volumes 1.14
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 HOPE 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 and 30 seconds. Purge ended at 1508. Water was a little murky. Left site at 1511 . Arrived on site at 1001. Depth to
water was 77.92. Samples bailed and collected at 1005. Left site at 1007.
Signature of Field Technician
~~~
Groundwater Discharge Permit e-.-~'!" . ,...--.. I : .·' }.-'
·-----·{ /i -~ .-,r~~ . ~l i.' ,l
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-07 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-07 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/202013:56
Sample Date & Time 3/18/2020 6:00 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 13
Purging Method 2 Casings Previous Well Sampled TW4-33
Casing Volume (gal) 24.89
Calculated Casing Volumes Purge Duration (min) 4.52
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) 82.87
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox(mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 14:00 49.50 1656 7.09 14.91 355 38.0 33.0
3/18/2020 5:59 1205 7.22 13.50 Before
3/18/2020 6:01 1253 7.22 13.56 After
!Volume of _!later p1.1rged (_g_als) 49.50
Pumpin_g_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.50 I Final Depth to Water (feet) 118.93 Number of casing Volumes 1.98
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?
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 1353. Purge began at 1356. Purged well for a total of 4 minutes and 30 seconds. Purged well-dry. Purge ended at 1401. Water was a little murky. Left site at 1403. Arrived on site
at 0557. Depth to water was 86.95. Same_les bailed and collected at 0600. Left site at 0602.
Signature of Field Technician
-2)~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e·r-·t~ ·--·· /{ '~~~ ... ·. -~ I ;~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-08 Sampling_Prog_ram Chloroform Monitoring
Field Sample ID TW4-08 03182020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 3/17/2020 12:21
Sample Date & Time 3/18/2020 5:32 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 13
Purging Method 2 Casings Previous Well Sampled TW4-18
Casing Volume (gal) 26.28
Calculated Casing Volumes Purge Duration (min) 4.77
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) 85.95
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17/2020 12:24 33.00 4910 6.57 14.99 510 1.1 1.1
3/17/2020 12:25 44.00 4912 6.70 15.01 504 1.5 1.0
3/17/2020 12:26 55.00 4908 6.76 15.02 499 1.6 1.1
3/17/2020 12:27 66.00 4911 6.80 15.03 494 1.6 1.1
Pumping Rate Calculations
jvolume of water purged (gals) 66.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 6.00
~inal Depth t.5> Water (fee!) 121.67 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?
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 1218. Purge began at 1221. Purged well for a total of 6 minutes. Purge ended at 1227. Water was clear. Left site at 1230. Arrived on site at 0529. Depth to water was 86.04.
Samples bailed and collected at 0532. Left site at 0534.
Signature of Field Technician
2)~
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 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/202011:11
Sample Date & Time 3/18/2020 5:08 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 11
Purging Method 2 Casings Previous Well Sampled TW4-09R
Casing Volume (gal) 33.87
Calculated Casing Volumes Purge Duration (min) 6.15
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) 68.22
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 11:16 55.00 2466 6.70 14.96 468 19.4 2.5
3/17/202011:17 66.00 2452 6.71 14.96 460 21.5 2.7
3/17/2020 11:18 77.00 2449 6.77 14.97 453 21.6 2.6
3/17/202011:19 88.00 2446 6.81 14.96 445 22.0 2.5
Pumping Rate Calculations
jvolume of water purg~Jgals) 88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00 I Final Depth to Water (feet) 77.90 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 1108. Purge began at 1111. Purged well for a total of 8 minutes. Purge ended at 1119. Water was a little murky. Left site at 1122. Arrived on site at 0503. Depth to water was
68.18. Samples bailed and collected at 0508. Left site at 0510.
Signature of Field Technician
-2>~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-09R Sampling Program
Field Sample ID TW4-09R 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/17/2020 11:00 [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 Casin9_ Diamete_r_(}
Specific Conductance () Depth to Water Before_Purgin9 (ft)
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 10:59 133.00 9.8 5.65 12.20 457 0 34.0
Pumping Rate Calculations
[volume of water purged () Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
[Final Depth to W~~~(feet) Number of casing Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory
AWSL
Analytical_§~mples 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 40ml VOA u HCI (pH<2), 4 Deg C y
Comments:
Signature of Field Technician
.:3=~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
--e·· .,,.-. F-=·.. ;-. h •
~· ,•i 7 ::· . .-~.-=it.eE7S
·-J -f
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-10 Sampling Program Chloroform Monitoring
Field Sample ID TW4-10 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/2020 14:54
Sample Date & Time 3/18/2020 6:25 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-29
Casing Volume (gal) 29.82
Calculated Casing Volumes Purge Duration (min) 5.42
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) 67.53
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 14:58 40.33 2810 6.25 15.04 515 20.4 36.2
3/18/2020 6:24 2716 6.89 13.30 Before
3/18/2020 6:26 2738 6.87 13.38 After
Pumping Rate Calculations
[volume of wate!_eurged (gals! 40.33 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.66
[ Final Depth to Water (f~t} 111.08 Number of casing Volumes 1.35
Volume, if well evacuated to dryness (gals) 40.33
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 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 1451. Purge began at 1454. Purged well for -a total of 3 minutes and 40 seconds. Purged well dry. Purge ended at 1458. Water was mostly clear. Left site at 1501 . Arrived on site
at 0621 . Depth to water was 67.55. Samples bailed and collected at 0625. Left site at 0627.
Signature of Field Technician
~=~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-11 Sampling Program Chloroform Monitoring
Field Sample ID TW4-11 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:49
Sample Date & Time 2/19/2020 12:50 js~mpler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 8
Purging Method 2 Casings Previous Well Sampled MW-26
Casing Volume (gal) 11.28
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) 85.12
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 12:49 3682 7.01 14.35 275 0 68.4
Pumping_ Rate Calculations
jvolume of wate~ !)_Urged O Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
jFin_al Depth to Water (feet) 100.01 Number of casing Volumes
Volume, if well evacuated to dryness O 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: I Arrived on site at 1245. Samples collected at 1250. Water was clear. Left site at 1252.
Signature of Field Technician
~t.t./VV~fC'T~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e ·~· .7 .· r--. .· .~ ' ,'• "-----t ,''-'--ii,~ .:,o·~~Y~T:r:S
..,.. J •'
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-12 Sampling Program Chloroform Monitoring
Field Sample ID TW4-12 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 10:22
Sample Date & Time 3/17/2020 8:45 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled TW4-32
Casing Volume (gal) 31.78
Calculated Casing Volumes Purge Duration (min) 5.77
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 54.52
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 10:26 41.25 1715 6.77 14.80 449 3.0 21.4
3/17/2020 8:44 1391 7.28 13.29 Before
3/17/2020 8:46 1408 7.25 13.33 After
[Volum~ of water purgf!__d_(gals) 41.25
Pumei_11_9 Rate Calculations
Flow Rate (0 = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.75
jFinal Depth to Water (feet) 100.95 Number of casing Volumes 1.29
Volume, if well evacuated to dryness (gals) 41.25
Name of Certified Analytical La_l)oratory
AWSL
Anal~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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1018. Purge began at 1022. Purged well for a total of 3 minutes and 45 seconds. Purged well dry. Purge ended at 1026. Water was clear. Left site at 1029. Arrived on site at 0842.
Deeth to water was 54.40. Samples bailed and collected at 0845. Left site at 0847.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
..-:::aL.::S> Field Data Worksheet For Groundwater
Location ID TW4-13 Sampling Program Chloroform Monitoring
Field Sample ID TW4-13 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 10:55
Sample Date & Time 3/17/2020 8:54 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 10
Purging Method 2 Casings Previous Well Sampled TW4-12
Casing Volume (gal) 32.55
Calculated Casing Volumes Purge Duration (min) 5.91
pH Buffer 7.0 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) 55.85
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox(mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 10:59 44.00 2090 6.70 14.86 486 0 61.9
3/17/2020 8:53 1679 7.34 13.18 Before
3/17/2020 8:55 1685 7.34 13.30 After
§1u_111e of water purg_ed (gals)
Pumping Rate Calculations
44.00 Flow Rate (Q = S/60} (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.00
[Fin~~ Depth to Water (feet) 103.79 Number of casing Volumes 1.35
Volume, if well evacuated to dryness (gals) 44.00
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 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 i 052. Purge began at 1055. Purged well for a total of 4 minutes. Purged well dry. Purge ended at 1059-:-Water was clear. Left site at 1103. Arrived on site al 0850. Depth to
water was 55.75. Samples bailed and collected at 0854. Left site at 0856.
Groundwater Discharge Permit
----~·' ::;::::c,-::;... I· ,---' s /--~~. ' ~y~-:z ··:~ ..
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-14 Sampling Program Chloroform Monitoring
Field Sample ID TW4-14 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 14:37
Sample Date & Time 3/17/2020 9:55 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 15
Purging Method 2 Casings Previous Well Sampled TW4-38
Casing Volume (gal) 11.46
Calculated Casing Volumes Purge Duration (min) 2.08
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) 77.55
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) Oxygen{%) Before/After
3/16/2020 14:38 11.00 5356 6.50 15.40 406 29.0 86.0
3/17/2020 9:54 5243 6.84 12.98 Before
3/17/2020 9:56 5245 6.82 13.05 After
Pumping Rate Calculations -
[volume o_!_vvater 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) 93.05 Number of casi ng Volumes 0.95
Volume, if well evacuated to dryness (gals) 11.00
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1434. Purge began at 1437. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1438. Water was a little murky. Left site at 1441 . Arrived on site at 0952. Depth to
water was 77.59. Samples bailed and collected at 0955. Left site at 0957.
Signature of Field Technician
-.:.3~-M-e
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan .,_......._e .··~-_ .. ~ I -~
_ .. ~i ..,·· "~Y~S"
~f ~ I
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-26 Sampling Program Chloroform Monitoring
Field Sample ID MW-26 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:38
Sample Date & Time 2/19/2020 12:40 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 8
Purging Method 2 Casings Previous Well Sampled TW4-39
Casing Volume (gal) 30.91
Calculated Casing Volumes Purge Duration ()
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) 73.98
Conductivity Dissolved
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/19/2020 12:39 3426 7.01 16.18 316 0 21.2
[volume of water purged ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 10.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 80.45 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytj~al 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 1235. Samples collected at 1240. Water was clear. Left site at 1242.
Signature of Field Technician
~ -~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-16 Sampling_ Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-16 03182020 Sameling_ Event 2020 Ql Chloroform
Purge Date & Time 3/17/2020 12:50
Sample Date & Time 3/18/2020 5:40 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 13
Purging Method 2 Casings Previous Well Sampled TW4-08
Casing Volume (gal) 49.37
Calculated Casing Volumes Purge Duration (min) 8.97
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) 71.98
Conductivity Dissolved Oxygen
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) {%) Before/After
3/17/2020 12:57 77.00 3703 6.73 14.85 435 14.5 2.7
3/17/2020 12:58 88.00 3641 6.84 14.85 428 14.2 2.2
3/17/2020 12:59 99.00 3643 6.90 . 14.84 422 14.0 2.3
3/17/2020 13:00 110.00 3626 6.94 14.86 401 14.3 2.4
§1u_!"!_Of water purged (gals) 110.00
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 10.00
!Final Depth to Water {feet) 140.45 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-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 1247. Purge began at 1250. Purged well for a total of 10 minutes. Purge ended at 1300. Water was a little murky. Left site at 1303. Arrived on site at 0536. Depth to water was
72.10. Samples bailed and collected at 0540. Left site at 0542.
Signature of Field Technician
-=:.)~-rrv~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-32 Sampling Program Chloroform Monitoring
Field Sample ID MW-32 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/18/2020 5:00
Sample Date & Time 3/18/2020 10:05 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 2
Purging Method 2 Casings Previous Well Sampled TW4-26
Casing Volume (gal) 32.61
Calculated Casing Volumes Purge Duration (min) 300.62
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) 80.65
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/18/2020 10:02 65.53 3671 6.54 13.85 280 16.5 9.0
3/18/2020 10:03 65.75 3672 6.60 14.00 266 17.0 8.0
3/18/2020 10:04 65.96 3677 6.62 14.01 256 18.0 6.8
3/18/2020 10:05 66.18 3682 6.65 14.00 252 18.0 6.7
Pumping Rate Calculations
[volume of water purged (gals) 66.18 Flow Rate (Q == S/60) (gal/min) .217
Tlme to evacuate 2 Casing Volumes (min) 305.00
~inal Depth t_o Water_(feet) 86.73 Number of casing Volumes 2.00
Volume, if well evacuated to dryness {) 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sam_eles 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 0455. Purge bega~ at 0500. Purged well for a total of 305 minutes. Purge ended and samples collected at 1005. Water was clear. Left site at 1015.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-18 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-18 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/202011:45
Sample Date & Time 3/18/2020 5:18 jsampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-09
Casing Volume (gal) 42.84
Calculated Casing Volumes Purge Duration (min) 7.79
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) 71.28
Conductivity DISSOIVea
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox(mV) Turbidity (NTU) Oxygen{%) Before/After
3/17/202011:51 66.00 1994 6.46 15.47 469 11.7 10.7
3/17/2020 11:52 77.00 1971 6.60 15.47 466 10.9 11.0
3/17/2020 11:53 88.00 1941 6.68 15.47 463 11.1 11.0
3/17/2020 11:54 99.00 1910 6.69 15.47 461 11.2 11.2
jvolume of water purged (gals) 99.00
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 9.00 I Final Depth to Water (feet) 71.62 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () D
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 HOPE u H2S04 (pH<2}, 4 Deg C y
Comments:
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-19 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TV\/4-19 02192020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 14:14
Sample Date & Time 2/19/2020 14:15 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled TW4-40
Casing Volume (gal) 35.62
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) 72.31
Conductivity Dissolved
Date/Time Gallons Purged {umhos/cm) pH (pH Units) Temp {deg C) Redox (mV) Turbidity {NTU) Oxygen{%) Before/After
2/19/2020 14:14 3166 6.82 15.42 359 0 39.2
[volume of water purged ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes () I Fi_nal Depth to Water (fe~!) 75.82 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AVVSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y VI/ATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y VI/ATER 1 500-ml Poly u None N
Nitrate/nitrite as N y VI/ATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on~ite at_1_i 11. Samples collected at 1415. V\/ater was clear. Left site at 1417.
Signature of Field Technician
~u.,~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e -~-. ·---t r -, ~ . '
..__• 7 • _ .-__ · __ ,.~Y~:S
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-20 Sampling Program Chloroform Monitoring
Field Sample ID TW4-20 02192020 Sam.e_ling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:23
Sample Date & Time 2/19/2020 12:25 jsami>_ler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 8
Purging Method 2 Casings Previous Well Sampled TW4-37
Casing Volume (gal) 21.09
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) 73.59
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 12:24 4377 6.95 15.51 357 0 39.3
[volume ~_water purged 11
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 4.5
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 77.98 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-mLHDPE u H2S04 (pH<2), 4 Deg C y
Comments:
ITrrived on site at 1220. Samples collected at 1225. Water was clear. Left site at 1227.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e-.--~,·----" _.-y .· . r
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~'.
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-21 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-21 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 9:28
Sample Date & Time 2/19/2020 9:30 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 2
Purging Method 2 Casings Previous Well Sampled TW4-60
Casing Volume (gal) 25.76
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .o 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) 79.35
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 9:30 2761 6.80 15.90 314 79.2 88.00
Pumping Rate Calculations
[volume of water purgedj}_ Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water {feet) 85.45 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: I Arrived ()_n site at 0926. Samples collected at 0930. Water was murky. Left site at 0935.
Signature of Field Technician
-=3=~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID 1W4-22 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID T\N4-22 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:07
Sample Date & Time 2/19/2020 12:08 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled T\N4-24
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .O 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) 63.98
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 12:08 5222 7.14 15.20 316 1.6 95.0
Pumping Rate Calculations
!volume of water purged() Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) 102.46 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Anal\f!ical Laboratory
AWSL
Analytical Sameles Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-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: I Arrived on site at 1205. Samples collected at 1208. \Nater was clear. Left site at 1211 .
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-23 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-23 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 13:28
Sample Date & Time 3/17/2020 9:37 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 14
Purging Method 2 Casings Previous Well Sampled TW4-35
Casing Volume (gal) 27.48
Calculated Casing Volumes Purge Duration (min) 4.99
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) 74.31
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/2020 13:32 44.00 3492 6.88 14.60 310 79.0 105.0
3/16/2020 13:33 55.00 3479 6.92 14.61 290 77.0 105.1
3/16/2020 13:34 66.00 3481 6.92 14.61 280 78.0 105.2
3/16/2020 13:35 77.00 3481 6.93 14.62 274 78.6 105.1
Pumping Rate Calculations
jvolume of wat~purged (gals) 77.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 7.00
[ Final Depth to Water (f~t) 93.89 Number of casing Volumes 2.00
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratol)'_
AWSL
Anal}'!ical 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:
Arnved on site at 1325. Purge began at 1328. Purged well for a total of 7 minutes. Purge ended at 1335. Water had an orange coloration but was clearing as purge went on. Left site at 1338.
Arrived on site at 0934. Depth to water was 74.22. Sam1;1les bailed and collected at 0937. Left site at 0939.
Signature of Field Technician
-:3~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e.· ·-=:·'' . r , .
.... /{ . .. r===--,=:,c eez: s ""'---'"":' ' ... ' ,. ~,. .
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White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-24 Sampling Program Chloroform Monitoring
Field Sample ID TW4-24 02192020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 11:57
Sample Date & Time 2/19/2020 12:00 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled TW4-25
Casing Volume (gal) 30.95
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 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} 67.39
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 12:00 6512 6.88 14.56 334 3.3 18.4
Pumping Rate Calculations
[voluri,_e of water p_1.1_rged () Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Wat~r (feet) 75.50 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analyt_ical Laboratory
AWSL
Anal~ical Samples 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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 1155. Samples collected at 1200. Water was clear. Left site at 1203.
Signature of Field Technician
Groundwater Discharge Permit --~· --· -----s -· ~.-r -.•
• ;/~ ~,~· .,-~Y""'l:esr:S
}'/ __ .
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-25 Sampling F>_rog_ram Chloroform Monitoring
Field Sample ID TW4-25 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 9:45
Sample Date & Time 2/19/2020 9:46 [sa111_eler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C 3
Purging Method 2 Casings Previous Well Sampled TW4-21
Casing Volume (gal) 40.76
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 74.28
Conductivity Dissolved Oxygen
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) (%) Before/After
2/19/2020 9:46 2495 7.04 14.84 266 0 50.0
PumpJng_ Rate Calculations -
Flow Rate (Q = S/60) (gal/min) 10.00 [volume of water Pl!l'ged ()
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 92.12 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?
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 0942. Samples collected at 0946. Water was clear. Left site at 0951 .
Signature of Field Technician
-:3~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~~,~· .~ _ _/ ~·.·· ,Vi . . ' .• ~er:::r s '-----8-:' ,,.. ,' / ~
'/ [_ -
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-26 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-26 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/2020 15:23
Sample Date & Time 3/18/2020 6:35 !Sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-10
Casing Volume (gal) 10.23
Calculated Casing Volumes Purge Duration (min) 1.86
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) 72.02
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 15:24 11.00 4545 6.68 15.55 440 6.4 86.0
3/18/2020 6:34 4670 7.06 13.20 Before
3/18/2020 6:36 4673 7.08 13.23 After
Pumping Rate Calculations
jVolume ~water purged_Jgals) 11.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
jFinal Depth to Water (feet) 85.20 Number of casing Volumes 1.07
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical l..aboratory
AWSL
Anal~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:
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 03172020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 15:39
Sample Date & Time 3/17/2020 10:14 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 15
Purging Method 2 Casings Previous Well Sampled TW4-06
Casing Volume (gal) 11.08
Calculated Casing Volumes Purge Duration (min) 2.01
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) 78.77
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 15:40 11.00 5140 6.48 15.49 427 16.7 11.6
3/17/2020 10:13 4956 6.87 13.73 Before
3/17/202010:15 4969 6.86 13.80 After
[volume of water pu_i:g_ed (gals) 11.00
Pumping_ Rate Calculations
Flow Rate {Q = S/60) (gal/min) 11.00
nme to evacuate 2 Casing Volumes (min) 1.00 I Final Depth to Water (feet) 93.22 Number of casing Volumes 0.99
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1535. Purge began at 1539. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1540. Water was mostly clear. Left site at 1543. Arrived on site at 1010. Depth to
water was 79.11 . Samples bailed and collected at 1014. Left site at 1016.
Signature of Field Technician
~~fb"'I~
Groundwater Discharge Permit ---~-W:.::I. --.,,Y r --
...____...., ~/ / ::_.. / .EJO.az.43G'Y~ ft7Z S
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-28 Sampling Program Chloroform Monitoring
Field Sample ID TW4-28 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 9:07
Sample Date & Time 3/17/2020 8:32 !sampler TH/OL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-42
Casing Volume (gal) 39.77
Calculated Casing Volumes Purge Duration (min) 7.23
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) 47.57
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/2020 9:11 47.66 1505 6.96 14.66 508 8.4 64.0
3/17/2020 8:31 1590 7.29 13.50 Before
3/17/2020 8:33 1597 7.27 13.61 After
!volume of water purged (g~ls)
Pumpin9_ Rate Calculations
47.66 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.33 I Final Depth to Water (fe~_t) 106.59 Number of casing Volumes 1.19
Volume, if well evacuated to dryness (gals) 47.66
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 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 H2504 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0904. Purge began at 0907. Purged well for a total of 4 minutes and 20 seconds. Purge ended at 0911 . Water was clear. Purged well dry. Left site at 0914. Arrived on site at
0828. Depth to water was 47.50. Samples bailed and collected at 0832. Left site at 0834.
Signature of Field Technician
~u./",JV~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-29 Sampling P_ro9ram Chloroform Monitoring
Field Sample ID TW4-29 03182020 Sameling Event 2020 Ql Chloroform
Purge Date & Time 3/17/2020 14:27
Sample Date & Time 3/18/2020 6:12 [sameler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-07
Casing Volume (gal) 11.38
Calculated Casing Volumes Purge Duration (min) 2.06
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) 77.05
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 14:28 11.00 4046 6.50 15.23 464 5.6 71.0
3/18/2020 6:11 3950 7.13 13.48 Before
3/18/2020 6:13 3959 7.13 13.56 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 (min) 1.00 I Final Dep_!_h to Water (feetJ 92.38 Number of casing Volumes 0.96
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1424. Purge began at 1427. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1428. Water was clear. Left site at 1430. Arrived on site at 0609. Depth to water
was 77.05. Samples bailed and collected at 0612. Left site at 0615.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-30 Sameling Program Chloroform Monitoring
Field Sample ID TW4-30 03172020 Sameling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 16:37
Sample Date & Time 3/17/2020 10:38 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 14
Purging Method 2 Casings Previous Well Sampled TW4-05
Casing Volume (gal) 12.21
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) 74.78
conduct1v1ty Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox(mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 16:38 14.66 4620 5.74 15.30 450 32.1 55.0
3/17/2020 10:37 3578 6.05 13.48 Before
3/17/2020 10:39 3621 6.05 13.50 After
Pumping Rate Calculations
IYolume of_water purged (gals) 14.66 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.33
!Final Depth t_o_W_!lter Jfeet) 91.20 Number of casing Volumes 1.20
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Anal'{t_ical Laboratory
AWSL
Analytical Sa"!eles 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 1634. Purge began at 1637. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 1638. Water was a little murky. Left site at 1641 . Arrived on site
at 1034. Depth to water was 74.85. Samp_les bailed and collected at 1038. Left site at 1040.
Signature of Field Technician
~"-~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~
-~--\-· ,----.. _----.,-~ ,· ,. ~-:rs ~ ·r -~ . . ~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-31 Sampling Program Chloroform Monitoring
Field Sample ID TW4-31 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 12:02
Sample Date & Time 3/17/2020 9:12 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-36
Casing Volume (gal) 20.26
Calculated Casing Volumes Purge Duration (min) 3.68
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) 76.45
Conductivity Dissolved
Date/Time Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp(deg C) Redox(mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 12:04 22.00 3990 6.65 15.20 398 21.5 30.0
3/17/2020 9:11 4053 7.14 13.44 Before
3/17/2020 9:13 4040 7.10 13.52 After
Pumping Rate Calculations
!volume of water purged (gal!.) 22.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 2.00
[Final Depth _to Wate!_(feet) 105.11 Number of casing Volumes 1.08
Volume, if well evacuated to dryness (gals) 22.00
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 1158. Purge began at 1202. Purged well for a total of 2 minutes. Purged well dry. Purge ended at 1204. Water was a little murky. Left site at 1207.
Arrived on site at 0908. Depth to water was 76.40. S_amples bailed and collected at 0912. Left site at 0914.
Signature of Field Technician
-=:=3~~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~
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. :.-··-
-~ .·· I .: . ,.. . . '·' .Er s81G'Y~-:Z: s
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White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-32 Sampling Program Chloroform Monitoring
Field Sample ID TW4-32 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 9:43
Sample Date & Time 3/17/2020 8:39 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled TW4-28
Casing Volume (gal) 38.81
Calculated Casing Volumes Purge Duration (min) 7.05
pH Buffer 7.0 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) 55.20
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/2020 9:48 55.00 6450 4.37 14.81 493 8.2 1.1
3/16/2020 9:49 66.00 6467 4.37 14.82 495 8.0 1.2
3/16/2020 9:50 77.00 6469 4.36 14.84 496 7.8 1.1
3/16/2020 9:51 88.00 6473 4.37 14.83 496 7.7 1.2
[Volume of water purged (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 Depth to Water (feet) 84.60 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratol'}'
AWSL
Analytical Safl!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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0940. Purge began at 0943. Purged well for a total of 8 minutes. Purge ended at 0951 . Water was mostly clear. Pump and hose had salt like particles on them when pump was
pulled from the well. left site at 0954. Arrived on site at 0836. Depth to wa_t_er was 54.91 . Samples bailed and collected at 0839. Left site at 0841 .
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan E!. ~ ~.-~-,' ..._, ___ ... ,..·· r ·,-· ~ .· I
. /·· .' ~y~--z:s
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-33 Same_ling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-33 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/17/202013:30
Sample Date & Time 3/18/2020 5:50 lsameler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 13
Purging Method 2 Casings Previous Well Sampled TW4-16
Casing Volume (gal) 6.25
Calculated Casing Volumes Purge Duration (min) 1.13
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) 76.65
Conductivity Dissolved
Date/Time Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/2020 13:31 5.50 4060 6.15 15.67 462 8.1 59.0
3/18/2020 5:49 4211 6.89 13.89 Before
3/18/2020 5:51 4208 6.90 13.98 After
Pumping Rate Calculations
IYolume of water purged (gals) 5.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.50
[Final Depth _!_o Water (feet) 84.05 Number of casing Volumes 0.88
Volume, if well evacuated to dryness (gals) 5.50
Name of Certified Analytical Laboratory
AWSL
Anal~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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1326. Purge began at 1330. Purged well for a total of 30 seconds. Purged well dry. Purge ended at 1331. Water was mostly clear. Left site at 1334. Arrived on site at 0546. Depth
to water was 76.92. Samples bailed and collected at 0550. Left site at 0552.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
;..oa~.::s:. Field Data Worksheet For Groundwater
Location ID TW4-34 Sampling Program Chloroform Monitoring
Field Sample ID T\N4-34 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 12:33
Sample Date & Time 3/17/2020 9:20 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 13
Purging Method 2 Casings Previous Well Sampled TW4-31
Casing Volume (gal) 13.24
Calculated Casing Volumes Purge Duration (min) 2.40
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 75.45
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 12:34 16.50 3533 6.72 15.15 403 13.2 42.S
3/17/2020 9:19 3453 7.25 13.45 Before
3/17/2020 9:21 3464 7.21 13.53 After
[volume of water purged (gals) 16.50
Pumpin_g 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) 93.42 Number of casing Volumes 1.24
Volume, if well evacuated to dryness (gals) 16.50
Name of Certified Analytical Laboratory
A\NSL
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1229. Purge began at 1233. Purged well for a total of 1 minute and 30 seconds. Purged well dry. Purge ended and 1234. \Nater was mostly clear. Left site at 1237. Arrived on
site at 0916. Depth to water was 75.36. Samples bailed and collected at 0920. Left site at 0922.
Signature of Field Technician
-:::3~
Location ID
Field Sample ID
Purge Date & Time
Sample Date & Time
Purging Equipment
Pump Type
Purging Method
Casing Volume (gal)
Calculated Casing Volumes Purge Duration (min)
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance (micromhos)
Date/Time Gallons Purged (gal)
3/16/2020 13:02
3/17/2020 9:27
3/17/2020 9:29
[volume of water purged (gals)
[Final DeJ,!!h to Water (fe~)
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Type of Sample/Analysis
voes-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
8.25
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-35 Sampling Program Chloroform Monitoring
TW4-35 03172020 Sampling Event 2020 Ql Chloroform
3/16/2020 13:02
3/17/2020 9:28 [sampler TH/DL
Pump Weather Conditions Sunny
Grundfos External Ambient Temperature (C) 14
2 Casings Previous Well Sampled TW4-34
7.58
1.37
7.0 Well Depth (ft) 86.50
4.0 Well Casing Diameter (in) 4
1000 Depth to Water Before Purging (ft) 74.89
Conductivity Dissolved
(umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
4353 6.56 15.50 377 8.1 44.0
4276 6.92 13.58 Before
4287 6.90 13.65 Aher
Pumping_ Rate Calculations
8.25 Flow Rate (Q = S/60) {gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.75
84.55 Number of casing Volumes 1.06
Volume, if well evacuated to dryness (gals) 8.25
Sample Container Preservative
Collected? Matrix Number Type Sample Filtered? Type Added?
y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
y WATER 1 500-ml Poly u None N
y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Arrived on site at 1258. Purge began at 1302. Purged well for a total of 45 seconds. Purged well dry. Purge ended at 1303. Water was mostly clear. Left site at 1305. Arrived on site at 0925. Depth
to water was 74.81 . Samples bailed and collected at 0928. Left site at 0930.
Signature of Field Technician
--=:3cu~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~'F-::·' ~--,r ··-. ., ...__._, •. · /4 r .·· ~/· ~y,=:c.-::zs
. :; -
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-36 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-36 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 11:31
Sample Date & Time 3/17/2020 9:03 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 11
Purging Method 2 Casings Previous Well Sampled TW4-13
Casing Volume (gal) 27.36
Calculated Casing Volumes Purge Duration (min) 4.97
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) 57.50
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 11:34 33.00 2432 6.88 15.20 250 70.3 7.4
3/17/2020 9:02 2388 7.22 12.86 Before
3/17/2020 9:04 2391 7.20 12.97 After
!Volume of wa_ter purged_(g_als) 33.00
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.00 I Final Depth to Water (feet) 97.63 Number of casing Volumes 1.20
Volume, if well evacuated to dryness (gals) 33.00
Name of Certified Analytical l..aboratory
AWSL
Analy_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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1128. Purge began at 1131 . Purged well for a total of 3 minutes. Purged well dry. Purge ended at 1134. Water was murky. Left site at 1137. Arrived on site at 0859. Depth to
water was 58.13. Samples bailed and collected at 0903. Left site at 0905.
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 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:15
Sample Date & Time 2/19/2020 12:16 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled TW4-22
Casing Volume (gal) 29.34
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) 68.78
Conductivity Dissolved
Date/fime Gallons Purged (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/19/2020 12:16 4154 7.06 16.05 323 0 72.1
Pumping Rate Calculations
[volume of water purged O Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes()
(final Depth to Water (feet} 80.24 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: I Arrived on site at 1213. Samples collected at 1216. Water was clear. Left site at 1219.
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e ·~--·· T -, t ;,---
<it'.. ~/ ~.[ .· .. ··' ' •
'. . -~..r .. ·· ,,·· ~~ s-
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-38 Sampling Program Chloroform Monitoring
Field Sample ID TW4-38 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 14:04
Sample Date & Time 3/17/2020 9 :45 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 15
Purging Method 2 Casings Previous Well Sampled TW4-23
Casing Volume (gal) 36.22
Calculated Casing Volumes Purge Duration (min) 6.58
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 58.45
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 14:09 55.00 1782 6.67 14.74 480 22.3 51.1
3/16/2020 14:10 66.00 1775 6.72 14.69 472 23.0 51.0
3/16/2020 14:11 77.00 1778 6.75 14.75 470 23.0 51.0
3/16/2020 14:12 88.00 1780 6.76 14.73 469 23.2 50.8
jvolume of water purged (gals)
Pumping Rate Calculations
88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min} 8.00 I Final Depth to Water (feet) 108.70 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 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 8 minutes. Purge ended at 1412. Water was a little murky. Left site at 1415. Arrived on site at 0942. Depth to water was
58.54. Samples bailed and collected at 0945. Left site at 0947.
Signature of Field Technician
~~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-39 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-39 02192020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 12:31
Sample Date & Time 2/19/2020 12:32 [same_ler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C 8
Purging Method 2 Casings Previous Well Sampled TW4-20
Casing Volume (gal) 31.38
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 72.67
Conduct1v1ty DISSOived
Date/Time Gallons Purged (um hos/cm) pH (pH Units) Temp (deg C) Redox {mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 12:31 2317 7.06 15.35 335 0 50.0
Pumping_ Rate Calculations
[volume of water~_l'9_ed O Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 91.03 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 on site at 1228. Samples collected at 1232. Water was clear. Left site at 1234.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-40 Sam_e_ling Program Chloroform Monitoring
Field Sample ID TW4-40 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:49
Sample Date & Time 2/19/2020 13:50 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C 9
Purging Method 2 Casings Previous Well Sampled TW4-04
Casing Volume (gal) 8.56
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 72.88
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 13:49 4003 7.11 15.32 311 0 73.6
[volume of_ wat~purged O
Pumping_ Rate Calculations -
Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 78.56 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Anal~ical 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 1246. Samples collected at 1250. Water was clear. Left site at 1252.
Signature of Field Technician
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 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 13:32
Sample Date & Time 2/19/2020 13:34 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Continuous External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled TW4-0l
Casing Volume (gal) 32.68
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) 75.50
Conductivity Dissolved
Date/Time Gallons Purged (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/19/2020 13:33 2778 7.24 16.00 330 0 95.0
Pumping Rate Calculations
[volume of water purged() Flow Rate (Q = S/60) (gal/min) 6.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 79.52 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytic.11 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 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 H2504 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 1330. Samples collected at 1334. Water was clear. Left site at 1336.
Signature of Field Technician
-:3~-M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
A5ILS" Field Data Worksheet For Groundwater
Location ID TW4-42 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-42 03172020 Sampling_ Event 2020 Ql Chloroform
Purge Date & Time 3/16/2020 8:38
Sample Date & Time 3/17/2020 8:23 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 4
Purging Method 2 Casings Previous Well Sampled TW4-03
Casing Volume (gal) 11.64
Calculated Casing Volumes Purge Duration (min) 2.11
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 68.17
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2020 8:39 13.75 3467 6.67 14.16 515 1.5 99.2
3/17/2020 8:22 3321 7.26 13.18 Before
3/17/2020 8:24 3334 7.25 13.29 After
[volumeJ>f water purged (gals)
Pumping_ Rate Calculations
13.75 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.25
[Final Depth to Water (feet) 84.00 Number of casing Volumes 1.18
Volume, if well evacuated to dryness (gals) 13.75
Name of Certified Analytical Laboratory
AWSL
Analytical Samp_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 0834. Purge began at 0838. Purged well for a total of 1 minute and 15 seconds. Purge ended at 0839. Purged well dry. Water was clear. Left site at 0841. Arrived on site at
0819. Depth to water was 68.07. Samples bailed and collected at 0823. Left site at 0825.
Signature of Field Technician
~~'7/b~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e•c;..._ --w;:~--/ "---
~· -,( . · r ' -,..-~e;;;z;s ~. f'-','~
-~ .
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-60 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-60 02192020 Sampling Event 2020 Ql Chloroform
Purge Date & Time 2/19/2020 8:57
Sample Date & Time 2/19./2020 9:00 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C 2
Purging Method 2 Casings Previous Well Sampled N/A
Casing Volume O
Calculated Casing Volumes Purge Duration O
pH Buffer 7 .0 7.0 Well Depth (ft)
pH Buffer 4.0 4.0 Well Casing_ Diameter O
Specific Conductance (micromhos) 1000 Depth to Water Before Purging_(ft
Conductivity Dissolved
Datemme Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/19/2020 9:00 10.3 9.04 15.54 301 0.7 28.8
Pumping Rate Calculations
lvolull!_e of water purged O 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 dryness () 0
Name of Certified Analytical Laboratory_
AWSL
Analyt_ical 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:
Signature of Field Technician
Groundwater Discharge Permit ----eF-/ ~ . ~ I"--. . .
_.,..· .(l._·· --. ,' ~,=uwsp; :S
'. ,."'..,.~··· /
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-65 Sampling Program
Field Sample ID TW4-65 03172020 Sameling Event 2020 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/17/2020 8:05 [sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature O
Purging Method Previous Well Sampled
Casing Volume()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Depth (ft}
pH Buffer 4.0 Well Casing Diameter O
Specific Conductance O Depth to W~ter_ Before Purging_(ft)
Date/Time Gallons Purged Conductivity pH Temp Redox Turbidity Oxygen Before/After ]
Pumpin.51. Rate Calculations
[volume of water purged() Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (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?
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
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
Comments:
[ Duplicate of TW4-03
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Qualtty Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-70 Sampling Program
Field Sample ID TW4-70 03172020 Sampling Event 2020 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/17/2020 10:24 !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 (ftl
pH Buffer 4.0 Well Casing Diameter _O_
Specific Conductance () Depth to Water_Before Purging (ft)
Date/Time Gallons Purged Conductivity pH Temp Redox Turbidity Oxygen Before/After J
Pumping Rate Calculations
!Volume of water p~rged () Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) Number of casing Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory
AWSL
Analytical S~mples 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
VOCs-Chloroform y WATER 3 40mlVOA 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: I Duplicate of TW4-05
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-75 Sampling Program
Field Sample ID TW4-75 03182020 Sampling Event 2020 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/18/2020 10:05 [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 .o Well Depth (ft)
pH Buffer 4.0 Well Casing Diameter _Q
Specific Conductance () Depth to Water _Before Purging (ft)
Date!Time Gallons Purged Conductivity pH Temp Redox Turbidity Before/ After
!Volume of water purged ()
Pume_ing Rate Calculations
Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) Number of casing Volumes
Volume, if well evacuated to dryness()
Name of Certified Analytical Laboratory
AWSL
Anal~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
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Comments:
[ DU J)liCate of MW-32
Signature of Field Technician
~~
TabC
Weekly and Monthly Depth to Water Data
Weekly Inspection Form
Date 1-1a -t9
System Operational (If no note r rme W II e D th* C ts bl / 8DI ommen an~ l!'O ems corrective actions}
r>QJ::7 MW-4 Cl.c' ,,,, Flow I.I I) ._ No
Meter ~ ~ q t.. q q 1 .'14' v.. No
O'l~H MW-26 711.l r:' Flow JI. ":l Va No
Meter 1.1 "f o t. t:. n n ~ No
f I ~z; TW4-19 4/)(f Flow I~ ,I) 4is> No
Meter ~n, :1. 71'1~ .4 }a. No
/)q .:1 ~ TW4-20 fl 1./. (,. (,. Flow C t:. ...._ No
Meter ~ ~ J"_ q 'R n ~ s-*11 No
JI) 17 TW4-4 q :l "'~ Flow JI:, ..., I Mia No
Meter ~ ~ n ~ "I I tJ ~ No
l)Qfl I TWN-2 ~49 . .!l q Flow ;.;: ~ ._.,. No
Meter 1 .:J ,;~'1"19., )fa No
l,')qJr;' TW4-22 • .,_ •11) Flow JfJ t) V. No
Meter t: ~ ~ n 1 ~ .,_ .... No
/)Qr,-, TW4-24 "11'1 /1" Flow I "1 I.I la No
Meter , -:1.l./, ~t;"J/ "22 *' No
l)K~.;° TW4-25 1'1.911 Flow , .!l ~ Ve& No
Meter ~ ~ q ::2 -, q._ ,.,..Q' 'm9r-No
,nn ll:" TW4-1 "11:1 .,0 Flow 1n # ~ No
Meter ~, ~ -• e111~.1 ~ No
lnq~J TW4-2 1111. ~, Flow J -:::J 1-*-No
Meter ~4~"'-" 7 , ~ No
l)q4~ TW4-11 an.c:r Flow JI',. I,( ~ No
Meter c..~ n •o ~ .. No
/)~"lq TW4-21 -,r_ .1"2. Flow J-, tZ '*9g. No
Meter :J/7,t /'Jfl~O nq ~No
nt1~1 TW4-37 7~-Hr{ Flow /11.IJ ~ No
Meter , ~,; ~ 7 ~ ct , 1 'Ye> No
,,Q'l\ \ TW4-39 "1C. 0 '1 Flow 1• a ~ No
Meter .r;q n ~ "'' n 'tr!lil9-No
,~~c TW4-40 1'1.11 Flow ,~ 0 -No
Meter ,. \ 4,; 7"(, II .. No
JIU!! TW4-41 -,4 Q ~ Flow s:. ,. ' ... No
Meter -:,r771 .. n 111 ' .... No
Operational Problems (Please list well number):
Corrective Action(s) Takep (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Monthly Depth Check Form
Date 1/ J?)/~02 0 Name Dee" L~/'110 1
Time Well Depth* Time Well Depth*
ag~a MW-4 :Z!.12.. 1!1.ll TWN-1 ,,...,s:
Q~s:1, TW4-1 ]£!10 QS2-'?a TWN-2 t;lf, t 3
Q9 &::t.. TW4-2 U i.,BI l~II TWN-3 1/J.9(;,
U 18 TW4-3 Ida .:z, l~ D. r. TWN-4 (,Q.lf f
'0. Q. g:_ TW4-4 tl,38 13!i'. I TWN-7 s,.,,
l:31a TW4-5 11J., l Z l~OQ TWN-18 i,,Lq2
a!ag TW4-6 lI,Z:l. 1J!:fi MW-27 s:, I,,,
l3Ql TW4-7 s.a. .1.a QS'.38 MW-30 z.,-, 9'4
lll2 TW4-8 S5,1'-Q831 MW-31 toB,l'f
13ilil TW4-9 t.il,l'
'313 TW4-10 fi.Z,5.l
1)91 !:I TW4-11 go,, a
I ~.c. TW4-12 £.~QJ
I j '2..3 TW4-13 r~.:s~ 1~3'2 TW4-28 114,9,a
l~l1 TW4-14 zz. £7. l~I~ TW4-29 14.73
(l9Qta TW4-15 9(.,!fg 1!=taJ TW4-30 ,-.,. "'
ll!lS TW4-16 Zl, f2 l~l21 TW4-31 1,. 2."I
asa.t, TW4-17 80., Ga ~ t!U3 TW4-32 S..,,,,
l~!:11 TW4-18 ll,A-5'. 13S'.~ TW4-33 '1C.,+4
IIQQ TW4-19 :,:a..~:&. l~U TW4-34 1':1,95
aa~~ TW4-20 1Q,-::t.Q 1~:UlGi TW4-35 7~,,o
DSQS TW4-21 80tQl t!t.2..1 TW4-36 ;1,13
aS!iS: TW4-22 ll-~2. QSS:.l TW4-37 :Ue, 4C,
08~1 TW4-23 23,91 133.1 TW4-38 sa. ,a.
a!33 TW4-24 ]2..!I& a9oa TW4-39 12..u
QSll TW4-25 j,S. ,:1 ,a13 TW4-40 11.a,4
·{29.Q'.?t TW4-26 711 l I Q95'.S TW4-41 7£90
ur• TW4-27 7R, 4,'( 13'19 TW4-42 41, ,.,
Comments: (Please note the well number for any comments}
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
"ilate 1-13 -;,2.o Name Deso f ,,,, Lymao
System Operational (If no note
Tl me W II D th* C t bl / ctl ti > e eo· ommen s an~ l:!ro ems corre veac ons
0~'11> MW-4 "'14. I~ Flow ~.« -No
Meter :J.H o,., /,,4~ -,.~ ._ No
n41tJ ,. MW-26 ~~-"'q Flow J 1 SI ¥811 No
Meter 41 ,., :::1 a R 1. ; ~ No
I I() n TW4-19 7.:1 Q~ Flow J 'ii I) W:O No
Meter '.] n~ n, !> < " ~No n,. r::"' TW4-20 '711.~~ Flow L."l.. '@:It No
Meter ~ .:1 7 ~ ; 1. -; o ~No
inn,; TW4-4 ~~ -:,,51 Flow I '"1 ,.., .,, -No
Meter t;.9 1 Lo\ 'i-' _q -No
""~'2 TWN-2 t:. Ir/. I~ Flow I t;i (J 'MB No
Meter , '.l ,; -, .:1_q ., ._ ~ ~ No
lt'J.Alt:° TW4-22 ~~-~1 Flow l 'X .tJ "-No
~ Meter ~ 1 o~ ~;. "'----No
11tl 1. :a. TW4-24 7j ,qt, Flow JC,.L/ )fa No
Meter , ~ If" fl i:: t:. n. ,., r:;-*8, No
l)~ I -i TW4-25 741 .r;I Flow ll''J I :l ~ No
Meter 3'-~ 13'B qS? ~No
/)(l'f., TW4-1 «I. "I 11 Flow / .:2 IA ,¥a, No
Meter 4 l t.f o on_ 1 -..No ---nq :i '!Ii TW4-2 ,,~.cu Flow :re;;-C. y ~ .. J.J,ty' -.. No
Meter ~.t:.l!.t:.11~. r;-¥a No
t'J4 '"' TW4-11 qo .ua Flow Jc;-_ /_ "-No
Meter ,;; I'.. n r; '3 i;-· ._ No
b•n• TW4-21 ~" Ot Flow 17. ~ v... No
Meter .:11Ht~.&f11.:2 GR ~ No
l.7R 'i" I TW4-37 -,1.. /_(. Flow /S,t!J *" No
Meter If. ,rg~ I I {) '-, No
nan ,, TW4-39 4~ :HI Flow I "1 '.i( ~ No
Meter z; ct"' £-t "1. , , .., No
1n1" TW4-40 ~, !2.G. Flow I 'i4 0 --No
Meter ~ ~ !1 r:; t) 4 .H'i e No
t14i:Sl TW4-41 -1e:'. an Flow 4 "' ~ No
Meter 2.1:; q ".l ,,_ q rm ~ 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 ,-ao-1,Q
Weekly Inspection Form
·Name U<M::~o?44.
System Operational (If no note
Ti me W II e D th* C ts bl / eo ommen anl£ ~ro ems corrective actions)
11,~ It( MW-4 era• ro Flow If .l) V. No
Meter ..:14', ~ ~, :2...-,, 1 .._ No
IOl'JQ MW-26 711.'19. Flow '"·" V. No
Meter .,~~,q llt-.fi ... No
, /"l~O TW4-19 "1/1 ~I) Flow JIIJ.h 'at-No
Meter ~ n:i. -,-, , ., f/1 -No
n1111c« TW4-20 '70. ~o. Flow .., . ,._ "9 No
Meter ~ ~-• ~ !I. c;" 11 ._ No
~
1nw1J TW4-4 Q'"1 n I Flow u. I. ... (Y.es_)No
Meter ~ tt :it:; r; -, • ,;-(Y~ No
n11=1n TWN-2 t..«.-,.., Flow /(,,. f .._ No
Meter, ..:1 ~q "7~•. ~ *87No
,,Q .. a;-TW4-22 7 I .&.If-Flow ,._,, -No
Meter~., .2_., 7tl. ~ -No
r
/JQ'.I.CI. TW4-24 "12.18 Flow If-,,/ .. No
Meter , ~ c:-c:l '2i.'7-q .1:1.,. .. No
nq1.,. TW4-25 «L Or./ Flow J ~ .,., ..._ No
Meter ~ 7 :1 "'1 q 11 c-"-No
JO '\n TW4-1 sri. t.l. Flow /!3 « ... No
Meter 1,,..-, Q~ D .. No
//)"l.~ TW4-2 JIJ •• I..~ Flow '"·o -No
Meter ~ t..., "1 • t. . ,;-'Ifs No
JIJII( TW4-11 .. n.,1-Flow 11: .• "-No
Meter ,!,.,i:: I b •. o ... No
,,Q~n TW4-21 -,":1.111 Flow JG • .2 -No
Meter ~nQ .,.., ~ ~. t.."1 ... No
mu::1 TW4-37 -,1... ~o Flow ,.,, '2 -No
Meter 1 ~,. ,:,. • l'1 • .., 'dlll No -
,n.na.1 TW4-39 Clo OC' Flow 1Q.O *9 No
Meter ,:ct« 11"' tJ. :1 .. No
1Dll< TW4-40 .,, .... Flow ••• /1 I ._ No
Meter ~ '11116/"1,, o fl .... No
I D"J t: TW4-41 '1C ,:: L Flow L/'J -No
Meter ~ ~-D < IJ :J... ti .., ._ 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 ,-a.7.30
Weekly Inspection Form
Name Peca c:;. ',c«nnn
System Operational Clf no note
Ti me W II e D th* eo· C t ommen s anll ~ro bl I I ems corrective act ons}
042."a MW-4 •1.._,_,_ Flow ~. '1.. .... No
Meter !l."' ::a n « ~ g. :::1.2. 'a No
n•~• MW-26 .,q_~ .. Flow Jl'J. (;. ~ No -Meter "l"l~"IOIJ.1 ~ No
II 1D TW4-19 -rLJ. Jil Flow ,.,_ -"-No
Meter .2_n "~ ,!:t t .. ., 1 .... No
n«.11 I TW4-20 Cl.II~~ Flow "'· ~ ~ No
Meter '1.2..ct 111 n. ,te, -No ,,.
TW4-4 Flow / \!a No ··--tlJ!. CII u: •. ~ .. ,..,
Meter 1 ... ~ 1 t. o§" 't/ ... ct -No
n•111 TWN-2 ~11-"'\ Flow }fl tJ ~ No -Meter 1 .:i , .. :, 2.:1 ~ a "ms No
b41~G TW4-22 ..,,. . ., Flow , •. D ~ No
Meter t..., "' ::J. ~ &f. G ~ No
n•~• TW4-24 a1.nL Flow JI'..~ \SI No
Meter ,~ t.. '"16/l'J'l.4t. \9 No
n•n1. TW4-25 -,L. :1.l Flow , n. '4 ~ No
Meter °''•&Ctr.QI ~ No
11411~1 TW4-1 10t. 10 Flow IZ. G. -No
Meter '-' 1 ,: .., 7 '1.11 'e No
t)q 1,: TW4-2 ,n-,. '111 Flow It.. I. )fD No
Meter ~ ,.11 '1111-r. ~ ~ No
/HIOC' TW4-11 a.,.011 Flow I~. I./. 'a No
Meter ~ t. '1 ~ q. t. 'm3 No
IJ7~f/l TW4-21 '1~. J .2 Flow Jr.. I.. ~ No /'
Meter .21 D IJ' ,,-,. u .:i.. 'ma No \_
n•"~ TW4-37 ., .. .,. Flow i•.n ~ No . Meter 11. t.Ql\-riQ. 3 ~ NO
IIJtlC' iJ TW4-39 7¥. ~,: Flow ·-------; ••·" 'CD No
Meter t:.n !J "I 111. I ~ No
t>4~tl TW4-40 ., 2.. •« Flow 19.. D ~ No
Meter ~!t•11~~.11 -No
Otlli/D TW4-41 7'?. ~a Flow /-.¥ ¥1=:g No
Meter ~/..1• 11."lq ~ No
Operational Problems (Please list well numb'er):
Corrective Action(s) Taken (Please list well n\Jmber): ----------------
\
I
* Depth is measured to the nearest Q_Q1 feet.
')!;)ate p, .. 3 ... Ul
'r
T" W II 1me e
in:i n MW-4
noc-, MW-26
J:J.J~ TW4-19
oq..,~ TW4-20
,n,.,11 TW4-4
!1Jd'1~ TWN-2
IUl..1 "7 TW4-22
oq11,. TW4-24
""' ,:re, TW4-25
10:!G. TW4-1 --..__
1011/ TW4-2
,on-r TW4-11
o« l!itJ TW4-21
nq~G""' TW4-37
l)ct.t;"f TW4-39
JIJl/0. TW4-40
111 '1.IJ TW4-41
Weekly Inspection Form
Name-::O~f:(~
System Operational (If no note
D th* C t bl I f r > eD· ommen s an¥ Rro ems correc 1ve ac ions
cal.# t.-, Flow ~-· __. No
Meter 2 4 ~ 'i4 « , o 'I :J. ... No
7~.~,;-Flow 1n. -:1 -No
Meter 1./1./7~ .2"?J. ~ .._. No
...,-z. a~ Flow I 8,0 ~ No
Meter ~n1..11t .. O'I.O ._ No
41&4 'I,'-Flow .,. . ,., .. No
Meter "3 ~ q a ::1 11 12 ~ VD No
'1q '"' Flow 17.n ~ No
Meter ~'J'/7~'1.~ YEl9 No
~q ~Q Flow 1 t:. if '*-' No
Meter ,-::1.,.'4.~q_q '* No
~1.12. Flow I "1~ ~ -No
Meter t."1l.'-191/ ~ -No
...,< '" Flow I/,. « ~ No
Meter , ~ 1t:n11/J.1~ ~ No
"'11.1./.U Flow JO I{ .... No
Meter ~« .r;--£1 q ~. ~ Q. *'-No
I /J I!. . :J. I} Flow I :::J.. I/ 'e No
Meter '31 ~ o 1./ ,. 1 "-' No
111.21 Flow , r: '.:2. ..._ \No
Meter '1/. 4 7 ~ 11. ~ ... No
~• -«o Flow '~-" ~ No
Meter ~ "--:i;,, q "" )fa No
'11 <~ Flow 1~.!I.. 'tm,. No
Meter :J , , ~ ~-IJt:J. !2 ~ ~ No
., t. "1.c;" Flow 1 ft. a -No
Meter H .. '7 "'/ /J 7 'I. ~ ma No
.,. ct f'J "' Flow I tjl () ._ No
Meter /.o~q&.1 :J.. ,q ._ No
..,, Cl~ Flow IQ() 'ta No
Meter 3&/ t:. ._, -=11. ~"" -No
g'"' . &.{ 1,. Flow I,, "' ... No
Meter :=> ,. ,:,. -::i. ~ 1, ,er .... 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 , ~ •a -a.,p Name Drrn vlyarea
System Operational Of no note
Ti W II D th* C ts bl / ti ti ) me e 8D ommen an:it: ~ro ems correc ve ac _ ons
11•17 MW-4 Qt..~'4 Flow I/, '.:I. ~No
Meter .:i." 1, '° -r ~ ~ 'I ,., .... No
na,-, MW-26 "7':l.ll"t Flow y /) .!l ...... No
Meter '-11./(l L4 ~,. ~ ._ No
/ 'l_ "l" TW4-19 L ... G,~ Flow lfJ.. t) ~ No
Meter -::, n 4" 111 ft..,. o ...... No
1)0/J II( TW4-20 "1« .. 11« Flow "'· 1. "81 No
Meter ~'\nt:. 7, .~ 7 Ya No
"""'" TW4-4 7q "~ Flow ,~ t. \a No
Meter ~«,: ~ 1.1.. , )am No
Of.'I l) TWN-2 1/4.nO Flow i«.o -No
Meter , .:i t. 7 ~ 'l _«. ~ )ma.-No
/)'}.~~ TW4-22 '111 .. ~ Flow IL.. 'I ... No
Meter /. '7 Q 'l -a n r: ¥sa No
n«u,. TW4-24 l'a I/. :J.. I Flow ,~ /J ~ No
Meter L .:1 «. '!I. -:a. ~ « 4 q ... No
/)Q 1../.J TW4-25 -,,3.. II/ Flow I I, I/ )la No
Meter 1 ll 2... IIR '1 .:1 • o 11 -No
17Q"l'3 TW4-1 , n<. ""t. Flow I,_, "1 .... No
Meter ~, , .. 7 ~ ,_, ~ ~ No
"q.,, l TW4-2 ,no. 1!'.J Flow I~.~ *9-No
Meter -:,. ., o ., If 11. "1 .. No
no~..-TW4-11 qo,O:J Flow //...,fl .._, No ~
Meter t;"-1'. ,;i:;. !l ..... No
n••• TW4-21 7• "n Flow ,., .4 ~ No
Meter .2..1 ':I. \ ~ 4J1 ~. 4;, 'wN No
n«<q. TW4-37 "7'1\. I.ti Flow I st. 11 .._ No
Meter 1 ~ ., q 1 "7 ii . t. ._ NO
nt:1no TW4-39 41 • l'"I Flow I -, :l .._ No
Meter l'.Dfll./-t,l •• 4. .... No
,n,11, TW4-40 -,~ 01 Flow JG.n ~ No
Meter 1~'1 ~ q di .:11 .. No
,,,,,:I} TW4-41 ..,,~ ~q Flow ,:. I,' ..... No
Meter 1.1.,., /-G -, . o ~ ~ 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
I , Date k/J-UJ
System Operational {If no note
Tl me W II D e eot h* C omments an)! ~roblems/corrective actlons}Jf'
I IJ II MW-4 ~, 11;"' Flow 1-/0 ~·No
Meter -:J.i.l4L/ 7 l 7. '12 Vs8 No
/}()f I:((') MW-26 t,q -~ ~ Flow ID LI "81 No
Meter 4 r; 1 4 , ~ ~ -. No
/:J(J(l TW4-19 7 J 2CI Flow I 9.. Ii "'-No
Meter ~ n,; "1 ~ '3 s? st Vat-No
/]q'2, ,_ TW4-20 7~ :2 ~ Flow L/. ~ .._. No
Meter ~ ~ 1 -:i. 4 7 tA -, v.. No
J/J'2t0 TW4-4 '-l.n ,.., Flow JIA. 1 ._ No
Meter r.. SI r... q (.,. , ::> ¥es> No
·:nqn'l TWN-2 ~~ • .::f\ Flow It.. 2 )&!a No
Meter , ~ 1'-GICI ~, • o ... No
net~.t:; TW4-22 /.. q ""' Flow I~ 0 -No
Meter ~ ~n, RS? ~ '1ft No
IJQ I/,. TW4-24 t:. K ':1.~ Flow Ir-0 .._ No
Meter 1 .2. ~q .2 q £.I_Q_; "el No -
I') flt; q TW4-25 '"1 ( • &;""r, \ Flow Ill 0 ¥ta-No
Meter '3ct 9,!l n~ ."2i~ ._.No
//Jl*'1 TW4-1 /{)'ii.oil Flow 1'2 ~ 'a No
Meter 3174.3/n q .._ No
I nOtn TW4-2 11"1n2 Flow / 7 .:2 "9e No
Meter 1 7 1 ~ SJ 9 ~ ¥98-No
tJ,., ;-/,. TW4-11 ~q,-,,n Flow JI,,.~ '8!S No
Meter "~ t:. 7 n c:. J./ ... No
O'J"f c;i TW4-21 7 SI 7t;f Flow It'.. .., -No
Meter ~ 1-:, aq ., ,_, ()-; 'im No
nq"31 TW4-37 (,. If'. 0~ Flow l~.O v.a No
Meter , r. g", n ~ . ,a ea No
nqLIL,/ TW4-39 -,~. '::1./'J Flow J 'l /) ~ No
Meter t, 1 ~ -, 1 q 1 V, No
,n~/ .. TW4-40 7/."'-'J~ Flow I st 0 YEe8 No
Meter ~ lo 2 I I 2 Q ~ ... No ,n~..,, TW4-41 ,c;, /.,.l. Flow t,. 0 ... No
Meter :, t" ~ q .:, 9 "J o '{m No
Operational Problems (Please list well number):
Correc_tive Action(s) Taken (Please list well number): ----------------
• Depth is measured to the nearest 0.01 feet.
.. .•. "···,
Weekly Inspection Form
Date
System Operational Clf no note r· 1me W II D th* e ec: C ts bl / I ) ommen anl£ ~ro ems corrective act ons
I n~t;l MW-4 Q~.L/1/ Flow' t../ "'.:> 'UIS No
Meter .J'-1;":t~q 1 14 )ms No
I') qr; IJ MW-26 17 /. '1 Flow I IJ '-I ¥:st No
Meter 1.1,::; ~ 1 /.:J 4 -No
I :J..{)0 TW4-19 An ~-n Flow I fl.() ~ No
Meter ~oto,1' ~, .7 ~ No
nq~q TW4-20 '13 ~I Flow ,;_ "{ VD No
Meter '3 ?, .:J I n ~ ~-~ 'ms No
JI"' 4 TW4-4 ~I,.,~ Flow , .. , «il 'mt No
Meter ~ SHI n , 11 1 'ml No
/)~t;IJ TWN-2 <t;. /1. Flow J 7 . .J.,( 'm No
Meter , ::, 1 ::J ~ "'? q. 'it ~ No
f1q~I) TW4-22 t:: q e:;,:; Flow I« I) -No
Meter ~ ~ , Q 1,. ,;-_ n ~ No
l]qt)q TW4-24 ..,,, '1 I) Flow 17 :1 'ml) No
Meter , ~ c::r i: ::i 7 A. "I ,n ..._ No
t') ~ "'.:1 TW4-25 "'14:1 '~ Flow I J /,. ~ No
Meter ~ l'J ,:-/) ~ q -, n 'm No
1n"2»q TW4-1 in"-1.~ I Flow ,-:::i ~ ~ No
Meter ~ 1 5{ n :i ,;-_ q 'a No
1n14 TW4-2 , ,~ (j/_ Flow 17.0 'im No
Meter 3 7...z 7 33 G. Va No
,nn, TW4-11 tJ.tJ -, I Flow I/.. /;. ~ No
Meter "" 1.a q ,; I) ~ .._ No
fHl ", '.l TW4-21 7 .:I. .:11''-Flow / 7 ;'J ~ No
Meter :, l -:1, Rn~~ . q c.. ~ No ·--
oq~a..t TW4-37 -r&.. 1-1. Flow J ~ (J 'tm No
Meter , 1. ~ q , 1 q. ~ 'CID No
nq44 TW4-39 Qn It;' Flow HIO 'teB_. No
Meter (DI fn t;, ~ ~ ,::; ~ No
1 I t;'t? TW4-40 i':J /J~ Flow IR(} ~ No
Meter '3 t.. 1 .. q ~~ ~ L.f ~ No
IJ ],;' TW4-41 7t:. e;q Flow ~ I) )tel No
Meter ::1 (,. .., ~ .., n ~ q 'ta 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 3 ""2:-2-.0
Weekly Inspection Form
Name'D~t-vnUtn.....
l
System Operational (If no note
Tl me W II e D th* eo C ommen ts I . anll eroblems corrective actions}
oq e: :i MW-4 71'/. /q Flow ~~ Y;as No
Meter -:l '-l (,, o L/ ~ ~ 5''-1 '9 No
I? q :::I. '-4 MW-26 ~ I -=I,::;' Flow JI :l. 'e No
Meter l./ 5 '1 q I Ci '-/ \3 No
II ~n TW4-19 ~q. ~ f\ Flow I 'R () ~ No
Meter ::J o 7 .:J ~ J 7. \ ~ No
/')qt') q TW4-20 7n 7q Flow t; r; 'm No
Meter 3 ~ .;z_ ~ -s-1l 3 t.. 'ms No
1n1~ TW4-4 ~0.fl~ Flow J 7. ia 'Hm No
Meter · i~ q I g .:2 ~ ~ No
/} 11 '3 '"' TWN-2 /,,,/ JO Flow JR n 'tes, No
Meter 1 ::J. 7 'I 7 q :i '::l ~ No
n «r; If TW4-22 -'/4/.:l~ Flow , -,. 'il ~ No
Meter ~ o 3 ~ n 3 r; 'ma No
IJRl/"I TW4-24 ~7. g7 Flow I 'I t:.. ~ No
Meter J ':l D 1 t:. 11 !1 ,:: !J )lo No
tJ ":l. ft, TW4-25 -,:3. ~r:. Flow I~. t:... "i1:ls No
Meter 'I 1 1 ,;-,; q_ q ~ ~ No
Jl)n:, TW4-1 Jn:J. ~I Flow J ::J.. (j ~ No
Meter ~ 1 ~ 7 1 7 4 'QI9 No
()qLI ~ TW4-2 un ~~ Flow /~ t,.{ \a No
Meter 3 7 ~ 4iH? r;: ,,._ ~ No
,Oq1 I TW4-11 q, 41 Flow J 7. '-I Yim No
Meter r.: 7 , q r:. q ~ No
nr:1 ,e:; TW4-21 7SI f"; Flow I 7 t'l )les No
Meter ~ 1 '-f (',, n ,, ~ ,; /J \a No
l}q()'3 TW4-37 71' QI'. Flow l i;f D ~ No
Meter , I';. q 'I :1 , .. 11,,1 , ~ NO
/)qJ-, TW4-39 7.t:: ,t;"/} Flow I fl b ~ No
Meter /-Jfl~~ 7 ~ ~ No
,n~; TW4-40 , ' r::' 1. Flow J ff, I) ~ No
Meter 3 7 7,;-7~, ,:J.. \Eel No
,n,~ TW4-41 -,tJ un Flow &. '-1 ~ No
Meter ::i L t;? LJ i; i;, J.f 1 's 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 J-j-16:Q Name Vese-fh:~, ~ deC/l;r 7
Time Well De~th* Time Well De~th*
095:g MW-4 891 :Z[ l:1..~Q TWN-1 Gi:Z. J Q
Q9S:~ TW4-1 SS:. Z5: 1aata TWN-2 5:, . ..!2
lQQ~ TW4-2 aa.:1...~ !33~ TWN-3 -!i.2... ~J..I
IDIQ TW4-3 (Q2,oa l~30 TWN-4 rao.t',<
ag~,;-TW4-4 ~3,33 l32l TWN-7 ii.,~
,oai.1 TW4-5 :zo.35: 13:Zl TWN-18 {Q.a.D2
02 ':I I TW4-6 17, $"ff 12>31 MW-27 s:1.oi •
09r;{D TW4-7 53-1.gs iQ~i MW-30 1'i.. U
1008 TW4-8 8t11aa: jQ3f.o.-MW-31 (a~.Q3
1a1g TW4-9 "2~13 ;-
1aa.~ TW4-10 '21. 7'.i.
IQQt;' TW4-11 901'2:l
0913 TW4-12 ~·1.. ~~
09.LQ TW4-13 5:,;, ii~ Q~lf.a TW4-28 ~:z. G" t)
nqa3 TW4-14 Z:Zdi'3 ass: 1 TW4-29 71...22
UJ.i!.:t. TW4-15 ,~139 Q. s ~Y. TW4-30 7~.gl
U2.3Q TW4-16 ::za.i' QfS~Q TW4-31 'U,. I M.8.
l0]3 TW4-17 aa.ga aq19 TW4-32 2 '>, .:i.a.
l~ ::tl TW4-18 1L,':i.Q OZ~l TW4-33 u,.,1a
13~Q TW4-19 :::zQ.~(Q 08~3-TW4-34 7.f.1 ~a -
LQS:.I TW4-20 -,~ I t;'!z._ Qj1~8 TW4-35 2~19Q
UllfQ TW4-21 70,te._ C9'2Z TW4-36 ~:z ~s
lldQ TW4-22 Ztnt ,~ 1Q~!:1. TW4-37 ""1i,I~
093, TW4-23 '1'1, 3 ;J /PIS:: TW4-38 Sf?, 5L •
ll'23 TW4-24 ~g, l:2. 1-os:a TW4-39 1'2.3a
l;J. (l TW4-25 -:J. I, a:i. ag.i1 TW4-40 -:1..a.oa.
Q93iil TW4-26 1;!... £ L[ D.9.~8. TW4-41 1 !t1 :2..~
OS37 TW4-27 7S,83 OR,1 TW4-42 4!. JQ
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
Date
S~stem Operationa;(no note
Time Well Deoth* Comments anv problems/corrective actions)
nq,;q MW-4
~'l '"' Flow l,f 0 'um No
Meter ~ LI r,. ~ 1 7 ~. 1r, q ¥ea, No
l)Q~"' MW-26 ~~ t~Ll Flow JI. 1../ 'io No
Meter "'<' ~ 'A "il 4 (n --No
f 14 Ci TW4-19 C. '1 'iG1 Flow t'8.n '3 No
Meter ::io 7q 7'//J.'1 ~ No
/J'l:J4 TW4-20 jQ /&; Flow LI 4 '9 No
Meter 3 ~ ~ 'i" 1 ) 9 4rl \!:es No
JIJ:J.(;. TW4-4 tJ c.. l.G Flow I~'{ ., --No
Meter t:. qt> 17 o ~ ~ No
.11qn:,. TWN-2 C:-1!... '5'7 Flow / fJ /) Vs No
Meter , !l 7 7 , "'l Q ~ ~ No
/'JQ I £4 TW4-22 -,/J /,,,q Flow I,;, I') 'imt No
Meter t:.l'r; ,_., 7 n .2'a No
nqnq TW4-24 t'..~ I./~ Flow / I,/ Cit 'mt No
Meter r~ n' 7 /J ~ o 11 ~ No
n 9. r;e:-TW4-25 -,, "11 Flow IO In Vm No
Meter "' , ~ , /-7 .., " ~ No
I() II TW4-1 ~t;" ~~ Flow I ::J. cg -No
Meter 3 1 q '-4 q "'7 ::, ~ No
nt.Jt;f TW4-2 ,1n c:n Flow /~.I/ 'um No
Meter 37'-/8 /fJ '3 ~ No
nqL/z:' TW4-11 QI ~/. Flow I~ .;, ~ No
Meter /,,. 7 ~ .,., 3 (,, -No
()RIIS TW4-21 77 7/J Flow / 7. t;l ~ No
Meter :, 1 Ii' I./ o :J ..,, IJ 1 ~ No
n ,,, t:I TW4-37 "7:J I>~ Flow 1'/l.n 'tt:9, No
Meter , t.qq 111 .., 'tes No
l']q 2_q TW4-39 ~0.()2. Flow Jrl,(') ~ No
Meter /.~, L/ 2 i; o ~ No
/{)~&{' TW4-40 '11. '7~ Flow I 'fl. [] .._ No
Meter 3,;.,~!J::,? oo ~ No
IOIQ TW4-41 "1« ,; Flow ,:. n ~ No
Meter :J r .. q 7 r; :J ,; :J 'tel 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 :s-u,-2,o NameQ«r+aaz 4,...-&t~
System Operational (If no note r· W II D th* C ts bl / ,me e eo· ommen anl£ 12ro ems corrective actions}
J/J l 0 MW-4 ~Sl LI,. Flow L/ 9. ~ No
Meter ::J J./ <1. n '1 t; .2. 1 r:? ~ No
JO() q MW-26 ~2 2Ci Flow JI~ ~ No
Meter t.1 '5" ~ ~ r,; 1 q ~ No
)~ 0 I) TW4-19 t: C, ,; :J Flow I 'ii I) 'abm, No
Meter !l n q 1 4 'il L/ q -No
'nq ,;-'7 TW4-20 7~ ~1 Flow 4. ~ 'm No
Meter i ~ I.{ e; 1 q q:3 ~ No
JO'i &: TW4-4 ~I II Flow I I,, R r ~ No
Meter c. q , q Q, r,, ~ No
OQII TWN-2 &J. 7 L/ Flow /~. ':l ._ No
Meter 1 ~ 110 '-I ~ 1 t> Yo No
.,.f/,)q~q TW4-22 7 ~ 'l.7 Flow I~ /) ~ No
Meter 1 . .''J 1.. t;" 1 9, ~ VP No
/)q~~ TW4-24 ~'l. ',/') Flow J L/ r.. ~ No
Meter , ~ J ~ Y 1 ~-t::'I 'm> No
F
1oqo1.1 TW4-25 .,~_~, Flow JI~ --No
Meter I./:, Sf~ 7 7 SJ7 ~ No
J/J ~ L/ TW4-1 tn:J. ~~ Flow /3 '.2 ~ No
Meter .3 :J..o '1 c. ,. tJ ~ No
Jf);J_~ TW4-2 JJ~ 'ln Flow J LI. '-I Vs No
Meter ~ 7 t:. 'In I/. 4 -No
J()J-Y TW4-11 QI) "'/J Flow J 7 /) Vs No
Meter t:. 7 '19. 7. ~ 'lm No
0R'>7 TW4-21 '"7 ~ • .l .:J Flow /,',,. L{ ~--No
Meter . ._.,, 1:. ~ ,;z a" "1'-1 'm-No
l/'JqL{; TW4-37 70. n-r Flow Ji 0 ~ No
Meter 17n7nc~ ~ ~ No
inn~ TW4-39 'iltl. I~ Flow J ~ /) ¥sB No
Meter /-2 IL.D; n. ~ ~ No
,ner, TW4-40 71, ~, Flow ,~ (} ,._ No
Meter 'l q 7 &.f /,. '-I n r,, 'ms No
JO~Q TW4-41 "7~ I~ Flow ~,~ )ms No
Meter ~ 7 / 9' Q IJ 1,, 1 ~ 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 :')/~Y/3.060
Tl W II me e D th* eo
i::t 1 ("~ MW-4 RY I~
1.1/)6 MW-26 ;,(()' I 'J
13D0 TW4-19 -l'-1 ~~
IJS.t TW4-20 7~. '11
1~:Yt TW4-4 ·,5,q~
lL'\Ci TWN-2 s&. ·i4
l )y7( TW4-22 IT.2 ) '1
I/ii TW4-24 (~9 37
11'.2;4 TW4-25 7:).. L\ C:.
12...2.S TW4-1 94 t)'/,
t2.I.S TW4-2 \0() .1>~
1111 TW4-11 C12..1::I~
ll~D TW4-21 ·7E,. c._q
r Lf.::J. TW4-37 17 D a,7
i.::t..Di TW4-39 io .os
ID'1 TW4-40 7~ t..tX
I:? ~c, TW4-41 ii ,q.11
Weekly Inspection Form
Name ~""'r /ku:ck~
System Operational (If no note
ommen an~ 2ro ems correct ve act onsl C ts bl I i I
Flow 4 () O<e.s )No
Meter )_i..l}{ y ,< 11 . K.3 ( YA0 No
Flow 10,A (Yes _No
Meter 1.H,,()q'7,C~ ( Yes "iNo
Flow IS< ,0 (.,.Yes 'No
Meter 2.0 9..St.. J '-l , Y ( Tes {No
Flow L-i , ::l (Y~o
Meter 3..1~8b.:2.. I I ( Yes r,Jo ,,
Flow il,,.S ('i'es ) No
Meter h 911; J_,; ':?. (Yes \No ,,
Flow IC..,n f v~, No
Meter D 5(2~'1L 0 (~s ) No ~-
Flow [55,0 c _Yes ) No
Meter b 'I. q L J'1. -b ( Yes) No
~
Flow 14.S ~Y.:ei;u No
Meter 1 ·3; 5f<. 1 ~ . '1 i::.. , Yes)No
Flow 1\,5 c ·Yes )No
Meter 4 ~ \ '1 L.. 5 .J; ( ores \No
Flow i3,D c .... ~o
Meter 3:2.0>< ~~ .-~ ( Yes J,.Jo
-
Flow 14 ,5 ( Y-e&:i No
Meter s7 t_ '1 '-.4 ,~ r Yes )No -~
Flow 17.0 (Yes )No
Meter 6 7 S £0 ,g (YeS\ No
'-~
Flow If:..~ r ..Xes 'No
Meter 2.17 15 c:..,;.. f,L./ (' , " "'N re~ 0
'-1 .......
Flow i 5<,0 (~o
Meter 17DC!Cf l:J.. () ( Yes NO
Flow ISCO ( 'les .No
Meter fo;;J... 7 c... 7 A 2 (Yes\ No
Flow 15C0 ( Yes J No
Meter L.JOlS'-7, ~5 (Yes )No
Flow ~ ~.D (~J No
Meter ;J..T:J.. •. r:; )7, (./ ( Yet 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 3 -30-M Name 12"4 e--Lj'cnqn,, fua4C Veta/,<
System Operational (If no note r· 1me W II D th* C ts bl / ti ti > e eo ommen 80:r'. !;!rO ems correc ve ac ons
l}Q&.lt... MW-4 ~J 4S\ Flow 41 'im No
Meter 'J...4q, :J 1,; 1. i:; ~ No
nq~~ MW-26 ~n 19: Flow JI I',. 'JS!I No
Meter "~"Jc:,;"'· tt 'a!,. No
1n1Jn TW4-19 /..~ ,c,,r Flow J 'l (J 'et, No
Meter 2.1 D 1 ll .-;.(". -:a. 'Im No
0'1/(J TW4-20 7~.,~ Flow ~.n 'tea No
Meter "'11 5 1 'ii ~ . , r... ~ No
J/)/}q TW4-4 <Ai, 7n Flow ·· I~.(. Y:es No
Meter t,.q ~, 71 1 -No
Os:t'-11 TWN-2 ~,e:' I~ Flow. J '7. :> 'tea No
Meter 1 "J 04 ~ 1 c:. 7 ¥:es No
1)9..~'f TW4-22 ., t.J (/If Flow Jt/. .tJ 'te3 No
Meter ~ q , (jf t.. ~ 'iii 'tes No
O'lt; I TW4-24 -,/J I. J Flow 1<.~ "ts No
Meter , ~, q :i .11. t.J7 '{:es-No
ni'l 15" TW4-25 7/ act Flow J 0."' ~ No
Meter " 3 71,. 7 s . t:J 11 ~ No
/)qtj7 TW4-1 Jt'J:J.. 7(,, Flow I~ I./ ~ No
Meter 3 2.1 Y ~ :>. n 'ta No
/}q'I f TW4-2 llfl -in Flow 17,&; ~ No
Meter '3 77'il :2 , ~ Yo No
no11 TW4-11 qr.~a Flow I&. ,.;t ~ No
Meter t;, 7 1,. q q . , ~ No
/7CUQ TW4-21 t;.9 . .1./(,,. Flow I~ ..:l ~ No
Meter ..:1 1 -, 'i I./ ,; ~ q , '(B9 No
nqnlf TW4-37 -, 2 . ,<"";\ Flow I oA .0 ~ No
Meter 17,"' 2. ,;q .t!f 'tBS No
/)QJ& TW4-39 (14.~'-I Flow I~() ~ No
Meter 1,.1 tJJ .n ~ . ~ ~ No
JOI/,. TW4-40 -11 1'i"" Flow J ~ (J V. No
Meter ..,n'il&.1~n .~i "0:19 No
JOnlJ TW4-41 -,q 7g Flow '1 1 ~ No
Meter ~.,~,.qr. .~i.f 't: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.
TabD
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary
Name: Deen Lyman
Date: 2/10/2020-2/13/2020
Depth to Depth to Depth to
Date Time Well Water (ft.) Date Time Well Water (ft.) Date Time Well Water (ft.)
2/13/2020 1331 MW-01 64.75 2/10/2020 937 MW-04 96.54 2/13/2020 1243 PIEZ-01 66.68
2/13/2020 1413 MW-02 109.63 2/10/2020 943 TW4-0l 105.46 2/13/2020 1232 PIEZ-02 44.39
2/13/2020 1011 MW-03A 84.01 2/10/2020 931 TW4-02 108.12 2/13/2020 1339 PIEZ-03A 55.48
2/13/2020 1427 MW-05 108.34 2/10/2020 1241 TW4-03 62.88 2/13/2020 920 PIEZ-04 65.18
2/13/2020 1431 MW-11 85.23 2/10/2020 956 TW4-04 79.09 2/13/2020 927 PIEZ-05 64.31
2/13/2020 1423 MW-12 107.81 2/10/2020 1252 TW4-05 70.20 2/13/2020 1322 TWN-01 67.55
2/13/2020 1459 MW-14 102.04 2/10/2020 1226 TW4-06 77.44 2/13/2020 840 TWN-02 49.00
2/13/2020 1455 MW-15 105.48 2/10/2020 1230 TW4-07 83.04 2/13/2020 1345 TWN-03 42.17
2/13/2020 946 MW-17 71.82 2/10/2020 1233 TW4-08 85.87 2/13/2020 1335 TWN-04 60.53
2/13/2020 1318 MW-18 73.32 2/10/2020 1248 TW4-09 68.21 2/13/2020 1314 TWN-06 80.02
2/13/2020 1239 MW-19 65.04 2/10/2020 1255 TW4-10 67.63 2/13/2020 1325 TWN-07 82.14
2/13/2020 1046 MW-20 87.09 2/10/2020 925 TW4-ll 90.02 2/13/2020 1302 TWN-14 59.80
2/13/2020 1035 MW-22 62.41 2/10/2020 1451 TW4-12 54.21 2/13/2020 1255 TWN-16 47.68
2/13/2020 1413 MW-23 113.92 2/10/2020 1448 TW4-13 55.55 2/13/2020 1329 TWN-18 61.91
2/13/2020 1359 MW-24 112.05 2/10/2020 1441 TW4-14 77.46 2/13/2020 1235 TWN-19 53 .67
2/13/2020 1505 MW-25 80.05 2/10/2020 1258 TW4-16 72.00 2/13/2020 1105 DR-05 83 .25
2/13/2020 917 MW-26 73.07 2/10/2020 1319 TW4-18 71.25 2/13/2020 1100 DR-06 94.16
2/13/2020 1351 MW-27 56.84 2/10/2020 1230 TW4-19 69.68 2/13/2020 1434 DR-07 92.03
2/13/2020 1405 MW-28 74.56 2/10/2020 905 TW4-20 78.88 2/13/2020 1122 DR-08 51.37
2/13/2020 724 MW-29 107.74 2/10/2020 818 TW4-21 78.30 2/13/2020 1115 DR-09 86.62
2/13/2020 907 MW-30 74.93 2/10/2020 855 TW4-22 70.95 2/13/2020 1055 DR-10 78.44
2/13/2020 901 MW-31 68.81 2/10/2020 1214 TW4-23 74.l l 2/13/2020 1001 DR-LI 97.98
2/13/2020 855 MW-32 80.67 2/10/2020 848 TW4-24 64.21 2/1 3/2020 956 DR-12 91.85
2/13/2020 1426 MW-33 DRY 2/10/2020 834 TW4-25 72.14 2/13/2020 952 DR-13 69.72
2/13/2020 1444 MW-34 107.55 2/10/2020 1223 TW4-26 71.95 2/13/2020 1133 DR-14 76.28
2/13/2020 1420 MW-35 112.36 2/10/2020 1417 TW4-27 78.65 2/13/2020 1020 DR-15 92.78
2/13/2020 1423 MW-36 110.55 2/10/2020 1455 TW4-28 47.l l 2/13/2020 1143 DR-17 64.72
2/13/2020 1448 MW-37 106.43 2/10/2020 1438 TW4-29 76.94 2/13/2020 1150 DR-19 63.32
2/13/2020 1038 MW-38 70.51 2/10/2020 1425 TW4-30 74.69 2/1 3/2020 1147 DR-20 55.55
2/13/2020 1030 MW-39 65.05 2/10/2020 1420 TW4-31 76.28 2/13/2020 1216 DR-21 100.78
2/13/2020 936 MW-40 79.83 2/10/2020 1458 TW4-32 54.80 2/13/2020 1157 DR-22 DRY
2/10/2020 1414 TW4-33 76.51 2/13/2020 1221 DR-23 70.51
MW-26 = TW4-15 2/10/2020 1433 TW4-34 75.16 2/13/2020 1201 DR-24 44.40
MW-32 = TW4-17 2/10/2020 1428 TW4-35 74.70
nme nts: 2/10/2020 1445 TW4-36 57.27
2/10/2020 859 TW4-37 73.68
2/10/2020 1244 TW4-38 58.32
2/10/2020 909 TW4-39 81.17
2/10/2020 1016 TW4-40 72.01
2/10/2020 950 TW4-41 76.29
2/10/2020 1409 TW4-42 67.87
@ estimated dry area
rw442 temporary perched monitoring well
¢ 5527 installed April, 2019 showing
elevation in feet amsl
MW-38 perched monitoring well
-<?"5463 installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
+5526 installed February, 2018 showing
elevation in feet amsl
M:,'55
504 perched monitoring well showing
elevation in feet amsl
TW4-12 h d . . II 0 5570 temporary perc e monitoring we
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
-1 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; TW4-1 , TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM, INC.
KRIGED 1st QUARTER, 2020 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE
H:/718000/may20/WUUwl0320.srf
FIGURE
D-1
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;
I I I I and forTW4-19, TW4-20, TW4-37 and TW4-39)
• ®
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
capture for nitrate pumping wells TWN-2,
TW4-24 and TW4-25 incorporated within
capture of chloroform pumping system)
estimated dry area
TW4-42 temporary perched monitoring well
¢ 5527 installed April, 2019 showing
elevation in feet amsl
MW-38 perched monitoring well
,¢,5463 installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
+5526 installed February, 2018 showing
elevation in feet amsl
M:;~04 perched monitoring well showing ~ elevation in feet amsl
TW4-12 . . 0 5570 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
-i 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, TW4-25 and TWN-2 are nitrate pumping wells; TW4-1, TW4-2 and TW4-11 water levels are be~w the base of the Burro Canyon Formation
~
HYDRO
GEO
CHEM,INC. APPROVED
KRIGED 1st QUARTER, 2020 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
DATE REFERENCE
H:/718000/may20/WUUwl0320.srf
FIGURE
D-2
' ·,
' '
estimated chloroform capture zone boundary
,;;;-stream tubes resulting from pumping. (note: , , f'' combined capture shown for MW-4, TW4-1,
/ / J # TW4-2, TW4-4, TW4-11, TW4-40 and TW4-41;
and for TW4-19, TW4-20, TW4-37 and TW4-39)
II
TW4-42
¢ !it,'},7
TW4-40
.5526
MW-25
e ssJJ
TW4-7
0 5538
PIEZ-2
g 5554
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
capture for nitrate pumping wells TWN-2,
TW4-24 and TW4-25 incorporated within
capture of chloroform pumping system)
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 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; TW4-1, TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
KRIGED 1st QUARTER, 2020 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
detail ma CHEM, INC. APPROVED DATE REFERENCE
H:/718000/may20/WL/Uwl0320cz.srf
FIGURE
D-3
TabE
Kriged Previous Quarter Groundwater Contour Map
@ estimated dry area
TW4-42 temporary perched monitoring well
¢ 5527 installed April, 2019 showing
elevation in feet amsl
MW-38 perched monitoring well
"9-5463 installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well
-+-5526 installed February, 2018 showing
elevation in feet amsl
M:,';5
503 perched monitoring well showing
elevation in feet amsl
TW4-12 h d . . II 0 5570 temporary perc e momtonng we
showing elevation in feet amsl
TWN-7 . . . A.5567 temporary perched nitrate momtonng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
'1 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 pumpin-9_ wells; TW4-1, TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM, INC.
KRIGED 4th QUARTER, 2019 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE
H:/718000/feb20/WUUwl1219.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) Monitorin~ (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) Monitoring (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
5,533.67 11/18/19 88.66 87.10
5,525.79 02/10/20 96.54 94.98
......
N 0
......
8
Depth Below Measuring Point (ft.)
00 0 O'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 ==:
06/03/93 ~ ......
10/16/94 ~
02/28/96 -~ "'1
07/12/97 t,
~
11/24/98 ~ -=r"
04/07/00 0 <
08/20/01 ~ "'1
01/02/03 ~ ... a
05/16/04 ~ --
09/28/05 ?
'r::t' -02/10/07 a ~
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
5,537.23 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
5,510.85 11/18/19 107.73 106.71
5,513.12 02/10/20 105.46 104.44
......
N 0
...... ......
0
Depth Below Measuring Point (ft.)
......
8 I.O 0 00 0 -.:i 0 °' V,
0 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 I ~
03/31/07 ~ 08/28/07
01/25/08 -~
06/23/08 ""S
~ 11/20/08 ~
04/19/09 "C -09/16/09 =-02/13/10 0
07/13/10 ~ ~
12/10/10 ""S
05/09/11 ~ ....
10/06/11 a
03/04/12 ~ -08/01/12 ? 12/29/12 ~ 05/28/13 -10/25/13 a "C 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
03/17/21
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 73.30 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 72.70 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 66.90 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 65.80 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
5,521.60 06/22/18 103.12 101.50
5,510.01 09/24/18 114.71 113.09
5,543.01 12/17/18 81.71 80.09
5,522.70 03/25/19 102.02 100.40
5,522.49 06/24/19 102.23 100.61
5,522.29 08/12/19 102.43 100.81
5,515.62 11/18/19 109.10 107.48
5,516.60 02/10/20 108.12 106.5
......
vJ 0 -N 0
...... ......
0
Depth Below Measuring Point (ft.)
......
8 \0 0 00 0 -.1 0 0\ 0
V,
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 .a.
11/01/06 I N
03/31/07 ~ 08/28/07
01/25/08 ;-
06/23/08 ""I
~ 11/20/08 ~
04/19/09 ~
09/16/09 ~
02/13/10 0
07/13/10 -< ~ 12/10/10 ""I
05/09/11 ~ ...
10/06/1 l 9
03/04/12 ~ -08/01/12 ? 12/29/12 i:::r 05/28/13 §" 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
03/17/21
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 63.30 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) Monitoring (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 50.40 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 48.20 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 48.60 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
5,571.83 06/22/18 60.40 59.38
5,571.34 09/25/18 60.89 59.87
5,570.99 12/17/18 61.24 60.22
5,570.21 03/25/19 62.02 61.00
5,570.28 06/24/19 61.95 60.93
5,570.04 08/12/19 62.19 61.17
5,569.68 11/18/19 62.55 61.53
5,569.35 02/10/20 62.88 61.86
Depth Below Measuring Point (ft.)
-..J -..J °' °' u, u, ~ ~ u, 0 V, 0 u, 0 u, 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 ,&;;;..
11/22/06 I ~
04/21/07 ~ 09/18/07
02/15/08 -~
07/14/08 "1
0 12/11/08 ~
05/10/09 "Cl -10/07/09 =-03/06/10 0
08/03/10 ~ ~ 12/31/10 "1
05/30/11 ~ ...
10/27/11 9
03/25/12 ~ .-.. 08/22/12 ? 01/19/13 C"' 06/18/13 -11/15/13 9 "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
04/07/21
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.J84 114.5
5,512.15 05/25/00 101 .34 100.16
5,518.99 06/09/00 94.50 93.32
5,512.15 06/16/00 101.34 100.16
5,517.47 06/26/00 96.02 94.84
5,520.15 07/06/00 93.34 92.16
5,521.44 07/13/00 92.05 90.87
5,522.01 07/18/00 91.48 90.30
5,522.95 07/27/00 90.54 89.36
5,523.49 08/02/00 90.00 88.82
5,523.85 08/09/00 89.64 88.46
5,523.89 08/15/00 89.60 88.42
5,524.56 09/01/00 88.93 87.75
5,513.24 09/08/00 100.25 99.07
5,516.67 09/13/00 96.82 95.64
5,519.09 09/20/00 94.40 93.22
5,522.17 10/05/00 91.32 90.14
5,524.67 11/09/00 88.82 87.64
5,518.55 12/06/00 94.94 93.76
5,527.70 01/03/01 85.79 84.61
5,529.09 02/09/01 84.40 83.22
5,529.54 03/27/01 83.95 82.77
5,530.24 04/30/01 83.25 82.07
5,530.27 05/31/01 83.22 82.04
5,534.41 06/22/01 79.08 77.90
5,533.15 07/10/01 80.34 79.16
5,534.04 08/20/01 79.45 78.27
5,534.47 09/19/01 79.02 77.84
5,533.29 10/02/01 80.20 79.02
5,533.87 11/08/01 79.62 78.44
5,534.28 12/03/01 79.21 78.03
5,534.72 01/03/02 78.77 77.59
5,535.44 02/06/02 78.05 76.87
5,536.45 03/26/02 77.04 75.86
5,536.41 04/09/02 77.08 75.90
5,537.34 05/23/02 76.15 74.97
5,537.33 06/05/02 76.16 74.98
5,537.98 07/08/02 75.51 74.33
5,538.83 08/23/02 74.66 73.48
5,539.28 09/11/02 74.21 73 .03
5,539.77 10/23/02 73.72 72.54
5,540.21 11/22/02 73.28 72.10
5,540.30 12/03/02 73.19 72.01
5,540.80 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 l.184 114.5
5,540.99 02/12/03 72.50 71.32
5,541.68 03/26/03 71.81 70.63
5,541.77 04/02/03 71.72 70.54
5,541.89 05/01/03 71.60 70.42
5,542.03 06/09/03 71.46 70.28
5,541.93 07/07/03 71.56 70.38
5,541.89 08/04/03 71.60 70.42
5,541.83 09/11/03 71.66 70.48
5,541.89 10/02/03 71.60 70.42
5,542.00 11/07/03 71.49 70.31
5,542.01 12/03/03 71.48 70.30
5,542.56 01/15/04 70.93 69.75
5,542.71 02/10/04 70.78 69.60
5,543.23 03/28/04 70.26 69.08
5,543.56 04/12/04 69.93 68.75
5,543.87 05/13/04 69.62 68.44
5,543.92 06/18/04 69.57 68.39
5,544.66 07/28/04 68.83 67.65
5,544.80 08/30/04 68.69 67.51
5,544.85 09/16/04 68.64 67.46
5,544.71 10/11/04 68.78 67.60
5,544.53 11/16/04 68.96 67.78
5,544.63 12/22/04 68.86 67.68
5,544.31 01/18/05 69.18 68.00
5,544.59 02/28/05 68.90 67.72
5,544.69 03/15/05 68.80 67.62
5,544.68 04/26/05 68.81 67.63
5,544.79 05/24/05 68.70 67.52
5,544.80 06/30/05 68.69 67.51
5,544.78 07/29/05 68.71 67.53
5,545.01 09/12/05 68.48 67.30
5,545.23 12/07/05 68.26 67.08
5,545.74 03/08/06 67.75 66.57
5,545.79 06/14/06 67.70 66.52
5,545.86 07/18/06 67.63 66.45
5,545.81 11/07/06 67.68 66.50
5,546.68 02/27/07 66.81 65.63
5,546.54 05/02/07 66.95 65.77
5,547.16 08/15/07 66.33 65.15
5,547.22 10/10/07 66.27 65.09
5,548.31 03/26/08 65.18 64.00
5,548.87 06/24/08 64.62 63.44
5,549.24 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
5,549.31 10/14/08 64.18 63.00
5,549.73 03/03/09 63.76 62.58
5,549.91 06/24/09 63.58 62.40
5,549.70 09/10/09 63.79 62.61
5,549.87 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
5,528.08 11/18/19 85.41 84.23
5,534.40 02/10/20 79.09 77.91
...... ......
0
......
8
Depth Below Measuring Point (ft.)
\0 0 00 0 -.J 0 0\ V, 0 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 ,.,
01/08/09 ~
06/07/09 ~ "Cl
11/04/09 ~
04/03/10 0 08/31/10 -<
01/28/11 ~ ,.,
06/27/11 ~ ... 11/24/11 a 04/22/12 ~
09/19/12 ,-.... ~ 02/16/13 .
07/16/13 C" -12/13/13 a
05/12/14 "Cl '-'
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
05/05/21
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) Monitorin; (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 121.85
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 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.LSD) Well
5,638.75 5,640.70 1.95 1.21.85
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 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
5,586.03 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 55.30 53.35
5,584.80 03/03/09 55.90 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 1.95 121.85
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
5,572.68 06/22/18 68.02 66.07
5,571.89 09/24/18 68.81 66.86
5,571.86 12/17/18 68.84 66.89
5,571.15 03/25/19 69.55 67.60
5,571.26 06/24/19 69.44 67.49
5,571.12 08/12/19 69.58 67.63
5,570.73 11/18/19 69.97 68.02
5,570.50 02/10/20 70.20 68.25
-..I Ul -..I 0
Depth Below Measuring Point (ft.)
0\ Ul 0\ 0 Ul Ul VI 0
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
12/12/20
'-----'-------'------'------'------'-05/11/21
~ ~ I tll
~ ;-.,
i Er
0 ~ .,
~ ... a ~ --?
C" §"
"'O '-"
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
5,522.28 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 70.80 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
5,531.69 11/18/19 77.09 75.64
5,531.34 02/10/20 77.44 75.99
Depth Below Measuring Point (ft.)
\0 00 00 -..J -..J 0\ 0\ u, u,
0 u, 0 u, 0 u, 0 u, 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:,..
I
05/19/07 °' 10/16/07 ~ 03/14/08 -08/11/08 ~ ""l
01/08/09 I:,
06/07/09 ~ "'C 11/04/09 e,
04/03/10 0 08/31/10 <
01/28/11 ~ ""l
06/27/11 ~
11/24/11 ....
9 04/22/12 ~
09/19/12 -..
02/16/13 ?
07/16/13 -r::r -12/13/13 9
05/12/14 "'C --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
05/05/21
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
5,539.13 11/18/19 81.94 80.74
5,538.03 02/10/20 83.04 81.84
00 VI 00 0
Depth Below Measuring Point (ft.)
-..J VI -..J 0 0\ VI ~ VI VI VI 0
t-----+-----+-----ir---4-:---t-----+----'I---+ 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
11/22/06
04/21/07
09/18/07
02/15/08
07/14/08
12/11/08
05/10/09
10/07/09
03/06/10
08/03/10
12/31/10
05/30/11
10/27/11
03/25/12
08/22/12
01/19/13
06/18/13
11/15/13
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
~--~---------'------~---------'----'-04/07/21
1-3 ~ I ....:J
~ it "'1
0 ('D
"Cl ~
0 -id ('D
"'1
1-3 .... ~ ---?
'a' -9 "Cl .._,,
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
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
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
5,550.68 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 63.11
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
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
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
5,548.80 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
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
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
5,555.56 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
5,536.30 03/25/19 85.10 80.50
5,536.67 06/24/19 84.73 80.13
5,536.82 08/12/19 84.58 79.98
5,536.37 11/18/19 85.03 80.43
5,535.53 02/10/20 85.87 81.27
-0 0 I.O 0 00 0
Depth Below Measuring Point (ft.)
~ 0\ 0 Vl 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 ,l;;l,.
11/22/06 I QO
04/21/07 ~ 09/18/07
02/15/08 ""'" ~
07/14/08 ""1
~ 12/11/08 ~
05/10/09 "'Cl
10/07/09 Er
03/06/10 0
08/03/10 -<d ~
12/31/10 ""1
05/30/11 ~ ....
10/27/11 a
03/25/12 ~ --08/22/12 ? 01/19/13 -r:r 06/18/13 -11/15/13 a "'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
04/07/21
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
5,577.09 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) (LSD) (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 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
5,577.24 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
5,571.69 06/22/18 65.90 64.42
5,571.20 09/25/18 66.39 64.91
5,570.92 12/17/18 66.67 65.19
5,570.16 03/25/19 67.43 65.95
5,570.17 06/24/19 67.42 65.94
5,570.01 08/12/19 67.58 66.10
5,569.66 11/18/19 67.93 66.45
5,569.38 02/10/20 68.21 66.73
-.J 0 0\ 00 0\ 0\
Depth Below Measuring Point (ft.)
i 0\ N 0\ 0
V,
00
V,
0\
V,
.j::.
V,
N
V,
0
'---~-t--~---+-~---1i---~-t------1a.1.:::~---1i---~-t--~---+-~---1i---~-;-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
12/13/06
05/12/07
10/09/07
03/07/08
08/04/08
01/01/09
05/31/09
10/28/09
03/27/10
08/24/10
01/21/11
06/20/11
11/17/11
04/15/12
09/12/12
02/09/13
07/09/13
12/06/13
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
04/28/21
~ ! I ',Q
~ ;-
~
t:, .g
~
0 ~ ~
~ ... 9 ~ -?
f "'C --
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 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
5,578.02 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 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
5,571.79 06/30/16 62.45 60.20
5,571.27 09/29/16 62.97 60.72
5,570.94 12/21/16 63.30 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
5,568.81 06/22/18 65.43 63.18
5,568.33 09/25/18 65.91 63.66
5,568.08 12/17/18 66.16 63 .91
5,567.33 03/25/19 66.91 64.66
5,567.39 06/24/19 66.85 64.60
5,567.21 08/12/19 67.03 64.78
5,566.88 11/18/19 67.36 65.11
5,566.61 02/10/20 67.63 65.38
Depth Below Measuring Point (ft.)
00 -.l °' Vl ~ w N ......
0 0 0 0 0 0 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 ~ 05/07/07 ~ 10/04/07 ~
03/02/08 I
i,-
07/30/08 0
12/27/08 ~ 05/26/09 """ ~ 10/23/09 ...
03/22/10 ~ ~
08/19/10 ~ """ 01/16/11 ::,"'
06/15/11 0
11/12/11 ~ ~
04/10/12 ...
~ 09/07/12 .... a 02/04/13 ~
07/04/13 ,,-..,
12/01/13 ~
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
04/23/21
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 64.00
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 TW4-11
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
5,529.85 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
5,530.36 06/22/18 93.26 91.56
5,530.41 09/24/18 93.21 91.51
5,531.96 12/17/18 91.66 89.96
5,532.84 03/25/19 90.78 89.08
5,533.62 06/24/19 90.00 88.30
5,532.49 08/12/19 91.13 89.43
5,532.50 11/18/19 91.12 89.42
5,533.60 02/10/20 90.02 88.32
....
8 \0 Ul \0 0
Depth Below Measuring Point (ft.)
00 Ul 00 0 -..J Ul -..J 0 °' Ul g Ul Ul Ul 0
l----+---+-------,l-----+--..... --1-----+----+---1---+ 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
03/02/08
07/30/08
12/27/08
05/26/09
10/23/09
03/22/10
08/19/10
01/16/11
06/15/11
11/12/11
04/10/12
09/07/12
02/04/13
07/04/13
12/01/13
04/30/14
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 .__ _ __.__ _ ___.._ __ .__ _ __.__-,--___.._ __ .___........._ _ __._ __ .__ _ _._ 04/23/21
~ ~ ,&;;I..
I ~ ~
~ ~ ""1
~ ~ "O g.
0 < ~ ""1
~ .... ~ ,,-....
?
r=" §"
"O --
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) Monitoring (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
5,570.06 11/18/19 54.17 52.32
5,570.02 02/10/20 54.21 52.36
VI \0 VI +>-
Depth Below Measuring Point (ft.)
~ \0 t w \0 w +>-
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
02/14/21
""'3 ~ ,&;;;..
I i,,-
N
~ """ ~ "1
~ ~ ~ """ t="'
0 < ~ "1
""'3 .... a ~ --?
-a--a ~ '-'
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
5,571.08 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
5,564.39 11/18/19 55.55 53.70
5,564.39 02/10/20 55.55 53.70
-0 0 \0 0
Depth Below Measuring Point (ft.)
00 0 -..J 0 g u,
0 .i,.
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 ~
03/19/09 ~ 08/16/09 '""'" t,
01/13/10 ""1
06/12/10 ~ t,
11/09/10 "C
04/08/11 g.
09/05/11 0 -< 02/02/12 t,
""1
07/01/12 ~ .... 11/28/12 !3
04/27/13 t, ---09/24/13 ~ .
02/21/14 ~
07/21/14 -!3
12/18/14 "C --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
02/14/21
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
5,522.24 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 12/17/14 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 78.10 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
5,535.09 11/18/19 77.68 75.83
5,535.31 02/10/20 77.46 75.61
......
8 -1
' '
\0 0
~
~. .
• • • •
' •
• • •
'
~
~
00 0
•
10
1, • • •• •• .
•• t
0 •
Depth Below Measuring Point (ft.)
-..l 0 ~ v-,
0
.j::,,.
0 VJ 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 i-3
12/25/07 ~
05/23/08 ,l;;l,..
I
10/20/08 i,,,,. ,l;;l,..
03/19/09 ~ 08/16/09 """ 01/13/10 ~ ""1
06/12/10 ~
11/09/10 ~ "'O
04/08/11 g.
09/05/11 0
02/02/12 < ~ ""1 07/01/12 i-3
11/28/12 ..... !3 04/27/13 ~
09/24/13 --? 02/21/14 C"
07/21/14 -!3 12/18/14 "'O '-' 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
02/14/21
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
5,558.77 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) Well
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
5,549.15 11/18/19 76.30 75.00
5,552.38 02/13/20 73.07 71.77
.....
8 I.O 0
Depth Below Measuring Point (ft.)
00 0
-..,l
0 0\ 0 lJl 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 N
10/20/08 ~
~ 03/19/09
08/16/09 -~
01/13/10 "1
~ 06/12/10 ~
11/09/10 "'C -04/08/11 ::r
0 09/05/11 -<
02/02/12 ~ "1
07/01/12 i-3 ....
11/28/12 a
04/27/13 ~ --09/24/13 ?
02/21/14 'a" -07/21/14 a
12/18/14 "'C --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
02/14/21
Water Levels and Data over Time
White Mesa Mill -Well TW 4-16
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 (hlw.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
5,556.90 11/18/19 71.75 68.38
5,556.65 02/10/20 72 68.63
Depth Below Measuring Point (ft.)
00 00 -.J -.J O'I O'I Ul Ul
Ul 0 Ul 0 Ul 0 Ul 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 1-3
12/25/07 ~
05/23/08 .a. I
10/20/08 ~
°' 03/19/09 ~ 08/16/09 -01/13/10 ~ "1
06/12/10 ~
11/09/10 ~ ~
04/08/11 -::r'
09/05/11 0
02/02/12 < ~
07/01/12 "1
1-3
11/28/12 ....
9 04/27/13 ~
09/24/13 --~ 02/21/14 CT'
07/21/14 e 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
02/14/21
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) Monitorin~ (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 05/01103 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
5,546.81 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
5,546.56 05/02/07 78.68 76.85
5,546.81 08/15/07 78.43 76.6
5,546.96 10/10/07 78.28 76.45
5,547.90 03/26/08 77.34 75.51
5,548.08 06/25/08 77.16 75.33
5,548.42 08/26/08 76.82 74.99
5,548.05 10/14/08 77.19 75.36
5,548.29 03/03/09 76.95 75.12
5,548.09 06/24/09 77.15 75.32
5,547.79 09/10/09 77.45 75.62
5,548.09 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
5,545.99 06/22/18 79.25 77.42
5,545.57 09/26/18 79.67 77.84
5,545.56 12/17/18 79.68 77.85
5,545.08 03/26/19 80.16 78.33
5,544.99 06/24/19 80.25 78.42
5,544.87 08/12/19 80.37 78 .54
5,544.70 11/19/19 80.54 78.71
5,544.57 02/13/20 80.67 78.84
00 .fa. 00 N
Depth Below Measuring Point (ft.)
00 0 -..J 00 -..J O'\ -..J .fa. -..J 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 ~ -12/25/07 ~ 05/23/08 I ~
10/20/08 N
03/19/09 ~ 08/16/09 -01/13/10 ~ ""1
06/12/10 ~
11/09/10 ~ ~
04/08/11 Er
09/05/11 0
02/02/12 < ~
07/01/12 ""1
~ 11/28/12 .... a 04/27/13 ~
09/24/13 --? 02/21/14 "r:::1"
07/21/14 -a 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
02/14/21
Water Levels and Data over Time
White Mesa Mill -Well TW4-18
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
5,585.83 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
5,585.15 05/02/07 56.13 53.98
5,586.47 06/24/08 54.81 52.66
5,586.30 08/26/08 54.98 52.83
5,585.21 10/14/08 56.07 53.92
5,584.47 03/03/09 56.81 54.66
5,584.35 06/24/09 56.93 54.78
5,583.88 09/10/09 57.40 55.25
5,584.43 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
5,570.39 11/19/19 70.89 68.74
5,570.03 02/10/20 71.25 69.10
00 0 -...l 0 0\ 0
Depth Below Measuring Point (ft.)
Vl 0 ~ 0 v.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 >--3
12/25/07 ~
05/23/08 ,l;;I,,.
I i,... 10/20/08 00
03/19/09 ~ 08/16/09 -01/13/10 ~ ""1
06/12/10 ~ ~ 11/09/10 "'C -04/08/11 =-
09/05/11 0
02/02/12 < ~ ""1 07/01/12 >--3
· 11/28/12 ....
9 04/27/13 ~
09/24/13 ,-..
? 02/21/14 O""
07/21/14 -9 12/18/14 "'C '-" 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
02/14/21
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 (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
5,543.59 02/27/07 87.80 85.94
5,544.55 05/02/07 86.84 84.98
5,558.97 08/15/07 72.42 70.56
5,559.73 10/10/07 71.66 69.8
5,569.26 03/26/08 62.13 60.27
5,535.47 06/25/08 95.92 94.06
5,541.41 08/26/08 89.98 88.12
5,558.45 10/14/08 72.94 71.08
5,536.90 03/03/09 94.49 92.63
5,547.76 06/24/09 83.63 81.77
5,561.48 09/10/09 69.91 68.05
5,548.14 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) Monitorin~ (blw.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
5,561.87 11/18/19 69.52 67.66
5,561.71 02/10/20 69.68 67.82
.....
8 \0 0
Depth Below Measuring Point (ft.)
00 0 -..J 0 0\ 0
U'I
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 >-3 10/10/06 ~ 03/09/07 .a;;...
08/06/07 I
""" 01/03/08 ~
06/01/08 ~ 10/29/08 -03/28/09 (">
"'1
08/25/09 0
01/22/10 ("> ~
06/21/10 -::r
11/18/10 0
04/17/11 ~ (">
09/14/11 "'1
02/11/12 >-3 ....
07/10/12 a
12/07/12 ("> --05/06/13 ?
10/03/13 O" -03/02/14 a
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
02/23/21
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
5,549.40 11/18/19 80.13 79.12
5,550.65 02/10/20 78.88 77.87
......
0 0 ~
Depth Below Measuring Point (ft.)
00 0 -...I 0 °'" 0
V,
0
.j:,.
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
10/08/20
03/07/21
~ ~ .,:.
I N Q
~ """ t'D ""l
~ t'D ~ """ =--0 < t'D ""l
~ .... a t'D -?
C" -a ~ "-'
Water Levels and Data over Time
White Mesa Mill -Well TW 4-21
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
5,555.91 11/18/19 83.44 82.29
5,561.05 02/10/20 78.30 77.15
\0 0 00 0 .....J 0
Depth Below Measuring Point (ft.)
°' 0 VI 0 ~ vJ 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
10/08/20
03/07/21
~ ~ ... I N ~
~ ;-
"1
t:,
~ ~ Er
0 < ~ "1
~ ... ~ ,-.,
?
-a-a ~ -
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
5,544.97 11/18/19 84.03 82.86
5,558.05 02/10/20 70.95 69.78
......
8 I.O 0 00 0
Depth Below Measuring Point (ft.)
-..J 0 0\ 0 VI 0
.i,..
0
(.J.)
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 ,&;...
I N
11/30/10 N
04/29/11 ~ ~ 09/26/11 ~ "1
02/23/12 0 ~
07/22/12 "O
12/19/12 ~
0 05/18/13 < ~
10/15/13 "1
03/14/14 ~ ... e 08/11/14 ~ --01/08/15 ?
06/07/15 a" -11/04/15 e "O
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
10/08/20
03/07/21
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 TW 4-23
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
5,533.51 11/18/19 73.86 72.26
5,533.26 02/10/20 74.11 72.51
-.l 0\ -.l ~
Depth Below Measuring Point (ft.)
-.l N -.l 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
""'3 05/25/11 ~
10/22/11 ,I;;.,,,
I N
03/20/12 ~
~ 08/17/12 """ ('D
01/14/13 lo'1
~
06/13/13 ('D
"CS """ 11/10/13 :r
04/09/14 0 < ('D
09/06/14 lo'1
""'3 ....
02/03/15 a ('D
07/03/15 ,.-..
?
11/30/15 -c::r
04/28/16 9
"CS
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
11/03/20
Water Levels and Data over Time
White Mesa Mill -Well TW 4-24
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
5,554.44 11/18/19 73.39 71.26
5,563.62 02/10/20 64.21 62.08
Depth Below Measuring Point (ft.)
\0 00 -.J 0\ Vl .j::,.. w N -0 0 0 0 0 0 0 0 0 0 0 0 0 0 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;:,..
I N
03/20/12 ,I;:,..
~ 08/17/12 !"I" ~
01/14/13 ""1
~
06/13/13 ~ "'C
11/10/13 ~
04/09/14 0 ~ ~
09/06/14 ""1
~ -· 02/03/15 e ~
07/03/15 -?
11/30/15 'r:::J"
04/28/16 a "'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
11/03/20
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) Monitorin; (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 05/29/09 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 TW 4-25
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
5,572.66 11/18/19 72.25 70.16
5,572.77 02/10/20 72.14 70.05
.....
N 0
.....
8
Depth Below Measuring Point (ft.)
00 0 0\ 0
.j::.
0 N 0 0
----------+-----+-------11..-i------+-----+ 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
03/20/12
08/17/12
01/14/13
06/13/13
11/10/13
04/09/14
09/06/14
02/03/15
07/03/15
11/30/15
04/28/16
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
,___ __ __. ___ __._ ___ __._ _________ _.__ ___ ......_ 11/03/20
""'3 ~ I N ~
~ ;-
"1
~ ~ "'O ;.
0 ~ ~ "1
""'3 ...
! -.. ?
'a" 9
"'O --
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
5,530.14 11/18/19 71.54 69.84
5,529.73 02/10/20 71.95 70.25
-..I
""" 0 0
-..I N 0 0
Depth Below Measuring Point (ft.)
-..I 0 0 0
°' 00
0 0
O'\ °' 8
i O'\ N 0 8 0
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:;.
I N
05/06/13 Q°'\
10/03/13 ~ -('D
03/02/14 "'1
~ ('D
07/30/14 "'O -=-
12/27/14 0 < ('D
05/26/15 "'1
~ ....
10/23/15 a ('D ,-.,
03/21/16 ?
08/18/16 'r:::1" -a
01/15/17 "'O --
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 TW4-27
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
5,529.12 11/18/19 78.82 77.07
5,529.29 02/10/20 78.65 76.90
I.O N 0 0
I.O 0 0 0
Depth Below Measuring Point (ft.)
00 00 0 0
00 a,
0 0
00 .j>,
0 0
00 N 0 0
00 0 0 0
.......
00 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 ""'3
07/30/14 ~ ~ I N .....:J 12/27/14 ~
05/26/15 ""'" ~ "'1
10/23/15 0 ~ "'O
03/21/16 ~
0 <
08/18/16 ~ "'1
""'3
01/15/17 ....
9 ~
06/14/17 -.. ?
C"
11/11/17 -9 "'O .._.,
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 TW4-28
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
5,569.87 11/18/19 47.13 43.65
5,569.89 02/10/20 47.11 43.63
VI 0
8
"""-VI
8
./
~
•
0
0
•
•
.
~
Depth Below Measuring Point (ft.)
"""-VJ VJ N N ,..... 0 VI O VI O VI o o o o o o 0 0 0 0 0 0
·~
0
0
•
•
' ••
• •
,
......
0 0 0
VI
8
0 0 0
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
09/26/20
~ ~ ,I::,..
I N oc
~ -~ "'1
~ ~ "Cl -=-0 -id ~ "'1
~ .... e ~ ---?
-r::J' -e "Cl ._,
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
5,529.23 11/18/19 76.81 73.33
5,529.10 02/10/20 76.94 73.46
-..J \0 g
-..J 00
8
Depth Below Measuring Point (ft.) ...J -..J -..J -..J -..J -..J 0\ V\ ~ vJ 8 g g g g
-..J -..J ~ .....
0 0 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
05/26/15 \C
~ 10/23/15 -~ '"1
03/21/16 ~ ~ ~ e,
08/18/16 0 < ~
01/15/17 '"1
~ ...
06/14/17 !3 ~ ,-..
11/11/17 ?
'a' -04/10/18 !3 ~ ,._,,
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 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) Monitoring (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
5,527.94 11/18/19 74.87 71.39
5,528.12 02/10/20 74.69 71.21
-..J 00
VI 0
-..J 00
8
Depth Below Measuring Point (ft.)
-..J -..J VI 0
-..J -..J
8
-..J
°' VI 0
-..J
°' 8
-..J Vl VI 0
-..J Vl
8
-..J ~
VI 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~ ~ 12/27/14 ,I:;;..
I ~ 0
05/26/15 ~ ....
10/23/15 ~ l"'1
0
03/21/16 ~ "" .... t:r"
08/18/16 0 < ~
01/15/17 l"'1
~ ...
06/14/17 a ~ -~ 11/11/17 .
er -04/10/18 a ~ '-'
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 TW4-31
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
5,528.02 11/18/19 76.56 73.08
5,528.30 02/10/20 76.28 72.80
00 0\ g
00 ,is.. g
Depth Below Measuring Point (ft.)
00 N 8
00 0 g
-..J
00
8
-..J 0\ 0 0
-..J ,is..
0 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
~
07/30/14 ~ ~ I tN 12/27/14 lo-
05/26/15 ~ ~ ~ "1
10/23/15 ~ ~ "'Cl
03/21/16 ~ =-0
08/18/16 < ~ "1
01/15/17 ~ ... !3 ~
06/14/17 --?
11/11/17 C" -!3
04/10/18 "'Cl '-"
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 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
5,556.86 11/18/19 54.98 53.34
5,557.04 02/10/20 54.80 53.16
u,
O'\
8
VI u,
0 0
u,
.j::a..
8
Depth Below Measuring Point (ft.)
u, w
8
u,
N 0 0
u, ......
8
u,
0
8
.j::a.. \0
8
.j::a..
00
8
.j::a..
-.l
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
04/29/20
09/26/20
1-3 .
~ I ~ ~
~ ;-
~
i:,
~ "'Cl g.
0 ~ ~ ~
1-3 ... = ~ ,-....
?
-c::r a "'Cl '-"
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
5,530.45 11/18/19 76.28 74.75
5,530.22 02/10/20 76.51 74.98
-..J -..J 8
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Depth Below Measuring Point (ft.)
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8
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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 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) Monitorin~ (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
5,528.30 11/18/19 75.04 73.30
5,528.18 02/10/20 75.16 73.42
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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
5,525.12 11/18/19 74.75 73.55
5,525.17 02/10/20 74.70 73.50
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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
5,559.28 11/18/19 57.31 55.90
5,559.32 02/10/20 57.27 55.86
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Water Levels and Data over Time
White Mesa Mill -Well TW4-37
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
5,560.14 11/18/19 71.71 69.99
5,558.17 02/10/20 73.68 71.96
..... N 0 8
-8 8
Depth Below Measuring Point (ft.)
00 0 8
0\ 0
8
~ 0 0
N 0
8
0
8
1-------+------+-------+-------+----+------1-12/27/14
07/15/15
01/31/16
08/18/16
03/06/17
09/22/17
04/10/18
10/27/18
05/15/19
12/01/19
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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) Monitorin_g (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
5,571.90 11/18/19 58.09 56.92
5,571.67 02/10/20 58.32 57.15
OZ/81/90 -.-----.,.----.--------,-----.------.-----.------,
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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
5,549.98 11/18/19 79.58 78.84
5,548.39 02/10/20 81.17 80.43
61/IO/Zl
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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) (blw.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
5,526.43 11/18/19 71.15 69.23
5,525.57 02/10/20 72.01 70.09
,-._
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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
5,536.69 11/18/19 78.27 76.62
5,538.67 02/10/20 76.29 74.64
,-....
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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
5,527.13 11/18/19 67.57 65.26
5,526.83 02/10/20 67.87 65.56
,-....
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i 00 l,C) 0 r-N r-\0 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 TW4-15 (formerly MW-26)
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 1307110 3370 4947411.4 l.6673E+l0 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 l.7 47780 930 180847.3 168187989 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
QI 2009 90710 2200 343337.4 755342170 755 1.7 52970 950 200491.5 190466878 190 0.4
Q22009 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
Ql 2010 68125 1600 257853.l 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 79859.1 1900 302266.7 574306718 574 1.3 63850 2200 241672.3 531678950 532 1.2
Q4 2010 90042.2 1500 340809.7 511214591 511 I.I 60180 970 227781.3 220947861 221 0.5
Ql 2011 76247.6 1700 288597.2 490615182 491 1.1 55130 450 208667.1 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 248364.1 178822174 179 0.4
Q4 2011 89735.0 1600 339647.0 543435160 543 l.2 50191.3 1800 189974.1 341953327 342 0.8
QI 2012 90376.4 1500 342074.7 513112011 513 1.1 31440.1 2400 119000.8 285601868 286 0.6
Q2 2012 90916.5 1400 344118.8 481766269 482 1.1 26701.2 3000 101064.1 303192353 303 0.7
Q3 2012 91607.0 1500 346732.5 520098743 520 l.l 25246 3100 95556.1 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
Ql 2014 69833.8 1390 264320.9 367406097 367 0.8 23263.l 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 l.O 19355.6 2680 73260.9 196339335 196 0.4
Ql 2016 90882.l 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 sos I. I 27489.9 1230 104049.3 127980604 128 0.3
Q42017 106679.8 1320 403783.0 532993617 533 1.2 26445.8 2570 100097.4 257250197 257 0.6
Table G-1
---------------·-------
MW4 TW4-15 (formerly MW-26) -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 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.l 1360 91525.5 124474630 124 0.3
Q4 2019 99220.8 1370 375550.9 514504705 515 1.1 22384.8 1390 84726.5 117769791 118 0.3
QI 2020 102597.0 1230 388329.6 477645370 478 1.1 24107.0 llOO 91245.0 100369495 100 0.2
Totals 6359573.59 104.3 2836255.3 36.7
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
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)
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 1100 1196362.8 1315999080 1316 2.9 70360 5200 266312.6 1384825520 1385 3.1
Q42007 334350 l!OO 1265514.8 1392066225 1392 3.1 63630 9000 240839.6 2167555950 2168 4.8
QI 2008 304784 1800 1153607.4 2076493392 2076 4.6 66520 13000 251778.2 3273116600 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 1100 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 1.1854E+IO 11854 26.l
QI 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
Q3 2011 141542.6 970 535738.7 519666578.8 520 I.I 72311.2 6800 273697.9 1861145666 1861 4.1
Q420ll 147647.2 2200 558844.7 1229458234 1229 2.7 72089.3 7900 272858.0 2155578204 2156 4.8
QI 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
QI 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 329460.1 8100 1247006.5 10100752476 10101 22.3. 19731 26800 7468 l.8 2001473178 2001 4.4
Q4 2013 403974 942 1529041.6 1440357178 1440 3.2 19280.2 15700 72975.6 1145716245 1146 2.5
QI 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
QI 2015 60553.0 4660 229193.l 1068039869 1068 2.4 15744.7 19900 59593.7 1185914421 1186 2.6
Q2 2015 75102.8 1570 284264.l 446294633.9 446 l.O 18754.1 17600 70984.3 1249323126 1249 2.8
Q3 2015 116503.9 7860 440967.3 3466002675 3466 7.6 17657.3 17000 66832.9 I 136158969 1136 2.5
Q4 2015 112762.7 7840 426806.8 3346165465 3346 7.4 15547.4 17000 58846.9 1000397453 1000 2.2
QI 2016 116597.0 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 392160.1 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
Q42017 108891.2 129 412153.2 53167761.77 53 0.1 14271.0 11600 54015.7 626582526 627 1.4
Table G-1
-. ·-·. -·--·--·~·· ~-... ~-~-~····-~-··-~----··--~--· -~·-···~-~-· ., --· --··· --
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 I.I
Q4 2018 107197.4 5270 405742.2 2138261178 2138 4.7 12841.1 9500 48603.5 461733494 462 1.0
QI 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
Q4 2019 98806.8 551 373983.7 206065039.6 206 0.5 8317.69 8790 31482.5 276730794 277 0.6
QI 2020 96857.9 8720 366607.2 3196814361 3197 7.0 9505.05 14300 35976.6 514465584 514 I.I
Totals 19125686.73 430.9 2469207.92 291.3
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-4 TW4-22
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
Q42007 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
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
Ql 2011 73360.0 1800 277667.6 499801680 500 l.l NA NA NA NA NA NA
Q2 2011 80334.6 1700 304066.5 516912983.7 517 I. I 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
QI 2012 101616.8 1200 384619.6 461543505.6 462 l.O NA NA NA NA NA NA
Q2 2012 87759.1 1500 332168.2 498252290.3 498 l.l NA NA NA NA NA NA
Q3 2012 80006.0 1600 302822.7 484516336 485 l.l 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 1256 l 06224.1 1256.1 2.8
Qi 2014 58992.9 1260 223288.1 281343039.4 281 0.6 24532.0 12100 92853.6 l 123528802.0 1123.5 2.5
Q2 2014 60235.3 1220 227990.6 278148544.8 278 0.6 24193.9 12400 91573.9 l 135516502.6 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
Qi 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. l 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
QI 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.l 5840 83815.4 489482044.0 489.5 I. I
Q4 2016 31656.0 1430 119818.0 171339682.8 171 0.4 23646.8 3370 89503.1 301625575.1 301.6 0.7
QI 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 I. I
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
.._ --• """""' ~ _.,.._.._.,.._.._.,.._.,, '-"O -•••'-''""' '-10 IOI .. , .... 001v, ,...,..., .......... a...,. ....... , • ._ ·-···-'-'' o• WI .. _., 0 .. 0101 ,,_...,.
'" . TW4-4 TW4-22
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)
QI 2018 23103.4 1160 87446.4 101437788 101 0.2 23982.8 4530 90774.9 411210287.9 411.2 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.J 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
Q4 2019 14399.8 1140 54503.2 62133697 .02 62 0.1 24052.5 3820 91038.7 347767881.8 347.8 0.8
Qi 2020 14439.2 1100 54652.4 60117609.2 60 0.1 24746.l 3910 93664.0 366226195.0 366.2 0.8
Totals 2119549.7 25.4 691876.8 41.4
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-24 TW4-25
I 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
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
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
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 216984.1 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
Ql 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
Ql 2017 99117.4 18.3 375159.4 6865416.3 6.9 0.015 161.2 1.15 610.1 701.7 0.0 0.0
Q2 2017 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
--··-· .. .__._. ......... ~·-·· ..,. -····,· ........ -·-··· ,._ ..... _ ................................................ , .........................
TW4-24 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 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 0.018 114458.2 0.0 433224.3 0.0 0.0 0.0
QI 2019 97701.0 28.l 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
Q4 2019 102211.02 43.3 386868.7 16751415.2 16.8 0.037 85928.53 0.0 325239.5 0.0 0.0 0.0
Ql 2020 86344.4 61.7 326813.5 20164391.6 20.2 0.044 85049.5 0.0 321912.2 0.0 0.0 0.0
Totals 3356779.3 1.065 3090929.0 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)
QI 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
Q2 2011 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
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
Ql 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 l 14.4 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 I 07035405.6 107.0 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 I 56172362. 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.l 68552633.1 68.6 0.15 17487.4 1780 66189.8 l 17817860.0 l 17.8 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
Ql 2017 16931.8 519 64086.9 33261081.9 33.3 0.07 19869.7 1570 75206.8 118074698.8 118.1 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 I 05591795 .3 105.6 0.23
Table G-1
UU.J\.VJ I"° -UJ\,,,,IUIU\..IV JJ VI _,,,v.1 v 1v 1111 ,,v111u.-vu UIIU J. "-"Lil.LI .-V I.UIII\,,,, ' ... ,. .... \.IJ I ua,1 _,....._.
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)
01 2018 12505.7 70.4 47334.l 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 0.01 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.l 894 36843.6 32938150.2 32.94 0.07 14106.9 797 53394.6 42555509.4 42.56 0.09
Q4 2019 9184.3 1070 34762.6 37195955.8 37.20 0.08 14220.9 934 53826.1 50273583.5 50.27 0.1 I
QI 2020 8796.7 1190 33295.5 39621656.3 39.62 0.09 13162.1 1880 49818.5 93658871.2 93.66 0.21
Totals 321422.0 2.55 377821.2 4.69
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-11 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
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
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
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
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
Ql 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q22014 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
Ql 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
QI 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
QI 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
... .._ ..... ......_..__ ........ ~ ........ ............... .., •••• .._ ............ _,. __ -.. ............ -••• '-4" ................... _.._ ..........................
TW4-11 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)
Ol 2018 2571.0 3090 9731.2 30069516.2 30.l 0.07 117832.0 421 445994.l 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
Q4 2019 1983.9 3250 7509.l 24404449.9 24.40 0.1 116167.55 794 439694.2 3491I7176.3 349.1 0.8
QI 2020 1947.4 2990 7370.9 22039017.9 22.04 0.0 106622.0 844 403564.3 340608275.8 340.6 0.8
Totals 67699.1 l.60 2178452.0 9.09
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
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 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
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
Q22013 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
Q22014 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
Ql 2015 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2015 29206.0 30200 l 10544.7 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
04 2015 111737.5 19500 422926.4 8247065531.3 8247.1 18.2 NA NA NA NA NA NA
Ql 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.l NA NA NA NA NA NA
Q3 2016 98377.6 15900 372359 5920511534.4 5920.5 13.l 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.l 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 5573.1 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
................ , ' -_.Le • ._..._,._..,, ...... _,,,._,, _., .... , 000 ''-""''''"' ._. .............. 0 ...,,...._. '""i'0 .... 00&-~-'• LA~-· ........ LI
. -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)
01 2018 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 IO.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 I 036379979.4 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.I 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
Q4 2019 66732.4 13100 252582.l 3308825955.4 3308.8 7.3 51808.6 1650 196095.6 323557659.2 323.6 0.7
Ql 2020 65554.2 12000 248122.6 2977471764.0 2977.5 6.6 43169.3 812 163395.8 132677390.0 132.7 0.3
Totals 1714259.9 228.1 630111.3 23.7
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-40 TW4-41
Total Total Total Total Total Volume
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
Q42007 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 [4.8 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
QI 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
QI 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
Q42011 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
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA 13.7 634286.1
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.J 950505.6
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA 10.3 990119.8
QI 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
Ql 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
QI 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
QI 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.l
Q4 2017 NA NA NA NA NA NA NA NA NA NA NA NA 16.9 841953.7
Table G-1
-... . . ---·--· -·-.-·· .. ••••-•-·••-••••• ••-•••n., ·---••-• ..,._. ·-···--· .. -·-· ....... -
TW4-40 TW4-41
Total Total Total Total Total Volume
Pumped Pumped Total Total Pumped Pumped Total Total Total Pumped
(hlarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds) (pounds) (gallons)
012018 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 l 77023110.1 177.0 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 l 67438543.9 167.4 0.37 24045.6 1190 91012.6 108304989.2 108.3 0.2 18.3 794827.4
Q4 2019 108281.89 314 409847.0 128691943.4 128.7 0.28 21186.4 1410 80190.5 l 13068638.8 113. l 0.2 13.0 844887.9
Ql 2020 102021.5 364 386151.4 140559115.2 140.6 0.31 17289.9 1200 65442.3 78530725.8 78.5 0.2 18.9 802209.2
Totals 408480.3 1.14 273696.3 3.0 1205.1 45613320.2
Table G-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 TW4-0l TW4-02 TW4-ll TW4-21 TW4-37 TW4-39 TW4-40 TW4-41 Quarter
Ouarter* (lbs.) (lbs.) (lbs.) (lbs,) (lbs.) (lbs.) (lbs.). (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) Totals (lbs.)
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
03 2007 2,2 0.8 2.9 3.1 NA NA NA NA NA NA NA NA NA NA NA NA 9.0
Q4 2007 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 03 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
QI 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 26.1 NA NA NA NA NA NA NA NA NA NA NA NA 49.4
OJ 2010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 4.5
02 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 1.3 1.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA NA NA NA 10.6
Q420l0 l.l 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA NA NA NA 17.9
QI 201 I I.I 0.2 12.9 9.6 I.I NA NA NA NA NA NA NA NA NA NA NA 24.9
Q2 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 201 I 1.2 0.4 I.I 4.1 1.2 NA NA NA NA NA NA NA NA NA NA NA 8.1
Q4 2011 1.2 0.8 2.7 4.8 1.4 NA NA NA NA NA NA NA NA NA NA NA 10.8
01 2012 l.l 0.6 0.8 7.0 1.0 NA NA NA NA NA NA NA NA NA NA NA 10.6
02 2012 I.I 0.7 0.7 6.9 I.I NA NA NA NA NA NA NA NA NA NA NA 10.4
Q3 2012 I.I 0.7 1.4 2.4 I.I NA NA NA NA NA NA NA NA NA NA NA 6.6
Q4 2012 0.9 0.3 2.0 32 0.8 NA NA NA NA NA NA NA NA NA NA NA 7,2
Ql 2013 0.9 0.4 7.4 2.8 0.7 1.5 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
Q3 2013 0.9 0.6 22.3 4.4 0.7 2.1 0.1 0.0 NA NA NA NA NA NA NA NA 31.1
04 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
01 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
02 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
042014 0.8 0.4 7.1 3.2 0.6 2.5 0.04 0.0 NA NA NA NA NA NA NA NA 14.6
Ql 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
Q2 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 0.03 0.0 0,21 0.24 0.03 0.29 18.8 NA NA NA 33.4
04 2015 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
QI 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
02 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
03 2016 1.0 0.5 5.2 2.4 0.6 I.] 0.01 0,0 0.15 0.26 0.08 0.42 13.l NA NA NA 24.7
04 2016 1.0 0.4 5.8 2.3 0.4 0.7 0.017 0.0 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 I.I 0.015 0.0 0.07 0.26 0.08 0.27 14.6 5.6 NA NA 27.2
Q2 2017 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 I. 1 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 1.4 0.2 0.9 0.014 0.0 0.07 0.23 0.06 0.49 I 1.3 0.3 NA NA 16.9
QI 2018 1.2 0.3 2.4 1.8 0.2 0.9 0.020 0.0 0.01 0.10 O.o? 0.41 9.1 1.4 NA NA 18.0
Q2 2018 I.] 0.4 2.8 1.3 0.2 0.6 0.022 0.0 0.09 0.13 0.06 0.52 10.l 2.0 NA 0.9 20.1
Q3 2018 1.0 0.4 1.7 I.I 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
04 2018 1.1 0.3 4.7 1.0 0.1 0.5 O.Dl8 0.0 0.06 0.11 0.06 0.59 9.7 2.0 NA 0.4 20.8
QI 2019 I.I 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
Q2 2019 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 26.1
Q32019 0.9 0.3 5.6 1.2 0.1 0.7 0.014 0.0 0.07 0.09 o.o 0.5 6.7 1.3 0.37 0.2 18.3
Q4 2019 l.l 0.3 0.5 0.6 0.1 0.8 0.037 0.0 0.08 0.11 0.1 0.8 7.3 0.7 0.28 0.2 13.0
Ql 2020 I.I 0.2 7.0 I.I 0.1 0.8 0.044 0.0 0.09 0.21 0.0 0.8 6.6 0.3 0.31 0.2 18.9
Well Totals 103.3 36.5 423.9 290.2 25.3 40.6 1.021 0.0 2.46 4.48 1.55 8.34 221.6 23.4 0.83 2.9 1205.1
* QI 2007 represents the cumulative 1otnl prior to and lnolud.in& QI 2007.
Table G-3 Well Pumping Rates and Volumes
Volume of Water Pumped
Pumping Well Name During the Quarter (gals) Average Pump Rate (gpm)
MW-4 102597.0 4.0
MW-26 24107.0 10.9
TW4-19 96857.9 17.8
TW4-20 9505.1 4.7
TW4-4 14439.2 16.6
TWN-2 32230.0 17.0
TW4-22 24746.1 17.8
TW4-24 86344.4 16.0
TW4-25 85049.5 11.0
TW4-0l 8796.7 12.6
TW4-02 13162.1 15.9
TW4-11 1947.4 16.5
TW4-21 106622.0 16.9
TW4-37 65554.2 17.9
TW4-39 43169.3 17.9
TW4-40 102021.5 18.0
TW4-41 17289.9 5.7
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01 2018
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01 2019
02 2019
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L~OG 170
L~OG 80
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Chloroform Removed (Pounds)
0 p 0 p 0
0 ...... f\) c.:> :i:. 0 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
032018
04 2018
01 2019
02 2019
03 2019
04 2019
01 2020
p
(11 0
0 0)
0
0
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p
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9~0G 170
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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
04 2019
01 2020
Chloroform Removed (Pounds) ...... ......
N ~ O> 00 0 N o o o o o o
......
~ 0
......
O> 0
......
00 0
N 0 0
~ .i::,.
I vJ ......
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(spunod) paAOW8l:f WJO!OJ014:J
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c:i
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6Wl ~O
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LWlPO
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-en ..c -.._
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I -.;:t"
3: I-
0 '<:I" 0
IO ('I)
0
0 ('I)
0
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0
0 IO O IO C\I ..... ..... 0 o o o o (spunod) paAOWact WJOJOJOIL.18
0 0
0
oiac:: ~o
6WcPO
6Wc£0
6~0c cO
-en .c ::=-...
Q) t: ~ :J a
>, .c
"C Q) > 0
E
Q) a:
E
0 -0 ...
0
..c (.) -0
en en ~ ~
,-
s:::t" I s:::t" ~
0 co 0 ~ ~ ~ ~ N ~ 0 0 0 0 0 0
(spunod) paAOW0\:I WJO!OJOILI:)
0 0
OGOG ~O
6~0G 170
6~0G 80
6~0c cO
6 ~Oc ~O
swivo
8~0G 80
8~0G GO
Volume Pumped by Quarter (gal.)
12000000.0 ~-----------------------------
10000000.0 ;---------------------------------------------
8000000.0 .l-1--------------------------------------------
6000000.0 .i....11--------------------------------------------
4000000.0 ..l-.1--------------------------------------------
2000000.0 ;-------------------------------------------------
0.0 -1--..................... ---.-.....,....~~~~---.----.---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 Ql
2007 2007 2008 2008 2009 2009 2010 2010 201120112012 2012 2013 2013 2014 2014 2015 2015 2016 2016 2017 2017 2018 2018 2019 2019 2020
1400000
'. ~ MW-04 Volume Pumped by Quarter (gal.)
1200000
1000000
800000
600000
400000
200000 A
_......._j i\_ ~ ------. _.... . -....._. ---.... . ~ -..... .... ~ --..,. ... -.,,.. .... ,. ..... -. . ... ... ...... ... . . . "' .....
0 -i I I I I I I I I 1 i I I I I I I I I I I I I I I I i ' I f I I I " r I I I
~ ~ ~ ~ ~ ~ ~ ~ y y ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ '\,<::5 ,-ss '\,<::5 ,-ss ,-ss '\,<::5 '\,(:) ~ '\,(:) ,-s:> '\,(:) '\,(:) '\,(:) ,-s:> ~ '\,(:) ,-s:> '\,(:) '\,(:) ~ '\,(:) ,-s:> '\,(:) '\,(:) '\,(:) '\,(:) '\,(:)
~~&~~~~~&~~~~~~~~~~~~~~~~~~
Ql 2007 represents the cumulative total prior to and including Ql 2007.
I-' I-' N N w U"I 0 U"I 0 U"I 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
I I Ql 2015
Q2 2015
Q3 2015
Q4 2015
Ql 2016 i I I I t I I -I :e
02 2016 I I I I ~I I I ~ I
0 ~
03 2016 I I I I< I I I ~ -04 2016 I I I t I I I C
3
012011 I I I I ~· I I I n,
"'C
C
02 2011 I I I t I I 3
"C
03 2011 I I I I ~ I I I n, a.
C"'
04 2011 I I I F l I I 1<
0
012018 I I I ~ I I I I C
QI .,
" 02 2018 I I I # I I I I n, ., -Q3 2018 I I fl I I I I 'm -• -Q4 2018
Ql 2019
Q2 2019
Q3 2019
Q4 2019
Ql 2020
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 2015
Q2 2015
Q3 2015
Q4 2015
Ql 2016 i I I I I/ I I -I ~
02 2016 I I I I I> I I .i::-I
0
N
03 2016 I I I I < I I I ~
04 2016 I I I I 't I I -C
3
012011 I I I I t I I tD
i:,
C
02 2011 I I I I f I I I 3
"tJ
03 2011 I I I I >I I I tD
Q.
C"'
04 2011 I I I I , I I I <
0
012018 I I I f I I I C
Q)
::i.
02 2018 I I I II I I I tD .., -03 2018 I I I i I I I OQ
Q) -• -Q4 2018
Ql 2019
Q2 2019
Q3 2019
Q4 2019
Ql 2020
.... .... N .i:,. CTI 00 0 N 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
Q2 2010
Q3 2010
Q4 2010
Ql 2011
Q2 2011
Q3 2011
Q4 2011
Ql 2012
Q2 2012 -I
Q3 2012 =:
Q4 2012 .,::.
I
Ql 2013 0 .,::.
Q2 2013 ~ Q3 2013 -Q4 2013 C
Ql 2014 3
tD Q2 2014 "'tJ
Q3 2014 C
Q4 2014 3
Ql 2015 "C
tD
Q2 2015 C.
Q3 2015 C"'
Q4 2015 <
0 Ql 2016 C
Q2 2016 DJ .,
Q3 2016 ,..
tD
Q4 2016 ., -Ql 2017 OQ
Q2 2017 DJ -.
Q3 2017 -
Q4 2017
Ql 2018
Q2 2018
Q3 2018
Q4 2018
Ql 2019
Q2 2019
Q3 2019
Q4 2019
Ql 2020
.... ....
Iv .i,. O'I 00 0 Iv 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 2015
Q2 2015
Q3 2015
Q4 2015
Ql 2016 i I /I I I I I -I ~
02 2016 I I >I I I I I .a::. I a-,a.
Q3 2016 I I '( I I I I I a-,a.
~
Q4 2016 I I t I I I I I -C
3
012017 I I t I I I I I ,,, .,,
C
02 2017 I I t I I I I 3
"C
Q3 2017 I I t I I I I I ,,,
C.
C"'
04 2017 I I f I I I I I <
0
012018 I I t I I I I C
Q,)
~
02 2018 I I I I I I I I ,,, .., -Q3 2018 I Ii I I I I I OQ
Q,) -• -. -Q4 2018
Ql 2019
Q2 2019
Q3 2019
Q4 2019
Ql 2020
MW-26 Volume Pumped by Quarter (gal.)
1000000 ~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
I•
900000 ++~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
800000 ++~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
700000 ...j.....11,--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
600000 +-11--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
500000 4-----~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
400000 4------~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
300000 +--I--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
200000
100000 4-------~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
~ _....... ...........
~ ~
0 -+-..---,---.---.---,-.--r--r--.--r--,-.--r-r----r--.--,---.-,r-T---,---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 Ql
2007 2007 2008 2008 2009 2009 2010 2010 201120112012 2012 2013 2013 2014 2014 2015 2015 2016 2016 2017 2017 2018 2018 2019 2019 2020
Q 1 2007 represents the cumulative total prior to and including Q 1 2007.
8000000
7000000
6000000
5000000
4000000
3000000
2000000
1000000
0
TW4-19 Volume Pumped by Quarter (gal.)
-~~y\ ~ . ~ . -
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 Ql
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 2020
Q 1 2007 represents the cumulative total prior to and including Q 1 2007.
700000
600000
500000
400000
300000
200000
100000
0
TW4-20 Volume Pumped by Quarter (gal.)
.
\
~-
_......
j T
T -V ---------T T ,.. --' ' . . . . 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 Ql
2007 2007 2008 2008 2009 2009 2010 2010 201120112012 2012 2013 2013 2014 2014 2015 2015 2016 2016 2017 2017 2018 2018 2019 2019 2020
Ql 2007 represents the cumulative total prior to and including Ql 2007.
N .i,. °' 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0
l I I I Q2 2015
Q3 2015
Q4 2015
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
Q4 2019
Ql 2020
..... ..... 1--' 00 0 N .i,.
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0
I
.....
°' 0 0 0 0
0
~ ~ I
N ....
a--C
3
tD
"'O
C
3
"C tD
C.
C"' <
0 C
QJ
~ tD
""I -CJQ
QJ -• -
.... .... N N w u, 0 u, 0 u, 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
b b b b b b b
Ql 2013
Q2 2013
Q3 2013
Q4 2013
Ql 2014
Q2 2014
Q3 2014
Q4 2014 i I I I I J I I -f :E Ql 2015 I I I I I < I I ~ I
Q2 2015 I I I I I ' ' I N
N
Q3 2015 1 I I I I /I I < 0
Q4 2015 -C
Ql 2016 1
I I I I C). I
3
tD
Q2 2016 .,,
C
Q3 2016 I I I I I ~ I I 3
Q4 2016 I I I I I " I I "C tD
Ql 2011 I I I ' I t I I a.
C"
Q2 2011 I I I I I \I I <
Q3 2011 I I I I I >I I J::J
C
Q4 2011 I I I I I f I I QJ
""' ....
Ql 2018 I I I I I I I '
tD
""' -Q2 2018 I I I I I ~ I I OQ m
Q3 2018 1 I I I '" I I -• -Q4 2018
Ql 2019
Q2 2019
Q3 2019
Q4 2019
Ql 2020
.... .... 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 0 0 0 0 0 0
t-Ql 2013
Q2 2013
Q3 2013
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Laboratory Analytical Reports
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2020
Lab Sample ID: 2002488-009C
Client Sample ID: MW-04_02192020
Collection Date: 2/19/2020 1315h
Received Date: 2/21/2020 1240h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 1209h
Units: µg/L Dilution Factor: 20 Method: SW8260D
Compound
Chloroform
CAS
Number
67-66-3
Reporting
Limit
20.0
Analytical
Result
1,230
Qual
--------------
Phone: [phone] Surrogate -------Units: µg!L CAS Result Amount Spiked %REC Limits Qual --------
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
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
l,o70
977
933
976
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratmy Director
Analyzed: 2/24/2020 1302h
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
1,000 107 72-151
1,000 97.7 80-152
1,000 93.3 72-135
1,000 97.6 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 54.3 50.00 109 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.6 50.00 101 80-152
Surr: Dibromofluoromethane 1868-53-7 50.3 50.00 101 72-135
Surr: Toluene-d8 2037-26-5 49.9 50.00 99.8 80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 31 of 50
All analyses applicable to I.he WA. SDWA. ti,nd RCRA are perfom1ed in accordance to NELAC protocols. PC'f11ncn1 SAmpJinK ihfo1m:ulon is located on the auached COC. Confidmtiul Business ln(ornuuoo: This repon is prm•ided ror1htS"~clU$l\'e u,;e or the
~ddressee. PriYile~es o~ sub ... seq~tnl ~~ of lhc r~~11c of this .co~pruty or any ~~ber of its slaff, or reproductiu!! ~r 1his ttpor; In ~un?Ctdo1~ ,vith the ~~·ertise~ent, P~?moti~1 ~r !nle of~·. Fd~cl urp~~cn, ~r in ~nn~c!ion w!lh lh~ r~·J11:'blic:uion o(this repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-009
Client Sample ID: MW-04_02192020
ANAL vr1 c AL LAoo RAT oR I es Collection Date: 2/19/2020 1315h
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: 2/21 /2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Tanner Holliday
Date Method Reporting
Analyzed Used Limit
3/3/2020 2005h E300.0 1.00
2/21 /2020 1514h E353.2 0.100
Analytical
Result Qual
48.1
6.22 ----
Report Date: 3/9/2020 Page 14 of 50
All onnl)~CS 11ppllcnblc to th1>C'WA. SDWA.1111d RCRA ore p,rrom .. •d 1n ""°"'dM« to NEI..AC: protocol~ P<11incn1>1nlpllni: nfonn,llon s locolcd '"' li101111nthro CO conndcnuol B1111nQ1 Tnformation1 Thi, n:pon 11 pro1idro foqhc o."lu<i1'e 111Cori1,.,
!dd~ Prhi.le~es of 1u~s1..'tl~~n, ~~ cr,ho ~~·~ui or1hl1501!1JNU\'' or M~' 1~1~1bcrorh11 6,lt\lT, or 1eprochtt1l°!? e!thii rcpot; in ... con!wcuon .. with the ~~-eni1i,monl. P~?nlOII~\ ~ anlc or~~:~roth!'t or pr.~1 ~r 111 ~nn~!ion ,,~1h th? r;p~bJlcmioo or 1h s ttporl
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2002488-007C
Client Sample ID: TW4-01_02192020
Collection Date: 2/19/2020 1324h
Received Date: 2/21/2020 1240h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 1130h
Units: µg/L Dilution Factor: 20 Method: SW8260D
Compound
Chloroform
CAS
Number
67-66-3
Reporting
Limit
20.0
Analytical
Result
1,190
Qual
Phone: [phone] Surrogate ---------------Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
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
1,070
1,010
943
984
--The reporting limits were raised due to high analyte concen/rafions.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1222h
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
1,000
1,000
1,000
----
107 72-151
101 80-152
94.3 72-135
98.4 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 53.2 50.00 106 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.6 50.00 101 80-152
Surr: Dibromofluoromethane 1868-53-7 49.5 50.00 99.0 72-135
Surr: Toluene-dB 2037-26-5 49.2 50.00 98.5 80-124
# -This compound exceeded {high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 29 of 50
All analyses ~pplicable to lheCWA, SOWA, Md RCRA are performed in accordance 10 NELAC prolocols .. P..:ninenl s1mplin¥, in(ormn!i,on is located on the attached COC. Conlid~Jilial Owinc-ss Infarma1fon This report is provided ror 1110 exclusi,·e use of1he
~dressee. PnY1lc~es of isu~sc~~cnl ~~e of the •!~~Nor lhis .con;tp;iny or any ~mber of ils slaff, or rq,todutli<I!~ ?.f tJ1is ~po'! in ~°"!1ecuon. with the a~~·enise~enl, p~~moti~, ~c ~c of !I'S: ~d~ct o, P~?'°~s., ~r in ~nn~~.tion w!lh th~ r~·p,.ablicaiion of 1his report
INORGANIC ANALYTICAL REPORT
3440 South 700 West
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-007
Client Sample ID: TW4-0l_02I92020
Collection Date: 2/19/2020 1324h
Received Date:
Analytical Results
Compound
2/21/2020 1240h
Units
Date
Prepared
3alt Lake City, UT 84119 Chloride
Nitrate/Nitrite (as N)
mg/L
mg/L
Date
Analyzed
3/3/2020 I 93 1 h
2/21/2020 I 5 I 2h --------------------
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
Used
E300.0
E353.2
Reporting
Limit
l.00
0.100
Analytical
Result
47.5
4.67
Qual
-------------------
Report Date: 3/9/2020 Page 12 of 50
All analyses applicable to tho CWA. SDWA. and RCRA ore perfonned ln nc<ord!lnce to NELAC pn,tOC<>li. P,·~lnc,11 s11mpllny informBllon is located on the ounched COC. Co11lidcnliol lluim<,ss lnformolion: This ropon is prol'ided for the exclusive use of the
~ddressee. Pridle~es o;su~"lic<1~n1 ~e of 1he ~~1e or ll~is .co1~pnny or rww 1~1!1bcr or its slnfT, or rq>f'O!.hM:ti~! ~ \hts ropo~ ln ~on~ac(i~ with the o~~·ertise~enl. P~?moti~ '?" ~~I! of!"~\ 1.,rodi~ct or P~?c~s, ~r in ~nn!c~ion w!th th~ r!~p~blicotion or this repor\
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2020
Lab Sample ID: 2002488-006C
Client Sample ID: TW4-02_02192020
Collection Date: 2/19/2020 1305h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 111 Oh
Units: µg/L
Compound
Chlorofonn
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 1,880
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0 5,360
460-00-4 5,070
1868-53-7 4,750
2037-26-5 4,950
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1201 h
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
5,000
5,000
5,000
107 72-151
101 80-152
95.0 72-135
99.0 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 53.9 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.7 50.00 103 80-152
Surr: Dibromofluoromethane 1868-53-7 50.6 50.00 101 72-135
Surr: Toluene-dB 2037-26-5 50.4 50.00 IOI 80-124
#-This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 28 of 50
All amilyses applicable 10 1hc CWA. SOWA. and RCRA arc perfom1ed in accordance to NELAC J)(Otoculs. Ptninm1 s1unphng in(Ofl)lP.tion is localed on the attached COC. Coond~tl11I BUS1n~s Information: This report is provided for the ~c.lu:Si\·e we of1he
~ddressee. PriYile~es Of suh;cq~s:nt ~t, or lht ~~!10 or1bis _co~pany or any ~mber or its sl3IT, or re1uoducl1~ ~f this relJO'!_ tn.~on!1cctlon_ \\·ilh the ~~·ertise~enl, P~?moli~ "!s.ilo r,f ?'!J F~cl or P~?Cess, ~r in ~M:C~ion \\'!lh th~ r~-p~blicntlOh or this report
3440 South 700 West
;alt Lake City, UT 841 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: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-006
Client Sample ID: TW4-02_02192020
Collection Date: 2/19/2020 1305h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride
Nitrate/Nitrite (as N)
mg/L
mg/L
Date
Analyzed
3/3/2020 1807h
2/21/2020 1511h --------------------
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 42.1
E353.2 0.100 6.07
Report Date: 3/9/2020 Page 11 of 50
All onnli·, .. D{lphcoblo 10 1hc WA, SOWA. ond RCRA 11rc pc,fom,cd in 1><cordonco 10 NELAC protocols. rcrtlntlll "'"l~IIIJ: nr()fn»I o,, , loc•lod o,, ~•• •uochcd CO (;wi\don1lol Bill n.,. lnfon1»1io11: Tiols r.:pon Is ,,ro,idod for 11,c osclu!W< ,~,. of the
nddt'C:SSC'Cr Prhitege:s orsub.iequou useor1f.cnM10 of1his comp1u~· or ony member orilS ~,orr, o, rC1uoduccion art.his ,opo,1 in connoclioo "ilh ,ho tK1,-crUsemen11 prorno1i0t, o, ,~coran~· product ot pt'OCC'$S, or in c:ono,ct on wnh 1'1e rc-publit41lon or this report . . . ... . .. .... . . -..... . . . ... . .. . . . . .... . .. . . "'. . .....
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-002C
Client Sample ID: TW4-03_03172020
~ ANA1.vT1 c A1 , Ano n,r o a,Fs Collection Date: 3/17/2020 805h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 858h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
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: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
53.2
51.1
48.7
49.6
50 00 106 72-151
50 00 102 80-152
50.00 97 3 72-135
50.00 99,2 80-124
Report Date: 3/31/2020 Page 41 of 85
All =,ri.,1)1C!o C.fll"fo:IWk~ IO ,hi: CWA. SOW A •. nnd R RA oro 1>,:rfonned in 11~'\.Wdtu1cc to NUI .At: r'"'•U~1I, Pcninl.'nl 'w!ttlphfl¥ i11fhrm:11f,,n i., lol·a1cd on iht au,u;-hi:11 (OC ... Con1ldcn1111l ll1,1~i11~""' h•(tmn.,1rruc TI1b, tt:txin ti.. provi,1c11 r,.., 1hL: tAdu~ivr-u~c of Lk
<nidrcs.,~'c. Pnvll~ ~ or:wbscqul,)1~t u~oor1hc ~,)r1.hi!loetrin1Nm)' 1W';t.11y mr:.mltet orlti 9Cti.,!T, Of rept,)l.fltl'lmn or thi, 1,"pOrl in (Ol'l~dnn \\1rh the advcrti,~nau, r1tun1dtlon oc ufo o(~y 1wodm'1..W 1wnc~ <'W' tn C'Ol\m.."i.'1.100 wilh 1hcl\•·rmbl1(';u1on of this rcpo1t
for a!\y pu1J~ 01h.:1 1h.:i.n for thl' ~Sec "tll l1r,,.• ,,ant.cJ only on conll<."1. ·1111~ co1url\ny ~~opl.."-no t1,,~1'lm:1bili1y '""'"ef"' (1'1' thc-,J\I~ l"-'tfomuncc of inspc,,:1fou A1tdlorrtn:,.l,:sh, io good foiLh 1u1rl .aixu<dllt,1!.10 lh~ mlO!l oflbc Lrad-: .aL\d. ,,rii:lc.ute
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-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: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-002
Client Sample ID: TW 4-03 _ 03172020
Collection Date: 3/17/2020 805h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2020 1703h
3/20/2020 I OOOh
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 27.7
E353-2 0.100 6.15
Report Date: 3/31 /2020 Page 9 of 85
All an.,iy~!io :irr!il"Xhk to lhC' CWI'\. SOWA.:wJ kCH.A IU\l p.·rf(mnc:d n 11cc«d,1U,'c\O ~f;l pr"~'\15. J'crtini;,nt ~11rhn" lnfotrrHmM i, ln.:otcd on 1>,~ nmn:hm t(.>{'" ('-onn1kn1i.ll O~ncs" lnrt'u11.1ttnn: Thi~ rcpon. provi,k,:I [i~ril1,~ •xdU!I.W U!..i! Mthe
nddn-s.s.\.:. l'n,..11"-);l;' or sub\(l({\tmt \l\\" or1hc nilm'# ~lht~ Cl'.'"ll"itn)' 1,.\C'ony ntcrobcr 01"11,. ~1UT. ortCf'h't.lu~tion or Lhl1 n.•110,1 in (OOOC\'tlon wnh 1hc advcni~mcm. 111011M-\lmo « Mic ot'tul)' p,odul;ii Oil' pt~~ or in onnc,'Uon with 1hc. l\'•,,Uhtfr:niun or 1his rcpou
for nnyr urrmo oth1.•r than fo,r th.:-11'Mf'Cllee. will be i;r11n1C'd on1. qn con111t Thi, com~)'.at rt 1Ml N"t.P'Mulbilily \"~Cfl fi'K 1hc tluc llt."':tJ(K'tl1!\ncc or Llbpi:~1fo11 :,,ml/or ru,.,1}'11,lt 11l g,'l(\(j; fal1h Md aic:c~)olinM co Lhc rnlC-\ '1f11!c Lrad~~ ortrl or \if:IC'tl<'n.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-00lC
Client Sample ID: TW4-03R_03162020
,,NAlYTlcA, 1Aao11.10Alfs Collection Date: 3/16/2020 745h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 819h
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 11.3
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qua!
52.9 50.00 106 72-151
50.6 50.00 101 80-152
48.8 50.00 97.6 72-135
49.8 50.00 99.6 80-124
Report Dntc: 3/3 1/2020 Page 40 of 85
All ~n.,I~ ~rll1..";bl,~ to ,he C\VA. SIJWA. Anil RCR,\ ort ,,..•,romltd io ~,;.)f&ntc 10 NOLA(; J'(i\ttK':()J, Pc.rtincnl -.,amrliny b,f\Jnn31.1on L, ltk·11cd on 1he i\lUlchA.'tl ' ("onfok-n1\a.t 01,1,lnass 11,rt,1111:11/on: Thh. 1.:port !o1 puwtdctl r-,, 1lil' .. ~A\'lu. \\' use or the
.tlidl\".S~·. Pl'Jvll~l:~~ ,,r.wbscq1,1~·11L \I\C-Cf 1ho n:a.lHC' "1' ihli-cs,,n1p,my "r.uw mcmbttorh, :,,ti,ff. \lf' n:p1~Ll!Lk.'d011 of th(\ t..:-1,on in <"t1rult1:1i"on \\ hh 1hc ndvcnf 111e1,1. fM'O\Ui'lf1tWt o, wlc u(M~· pt'Orluct or ,,r~c..< (11 in t:onncctlan "1th 1ho "'-ruhhn1lim uf this ropo11
fori:inyp1,11~ utl~r1h:i.n for llu,utf<ltcw:c will~ @J:ttUcJ only on COl'lll't(l 'rl)i" eotnr,My.ci,'\.-q,tr. o,, ti;')f100 ibili1y ,•:h'l!J'I (i)r-1~ 1!11i:: r•crfo.rtnlm,: • ofi11~·i.:11on nnJrore1nnly.~ In g\'Jt'ld fl,i1h And AOConllng 10 1h,· n.ikt, ol'ihc ~-:-.a1ut uir~IYK'e.
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-00 l
Client Sample ID: TW4-03R_03162020
Collection Date: 3/16/2020 745h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/27/2020 753h
3/20/2020 959h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Repon D11tc: 3/3112020 Page 8 of 85
All O.Ml)'~ r,rll~hk' to 1h~ CWI\, SDWA. :mt! RCRA arl; lli.'f(onnt'J Jn'lk(;14diu1.:ctn 'ULA~~ ll"'l('0.,1s... r nin~m unpHng inform:1,1ion lo .. ·nii.:d or\ 1h1.· RU:i,iJ)1..,t l~ ('1,nlhJcmll-.l ll\l'llnc, .. 1nnw:ma1lnl'I,; Th"Ji!i, h,l)(lr'i i!i. pm\·lill'(1 fM Lhl:'\\t.\':T11.~\\: 1Ju• ,lfdK.·
ndt.l~)l.·~. itn\')kv ..... <'r>1Jbscqu~nt li\C af 1hr."> n.:urJ.t or-.~ \ l.!l)l11Jklll)' or i.ny mcmbc.•r or hp. MIIIT. "'r rq,n><l,1~·1ii;M1 of lhl'i n.•pon i11 C'Mni:"Clion with 1hc advc111Wmat1. p,anw,ii,~i or ~le cil':uw pcodu(1 or p(tK'C\S. or in t0ftn«1ion wfth 1hc h .. ·1t11bliC"111lon flf 1hl'I-ft'f1'1'1 l
for nny fltl''Ptl:SC mbcr 1h:1n r,n 1h;.• 11ckl, ~c will 1)1.• s;.ml\tc:,..t ~ly oi1,'0C\lnn Thi'\ ~nr,;uiy .'IUC1.-p1, uo l\" .. 1,c,n,lbility ~(),Cll'f'!1. ({'r 1ho Ju.e p....-f1.u1n.:1ncl' of i1hpc,~uo11 cu11,ll0f'~M!)'~i.t 1n ~I ra1Jh dtut '"' •nr,linl:l, u, tb,.• n,1~ ollt,t tmd~ omt L,f M:il.'T'ltu.
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-008C
Client Sample ID: TW4-04_02192020
Collection Date: 2/19/2020 1340h
Received Date: 2/21/2020 1240h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 1149h
Units: µg/L Dilution Factor: 20 Method: SW8260D
Compound
Chloroform
CAS
Number
67-66-3
Reporting
Limit
20.0
Analytical
Result
1,100
Qual
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
----------
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
1,070
979
946
968
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1242h
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
1,000 107
1,000 97.9
1,000 94.6
1,000 96.8
Method:
Reporting
Limit
1.00
1.00
1.00
72-151
80-152
72-135
80-124
SW82600
Analytical
Result
< 1.00
< 1.00
< 1.00
Qual
#
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
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
53.8 50.00
50.9 50.00
50.0 50.00
49.7 50.00
108
102
100
99.4
72-151
80-152
72-135
80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 30 of 50
All amilyses ~plicable to lhe CWA SDWA~ Md RCRA .are performed in accordance t~ NELAC protocols. ~cnlnen~ samplin~ informat_ion is. located on ~e attached COC: Conlidtnli.il Business lnromuulon: Th.is repon i~ prm•!ded for 1hee.\'.;c.ha~,c use ~flhe
~ddressee. Pnnle;es of' su~seq!ICIU !~"a oflhe ~:1'."c of this .co~pany or any ~~her of its slaff, or rqlfochicll~ ~~ this repo~ m ~o~eclto",. with the ~~·ert1se~ent, P~?mo11~, ~ 11\10 of ~!r. ~rod~cl °' l'~~m, ~rm 7°nm;c!1on w!th th~ r~-p~bltct1h01'1 of 1h1s report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-008
Client Sample ID: TW4-04_02192020
LADOR,HoA1Es Collection Date: 2/19/2020 1340h
3440 South 700 West
:lalt 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: 2/21/2020 1240h
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
3/3/2020 1948h E300.0 1.00 43.4
2/21/2020 1513h E353.2 0.100 4.58 ------
Report Date: 3/9/2020 Page 13 of 50
All annlyses applicnblc lo lho CWA. SOWA. and RCRA nre perfom1ed in nccordnnce to NE LAC protocols. P•nlnonl snmplinH inrornllllion is located on tl1e nunched COC. Confidential Buiiness 1nrorn,01ion: This ropon is prol'ided ror tho e.«lu,il•c use of the
~ddressee. P11\'ile~es o[ sl.l~sc~~ont ~1~e of the ~~le of this .co1~pru»· or nny 1~1~ber of its stnff, or reproductl°!? ~fthis r~po~ in ~on~icol an, with the o~~·ertise~enl. P~?mot10!1 ~, ~ale of ~!f, ~•od~cl or pr~ess, ~r in ~nn;c!ion "'!th th; r~Tpubl talion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-018C
Client Sample ID: TW 4-05 _ 03172020
ANALvr,c., , Aso11•ro""s Collection Date: 3/17/2020 1024h
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1455h
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 14.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55,l 50.00 110 72-151
50.3 50 00 IO! 80-152
48.7 50.00 97.5 72-135
49.1 50.00 98.2 80-124
Report Date: 3/31/2020 Page 57 of85
All 1:rn:.1)1-"C} :i:rrlkahk II\ 1bt4 (. WI\, SOWA, ;,nd R.CltA ~t\.' pi.·,romtcJ in flt<'Oll'(l.nMe ,o Nl:I.AC pl'll1t'IU\llJi. P~nin1.'11,~11pJin» mr1wm::uion t' ~-.nwd on lhc-1:1,t~hcd C( • ("uuf11J.:111 3.1 Ou,io~'j" lnfo1111lhQf'I~ llli\. i\'port Is proviiJ1."il for 1h1,.•1.·Al!'iu~iw us~ ofthl'
nddf'Q)I,," l1ti\'H1,.•~~ iir w~,e1q11i.111 uw nriho n:.mo or1hi\ 1:'"l"lt>nn. t'tf any 111tn1~·r l)r11,. M11ff. or rqmldu..:tlun or thh, t\"'lklfl in l!'Onn«dcm "i1h 1ho :,dvcni .. ~11'H?nt, pr01uo1lun i,r~lc ol";i.nr JJ(odui:1 v1: Jlfl),,,""CM,. min "'cinnc,.:tion wi1h tt}c rc-rub.H(";1d1m of !his rcpo1 L
for an)' fl\lrfl<"C otlk"r 1hon (or1hc iul.:lt sec win b,: ;;ran.IN only on L'on1acl, Thi (1Jt11f'llTIY Oct·cpts nd n..~Mlbili1y "'"~r• (I)( 1hg lluc ~,fonn:'lni; • of inliJl('\"(1011 and/or1u1;,h·tl.~ in got"il f11i1h .ind~ ~)uhni IO th· nalo.nf1he tradL• llllrl urSt:lcnce.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-018
Client Sample ID: TW 4-05 _ 03172020
""A, n, c" , •" o ,, Arn "" s Collection Date: 3/17/2020 1024h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) rng/L
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/27/2020 113h E300.0 1.00 48.3
3/20/2020 I 034h E353 .2 0.100 7.10
Report Date: 3/31/2020 Page 25 of 85
All ~l)'K\ arplk&hJ~ 10 1hA.-l 'W./\, Sl)WA, and k rH,,.\ IU~ ll<T'ronucU In ;11C(\'lf(~'IJI~"¢ IU NEl.A(" ph~10Cllk. l'cni11cn! J.:IJ11pllnw; inrorn'ltultin l'l lo-:i[t"d Oil .~ 61\~i,,·hcd Cf •• (oo(ld.:nli.11 OU:l.il~ l111'runutimr This n:ron ls provicll'\1 rC'r 1m.· ,•.t.ehH,i\'t' use or the
addtn~ Privilttt.,. nr _,.,1,, e,,io~'lH u~o ottho n:urn, or1hh t..lmp11nyor 4ny trt~nb..."t llftb il11i1: 01 rcproch1,·tKJ11 or 1h1\ 1\'pon in ('MIJlC&:l{an whh lhl advc11li.t.'nwm1. pmutt·,u,,n or J.Dlc of :in~ prod,Jc"l\'N' J'N'4X'C\S.. or in coon«lion wJU, llw 1\.··{'l,1bhc,·uior1 of this rcpo1 l
for 111.n)' (I\JtJ1oi;c: 01hcr th!m l\K 1h\.1 i:ukh~· will tK" smritt"J anl)· on t"On\Jtct. lhl, c-oi.UflA,11t AC"("('fX,-lh) h~tm.lbility "A~"Cfl; for tho .Jue ~"t'fotm:\n~~ of in>J'K'"tio11.:md/c11· 1,1Qly.,1) in g,,od fOi1h and ~c:,orc~n~ In tht n1leo. of1hc trad~· 1111d ._,r.\C'i or:c
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: !st Quarter Chloroform 2020
Lab Sample ID: 2003454-016C
Client Sample ID: TW4-06_03 l 72020
ANArm c "' , •so e,,ro s,rs Collection Date: 3/17/2020 1005h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1416h
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
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 6.93
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
53.6 50.00 107 72-151
49.8 50.00 99.6 80-152
48.3 50.00 96.6 72-135
47.8 50.00 95.7 80-124
Report Date: 3/31/2020 Page 55 of 85
All nNl)·M.'$ applici,1,lri~ tn tht t'WA, SJ')\\'A, n.ml RCR • ..\ 111\" 1~rrfou,1cd 111 tll!(!<'H'dnm.•c 10 N(U .• AC pM1oa,t Pcrti1tl.'1H mphriy mfi:qTI,n1fo."1 1ii t~1cd on 1hc-auu.~·~ (..'fX:.. ('0111i1k111l:1J n.,..1n .. :-s 111ron1mic-.n.1 Thiu,.::pnn Is provfd1.'\I ronb,~~ ... ~1usivc-u.,c o{ thc-
a,1dl\"M\~ Pri\'ilfgc;, \\f ~l~1,•1U U\C i)flho n;nnc-orlhl\ COIIIJJaH)' \If IJll)' mtmb.rorh) $1:tff. Ol n:rotd11t.'1lOO of ttJh. A."P!lfl in ,•nnnca.'tfol1 whh thi: r1J\.'cni,cmctU. lJIOl1lollli('II\ OJ Mlle of :,,1y proth1ct or IKn.."'(j,~ or in fOCIMti;tion with 11\0 IV•f1111bll~Uion of 1his rcpo1 L
lbr 1·u1y fl'n·r,o::.c otlti:r 1hon '4'1f Ul-c adJreue:r wnt '"' ~mntoJ unly t'N'l l.'an.t.,.('t, Thi, m np:1n.)' oc~·ept rk1 l\~:,1por1!1lbility c.·,,·cr1 i« lhC' Jue pc11011n:i~ of in,p,c\'lkio i:md'm-an:tl~"St" fn go,ud r.,hh and accori1in; to the nala. o(thc h~t<lc n11cl orKicncc
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-016
Client Sample ID: TW4-06_03172020
• N •, v r, c ,., , • ''° ",-r o"" s Collection Date: 3/17/2020 1005h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 038h E300 0 1.00 43.2
3/20/2020 I 03 l h E353.2 0.100 0.222
Report Date: 3/31/2020 Page 23 of 85
All isn.:1\)'M."3, applicabk to Lhc C\VA, SDWA,.nnd RCRA nrc pert'onncd in nccordan..:c to NELAC protoi.;ols Pertinent sr1111pling information is loco1cd on the attnchcd l'OC. Confidential Ousinc:,. ln(t'1111111ion; This upo.n is pro"i~1I (,)I' th('\' d11>i\\' use or the
nJdrl.S~ Privilcg:l!'s or subsequent use of llHJ. QllnQ \lrthis Cl)111pany or any member of its slalT. or rep!i'ltlllt'liou M this r..:port in ..:onncction with the :tdvcrti5'cmc111. prornolilln or sale or :i.ny produc, m J'M'Ol."o..(.. or in coo~ Lion with Ille h:•l)Uhlh:~fotl of this rcpor t
for any pu1posc other than for Lhl' llddrcsscc will hl' grnnlcd only on conl:i.ct. This compRny ac~·cpls 110 C\"i.j>Ol't\ibility i.'xccpl ror 1hi; due ~rformancl' of iuspccLion and/or analysis in goml foilh 11nll .ticc:nntrn11 tO Lhl' nd~cithc lrad~ arwl nf~l~e.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-026C
Client Sample ID: TW4-07 _03182020
AliALYTlcA• , AnoaAroairs Collection Date: 3/18/2020 600h
Contact: Tanner Holliday
Received Date:
Analytical Results
3/19/2020 1420h Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
Analyzed: 3/23/2020 1245h
Units: µg/L
Compound
Chloroform
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
CAS Result Amount Spiked %REC
17060-07-0 526 500.0 105
460-00-4 516 500.0 103
1868-53-7 470 500.0 94 0
2037-26-5 489 500.0 97.9
--The reporting limits were raised due to high analyte concentrations,
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/20/2020 2133h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 1
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 54.2 50.00 108
460-00-4 51.5 50.00 103
1868-53-7 49.8 50.00 99,7
2037-26-5 49.2 50.00 98.4
SW8260D
Analytical
Result Qual
746
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: 3/31/2020 Page 65 of 85
1\\1 Jn.'1.l)~ :ipplicahk 10 the CWA, SOWA, ~ml RCRA nri! l)l'rfonncd in £1ccor<llu1,c 10 NELAC p1,llllClllr., Pcrtin.:111 salHpling infonmui,,n is lo,·a1cd 0111hc auochcd COC, Cu11foJcnti:\I Uusi11ci.s lnfo1m:i.1ion: This report is prnvidc..i for thl.' 1.•.xdusiw use 1Jf' thl'
tlAitJ ~k.'C'. Privih:(!l'li of subscqucnL uw of 1hc nt1mc M this Cl)lllpaU)' \'II :u1~· member of ils slt11T. or rcptudlii\1lk111 of Lhis 1\'J)Ml in rnnnccLion wiLh the ;i,1vcniscmcnl. promolioll or sale of:my prod~Lcl m pro\·css. or in connc<.:tion with !he rc•rmblic.i.tion nf tl1is rerun
tor any pu1 fH'SC oth~L 1h:1n l'l)L' thl.' 1ul,1rcsscc will h1.• grnn1cd only on ~nnl:."ld . This company acl'cpts 110 n.~•'Km._.il>ilily i.>.xccpl Ji.,r lhl' tluc pcr10nnancl' ol'insr,cction :mi.I/or analysis i11 fl.lllld foilh onrl according to the rules of Lhll' Ltack illl<t or science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-026
Client Sample ID: TW 4-07 _ 03182020
•NA,v11c,, , •oos.roairs Collection Date: 3/18/2020 600h
3440 South 700 West
Salt Lake City, UT 841 I 9
Phone: [phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 313h E300.0 1.00 42.1
3/20/2020 1055h E353.2 0.100 3.75
Report Date: 3/31/2020 Page 33 of 85
All nnalyscs applicable Lo Lh!,,': CWA, SDWA, nnd RCRA ore IX'rfom1cd in accordan .. ·c to NELAC pro1ocols, rcrlin~m sa111pling info1 mnlil1n is locn1cci 011 lhc attached COC. C'o111idc1\lial Ousincss Information: This rcpor1 is provilfcd for thl' rxdnsivr use l)f lh\.'
nddrcssrc. Pri\•ilegc-s of subscquc1\l usc of 1hc nnmc of this cilllll)Ull)' or any member of iLs slalT. or reproduction of Lhis report in connection wilh the advcrtiscrncnl. J>romolil1n or sale of any product l)f process. or in connection wiLh 1hc fl!-p11blicnlion of this rcpo1 L
for ony pu1 pose other lha.n I'm Lhl· adc\rcssce will he granted only on contact. This company oc~·cpts no responsibility i:xccpt rm the due pl:!tfonnnnCl' of illspecLion and/oi·nnnlysis i11 good fo ilh and accord in~ to Lhc-rules of the t1adc and of science.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2020
Lab Sample ID: 2003454-023C
Client Sample ID: TW4-08_03182020
h N ALvr 1c •1 1 AaoRt.roAlfs Collection Date: 3/1 8/2020 532h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 2033h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
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 55.0
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: awal(cyawal-labs.com 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
54.9 50.00 11 0 72-151
51.1 50.00 102 80-152
49.0 50.00 98.0 72-1 35
48.9 50 00 97.8 80-124
Report Date: 3/3 I /2020 Page 62 of 85
All analyses applicable to 1hc CWA. SOWA, :i.nd RCRA arc 1~1 IOnncd in accordance 10 NEL.AC prnlocols Pcrtinc-nt sampling information is lol·1ucc\ on !he auachcd COC. Coniidcnti:i.J Business lnforma1ion: l hi."> report is prodded rm the cx,:lusi\'l' 11sc of thi:
addresst:e. Privileges or subsequent use of rhc n:tmc ,)f lhis company or any mcmb..:r of ils slaff. 01 rcp1odu'-·1ion l)f this 1..:porl in conncclion wilh the :,dvcnisemcnt. promolion or sale of any product or process. or in ... ·onncction with lhc r<'-publicmion of lhis rcpo11
for any pu1 po5e other lhan fo1 thi: oddrc.<.scc will be grnnlcd only on contacl This company acccpls no r ... -sponsibility ... ·xccpl for the due pc, fo1 man cc of inspcl.'tion andlor analysis in g,1ocl foith amt according to lh(' rules of tltc lrad~ and of sdcncc
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-023
Client Sample ID: TW 4-08 _ 03182020
ANA,vr1cA 1 1 AaoA.roAJfs Collection Date: 3/18/2020 532h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3(27/2020 22 lh E300 0 1.00 53.8
3(20/2020 1049h E353 .2 0.100 1.04
Report Date: 3/31/2020 Page 30 of 85
All nnalyscs applicahle to the CW A, SDWA, and RCRA arc JJC1 fonncd iu uccordru1i:c to NELAC phltocol~. Pcrtim.'nt sampling info1ma1ion is locntcJ on 1hc auachcd COC. Conlide1uial Dusill\."SS lnlllnnation: This report is provided for th,: exdusi\'C use or thc-
nddn.-sM'C Privih.·ges of ~ubscquent u.w of !he n:1.mc llf lhis company llt M.ll)' member of its staff. m rcprodm.:tion of 1hi!j ,·eporl in connection with the :\tlvcni~emcnt, promolion or sale of any product or procc.,:;s. or in connection wi1h the rc-public:itiun of this rcpml
for any puiposc other 1h,m ror th~· addressee will ~ granted only on conta.:t. This company accepts no responsibility except roe thiJ due performance of in spec Lion and'o1 annlysis in good fnith and accor<ling to thl' rules of the Ltack 1111d of science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-021C
Client Sample ID: TW 4-09 _ 03182020
ANA Lrnc •, , •sosAroa,rs Collection Date: 3/18/2020 508h
3440 South 700 West
Salt Lake City, UT 841 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1953h
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-dB
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 48.9
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
53.3 50.00 107 72-151
50.0 50.00 99.9 80-152
48.3 50.00 96.6 72-135
48.4 50.00 96.7 80-124
Report Date: 3/31/2020 Page 60 of 85
All analyses applicahk Lo Lhc CWA, SDWA, and RCRA arc 1~rfo,mcd i11 nccorclirncc Lo NELAC p1otocols, Pcninl."nt sampling i11fo1111a1ion is locmcd on 1hc attached COC Conlii.lcntinl l3uslnes.s l11fh1mation: This reporl is provilkli fm Lhc cxdusi\C use of Lhc
,uidressl'C~ Piivllcg~·s of subsequent use of the nnme of tllis Cl)lllpt:my ill R11y 111cmbc1 of iLs staff, m rcp1 oducLion of this re1xm in l'onncction with lhc alivcrtiscmenl, promo\ion or i.alc of any product l1T process. or in connection v. iLh lhc tl~-publication of 1hi:s. rcpo1t
for any pu1·po:s.c other thnn llw thi: ac\clrcssci: will be-granted only on contact. This company occcpts no responsibility ex cert for the due pcrlb1manci: of inspection and/01 analysis i11 g1lNt foi1h nnd according Lo LhC' mies of thl" l1a,k and l,f science
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454-021
Client Sample ID: TW4-09 _03182020
•NA, vr, c"' , •Ro R •roe" s Collection Date: 3/18/2020 508h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
To11 Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 147h E300.0 1.00 37.7
3/20/2020 1040h E353.2 0.100 0.855
Report Date: 3/31/2020 Page 28 of 85
All nnnlyf.cs applicahk~ to the CWA, SDWA, rind RCRA nrc pl~1 Conned in accorclancc to NELAC p101oools Pcrtincllt sa111pling int'ormnlion is locnlcd on 1hc attached COC. Confide111it1I Uusincss lnlimnation: This report is providcli for I.he l~xclusivc-use or the
addn."'Sst'C. P1 ivikgl'!i or subscqm.'nl uf-tc of the name of this cmnpany l,r ;my member of its slaff. 01 reproduction of this 11.'1>0rt i11 l'onncction \.\ i1h the advcrtiscmcnl. pronrn1ion or i;;alc ol' any produt.L or procc.. .. s, or in connection with 1hc rc-public.uion of this rcro1 t
for nny pu1 pC'l!iiC othi:-r lhan for lht~ addressee will bc grnnlcd only on contact This company occcpl'i no responsibility except fl,r lhl.\ liuc ~1fo1111nnt·c-of inspcclion and/oi·nnalysis itt gl)C'ld faith nnrl act:orrling 10 1hc mies of the trndc ond of science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-020C
Client Sample ID: TW4-09R_03172020
ANALvr,chl, •uoaAroairs Collection Date: 3/17/2020 1100h
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 83 8h
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
1
Contact: Tanner Holliday
Test Code: 82600-W-DENlOO
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 12.3
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
52.7 50.00 105 72-151
51.0 50.00 102 80-152
48.3 50.00 96.6 72-135
49.8 50.00 99.6 80-124
Report Date: 3/31/2020 Page 59 of 85
All analyses ar,plicahk Lo Lhc C\VA, SDWA, and RCRA arc pc1fo11ncd iu nccordnnl'.'c lo NGLAC pro1ocols PcrLincnL samplin~ iufo1mmion is Joctill!li on the auachcd COC, Conlidculial f3usincss lnfo1malion: This rcpor1 is providccl for the l!>.:dusiw use o( the
addrt.'Sscc, Privilcg~s of subscqucllt use of the name or this Cl)Jllpany or nuy mcmbc1• of iLs slaff. 01 rcprnduclion of this 11.'port in connection with the :llh cniscmcnl. promo1ion or sale of any product or process. or in connection with lhc re-publication of this rcpo1 l
for ony pu1 pose oLhl'l lhan for the a<ldrcssci: will he gronlcd only on conlacl, This company accepts no responsibility l'Xl'cpl fn1 the due pcifonnancl· or inspcl'tion andior .innlysis in good foilh and occording 10 Lhc rule~ 0J'1hc Ltadc illld or science.
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2020
Lab Sample ID: 2003454-020
Client Sample ID: TW4-09R_03172020
Collection Date: 3/17/2020 1100h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2020 181 Oh
3/20/2020 I 036h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 3/31/2020 Page 27 of 85
All analyses .i.pplicahl~ lo Lhc CWA, SDWA, nnd RCRA arc 1>e1 l'onncd i11 occorclancc to NELAC pro\ocols. Penincm ~ampling inlb1ma1ion is lo~'rtlcd 011 the altachcd COC. Conlidcn1inl Business l111h1mation: 11lis report is pro,·ilicd f11r Lhccxdu$iV!.' use orthl'
add1 ~'SSl'C. P1 ivikg:cs of subsequent use of the name nf this cm,1i,any M m1y member of il5. staff. oncp1 odm•lion l,f this rcpml in rnnnccLion with the ndvcniscrncnl. promolim1 or sale l'f any ~roduc1 or process, or in connection with lhc 1i:-public.nion of lhis rcpoll
for any pu1 pl,sc oLhi!t lhnn for lhl' nddrcsscc will hl' grnn1cd only on conta~·L. This company occcpl.r; no i~~sponsibiliLy i:x.,:cp1 rl,1 1hc Jue pc1 fonnnnc-l' or il1spc,:Lion and/01 annlysis in gor,d foi1h and oecorc1ini; Lo Lhl' mies orthc trn.d~ 011c1 or science_
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-028C
Client Sample ID: TW 4-1 O _ 03182020
•NA, vr, c"' , • a a"• rn R" s Collection Date: 3/18/2020 625h
Contact: Tanner Holliday
Received Date:
Analytical Results
3/19/2020 1420h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
Salt Lake City, UT 84119
Analyzed: 3/23/2020 1404h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC -----------------------
Toll Free: [phone]
Fax: [phone]
e-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
536
514
487
493
--The reporting limits were raised due to high ana/yte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/20/2020 2212h
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
500.0
500.0
500.0
500.0
107
103
97.4
98.6
Method:
Reporting
Limit
1.00
l.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4 17060-07-0 53.7 50.00 107
Surr: 4-Bromofluorobenzene 460-00-4 50.1 50,00 100
Surr: Dibromofluoromethane 1868-53-7 49 4 50,00 98.7
Surr: Toluene-d8 2037-26-5 49 0 50.00 98.0
SW8260D
Analytical
Result Qual
798
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: 3/31/2020 Page 67 of 85
All nnnlyscs ar,pliL:ahk 10 1hc CWA. SOWA, nn<l RCRA nre lh'1 l'onncd i11 oci.:mdnni:c lo NELAC p1n1oclils. Pcnini:nl srn11i,lin1; informaiinn is loi:ntcd on Lhc allaehcd COC. Co11fok11ti:1I 13usinc.s.s l11l\i1maLion: lllis rcpor1 is prr)\'ilkd fl)r Lh.: ,:,.dH$.i\·~· UM~ of 1hc
addl'C,'i!tl'C P1 il•ikpi:s l)f subscquct\L use of 1hc name l,r Lhis tam1pt:1ny lit m1y mcmbcl' ,,r its slall: 01· rcprodUl'Lio,1 l,r Lhi.'i 1cpor1 iu conncc1ion wiLh the :1l1vc11iscmc111. promolion or :.ale of any product or procc.~s. or in L'onnci.:::tion wiLh the 11>pul>lica1ion of this rcrm L
lor any pui rmso uthc1 lhan Ji.,r th~· uddrcsscc will ll~· grnntcd onl~· on c-onlal'I This COlllfllt!lY acccpls 110 ,-...~sponsibility except l'l,r th~ liuC pe1fo1 mnncL' or inspection and/01 analysis i,, g,,L,cl l'nilh one! uccording to the rules of the track and of scic11c-c
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-028
Client Sample ID: TW 4-10 _ 03182020
ANALvr,c•, , ABoRAroairs Collection Date: 3/18/2020 625h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 422h E300.0 1.00 53.5
3/20/2020 1058h E353.2 0.100 7.83
Report Date: 3/31/2020 Page 35 of 85
All nnolyscs applicabl~ Lo 1hc C\VA, SOWA, and RCRA nrc 1~1 l'anucd in accordance 10 NEL.AC prolocols Pcnint."1ll sampling inf'o1ma1inn is locnicd on the auachcd COC. C:011Jidc11Lial Business ln11.,nnation: This rcporl is providi.:d [01 Lh~ exclusive-us~ of Lhl'
addn.>ssl'C Privilcg:~ or ~ubscqucul usc or the mime l1f this Cl111lpany or any member' llf iLs sl:iff. m' reprodu~'1ion ,1f thi~ 1 cporl in rnnnccLion with 1hc advertisemcnL promotion or s.ilc or any product or procc:r;!<>, or in connci.:Linn wllh !he re-publication or this rcpo1 t
for any pu1posc mber lhan for thl' addrc..,,sce will bl· granlcd only on conlact This company ac~~cpls no responsibility exrcr1 for the due perfo,m;mcC" of in.!.pcr1iou andior an:1l)'sis in goOO foilh .ind uccording to thl" rules of the 11ad~ ond of science,
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-0 l 3C
Client Sample ID: TW4-l 1~02192020
Collection Date: 2/19/2020 1250h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/21/2020 1240h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 1330h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 100
CAS
Number
67-66-3
Method:
Reporting
Limit
100
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
5,320
4,950
4,620
4,920
--The reporting limits were raised due lo high analyte concentrations.
Analyzed: 2/24/2020 1422h
Units: µg/L
Compound
Extracted:
Dilution Factor: I
CAS
Number
5,000 106
5,000 99.1
5,000 92.4
5,000 98.3
Method:
Reporting
Limit
SW8260D
Analytical
Result Qual
2,990
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: l,2-Dichloroethane-d4 17060-07-0 54.1 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.2 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 50.8 50.00 102 72-135
Surr: Toluene-d8 2037-26-5 50.2 50.00 100 80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 35 of 50
All analyses applicable lo lhe CWA, SOWA. and RCRA are performed in accordance 10 NELAC protocols. Pertinent sampling informa1ion is localed on lhe a1tached COC. Conlidential·Business [nformation: This report is provided for the exclusive use of1he
~dressee, Privile~es of sub .. seq~ent ~:e or1he ~~e of this .co1:1pany or any ~mber of ils staff, or reproduclio~ ~! Lhis repo~ in ~o~eclion ... with Lhe ™!ver1isemenl, P~?moti~n ~r ~ale of :11!Y. rrod~ct or p~ocess, ~r in :°nm;.c.tion w!th th~ 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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-013
Client Sample ID: TW4-11_02192020
Collection Date: 2/19/2020 1250h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2145h
2/21/2020 1519h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 51.9
E353.2 0.100 7.07
Report Date: 3/9/2020 Page 18 of 50
All analyses applicable lo the CWA, SDWA, and RCRA are perfonned in accordance to NELAC prolocols Pertinent sampling information is located on the attached COC Conliden1ial Business lnfonmilion: This repon is prm·ided for lhe e:xclusi,·e l.L',e of the
~ddressee Pri, ile~es o,C sub .. seq~ent ~~e of the ~~e of this .co~pany or any ~'!"ber of its staff, or reproductio~ ~~this repo~ in 0Co~1ection .. with the a~:ertise~enl, P~?motio.n ~r ~ale of!"!): ~rod~cl or P~?cess, ~r in ~nn:c!ion w!th th? r~-p~blication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-006C
Client Sample ID: TW 4-12 _ 03172020
ANALn,cA, 1AnoaAroa1Es Collection Date: 3/17/2020 845h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1057h
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
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-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
53,6 50,00 107 72-151
51.2 50.00 102 80-152
48.4 50,00 96.8 72-135
49.8 50.00 99,6 80-124
Report Date: 3/31/2020 Page 45 of 85
All analyses applieabli: Lo Lhc CWA, SDWA, and RCRA ore p1.~1 fm111cd iu accorclmtcc Lo N8LAC p1 lllC1cols. Pertinent sarnpling inlb1 miuion is locn1cd on the au.:ichcd COC, Confidc1uial Business lnli.mnalion: This rcp0t1 is provided for the 1.~xclusivc u~c or thl'
addii..~scc, Pt ivikgc.~ or subsequent use of 1hc name l)f this company ll1 any member of i1s staff. 01 reproduction of this 1cporl in con nee Lion with the advertisement. µromotion or sale of ;my product or process, or in rnnncction wilh !he 1\'-publication of Lhi~ repon
for any pu1 pose oLh,:1 lhan f'm· Lhl' addressee will be-granted only on contact This company accept:-. no r('sponsibilily exec pl t't.)1 the due pcrfo1 mam:c-of inspcclion and/01·,inalysis in good faith and according lo lhi." rules of the IL ad(' 1111cl of science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-006
Client Sample ID: TW4-12~03 l 72020
• .,., vr, c •, , AB 011A ro"" s Collection Date: 3/17/2020 845h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 190 lh E300 0 1.00 53.0
3/20/2020 IO 15h E353.2 0.200 6.39
Report Date: 3/31/2020 Page 13 of 85
All tm.i.l)'Ml)~r1ic,1bk Lo the CW • Sl)\\'A.~d kCRA or,:, p.¥1'ormcd in accordan..:c Lo NELAC pmll)c,,li.. Pertinent sampling inform:Hil10 is Jm:mcd on 1hc aum:hl.·d COC. Coni"Jdc11lial Ousint.-ss lnfonnaLion: This r~porl is proviltcd for the ex(lush·~· ui;c or1he
aJdn'-'i':'..-. l'rivil~g~ I)[ subscq1,·1u u:w 1,rtht n11mi: 0(1hb, C\-.i,1p;my or ;,ny member or its staff. or rcprodu~·,ion of this report in connection with the advcniscmcnt. pronhllion or sale or any product or procc.c.s, or in connection wilh the fl'-p11hlica1ion of 1his rcpo11
for J)Q}' ru.rrri,.o olhn 1han for \ll<'llckl~c "-'111 Ix-q1an1cdonl)' on con1ai:1 This compMy OCl'Cpts no rl~sponsibility ~·xccpt li:ll the due pi!rfo1mancr: or inspi.x·tio11 ,mt:1/01 aMlysis in g1lod faith nnd according to the rule~ of the 11ack• a11ct of !.Cicncc
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-007C
Client Sample ID: TW 4-l 3 _ 03172020
ANAcvr,cAL , ABonAroairs Collection Date: 3/17/2020 854h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1117h
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 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: [phone]
e-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-dB
l 7060-07-0 53,6
460-00-4 50,8
1868-53-7 48.6
2037-26-5 49.2
50.00 107 72-151
50.00 102 80-152
50.00 97.2 72-135
50 00 98.4 80-124
Report Date: 3/31/2020 Page 46 of 85
All am1.lyscs :tr,plicahlc 10 1hc CWA, SDWA, and RCRA t1rc pl'Jfonncd i1111ccMclaucc lo NELAC p101ocols Pcrtinc11L samplint;. in!b1ma1ion is lm'nh.:d on the attached COC Co111iUc111inl Ousincss l11h.11mation: This rcpor1 is provided fo1 Lhl' l.'.'Xdu~i\'i.' use or1hi:
ndd11.-ssec. Privil~g:cs of subsequent use or the nnmc l)f Lhis cn1npo.ny l)l any 111cmbc1' or i1s staff. 01 rcp1oducLio1t llf this r~·pi)rl iu conncclion wiLh the nd~·cttiscmcnl. promo1io1t or ~a.le ol"any µrocluct m process. or in connection wilh 1he ,~-pul>lica1ion of I his rcpo11
for any pu1 po~c 01hc1 than fm Lk uctclrcsscc wi[[ ht i;?rnntcd only on conli\~'l This company oc~·cpls no r,:sponsil>iliLy except llw 1hc due pcrfo1mnncc or inspcclion and/or am1lysis ii, glll)d foilh onrl occorcling to Lhc mies of tile L1ack ;11tC, of scic1\cc,
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-007
Client Sample ID: TW4-13_03 l 72020
ANALn1cA1 1 ""o"""°""s Collection Date: 3/17/2020 854h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
'l/7.61?.020 1917h E300.0 1.00 63.9
3/20/2020 1016h E353.2 0.100 5.50
Report Date: 3/31/2020 Page 14 of85
All nnnlyscs applicahl~ Lo 1hc CWA. SDWA, nm.I RCRA, arc 1~1Jonncd in accordaHl.'C to NELAC p101ocols. Pcrli11cnt srunpling i11fo1mnli1rn is lo\'.'.H~d on ,he t1tlachcd COC Conlidcnlinl Busincl\s l111i.111na1ion: This rcporl is prnvi,lcd for th~ l.'xdu..~[,~· uiic ol lhl'
ndd1\~scc Privileges or subscqucm usc of 1hc nnmc of this Clllllpany or Rny member of iLs slaff. or rep1·odu~'tio11 of this fl.'J)On i11 ..:onncmion wilh lhc advcrtiscmcnl. promo1ion or &ale of any produc1 or proC'c.'is. or in cooncclion wi1h lhc ri:-pul>lic:uion of lhis rcpo11
for any pu1pos.c 01h..-1 lhat1 fo1 lh'-' addressee will be granlcJ only on conlaC't This company ::icccpL.-. no rcsponsibilily ""\~Cpl for lht.: \\uc p..-rfonnnnc\" or im,pt.:\·tiou and/01 """lysis in g\llld faith ond according to the rules of 1h..-lnHk onrl or scknce.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-015C
Client Sample ID: TW4-14_03172020
ANALYTIC Al , AaosAroa!Fs Collection Date: 3/17/2020 955h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1356h
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 2.98
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-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
53.7 50.00 107 72-151
49.8 50.00 99.7 80-152
48.4 50.00 96,7 72-135
48.9 50.00 97.8 80-124
Report Date: 3/3 1 /2020 Page 54 of 85
All :1n.ilY).cs .ivrlkablc lo rhc C\VA.Sl'.>WA. a.nJ RCRA Q.ft' p,:rlbnncd ill occorclm1l'C to NELAC prolllCols. Pcrtiucn1 sampling informmion is lo.;011~,i 011 thc au .. ·n.:hcd COC. Confidential Business lnlhrmation: This rcporl is pro,·iderl for the l~xdus.i\'C' use l,rthl·
ndd(\":>-)('('. Pri\'lk):.\·jorsubscqu...-111 U\Uorth~ n:uooor1hl1' a"lfllJMlly ~w auy member of its s1a1T. or rcprodtKtion of this r..-port in connection with thcadlicrrii,:cmcnl. promolion or sale ornny product or procc.,;s. or in rnnncc1ion with lhc r,:-publicruion oflhis rcpon
for nny pUrpc.'154otht·t' 1h,rn ror 1h~ iwMrer...;.cc ,,m hii,• &ntnlt1.l Ord~· on conta,:t This company llCl'CpLs no responsibility ,:x,:cpl I~" 1hi.: due pi::1fo1mnnci;-or inspci:Lion and/01 nnnlysis in good foi1h and accorclini;; to LhC" rules 0J'1h,: trade-and of st.:ii:::ncc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2020
Lab Sample ID: 2003454-015
Client Sample ID: TW4-14_03 l 72020
ANAl vr,cA, 1.Aoo11AroR1rs Collection Date: 3/17/2020 955h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 234 7h E300.0 1.00 48.4
3/20/2020 I 030h E353.2 0.100 6.17
Report Date: 3/31/2020 Page 22 of 85
All analyses applicahk• 10 the CWA, SOWA, ond RCRA arc p ... ~1 fom1cd in occordancc lo NELAC p1 olocols. Pertinent sflmpling info1 m:11ion is locatcl1 on 1hc aLLocl,cd COC Conlii.lc:1Hinl Businc~s Jnfo1 rnation: This rcpor1 is provilicli rm Llh." cxdu~iw use or Lhc
add1 ~-ssrc Pi ivilcgi:s of subsequent use of the name of this compimy or any mcmbc1 or its. staff. 01 rcp1 odu~·lion 1lf this 1cpor1 in (onncction with the advcniscmcnt. promo lion or sale of any producL or process. or in connccLion v.·ith 1hc r~-p11blicn1ion of lhis n.:po11
IOr ::iny pm pl,~C 0Lh~1 than fm' Lhl~ addrcsscL; ,,1ill b,: r:ran.Lcd only on contact. This company O!XcpL-; no ,~sponsibility l~xccpl for 1hc due p~tfoimnncl' or inspccLion and/oi annlysis in g1iod fnilh nnd nccorcling Lo the rulc)i orlhc L1adc ond or science
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2002488-01 oc
Client Sample ID: MW-26 02192020
Collection Date: 2/19/2020 1240h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 1229h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qua!
67-66-3 20.0 1,100
-----
Phone: (80 I) 263-8686 Surrogate --------CAS Result Amount Spiked %REC Limits Units: µg/L Qual
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
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
1,080
1,010
961
993
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1322h
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
1,000
1,000
1,000
108 72-151
IOI 80-152
96.1 72-135
99.3 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qua!
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 53.9 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.9 50.00 102 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 99.1 80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 32 of 50
All analyses appl t:t.blc to lhc CWA, DWA. Md R RA a.re pr1fom1ed in accordance 10 NELA p101ocols. Pertinent somphng m(Of'nllllion is located on the attached COC. Confidential Bbdne$s Information: This repon is prm•ided ror 1hc-exchash1: ll,te of the
~ddressee. Pri,·ilr~cs. of s~e~~enl .u~or111e t~:"'~ne ofthis.C'Qn:iP-mr or My ~~ber of its starr, or tq,rodoctio~ ~~this rcpo~ in .-=Ol~H!Cfion~ ,.,,ilh the ~,·ertise~enl, P~?moti~n ~r ~ale of ;"!))?"od~ct or P~?ce~s, ~r in ~nn~c!ion w!lh 1h~ r~·ptJblicalio1:1 or this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-010
Client Sample ID: MW-26_02192020
ANALvrrcAL LAeoRAToR1Es Collection Date: 2/19/2020 1240h
3440 South 700 West
salt 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: 2/21/2020 1240h
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
3/3/2020 2021 h E300.0 1.00 88.9
2/21/2020 1515h E353.2 0.100 1.17
Report Date: 3/9/2020 Page 15 of 50
All nnalyses applicable 10 th-, CWA. SOWA. and RCRA are performed in RCCordence 10 NE LAC protocols. Pertinent sampling information is loctited on the attached COC. Conlidentiol Business tnrormalion: This repon is pro\'ided for the e..'iclusi, e use or the
~ddressoe. Privile~es of sub .. seq!tent ~1~e of1he ~~eofthis ,con,iptmy or RR}' ~mber of its stnff, or reproduclio~ ~flhis repo~ in ~on~eclion .. with the ~~·ertise~enl, P~?moli~n ~r ~aleof ~!Y._rrod~t or p1.?Cess, ~r in <:°nn~~ion w!th 1h? r:-p~blicatio1\ oflhis rtport
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-024C
Client Sample ID: TW 4-16 _ 03182020
I
ANALvr1c•1 1AooaAroa"s Collection Date: 3/18/2020 540h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 2053h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
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 1.00 113
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 17060-07-0 55,2 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.4 50.00 103 80-152
Surr: Dibromofluoromethane 1868-53-7 49.8 50.00 99.5 72-135
Surr: Toluene-d8 2037-26-5 49.6 50.00 992 80-124
Report Date: 3/31/2020 Page 63 of 85
All analyses applicable Lo the CWA, SDWA, and RCRA nrc pcrfonncd in accordimcc to NE LAC pn)lllcols, Pertinent sampling info1 mat ion is located on the attached COC-Con[idcntial Business Information: This repor1 is provided for th~' exclusive usc or the
add1 t'-'>Sl'C Privikgcs of subsequent use of the name nf this cnmµany of any membc1 of ils stalT. or rcproduc1ioi1 of this report in connection with the udvcrtisemctH, promolion or sale or any product or process. or in connection with lhe re-publication of this rcpu1 L
for any pu1 pose other than for the addressee \Viii ~ granted only on con I act. This company accepts no 1esponsibility exccpl f'or the due perfo1mancc of im,pecLion and/01 analysis in good faith and according Lo Lhc rules of Lhe trade and of sdencc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-024
Client Sample ID: TW4-16_03182020
M ,A,n1cA1 , hllo~Ar o Air s Collection Date: 3/18/2020 540h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 239h E3 00.0 1.00 76.2
3/20/2020 1051 h E353.2 0.100 3.91
Report Date: 3/31/2020 Page 31 of 85
All nnalyscs applicabll' to 1hc CWA. SDWA, and RCRA nrc ,~, fonncd in acl.'orc1Ju1!.'c lo NELAC proloccils. Pertinent samplin~ infoimiuil,n is lo~·ntcd on Lhc aLtachOO COC Conlidcntinl Busin~s lnfonn:uiot,: This rcpon is IMO\'illcd for the cx~-h1si,·l' use of lhl·
addtcSSl'C~ Ptivih:gcs of subsequent us1,; of the name l,f this company 01 any member l\f its slaff. 01 rcp1odul.'tion of this rc1)ort i11 rnnncction wi1h the ad.,:cniscmcnc. prornolion or sole or any prodm.;l or pro\'C.'-5. or in l'Onnc..:lion with the rc-p11l>lica1ian of this rcro1t
for any rui JlDSC Olbc1 lhan rm th~-.addressee will bl· gronlc~1 only on cnnlact l11is company a..:l·cpts 110 r,.:,sponsibility ~xccpl ii.n 1hc t1uc pcrfonnam:<-of inspci:tion anJ./01 nnalysis in goC'd fuilh and according 10 lhl.' rules oflhc !lade ond of science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-013C
Client Sample ID: MW-32_03182020
ANALrncA, , •oon•ro""" Collection Date: 3/18/2020 1005h
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1316h
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
17060-07-0
460-00-4
1868-53-7
2037-26-5
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
53.9 50.00 108 72-151
50.9 50 00 102 80-152
48.5 50 00 97 I 72-135
49.5 50 00 99 0 80-124
Report Date: 3/31/2020 Page 52 of 85
All nnalyscs apr,licahk lo 1hc CWA, SOWA, :md RCR;\ MC pe1 Jo1111cd in acc,ml;m~c lo NEL AC prn1oculs Pcrtin<-m sampling i11J'o1 mmi,m is lol·atcti 011 Lhc attached CUC Conlidenliai Business Jn1i,,1 inacion: Thi!> report is pro\'idcd for Lhl' exclu~iw use of th1.•
.iddn .. -sscc. P1ivikges of subscqu~nt use of the name of 1his cl.lmpany 01 any membe1 of its staff. m• rcp1oduc1ion l)f 1his 1.:port in connec1ion wi1h the advertisement. promotion l1r sale of :my pror1uct or process. or in rnnnec1ion wi1h 1hc l'l'-publication of \his repo11
for .iny pu1pose oth.:1 lhan ll)1 th.: addressee will be granted only on conlact This company oc,·cpts no 1.:ic.ponsibili1y .:xccpt for 1hc ,foe perfo,mancc-of inspection andio, anti.lysis in good faith and according 10 th,· rule~ of the had~ and of s.ci~ncc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-013
Client Sample ID: MW-32_03182020
ANA1v11 c:hl ,."o""'o""s Collection Date: 3/18/2020 1005h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 2238h E300.0 1.00 36.0
3/20/2020 I 023h E353.2 0.100 < 0.100
Report Date: 3/31/2020 Page 20 of 85
All analyses applicable Lo Lhc C\VA, SOWA, and RCRA arc pc1fonued in accordance lo NELAC pH)lOcols. Pcnincnt sa111plin~ information is locr11cd on the aLtm.:hcd COC Conlidc111ial Business lnfonn:uion: This rcporl is pro\'idcd fnr the cx~·1t1:-ivl' use Mthc
addn,·ss"c P1 h·ili;;g.cs o[ subscqucnl use of 1hc name of this company or any member ~lf its s1arc or rcpioduction or this 1qmrt in connccLion with 1hc :tdvcrtiscmcnt. promolim, or sale of :my Drodt1cl or process. or in con nee Lion wiLh lhc rc-publicr11io11 of this rcpo11
for any pu1p,,sc olhcr than fi.lr the addressee will be granlcd only on con1a~·l This company i:u.:ccpts no responsibility exccpl J'1.1r Lhc ,iuc p,.:1 foimnncl' of inspccliou and/or anal)·sis i11 g1.wd fohh and nccorcling to lhC' rules of Lhc t1aclc and uf scic11cc,
3440 South 700 West
Salt Lake City, UT 841 I 9
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-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: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-022C
Client Sample ID: TW 4-18 _ 03182020
Collection Date: 3/18/2020 518h
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 2013h
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 Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 57.0
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
54.1
50.1
49.2
48,8
50.00 108 72-151
50.00 100 80-152
50.00 98.4 72-135
50.00 97,5 80-124
Report Date: 3/31/2020 Page 61 of 85
All am1ly.'>cs applicable Lo the CWA. SDWA, and RCRA arc pe1 fo1mcd in accordance to NELAC prn1ocol!-. Pertinent sampling information is localcli on Lhc attached COC ConfldcntiGl Business l11fo1malion: This report is providcli fo1 Lhc cxdusiw usc of the
addre5scc P1 ivilcgcs of ~ubscqucnt usc or the nnrnc nf this company or any member of its staff. m reproduction of this 1cport in connection wilh !he advertisement. prmnolinn or sale or any produ(;t or process, or in conncL:tion with the rc·publication of thi~ repm t
for any pm pose other lhan for thl' addressee will bc granted only on conlact This company accepts no ,l~sponsibility l~xcept ro, the due pc1fo1 mancC" of inspection and/ol'analysis in good failh and ac!.:orrling to thC" rules of the tt-adc and of science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-022
Client Sample ID: TW 4-l 8 _ 03182020
ANA1vr1cA1 1AsonAroa,rs Collection Date: 3/18/2020 518h
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 204h E300 0 1.00 39.4
3/20/2020 1041h E353.2 0.100 3.71
Report Date: 3/31/2020 Page 29 of 85
All tln(llyscs appliuahk lo the CWA. Sl)WA, nml RCR,\ tire pertbm1cd i11 accordance to NELAC prn1ocL1ls Pcnilwlll smnpling inlo1 maLion is IOl'Ulcd on Lhi.: altuchcd COC. Cor11'1denlinl Business lnfo1maLion: This report is provided for Lhl' l.'Xl.'lusivi: use orthl'
addJ'l'SSl'C Privikgc-s o[ subscqul.'t\l llSC of ,he name of thi!> Cl)lllpony nr any rncmbct \)r iLs staff. m rcpiodui:tion nf lhis 11.'porl in i:onnccLion with the advcrtiscrncnL pro11101io11 or sale or any producL or process. or in l'onnection with lhc 1L"-publica1ion or I his rcpoll
tbr ony pui pose uthc1· than li.w the addressee will be-grun1cd only on conlacl. This company acccpL.;; no r~·sponsibility l'Xccpt li.w the due peiformance of inspection c1nd/or .lnalysis ill good foilh and according Lo Lhc rules of the tiadc and or science.
ORGANIC ANALYTICAL REPORT
3440 South 700 West
;alt Lake City, UT 84119
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2002488-004C
Client Sample ID: TW4-19 02192020
Collection Date: 2/19/2020 1415h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 1029h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Phone: (80 l) 263-8686 Surrogate Units: µg/L CAS
Toll Free: [phone]
Fax:[phone]
:-mail: [e-mail]
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
100
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 100 8,720
Result Amount Spiked %REC Limits Qual
5,260 5,000 105 72-151
4,850 5,000 97.0 80-152
4,720 5,000 94.3 72-135
4,830 5,000 96.6 80-124
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/21/2020 1714h
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-d8
Extracted:
Dilution Factor: Method: SW8260D
CAS
Number
Reporting Analytical
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
56-23-5
74-87-3
75-09-2
Result Amount Spiked
53.4 50.00
51.4 50.00
48.1 50.00
50.5 50.00
Limit Result Qual
1.00 13.7
1.00 5.41
1.00 < 1.00
%REC Limits Qual
107 72-151
103 80-152
96.1 72-135
101 80-124
Report Date: 3/9/2020 Page 26 of 50
All annl)'ses applicable lo lhe CWA. SOWA, and RCRA are performed in accordance lo NELAC prolocols, Pertinenl sampling informalion is located on Lhe altached COC Conr'idential Business Jnforma1ion: This repon is pro\'ided for lhe exclU5iYe use oflhe
~ddressee Pri, ile~es o_f sub,.seq~enl ~~e or the ~?1,Ile of this .cor~pany or My ~'?ber of ils slnIT, or reproduclio~ ~rthis repo~ in ~o~eclion ... \\·ith the 4'!~-ertisemenl, P~?motio.n or sale of ~y ~rod~ct or P~?cess, ~r in ~nn~~on w!lh th~ r:-p~blication of I his 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: I st Quarter Chloroform 2020
Lab Sample ID: 2002488-004
Client Sample ID: TW4-19 _02192020
Collection Date: 2/19/2020 1415h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 1734h
2/21/2020 1553h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
£300.0 5.00 205
£353.2 0.200 10.1
Report Date: 3/9/2020 Page 9 of 50
All nnal, ses app\icuble to the CWA, SOWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent swnpling infonnation is located on lhe allached COC Confidential Business lnfonnotion: This report is pro\'ided for the exclusi, e use or the
~ddressee. PriYile~es or sub .. seq~ent ~~e of the ~~e or ~his .con;ipnny or M) ~mber or its slnIT, or reproductio~ ~f this repo~ in ~on~ection .. with the 8'!~ertisemenl, P~?moti~ ~r ~ale of ~!Y ~rod~ct or p~~ess, ~r in ~onn:c~ion w!th th? n;-publicotion of lhis repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2020
Lab Sample ID: 200248&-015C
Client Sample ID: TW4-20_02192020
Collection Date: 2/19/2020 1225h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/21/2020 1240h Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
)alt Lake City, UT 84119
Analyzed: 2/25/2020 1410h
Units: µg/L
Compound
Chloroform
Phone: [phone] Surrogate Units: µg/L
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
Surr: J ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 500 Method:
CAS Reporting
Number Limit
67-66-3 500
CAS Result Amount Spiked %REC
I 7060-07-0 27,100 25,000 108
460-00-4 25,800 25,000 103
1868-53-7 23,800 25,000 95.2
2037-26-5 24,700 25,000 98.8
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1502h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: J ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
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 53.7 SO.OD 107
460-00-4 51.0 50.00 102
1868-53-7 47.7 50.00 95.5
2037-26-5 49.2 50.00 98.4
SW8260D
Analytical
Result Qual
14,300
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
8.60
10.7 *
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
* -This compound exceeded (high) the control limit for the CCV. The compound concenlralion is estimated and may be biased high.
Report Date: 3/9/2020 Page 3 7 of 50
All analyses applicable lo 1he CWA, SOWA. and RCRA are performed in accordance 10 NELAC prolocols Pertinent sampling information is located on the altached COC Confidenlial Business lnformalion: This report is pro\'ided for the exclusive use 0(1he
~dressee. PrfriJe~es or su~eq~tenl ~ of lhe ~~le or this .co~lpnny or any ~mber of its slaff, or reproducli~ ~f this repo~ in ~~eel ion .. with the ~~1ertise~ent, P~?motio.n or ~ale of~·-~rod~cl or P~?Cess, ~r in ~nn:c!ion w~th th~ r:-p~blication of this report
INORGANIC ANALYTICAL REPORT
3440 South 700 West
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2020
Lab Sample ID: 2002488-015
Client Sample ID: TW4-20_02192020
Collection Date: 2/19/2020 1225h
Received Date:
Analytical Results
Compound
2/21/2020 1240h
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
3/3/2020 2252h
2/21 /2020 1529h
Contact: Tanner Holliday
Method
Used
E300.0
E353.2
Reporting
Limit
5.00
0.100
Analytical
Result
310
9.81
Qual
Report Date: 3/9/2020 Page 20 of 50
All analyses applicable lo lhe CWA, SOWA, and RCRA are performed in accordance to NELAC prolocols Pertinenl sampling information is located on lhe auached COC Confidenlinl Business Jnformulion: This repon is pro\'ided for lhe exclusi,·e use of lhe
!ddressee Pri, ile~es o.f su~eq~enl ~~e of the ~?-':"e of lhis .co1t,1pany or any ~mber of its staff, or reproducfio~ ~f this repo~ in ~o"?ection .. with the a~~·ertisemenl, P~?motio
1
n ~r ~a1e of ?1!) ~rod~cl or p~ocess, ~r in ~nn:'~ion "'!'h th~ r~-p~blic.:ition of I his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-005C
Client Sample ID: TW4-21_02192020
Collection Date: 2/19/2020 930h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/21/2020 1240h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 2/25/2020 1049h
Units: µg/L
Compound
Chloroform
Units: µg/L Phone: [phone] Surrogate --------------
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
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 1,070 1,000 107
460-00-4 1,000 1,000 100
1868-53-7 951 1,000 95.1
2037-26-5 988 1,000 98.8
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/21/2020 1734h
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-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 53.8 50.00 108
460-00-4 51.2 50.00 102
1868-53-7 50.1 50.00 100
2037-26-5 50.5 50.00 101
SW8260D
Analytical
Result Qual
844
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
2.58
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 3/9/2020 Page 27 of 50
All analyses applicable lo lhe CWA, SDWA, and RCRA are performed in accordance lo NELAC prolocols Per1inenl sampling informalion is localed on the atlached COC ConUdenlial Business Jnformation: This report is provided for the exclusi,·e use of the
~ddressee~ Pri,·ile~es o,rsub,_seq~enl ~~e of lhe ~:n,ne of Ibis
0
co~pany or any ~~ber ofils slaff, or reproductio~ ~f lhis repo~ in ~rn~eclion~ \\ilh lhe n~~ertise~enl. P~?motio.n ~r ~aJe of~!)~ ~rod~ct or p1:?cess, ~r in ~onn~c~ion w~lh th~ r~-p~blication of Lhis 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: I st Quarter Chlorofonn 2020
Lab Sample ID: 2002488-005
Client Sample ID: TW4-21_02192020
Collection Date: 2/19/2020 930h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/4/2020 952h
2/21/2020 1509h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
£300.0 5.00 446
£353.2 0.100 8.93
Report Date: 3/9/2020 Page l O of SO
All analyses applic:oble to the CWA, SOWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on the attnched COC. Confidential Business lnronnntion: This report is provided for 1he exclusive use oflhe
~ddressee. Prhile~es of su~seq~ent ~~e of lhe ~!11:"e of this .co~pnny or any ~mber of its stnff, or reproductio~ ~~ this repo~ in ~OR)le<:lion .. wilh lhe a~~·ertisement, P~?mo1io_n ~r sale of !11!Y ~rodl~ct or P~?Coss, ~r in ~nn~c~ion w!th th? ~·p~blicntion of 1his report
A merican West
ANALYTICAL LABORATOR I ES
3440 South 700 West
,alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-014C
Client Sample ID: TW4-22_02192020
Collection Date: 2/19/2020 1208h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 1350h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 3,910
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual ----------------------------
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0 5,340
460-00-4 5,020
1868-53-7 4,660
2037-26-5 4,860
--The reporting limits were raised due to high analyte concentrations,
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1442h
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
5,000
5,000
5,000
107 72-151
100 80-152
93.3 72-135
97.2 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 53.8 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.0 50.00 100 80-152
Surr: Dibromofluoromethane 1868-53-7 49.7 50.00 99.3 72-135
Surr: Toluene-d8 2037-26-5 49.2 50.00 98.4 80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 36 of 50
All anolyses applicable lo the CWA, SOWA, and RCRA are perfom1ed in accordance Lo NELAC protocols Pertinent sampling information is localed on the altached COC Confidential Business Information: This report is provided for the exclush e use of the
~ddressee Pri,·ile~es o.f su~seq~enl ~~e of the ~~e of lhis .con;ipany or any ~';1ber of ils staff, or reproduclio.~ ~rthis repo~ in ~on~ection~ wilh the ~~ertise~ent. P~?motio.n ~r ~ale of ~~r rrod~ct or P~?cess, ~r in ~nn;c~ion w!th th~ r;-p~blication of this report
American West
ANAi YTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
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: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-014
Client Sample ID: TW4-22_02192020
Collection Date: 2/19/2020 1208h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2202h
2/21/2020 1527h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 606
E353.2 0.500 57.7
Report Date: 3/9/2020 Page 19 of 50
All anal) ses applicable to lhe CWA, SDWA, and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling infommtion is localed on the attached COC Confidential Business lnformalion: This repor1 is provided for the e:xclusi\•e use of1he
~ddressee. Pri,·ile~es of sub~seq~enl ~?e of the ~~e of this .con:ipany or any ~'!lber of its slaIT, or reproduclio~ ~r this repo~ in .co~1eclion~ with the ~'.:ertise~en~ P~?molio.n ~r ~ale of~!): ~rod1~cl or P~?Cess, ~r in ~OM~c~ion w!th th~ r1;-p~blication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-012C
Client Sample ID: TW4-23_03I 72020
ANAL ,r, c" , A " o HAro"" s Collection Date: 3/17/2020 937h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1256h
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 l.00 < 1.00
75-09-2 1.00 < 1.00
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-mail: awal@awal-l,1bs.com 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
54.5 50 00 109 72-151
51 .7 50 00 103 80-152
49.6 50 00 99.2 72-135
49.7 50 00 99.4 80-124
Report Date: 3/31/2020 Page 51 of 85
All analy~cs applicable to thi.: CWA, SOWA, and RCRA nrc 1x~1'1'01111cd in aci.:orcbrncc Lo N8LAC prolocols. Peni11~·11t sa111rling iufo1 m~nion is Joc:ilcd on 1hc attached COC. CoufidcnLiai llusi11c~s 1nro1mation: This report is providcli for the cxdusivl• usc 0f th~·
Ul1dn .. 'SS(.'C P1 i\'ikg.\.'S of subsequent use of 1he name of Lhis cm11ptmy or auy 111embc1 of i1s staff. or rcptoductioH l1f this 1cport i11 conncc1ion v, iLh lhc advertisement. prorno1io11 or sale oL' any product or process, or in connection wilh the r~··publicntion of Lhis rcpu11
for any purpose 01hc1· thnn ror Lhc addrc.'iscc will bi;:, gnmlcd only on comact. This company accepts no r"sponsibilily CXl'Cpl 1~1r 1hc tiuc ~1 foimanCl' of inspection and/01 analysis in gi.iod foilh nnd ac:cor<ling to lhc-rules of the l1 a,k and of scic11cc
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-012
Client Sample ID: TW 4-23 _ 03172020
ANA1vrrcAr rABosA-roarFs CollectionDate: 3/17/2020 937h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 2148h E300.0 1.00 50.0
3/20/2020 1022h E353 2 0.100 < 0.100
Report Date: 3/31/2020 Page 19 of 85
All analyses applicable to the CWA, SDWA, and RCRA ore pe1 fonned in accordance lo NELAC p1n1ocols. Pcrtinc1u sau1pling infmmaLion is localed on the aLLnchcd COC. Confidential 8usin..-::ss lnl'o1malion: This report is prO\idcd for thl' l'Xdusiw use of the
addrtssC"c P1 ivikgcs or subsequent w;c of the name nf this company or any member of its staff. 01· rcp1oducLion nr this 1cporl iu connection with lhc advcrcisemcnt. promolion or sale or any product or process. or in connection wilh the 1c~p11blicaLion or this rcpoi t
for any pu1 pose other than for the addressee will be granted only on contact. This company acccpl"' no I csponsibility cxccpl Jix 1hc liuc pe1Jo1mance of inspcclion and/01 analysis i11 glWd faith and according Lo Lhc ndcs of the trade and of science
3440 South 700 West
;;alt Lake City, UT 84 l l 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: Ener~ Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-002C
Client Sample ID: TW4-24_02192020
Collection Date: 2/19/2020 1200h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/21/2020 1413h
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 61.7
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: 1,2-Dichloroethane-d4 17060-07-0 55.1 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.0 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 50.1 50.00 100 72-135
Surr: Toluene-d8 2037-26-5 50.8 50.00 102 80-124
Report Date: 3/9/2020 Page 24 of 50
All analyses applicable to lhe CWA. SOWA, and RCRA are performed in accordance to NELAC prolocols Pertinenl sampling infom1ation is localed on the auached COC Confidenlial Business lnfonnalion: This report is pro,·ided for lhe exc.lusi\ e use oflhe
~ddressee. Pri, ile~es of sub .. seq~1enl ~~e of the ~~e of I his .con:ip:lny or any t~~ber of its staff, or reproductio~ ~~ I.his repo~ in ~o~eclion~ with lhc a~~·ertisc~enl, P~?motio.n or ~a1e of :U!Y, ~rod~l or "':ocess, ~r in ~nn~~ion w!th lh~ r~-~blication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-002
Client Sample ID: TW4-24_02192020
ANALvT1cAL LA00RAT0R1Es Collection Date: 2/19/2020 1200h
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: 2/21/2020 1240h
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
3/3/2020 J 700h E300.0 10.0 1,010
2/21/2020 1456h E353.2 0.200 37.1
Report Date: 3/9/2020 Page 7 of 50
All analyses applicable to Lhe CWA. SOWA. and RCRA are perfomled in accordance to NELAC prolocols. Pertinent sampling information is located on lhe au ached COC Confidential Business Information: This reporl is ptO\'ided for lhe e....:clusiYe use of lhe
';'1dressee Prfrile~es o~ sub__seq?ent ~~e of the ~~ne or this .co":'pany or an}' ~':1ber of its staff, or reproduclio~ ~~this repo~ in ~on)1eclion~ with the ~,·ertisement, P~?motio.n or sale of ~!Y ~rod~t or P~?Cess, ~r in 4;0nn~!ion '''!th th~ r~-p~blica1ion or1his repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: l st Quarter Chlorofonn 2020
Lab Sample ID: 2002488-00lC
American West Client Sample ID: TW4-25_02192020
ANALvr1cAL LAB0RAr0R1Es Collection Date: 2/19/2020 946h
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: 2/21/2020 1240h
Analytical Results
Analyzed: 2/21/2020 1405h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: I ,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 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %'REC Limits Qual
53.0 50.00 106 72-151
52.3 50.00 105 80-152
52.8 50.00 106 72-135
51.4 50.00 103 80-124
Report Date: 3/9/2020 Page 23 of 50
All analyses applicable to Lhe CWA, SOW A, and RCRA are performed in accordance to NELAC protocols. PertinerU sampling information is localed on the attached COC Confidential Business lnformalion: This repon is pro\'ided for the exc\usi\'e use of 1he
~ddressee. Pri\'ile~es of sub .. seq~ienl ~~e of the ~~e of this ,con;1pany or M) n~mber of its staff, or reproduclio~ ~f 1his repo~ in ~~eclion .. wilh the a~ver1isement, P~?mo1io.n ~r sale of ~!Y ~rod~cl or p~ocess, ~r in ~onm;.c.tion w~lh th~ n;-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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-001
Client Sample ID: TW4-25_02192020
Collection Date: 2/19/2020 946h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 1644h
2/21/2020 1452h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 2.00 86.0
E353.2 0.100 0.607
Report Date: 3/9/2020 Page 6 of 50
AJI analyses applicable 10 the CWA, SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is localed on the allached COC Conlidential Business [nformalion: This repor1 is provided for lhe exclu.si, e use of the
~ddressee Pri,i le~es of sub__seq~enl ~e of the ~:1':"e oflhis .co~pany or any ~mber ofils slaJT, or reproducli~ ~fthis repo~ in .co~ection .. with the ~\'ertise~enl, P~?moti~ or sale of :U!Y ~rod~cl or p1:ocess, ~r in :°nnl;C!ion w!Lh th~ r1;-p~blica1ion of !his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-029C
Client Sample ID: TW4-26_03182020
ANA,vr1cA1 1 AnoaAioarcs Collection Date: 3/18/2020 635h
Contact: Tanner Holliday
Received Date: 3/19/2020 1420h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
Salt Lake City, UT 84119
Analyzed: 3/23/2020 1424h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20 Method:
CAS Reporting
Number Limit
67-66-3 20.0
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC ---------------------------
Toll Free: [phone]
Fax: (80 I) 263-8687
e-muil: [e-mail]
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
1,060
948
952
959
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/20/2020 2232h
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
1,000 106
1,000 94 8
1,000 95.2
1,000 95.9
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: l,2-Dichloroethane-d4 17060-07-0 54.7 50.00 109
Surr: 4-Bromofluorobenzene 460-00-4 51.2 50.00 102
Surr: Dibromotluoromethane 1868-53-7 49.6 50.00 99.2
Surr: Toluene-dB 2037-26-5 49.0 50.00 97.9
SW8260D
Analytical
Result Qual
1,090
Limits Qua!
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: 3/31/2020 Page 68 of 85
All nna1yscs applicabl~ Lo Lhc CWA. SDWA, and RCRA ore IK'I limned in accord11.11cc to NELAC prn1ocols Pcninc-nt sampling intbrm:uion is locEl!cli on the aum::hcd COC Conli<lcnli.il Ousincss l11f01maLion: This report is pro\'ilicd fo1' th .. • l."Xdusiw ll.\c orthc-
ad<lrl."sm:: Privil~'f!l'S or subsequent u~c or 1he name or Lhis cmnµany l)f 1u1y mcmbc1 Dr its s1arr. m reproduction or thi . .-. 1cp1Hl In conncclion v. ilh the advcrtiscmc111. promolion or sale l1f :my produce or procc.~s. or in conncr.::tion wiLh \he 1\··puhllca1ion or this rcpo1 L
for ,my pu1 pose oLhc,· 1han ror Lh.,,• addressee wilt b.,,· grnnlcd m1ly on rnnta .. ·t This company m:ccpts no r .. ·sponsibility .. ·x~·cpl for 1hc due ~rfo1 man<.:l' or inspection and/01' anr.lysis i11 g'.wd faith t1ncl accorriing to thc rules orthc track and or sdcncc
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-029
Client Sample ID: TW4-26_03182020
ANA1.mc" , AaoaAToa11 s Collection Date: 3/18/2020 635h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 439h E300.0 1.00 36.3
3/20/2020 1104h E353.2 0.100 11.9
Report Date: 3/31/2020 Page 36 of 85
All analyses applicable to the CWA, Sl1WA, nnd RCRA nrc 1,c-1 fonncd i1111ci.:orda.ncc 10 NELAC pro1ocols. Pertinent sampling i11Jb1m:uion is Jo.;-nLcd on 1hc aunchcd CCJC. Conlidi:1lli:1l Business lnl'ormalion: 1his rcporl is provided fo1 lhc .:-xclu1-i\'(' ust: of thi:
addressee Pt h·ilcg('s or subsequent us~ of the name llf this cmnp1my or any member nf iLs staff. m rcprodurtion of lhis 1cport in rnnncc1ion with the ndvcttiscmcnl. promolim1 or sale of any product or process, or in connection with 1hc n.•-publicaiion of lhis rcpo11
for ony pm pL\~.c oth~r lhan fot Lhc arldrc.sscc will bl• granlcd only on conlal·t. This company O!Xcpls no re-sponsibili1y c.i.:..-crl fM 1hc due perfo,mam:L' of i11spccLio11 and/or analysis ill gL)L,d fol1h onc1 occorcling to the rules of 1hc lracle one'! of sdcocc
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-017C
Client Sample ID: TW4-27 _03172020
ANA cn,cA1., ABoR •ro•ies Collection Date: 3/17/2020 1014h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal(i'.i)awal-labs.corn
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1435h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
S urr: 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 8.04
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
54 3 50 00 109 72-151
50.5 50.00 IOI 80-152
48.8 50.00 97.5 72-135
48.9 50.00 97 8 80-124
Report Date: 3/31/2020 Page 56 of 85
All analyses applh;ablc to 1hc CWA. SDWA, and RCRA rirc pe1fonncd in ucconlai1cc to NRLAC prnlocols Pertinent sampling i11fo1ma1i,1n is lol·a1eti on the attached COC. Conlidenlial tlusincss lnfonnation: This rcpon is pro\idcd for th~ ~xd11si..-c-use of th('
.i.ddn.'SS<'c. P, ivileg:es orsubscqn.:111 mic or the name t)f this cM1p,my or ,my member of its staff. or rcprodu .. ·tion of this r.:port in connection "·ith the advcrtiscmcnl. µromolion or sale of any product or pro<'css. or in connection with 1hc n:-publicalion of 1his rcpo11
for ony pu1 pose othe1 lhan for th1.• eddrc.\.~Ce will 1:1..:-grnn1cd only on rnnla1,·t This cmnpany ac .. ·cpts no r1,~sponsibility t,:/iccpt for 1he due pcrfonnancc of inspection and!ot annly~is in good foilh ond nccording to thl' n,lcs. of the track ~nd of science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-017
Client Sample ID: TW4-27 _03 l 72020
ANA,vr1c,1 , •aoi,AroR,rs Collection Date: 3/17/2020 1014h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 055h E300.0 1.00 27.6
3/20/2020 I 033h E353 2 0.200 23.6
Report Date: 3/3 1/2020 Page 24 of 85
All analyses aprlicahlc lo the CWA. SOWA, and RCRA are prrfo11ncd in accorcl;inl'c to NELAC pll)locols Pcni11cm s.iu1pling int'oim;uion is loc~1c(I on the anochcd COC Conlidcntial llusiness lnfrnm:ttion: This repor1 is pro,·i\k"O for th(' cxdusi,·c use ofth~-
adchcssec. P1 i,•ikg-cs of subscquo:nt use or the munc 1lf this com~1:my or any member l)f ils slalT. or reproduction of this I cporl in i.:onncclion with the ad1t·crtiscrncnt, promolion or sale or any producL or process. or in connection with !he rc-publicaLion of this rcpor l
for any pm pose 0Ll11.'r th:rn for th1.• acld rcssec will be grnnlcd only on contact This company act."cpts no responsibility cxccpl fiw the due pc1fo1mnnc1.• of inspection and/or nnalysis in good fo i1h and accorcling 10 thi:-rnlcs of die trn.<lc and o[ science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-004C
Client Sample ID: TW4-28_03172020
AN Acvr,c" , •r,oa•roa 1Es Collection Date: 3/1 7/2020 832h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 93 8h
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-dB
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
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
52.9 50,00 106 72-151
50.6 50,00 101 80-152
48.3 50.00 96.6 72-1 35
49.2 50.00 98.4 80-124
Report Date: 3/31/2020 Page 43 of 85
All annlyscs applicabk• to 1hc C\VA. SDWA, and RCRA an.:: pr1 fonncd in accordai11."c to NELAC prn1nco\s Pcnin~nt &,1;111r,ling infomi:uion is lo1.·a1cd on lhc alt.'lchc(l COC Co111idc1Hial Business lnfonnaLion: This rt."!porl is pro, idOO for th(' exclusiw .. • us1; of ch1..'
add11 .. 'SSf'C Privikg:1..>s of subscgul!nl use of the name of this Cl)lllp1111y or any 111cmbc1 of its s1a1T. or rcprodw:tion of this rcpmt in connection with lhc alkcrtiscmcnl. promolillll or i-alc or any product or prol·css, or in connection with 1hc Tl'-pul>lication of this rcpo11
IOr nnf purpose othc1·1han li.w the-addressee will b1.• granted only on conlacL. This compa.ny OCl'Cpl, no 1esponsil>ilit)" .:-xc-cpt 101 thl' liuc 1>crfo1manc-1.· or inspcl'.'tion andtornnalysis in good failh and according to th(" n,lc., of the-trad.:-and of science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-004
Client Sample ID: TW4-28_03 l 72020
• N "-v" c., , ., a o ",, r o"" s Collection Date: 3/17/2020 832h
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 1737h E300.0 1.00 52.1
3/20/2020 l 005h E353.2 0.200 9.87
Report Date: 3/31/2020 Page 11 of 85
All analyses ar,plii:ahl~' 10 1hc C\VA, SDWA, nnd RCRA ore 1x~1 fonncd in nccorrlrulcc 10 NELAC p1 otocols Pcrtinctll san1pling i11fo1 m:uinn is lo~·ritcd 011 lhc attached COC Conlidc111i.il Ousincss l11tl11 ination: This rcpor1 is prm idcd for the cxdu~iw use or 1he-
add1t."SSL'C P1 ivlkgcs of ~ubscquc1u use of the name of this Cl,1\lpany l,r 11.ny mcml>c1 of its staff. m rcprodu~·Lion llf this rc1>orl in c:onnccLion with the ildvertiscmcnl. promolillll or sale of any producl or process.. or in connection with 1he rl~-publicmion of 1his rcro1 t
for any pui Pl)"'C oLh.:-1 1h::m rrn thl' addresser.; will b,: granlcd only on contal'L This company OC\'cpl:. no rc-sponsibility ,:x,:,cpl fl)I thL' liuc ~rlbtinancc or iuspL"\'tion and/or analysis in gl)l)ci foi1h nnd according to the-rules of the trruk anc1 of science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-027C
Client Sample ID: TW4-29_03182020
ANALrnc", A~oaAroRir s Collection Date: 3/18/2020 612h
Contact: Tanner Holliday
Received Date:
Analytical Results
3/19/2020 1420h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
Salt Lake City, UT 84119
Analyzed: 3/23/2020 1344h
Units: µg/L
Compound
Chlorofonn
Units: µg/L
Extracted:
Dilution Factor:
CAS
10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
Result Amount Spiked %REC Phone: [phone] Surrogate ----------------------------
Toll Free: [phone]
Fax: (80 I) 263-8687
e-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
531
503
486
489
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/20/2020 2152h
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
500,0
500,0
500,0
500 0
106
101
97.2
97.8
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: l,2-Dichloroethane-d4 17060-07-0 54.6 50.00 109
Surr: 4-Bromofluorobenzene 460-00-4 48.0 50.00 95.9
Surr: Dibromofluoromethane 1868-53-7 50.1 50.00 100
Surr: Toluene-d8 2037-26-5 48.5 50.00 97.0
SW8260D
Analytical
Result Qual
652
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qua!
72-151
80-152
72-135
80-124
Report Date: 3/31/2020 Page 66 of 85
All nnaly~cs ai,rlicehli: to Lhc CWA, SDWA, and RCRA arc 1~1 fonncd in occorclancc lo NRLAC p101ocols. Pertinent ~a111plin~ inlbrmn1il1n is locritcd m1 the alt3ched COC. Confidc111inl Ousincss l11ll)11naLion: This report is provided rm the l~xdusi\·i;-use ol 1hc
addrL'SSrc. Pl1\'ill'l,1l'S or subsequent w,c or th~ nnmc or thi.~ l:'Olllpll1\y or any mcinbc1 of i1s slalT. or rcp1oducLio11 of \his 1l!porl in conncciion wilh lhc :idvcniscmcn1. promolim, or sale or nny procluct or process, or in connection with ,he n:-pul>lic:uion of 1his rcpoll
for .:iny pm rms.c oll1~r 1hnn for 1hc oclrlrcsscc will he srnntcJ only on contai:1. This compMy Dl:'ccpL....; no n•sponsibi!ity L'X.ccpt li:i1· 1hc lluc pcrformancl.' of i11spci:Lio11 and/or rinalysis i11 goC'ld foi1h onc1 accorcling to Lhl.' rnlcs ot'tltc 1rn.dc a11cl. or scie11cc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-027
Client Sample ID: TW4-29 _03182020
ANALYTICAL , AGonAroalfs Collection Date: 3/18/2020 612h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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!
3/27/2020 404h E300.0 1.00 41.0
3/20/2020 1057h E353 .2 0.100 3.10
Report Date: 3/31/2020 Page 34 of 85
All nnalyscs applicabk Lo the CWA, SDWA, nnd RCRA nrc pc1 tb1111ed in accordan'°c Lo NELAC p1ntocols, Pertine11t sa111pling inlOrmnlion is lo~·atcd 011 1hc auachcd COC. Confideutinl Business l11fo11naLion: This rcporl is provided for the exclusive u~c or the
nddres~cc Privikgcs of subsequc1u use of th~ name of Lhis company or any mcmbe1 of its slalT. 01 rcpmdm:tion of this rcpon i11 i:onncction \'i ith lhc advcttiscmcnl. promolion or sale of any product or process, or in connection with the rl'-publicaLion of this rcpo1 t
for any purpose othcL lhan for Lhc addressee wi[[ be grnrtlcd only on conlacl. This company ncccpls no r~sponsibiliLy ~xcepl for 1hc due pi::1 fonmincc of inspection and/or analysis i1t good foith nnd according to the-rules of the 1raclc ancl of science.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-019C
Client Sample ID: TW4-30_03 l 72020
ANALYTICAL , AllORATORlfs Collection Date: 3/17/2020 1038h
3440 South 700 W~st
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal(i~uwal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1515h
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
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 Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 53.1
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
54 5 50 00 109 72-151
51 1 50.00 102 80-152
48.9 50.00 97.8 72-135
49.3 50.00 98 6 80-124
Report Date: 3/31/2020 Page 58 of 85
All analyses irrlh:abli.'" to 1hc CWA, SDWA, and RCRA ore ]~l f'o1mcd i11 accorchu1.:c lo NELAC prnlocnls Pcrtinl'1U smnr,ling informn1ion is located on 1hc allachcd COC Conlii.lclllinl Ousincs;s lnlh1maLion: This ri:=port is provhfod for thl~ ~~xi:lrn;i,·C' use of the
addn:ssrc Privill'Sl'S or subsequent use or the name l1f Lhis Cl11llp1my lW any mcmbc1 nf its slal r. oi rcprodm·Lion of this 1cporL in ~·onnct:tion ,,., ith lhc :idvcniscmcnl. pronrnliM or !-ale of :tny producL or process, or in connection with the rl~-publication of Lhi~ rcpo1 t
for any pu1 PL\f.C othc1 lh:tn l'or thC' ac\drcsscc \\:ill bC' grnntcd only on conlact. This company oc~·cpl<; no rL~sponsibility C'Xl'Cpl ror 1hu due pc1J'o1mance or in~C'C'Lion and/01 ~nalysis in gl)Qc\ foilh ancl uccording to the rules of the lladc and of science,
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-019
Client Sample ID: TW4-30_03 l 72020
ANA• vr,cA, , •non,ro""s Collection Date: 3/17/2020 1038h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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)
3!27/2020 130h E300 0 1.00 37.5
3/20!2020 I 035h E353 2 0.100 3.85
Report Date: 3/31/2020 Page 26 of85
All analy~cs applii;ahlc lo the CWA, SOWA, and RCR:\ MC per fonned in accmclan(:e to NEL AC prnrocnl~ Pcrtin~·JH sampling info,matilm is lo~·ntcl1 on rhc altachcct COC C'ouftdcntinl Ousines~ lnlb111L'Hion: This rcpon is pro"idcd for the .!xc\u:-iw 11.'<,c of lh~·
addrt'SSl"C. Pri,•ilcg.cs of subscqui:11t use of Lhe name t,f lhis company or any member of ils slaff. or rcpn>dlKtt<,111 l1f this rcporl iu ~onnccLion with the advcrciscmcnt. µromnlion or sale or :i.ny µroducL or prol·css. or in connection wilh the re-publica1ion af Lhis rcpor L
for .iny purrosc otltl.'r lhan ror lhl' actdrcsscc will b~ grnnlcd onl)• on contact This company ncccpts no N",1,fHtl\triibi liLy except ror Lhi; liuc l)Crformancc of inspection and/or analysis in gl)od foith and accorcling 10 Lhc ndcs of Lite ltacll.' nnd or scicnct:
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-009C
Client Sample ID: TW 4-3 l _ 03172020
ANA,vr,c., 1AsoRAroa,rs CollectionDate: 3/17/2020 912h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1157h
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-dB
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 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
54.1 50.00 108 72-151
51.0 50.00 102 80-152
49.2 50.00 98.5 72-135
49 3 50.00 98.7 80-124
Report Date: 3/31/2020 Page 48 of 85
All rmalyi;cs applicahk Lo Lhc CWA. 8DWA, and RCRA arc pctfonncd ill occordancc tc1 NELAC p11)locols Pcnincnt samplin~ info1mation is localed on the aucn:hcd COC Confldenlinl Business lnfllnnaLion: Thi~ rcporl is provided for Lhc \'Xclusivi: use of the
add1 C-SSl'C P1 ivikges o[ subsequent use or thi.: n:1mc or this company 01 any member of ils s1aff. 01 rcprodul.'lion L)f this report in connection with lhc alivcrtiscmen1, promotion or sale of any produt:t or process, or in connection wilh lhc rc-publlcatlon of I his rcpot L
for any purpose otilc1' lhan rm thi: addressee \'1-'i[[ be granted only on i:ontacl, This company ac~·cpls no ,csponsibilily c,1,.ccpt ll)1 the due pelfo1mGt1Cl' of inspi:ction and/or omalysis in good foi1h and according to Lhl' rules of Lhc traclc and or science
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2020
Lab Sample ID: 2003454-009
Client Sample ID: TW4-31_03 l 72020
Collection Date: 3/17/2020 912h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2020 195 lh
3/20/2020 1018h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.2
E353,2 0.100 0.572
Report Date: 3/31/2020 Page 16 of 85
All t1.nalyscs applii •. -ahk to Lhc CWA. SDWA, and RCRA MC p~• frmncd in accorcla111.·c 10 NGL.AC p101000\s Pcrtim:nl 5;u11pling informniion is lo\·.:11cd on 1hc au,u.:h~-t COC. Confidential Ousincss lnfounation: This r~por1 is pro"idcd for lhl· c>.du:-i,·1.• ui:.i.: of 1h"
.tddn:sscc. Pr ivileg:l's of subscqu1.·nt usc or 1hc n,1mc of 1his Cllllll)illl)' rn' any member of its staff. rn rerrodut."lion of this report in ..:onncction wilh the advcniscmcnl prom,ltion or sale or any product or process. or in .:onncc1ion with the ft'-publicalion of ibis rcro•t
for any pUlp<lSC othc1 lhan r,.1r th .. • addressee ,,. .. ill be granted only on conta~·t. This compa.ny 11c,.·cpt.s no responsibility except li.l1 the \luc pcrfo1mancc of inspl.'\.'Lion and,'01 analysis in gol1d failh nnd according to thC' rules of the 1nul~ and of science_
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-005C
Client Sample ID: TW 4-32 _ 03172020
•N•1vr,c., 1AuonArna"s CollectionDate: 3/17/2020 839h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 958h
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
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-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
53 7 50.00 107 72-151
51 3 50.00 103 80-152
48.7 50.00 97.4 72-135
49 4 50.00 98.9 80-124
Report Date: 3/31/2020 Page 44 of 85
All nnrilyscs applicabk to 1hc CWA, Sl1WA, and RCRA nrc pe1 fonncd in accnrilirncc lo NELAC p1nlocols. PcrLinl.'11t sampling i11l'01mrnion is localed on Lhc auachcli COC, Conlitlc111inl Business lnfb1mation: This rcporl is pro\'idcd for Lhc exclusive use o( the
add1 l'SSl'C P1 ivilcg:cs of subsequent use of 1hc numc of"this company lll' Any member of i1s slHff. or reptodUl'Lion of Lhis I cporl i11 connection with 1hc ndvcniscrnc,u, pro1nolilm or sale or any product or procc.<,s. or in connection with !he rc-p11blicalion of 1his rcpoi L
for CITI)' pu1'pl1.<,c olhcl'thon for Lhl' addressee will be gran1cd only on contact. Ibis company E1cccp1.s; no r?sponsibilily C"x:ccpl ror the due perfo1mancl' or inspection anJ/m· om,lysis i11 gm1d failh and according Lo the rules of the Liadc-,111d o[ science
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-005
Client Sample ID: TW4-32_03172020
Collection Date: 3/17/2020 839h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2020 1754h
3/20/2020 1013h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 59.7
E353 2 0.100 1.97
Report Date: 3/31/2020 Page 12 of85
All nnalyi.es applicahk lO the C\V A. SOWA, and RCRA nre p('1 fo1111cd in cccordnnl.'c to NELAC p1lllOC\lls rcrtil\l.'111 Sl1111(llinl; i111U1ma1itln is lol.'1Hc<1 on the auachcd l'OC. ConJidcnti:11 Uusincss lnlo1 mation: This repon is JlfO\'ilictl for th,: ... ·xdusiw use of 1hc-
odd1 .. 'SWC P1ivikgt·s of subscqu.:n1 use of1hc n.imc of this Cllmpa.ny tll'rui_y member of its shill or rcprodul.'tion llf this ll'l"lrt in connection with 1hoat1vcniscmcnt. promolion or 5alc of any protluc1 or pro,'C.'iS, or in connection with lhc 1\•-publica1ion of1bis. rcpo11
for ony purpusc othtt lhan li.lt' th,: ocldrcsscc will bL· grnn1C\1 only on con\a('t, This company aci:cpl~ no rcsponsil>ilily ,.;,x~·cpl ti.1r the due per fo1manCl' or insp~,lion anJ/01 analysis in g1.1ocl faith ond according to the rules oJ' the Ltad,.;, 1llld uf science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-025C
Client Sample ID: TW4-33_03182020
ANA, vr,c., , •noaAro R,,s Collection Date: 3/18/2020 550h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 2113h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor: 1
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 93.7
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
54.8 50.00
50.6 50.00
49.0 50.00
48.9 50.00
110 72-151
IOI 80-152
97.9 72-135
97.7 80-124
Report Date: 3/31/2020 Page 64 of 85
Alt nnalyscs applicahlr to tht C\VA, SOWA, .ind RCR:\ arc pcdOnncd iu accordan"c to NGLAC prt,rocols. Pertinent samplin~ in!Ormaiion is loct11cd on the auachcd C'OC Conridcnti.:tl Ousin~s Jnfonn:uion: This rcporl is prO\ idcd for th .. ~ cxdu!>i\'C U!.C tlf the
addressee. P1 i,•ilc-gcs or !-ubscqu~ut us~ or lhc name ~lr this Cl)tnpany or a11y membc1 or ils s!aff. 01 rep1 odui.:tion of this rq1orl in con nee Lion with the nd,.·cniseme111. prom1llion or sale or any product or pron;,...s. or In connection wllh !he re-p11lllicnlioo of this rcpo1 L
for any pu1 pose other I hon rrn th,: addressee will he grnnlcd only on conlai:t Tbis comrany oc~·cpts no responsibility except rm Lhc liue pcrfotmMCC' of inspci:-Lion amJ/01' analysis in good foilh and according Lo Lhc-rules oftl1c ltadc and or seicncc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-025
Client Sample ID: TW4-33_03182020
ANA1vr,cA, 1AuosAroairs Collection Date: 3/18/2020 550h
3440 South 700 West
Salt Lake City, UT 841 19
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/27/2020 256h E300.0 1.00 45.3
3/20/2020 I 054h E353.2 0.100 2.44
Report Date: 3/31/2020 Page 32 of 85
All nnalyscs appli4.:ahl~ to the CWA. SOWA, nnd RCR:\ arc 1x·,fonucd in nccorctru11:-c to NELAC p101ocols Pcnim:nr sampling iulormmi,,n is lol·atcd on 1hc aunchcd COC Confidenti:i.l Ousincss lnfo11na1ion: lhis report is pro,·idcd for th.: l'xdusi\'(' use of the
addressee. Pt'ivikgcs a[ subsequent use or lh~ name l,f this company or any member nf ils staff. 01 rcp1oduc1ion ,1f Lhis rcporl in connection with lhc .1dvcrtiscmcnt. promolion or sale of any product or procc.,;s. or in conn cc Lino with the rc-pul>licatilln or this rcpvn
for any pu1posc oth~1 lhan for thi.' aclclrc..<:..scc will be grnnlcd only on conlacL This company accepts no rc.sponsibilily e.-;ccpt ror lhc due pc, fonn:i.ncc or inspi:.cLion and/or analysis in good foilh and according Lo Lhc rules of Lhc track and or science.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-0IOC
Client Sample ID: TW4-34_ 03 l 72020
<NA, vr,cA, , AtloaAro•1rs Collection Date: 3/17/2020 920h
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 l) 263-8686
Toll Free: [phone]
Fax: (80 l) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1217h
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
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 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
Result Amount Spiked %REC Limits Qual
54.1 50.00 108 72-15 l
50.8 50.00 102 80-152
48.2 50.00 96.5 72-135
48.7 50.00 97.4 80-124
Report Date: 3/31/2020 Page 49 of 85
All analyses applicabk' 10 the CWA. SOWA, nnd RCRA arc pi:1 fonncd in accordai1,c 10 NEl.AC p101oco\s Pcnint'tll Mtmrling info1 mmion is Jo"·n1cd on ihc auachcd COC Confidential Busini:ss lnfonna1ion: Toil, rcpon is provillcd for Lh.: \."xdusivc use of the
add1'-'SS1.'C P1 ivikg"-s of subsequent usc or1hc name of 1his company or any member of i1s slalT. or rcprodul.'.'lion of 1his r1.C1>0rl in l·onncc1ion wi1h the adveniscme111. protnolion or sale or any producl or profess. or in conncclion with the t\'-publication of d1is. rcpo1 L
for ony pu1posc olhc, lhan for thl' addressee will be gran1cd only on contal'l This company acl·cpt;, no rl'sponsibility ('xccpt for 1hc tfoc pcrfo1mancc of inspcL'lion and/or analysis in good failh and according 10 lh(' rule.<, of the haclc ond of science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-010
Client Sample ID: TW4-34_03 l 72020
,.,,011AT0R11a Collection Date: 3/17/2020 920h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: ( 801) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 2007h E300.0 1.00 20.1
3/20/2020 1019h E353 2 0.100 1.09
Report Date: 3/31/2020 Page 17 of 85
All analyses applicahk lO the CWA. SDWA, ond RCRA arc pc1 fom1cd in accordani:c lo NELAC p1l)locols. Pertinent sampling info1mmion is loi:alcd on 1hc aLLachcd COC. ConfidenLinl Business lnl'mmation: This report is pro\·idccl for Lhc cxd11sivc use of the
addn:·ssc-c P, ivik'gl~s of subsequent use of the name of Lhis company or any member of its staff. or rcprodu~·Lion of Lhi~ 1~porL in connection with lhc aLivertisemct\l. promolion or sale of any product or process, or in connection with the rc-publicruion of this rcpon
for any purpose other than fm Lhc addressee will rn:" gran1cd only on conlacl. This company acccpl<; no responsibili1y except f'or the due pcrfo1mancc or inspection and/oranalysis in good failh and according to Lht· rules of 1be I rack an<l or science.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-01 lC
Client Sample ID: TW4-35_03 l 72020
ANA,vr,cAL 1.•~on•ro Airs Collection Date: 3/17/2020 928h
3440 South 700 West
Salt Lake City, UT 84 1 19
Phone: (80 I) 263-8686
Toll Free; [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1236h
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
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 < 1.00
74-87-3 1.00 < l.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qua)
54,6
48.3
48.8
48,8
50.00
50.00
50.00
50.00
109
96.6
97.6
97.6
72-151
80-152
72-135
80-124
Report Date: 3/31/2020 Page 50 of 85
All nm,lyscs applicabk-Lo the CWA. SDWA, and RCRA nrc pc1 fo1111cd in accord,111cc lo NELAC prn1ocl1ls, Pcrtinl.'1\1 i,ampling i11l'o1mmi~)n is located on ihc aLLm.:hcd COC t'onfi<lcntinl Ousincs~ l1,(Num.1lot1: Thu, rcp(ut Is ,m~\MCll r.,r1l'l~~~~rlu~h\.· ll<c orlhc
adLlrl"SSC'C. Priv\kgl'S or subscqul.'nl usi.: or the name of lhis company or any member or its staff. or rcpo)J'i.a.1k1u or 1his rl.'porl in connection with lhe ~dvcrtiscmc1,1. µromolilll\ or sale or any prodoc, of ~'CM.. nr ln (()l'll'ICCLion "1th 1ho l\.'•puUl1~lK-Tfl of 1his rcpo1i
for ony purpll~C oth..:r lhan li.1r lhl~ a1ldrcssce will th.· gronlcd only on con1ar1. This company .accepts no h-'Jl*'~ibilily l~xccpt for 1he due pc1fo1mancl· of inspcl·tion and/01 :inalysis in g\100 foith ond «c0t11ing Ki the tnlt' 01"1hc 11,.tc and of tdmcc.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-011
Client Sample ID: TW4-35_03172020
•NA,vr,c,, 1Asoa,.,oairs Collection Date: 3/1 7/2020 928h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 2024h E300.0 1.00 34.5
3/20/2020 1021h E353.2 0.100 0.595
Report Date: 3/31/2020 Page 18 of 85
All OMl)'Ml~ :1pp!it11hk to 1he CW • SOWA. Md ftCRA tile 1>crronncd in acc.:>r<L'Ut("c to NELAC pmtocnls. Pcnin\'nt sampling infonnmitln is loco1cd on the attached COC. Confldcntial Busi111..-ss lnfo11na1ion: This rcporl is pro\·idcd for thl! C'-' hL1l\'I.' u'.i: or the
l\ddtt,.SC • l•ri,•11\•gN t.>ri-ubscquc,n u\C of'ihc: n.uoc,,r th ;,. C'!'U'PJ11Y llr any member llf its staff. or reproduction of thi& r,.-porl in i:onncction wilh lhc ndvcn:iscmcnt. promotinll Of ,i1lo or :my product or prorc~~. or in connection with the rc-publLC\\tlOn of U1is rcpotl
fnrnny pu~ 01Jx"t'th.'ln f'or the 1ddt1S..<ec will bt-lCi'DnU:d only on con1ii.c1. This company ac~·cpts no respom,ibiJiLy ~xccpl f'nr the due pc1f01mam.:c of i11spccLion and/or:malysis in goCld foi1h nnd according to the rules ofLhe trade ottd of science
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-008C
Client Sample ID: TW4-36_03 l 72020
•N•,vr,c•, , AB0n•r o s1Fs Collection Date: 3/l 7/2020 903h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1137h
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 l.00 < 1.00
74-87-3 l.00 < 1.00
75-09-2 1.00 < 1.00
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-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-dB
17060-07-0 53.3
460-00-4 51.4
1868-53-7 48.0
2037-26-5 49.4
50 00 107 72-151
50 00 103 80-152
50,00 96.l 72-135
50.00 98.8 80-124
Report Date: 3/31/2020 Page 4 7 of 85
All nl'l:i.1)1.CiS appliL\\bk Lo iht ('\V • Sl)WA1 and It :•RA ort pi..--rft,rou:-J hi i11ici.:urrl.,m:c to Nl!LA ~ f'M'l\t"C(II~ l'cni11..:-111 wupUng inform.:ullln l,c kk·a1cd on 1hc t1uni.-:hl."1 ( C <'Ntlkl~1ttln! tlu ln-tss lnli.mn:uion: Tht~ rc1w,n ls i,ro\'idc:,t rot th\· '""'du~h"t" u\c of th~
[llitlt().!<('-. Privilq:l: d( su~o,:nl mt ~,riho n:uno ,,r th~ C'OfUJ)Jnr l)f nny mi.111'.:r of ilJ.MAIT~ or: rcprOOn.-.lian (l[ Lhl"t-rq>01L in \·onm:·c•lon whh the advcni~1ncn1. 1-1onl1\lll,h lK' :t-illc ol':m~ pfodu L nr pr°'"~ .... '1r i11 con rte tion wiih 1ho, ... ·,,fl'1ltf!~don of 11\Ls rcpu1 L
for OJ1y purpose UC!'k.·r lhan (a, th~ cdifl'C\.~c \'-Ill be crn.nltd only on tonl-"'l. Thk eotnrW1)"G\l,'Crc,,. 00 N".,.,,on,lhiJily C C:f'I for the Ju-c J",.."110rm!'lincc of in~,1Wn W ~or i,n.il~~\ in g,\(1111 foilt\ and ~ordms-w 1hl.-ruler. ofihc trndtaM ~~r 1.Cil'Dl"C..
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-008
Client Sample ID: TW4-36_03 l 72020
ANAtrncn, 1a11oanrosirs CollectionDate: 3/17/2020 903h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 1934h E300.0 1.00 69.1
3/20/2020 l O l 7h E353 2 0.100 < 0.100
Report Date: 3/31/2020 Page 15 of85
All analy!'ics arplicahk lo lhc CWA. SOWA, nnd RCRA arc 1~1 fonncd in accorda.11l·e 10 NELAC prnloco\s, Pcrlin~nt saa11plin1?, i11fo1m:11ion is lo~o1ed on lhc aunchcO COC Confidcnlinl Businc!".s lnfo,mation: This rcporl is prm·il1cd for 1hr rxdu:-iw use of 1h~'
addrt'Sstc. Privill'gl"s of subscqu.:1u use of 1hc n.1me or this company or any member of its slaff. or rcp;oJUl.1 on of this r~pmt i,1 .:onncction wilh the advertisement promotion or ~ale of any product o, procc.c;s. °' in conncclion wi1h 1hc r.:-·rul>lication of 1his rt:Jlo•t
for any purpose othc1 lh:m li.lr the addressee will be gran1cd only on conta,:t This company accepts no h"5tk)nsibility l'~.:ept for 1hc Jue pcrfo,manc1.• of inspection and/or analysis in good faith and according to thl' rules of the irack and of science.
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-016C
Client Sample ID: TW4-37_02192020
Collection Date: 2/19/2020 1216h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 1450h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
500 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 500 12,000
CAS Result Amount Spiked %REC Limits Qual Phone: [phone] Surrogate -----------------Units: µg/L
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
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
26,600 25,000
24,900 25,000
23,200 25,000
24,600 25,000
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1523h
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
107 72-151
99.7 80-152
92.9 72-135
98.2 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 8.53
1.00 12.3
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 54.5 50.00 109 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.4 50.00 IOI 80-152
Surr: Dibromofluoromethane 1868-53-7 48.5 50.00 97.0 72-135
Surr: Toluene-d8 2037-26-5 49.4 50.00 98.8 80-124
* -This compound exceeded (high) the control limit for the CCV. The compound concentration is estimated and may be biased high.
Report Date: 3/9/2020 Page 38 of 50
All analyses applicable to lhe CW A: SDWA. and RCRA are performed in accordance to NE LAC protocols Per1inen1 sampling information is localed on lhe altached COC. Confidenlial Business [nformalion: This report is provided for the exclusirn use of the
~ddressee.. Pri, ile~es o_f sub,.5eq~enl ~~e of the ~?1:11e of lhis .con_1pany or an) ~i:nber of its staff, or reproductio~ ~f this repo~ in ~on~eclion ... wilh the ~' ertise'!1enl, P~?mo1io.n or sale of~!)'. ~rodl~Ct or p~ocess, ~r in ~nn:c.tion w!th th~ ri;-p~blicalion 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.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-016
Client Sample ID: TW4-37_02192020
Collection Date: 2/19/2020 1216h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2309h
2/21/2020 1530h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 236
E353.2 0.200 28.3
Report Date: 3/9/2020 Page 21 of 50
All analyses applicable 1o Lhe CWA, SOWA. and RCRA are perfonned in accordance to NELAC protocols, Pertinent sampling information is located on the anached COC, Confidential Business Jnformalion: This report is provided for the exclusi,·e use of the
~ddressee PriYile~es o,r sub ... seq~enl ~:'e of the ~~e of Lhis .con_1pany or any ~mber of ils slnIT, or reproduclio~ ~~this repo~ in ~o~eclion_. \\~lh the ~~·ertisen_1ent, P~?motio.n ~r ~ale of :11!). ~rod~ct or p~ocess, ~r in ~nn:_c!ion w!Lh th~ r:_-publication of this report
Client:
Project:
Lab Sample ID:
ORGANIC ANALYTICAL REPORT
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454-014C
Contact: Tanner Holliday
Client Sample ID: TW4-38_03172020
ANALvr,cAL , •Bon•roRirs Collection Date: 3/17/2020 945h
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 1336h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
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 54.7 50.00 109 72-151
Surr: 4-Bromotluorobenzene 460-00-4 50.7 50.00 101 80-152
Surr: Dibromotluoromethane 1868-53-7 48.5 50.00 97.0 72-135
Surr: Toluene-d8 2037-26-5 49.3 50.00 98.7 80-124
The pH of the sample was >2. Analysis was performed wilhin the 7 day holding lime.
Report Date: 3/31/2020 Page 53 of 85
All nnnlp,os applii.:ahr~· 10 Lhl! CWA, SOWA, and RCRt\ ore 1~·1 fo1111cd in occordancc to NEL.AC pro1ocols. Pcnincm ~ampling i11fo1mali\1n is lo~·ntcli on 1hc auo.chcd COC.Conl1dc11tial Ousiucss l111'b1malion: This report is pro\idcd rm Lhc ,~>.clu~ivt.• usc ol lhc
.iddresst•c, Pt i"ilctz~s of subscqucnl use of 1hc name of lhis c,1111pa11y M ;my member of ils slaff. or rcprodut'lion ,,r Lhis rcpnrl in cnnnccLion wiLh lhc advertisement, prom1.11ion or :-ale or any produi..:L or prol'css, or in rnnncction with the n::-public.uion of this rcpm c
for any purpL1sc other 1h:in f1.11 Lh'-' addressee will b'-' P.rnnlcd only on i.:on,a,·l. This compRny eccepls no r1.'sponsibiliLy CXl'Cpl for 1hi.: due pc1fo1 mnm:r of i11spct:lion .,m,J/or analysis i11 Sl'cxl foilh ond accorclin~ lo thl' mies of Lhe traclc a11d of s1.:ic11cc
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-014
Client Sample ID: TW4-38_03172020
ANA, vr, c., , A1, o sAro"" s Collection Date: 3/17/2020 945h
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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!
3/26/2020 2330h E300.0 1.00 33.4
3/20/2020 I 024h E353.2 0.100 8.11
Report Date: 3/31/2020 Page 21 of 85
All nnaly'-CS applicahil' 10 1hc C\VA, SDWA, and RCR:\ rirc p~1 l'om,cd i1, occ1mlancc to NELAC p101oco[s Pertinl'ill sau1pling informntion is lnca1cd on Lhc <1llachcd COC. ConJic..lcnLinl Business l11lb11nation: This report is providcli for th~ l'Xclusiv" u~i.: of Lhc
nlill1 l'Ssrc Privill'gl'S. of subscquenl use of 1hc name of this Clllllpany Lll \Ul)' membc, of its slaff. 01 rcproductiou llf this icp,.ul in conncc1ion wilh the ndveniscmcnl. promo1io11 or sale or any proclui.:l or process. or in connection with the r~-publicn1ion of this rcpon
for on)' pu1posc othi:-r 1han for Lhc acJclrcsscc-will hi:-grnntcl1 only on cnntaN. This company accepts no l"l~ponsibility ~3xccpt f'N the liuc pi:-rroim:rnl'L' or inspection and/01-nMlys.is in £llClcl foilh omt according to Lhc rulc.1; of Lhc track and of ~ic1'(·c,
American West
ANALYTIC.AL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-012C
Client Sample ID: TW4-39_02192020
Collection Date: 2/19/2020 1232h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/25/2020 1309h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: IO
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 812
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: (80 I) 263-8687
:-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
533
502
471
490
--The reporting limits were raised due lo high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1402h
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
500.0 107 72-151
500.0 100 80-152
500.0 94.3 72-135
500.0 98.0 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qua)
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 54.1 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 5 l.l 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 49.5 50.00 98.9 72-135
Surr: Toluene-dB 2037-26-5 50.0 50.00 99.9 80-124
# -This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 34 of 50
All analyses applicable to 1he CWA, SOWA and RCRA are performed in accordance to NELAC protocols. Per1inent sampling information is locnted on the attached COC Conlidenlinl Business lnfonnalion: This report is provided for the exclusive use of the
~ddressee Pri, ile~es of sub .. seq~enl ~e of the ~?1:"'e of this .co~pany or any ~mber of ils slaff, or reproduclio~ ~[this repo~ in ~0°!1ec1ion_ wilh the ~~'ertise~enl, P~?molio.n or sale of ~;y ~rod1~cl or p~ocess, ~r in ~nn~)ion w!lh th~ r~-p~blicaLion of 1his report
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-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2020
Lab Sample ID: 2002488-012
Client Sample ID: TW4-39_02192020
Collection Date: 2/19/2020 1232h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2128h
2/21/2020 1518h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 2.00 76.5
E353.2 0.100 0.792
Report Date: 3/9/2020 Page 17 of 50
All ennlyses applicable to the CWA, SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling information is localed on ~1e auached COC. Con£idential Business Inronnation: This report is provided for the c.\:chL'fih o wci of lhe
~ddressee, Pri\•ile~es o:sub .. seq~ent ~~e of the~~ of lhis .co1~pnny or nny ~~ber or its stn1T, or reproduc1i~ ~f this repo~ in .con~ection .. wilh lhe nc!~ertis~ent, p~moli~n ~ ~ale of ?J!): .rrod~ct or P~?Cess, ~r in ~onn;.c!ion w!th 1h! r:-p~l,tk111 on or 1his n,port
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-003C
American West Client Sample ID: TW4-40_02192020
ANALYTICAL LAB0RAT0R1Es Collection Date: 2/19/2020 1350h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/21/2020 1240h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 929h Extracted:
Units: µg/L Dilution Factor: 10 Method: SW8260D
3440 South 700 West
~alt Lake City, UT 84119 CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 10.0 364
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone] Surr: l ,2-Dichloroethane-d4 17060-07-0 535 500.0 107 72-151
Surr: 4-Bromotluorobenzene 460-00-4 505 500.0 101 80-152
Fax: [phone] Surr: Dibromotluoromethane 1868-53-7 482 500.0 96.3 72-135
:-mail: [e-mail] Surr: Toluene-dB 2037-26-5 492 500.0 98.5 80-124
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/21/2020 1654h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor: 1
CAS
Number
56-23-5
74-87-3
75-09-2
Method:
Reporting
Limit
1.00
1.00
1.00
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 53.8 50.00 108 72-151
460-00-4 51.5 50.00 103 80-152
1868-53-7 49.6 50.00 99.2 72-135
2037-26-5 50.0 50.00 99.9 80-124
Report Date: 3/9/2020 Page 25 of 50
All an.i.lyses applicable to lhe CWA, SOWA. and RCRA are perfom1ed in accordance to NELAC profocols. Pertinenl sampling information is localed on lhe altached COC Confidenlial Business fnformalion: This report is pro,•ided for the e..xclusirn use of lhe
~dressee Pri, ile~es o! sub.5eq~enl ~e of the ~~e of lhis .co"!pany or an) ~mber of its stnff, or reproductio~ ~~ this repo~ in ~o~ection ... \\ilh the "'!~ertise~enl, P~?moli~ or sale of ~y ~rod~r or ~~s, ~r in ~nn~c~ion with th~ r~-publication of lhis 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: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-003
Client Sample ID: TW4-40_02192020
Collection Date: 2/19/2020 1350h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 1717h
2/21/2020 1457h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.5
E353.2 0.100 2.98
Report Date: 3/9/2020 Page 8 of 50
All analyses applicable to lhe CWA, SDWA. and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is localed on the altached COC Confidential Business Informalion: This report is provided for the exclusi,·e use of1he
~ddressee.. Pri,·ile~es o,C sub .. seq?ent ~;e of the ~~e of this .co",lpnny or any ~mber of its slafT, or reproduclio~ ~f Lhis repo~ in ~o~ection .. with lhe &!ver1isement, P~?motio.n ~r ~ale of :11!), ~rod~ct or p~ocess, ~r in ~nn~c~ion ,,·!th th? r~-publicalion of this repon
3440 South 700 West
,alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-01 lC
Client Sample ID: TW4-41_02192020
Collection Date: 2/19/2020 1334h
Received Date: 2/21/2020 1240h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/25/2020 1249h
Units: µg/L Dilution Factor: 20 Method: SW8260D
Compound
Chloroform
CAS
Number
67-66-3
Reporting
Limit
20.0
Analytical
Result
1,200
Qual
Phone: (80 I) 263-8686 Surrogate -------Units: µg/L CAS Result Amount Spiked %REC Limits Qual
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
1,070 1,000
1,030 1,000
937 1,000
990 1,000
107
103
93.7
99.0
72-151
80-152
72-135
80-124
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/24/2020 1342h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer 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
CAS
Number
56-23-5
74-87-3
75-09-2
Method:
Reporting
Limit
1.00
1.00
1.00
Result Amount Spiked %REC
53.9 50.00 108
50.7 50.00 IOI
49.7 50.00 99.5
49.4 50.00 98.8
SW8260D
Analytical
Result
< 1.00
< 1.00
< 1.00
Qual
#
Limits Qual
72-151
80-152
72-135
80-124
#-This compound exceeded (high) the control limit for the CCV. The data is acceptable since the compound was not detected in the
sample.
Report Date: 3/9/2020 Page 33 of 50
All anulyses applicable to the CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinenl sampling information is localed on lhe allached COC Confidential Business lnformalion: This report is pro\'ided for the exclusiYe we of the
~ddressee Pri, ile~es o:sub .. seq~enl ~~e of 1he ~~e of lhis .co1~pany or nny ~mber of its slnlT, or reproduclio~ ~f this repo~ in ~ection~ ,,,ith the ~~enisemenl, p~~motio.n ~r sale of ~!Y ~rod~c:t or p~ocess, ~r in ~nn~c!ion '''!th th~ n;-publication of this repon
3440 South 700 West
3alt 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: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-011
Client Sample ID: TW4-41_02192020
Collection Date: 2/19/2020 1334h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2112h
2/21/2020 1517h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 44.4
E353.2 0.100 6.12
Report Date: 3/9/2020 Page I 6 of 50
All Mnlyses npplicnble 10 the CWA. SOW Ai Rnd RCRA nre perfonned in accordance to NELAC protocols Pertinent sampling informo.1ion is locnted on the aunched COC. Confidential Business Infonnntion: This repon is provided Jar tho e:s:clusivo tne of the
~ddressee, Pririle~es o,r sub,.5eq~en1 ~~e of the ~~e or I his .co1~pnny or any ~r,nber of ils stnlT, or reproductio~ ~r this repo~ in ~on~ection .. wilh the o~~·ertisement, P~?motio
1
n ~r ~ale or~;r. ~rod~cl or p1:?Cess, ~r in ?>nn~~ion ,,·!•h 1h? t:·P~bticn,ion or this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-003C
Client Sample ID: TW 4-42 _ 03172020
ANA ,vr,c" , •r.onA ro a,rs Collection Date: 3/17/2020 823h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 918h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 82600-W-DENlOO
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]
e-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 52.8
460-00-4 50.1
1868-53-7 48.2
2037-26-5 48.8
50.00 106 72-151
50.00 100 80-152
50.00 96.4 72-135
50.00 97.6 80-124
Report Date: 3/31/2020 Page 42 of 85
All anal)'scs applicable 10 the CW/\, SOWA, and RCRA arc 1x-1fo1111cd in accordaJ1.:c to NELAC p1lllocols Pcr1inc1n sampling infonn:nilln is lo.:.:11ccl on 1hc auachcd CCJC, Co11fidcn1ial Businc.,s lnh.l1t11ation: This rcpon is provi,lcd fo1 lhl' .:xdusi\'l' w,c M1hc
add11.'SSl'C P, ivilcgcs or subscqUl'tll use or 1he name or 1his ~,rnpany or 1my mcmbc1 of i1s slalT. 01 rcprndttl·lion of this r('pnrt in connection wilh lhc t\dvcniscrncnl. promotion or i-alc or :rny product or pro\'CS!i. or in i:onnection with 1hc r~-publii::uion ol'1his report
for any ru1 pose oth~r lhnn f,w thl• aclclrcssci: will hi: grnnlcd only on conlal·l This comr,any ac,cpt!i no r~sponsil1i/ity ~>:('cpl li..)r the due per fonmmcc or inspccLion amL'o, anal)·sis in good faith and accorcling to thl' rules of the trt1.<k oHd uf science
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-003
Client Sample ID: TW4-42_03172020
,,.A, vr, c,, , •so ""ro R, rs Collection Date: 3/17/2020 823h
3440 South 700 West
Salt Lake City, UT 84 l 19
Phone: [phone]
Toll Free: [phone]
Fax: ( 801) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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
3/26/2020 1720h E300.0 1.00 23.2
3/20/2020 100 lh E353.2 0.100 2.88
Report Date: 3/31/2020 Page 10 of85
All nmil):!liC> :applicdlk to 1hc CW,\, SOWA.,i.nd A. 'R,\ Mi.: Jll(f'formi:d lo 11e1,'ffl'duiccto 'fiLAC pn.ll~'C:Ol\.. Patin~n1/,,:llllflling uH"brnuuian 1"" Cni;-a1cd on 1bc 1:1und11, ... t ("(){ .. f'onl1rJc::111bl UU\in4S ln(om~1rnn: Thi., Ji.'i'W'lr1 ts provi,kd r\lf 1ht!t-.1.1i.•lu!iin• use o!'ih..-
nMn.~-c-l'rh·\kg~ or~ob.c.cq11~111 ut.0 of1hL, n:uno nrihb c-xupnuy ~11,1y mc:mb..Y ,)(ilJ )Iii.ff. 01 n7JWt"HhK'lio11 of thh, n1>i'1rt i11 "onn,,,,'""1fon \\ hh 1hc advcn n\¢111, 1mnno1lro or Mtc or Mr pn)dUl.'.t ot-fl('IXG.'l.<. nt iJ1 ~i,noclion wi1b 1h~ n'-ru~k;ui()n of this rcpo1 l
for ony rurp;.:t.qJ otl1~·, 1hnn for Lh~' "™1~,;i:ci wm lk.• ,t;nnuiJ bl'll)' oi1 C'onla-1.·L ll,i( 1:ornp.'t.11} ac~·cpt, ni>n-,.pcmsibili1y ,~~ ... "'(rt r~w 1ht' ,1uc p..,·nwm.incc or i11\~--&ion :1~/ort\Ml)-s~ 1n soJIOII r1111h and ~In~ 10 1lw tol~ 01'11, .... trnd.:-#"!Wl ttr M."lc:nN.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2002488-017C
American West Client Sample ID: TW4-60_02192020
ANALvncAL LAaouroR1Es Collection Date: 2/19/2020 900h
3440 South 700 West
~alt Lake City, UT 84119
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/21/2020 1425h
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
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 54.0
460-00-4 48.7
1868-53-7 53.4
2037-26-5 59.6
50.00 108 72-151
50.00 97.4 80-152
50.00 107 72-135
50.00 119 80-124
Report Date: 3/9/2020 Page 39 of 50
All analyses applicable to lhe CW A. SOW A. and RCRA are perf'onned in accordance to NELAC prolocols. Peninent sampling information is localed on the oltached COC. Conridenlial Business Information; This report is pro\'ided for !he exclusiye use of lhe
~ddressee, Prh·ile~es o_f sub,,seq~enl ~e of the ~~e of this .con:1pany or any ~mber of its s1aIT, or reproducli~ ~f this rcpo~ in fo~eclion .. willt lhe a~:enise'?enl, P~?mo1io.n ~r ~ale of ~!Y ~rod~cl or p~ocess, ~r in ~nn~c.lion w!th t~ r~-p~blicalion of this report
3440 South 700 West
Mt 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: l st Quarter Chloroform 2020
Lab Sample ID: 2002488-017
Client Sample ID: TW4-60 _ 02 I 92020
Collection Date: 2/19/2020 900h
Received Date: 2/21/2020 1240h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2020 2326h
2/21/2020 1531h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100 ----
Report Date: 3/9/2020 Page 22 of 50
All analyses applicable 10 lhe CWA, SOWA, and RCRA are performed in accordance to NELAC protocols_ Pertinent sampling infom1alion is located on the allached COC Confidential Business Information: This repon is pT0\1ided for 1he (\XChni,c, U!e of the
~dressee_ Pri,ile~es o~sub~seq~nl ~e of the ~~e of this .co~pany or any ~'!1ber of its staff, or reproducli~ ?.~this repo~ in f0~1ection .. wilh the «<!~ertise~enl, P~?motio.n ~r ~ale of ~!Y. -~rod~cl or P~?ce~s, ~r in ~nn:C!ion '''!th 1h~ n_:-publicn1lon or this repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-030C
Client Sample ID: TW 4-65 _ 03172020
ANAL vr, c., 1.1.r, o R Aro R, rs Collection Date: 3/17/2020 805h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/23/2020 1225h
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: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
e-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
53.3 50 00 107 72-151
48.1 50.00 96.2 80-152
48 9 50 00 97.8 72-135
48.2 50.00 96 3 80-124
Report Date: 3/31/2020 Page 69 of 85
All analysus applit:ablc to 1hc CWA. SDWA, nttd RCl(A .\re pL'rfonncd ill 11ccorda11cc 10 NGL AC prnlnctlls. Pcni11c111 .'*1UPlin~ i11fo1ma1ion is localed on the aunchccl CCX:, Coulidcntinl Business l1Uh1maLion: This report is prm·il"lcd [01 Lhc CAclusiv,: use ol Lhc
::iddn:~>Sl'e. Privileges of subsequent use of llu: n:une !.'lr1his Clltnpany or any member llf its staff. or rcp1\JJm·1io11 llf this rcr)Ort in connection with lhc advcniscmcoL promotion or ~le or any product or process.. or in connection with the rc-pul>Jic:llion of this rcpo1 L
for any pu1pl1sc othc1 than ror thl' addressee will be grnnlcl1 only on contact This company oc~·cpts no n; ~ibilily cxccpl for the due pcrformancC" ofi11spectiou and/or nnnlysis in gm,d faith rmd accorcling to Lh1; rules of the trade .:rnd of science.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-030
Client Sample ID: TW4-65_03172020
ANA1vric" , AllnnATOA!fs Collection Date: 3/17/2020 805h
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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)
3/27/2020 456h E300.0 1.00 26.0
3/20/2020 1105h E353.2 0.100 6.38
Report Date: 3/31/2020 Page 37 of 85
All nnc,t~'ICS ~rrt c::ilik to the CW , • OWA1 ~n,d RCRA nrti.· 1>r1.·tfonncd in accordance to NGL.AC pmtllcols. Pcrtincm sarnrling infonn,uion is localed on the auachcd COC. Conlidcnlial Business lntO,mation: This report is pro\'idcd for th~ cxdu:-ivc use of th<'
add, ~ P,ivih.ito or subscqui:1H u,~ \)(tho M111cof this C-t)llipany or ;my member of its staff. or rcprnd11l'lio11 of this r.:port in l'Onncction wilh the adveniscmcn1. pronin1ion or sale of any product or proi'CS,S,. or in conncc1ion with lhc re-public.:uion of this rcpo11
for oil)!" pm11~ 01h,•.t than for 1hi· ,tddr~.,.Kc \\UI b\~p11n1cd only on conlai·t TI,is company accepts no 1.:s.ponsibiJiLy L'xccpt for 1hc iluc perfo1manCl' or irn~pcction and/01·analysis in good foith and accorcHng Lo LhC" rules of 1hi:: trade mtd or science
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454-03 l C
Client Sample ID: TW 4-70 _ 03172020
AN" vr, c" , ""a" Aro s" s Collection Date: 3/17/2020 1024h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 2312h
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 14.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: ( 80 l) 263-8687
e-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 54.3
460-00-4 49.9
1868-53-7 48.4
2037-26-5 48.5
50 00 109 72-151
50 00 99.8 80-152
50,00 96,9 72-135
50,00 97.0 80-124
Report Date: 3/31/2020 Page 70 of 85
All analyses applit..:llllk' Lo Lhc C\VA.. SDWA, and RCRA nrc 1x'rfon11cd i11 occordi1ui:-c to NELAC p101ocols Pcrli11i:11t sr1rnpling information is locmcd on Lhc aHachcd COC. Conlidc111inl Business lnli.rnnation: This report is pro\'ilicd ror the l.">.i:lu:;in-use orth,:
addn:·ssrc, Pri\'ilL.'g-cs or subsegul.'nt u.w oflhc nnmc l,f this et,mpnny or auy member or i1s stal'C 01 reprodnl.'tion of this 1~p1m iu L'onnceLion with the ndvcnisemcn1. 11romo1ion or sale ol' any prorlucL or process, or in connccLion wiLh lhc r,:.publica1ion of this repoit
for :my purr,o!ic 01h~r than for thi: addressee \\·ill ~ granted only on conlal'L, Titis company accepts no responsibility except 1'1.11 1hc 1.luc pc, f'o1 mrincc or inspection and/or analysis in g1.)od foilh onrl according to thL· mies of the \Lack• ::met of science,
At rnt;·r~r:~_.~ii~~ \ ~:::--:: 1.
ANAI.YTfC/\.L l ABORATOA1rs
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
e-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: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-031
ClientSampleID: TW4-70_03172020
Collection Date: 3/17/2020 1024h
Received Date: 3/19/2020 1420h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/27/2020 513h
3/20/2020 1106h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 48.4
E353.2 0.100 7.72
Report Date: 3/31/2020 Page 38 of 85
All 11Mly1,c,: applicab1~~ to lhc CWA. SDWA, ljlnd ftCkA nri: performed in aceorctani:c to NELAC p1n1ocol~ PcrLincl\l sR111plin~ i11lb1ma1ion is lo('lllCl1011 the allllchcd COC. Connde11Linl Business l11ll1nnation: This rcpnn is provilicd for Lhl~ l~>.d usiv(' use of the
addh.~¥,"'C'. l1rivih:gl'S of subsequent use of 1hc n:ur,o .'If this company or any member of ils stall. or rcpt1khl(tfo11 t)f Lhi.~ r,.:porl in i:onnection with the :1dve11iscmcnt, pro11101iot1 or sale of :my prodm;t OJ~~ or in connection with lhc rl·-publica!ion of ll1is rcpoi c
for tiny purpose 01he1 than I'm the addressee will he grnnlcd only on con1a1..'l. This company ac~·cpls no r,.,.ptlnsibilil)· ,,x,cpl for 1hc \foe pcrfonmincr or i11spc1..·tio11 and/or analysis in gt)od foilh aml t1c~di1~ to lh<' mies oflhc 11ad~ and of science.
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-032C
Client Sample ID: TW4-75_03182020
ANA,vnc AL, Asos•roR1rs Collection Date: 3/18/2020 1005h
3440 South 700 West
Salt Lake City, UT 84119
Received Date: 3/19/2020 1420h
Analytical Results
Analyzed: 3/20/2020 233 lh
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
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: ( 801) 263-8687
e-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 54.3
460-00-4 50.6
1868-53-7 48,l
2037-26-5 48.9
50.00 109 72-151
50.00 IOI 80-152
50.00 96.1 72-135
50.00 97.7 80-124
Report Date: 3/31/2020 Page71 of85
All analyses :tflflllcc.bk lo lhc CWft., SOWA. and R<;ltA "fe IJr..'ifom1cd i,1 occordanl'.'c 10 NELAC pm1oculs. Pcrtint.'nt sampling iuformmion is lo,at~d 0111hc aum.;hcd COC. Con11dcnlial Business Information: This t(:porl is pro\'irlcd for lht.·1.·x,:lu~iw u!<.c of lht·
addn"Sscc. PrivU"t;e1, of subscq\liii.'111 u,o Qr1hc n:amc 1lrthJu :tt1llJltlin)' \lr any member t,f its staff. \)r rcpruduction tlf this rc1>or1 in l'Onncction with the :i.dvcniscmcnt. promoliM or sale of any product or procC!>!>. or in connection with 1hc rc-public:i.tion of Lhis rcpo1t
for ony purpDiO oth.·t' lh.:in for the iuMn:i.\~c \\ill 11\.~ ffllllllll:'J only on conla\.'L Tiiis compM)' nc~·cpls no rC"sponsibiliLy \.~xccpL for the due pcrfo1mnncc-of im,pcction and/01 analysis in gooct foi1h and according to the-rules oflhc Lradc and of science.
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2020
Lab Sample ID: 2003454-032
Client Sample ID: TW4-75_03182020
ANALn1cA1 , Aoon A10 ••'" Collection Date: 3/18/2020 1005h
3440 South 700 West
Salt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal@a wal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2020 1420h
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!
3/27/2020 530h E300.0 1.00 34.8
3/20/2020 1136h E353.2 0.100 < 0.100
Report Date: 3/31/2020 Page 39 of 85
All niut)\\CS , pPlt4'3ble to the CWA, Rl'>\V A, .ind RCR A arc p, .. ,formcd in aci.;ordan~·e 10 NELAC p1iuoo.,k,. Pcnincn1 sampling informn1i1,11 is localed on 1h~ auachccl C'OC. Cool11lentint Businc:-s li1fo11n:uion: This rcpo11 is pro\'idccl for Lhi: exdu4 · u~ or th\'.'
ndd1'\"S.)(('. PtivHey:l"' or s.ubscq1k'IU tJ\.C "r lhi: n~,m ,1( this C(l!1tpu.o.y m any member of its slalT. or r~pruth1~·1ion of this report iu connection with the rtl1\.cniscmcnt, promotion oc ~1t or any product or process. or in connection wiLh !he rc-publiccillM or this rcpo1 t
for An)' (K,lrp~~c 1,illlJ\.'T lhan for 1hr oddra,.1(:i; will be tJ(t.lnlcd oolr on contact This company ac.:cpts no rcsponsibilily except ro1 the due P'!l'fo1 mane" of i11spccLion and/or analysis in good failh and accor<ling to lhr: rules ol'Lhc Lrack and of science
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.
1st Quarter Chloroform 2020
2002488-018A
Client Sample ID: Trip Blank
Collection Date: 2/19/2020 900h
Received Date: 2/21/2020 1240h
Analytical Results
Analyzed: 2/21/2020 1445h
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
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 53.3 50.00 107 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.0 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 53.3 50.00 107 72-135
Surr: Toluene-d8 2037-26-5 51.2 50.00 102 80-124
Report Date: 3/9/2020 Page 40 of 50
All anaJyses applicable 10 lhe CWA SDWA, and RCRA are perfonned in accordance to NELAC prolocols Pertinent sampling informa1ion is localed on the at1ached COC Conl'idential Business Information: This report is pro,1ided for the exclusiYe use of1he
~ddressee. Pri, ile~es o_f sub__seq~enl ~~e of the ~~e of this _con:ipany or any ~~ber of its staff, or reproduclio~ ~~ this repo~ in ~o~eclion .. with the ~~ertise~enl, P~?motio.n ~r ~ale of :11!). ~rod~cl or P~?cess, ~r in ~nn:c~ion w!th th7 r1;-p~blication of lhis report
ANAlYTlCAt I AHORATOAlfS
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454-033A
Client Sample ID: Trip Blank
Collection Date: 3/16/2020
Received Date: 3/19/2020
Analytical Results
Analyzed: 3/20/2020 1854h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
745h
1420h
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
52.3
46.8
46.9
47 2
50.00 105 72-151
50.00 93.5 80-152
50.00 93.8 72-135
50.00 94.4 80-124
Report Date: 3/31/2020 Page 72 of 85
All nnalyr.cs applicable Lo Lhc CWA, SDWA, and RCRA arc pe1 fonncd in accordance lo NELAC p]l)IOcols Pertinent smupling inlb1 mnlion is localcli Oil Lhi.:: alluchcd CDC Confidenlial Business lnl{mllation: Thi5 report is provided for the exc\usi\'C ur.c of the
add1 e.ssl'c Prh•ilcges or subsequent use or the namr.; of this company or any member of its staff. oi rcprnduction or this I cport iu connci::tion with !he advcniscment. pro11101ion or sale or any protlui::L or process, or in connection with lhe re-publication of this repolt
for any pm pose olhcr than for the addressee will b? granted only Oil contact This company accepls no responsibility except l'or 1hc due pc1fo1mancl' of inspcclion and/01 analysis in good faith and accorclin~ Lo Lhc.' rules of Lhc track and of science
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2020
Dear Tanner Holliday:
3440 South 700 West
Lab Set ID: 2002488
;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
American West Analytical Laboratories received sample(s) on 2/21/2020 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,
Approved by:
K I F Digitally signed y e . by Kyle F. Gross
Date:
Gross 2020.03.09
· 12: 13:56 -06'00'
Laboratory Director or designee
Report Date: 3/9/2020 Page I of 50
All an.:ilyses applic.1ble to lhe CWA, SDWA. nnJ RCR,A OJC perfom1ed in accordance 10 NELAC prou~otJ. Pertinent snmi>ltng iurom\nlion is located on the au ached COC. Confidcntiul Business lnrormation: This report is provided ror 1hc csclush-e. ~ or1he
~ddressee. Pri,·ile~es o.f sub~seq~enl ~~e of tht: '!~(I of I his .con:1-pany or any ~'!lber or its slaff, or fCfUoduclim~ ~f this YC?Df.! m ~~1cc-1rnn,, ,vilh the n~Yertise'!1enl, P~?moli"'.'1 ~ gale of ~lY ~rodt~cl or p~ocess, ~r in ~onn~c!ion w!lh 1h~ ~·'"!blic:111ion er !his report
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: I st Quarter Chloroform 2020
Lab Set ID: 2002488
Date Received: 2/21/2020 1240h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2002488-00lA TW4-25 02192020 2/19/2020 946h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2002488-001B TW4-25 02192020 2/19/2020 946h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-001 C TW4-25 02192020 2/19/2020 946h Aqueous VOA by GC/MS Method
8260D/5030C
Phone:[phone] 2002488-002A TW4-24 02192020 2/19/2020 1200h Aqueous Anions, E300.0
2002488-002B TW4-24 02192020 2/19/2020 1200h Aqueous Nitrite/Nitrate (as N), E353.2 Toll Free: [phone] 2002488-002C TW4-24 02192020 2/19/2020 1200h Aqueous VOA by GC/MS Method
Fax: [phone]D/5030C
:-mail: [e-mail] 2002488-003A TW4-40 02192020 2/19/2020 1350h Aqueous Anions, E300.0
2002488-003B TW 4-40 02192020 2/19/2020 1350h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2002488-003C TW 4-40 02192020 2/19/2020 1350h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-004A TW4-19 02192020 2/19/2020 1415h Aqueous Anions, E300.0
Kyle F. Gross 2002488-004B TW4-19 02192020 2/19/2020 1415h Aqueous Nitrite/Nitrate (as N), E353.2
2 0024 8 8-004C TW4-19 02192020 2/19/2020 1415h Aqueous VOA by GC/MS Method Laboratory Director 8260D/5030C
2002488-00SA TW4-21 02192020 2/19/2020 930h Aqueous Anions, E300.0
Jose Rocha 2002488-00SB TW4-21 02192020 2/19/2020 930h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2002488-00SC TW4-21 02192020 2/19/2020 930h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-006A TW 4-02 02192020 2/19/2020 1305h Aqueous Anions, E300.0
2002488-006B TW 4-02 02192020 2/19/2020 1305h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-006C TW4-02 02192020 2/19/2020 1305h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-007 A TW 4-01 02192020 2/19/2020 1324h Aqueous Anions, E300.0
2002488-007B TW 4-01 02192020 2/19/2020 1324h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-007C TW4-0l 02192020 2/19/2020 1324h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-008A TW 4-04 02192020 2/19/2020 1340h Aqueous Anions, E300.0
2002488-008B TW4-04 02192020 2/19/2020 1340h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-008C TW4-04 02192020 2/19/2020 1340h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-009A MW-04 02192020 2/19/2020 1315h Aqueous Anions, E300.0
2002488-009B MW-04 02192020 2/19/2020 1315h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-009C MW-04 02192020 2/19/2020 1315h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-01 OA MW-26 02192020 2/19/2020 1240h Aqueous Anions, E300.0
Report Date: 3/9/2020 Page 2 of 50
All nnalr ses applicable to the CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is located on lhe allached COC. Confidential Business Information: This repor1 is pro,•ided for the exclusirn use or the
~ddressee Pri, ile~es o.f su~seq~ent ~~e of the ~~e or this .co11;pany or nfl)' ~~ber of its staff, or reproduclio~ ~f this repo~ in .co~eclion .. "ith the «<!~'ertisement, P~?motio.n or sale of ?1!Y ~rod~ct or P~?cess, ?r in ~nn~c!ion w~lh th~ r~-publicalion of lhis report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
American West Lab Set ID: 2002488
ANALYTICAL LABORATORIES Date Received: 2/21/2020 1240h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2002488-01 OB MW-26 02192020 2/19/2020 1240h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2002488-01 oc MW-26 02192020 2/19/2020 1240h Aqueous VOA by GC/MS Method
8260D/5030C
;alt Lake City, UT 84119 2002488-01 lA TW4-41 02192020 2/19/2020 1334h Aqueous Anions, E300.0
2002488-011 B TW4-41 02192020 2/19/2020 1334h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-011 C TW4-41 02192020 2/19/2020 1334h Aqueous VOA by GC/MS Method
Phone:[phone]D/5030C
2002488-012A TW4-39 02192020 2/19/2020 1232h Aqueous Anions, E300.0
Toll Free: [phone] 2002488-012B TW4-39 02192020 2/19/2020 1232h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 2002488-012C TW4-39 02192020 2/19/2020 1232h Aqueous VOA by GC/MS Method
:-mail: [e-mail] 8260D/5030C
2002488-0BA TW4-ll 02192020 2/19/2020 1250h Aqueous Anions, E300.0
web: www.awal-labs.com 2002488-013B TW4-ll 02192020 2/19/2020 1250h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-0 l 3C TW4-ll 02192020 2/19/2020 1250h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-014A TW4-22 02192020 2/19/2020 1208h Aqueous Anions, E300.0 Kyle F. Gross 2002488-014B TW4-22 02192020 2/19/2020 1208h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2002488-0 l 4C TW4-22 02192020 2/19/2020 1208h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2002488-015A TW4-20 02192020 2/19/2020 1225h Aqueous Anions, E300.0
QA Officer 2002488-015B TW4-20 02192020 2/19/2020 1225h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-0 l 5C TW4-20 02192020 2/19/2020 1225h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-016A TW4-37 02192020 2/19/2020 1216h Aqueous Anions, E300.0
2002488-016B TW4-37 02192020 2/19/2020 1216h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-0 l 6C TW4-37 02192020 2/19/2020 1216h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-017 A TW4-60 02192020 2/19/2020 900h Aqueous Anions, E300.0
2002488-017B TW 4-60 _ 02192020 2/19/2020 900h Aqueous Nitrite/Nitrate (as N), E353.2
2002488-0l 7C TW4-60 02192020 2/19/2020 900h Aqueous VOA by GC/MS Method
8260D/5030C
2002488-018A Trip Blank 2/19/2020 900h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/9/2020 Page 3 of SO
All analyses applicable 10 the CWA, SDW A. and RCRA are performed in accordance 10 NELAC prolocols Pertinent sampling inrorma1ion is located on the altached COC Confidential Business lnformalion: This report is provided for 1he exch1.~h e use of lhe
~ddressee Prl\"ile~es o.r sub .. seq~ent ~~e of !he ~~e of this .con:ipany or any ~mber of ils staff, or reproduclio~ ~f this repo~ in ~o~ection .. \\~th the D~vertisement, p~~motio~ ~r saJe of ~y ~rod~cl or p~~s, ~r in ~""~!ion w~th th~ r:_·publicillion 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 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:
l st Quarter Chloroform 2020
2002488
2/21/2020
2/19/2020
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, RPO :
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: 3/9/2020 Page 4 of 50
AH analyses applicable to lhe CWA, SDWA, and RCRA Elfe performed in accordance to NELAC prolocols-Pertinent sampling information is located on the altached COC Confidentlal Business lnfonnation: This repon is provided for the exclush e use of the
~ddressee Pri, ile~es o_f sub~seq~enl ~~e or the ~:u:ne of this _cot1,1pany or any ~mber or ils staff, or reproduclio~ 2f this repo~ in ~on?ection,. ,viU1 the ~vertisement, P~?motio.n ~r ~aJe of?-'!): ~rod~cl or P~?cess, ~r in ~nn~c~ion w!th th~ r~-publication of this report
3440 South 700 West
;alt Lake City, UT 84 I 19
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
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:
1st Quarter Chloroform 2020
2002488
2/21/2020
2/19/2020
Intact
None
SW-846 8260D/5030C
Volatile Organic Compounds
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, 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: 3/9/2020 Page 5 of 50
All analyses applicnble to lhe CW A. SOWA, and RCRA are performed in accordance to NE LAC prolocols~ Pertinent sampling information is located on Lhe altached COC_ Confidential Business lnfonnation: This report is proyided for the e:-.clusi,·e use of 1he
~dressee Pri, ile~es o,C sub,_seq~ent ~~e of lhe ~:11:°e of I his .con;ipany or any ~mber of ilS slaIT, or reproductio~ ~~ Lhis repo~ in ~o~ection_ \\"ilh the o~,•ertisemenL P~?motio,n or sale of?-'!~. ~rodl~ct or p~ocess, ~r in :onn~c~ion "'!th th? r~-p~blicalion of this report
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: 1st Quarter Chloroform 2020
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-Iabs.com
_QC SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QC Type:
Amount
Spiked
Tanner Holliday
WC
LCS
Spike Ref.
Amount %REC
Lab Sample ID: LCS-R136353 Date Analyzed: 03/03/2020 1627h
Test Code: 300.0·W
Chloride 5.47 mg/L E300.0 0.0565 0.100 5.000 0 109
Lab Sample ID: LCS-R135994 Date Analyzed: 02/21/2020 1432h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.01 mg/L E353.2 0.00494 0.0100 1.000 0 101
Limits
90 -110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPD
Amt % RPD Limit Qual
Report Date: 3/9/2020 Page 41 of SO
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 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: 2002488
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: MB-R136353 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R135994 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
03/03/2020 16 l Oh
mg/L E300.0 0.0565 0.100
02/21/2020 1430h
mg/L E353.2 0.00494 0.0100
Tanner Holliday
WC
MBLK
Spike Ref.
Amount %REC Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
Report Date: 3/9/2020 Page 42 of 50
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 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
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2002488-006AMS Date Analyzed:
Test Code: 300.0-W
Chloride 95.3
Lab Sample ID: 2002488-01 OAMS Date Analyzed:
Test Code: 300.0-W
Chloride 140
Lab Sample ID: 2002488-00 lBMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.70
Lab Sample ID: 2002488-004BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 30.1
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 RE~ORT
Contact: Tanner Holliday
Dept: WC
QCType: MS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/03/2020 1824h
mg/L E300 0 0.565 1.00 50.00 42.1 106 -03/03/2020 2038h
mg/L E300.0 0.565 1.00 50.00 88.9 103
02/21/2020 1454h
mg/L E353.2 0.00494 0.0100 1.000 0.607 109
02/21/2020 1554h
mg/L E353.2 0.0988 0.200 20.00 IO.I 100
Limits
90 -110
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 3/9/2020 Page 43 of 50
analyses applicable to the CWA, SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sarnp]ing information is located on the attached COC Confidential Business [nforrnation: 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-pub} ication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 70~ West
' Kyle F. Gross Salt Lake City, UT 84119
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: Tanner Holliday
Lab Set ID: 2002488 Dept: WC
Project: 1st Quarter Chlorofonn 2020 QC Type: MSD
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 2002488-006AMSD Date Analyzed: 03/03/2020 184 lh
Test Code: 300.0-W
Chloride 95.I mg/L E300.0 0.565 1.00 50.00 42.1 106 90 -110 95.3 0.260 20
Lab Sample ID: 2002488-01 OAMSD Date Analyzed: 03/03/2020 2055h
Test Code: 300.0-W
Chloride 140 mg/L E300.0 0.565 1.00 50.00 88.9 103 90 -110 140 0.0820 20
Lab Sample ID: 2002488-00lBMSD Date Analyzed: 02/21/2020 1455h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.65 mg/L E353.2 0.00494 0.0100 1.000 0.607 105 90 -110 1.7 2.45 10
Lab Sample ID: 2002488-004BMSD Date Analyzed: 02/21/2020 1508h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 29.7 mg/L E353,2 0.0988 0.200 20.00 10. l 98.3 90 -110 30.1 1.10 10
Report Date: 3/9/2020 Page 44 of 50
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infom,ation is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee. Privileges of subsequent use oftr
Tie 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: 2002488 Dept: MSVOA
Project: I st Quarter Chloroform 2020 QC Type: LCS
-
Reporting Amount Spike Ref. RPDRef. RPO
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: LCS VOC-2 022120A Date Analyzed: 02/21/2020 642h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 19.3 µg/L SW8260D 0 859 1.00 20.00 0 96.5 77 -143
Chloroform 20.3 µg/L SW8260D 0.166 1.00 20.00 0 IOI 85 -124
Chloromethane 22.4 µg/L SW8260D 0.802 1.00 20.00 0 112 30 -149
Methylene chloride 22.6 µg/L SW8260D 0.381 1.00 20.00 0 113 65 -154
Surr: l,2-Dichloroethane-d4 53.7 µg/L SW8260D 50.00 107 80 -136
Surr: 4-Bromofluorobenzene 49.2 µg/L SW8260D 50.00 98.3 85 -121
Surr: Dibromofluoromethane 49.9 µg/L SW8260D 50.00 99.8 78 -132
Surr: Toluene-d8 48.8 µg/L SW8260D 50.00 97.6 81 -123
Lab Sample ID: LCS VOC-1 022120A Date Analyzed: 02/21/2020 656h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 19.7 µg/L SW8260D 0.859 1.00 20.00 0 98.5 77 -143
Chloroform 18.2 µg/L SW8260D 0.166 1.00 20.00 0 91.2 85 -124
Chloromethane 18.7 µg/L SW8260D 0.802 1.00 20.00 0 93.5 30-149
Methylene chloride 15.3 µg/L SW8260D 0.381 1.00 20.00 0 76.7 65 -154
Surr: l,2-Dichloroethane-d4 SO.I µg/L SW8260D 50.00 100 80 -136
Surr: 4-Bromofluorobenzene 46.3 µg/L SW8260D 50.00 92.5 85 -121
Surr: Dibromofluoromethane 50.6 µg/L SW8260D 50.00 IOI 78 -132
Surr: Toluene-dB 51.1 µg/L SW8260D 50.00 102 81 -123
Lab Sample ID: LCS VOC-2 022420A Date Analyzed: 02/24/2020 741 h
Test Code: 8260D-W-DENIOO ------
Carbon tetrachloride 19.4 µg/L SW8260D 0.859 1.00 20.00 0 97.0 77 -143
Chloromethane 26.5 µg/L SW8260D 0.802 1.00 20.00 0 133 30 -149
Methylene chloride 22.2 µg/L SW8260D 0.381 1.00 20.00 0 Ill 65 -154
Surr: l ,2-Dichloroethane-d4 54.4 µg/L SW8260D 50.00 109 80 -136
Surr: 4-Bromofluorobenzene 50.9 µg/L SW8260D 50.00 102 85 -121
Surr: Dibromofluoromethane 51.3 µg/L SW8260D 50.00 103 78 -132
Report Date: 3/9/2020 Page 45 of 50
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Peninent sampling information is located on the attached COC Confidential Business Information: This repon is provided for the exclusive use of the addressee. Privileges of subsequent use oftr
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 wi11 be granted only on contact. This
American West :ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: 1st Quarter Chloroform 2020
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-2 022420A Date Analyzed: 02/24/2020 741h
Test Code: 8260D-W-DEN100
Surr: Toluene-d8
Lab Sample ID: LCS VOC-2 022520A
Test Code: 8260D-W-DEN 100
Chloroform
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
51.2
Date Analyzed:
20.9
54.1
49.5
49.6
49.6
µg/L SW8260D 50.00 102
02/25/2020 849h
µg/L SW8260D 0.166 1.00 20.00 0 104
µg/L SW8260D 50.00 108
µg/L SW8260D 50.00 99.0
µg/L SW8260D 50.00 99.3
µg/L SW8260D 50.00 99.2
Limits
81 -123
85 -124
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: 3/9/2020 Page 46 of 50
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 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-Thls
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: I st Quarter Chlorofonn 2020
Analyte Result
Lab Sample ID: MB VOC-2 022120A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride < 1.00
Chloroform < 1.00
Chloromethane < 1.00
Methylene chloride < 1.00
Surr: l,2-Dichloroethane-d4 53.8
Surr: 4-Bromofluorobenzene 50.1
Surr: Dibromofluoromethane 49.2
Surr: Toluene-d8 49.8
Lab Sample ID: MB VOC-1 022120A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride < 1.00
Chloroform < 1.00
Chloromethane < 1.00
Methylene chloride < 1.00
Surr: l,2-Dichloroethane-d4 54.7
Surr: 4-Bromofluorobenzene 49.3
Surr: Dibromofluoromethane 55. l
Surr: Toluene-d8 52.4
Lab Sample ID: MB VOC-2 022420A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride < 1.00
Chloromethane < 1.00
Methylene chloride < 1.00
Surr: l,2-Dichloroethane-d4 53.9
Surr: 4-Bromofluorobenzene 52.2
Surr: Dibromofluoromethane 49.0
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
Contact:
Dept:
QC Type:
Reporting Amount
Units Method MDL Limit Spiked
02/21/2020 702h
µg/L SW8260D 0.859 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.802 1.00
µg/L SW8260D 0.381 1.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
02/21/2020 716h
µg/L SW8260D 0.859 1.00
µg/L SW8260D 0.166 1.00
µg/L SW8260D 0.802 1.00
µg/L SW8260D 0.381 1.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
02/24/2020 80 I h
µg/L SW8260D 0.859 1.00
µg/L SW8260D 0.802 1.00
µg/L SW8260D 0.381 1.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
Tanner Holliday
MSVOA
MBLK
Spike Ref.
Amount %REC
108
100
98.5
99.5
109
98.6
110
105
108
104
98.1
Limits
80 • 136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 3/9/2020 Page 4 7 of 50
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 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
AtlAlYTICAl lA60RATORIE9
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: 1st Quarter Chloroform 2020
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
MBLK
Spike Ref.
Amount %REC
Lab Sample ID: MB VOC-2 022420A Date Analyzed: 02/24/2020 801h
Test Code: 8260D-W-DENIOO
Surr: Toluene-d8
Lab Sample ID: MB VOC-2 022520A
Test Code: 8260D-W-DEN100
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
50.7
Date Analyzed:
< 1.00
54.4
51.6
49.2
50.6
µg/L SW8260D
02/25/2020 909h
µg/L SW8260D 0.166
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
1.00
50.00
50.00
50.00
50.00
50.00
101
109
103
98.5
101
Limits
81 -123
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: 3/9/2020 Page 48 of 50
analyses applicable to the CWA, SOWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infom1ation is located on the attached COC. Confidential Business Information: 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 repon for any purpose other than for the addressee will be granted only on contact_ This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2002488
Project: I st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2002488-002CMS Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 16.9
Chloroform 78.7
Chloromethane 20.4
Methylene chloride 21.3
Surr: l,2-Dichloroethane-d4 54.9
Surr: 4-Bromofluorobenzene 50.3
Surr: Dibromofluoromethane 50.4
Surr: Toluene-d8 49.4
Lab Sample ID: 2002488-00ICMS Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 20.4
Chloroform 19.8
Chloromethane 15.6
Methylene chloride 22.1
Surr: 1,2-Dichloroethane-d4 50.3
Surr: 4-Bromofluorobenzene 48.0
Surr: Dibromofluoromethane 51.4
Surr: Toluene-d8 51.3
Lab Sample ID: 2002488-00JCMS Date Analyzed:
Test Code: 82600-W-DENIOO
Chloroform 564
Surr: l ,2-Dichloroethane-d4 543
Surr: 4-Bromofluorobenzene 493
Surr: Dibromofluoromethane 495
Surr: Toluene-d8 486
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:
Dept:
QC Type:
Reporting Amount
Units Method MDL Limit Spiked
02/21/2020 1453h
µg/L SW8260D 0.859 1.00 20.00
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
02/21/2020 1505h
µg/L SW8260D 0.859 1.00 20.00
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
02/25/2020 949h
---
µg/L SW8260D 1.66 10.0 200.0
µg/L SW8260D 500.0
µg/L SW8260D 500.0
µg/L SW8260D 500.0
µg/L SW8260D 500.0
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
0 84.4
61.7 85.l
0 102
0 106
110
101
101
98.8
0 102
0 99.2
0 78.0
0 Ill
101
96.0
103
103
365 99.8
109
98.6
99.1
97.2
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
85 -124
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 3/9/2020 Page 49 of 50
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 tr
ne of this company or any member of its staff, or reproduction of this repon 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: 2002488 Dept: MSVOA
Project: 1st Quarter Chloroform 2020 QC Type: MSD
---
Reporting Amount Spike Ref. RPDRef. RPO
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: 2002488-002CMSD Date Analyzed: 02/21/2020 1513h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 18.7 µg/L SW8260D 0.859 1.00 20.00 0 93.5 77 -143 16.9 10.2 35
Chloroform 82.4 µg/L SW8260D 0.166 1.00 20.00 61.7 104 85 -124 78.7 4.57 35
Chloromethane 22.2 µg/L SW8260D 0.802 1.00 20.00 0 Ill 30 -149 20.4 8.63 35
Methylene chloride 23.7 µg/L SW8260D 0.381 1.00 20.00 0 119 65 -154 21.3 10.8 35
Surr: l ,2-Dichloroethane-d4 55.1 µg/L SW8260D 50.00 110 80 -136
Surr: 4-Bromofluorobenzene 49.8 µg/L SW8260D 50.00 99.5 85 -121
Surr: Dibromofluoromethane 50.9 µg/L SW8260D 50.00 102 78 -132
Surr: Toluene-d8 49.3 µg/L SW8260D 50.00 98.6 81 -123
Lab Sample ID: 2002488-001 CMSD Date Analyzed: 02/21/2020 1525h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 22.8 µg/L SW8260D 0.859 1.00 20.00 0 114 77 -143 20.4 11.3 35
Chloroform 21.4 µg/L SW8260D 0.166 1.00 20.00 0 107 85 -124 19.8 7.85 35
Chloromethane 17.0 µg/L SW8260D 0.802 1.00 20.00 0 85.2 30 -149 15.6 8.76 35
Methylene chloride 24.3 µg/L SW8260D 0.381 1.00 20.00 0 121 65 -154 22.1 9.18 35
Surr: 1,2-Dichloroethane-d4 50.4 µg/L SW8260D 50.00 IOI 80 -136
Surr: 4-Bromofluorobenzene 48.0 µg/L SW8260D 50.00 95.9 85 -121
Surr: Dibromofluoromethane 51.0 µg/L SW8260D 50.00 102 78 -132
Surr: Toluene-d8 50.6 µg/L SW8260D 50.00 IOI 81 -123 -Lab Sample ID: 2002488-003CMSD Date Analyzed: 02/25/2020 l 009h
Test Code: 82600-W-DENlOO
Chloroform 545 µg/L SW8260D 1.66 10.0 200.0 365 90.1 85 -124 564 3.52 35
Surr: l ,2-Dichloroethane-d4 536 µg/L SW8260D 500.0 107 ?O -136
Surr: 4-Bromofluorobenzene 479 µg/L SW8260D 500.0 95.9 85 -121
Surr: Dibromofluoromethane 495 µg/L SW8260D 500.0 99.0 78 -132
Surr: Toluene-d8 485 µg/L SW8260D 500.0 97.0 81 -123
Report Date: 3/9/2020 Page 50 of 50
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business Jnfom,ation: 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-pub] ication 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
1st Quarter Chloroform 2020
Contact: Tanner Holliday
QC Level: III
Work Order: 2002488
Due Date: 3/6/2020
WO Type: Project
Comments: QC 3 (no chromatograms). EDD-Denison. CC [e-mail] and [e-mail]. Do not use "*R_" samples as MS/MSD.;
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2002488-00lA T\V4-25_02192020 2/19/2020 0946h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2002488-00lB N02/N03-W-353.2 df-no2/no3
1 SELAlla/ytes: N03N02N
2002488-00lC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Su": 4
2002488-002A T\V4-24_02192020 2/19/2020 1200h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2002488-0028 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2002488-002C 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analyles: 4/# of Su": 4
2002488-00JA T\V4-40_02192020 2/19/2020 1350h 2/21/2020 1240h 300.0..W Aqueous df-wc
1 SEL Analytes: CL
2002488-0038 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2002488-00JC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
2002488-004A T\V4-19_02192020 2/19/2020 1415h 2/21/2020 1240h 300.0..W Aqueous df-wc
1 SEL Analytes: CL
2002488-0048 N02/N03-W-353.2 df-no2/no3
1 SELA11alytes: N03N02N
2002488-004C 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4/# ofSurr: 4
2002488-00SA T\V4-21_02192020 2/19/2020 0930h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2002488-0058 N02/N03-W-353.2 df. no2/no3
1 SEL Analytes: N03N02N
2002488-00SC 8260D-W-DEN100 VOCFridge
Test Gro11p: 8260D-W-DENJOO; # of hla/yres:_j_l#ofSurr: 4
UL
Denison
Page 1 of4
t)Jj
j
3
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Printed: OW.1/20 13:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK~~-HOK~~-HOK__ COC Emailed -JJ() 4/2_,j} W
WORK ORDER Summary
Client:
Sample-ID
2002488a006A
2002488-006B
2002488-006C
2002488-007 A
2002488-007B
2002488-00?C
2002488.:.008A
2002488-008B
2002488-00SC
2002488-009A
2002488-009B
2002488-009C
2002488-01 OA
2002488-0lOB
2002488-01 oc
2002488-0 l lA
2002488-0llB
2002488-01 lC
Energy Fuels Resources, Inc.
Client Sample ID
T\V4-02_02192020
T\V4-01_02192020
T\V4-04_02192020
MW-04_02192020
MW-26_02192020
1W 4-41_ 02192020
Work Order: 2002488
Due Date: 3/6/2020
Collected Date Received Date Test Code Matrix Sel Storage
2/19/2020 1305h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Anal),tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana[ytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; #of Analytes: 4/~ofSurr: 4
2/19/2020 1324h 2/21/2020 1240h 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: 8260D-W-DENJOO; # of Analytes: 4 I# of Surr: 4
2/19/2020 1340h 2/21/2020 1240h 300.0-W Aqueous df-wc
I SEL A11alJ1_tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana[ytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group, 8260D-W-DENJ 00; # of Analytes: 4 I~ of Surr: 4
2/19/2020 1315h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Ana_l)l__tes: 4 I# o[Surr: 4
2/19/2020 1240h 2/21/2020 1240h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DENIOO VOCFridge
Test Group: 8260D-W-DENJOO; # of Ana_l)ltes: 4 I# of_Surr: 4
2/19/2020 1334h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DENIOO VOCFridge
Test Group_: 8260D-W-DENJOO; # of Analytes: 4 I# of Surr: 4
Page2of4
3
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3
3
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Printed: 02/21/20 13:58 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK __ HOK __ HOK___ COC Emailed _____ _
WORK ORDER Summary Work Order: 2002488 Page3 of4
Client: Energy Fuels Resources, Inc. Due Date: 3/6/2020
Sample ID Client Sa~ple ID Collected Date Received Date Test Code Matrix Sel Storage
2002488-012A 1W4-39_02192020 2/19/2020 1232h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2002488-012B N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
2002488-012C 8260D-W-DEN100 VQCFridge 3 .... Test Group: 8260D-W-DEJ.lj()O; # of Analytes: 4 I# of Surr: 4
2002488-0BA 1W4-11_02192020 2/19/2020 1250h 2/21/2020 1240h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2002488-0BB N02/N03-W-3S3.2 df-no2/no3
I SEL Analytes: N03N02N
2002488-0BC 8260D-W-DEN100 VOCFridge 3
•• t-.i ••. Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Su": 4
2002488-014A 1W4-22_02192020 2/19/2020 1208h 2/21/2020 1240h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2002488-0 l 4B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2002488-014C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-D§N_J_OO; # of Analytes: 4 I# of Surr: 4
2002488-015A 1W4-20_02192020 2/19/2020 1225h 2/21/2020 1240h 300.0-W Aqueous df:wc
1 SEL Analytes: CL
2002488-015B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2002488-0lSC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DEN100; # of Analytes: 4 I# of Surr: 4
2002488-016A 1W4-37_02192020 2/19/2020 1216h 2/21/2020 1240h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2002488-0168 N02/N03-W-3S3.2 df-no2/no3
I SEL Analytes: N03N02N
2002488-016C 8260D-W-DEN100 VOCFridgc 3
Test Group: 8260D-W-DENJOO; # of Analytes:_ 4 I# ofSu": 4
2002488-017A 1W4-60_02192020 2/19/2020 0900h 2/21/2020 1240h 300.0-W Aqueous df-wc
I SELAnalytes: CL
2002488-0 l 7B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
Printed: 02/21/20 13:58 LABORATORY CHECK: %M 0 RTO CNO TAT 0 aco LUOO HOK __ HOK __ HOK __ COC Emailed
WORK ORDER Summary
Client: Energy Fuels Resources, Inc;
SanipleID Client Sample ID
2002488-0 l 7C T\V4-60_02192020
2002488-018A Trip Blank
Collected Date Received Date Test Code Matrix
2/19/2020 0900h 2/21/2020 1240h 8260D-W-DEN100 Aqueous
Work Order: 2002488
Due Date: 3/6/2020
Sel Storage
VOCFridgc
Test Group: 8260D-W-DEJ!!00;_ #of Analytes: 4/#ofSu": 4
2/19/2020 0900h 2/21/2020 1240h 8260D-W-DEN100 Aqueous
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# ofSurr: 4
VOCFridgc
,···· . .. . · ....
Page4 of4
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Printed: 02/21/20 13:S8 LABORATORY CHECK: %M O RT D CN O TAT D QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed ____ _
2
3
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake Ctty, lJT 84115
Phone# [phone] Toll Free # [phone]
,
Address: 6425 S. Hwy. 191
BlancliDg, UT 84511
Contact: Tanner Holliday
Phone#: [phone] Cell#:
gpiJiii~com; [e-mail];
Email: tho1lidaJ@)e,uir£!!!!:els.com
Project Name: 1st Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samele ID: Sameled
TW4-25_02192020 2/19/2020
TW4-24_02192020 2/19/2020
TW4-40_02192020 2/19/2020
TW4-19_02192020 2/19/2020
TW4-21_02192020 2/19/2020
TW4-02_02192020 2/19/2020
TW4-01_02192020 2/19/2020
TW4-04_02192020 2/19/2020
MW-04_02192020 2/19/2020
I MW-26_02192020 10
11
2/19/2020
TW4-41_02192020 2/19/2020
12 : TW4-39_02192020 2/19/2020
13 I TW4-11_02192020 2/19/2020
Rollnqulchod by,.--, . #r;(1;£,,, Oal_o:
Si<,rllllure ~~ J. 2/"""'1" u nmo:
Print Namec Tannor Hollld,,v 1030
..... r,qulahod by, Dalo:
.SJnnalun,
T"omo:
PtfnlNamo:
Rellnqulshod by, DAio: -~,mo:
l'Jln!Namo:
Roll~by: Dalo:
S1onotu1o
Time:
PrinlNalno,
Time
Sameled
946
1200
1350
1415
930
1305
1324
1340
1315
1240
1334
1232
1250
Received by:
Sianature
Prlnl Name:
Received by:
Slanature
t?rlnt 1'4ame:
Received by:
Sh::malure
Prirt Name:
Recaived by:
ls.nnen.,,
"rin!Namo:
I
CHAIN OF CUSTODY
All analyois will be comuded using NELAP acaedHed melhods em ell date will be reported using AWAL's standard analyte Msts and reporting
limits (PQLJ unless specincaly raquested othelW!se on this Chain or CU61Ddy end/or ettadled documentaion.
QC Level: I Turn Around Time: Unless other arrangem9fll& ha ... e 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 Compliance With:
D NELAP
D RCRA
D CWA
D SOWA
D ELAP/A2LA
c' D NLLAP ~ c D Non-Compliance
f:i C D' D Other. "' f? X Q .. C QI 0 \() C: ·c: t') "iii <ii g C ~ c :::;; C Known Hazards \/) 0 a, ..... ~ .. (.) C. a 0 & '5 E ti g "' Samele Comments .. Ul li!'l
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:
2W~
AWAL Lab Sample Set#
Page 1 of 2
Due ;e; U2 I 2-CJ
Laboratory Use Only
Samples Were: L.A .. f?
~';f.~~
2
3 Temperature ~ ·c
4 Received Broken/Leeklng
(1""""""'1YSea~ y N
5/~Y Preserved y N
Chockod at bench
y ~
6 Received Wlthln
g ~Tim~ N
CDC Tepe Was: :cg~--· N NA
2 OJ1 on OU:er Package
Y N NA
3 p;...,,,. on Sample B
Y N NA
4 Unbroken on Sample G
Y N NA
~-~ L,,bo'6,m·COC Rocord?
y N
Oate: See the Analytical Scope of Work for Reporting Limits and voe
analyte list.
Time:
Date:
rr,ma:
-. I
f )OAA ,Ar...)/.,1-7' .•• ) o.i.: 21 z..i I zo
Qf),A,~ ~(l. '.vL,V\ rnme: T fZ.1;&.\-0
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# (801) 2~686 To~ Free# [phone]
_L-~ Fax# (801) 263-a687 Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc-
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Tanner Holliday
Phone#: [phone] Cell#:
iP&[e-mail]; KWeliiefslenergyflleiicom;
Emait thoWdaY(@energyfQels.com
Project Name: 1st Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samole ID: Samoled
TW4-22_02192020 2/19/2020
TW4-20_02192020 2/19/2020
TW4-37_02192020 2/19/2020
~ TW4-60_02192020 2/19/2020
Trip Blank 2/19/2020
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Print Name:
CHAIN OF CUSTODY
All analysis v.l be conducted using NELAP accredited methods end ell data v.11 ba ,_rted using AWM.'s standard analyte Usts and reporting
limits (POL) "11ess specificalty n,quested ott,er.,lse on this Chain of Cuslcdy and/or attached documenlation.
QC Level: I Tum Around Time: Unless other arrangements have bean made,
signed reports v.11 ba emailed by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
D NELAP
D RCRA
D CWA
D SOWA
D ElAPIA2lA
o' D NLLAP ~ c D Non.Compiance f;j C, D' D Other: 0) I!! '2. ... C, CD >< Q IO C: :s l'l C, ~ ]i OJ g ::; C, ~ Known Hazards C: \/) 0 CD ..... ~ .. t) a. N t.) & '5 E g tl g OJ Samele Comments .. "'
5 w X X X
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Date: Special Instructions:
Time:
2.C()2i.\~
AWAJ.. Lab Sample Set#
Page 2 of 2
1""'";1 ~ /201
Laboratory Use Only
Samples Were: ~s
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4 Ro<:uiv..i Broko:ong
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"-OCT!IJ)OWas: 1(:)-rt on Outer Package
N NA
Y N NA
2C)'""'°"OutorPac:l<age
3 ---~ Y N NA
4 Unbroken en Sample
Y N NA
Discrepancies Between Sample
Labels end COC R~
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Received by: Date: See the Analytical Scope of Work for Reporting Limits and voe
tSipnature analyte list.
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P.rintName:
Received by: Oate:
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.e...l,'\1~ 1=3v'l J. vV"""' lflme: ·1 'L[) Print Name: z. : .
Analysis
Ammonia
COD
Cyanide
Metals
N02/N03
O&G
Phenols
Sulfide
TKN
TP04
CrVI+
Procedure:
Frequency:
Preservation Check Sheet
s le Set Ext, amp1
Preservative -001 -oci -cc"> -otxr -OC5 -oow
pH<2H2S04
pH<2 H2S04
pH>12NaOH
pH<2HNOJ
pH<2H2S04 'lie0 ''"--~ ,t()";> \Je. s 1'1e-~ \1e.s
pH<2HCL \ t [, I· i l
pH<2H2S04
pH>9NaOH,
Zn Acetate
pH<2H2S04
pH <2H2S04
pH>9 -
(NTuhS04
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
-001
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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 .
-O(Z.
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Lab Set ID:
pH Lot#:
-013 ·-011
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I I ,
IINAI YTiCAl l AHOi1/1TORlfS
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal(ii,)awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2020
Dear Tanner Holliday: Lab Set ID: 2003454
American West Analytical Laboratories received sample(s) on 3/19/2020 for the analyses
presented in the following report.
American West Analytical Laboratories (AW AL) 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.
J OS e G ~~~~~,e.Jose G. Rocha,
• o=Amerioan West Analytical
Laboratories, ou=UT00031, RO Ch a ~::-ttjose@awal-labs com,
Date: 2020.03.31 11 :30:27 Approved by: -06·00·
Laboratory Director or designee
Report Date: 3/31/2020 Page I of 85
All analyses arplii.:abk to Lhc CWA. SDWA, and RCRA arc pe1 fo1,ncd ill accordance to NELAC p101ocols Pertinl'nt sampling inl01maLion is loc.1tcd on the attached COC. ConJidcnli(I] Business lllfllnnation: This rl'port is pro\·idcd for Lhc cxclusiv(' use ofthi:
add1cssl'C Privileges or subscguc1H use of 1hc name of this company or auy member of its staff. 01 rcp1 oduclion or chis report in connection with the advertisement. promolinn or s.alc or any product or process. or in ~·onncction with lhc rc-rmblicalion of this rcpo11
for uny pu1·pose other lhan frn Lhi: ad<lrcsscc-will be granted onl)' on contact. This company occepts no ,~~sponsibilily .:-xccpt l"lw th~ due pe1fo1manc!.' of inspwLion and/m rinalysis in good faith anc\ accord in!;\ 10 the-mies of 1hc Ltaclc and or science
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Set ID: 2003454
Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2003454-00lA TW4-03R_03162020 3/16/2020 745h Aqueous Anions, E300.0
Salt Lake City, UT 84119 2003454-00lB TW4-03R_03162020 3/16/2020 745h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-001 C TW4-03R_03162020 3/16/2020 745h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 2003454-002A TW4-03 03172020 3/17/2020 805h Aqueous Anions, E300.0
2003454-002B TW4-03_03172020 3/17/2020 805h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 2003454-002C TW4-03_03 l 72020 3/17/2020 805h Aqueous VOA by GC/MS Method
Fax: [phone]D/5030C
e-mail: [e-mail] 2003454-003A TW4-42 03172020 3/17/2020 823h Aqueous Anions, E300.0
2003454-003B TW 4-42 03172020 3/17/2020 823h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2003454-003C TW4-42 03172020 3/17/2020 823h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-004A TW4-28 03172020 3/17/2020 832h Aqueous Anions, E300.0
Kyle F. Gross 2003454-004B TW4-28 03172020 3/17/2020 832h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-004C TW 4-28 03172020 3/17/2020 832h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2003454-005A TW 4-32 03172020 3/17/2020 839h Aqueous Anions, E300.0
Jose Rocha 2003454-005B TW4-32 03172020 3/17/2020 839h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2003454-005C TW4-32_03 l 72020 3/17/2020 839h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-006A TW4-12 03172020 3/17/2020 845h Aqueous Anions, E300.0
2003454-006B TW4-12 03172020 3/17/2020 845h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-006C TW4-12 03172020 3/17/2020 845h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-007 A TW4-13 03172020 3/17/2020 854h Aqueous Anions, E300.0
2003454-007B TW 4-13 _ 03172020 3/17/2020 854h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-007C TW4-13 03172020 3/17/2020 854h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-00SA TW4-36 03172020 3/17/2020 903h Aqueous Anions, E300.0
2003454-00SB TW4-36_03172020 3/17/2020 903h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-00SC TW4-36_03172020 3/17/2020 903h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-009A TW 4-31 03172020 3/17/2020 912h Aqueous Anions, E300.0
2003454-009B TW4-31_03 l 72020 3/17/2020 912h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-009C TW4-31_03172020 3/17/2020 912h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-01 OA TW4-34 03172020 3/17/2020 920h Aqueous Anions, E300.0
Report Date: 3/31/2020 Page 2 of85
,\II anal)'!iCs :1r,rJi1m11li: to 1hc C\V/tt., Sl)WA.;1Dd RCRA an,: ,,.,"11omtcd in accorchuJCc to NGLAC prn1l,cl1ls. Pcnin~'l\l $<\111plin~ inform.ui,ln is loi:ntcd 011 lhc a1Hu.:hcd <:OC. Conlidl!ntial Ousine:..li ln(('tmo1inn• Thi\ rcpon is pto\•idc<I (or' d,,.,-.,clu}h'C' use of1hc
n,ldr1.-ss1.•c. Pri,•ll1i.'l;\:',. or subscq111!1\t u,o of1h1;1 n:imo ,,r this «un~,y ,w any member ,lf i1s stall: or rcprodu.:1ion ,lf this rcp,lrt in l.'.onncction with the aJvcni~cmcol. promo1i,lt1 or s11lc of :my produti 1,r J)MtC'f.. o, t11 i:or11wl:tioo "ith thO r,."·1,ubHC'31 ,,n of this rcpo•t
l'or any purpL\'1-CO\lh."t than l\lr th1.• 11tkh~,s.cc will lk" pontcJ only on conta,:t. This company o~l'Cpl!. 110 r .. ~ponsibilit;· 1.•x,.·cpt for 1hc due pc1fo1m:tncl' of inspcrtion :wl/01 nnalysis in l?~lllfl foilh and tMX:Ordins 10 ih,(' rules ufthe 1mck 1111d .-,r M.'i'-'ntoc.
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Set ID: 2003454
At-~Al ~'l lCI\! l ,\80RATOR!f S Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2003454-0lOB T\V4-34 03172020 3/17/2020 920h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2003454-01 oc T\V4-34 03172020 3/17/2020 920h Aqueous VOA by GC/MS Method
8260D/5030C
Salt Lake City, UT 84119 2003454-01 lA T\V4-35 03172020 3/17/2020 928h Aqueous Anions, E300.0
2003454-01 lB T\V4-35 03172020 3/17/2020 928h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0llC T\\!4-35_03172020 3/1 7/2020 928h Aqueous VOA by GC/MS Method
Phone: [phone]D/5030C
2003454-012A T\\!4-23_03172020 3/17/2020 937h Aqueous Anions, E300.0
Toll Free: [phone] 2003454-012B T\V4-23 03172020 3/17/2020 937h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 2003454-012C T\\!4-23_03172020 3/17/2020 937h Aqueous VOA by GC/MS Method
e-mail : [e-mail] 8260D/5030C
2003454-013A M\V-32 03182020 3/18/2020 1005h Aqueous Anions, E300.0
web: www.awal-Jabs.com 2003454-013B MW-32_03182020 3/18/2020 1005h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-013C MW-32 03182020 3/18/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-014A T\V4-38 03172020 3/17/2020 945h Aqueous Anions, E300.0 Kyle F. Gross 2003454-014B T\\!4-38_03172020 3/17/2020 945h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2003454-014C T\\!4-38_03172020 3/17/2020 945h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2003454-015A T\V 4-14 03172020 3/17/2020 955h Aqueous Anions, E300.0
QA Officer 2003454-015B T\V4-14 03172020 3/17/2020 955h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-015C T\V4-14 03172020 3/17/2020 955h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-016A T\\!4-06_03172020 3/17/2020 1005h Aqueous Anions, E300.0
2003454-016B T\V 4-06 _ 03172020 3/17/2020 1005h Aqueous Nitrite/Nitrate (as N), E353 .2
2003454-016C T\V4-06 03172020 3/17/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-017 A T\V4-27 03172020 3/17/2020 1014h Aqueous Anions, E300.0
2003454-0l 7B T\\!4-27_03172020 3/17/2020 1014h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-017C T\V 4-27 _ 03172020 3/1 7/2020 1014h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-018A T\\!4-05_03172020 3/17/2020 1024h Aqueous Anions, E300.0
2003454-018B T\V4-05 03172020 3/17/2020 1024h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0 l 8C T\\!4-05_03172020 3/17/2020 1024h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-019A T\\!4-30_03172020 3/17/2020 1038h Aqueous Anions, E300.0
2003454-019B T\\!4-30_03172020 3/17/2020 1038h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0 l 9C T\\!4-30 _ 03172020 3/17/2020 1038h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2020 Page 3 of 85
All :tn:ily~cs l\{'flH~~bl\' to the CWA. SllWA. nnd RCR.•\ .'H'~ p,.'1fonncd in accor<Lttn\'C I~ NELAC prolocolf.. '.cnin.:n~ samplin~ i11fom\.'l.i11ln is. lOl'i'llcli 011 t~c aun.;hcd C.:OC: Conlidcnli~I llusincf.s lnfonnation: Th_is report i~ prov!dcd for 1hc \'~_d wth"C me ?r th('
atidf\")k~ Pnvil\'1:-('f. orsubscqt1l'1tl t,iu ~1he n:una tJI thtJ corup11ny \W any member of us staff. or rcproduc\1on or lh1s r~por1 111 l'nnnccdnn wuh the advcrt1scmcn1. promolRlll or :-ale ol :my pruduu or prol·~s. or in connccuon with 1hc 1\~-puhhca1KJn o(lh1s rcpo11
lbr d.n)' purpt\',C othn' lhan for lh\' ttJdr~«c v.ill b.: 1;r;inlt'1 only on conlael This compM)' llCl'Cpts no rl·sronsibility \\\:.:-cpl for the liuc pcrfo,m:mn-orinspc.:-1im1 and/01 :malysi~ in gt:Hld foith ond accordini; to the rules of !he tr.ick oncl of science..
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Set ID: 2003454
l1NAi YTICfll 11,noR11TORlf S Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2003454-020A TW4-09R 03172020 3/17/2020 1100h Aqueous Anions, E300.0
3440 South 700 West 2003454-020B TW4-09R 03172020 3/17/2020 1100h Aqueous Nitrite/Nitrate (as N), E353.2
Salt Lake City, UT 84119 2003454-020C TW4-09R_03 l 72020 3/17/2020 1100h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-02 lA TW4-09_03182020 3/18/2020 508h Aqueous Anions, E300.0
2003454-021B TW4-09_03182020 3/1 8/2020 508h Aqueous Nitrite/Nitrate (as N), E353.2
Phone: [phone] 2003454-021C T\\14-09 03182020 3/18/2020 508h Aqueous VOA by GC/MS Method
8260D/5030C
Toll Free: [phone] 2003454-022A T\\14-18 03182020 3/18/2020 518h Aqueous Anions, E300.0
Fax: [phone] 2003454-022B TW4-18 03182020 3/18/2020 518h Aqueous Nitrite/Nitrate (as N), E353.2
e-mail: [e-mail] 2003454-022C T\\14-18_03182020 3/18/2020 518h Aqueous VOA by GC/MS Method
8260D/5030C
web: www.awal-labs.com 2003454-023A T\\14-08_03182020 3/18/2020 532h Aqueous Anions, E300.0
2003454-023B T\\14-08_03182020 3/18/2020 532h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-023C TW4-08 03182020 3/1 8/2020 532h Aqueous VOA by GC/MS Method
Kyle F. Gross 8260D/5030C
2003454-024A T\\14-16_03182020 3/18/2020 540h Aqueous Anions, E300.0
Laboratory Director 2003454-0248 T\\14-16_03182020 3/18/2020 540h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-024C TW4-16_03182020 3/18/2020 540h Aqueous VOA by GC/MS Method
Jose Rocha 8260D/5030C
QA Officer 2003454-025A TW4-33_03182020 3/1 8/2020 550h Aqueous Anions, E300.0
2003454-025B T\\14-33_03182020 3/18/2020 550h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-025C TW4-33_03182020 3/18/2020 550h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-026A TW4-07 03182020 3/1 8/2020 600h Aqueous Anions, E300.0
2003454-0268 T\\14-07_03182020 3/18/2020 600h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-026C TW 4-07 03182020 3/18/2020 600h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-027 A T\\14-29 _03182020 3/18/2020 612h Aqueous Anions, E300.0
2003454-027B T\V 4-29 03182020 3/18/2020 612h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-027C TW4-29_03182020 3/18/2020 612h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-028A TW4-10 03182020 3/18/2020 625h Aqueous Anions, E300.0
2003454-028B T\\14-10_03182020 3/18/2020 625h Aqueous Nitrite/Nitrate (as N), E353 .2
2003454-028C T\\14-10_03182020 3/18/2020 625h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-029A T\\14-26_03182020 3/18/2020 635h Aqueous Anions, E300.0
2003454-029B TW 4-26 _ 03182020 3/1 8/2020 635h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 3/31/2020 Page 4 of 85
All nnal)'M!S :tpplicahll' 10 1h1.: CWA. SOWA, anti RCRA ore 1x.·1fo1mcd i11 ncctlrdnncc 10 NGLAC prn1ocl1ls Pcrtin~'nt sa111plin~ i11fo1matilln is loca\l.'d 0111hc <1Unchcd l'OC. C:0111idc11tial Uusinci.s l111h11nalion: This rcpor1 is provided ro, the cxclu::-iw u~c 1lf thi:
.itfc.h,·s!!l'l', P1i"ill'f?l'S of ~ubscqttcnt use 11f the name 1lf this company or ruiy member 1lf its Sl(lff. or rcr1odu,·tio11 of this rq)orl i11 ,·onncction "i1h lhc advcrti5cmcnl. promnlhln or sale of any ,,roduct or pro,~css. or in l'onncction "ith 1hc 1c-public:uion of this rcpmt
for ony pm pose othl'I than li.l1 1h1.• adc\rc.\.<;CI:' will h~-grnnlcd only on l'Ont;,ct. This company c11.:~·cpb1 110 t~'sponsibility l'X.:cpl r,w the due pcrfo1manc1.' of inspc.:tiou :md/or:inalysis in g,lCld failh Bod according 10 the rule)!. of th~ trade and of science.
AN/\LYTICII! I ABORAT0Rlf5
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client:
Project:
Lab Set ID:
Date Received:
Lab Sample ID
2003454-029C
2003454-030A
2003454-030B
2003454-030C
2003454-03 lA
2003454-03 lB
2003454-03 l C
2003454-032A
2003454-032B
2003454-032C
2003454-033A
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454
3/1 9/2020 1420h
Client Sample ID
TW4-26 03182020
TW4-65 03172020
TW 4-65 _ 03172020
TW4-65 03172020
TW4-70_03172020
TW4-70_03172020
TW4-70 03172020
TW4-75 03182020
TW4-75 03182020
TW4-75 03182020
Trip Blank
Contact: Tanner Holliday
Date Collected Matrix Analysis
3/18/2020 635h Aqueous VOA by GC/MS Method
8260D/5030C
3/17/2020 805h Aqueous Anions, E300.0
3/17/2020 805h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2020 805h Aqueous VOA by GC/MS Method
8260D/5030C
3/17/2020 1024h Aqueous Anions, E300.0
3/17/2020 1024h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2020 1024h Aqueous VOA by GC/MS Method
8260D/5030C
3/18/2020 1005h Aqueous Anions, E300.0
3/18/2020 1005h Aqueous Nitrite/Nitrate (as N), E353.2
3/18/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
3/16/2020 745h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/3 1/2020 Page 5 of 85
All :'\n:lilyM'J "ll('lii:nhk 10 1he l'\\f A. SOWA. :md RCR..\ ore µ..~,fom,cd in acc1)rda11('c to NELAC rn,ttocols. Pertin~m siu.upllnu infol'm:uion is loca1cd on 1hc attached COC. Confidential Buot,ln l111\,,ru11dtm Thh. ,-"Im 1,.1,ro\·i,kd (or lh~\"').c)u~h\l' u"iit< or thl'
addJ\~, l'rMlq;I.'~ of sub.<.c~o,.·m U\t" ,1f 1ho n:1111;-,\(lhb. ru111p1any l)\' all)' member nf i1s s1alT. 01 ri;pn"111ction l)f this n·1x,n ln \"Onncction with 1hc advcnisciuc1\I. J>rOJ111)tio11 or sale of any 1~1 or prn,:c.<s. o, ln «)fln(!i:tlon with 11'-a f\ .. r,Ybln,1i11h ufthis rcpo11
for My f'l'II~ 01)11:"1 lhan for tb,• llldrcs.sec will W ,Pftlnll~ onl~· on conta~·L. Tllis company ac;~cpls no ri:sponsibility c>.:ccpl fnr the due pcrfo1m:mcc-of inspix-Lion and/or:1n.'.llysis in gOlxl faith ond IIC!t'Ol'rling 10 1hc min of1~c 1rac1, 1:m11 >Jof,1."11."lM'Q.
Af'IAl'f11(';hl I AHOHfllORlfS
3440 South 700 West
Salt Lake City, UT 841 19
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
e-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:
1st Quarter Chloroform 2020
2003454
3/19/2020
3/16-3/18/2020
Intact
None
Holding Time and Preservation R,equirements: 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: 3/31/2020 Page 6 of 85
All analyses applicahk lo 1hc C\VA, SOWA, and RCRA nrc p~1 fonncd ill accorrtaucc lo NELAC p1olocl1ls Pcrtin..-111 sampling inlbi mn1ion is locawd on the auachcct COC. Confidcntinl 13usin..-ss 1111l11nmLion: lhis report is pro\'ilfod fm Lh~~ ,:xdu;11iw U\C or the
nddtl'SSC\"! Privilrgl'S or ~ubscqucnt l1sc of thi.; name l,r1his c,,inptl.11)' nr a11y member of i1s staff. m reproduction nf this 1 ,:port in l'Onncction wi1h the :idvcrtiscmcnt, promotion or sale ol' any produi.::c or proo:css. or in connection with 1hc I o:-publication of this rcpo1 t
for any pu1pose oth,:r lhnn for 1hc uddrcssci.; will be-grnnlcd only on conli'lt:l This company DC:l'cpls 110 responsibility ,:x.:cpl for the liuc p..-rfo1mnnc,: of inspc.:liou and/ornnalysis it1 gm,d foilh nnd uccorcling Lo Lhc rulc1. ofthl' lrack 1111d or sc:ic1tcc.
ANALYTICl\i l Al'i011AlOA![ S
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
e-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: I st Quarter Chloroform 2020
Dear Tanner Holliday: Lab Set ID: 2003454
American West Analytical Laboratories received sample(s) on 3/19/2020 for the analyses
presented in the following report.
American West Analytical Laboratories (A WAL) 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.
J Os e G ~~c~~=Jose G. Rocha,
• o=American West Analytical
Laboratories, ou=UT00031, R QC ha :[e-mail],
Date: 2020.03.31 11 :30:27 Approved by: -06'00·
Laboratory Director or designee
Report Date: 3/31/2020 Page l of 85
All analyses applh.:ahlc Lo the CWA. SOWA, nnd RCR:\ nrc 1~1 Jbnncd in accordance lo Nm AC pro1l,cols. Pcnino."nt sarnrling i11Jb1 m:uion is lol·atcd on lhe allaeheli COC Co11ndc11Linl (lusincss lnfoimaLion: This rcpor1 is provilh:d f11r Lhc exclusive m,e of thl'
addrl'SSCC Privilcgl'S l,r subsequent use: o[ the name of Lhis el1mpany l,, auy member llf its slaff. oi rcprodul'tion l1[ this 11.'porl i11 l.'onncction wilh the ndvcniscrncnt. promotil111 or s.alc or any µrodu1:l or procc.,;s, or in connection with the rc-publicmion of tltis rcplll L
for any pu1~1sc oLbt:r 1han frn the addrc.,;scc will be grnnled only on conla~·L This company n.ccepl'-110 responsibility ex.cc pl for lh~ due p,.:rfo1mam:l' of i11spcl'Lio11 and/01 analysis i11 good foi1h onct according to Lhc-rule:-. of 1ltc 1r;:i.,II.' ,md of si.;icncc
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chlorofonn 2020
Lab Set ID: 2003454
Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2003454-00lA TW4-03R_03162020 3/16/2020 745h Aqueous Anions, E300.0
Salt Lake City, UT 84119 2003454-0018 TW4-03R_03162020 3/16/2020 745h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-001 C TW4-03R 03162020 3/16/2020 745h Aqueous VOA by GC/MS Method
8260D/5030C
Phone:[phone] 2003454-002A TW4-03 03172020 3/17/2020 805h Aqueous Anions, E300.0
2003454-002B TW4-03 03172020 3/17/2020 805h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 2003454-002C TW4-03_03172020 3/17/2020 805h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260D/5030C
e-mail: [e-mail] 2003454-003A TW4-42_03172020 3/l 7/2020 823h Aqueous Anions, E300.0
2003454-003B TW4-42_03172020 3/17/2020 823h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2003454-003C TW4-42 03172020 3/17/2020 823h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-004A TW4-28_03172020 3/17/2020 832h Aqueous Anions, E300.0
Kyle F. Gross 2003454-004B TW4-28_03172020 3/17/2020 832h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-004C TW4-28 03172020 3/17/2020 832h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2003454-005A TW4-32 03172020 3/17/2020 839h Aqueous Anions, E300.0
Jose Rocha 2003454-005B TW4-32_03172020 3/17/2020 839h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2003454-005C TW4-32_03172020 3/17/2020 839h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-006A TW4-12 03172020 3/17/2020 845h Aqueous Anions, E300.0
2003454-006B TW4-12 03172020 3/17/2020 845h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-006C TW4-12_03172020 3/17/2020 845h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-007 A TW4-13_03172020 3/17/2020 854h Aqueous Anions, E300.0
2003454-007B TW4-13_03172020 3/17/2020 854h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-007C TW4-13_03172020 3/17/2020 854h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-008A TW4-36_03172020 3/17/2020 903h Aqueous Anions, E300.0
2003454-008B TW4-36_03172020 3/17/2020 903h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-008C TW4-36_03172020 3/17/2020 903h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-009A TW4-31_03172020 3/17/2020 912h Aqueous Anions, E300.0
2003454-009B TW4-31_03172020 3/17/2020 912h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-009C TW4-3I_03l72020 3/17/2020 912h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-0 I OA TW4-34_03172020 3/17/2020 920h Aqueous Anions, E300.0
Report Date: 3/31/2020 Page 2 of 85
.-\\I .;m;1l)1'C) applicabk lo lhe CWA. SOWA, nnd RCH:\ :ire p,.•rfonueJ i11 accordm1,c to NELAC p1'olowls Pcnin.:lll s:unpling info,mation is lo-:-a1cd on lhc anachcd <:OC Conlidenti!\I Ousincss lnl(lunation: lhis rcpor1 is pro,·idt..>ti for th.: exdu$iv1.· uM~ of1h1.'
add1 ~"'C. Privil~g:cs or.subscqu,:nt use or tho ~nc ar this cmupnuy lll any mcmbc1 of its staff. 01 rcprodoelion of this 1-.'pMI in l·onncction with 1hc.1d\/cnisemcn1. prom,)lion or :i.3lcor:my produc1 (lT procCT.s, or in .:onncction with the tl~-publicmion of this rcro11
for any pu1pl1sc mhl'r lhan for thl• a1lllr~\C~ will b,.• grantc(\ only on l"Ontai:t This company llCl'Cpts no r,:~ponsil>ility .:x.:cr,t for 1hc due pet lb1mam:c of i11spc.:1io11 :mdlot analysis in gooct failh and according to thl" mies of the had.: and of science
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Set ID: 2003454
ANAi YT!(;f,I l ABOHATORif-S Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2003454-01 OB TW4-34 03172020 3/17/2020 920h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2003454-0lOC TW4-34 03172020 3/17/2020 920h Aqueous VOA by GC/MS Method
8260D/5030C
Salt Lake City, UT 84119 2003454-01 lA TW4-35_03172020 3/17/2020 928h Aqueous Anions, E300.0
2003454-01 lB TW4-35 03172020 3/17/2020 928h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-01 lC TW4-35 03172020 3/17/2020 928h Aqueous VOA by GC/MS Method
Phone: [phone]D/5030C
2003454-012A TW4-23_03172020 3/17/2020 937h Aqueous Anions, E300.0
Toll Free: [phone] 2003454-012B TW4-23 03172020 3/17/2020 937h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: (80 I) 263-8687 2003454-012C TW 4-23 03172020 3/17/2020 937h Aqueous VOA by GC/MS Method
e-mail: [e-mail] 8260D/5030C
2003454-0BA MW-32 03182020 3/18/2020 1005h Aqueous Anions, E300.0
web: www.awal-labs.com 2003454-0 l 3B MW-32 03182020 3/18/2020 1005h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-013C MW-32 03182020 3/18/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-014A TW4-38_03172020 3/17/2020 945h Aqueous Anions, E300.0 Kyle F. Gross 2003454-0 l 4B TW4-38_03172020 3/17/2020 945h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2003454-0 l 4C TW4-38 03172020 3/17/2020 945h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2003454-015A TW4-14 03172020 3/17/2020 955h Aqueous Anions, E300.0
QA Officer 2003454-015B TW 4-l 4 _ 03172020 3/17/2020 955h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0 l 5C TW4-14_03172020 3/17/2020 955h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-016A TW 4-06 _ 03172020 3/17/2020 1005h Aqueous Anions, E300.0
2003454-0 l 6B TW 4-06 _ 03172020 3/17/2020 1005h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-016C TW 4-06 03172020 3/17/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-017 A TW 4-27 03172020 3/17/2020 1014h Aqueous Anions, E300.0
2003454-0l 7B TW4-27 _03 l 72020 3/17/2020 1014h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0l 7C TW 4-27 _ 03172020 3/17/2020 1014h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-018A TW 4-05 _ 03172020 3/17/2020 1024h Aqueous Anions, E300.0
2003454-0 l 8B TW 4-05 _ 03172020 3/17/2020 1024h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0 l 8C TW4-05 03172020 3/17/2020 1024h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-019A TW4-30_03172020 3/17/2020 1038h Aqueous Anions, E300.0
2003454-0 l 9B TW4-30_03172020 3/17/2020 1038h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-0 l 9C TW4-30_03172020 3/17/2020 1038h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2020 Page 3 of 85
All analyr.cs applicable lo 1hc C\VA. SOWA. and RCRA ore ,~1fo11ncd in accordan"·c 10 NELAC pmlocols Pcrtin.:1u sampling infommtinn is lo-.·Jllcd 011 1hc Rllochcd COC. C'onlitkntial Ousine:.s lnfonnation: This report is pro"iti1.:-1.i ror th"~ exdnsin· use ol ll1..-
aJd1 ._'SS('C. Privikges or subscqu~nt use or the n:1mc of this company m any member o( ils slaff. 01 rcp1 odt1.:tion of this 1..:pon in rnnncctioo with the adveniscmco1. promolion or sale l'f :my product or ptol'CSS. or in connection with 1hc rc-rublication of this rcpo11
for any ru1posc oth.:r 1han fo, the-addressee will hl' gron1cd only on coma.:l This company accepts no responsibility l'Xl.'ef'I f,.lr the due p,:rfo1mam:c or insp<X·tion andlor analysis in gm,d foi1h nnd according lo 1hc mies of 1hc 11 ade and or science,
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2020
Lab Set ID: 2003454
ANAi fT e;,,l I /'>.BORATORI!-S Date Received: 3/19/2020 1420h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2003454-020A TW4-09R_03172020 3/17/2020 1100h Aqueous Anions, E300.0
3440 South 700 West 2003454-020B TW4-09R_03172020 3/17/2020 1100h Aqueous Nitrite/Nitrate (as N), E353.2
Salt Lake City, UT 841 19 2003454-020C TW4-09R_03 l 72020 3/17/2020 1100h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-021A TW 4-09 03182020 3/18/2020 508h Aqueous Anions, E300.0
2003454-021B TW 4-09 03182020 3/18/2020 508h Aqueous Nitrite/Nitrate (as N), E353.2
Phone: (80 I) 263-8686 2003454-021 C TW 4-09 03182020 3/18/2020 508h Aqueous VOA by GC/MS Method
8260D/5030C
Toll Free: [phone] 2003454-022A TW4-18 03182020 3/18/2020 518h Aqueous Anions, E300.0
Fax: [phone] 2003454-022B TW4-18_03182020 3/18/2020 518h Aqueous Nitrite/Nitrate (as N), E353.2
e-mail: [e-mail] 2003454-022C TW4-18 03182020 3/18/2020 518h Aqueous VOA by GC/MS Method
8260D/5030C
web: www.awal-labs.com 2003454-023A TW 4-08 03182020 3/18/2020 532h Aqueous Anions, E300.0
2003454-023B TW 4-08 03182020 3/18/2020 532h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-023C TW 4-08 03182020 3/18/2020 532h Aqueous VOA by GC/MS Method
Kyle F. Gross 8260D/5030C
2003454-024A TW4-16 03182020 3/18/2020 540h Aqueous Anions, E300.0
Laboratory Director 2003454-024B TW4-16 03182020 3/18/2020 540h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-024C TW4-16_03182020 3/18/2020 540h Aqueous VOA by GC/MS Method
Jose Rocha 8260D/5030C
QA Officer 2003454-025A TW4-33 03182020 3/18/2020 550h Aqueous Anions, E300.0
2003454-025B TW4-33 03182020 3/18/2020 550h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-025C TW4-33 03182020 3/18/2020 550h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-026A TW4-07 03182020 3/18/2020 600h Aqueous Anions, E300.0
2003454-026B TW 4-07 03182020 3/18/2020 600h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-026C TW 4-07 03182020 3/18/2020 600h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-027 A TW4-29 _03182020 3/18/2020 612h Aqueous Anions, E300.0
2003454-027B TW4-29 03182020 3/18/2020 612h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-027C TW4-29 03182020 3/18/2020 612h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-028A TW4-10 03182020 3/18/2020 625h Aqueous Anions, E300.0
2003454-028B TW4-10 03182020 3/18/2020 625h Aqueous Nitrite/Nitrate (as N), E353.2
2003454-028C TW4-10 03182020 3/18/2020 625h Aqueous VOA by GC/MS Method
8260D/5030C
2003454-029A TW 4-26 03182020 3/18/2020 635h Aqueous Anions, E300.0
2003454-029B TW 4-26 03182020 3/18/2020 635h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 3/31/2020 Page 4 of 85
All nnaly!',cs applicablL' Lo the C\VA, SDWA, anti RCRA ore p<'1 fo1111cd in accorclan("c lo N8LAC prolocols. PcrLini:nt ~amrling inlb1 maiion is localed on the auochcct C'OC. Confolcntinl Dusincs.~ lnfoimation: 1his report is provi~kd for the \'xdusin' use or the
nti<ln.-ssl'C Ptivill'ges or subsequent u~c or the n:1mc of this company 01· ru1y rncrnbc1· of its slal'f. or rcp1oduction or thi!'. report in conncclion with !he advcrtisc111cn1. µromolion or sale or any product or pro\.'Css, or in l'Onncction with lhc l'l'-pnblicalion of thi~ rcpo11
for anr pu1 pose othl.'1 lhan Ii.)! Lh.: addressee will ~ grnntcd only on l'onla.:L This comrnmy llcccpts no tl~sponsil>ility l~xccpl li.lr 1hc line pc1 Jb1mancl' of inspi:i::Liou and/or anfllysis in good failh cmcl uccor<ling to Lhl' mlc!. of Lhc liack an<l o[ science,
AN/I.I YflC/1.1 t Al-OH/1.iOAIFS
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
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client:
Project:
Lab Set ID:
Date Received:
Lab Sample ID
2003454-029C
2003454-030A
2003454-030B
2003454-030C
2003454-03 lA
2003454-03 lB
2003454-031 C
2003454-032A
2003454-032B
2003454-032C
2003454-033A
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2020
2003454
3/19/2020 1420h
Client Sample ID
TW4-26_03182020
TW4-65_03172020
TW4-65 03172020
TW4-65 03172020
TW4-70_03172020
TW4-70_03172020
TW4-70 03172020
TW4-75 03182020
TW4-75 03182020
TW4-75 03182020
Trip Blank
Contact: Tanner Holliday
Date Collected Matrix Analysis
3/18/2020 635h Aqueous VOA by GC/MS Method
8260D/5030C
3/17/2020 805h Aqueous Anions, E300.0
3/17/2020 805h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2020 805h Aqueous VOA by GC/MS Method
8260D/5030C
3/17/2020 1024h Aqueous Anions, E300.0
3/1 7/2020 1024h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2020 1024h Aqueous VOA by GC/MS Method
8260D/5030C
3/18/2020 1005h Aqueous Anions, E300.0
3/18/2020 1005h Aqueous Nitrite/Nitrate (as N), E353.2
3/18/2020 1005h Aqueous VOA by GC/MS Method
8260D/5030C
3/16/2020 745h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2020 Page 5 of 85
All .inalyscs applicable lo 1he CWA. SOWA, .ind RCR:\ arc pl:'1fonnct1 in accordru1.:c \o NEL.AC p1nlocDI" Pcr1in1.•nt sampling infmmati,)n is /01.'oled on 1hc au.ached C(X:_ Conlide1\lial Dusinc~s lnfo,11cuion: This report is provi,icd for th~ (')t.du!livc UM' .. of th('
a,id1cssec. Privileges of subsequ~11t use of 1h~ name of this e1.,mpo11y or any member of i1s s1a1T. ol' rcprodu1.·tion 1.\f this r('p1ut in connection with the advcnisemc111. prmno1i1.1n or sale of any product or proc-css. or in c-onneet.ion with 1hc r('-publication of lhis rcpo11
for any ('IUlpllSC oth,:1 than for the adrlrcsscc will bl' grnntcd only on c-onlacl This company llCl'Cpts no r ... ~ponsibility cxl.'cpt frn the due pcrfo,mancc of inspc...·tion am.liar anal)·sis i,, g\,00. foilh and uccorrling to lhl• rules ol'thc lracl(' on,l of science.
/\NAlYllCAI I AHOA/1lORlfS
3440 South 700 West
Salt Lake City, UT 84 119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
e-mail: awal(c9awal-labs.com
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:
1st Quarter Chloroform 2020
2003454
3/19/2020
3/16-3/18/2020
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, RPO:
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: 3/31/2020 Page 6 of 85
All analyses applicabk Lo the CWA, SOWA, and RCRA arc pcrt'onncd in accordm1cc Lo NELAC p101ocols Pcnincnt smnpling information is lm:a1cd on 1hc auochcd COC Co11!itle11Liril Business lnfmination: This report is provided for the exclusive w,c of thl.'
add1l'Ss.t'c. Privikgcs of subscqu.:nt use of the name of this Cl)lllpany 01 auy mcmbc1 of its staff. or reproduction of Lhis report in connection with the ativcrtiscmcnt, pro11101ion or sale or any product or prorcss, or in connection with the 1c-p11blica1ion of Lhis rcpotl
for any purpose oth~1· lhan fnt· thl' addressee will b,.,. granted only on ~·onlao,'"t This company acccpL'i no rcsponsibilily ~-xcept rot the due pc1fo1mancc of inspccLioH and/or analysis ii1 good faith and 11ccording 10 thl' rules oJ'lhc LrnM and or science.
IINALYl IC/\1 \ /\[~DR/\TORlf S
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
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:
1st Quarter Chloroform 2020
2003454
3/19/2020
3/16-3/18/2020
Intact
None
SW-846 8260D/5030C
Volatile Organic Compounds
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 pH of sample 2003454-014C was >2. Analysis was
performed within the 7 day holding time. 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: 3/31/2020 Page 7 of 85
All nnalyf.cs applli.:abk lo lht.: C\VA.. SDWA, and RCR:\ arc [h'1 lb1mcd in 11ci.:orclru1cc lo NELAC pro\ocols Penincnt s.-unpling inform:uion is loca1crl 0111hc allrichcrl COC Conlide1Hinl Uusinc5s lnll)11naLion: This. rcpor1 is IHO\'ilicd for th~ cxdu~i,·~, UM; or the
add11.."Ssrc, P1ivilc(!:l'S or subsequent use of the name l,r Lhis enmi,any or imy ntcmlx:1 or its staff. 01 rcprodu~·tion l,r this n.'[h)rl in l'Onnci:1ion wilh the advertisement. promo1in11 or :i.E1lc ol' any produc1 or process. or in l'onncction wiLh 1hc 1·,:,-p11blic:uk,n or this rcro11
for nny pu1 po$c other than l~lr the addressee will b,:, granted only on conla~'l This company .:icccpls no r,:,sponsibility cxccpl t'lll 1hc ~iuc l)l.'rformanrc or inspcc1ion and/or analysis i1, gl){)(f foi1h ond .:iccorcting lo the rules of the traCIL! and or scic1,cc
ei~fc';£:·:., :. \!'\:·c:.:s;:
ANALYTiCAi. LAS0RAT0filES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: I st Quarter Chloroform 2020
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:
Dept:
Tanner Holliday
WC
Method MDL
Reporting
Limit
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS-R136998 Date Analyzed: 03/26/2020 1038h
Test Code: 300.0-W
Chloride 5.05 mg!L E300.0 0,0565 0.100 5.000 0 101
Lab Sample ID: LCS-R137024 Date Analyzed: 03/26/2020 2131 h
Test Code: 300.0-W
Chloride 4.88 mg/L E300.0 0.0565 0,100 5.000 0 97.5
Lab Sample ID: LCS-R136797 Date Analyzed: 03/20/2020 1039h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0 994 mg/L E353.2 0.00494 0 0100 1.000 0 99.4
Lab Sample ID: LCS-R136796 Date Analyzed: 03/20/2020 958h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.03 mg/L E353,2 0.00494 0.0100 1.000 0 103
Limits
90-110
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Limit Amt %RPO Qual
Report Date: 3/31/2020 Page 73 of 85
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on the attached COC. Confidential Business Information: fhis report is provided for the exclusive use of the addressee. Privileges of subsequent use of the
name of this company or any member ofit5 staff, or reproduction or 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 1.:ontact. lbis
company accepls nn responsibility except f'or the due performance of inspection anti/or analysis in good faith and according to the mles of the trade and oFscience.
~-:::\_ r: ;; t~ r ; c ~1 r1. \/\./ r::; st
ANALYTiCAL LAS0R'AT0fi1 ES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: MB-RI36998 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-Rl37024 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-Rl36797 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) <0.0100
Lab Sample ID: MB-Rl36796 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-Jabs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Repo~ting Amount Spiked
Units Method MDL Limit
03/26/2020 1021 h
mg/L E300.0 0.0565 0.100
03/26/2020 2114h
mg/L E300.0 0.0565 0.100
03/20/2020 1037h
mg/L E353.2 0.00494 0.0100
03/20/2020 957h
mg/L E3532 0.00494 0.0100
Tanner Holliday
WC
MBLK
Spike Ref.
Amount %REC Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 74 of 85
AH analyses applicable to the CWA. SDWA, and RCRA are perfom,ed in accordance to NELAC protocols, Pertinent sampling information is located on the attached COC. Confidt:ntial Business Information: This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the
name of this ct)mpany or any member of its staff. or r~production of this report in connet.:tion with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of rhis report for any purpose other 1han for 1he addressee will be granted only on contact, This
company accepts no responsibility except for the due performance of im,pectiun and/or analysis in good faith and according to the rules of the 1Tadc: and of science ..
/\.n,erican V\/est
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: I st Quarter Chloroform 2020
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:
Dept:
Tanner Holliday
WC
Method MDL
Reporting
Limit
QC Type: MS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: 2003454-012AMS Date Analyzed: 03/26/2020 2205h
Test Code: 300.0-W
Chloride 97.2 mg/L E300.0 0.565 1.00 50.00 50 94.5
Lab Sample ID: 2003454-013AMS Date Analyzed: 03/26/2020 2255h
Test Code: 300.0-W
Chloride 83.5 mg/L E300.0 0.565 1.00 50.00 36 95.1
Lab Sample ID: 2003454-022BMS Date Analyzed: 03/20/2020 I 04 7h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 14.3 mg/L E353.2 0.0494 0.100 10.00 3.71 106
Lab Sample ID: 2003454-024BMS Date Analyzed: 03/20/2020 l 052h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 14 5 mg/L E353.2 0.0494 0.100 10.00 3.91 106
Lab Sample ID: 2003454-00JBMS Date Analyzed: 03/20/2020 I 003h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite ( as N) 13.6 mg/L E353.2 0.0494 0.100 10.00 2.88 107
Lab Sample ID: 2003454-004BMS Date Analyzed: 03/20/2020 I 006h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 31.4 mg/L E353,2 0.0988 0.200 20.00 9.87 107
Limits
90-110
90-110
90-110
90 -110
90-110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Limit Amt %RPO Qual
Report Date: 3/31/2020 Page 75 of 85
All analyses applicable to the CW A, SDW A, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling infonnacion is located on the attached COC. Confidential Business Information: This repon is provided for the exclusive use of the addressee. Privileges of subsequent use of [he
name of this company or any member of its staff. or reproduction of this repon in connection with Lhe 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
company accc:pts no responsibility c:-xcept for the due performance of inspection and/or analys.is in good faith and according ro the rules of the trade and of science.
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: (80 I) 263-8686, Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
i\merican Vvest QC SUMMARY REPORT ANALY'TiCAL LAS0R'...tiT08!ES
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 2003454 Dept: WC
Project: 1st Quarter Chloroform 2020 QC Type: MSD
Reporting Amount Spiked Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: 2003454-012AMSD Date Analyzed: 03/26/2020 2221 h
Test Code: 300.0-W
Chloride 98.4 mg/L E300.0 0.565 1.00 50,00 50 96 9 90-110 97.2 1.25 20
Lab Sample ID: 2003454-013AMSD Date Analyzed: 03/26/2020 2312h
Test Code: 300.0-W
Chloride 83.0 mg/L E300,0 0.565 1.00 50.00 36 94.0 90-110 83,5 0.661 20
Lab Sample ID: 2003454-022BMSD Date Analyzed: 03/20/2020 I 048h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 13.7 mg/L E353.2 0.0494 0.100 10.00 3.71 99.7 90-110 14 3 4.22 10
Lab Sample ID: 2003454-024BMSD Date Analyzed: 03/20/2020 I 053h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 14.5 mg/L E353.2 0 0494 0.100 10.00 3.91 106 90-110 14.5 0.0691 10
Lab Sample ID: 2003454-003BMSD Date Analyzed: 03/20/2020 I 004h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 13,5 mg/L E3532 0.0494 0.100 10.00 2.88 106 90-110 13.6 0.737 10
Lab Sample ID: 2003454-004 BMSD Date Analyzed: 03/20/2020 I 007h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 30.0 mg/L E353.2 0.0988 0 200 20.00 9,87 100 90 -110 31.4 4.57 10
Report Date: 3/31/2020 Page 76 of 85
All analyses applicable to the CW A, SDW A, 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 exclusive use of the addressee. Privileges of subsequent use of the
name uf 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 connecrion wirh the re-publication of this report for any puqmse other than for the addressee will be granted only on conlact .. This
company accepts no responsibility except for the due performance of inspection an<l/or analysis in good faith anJ according to the rules of the trade an<l of science.
American West
ANALYTiCAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: LCS VOC-1 032020A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 20.8
Chloroform 20.6
Chloromethane 14.2
Methylene chloride 20.8
Surr: l,2-Dichloroethane-d4 52.l
Surr: 4-Bromofluorobenzene 49.4
Surr: Dibromofluoromethane 49.2
Surr: Toluene-d8 49.5
Lab Sample ID: LCS VOC-1 0320208 Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 22.3
Chloroform 21.6
Chloromethane 16.9
Methylene chloride 22.6
Surr: l,2-Dichloroethane-d4 53.5
Surr: 4-Bromofluorobenzene 46.5
Surr: Dibromofluoromethane 49 2
Surr: Toluene-dB 48 1
Lab Sample ID: LCS VOC-1 032320A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 22.0
Chloroform 21.0
Chloromethane 17.6
Methylene chloride 22.9
Surr: l,2-Dichloroethane-d4 53.6
Surr: 4-Bromofluorobenzene 49.5
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:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
03/20/2020 739h
µg/L SW8260D 0.859 LOO 20.00
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
03/20/2020 1714h
µg/L SW8260D 0.859 1.00 20.00
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20 00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
03/23/2020 807h
µg/L SW8260D 0.859 1.00 2000
µg/L SW8260D 0.166 1 00 20.00
µg/L SW8260D 0.802 1 00 20.00
µg/L SW8260D 0.381 1.00 20 00
µg/L SW8260D 50 00
µg/L SW8260D 50 00
Tanner Holliday
MSVOA
LCS
Spike Ref.
Amount %REC
0 104
0 103
0 70.8
0 104
104
98.9
98.4
99,0
0 112
0 108
0 84.4
0 113
107
93.0
98.3
96.2
0 110
0 105
0 88.0
0 114
107
99,l
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
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 77 of85
All analyses applicable to the CWA, SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidenti;;,\ Business Information: This report is provide<l for the exclusive use of the addressee Privileges of subsequent use of the
name 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 addre:.see will he granted only on contact, This
company ~c.cepts no responsibility excepl for the due performance of inspection and/or analysis in good faith and according to the rules ufthe trade and of science.
/,.rnedcS\:1 '·.Nest
ANALYTICAL LAS0R'AT0fi 1ES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: LCS VOC-1 032320A Date Analyzed:
Test Code: 8260D-W-DEN100
Surr: Dibromofluoromethane 49.7
Surr: Toluene-d8 50.2
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:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
LCS
Spike Ref.
Amount %REC
03/23/2020 807h
µg/L SW82600 50.00 99.4
µg/L SW8260D 50.00 100
Limits
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 78 of 85
All analyses applicable to the CWA. SDWA, and RCRA arc performed in accordance to NELAC protocols. Peninent sampling information is \occtted on the anacbed COC. Confidential Business Information: This report is provided for the exclusive use of the addressee. Privileges of subsequent use uf the
name of this company or any member of its staff. or reproduction of this report in connecti()n with the advertisement, promotion or sale of any product or process, or in connection with the re-publication of this report for any purpo:.e other than for the addressee will be granted only un s.:ontact. This
company accepts no responsibility except for the due perfonnance of inspection and/or analysis in good faith and according to the rules of the trade and of science.
)'>.,n,e:-ic·an "sf/E:~st
ANALYT!CAL LABOR'ATO~JES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: LCSD VOC-1 032020B Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 20.6
Chloroform 21.2
Chloromethane 15.8
Methylene chloride 21.9
Surr: l,2-Dichloroethane-d4 53.0
Surr: 4-Bromofluorobenzene 47,9
Surr: Dibromofluoromethane 48.8
Surr: Toluene-d8 48.8
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:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
LCSD
Spike Ref.
Amount %REC
03/20/2020 1734h
µg/L SW8260D 0.859 1.00 20.00 0 103
µg/L SW8260D 0.166 1.00 20.00 0 106
µg/L SW8260D 0.802 1.00 20.00 0 78,8
µg/L SW8260D 0.381 1.00 20,00 0 110
µg/L SW8260D 50.00 106
µg/L SW8260D 50 00 95.8
µg/L SW8260D 50 00 97.7
µg/L SW8260D 50.00 97.6
Limits
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
22.3 7.73 35
21.6 1.82 35
16.9 6.80 35
22.6 2.92 35
Qual
Report Date: 3/31/2020 Page 79 of 85
All analyses applicable to the CWA, SDWA, 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 exclusive use of the addressee, Privileges of subsequent use of the
name of this company or any member of its staff, or reproduction of this repon in connection with the advertisement, promotion or sale of any product or process, or in c.:onnection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
company accepts no responsibility ~xccpL for the due performance of inspection and/or analysis in good faith and according to the rules of the trade and of science
.t\rr,e:~tc::.~a1·3 \/\!&st
ANALYTICAL LABOJ::ATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: I st Quarter Chloroform 2020
Analyte
Lab Sample ID: MB VOC-1032020A
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-1 0320208
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-1 032320A
Test Code: 8260D-W-DENJOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Result
Date Analyzed:
< 1.00
< 1.00
< 1 00
< 1 00
52.1
50.8
48.4
49.8
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
53.6
47 8
47 8
48,2
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
54.1
48.8
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: Tanner Holliday
Units Method MDL
03/20/2020 759h
µg/L SW8260D 0.859
µg/L SW8260D 0.166
µg/L SW8260D 0.802
µg/L SW8260D 0.381
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
03/20/2020 1754h
µg/L SW8260D 0.859
µg/L SW8260D 0.166
µg/L SW8260D 0.802
µg/L SW8260D 0.381
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
03/23/2020 827h
µg/L SW8260D 0 859
µg/L SW8260D 0.166
µg/L SW8260D 0.802
µg/L SW8260D 0.381
µg/L SW8260D
µg/L SW8260D
Reporting
Limit
l.00
1.00
l.00
1.00
1.00
1.00
1.00
1 00
1.00
1.00
1.00
LOO
Dept: MS VOA
QC Type: MBLK
Amount Spiked Spike Ref.
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
Amount %REC
104
102
96.8
99.7
107
95.6
95.5
96.4
108
97.7
Limits
80 -136
85 -121
78 -l 32
81 -123
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 3/31/2020 Page 80 of 85
All ao<1lyses applicabk to the CW A, SDW A. and RCRA are performed in accordance to NE LAC protocols. Pertinent sampling infonnation is located on the attached COC. Confidential Businc::ss lnfonnation: This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the
name of this comp:my or any member of its staff, or repro<luction of this report in connection with the advertisement, promotion or sale of any product or p1ocess. or in connection with the re-publication of chis report for any purpose other than for the addressee will be granted only on contact. This
company acCt!pLs no responsibility except for 1he due performance of inspection an<l/or analysis in go<.ld faith and accQrding to th!! rules ufthe trade aml of science,
ANALYTICAL
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: MB VOC-1 032320A Date Analyzed:
Test Code: 8260D-W-DENIOO
Surr: Dibromofluoromethane 49 0
Surr: Toluene-d8 48.7
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:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
MBLK
Spike Ref.
Amount %REC
03/23/2020 827h
µg/L SW8260D 50,00 98.0
µg/L SW8260D 50,00 97.4
Limits
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 81 of 85
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on the artached COC. Confidential Business information: This repon is provided for the exclusive use of the addressee Privileges of subsequent use of the
name of this company or any member of its staff, or reproduction of this report in connection with the advertisemen~ 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
company accepts no responsibility except for the due performance of inspection and/or analysis in good faith and according to the rules of the trade and of scienct:.
American West
ANAIY'TlCAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2003454-002CMS Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 20.8
Chloroform 20.2
Chloromethane 14.1
Methylene chloride 20.9
Surr: l,2-Dichloroethane-d4 53.1
Surr: 4-Bromofluorobenzene 49.6
Surr: Dibromofluorornethane 49.6
Surr: Toluene-d8 49.2
Lab Sample ID: 2003454-012CMS Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 18.6
Chloroform 19.6
Chloromethane 12.2
Methylene chloride 20.9
Surr: l,2-Dichloroethane-d4 52.8
Surr: 4-Bromofluorobenzene 46.8
Surr: Dibromofluoromethane 49 0
Surr: To] uene-d8 48 0
Lab Sample ID: 2003454-026CMS Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 222
Chloroform 956
Chloromethane 170
Methylene chloride 231
Surr: l,2-Dichloroethane-d4 524
Surr: 4-Bromofluorobenzene 480
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:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
03/20/2020 1018h
µg/L SW8260D 0.859 1.00 20.00
µg/L SW8260D 0.166 1.00 2000
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
03/20/2020 1814h
µg/L SW8260D 0.859 1.00 20.00
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0 802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
03/23/2020 1304h
µg/L SW8260D 8.59 10.0 200.0
µg/L SW8260D 1.66 10.0 200 0
µg/L SW8260D 8.02 10.0 200.0
µg/L SW8260D 3.81 10 0 200.0
µg/L SW8260D 500.0
µg/L SW8260D 500.0
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
0 104
0 101
0 70.3
0 105
106
99 3
99.3
98.4
0 93.1
0 98.0
0 61.l
0 104
106
93,5
98.0
95.9
0 111
746 105
0 85,l
0 116
105
96.0
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
77 -143
85 -124
30 -149
65 -154
80 -136
85 -121
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 82 of 85
All analyses applicable to the CWA, SOWA, and RCRA are perfonned in accordance to NELAC protot:ols. Peninent sampling information is located on the anached COC. Confidential Business Information: This report is provic.le<l for the exclusive use of the addressee. Privileges of subsequent use of the
name of this company or any member of its st.aff, or reprnd11cLion of this repon in connection with 1he advertisement, promolion 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
company accepts no responsibility excepl for the due perfi:>rmance ofinspection and/or analysis in good faith and according to tht! rules of the trade and of science,
P .... mer;can \;\/est
ANALYTICAL LA60RATORlES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2003454-026CMS Date Analyzed:
Test Code: 8260D-W-DENJOO
Surr: Dibromofluoromethane 488
Surr: Toluene-d8 485
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:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
03/23/2020 1304h
µg/L SW8260D 500.0 97.7
µg/L SW8260D 500.0 97.0
Limits
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 83 of 85
All 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 the
name of this company or any member of ils staff, or reproduction of this repon in connectilm 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 addre~see will be granted only on contact. This
company accepts no responsibihty except for the due perfonnance of inspection and/or analysis in good faith and according co the rules of the trade and of science.
American est
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: I st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2003454-00lCMSD Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 22.6
Chloroform 21.8
Chloromethane 13.8
Methylene chloride 22.3
Surr: l ,2-Dichloroethane-d4 53.0
Surr: 4-Bromofluorobenzene 49.7
Surr: Dibromofluoromethane 49.7
Surr: Toluene-d8 49.4
Lab Sample ID: 2003454-0llCMSD Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 20.1
Chloroform 20.7
Chloromethane 13.9
Methylene chloride 21.9
Surr: I ,2-Dichloroethane-d4 53.7
Surr: 4-Bromofluorobenzene 48.9
Surr: Dibromofluoromethane 48.9
Surr: Toluene-dB 48.8
Lab Sample ID: 2003454-026CMSD Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 212
Chloroform 924
Chloromethane 159
Methylene chloride 224
Surr: l,2-Dichloroethane-d4 527
Surr: 4-Bromofluorobenzene 486
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:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
03/20/2020 1037h
µg/L SW8260D 0.859 I 00 20.00
µg/L SW8260D 0.166 I 00 20.00
µg/L SW8260D 0 802 1.00 20.00
µg/L SW8260D 0.381 1 00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50_00
µg/L SW8260D 50.00
03/20/2020 1834h
µg/L SW8260D 0.859 1.00 2000
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 0.802 1.00 20.00
µg/L SW8260D 0.381 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
03/23/2020 1324h
µg/L SW8260D 8.59 10,0 200,0
µg/L SW8260D 1.66 10,0 200.0
µg/L SW8260D 8.02 10.0 200,0
µg/L SW8260D 3.81 10.0 200,0
µg/L SW8260D 500,0
µg/L SW8260D 500.0
Tanner Holliday
MSVOA
MSD
Spike Ref.
Amount %REC
0 113
0 109
0 68.9
0 Ill
106
99.4
99.3
98.7
0 101
0 104
0 69.6
0 110
107
97.8
97.8
97.6
0 106
746 88.8
0 79.4
0 112
105
97.2
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
77-143
85 -124
30 -149
65 -154
80 -136
85 -121
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit
20.8 8.07 35
20.2 7.38 35
14.1 2.01 35
20.9 6.21 35
18.6 7.64 35
19.6 5.51 35
12.2 13.1 35
20.9 4 86 35
222 4 75 35
956 3.46 35
170 6.81 35
231 3.16 35
Qual
Report Date: 3/31/2020 Page 84 of 85
All 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 the
name of this company or any member of its staff, or reproduction of this repon 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
company accepts no responsibility excepl for the due performance of inspection and/or analysis in good faith and according to the rules of the trade and ~lfscience.
,(,,n:edcan VVE~s't
ANALVTtCAL LABOFlATOR:IES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2003454
Project: 1st Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2003454-026CMSD Date Analyzed:
Test Code: 8260D-W-DENJOO
Surr: Dibromofluoromethane 490
Surr: Toluene-d8 488
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
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
MSD
Spike Ref.
Amount %REC
03/23/2020 1324h
µg/L SW8260D 500.0 98.0
µg/L SW8260D 500.0 97.5
Limits
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2020 Page 85 of 85
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols, Pertinent sampling infonnation is located on the attached COC. Confidential Business Information: This report is provided for the t":Xclusive use of the addressee. Privileges of subsequent use of the
name of this company or any member of its staff, or reproduction of this report in connectilm with the advertisement, promotion or sale of any product or process, or in connection with the re-publication of this report for any puqrnse other than for the addressee will be granted only on contact. This
company accepts no responsibility except for the due performance of inspection and/or analysis in good faith and according to rhe rules of the trade and of science
American West Analytical Laboratories Rpt Emailed: UL
Denison
WORK ORDER Summary Work Order: 2003454
Due Date: 4/2/2020
Page I of6
Client:
Client ID:
Project:
Comments:
Sample ID
2003454-00 I A
2003454-001 B
2003454-001 C
2003454-002A
2003454-002B
2003454-002C
2003454-003A
2003454-003B
2003454-003C
2003454-004A
2003454-004 B
2003454-004C
2003454-005A
2003454-005B
Printed: 03/30/20 16:54
Energy Fuels Resources, Inc.
ENE300 Contact: Tanner Holliday
1st Quarter Chloroform 2020 QC Level: III WO Type: Project
QC 3 (no chromatograms). EDD-Denison. CC [e-mail] & [e-mail]; (USE PROJECT for special DLs). Do not use
"*R_" samples as MS/MSD.;
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
TW4-03R_03162020 3/16/2020 0745h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
N02/N03-W-353.2 ~ df-no2/no3
J SEL Analytes: N03N02N
8260D-W-DENIOO ~ VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
TW4-03_ 03172020 3/17/2020 0805h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 ~ df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DENIOO ~ VOCFridge
Test Group_:_ 8260D-W-DEN I 00; # of Analytes: 4 I# of Surr: 4
TW4-42_03172020 3/17/2020 0823h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL A11a/y1es: CL
N02/N03-W-353.2 ~ df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 0 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
TW4-28_03172020 3/17/2020 0832h 3/19/2020 1420h 300.0-W Aqueous df-wc
1 SEL A11al)•tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anag,_tes: N03N02N
8260D-W-DEN100 ~ VOCFridge
Test Group: 8260D-W-DE!v/OO; # of Analytes: 4 /# ofSurr: 4
TW4-32_03172020 3/17/2020 0839h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Anag,_tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anag,_tes: N03N02N
LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ _ HOK ___ _ HOK COC Emailed ______ _
3
3
3
WORK ORDER Summary Work Order: 2003454 Page 2 of6
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2003454-00SC T\\14-32_03172020 3/17/2020 0839h 3/19/2020 1420h 8260D-W-DENIOO Aqueous ~ VOCFridge 3
Test Group: 8260D-W-DEN I 00; # of Analytes: 4 I # of Surr: 4
2003454-006A TW4-I2_03172020 3/17/2020 0845h 3/19/2020 l 420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
2003454-0068 N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-006C 8260D-W-DENIOO 0 VOCFridge 3
Test Group: 8260D-W-DEN I 00; # of Analytes: 4 I# of Surr: 4
2003454-007 A TW4-13_03172020 3/17/2020 0854h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
2003454-0078 N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-007C 8260D-W-DENIOO 0 VOCFridge 3
Test Group: 8260D-W-DENIOO: # of Analytes: 4 I # ofSurr: 4
2003454-008A T\\14-36_03172020 3/17/2020 0903h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Ana/ytes: CL
2003454-0088 N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-008C 8260D-W-DENIOO ~ VOCFridge 3
Test Group: 8260D-W-DEN I 00; # of Analytes: 4 I # of Surr: 4
2003454-009A TW4-3l_03I72020 3/17/2020 0912h 3/19/2020 1420h 300.0-W Aqueous 1.11 df-wc
I SEL Ana/ytes: CL
2003454-0098 N02/N03-W-353.2 1.11 df-no2/no3
I SEL Analytes: N03N02N
2003454-009C 8260D-W-DENIOO ~ VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I # ofSurr: 4
2003454-0JOA TW4-34_03172020 3/17/2020 0920h 3/l 9/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL A11alytes: CL
2003454-01 OB N02/N03-W-353.2 ~ df-no2/no3
I SEL A11alytes: N03N02N
2003454-01 OC 8260D-W-DENIOO ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
2003454-011 A TW4-35_03I72020 3/17/2020 0928h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL A11alytes: CL
Printed: 03/30/20 16:54 LABORATORY CHECK: %M 0 RT 0 CN D TAT 0 QC D LUO O HOK ____ HOK ----HOK ____ COC Emailed _______
WORK ORDER Summary Work Order: 2003454 Page 3 of6
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2003454-0 l lB TW4-35_03172020 3/17/2020 0928h 3/19/2020 1420h N02/N03-W-353.2 Aqueous J;;i] elf-no2/no3
1 SEL Analyzes: N03N02N
2003454-011 C 8260D-W-DENIOO ~ VOCFridge 3
Test Group: 8260D-W-DEN I 00; # of Analytes: 4 I# of Surr: 4
2003454-012A TW4-23_03172020 3/17/2020 0937h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
2003454-012B N02/N03-W-353.2 J;;i] elf-no2/no3
I SEL Analytes: N03N02N
2003454-0 l 2C 8260D-W-D ENIOO ~ VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I # ofSurr: 4
2003454-0BA MW-32_03182020 3/18/2020 I 005h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
2003454-0 !3B N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N0 2N
2003454-0 l 3C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DEN JOO; # of Analytes: 4 I # of Surr: 4
2003454-014A TW4-38_03172020 3/17/2020 0945h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Analytes: CL
2003454-014B N02/N03-W-353.2 ~ df-no2/no3
1 SELAnalytes: N03N02N
2003454-014C 82600-W-DENIOO 0 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 /# of Surr: 4
2003454-0ISA TW4-l4_03I72020 3/17/2020 0955h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-0 l 5B N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-0 I SC 8260D-W-DENIOO ~ VOCFridge 3
Test Groul!.: 8260D-W-DENJOO; # of Analytes: 4 I # of Surr: 4
2003454-016A TW4-06_03172020 3/17/2020 1005h 3/19/2020 1420h 300.0-W Aqueous !Jl df-WC
1 SEL Analyzes: CL
2003454-016B N02/N03-W-353.2 ~ elf-no2/no3
1 SEL Analytes: N03N02N
2003454-0 l 6C 82600-W-DENIOO ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 /# ofSurr: 4
Printed: 03/30/20 16:54 LABORATORY CHECK: %M 0 RT 0 CN 0 TAT 0 QC O LUO O HOK ___ _ HOK ___ _ HOK ___ _ COC Emailed ______ _
WORK ORDER Summary WorkOrder: 2003454 Page 4 of6
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2003454-017 A TW4-27_03172020 3/17/2020 1014h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-0178 N02/N03-W-353.2 vi df-no2/no3
1 SEL Ana/ytes: N03N02N
2003454-017C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 !# ofSurr: 4
2003454-018A TW4-05_03172020 3/17/2020 1024h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-0188 N02/N03-W-353.2 vi df-no2/no3
1 SEL Ana/ytes: N03N02N
2003454-018C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # of Surr: 4
2003454-019A TW4-30_03172020 3/17/2020 1038h 3/19/2020 1420h 300.0-W Aqueous vi df-wc
1 SEL Analytes: CL
2003454-0198 N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-019C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
2003454-020A TW4-09R_03172020 3/17/2020 1100h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-0208 N02/N03-W-353.2 ~ df-no2/no3
1 SEL Analytes: N03N02N
2003454-020C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Surr: 4
2003454-021 A TW4-09_03182020 3/18/2020 0508h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-0218 N02/N03-W-353.2 ~ df-no2/no3
1 SEL Analytes: N03N02N
2003454-021 C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I # ofSurr: 4
2003454-022A TW4-18_03182020 3/18/2020 0518h 3/19/2020 1420h 300.0-W Aqueous ~ df-WC
1 SEL Analytes: CL
2003454-0228 N02/N03-W-353.2 ~ df-no2/no3
1 SELAnalytes: N03N0 2N
2003454-022C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Surr: 4
Printed: 03/30/20 16:54 LABORATORY CHECK: %M 0 RT 0 CN 0 TAT 0 QC O LUO O HOK ____ HOK ----HOK ____ COC Emailed -------
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID Collected Date
2003454-023A TW4-08_03182020 3/18/2020 0532h
2003454-023B
2003454-023C
2003454-024A TW4-16_03182020 3/18/2020 0540h
2003454-024B
2003454-024C
2003454-025A TW4-33_03182020 3/18/2020 0550h
2003454-0258
2003454-025C
2003454-026A TW4-07_03182020 3/18/2020 0600h
2003454-026B
2003454-026C
2003454-027 A TW4-29_03182020 3/18/2020 0612h
2003454-0278
2003454-027C
2003454-028A TW4-10_03182020 3/18/2020 0625h
2003454-0288
Work Order: 2003454
Due Date: 4/2/2020
Received Date Test Code Matrix Set Storage
3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 ~ df -no2/no3
I SEL Analytes: N03N02N
8260D-W-DENIOO ~ VOCFridge
Test Grouf)_: 8260D-W-DENJOO; # of Anal)'tes: 4 I # o[Surr: 4
3/19/2020 1420h 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-JY-DEN 100; # of Analytes: 4 I# of Surr: 4
3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL A1tal)l_tes: CL
N02/N03-W-353.2 ~ df -no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 ~ VOCFridge
Test Groue_: 8260D-W-DEN I 00; # of A11a/y1es: 4 I # of Surr: 4
3/19/2020 1420h 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-DENJOO; # of Analytes: !_I# ofSurr: 4
3/19/2020 1420h 300.0-W Aqueous ~ df-wc
I SEL Anail_tes: CL
N02/N03-W-353.2 ~ df -no2/no3
1 SEL Anail_tes: N03N02N
8260D-W-DEN100 ~ VOCFridge
Test Group_: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
3/19/2020 1420h 300.0-W Aqueous df-wc
I SEL A11al.f_1es: CL
N02/N03-W-353.2 ~ df -no2/no3
1 SEL Anail_tes: N03N02N
Page 5 of6
3
3
3
Printed: 03/30/20 16:54 LABORATORY CHECK: %M O RT O CN O TAT D QC O LUO 0 HOK ___ _ HOK ___ _ HOK_ _ _ _ COC Emailed ______ _
WORK ORDER Summary Work Order: 2003454 Page 6 of6
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2003454-028C TW4-10_03182020 3/18/2020 0625h 3/19/2020 1420h 8260D-W-DEN100 Aqueous ~ VOCFridge 3
Test Group:_§260D-W-DENJOO; # of Analytes: 4 I # of Surr: 4
2003454-029A TW4-26_03182020 3/18/2020 0635h 3/19/2020 1420h 300.0-W Aqueous ~ df-we
1 SELAnalytes: Cl
2003454-029B N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N02N
2003454-029C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I # of Surr: 4
2003454-030A TW4-65_03172020 3/17/2020 0805h 3/19/2020 1420h 300.0-W Aqueous vi df-wc
1 SEL Analytes: CL
2003454-030B N02/N03-W-353.2 ~ df-no2/no3
1 SEL Analytes: N03N02N
2003454-030C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 /# ofSurr: 4
2003454-03 I A TW 4-70 _ 03172020 3/17/2020 1024h 3/19/2020 1420h 300.0-W Aqueous ~ df-wc
1 SEL Analytes: CL
2003454-03 l B N02/N03-W-353.2 ~ df-no2/no3
I SEL Analytes: N03N0 2N
2003454-031 C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Surr: 4
2003454-032A TW4-75_03182020 3/18/2020 1005h 3/19/2020 1420h 300.0-W Aqueous vi df-wc
I SEL Analytes: CL
2003454-032B N02/N03-W-353.2 vi df-no2/no3
1 SEL Ana lyres: N03N02N
2003454-032C 8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I # ofSurr: 4
2003454-033A Trip Blank 3/16/2020 0745h 3/19/2020 1420h 8260D-W-DEN100 Aqueous ~ VOCFridge 3
Test Group: 8260D-W-DENJOO; # <>[A11al)!_tes: 4 I # of Sw·r: 4
Printed: 03/30/20 16:54 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# [phone] Toll Free# [phone] L~ Fax# [phone] Email awal@awal~abs.com
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Tanner Holliday
Phone#: [phone] Cel #-.
gpalmei@e,,ergyf\tels.com; [e-mail];
Email: tho~erufaeI£.com
Project Name: 1st Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samele ID: Samoled
TW4-03R_03162020 3/16/2020
• TW4-03_03172020 3/17/2020
, TW4-42_03172020 3/17/2020
· TW4-28_03172020 3/17/2020
• TW4-32_03172020 3/17/2020
1 TW4-12_03172020 3/17/2020
TW4-13_03172020 3/17/2020
TW4-36_03172020 3/17/2020
TW4-31_03172020 3/17/2020
l TW4-34_03172020 3/17/2020
I TW4-35_03172020 3/17/2020
z TW4-23_03172020 3/17/2020
~ ;MW-32_03182020 3/18/2020
R~od Irr-.\ ...J....l _// ./_ On!«
--.... a.llllb;r , I J -3118'2020
(/ Tuno:
PrlntN.:.ma: Tannor Hottldov I""'
Rollnq<llehed Irr-D:ilo:
Sk,Mluro
Timo:
PM! N<lmo:
-~by. llalo:
ISlonotoro
Tlmo:
Prir4Nlll!10;
Rolinoliiiliodoy: ODCo;
Sinn.In,,.
Tlmo:
Pr1nt Nam«
I
Time
Sampled
745
805
823
832
839
MS
854
903
912
920
928
937
1005
~eceived by:
Sicnature
Print Name:
CHAIN OF CUSTODY
All analysis v.(~ be conducted using NELAP accntdited methods ard aJI data v.,11 be reported using AWAJ..'s sta:idaro analyte lists ard reporting
llmtts (PQL) i.mless spedftcaKy requested otherwise on this Chain of Custody and/or attached documentatk>n.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed ra~rts will be emaned b)' 5:00 pm on
3 Standard the day they are due,
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
D RCRA
D CWA
D SDWA
D ELAP /A2LA
c' D NLLAP
<'I' c:i D Non-Compliance ~ C, G' tJ other. 0) ~ l2. !; C, ~ -~ (') IO
19 iii 0 C, cs
C: :::;; I!; Sl !£. Known Hazards 0 ., ...... ~ .. u a. ('I 0 & 'o E g ti g .. Sample Comments .. "'
5 w X X X
5 w X X X
5 w X X X
s w X X X
5 w X X X
5 w X X X + ~ C,l borlle.,-l i;.i ,CpJJ
5 w X X X Off_:--.~-:~.,--;
5 w X X X .,r• .. ~.
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•
2 CO::tit> L\
AWAL Lab Sample Set#
Page 1 of 3
DueD4) 2q fro
Laboratory Use Only
s-p; ... w.,.. uJ>5
~-d,llven,d
2 Am!x.,,(~
3 Ton.....,.uro •03 •c
4 -odBn>t.-1ng
~.,t;'N l!,I ~
5d::Preserved y N
at bench
y ~
6 Recolved Wnhin
(!!Times N
Coe Tape Was:
1 PrasentonOtJterP~
Y N NA
2 --0-~~ Y N NA
3 Present on Sample
y N
Cl
'4 Unbroken on Sample
Y N " NA
Discrepancies Between Sample
~abels and Coe Recoor>~
y N
Received by: Da1e: See the Analytical Scope of Work for Reporting Limits and voe
Sl~mature analyte list. lime:
Prfi,tNa.i:na:
Received t>y: foale:
Si!:mature
Time:
Prin1:Name: -,.. I =by: t' JO .u, ~ L\O~ 1 AJJ IOate: ~ }Cd2D
J..lc:>Y\\~~ ...... 11, 1n Time: 1 tJ./.!2...0 Print Name:
~
15
,v
11
\i
ff .,,.
").I
y
'/1),
')-'r
,,j
,Jf)
~
American West
Analytical Laboratories
463 W. 3600 S. Salt Laka City, VT 84115
Phone# [phone] Toll Free# [phone]
Fax# [phone] Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
BlaDding, UT 84511
Contact: Tanner Holliday
Phone#: [phone] Cell#:
CHAIN OF CUSTODY 2~:i
Alt analysts will be conducted tJsing NELAP accredited methods and all data will be reported us;ng AWAJ..'s standard analyie lists and reporting
limits (POL) mless specifically requested olherwise on this Chain of Custody and/or attached documentation.
AWAf. Lab Sample Set-#
Page 2 of
QC Level:
3 J Tum Around Time:
Standard
Unl866olherarrangements have been made, 11Due Dat4e: )~
slgnoo A>ports ~II be emailed by 5:oo pm on --, c)
the day they are due. I..,,
X Include EDD:
LOCUS UPLOAD
EXCEL
Laboratory Use Only
Field Filtered For: Sam~W-: ll'f) 1-~~~~~~~~~~---11 ~~
For Compllance With:
3
gpaJ.ma@cJ>ci@iioll,com; KWm.oa!@euerofu-o'"b-.co-m-;---------D NELAP
D RCRA
3 Temperall>'a ~·c
Email: tholllday@eD'-&)'fuc1-.com
Project Name: 1st Quarter Chlorofonn 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Samole ID:
TW4-38_03172020
TW4-14~03172020
TW4-06_03172020
TW4-27_03172020
TW4-0S_03172020
TW4-30_03172020
TW4-09R_03172020
TW4-09_03182020
TW4-18_03182020
TW4-08_03182020
TW4-16_03182020
TW4-33_03182020
TW4-07 _03182020 rff~~ _, #-vi,£.~ Slgnalura -J a,JI.-IVI{ , •
Print Name:
Prtnt_Na_me:
RoJ!nq!Jlsl),,d by.
ISlonoluno
Print Name:
Rollnquilll!OO by.
is<iinowro
Print Name:
Tanner Holliday
~ ~
Date
Sampled
~ X !2. .. <= '<= I') ·;; 1ii 0 C: ::. 0 CL> I!!;
{.) ,, Time C. N '1; E ~ Samoled .. .. "'
3/17/2020 945 5 w X
c" c C D' "> ... C 0 "' C "' C ~ 11) Ill ~ t)
6 g
X X
0 CWA
0 SOWA
0 ELAP/A2LA
0 NLLAP
D Non-Compliance
D Other.
Known Hazards
&
Sample Comments
• RocolvodBIOk~
(lmp,,,por1tS.•lady~-
Y ~
5 O.:' Pr.-ved V II
albr.irlcJ>'
y -c:,
e floetrlvorlWltllln
~Times u N
955 5 w X X X
1005 5 w X X X
1014 5 w X X
~/1'7/'>:tv>n ------1 ,l"lr,, 1 Jlr,, I .ll,. I I I I I I I I I I ·~OCTapeWas: ~
II I PJ1IS80!onOutarP lxlxlxl I I I I I I I I I I v N ""
IW I X I X I X I I I I I I I I I I II 2 UnbrokenonOuterPac~
1024 5 w X X
1038 s w X X X
1100 5 w X X X
508 5 w X X X
II Y N NA
.11...:.X:...LI :..:.X.J.I ~X:..JI_J-1 __J..1--11-+-I --41-~I -+I HIHII--------,, _ -----· ----·
3/1'1/2020 3 Prasent on Semplo ~
y N V
4 Unbroken on Semple ~
y N '\....._)
3/17/2020
3/18/2020
518 s w X X y
532 5 ·w X
540 5 w X )\. )\.
~,1Rt2.m>.n ----·· , "oloctopond ... -8
I ll.obels arid COC Roc:o,a?. XXX I I I I I I I 11 I y N
I II ~/ J.a/-;/,\TI/U --....... •~
3/18/2020 550 5 w X X X
3/18/2020 600 5 w X X X
Date: eoe1ved by:
3/18/2020 s· nat1Xe Special Instructions:
l'tme~
1030 Print Name:
Date: Received bl iate: !Received by: josta: II See the Analytical Scope of Work for Reporting Limits and voe
Sinna
'TimEr
s· natu,e lanalyte list.
Print Name:
Date: Received by:
Slanature
Time:
Print Name: ..... _l_ I
Date: Recel'ved by:
l~lnnotura \O~.J:i>, 1 ~ Dato: 3/lqJ~
Time:
Print N.sm._!t .--1 ~ ~\.~ 6-c-i.t.4'1 !Tim•= 'Jq,. 2.D
7
American West
Analytical Laboratories
463 W. 3600 S. Saltlake City, UT 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: Tanner Holliday
Phone#: [phone] Celllt.
gpal.me<@enciijfiiela.com, KW6lncl@=C<Ofaeb.com;
Email: thollidll,Y(?,cnercfueh.com
Project Name: 1st Quarter Chloroform 2020
Project#;
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Sampled
TW4-29_03182020 3/18/2020
~. TW4·10.c03182020 3/18/2020
I~ TW4-26_03182020 3/18/2020
) , TW4-65_03172020 3/17/2020
. , TW4-70_03172020 3/17/2020
~ TW4-75_03182020 3/18/2020
~ Trip Blank 3/16/2020
8
g
10
11
12
13
RB/1nquished by: \,1 It//,/ '7,/ Oata:
S~nature • D ,1 ~ w-Zl1Bl"l020
I Time:
Print Name: Tanner Hollldav 1000
Retinquished by: Date:
Slanature
Time:
PdrtNamo,
Rellnqu\shed by: Date:
Slonahn&
Tme:
Print Name:
R.effnquished by; f.)ale:
Signature
rnme:
Print Name:
Time
Sampled
612
625
635
805
1024
1005
745
RACelved by:
SignalUl'8
Pr1ntNeme:
l](ecelved by:
ISli:inature
PrfntNarr:ie:
Received by:
Signatore
PJ1ntNeme:
Receivea by:
Sicmature
Prial Name:
I
CHAIN OF CUSTODY
All anmysi°6 will be conducted using NELAP accredited methods and all data will be reported using AWAL's standard analyte Hsts and reporting
limit6 (POL) unless specifically requested otherwfse on this Chain of Clnitody and/or stteched documentation.
QC Level: I Tum Around Time: Unless other a1Tangements have been made,
signed reports will be emailed by 5:00 pm""
3 Standard the day they are due.
IX Include EDD:
LOCUS UPLOAD
!!.XCEL
Field Fdlered For.
For Compliance With:
D NELAP
D RCRA
I D CWA
I D SOWA
D ElAP/A2LA
c' D NLLAP ~ c:i 0 Non-Compliance ~ C, D' D Other.
'2. <') s ... C, " 0 IQ C: :s (') C, ~ ~ <D 0 :;; C, Known Hazards 0 ID la: It) ...... :t. lJ u a. N & 0 E 0 tl g <D la: Sample Comments .. ti)
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
3 w X
Date: Special Instructions:
lll<TlB'
Zeo11i151
AWAL Lab Samplo Set#
Page 3 of 3
Due4\2, }])
Laboratory Use Only
Sam~w-: ~~:J
~rhn "im
~ Amlll...te
3 Temperature 16 0? •c
4 Reoeived Broken/Leaking
~:v 6 ....-,oc1
N
atbono/,
6 :ceivedWllhln6 ()Tim~ N
COC Tepe Was:
1 Present on Outer P~
Y N NA
2 Unbrcken on OutorP~
Y N NA
3 ·-·-8 y N
4 Unbroken on &Hrt;pt9
Y N NA
)),=-.. e-GS Labels and COC Reco ?
y N
Date: See the Analytical Scope of Work for Reporting Limits and VOC
analyte list.
l'flme:
O,ne:
Time:
A -I 1() A,1 i A ()j/,,1.:, ln .u..) Deto: 3 /19 }2.-0
.~n\c::..o l6n.A.11h Tinw. • /'-(: 21)
-
Preservation Check Sheet
Lab Sample Set#: 2003454
"~001 .~002 -OQ3 -<f04 -:-005 ~006 -001·~ ~008 --0Q~f ·,"9~0 :-Op.--01_2 . -013 -914 · -015 ,, -QJ6 '
NOJN03: pH <2 H2S04 YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES
: ~J7 '-0~~ ~1, -Q2Q ' -Q.?1 -0n . -023 ~024 -025 ~Q~6 . -02·L C -02i -02? ·, -Q~~;.· ~03,1,-~ ,--032~
NOJN03: pH <2 H2S04 YES YES YES YES YES YES YES YES YES YES YES YES YES YES YES yes
NOJNO,: pH <2 H,so, jJ! I ' . 1 ··. I ; I ' ·1 1· . ' I I ' I ' I 1 .. I ' I r ·I I
~ ·31·,C\ \ 2..0
Tab I
Quality Assurance and Data Validation Tables
1-1 · Field QA/QC Evaluation
lx Casing 2x Casing
Location Volume Volume Pumped Volume Volume Check Conductivity RPO pH RPO Temperature RPO Redox Dissolved Oxygen RPO Turbidity RPO
MW-04 NA Continuousl:,,, Pumped well --1886 NC 7.39 NC 14.22 NC 255 0 NC
TW4-01 NA Continuously Purnped well ~-2414 NC 7.25 NC 14.15 NC 338 0 NC 72.5
TW4-02 NA
~ ... ··-;48-. --
TW4-04 NA
0 NC
r --:NM _,IIG·
0 NC
79.6
•. : T": ;NM ~
128.5
Continuously Pumped well --3798 NC 7.24 NC 14.40 NC 263 NC
-,:... -~ ,t<J•j_l1!lJJ -.-. _:: _J ,-. ~ ·-,,. _,, __ , Drv.. II .!11= JI. lie ~-0,on ,: • --6:HH ,_o q .· 11:eo• i -U;'l!l,I -1 1 · 13:'1.6! :iii. I,~.. l --.. NM' Ii
Continuously Pumped well -2362 NC 7.27 NC 14.85 NC 286 NC
TW4-05 33.70 3.0 3.0 0.00 57.0 56.4 88.00 67.4 okay 1495 1488 0.47 6.87 6.91 0.58 15.44 15.44 0.00 436 432 1.06
I ' ' ' 1'4.~-; _NM~.-NG---, l. ·11'1 11)1 . ~ . -~-185<f -~ _ , '28':n...-RumpeJf•l:>rv ,---_ r 3Hf:if) • .o:os · --T.B.16 . •· ... e:76 · .a::15 ,~ 13.48 ... _ , 13.50 , :: ·,0.15.o:.' , NM ·-_ , : :NC,
~.Io ':Z4.Ji\J __ ~, NM,· -I Ne--~:..."'::-JIM --49.~. ~ ... -~ ~~78 . ~ •Pum _ :-,f205 ~-~ ..::'"'1253'" --· 7·, .3,91 7,;22 __ , ~ 7.22 , ,, ~Q.oo .,. 13.50 1•, f3.56:-111 o.~·. NM ' . lll~-
TW4-08 26.28 1.6 1.6 0.00 1 .1 1.1 66.oo 52.56 okay 4908 4911 0.06 6.76 6.80 o.59 15.02 15.03 0.07 499 494 o.oo
TW4-09 33.87 88.00 67.74 okay 2449 2446 0.12 6.77 6.81 0.59 14.97 14.96 0.07 453 445 21.6 22.0 1.83 2.6 2.5
1W~1(if 'r .zu,r -
-_,NM -:;...:_ ; NC ,_ -"M -= -_ -, 40.33 _ _ • 159.84 , Pumoed,oa:v ZT.18 , L2738 , . o.81 6:89·· 6.87. ·· ·. ~o.29 (' f3.30 -: 13.38 -.:.0~ :-. -_ NM~ .,-
TW4-11 NA C0ntinu0usly Pumped w~II ·-3682 NC 7.01 NC 14.35 NC 275 NC 0 NC 68.4
I ~l;IV.~Jl~ ! ,J c 3t.'Z8-=...
, TW~1:1 f,I '' 32;55
"FW4"i~·-11.46 ii
_ =' -~ ~-4.'1;20 .-.:__ .·; I.~ sass-a.: ·_p.ufflDedll]) {_~ 139f l'i -14'08 -, .. r '11.21 , .., 1:28 , i\25 .. .'.. o:1v , 1,,. -1jj;-'9 13.3..3. • • 0.30 ~ • _ NM ~ --I · NC -'"'--NM& _,. -· .'. ~" _,: -: -· _l'!,I -
-:.: -44.00 .,, .•• --_ ··.-::. ~~ _ · PUIJ'INld'IO: , 1' 1ffi · ,_ -1E -o:36 ; -, 7),M: -7;34-,_ •• u:uu -_fS:18' ,-1;3:30 -I: ··01u, .. _.:: ' ~ .Nllif-• I~ NC_ ' . _c NMl -:·.-N\::i, -~·-.... ~ • _, = :N ;;
n .oo ;, -· 22:92"'-Pump.ed1c v '" -5243-.-, 5245 -~ ::..,Oi()i4 ' Bi~ _--=--e:~ _ 0.29 ·• 12~115 ,_ 1'3.05 ~ 0~54 . ,· NM _ .NC ·J tiM ,NS. , z • , :,NM .... ~N -
MW-26 NA Continuously Pumped well --3426 NC 7.01 NC 16.18 NC 316 NC O NC 21.2 NC
TW4-16 49.37 110.00 98.74 3643 3626 0.47 6.90 6.94 0.58 14.84 14.86 0.13 422 401 5.10 14.0 14.3 2.12 2.3 2.4 4.26 okay
MW-32 32.61 66.18 65.22 3677 3682 0.14 6.62 6.65 0.45 14.01 14.00 0.07 256 252 1.57 18.0 18.0 0.00 6.8 6.7 1.48 okay
TW4-18 42.84 99.00 85.68 1941 1910 1.61 6.68 6.69 0.15 15.47 15.47 0.00 463 461 0.43 11.1 11 .2 0.90 11 .0 11 .2 1.80 okay
TW4-19 NA eontlnuouslv Pumped well 3166 NC 6.82 NC 15.42 NC 359 NC o NC 39.2 NC --
TW4-20 NA y Pumped well 4377 NC 6.95 NC 15.51 NC 357 NC O NC 39.3 NC --
TW4-21 NA Continuously Pumped well 2761 NC 6.80 NC 15.90 NC 314 NC 79.2 NC 88.00 NC --
TW4-22 NA ly Pumped well 5222 NC 7.14 NC 15.20 NC 316 NC 1.6 NC 95.0 NC ..
TW4-23 27.48 okay 3481 3481 0.00 6.92 6.93 0.14 14.61 14.62 0.07 280 274 2.17 78 .0 78.6 -0.77 105.2 105.1 0.10
TW4-24 NA .. tinuously Pumped well 6512 NC 6.88 NC 14.56 NC NC 3.3 NC 18.4 NC 334
TW4-25 NA -266
NM'
IM ~-
IM .
M• l-
TW4-32 38.81 88.00 77.62 okay 6469 6473 0.06 4.36 4.37 0.23 14.84 14.83 0.07 496 496 0.00 7.8 7.7 1.29 1.1 1.2 8.70 .. 11.:, .. i2S ~ ,\_.: ,!2~ -;!O'!c
,~ liW:~ •. -;. 27.36·:· -
,_ -_ il.5:~ -~---.· .-, ':i: ~ 12;.5:;~ ";'.R(ifi~J::lr.v, ,, 4,!1.1 .--:, r _ -4 ~ .o:or :::., ir 6:89·_ -•,. 6;9J).1 .: :8.·1'5 Ir l 389'" II 13.98,., .-0..65 J: --NM._~---~ I'·-· "':.:NM'" .... ~-;·, rT ·,NM : C•• =•·~
...... • 1 ,18.50" t • -' ••· -.. ,pjj ffiritWY·. 11 -~ • _'" -.,_ O,:.v •. '!'tr~~ --,r~· 1 u 0.55 -.... 1~~ • ·, ,13,~:.. .. P:59 r ., .-, . NML -' -Nl3i --,Nu.;.:... -1 =· F 1.....-.;~r Nt.il -
• ,i!H251 I L -·-;c I• ::._ -· '427_.a1 --I',,· 4 " -~ Q;2t! --,-R';~_ ,_ o.~Jj ;;·. -n.?9 _,a.58 1'3:65. ~~ ;,()!5.1--· .!'."::: -· NM ,. --. I.. N ... , ., ..:.'Nllit. . ! -:. L. ,NM/ I, .C
·· -• · 33J>0.1~ :1-· ... . -._.P.unoecD.rv.,•;;,r_:z-~8:. \/ 238., .• 1 ,_..1),13.-. _.-u oCill:_,iii, ~1.N : ~"'0:28-_1 1e:a.B·-_ .Tz.117 -o}i;-,:: -.NM1: -"--NC ·, ~..:.-.NM•·,' -•''NC'~,t~. :NMr.~. '':NG!··
TW4-37 NA Continuously Pµmped well --4154 NC 7.06 NC 16.05 NC 323 NC O NC 72.1 NC
TW4-38 36.22 88.00 72.44 okay 1778 1780 14.75 14.73 0.14 470 469 0.21 23.0 23.2 0.87 51.0 50.8 0.39 0.11 6.75 6.76 0.15
TW4-39 NA NC 7.06 NC Continueuslv Pumped well --2317 15.35 NC 335 NC O NC 50.0 NC
TW4-40 NA NC 7.11 NC Continuously Pumi:>ed well •· 4003 15.32 NC 311 NC O NC 73.6 NC
TW4-41 NA NC 7.24 NC Continuously Pumped well -2778 16.00 NC 330 NC O NC 95.0 NC
1, lW~,42 • r 111.64 I::-< O,-sa-~ _ (t -1p,LD i;:: 7.25 .. _0.14',: -·-. I 13.7$ -· -I I I' ---23.28'." ·], .. P.titni>ed Ji1rv II. ~L .1lr ,!,3334 t3~1a: .. ,_ j 3J2!:r ~ -• l>lr3 « ,., -NM -Ii NC l'I~ NM·---... ~c=-: 1 ~ _NM ~ .• n ~ NG .• ,
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.
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
Trip Blank Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
Trip Blank Chloroform 2/19/2020 2/21/2020 2 14 OK
Trip Blank Chloromethane 2/19/2020 2/21/2020 2 14 OK
Trip Blank Methylene chloride 2/19/2020 2/21/2020 2 14 OK
Trip Blank Carbon tetrachloride 3/16/2020 3/20/2020 4 14 OK
Trip Blank Chloroform 3/16/2020 3/20/2020 4 14 OK
Trip Blank Chloromethane 3/16/2020 3/20/2020 4 14 OK
Trip Blank Methylene chloride 3/16/2020 3/20/2020 4 14 OK
MW-04 Chloride 2/19/2020 3/3/2020 13 28 OK
MW-04 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
MW-04 Chloroform 2/19/2020 2/25/2020 6 14 OK
MW-04 Chloromethane 2/19/2020 2/24/2020 5 14 OK
MW-04 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
MW-04 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-0l Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-01 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-01 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-0l Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-0l Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-01 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-02 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-02 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-02 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-02 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-02 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-02 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-03 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-03 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-03 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-03 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-03 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-03 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-03R Chloride 3/16/2020 3/27/2020 11 28 OK
TW4-03R Carbon tetrachloride 3/16/2020 3/20/2020 4 14 OK
TW4-03R Chloroform 3/16/2020 3/20/2020 4 14 OK
TW4-03R Chloromethane 3/16/2020 3/20/2020 4 14 OK
TW4-03R Methylene chloride 3/16/2020 3/20/2020 4 14 OK
TW4-03R Nitrate/Nitrite (as N) 3/16/2020 3/20/2020 4 28 OK
TW4-04 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-04 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-04 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-04 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-04 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-04 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-05 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-05 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-05 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-05 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-05 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-05 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-06 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-06 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-06 Chloroform 3/17/2020 3/20/2020 3 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-06 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-06 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-06 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-07 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-07 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-07 Chloroform 3/18/2020 3/23/2020 5 14 OK
TW4-07 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-07 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-07 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-08 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-08 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-08 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-08 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-08 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-08 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-09 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-09 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-09 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-09 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-09 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-09 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-09R Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-09R Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-09R Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-09R Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-09R Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-09R Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-l0 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-l0 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-l0 Chloroform 3/18/2020 3/23/2020 5 14 OK
TW4-l0 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-l0 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-l0 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-11 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-ll Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-ll Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-ll Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-11 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-ll Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-12 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-12 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-12 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-12 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-12 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-12 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-13 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-13 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-13 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-13 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-13 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-13 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-14 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-14 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-14 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-14 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-14 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-14 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
MW-26 Chloride 2/19/2020 3/3/2020 13 28 OK
MW-26 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
MW-26 Chloroform 2/19/2020 2/25/2020 6 14 OK
MW-26 Chloromethane 2/19/2020 2/24/2020 5 14 OK
MW-26 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
MW-26 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-16 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-16 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-16 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-16 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-16 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-16 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
MW-32 Chloride 3/18/2020 3/26/2020 8 28 OK
MW-32 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
MW-32 Chloroform 3/18/2020 3/20/2020 2 14 OK
MW-32 Chloromethane 3/18/2020 3/20/2020 2 14 OK
MW-32 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
MW-32 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-18 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-18 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-18 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-18 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-18 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-18 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-19 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-19 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-19 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-19 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-19 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
TW4-19 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-20 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-20 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-20 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-20 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-20 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-20 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-21 Chloride 2/19/2020 3/4/2020 14 28 OK
TW4-21 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-21 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-21 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-21 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
TW4-21 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-22 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-22 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-22 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-22 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-22 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-22 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-23 Chloride 3/17/2020 3/26/2020 9 28 OK
1-2: Holding Time Evaluation
Hold Time All9wed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-23 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-23 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-23 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-23 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-23 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-24 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-24 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-24 Chloroform 2/19/2020 2/21/2020 2 14 OK
TW4-24 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-24 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
TW4-24 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-25 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-25 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-25 Chloroform 2/19/2020 2/21/2020 2 14 OK
TW4-25 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-25 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
TW4-25 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-26 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-26 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-26 Chloroform 3/18/2020 3/23/2020 5 14 OK
TW4-26 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-26 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-26 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-27 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-27 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-27 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-27 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-27 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-27 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-28 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-28 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-28 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-28 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-28 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-28 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-29 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-29 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-29 Chloroform 3/18/2020 3/23/2020 5 14 OK
TW4-29 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-29 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-29 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-30 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-30 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-30 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-30 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-30 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-30 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-31 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-31 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-31 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-31 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-31 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-31 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 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
TW4-32 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-32 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-32 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-32 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-32 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-32 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-33 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-33 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-33 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-33 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-33 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-33 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
TW4-34 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-34 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-34 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-34 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-34 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-34 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-35 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-35 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-35 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-35 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-35 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-35 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-36 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-36 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-36 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-36 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-36 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-36 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-37 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-37 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-37 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-37 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-37 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-37 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-38 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-38 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-38 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-38 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-38 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-38 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-39 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-39 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-39 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-39 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-39 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-39 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-40 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-40 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-40 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-40 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-40 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
I-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) 2/19/2020 2/21/2020 2 28 OK
TW4-41 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-41 Carbon tetrachloride 2/19/2020 2/24/2020 5 14 OK
TW4-41 Chloroform 2/19/2020 2/25/2020 6 14 OK
TW4-41 Chloromethane 2/19/2020 2/24/2020 5 14 OK
TW4-41 Methylene chloride 2/19/2020 2/24/2020 5 14 OK
TW4-41 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-42 Chloride 3/17/2020 3/26/2020 9 28 OK
TW4-42 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-42 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-42 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-42 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-42 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-60 Chloride 2/19/2020 3/3/2020 13 28 OK
TW4-60 Carbon tetrachloride 2/19/2020 2/21/2020 2 14 OK
TW4-60 Chloroform 2/19/2020 2/21/2020 2 14 OK
TW4-60 Chloromethane 2/19/2020 2/21/2020 2 14 OK
TW4-60 Methylene chloride 2/19/2020 2/21/2020 2 14 OK
TW4-60 Nitrate/Nitrite (as N) 2/19/2020 2/21/2020 2 28 OK
TW4-65 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-65 Carbon tetrachloride 3/17/2020 3/23/2020 6 14 OK
TW4-65 Chloroform 3/17/2020 3/23/2020 6 14 OK
TW4-65 Chloromethane 3/17/2020 3/23/2020 6 14 OK
TW4-65 Methylene chloride 3/17/2020 3/23/2020 6 14 OK
TW4-65 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-70 Chloride 3/17/2020 3/27/2020 10 28 OK
TW4-70 Carbon tetrachloride 3/17/2020 3/20/2020 3 14 OK
TW4-70 Chloroform 3/17/2020 3/20/2020 3 14 OK
TW4-70 Chloromethane 3/17/2020 3/20/2020 3 14 OK
TW4-70 Methylene chloride 3/17/2020 3/20/2020 3 14 OK
TW4-70 Nitrate/Nitrite (as N) 3/17/2020 3/20/2020 3 28 OK
TW4-75 Chloride 3/18/2020 3/27/2020 9 28 OK
TW4-75 Carbon tetrachloride 3/18/2020 3/20/2020 2 14 OK
TW4-75 Chloroform 3/18/2020 3/20/2020 2 14 OK
TW4-75 Chloromethane 3/18/2020 3/20/2020 2 14 OK
TW4-75 Methylene chloride 3/18/2020 3/20/2020 2 14 OK
TW4-75 Nitrate/Nitrite (as N) 3/18/2020 3/20/2020 2 28 OK
Table 1-3 Recipt Temperature Check
Sample Batch Wells in Batch Temperature
MW-04, TW4-01, TW4-02, TW4-04, TW4-ll, MW-26, TW4-19, TW4-20,
2002488 TW4-21, TW4-22, TW4-24, TW4-25,TW4-37, TW4-39, TW4-40, TW4-41, l.8°C
TW 4-60, Trip Blank
TW4-03, TW4-03R ,TW4-05, TW4-06, TW4-07, TW4-08, TW4-09, TW4-09R,
TW4-10, TW4-12, TW4-13, TW4-14, TW4-16, MW-32, TW4-18, TW4-23,
2003454 TW4-26, TW4-27, TW4-28, TW4-29, TW4-30, TW4-31, TW4-32, TW4-33, 0.03°C
TW4-34, TW4-35, TW4-36, TW4-38, TW4-42, TW4-65, TW4-70, TW4-75,
Trip Blank
1-4 Analytical Method Check
Parameter Method Method Used by Lab
SW8260B,
Carbon Tetrachloride SW8260Cor SW8260D
SW8260D
A4500-Cl B or
Chloride A4500-Cl E or E300.0
E300.0
SW8260B,
Chloroform SW8260Cor SW8260D
SW8260D
SW8260B,
Chloromethane SW8260Cor 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 5 R -eporttnfl. 1m1t ec L .. Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
Trip Blank Carbon tetrachloride 1 ug/L u 1 I OK
Trip Blank Chloroform 1 ug/L u 1 I OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
Trip Blank Carbon tetrachloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
MW-04 Chloride 1 mg/L 5 1 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 1 OK
MW-04 Methylene chloride 1 ug/L u 1 1 OK
MW-04 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-01 Chloride 1 mg/L 5 1 OK
TW4-01 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-0J Chloroform 20 ug/L 20 1 OK
TW4-0l Chloromethane 1 ug/L u 1 1 OK
TW4-01 Methylene chloride 1 ug/L u 1 1 OK
TW4-0l Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-02 Chloride 1 mg/L 10 1 OK
TW4-02 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-02 Chloroform 100 ug/L 100 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 10 0.1 OK
TW4-03 Chloride 1 mg/L 5 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 10 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 I 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 5 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 1 1 OK
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 5 1 OK
TW4-05 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-05 Chloroform 1 ug/L 1 1 OK
TW4-05 Chloromethane l ug/L u l 1 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 5 1 OK
TW4-06 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-06 Chloroform 1 ug/L 1 1 OK
TW4-06 Chloromethane 1 ug/L u 1 1 OK
-eporung· Imlt ec I 5 R L' . Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor .Reporting Limit RLCheck
TW4-06 Methylene chloride 1 ug/L u 1 1 OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-07 Chloride 1 mg/L 5 1 OK
TW4-07 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-07 Chloroform 10 ug/L 10 1 OK
TW4-07 Chloromethane 1 ug/L u 1 1 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 5 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 1 0.1 OK
TW4-09 Chloride 1 mg/L 5 1 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 1 1 OK
TW4-09 Methylene chloride 1 ug/L u 1 1 OK
TW4-09 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-09R Chloride 1 mg/L u 1 1 OK
TW4-09R Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-09R Chloroform 1 ug/L 1 1 OK
TW4-09R Chloromethane 1 ug/L u 1 1 OK
TW4-09R Methylene chloride 1 ug/L u 1 1 OK
TW4-09R Nitrate/Nitrite (as N) 0.1 mg/L u 1 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 10 ug/L 10 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-ll Chloride 1 mg/L 10 1 OK
TW4-11 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-ll Chloroform 100 ug/L 100 1 OK
TW4-ll Chloromethane 1 ug/L u 1 1 OK
TW4-11 Methylene chloride 1 ug/L u 1 1 OK
TW4-11 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-12 Chloride 1 mg/L 10 1 OK
TW4-12 Carbon tetrachloride 1 ug/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 1 OK
TW4-12 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-I3 Chloride 1 mg/L 10 1 OK
TW4-13 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-13 Chloroform 1 ug/L u 1 1 OK
TW4-I3 Chloromethane 1 ug/L u 1 1 OK
TW4-I3 Methylene chloride 1 ug/L u 1 1 OK
TW4-I3 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-14 Chloride 1 mg/L 5 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
I 5 R -eportmg 1m1t ec L' . Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
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
MW-26 Chloride 1 mg/L 10 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 u 1 1 OK
MW-26 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
MW-32 Chloride 1 mg/L 5 1 OK
MW-32 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-32 Chloroform 1 ug/L u 1 1 OK
MW-32 Chloromethane 1 ug/L u 1 1 OK
MW-32 Methylene chloride 1 ug/L u 1 1 OK
MW-32 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-18 Chloride 1 mg/L 5 1 OK
TW4-18 Carbon tetrachloride 1 ug/L u 1 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 Chloromethane 1 ug/L 1 1 OK
TW4-19 Methylene chloride 1 ug/L u 1 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.2 mg/L 20 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 500 ug/L 500 1 OK
TW4-20 Chloromethane 1 ug/L 1 1 OK
TW4-20 Methylene chloride 1 ug/L u 1 1 OK
TW4-20 Nitrate/Nitrite (as N) 0.1 mg/L 10 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 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 5 mg/L 50 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) 0.5 mg/L 50 0.1 OK
TW4-23 Chloride 1 mg/L 5 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
I 5 R -eportmg 1m1t ec L" . Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting 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 10 mg/L 100 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 1 ug/L u 1 1 OK
TW4-24 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-25 Chloride 2 mg/L 20 1 OK
TW4-25 Carbon tetrachloride 1 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 1 0.1 OK
TW4-26 Chloride 1 mg/L 5 1 OK
TW4-26 Carbon tetrachloride 1 ug/L u 1 1 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 5 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) 0.2 mg/L 20 0.1 OK
TW4-29 Chloride 1 mg/L 5 1 OK
TW4-29 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-29 Chloroform 10 ug/L 10 1 OK
TW4-29 Chloromethane 1 ug/L u 1 1 OK
TW4-29 Methylene chloride 1 ug/L u 1 1 OK
TW4-29 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-30 Chloride 1 mg/L 5 1 OK
TW4-30 Carbon tetrachloride 1 ug/L u 1 l OK
TW4-30 Chloroform 1 ug/L 1 1 OK
TW4-30 Chloromethane 1 ug/L u 1 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 5 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 1 ug/L u 1 1 OK
TW4-3I Nitrate/Nitrite (as N) 0.1 mg/L 1 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
-eportmg 1mtt ec I 5 R L' . Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-32 Methylene chloride 1 ug/L u 1 1 OK
TW4-32 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-33 Chloride 1 mg/L 5 1 OK
TW4-33 Carbon tetrachloride 1 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 l 1 OK
TW4-33 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-34 Chloride 1 mg/L 5 1 OK
TW4-34 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-34 Chloroform 1 ug/L u 1 1 OK
TW4-34 Chloromethane 1 ug/L u l 1 OK
TW4-34 Methylene chloride l ug/L u l J OK
TW4-34 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-35 Chloride 1 mg/L 5 l OK
TW4-35 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-35 Chloroform l 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 I OK
TW4-35 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-36 Chloride 1 mg/L 10 1 OK
TW4-36 Carbon tetrachloride 1 ug/L u 1 l OK
TW4-36 Chloroform 1 ug/L u 1 J 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 500 ug/L 500 1 OK
TW4-37 Chloromethane 1 ug/L 1 1 OK
TW4-37 Methylene chloride 1 ug/L u 1 I OK
TW4-37 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-38 Chloride 1 mg/L 5 1 OK
TW4-38 Carbon tetrachloride 1 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 10 0.1 OK
TW4-39 Chloride 2 mg/L 20 1 OK
TW4-39 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-39 Chloroform 10 ug/L 10 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 5 1 OK
TW4-40 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-40 Chloroform 10 ug/L 10 l OK
TW4-40 Chloromethane 1 ug/L u 1 1 OK
TW4-40 Methylene chloride l ug/L u 1 I OK
TW4-40 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-41 Chloride 1 mg/L 5 1 OK
TW4-41 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-41 Chloroform 20 ug/L 20 1 OK
TW4-41 Chloromethane 1 ug/L u 1 1 OK
I 5 R -eportmg 1m1t ec L' . Ch k
Lab
I Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-41 Methylene chloride 1 ug/L u l 1 OK
TW4-41 Nitrate/Nitrite ( as N) 0.1 mg/L 10 0.1 OK
TW4-42 Chloride 1 mg/L 5 1 OK
TW4-42 Carbon tetrachloride l ug/L u 1 1 OK
TW4-42 Chloroform 1 ug/L u 1 1 OK
TW4-42 Chloromethane l 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 m_g/L 10 0.1 OK
TW4-60 Chloride 1 m_g/L u 1 1 OK
TW4-60 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-60 Chloroform 1 ug/L u 1 l 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 mg/L 5 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 u_g/L u 1 l 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 l OK
TW4-70 Chloroform 1 ug/L 1 1 OK
TW4-70 Chloromethane 1 ug/L u 1 1 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 1 ug/L u 1 1 OK
TW4-75 Chloroform 1 ug/L u 1 1 OK
TW4-75 Chloromethane 1 ug/L u 1 l OK
TW4-75 Methylene chloride 1 ug/L u 1 1 OK
TW4-75 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
1-6 Trip Blank Evaluation
Lab Report Constituent Result
Carbon tetrachloride ND ug/L
2002488 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
2003454 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
1-7 QA/QC Evaluation for Sample Duplicates
Constituent
Chloride (mg/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/L)
Nitrate+ Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
RPD = Relative Percent Difference
ND = The analyte was not detected
TW4-03
27.7
6.15
ND
ND
ND
ND
TW4-05
48.3
7.1
ND
14.8
ND
ND
MW-32
36.0
ND
ND
ND
ND
ND
TW4-65 %RPD
26.0 6.3
6.38 3.7
ND NC
ND NC
ND NC
ND NC
TW4-70 %RPD
48.4 0.2 J
7.72 8.4
ND NC
14.8 0.0
ND NC
ND NC
TW4-75 %RPD
34.8 3.4
ND NC
ND NC
ND NC
ND NC
ND NC
1-8 QC Control Limits for Analysis and Blanks
Method Blank Detections
All Method Blanks (MB) for the quarter were nondetect.
Matrix Spike % Recoveries
All MS/MSD results 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
Rinsate
Rinsate Result
Sample· Parameter (ug/L) Previous Well Sampled
TW4-03R Chloroform 11.3 NA
TW4-09R Chloroform 12.3 TW4-30 (53.1 ug/L)
NA= This rinsate sample was collected prior to the first use of the pump.
TabJ
Kriged Current Quarter Chloroform Isoconcentration Map
NS = not sampled; ND = not detected
ND 40 =not detected in fourth quarter
MW-24A installed during December, 2019
....._70
TW4-42
¢ND
TW4-40
.. 364
MW-38
"¢-ND
MW-32
e ND
TW4-7
0 746
TWN-1
~NS
PIEZ-1
QNS
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
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 1st QUARTER, 2020 CHLOROFORM (µg/L)
WHITE MESA SITE
CHEM, INC. APPR0\11:0 DATE REFERENCE
H:/718000/may20/chloroform/Uchl0320.srf
FIGURE
J-1
NS = not sampled; ND = not detected
ND 4Q = not detected in fourth quarter
.__ 70
TW4-42
¢ND
TW4-40
... 364
MW-32
.ND
TW4-7
0 746
PIEZ-2
~ 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 1st QUARTER, 2020 CHLOROFORM (µg/L)
WHITE MESA SITE
APPROVED DATE
(detail map)
REFERENCE H:n18000/may20/
chloroform/Uchl0320det.srf
FIGURE
J-2
NS = not sampled; ND = not detected
ND 40 = not detected in fourth quarter
...._ 70
TW4-42
¢ND
TW4-40
... 384
MW-32
.ND
TW4-7
0 746
PIEZ-2
~ 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)
' 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
HYDRO
GEO
CHEM,INC.
1st QUARTER, 2020 CHLOROFORM
GREATER THAN OR EQUAL TO 70 µg/L GRID
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/may20/
chloroform/Uchl0320det.srf
FIGURE
J-3
.TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
Chlorofel311" Carbon e& ometlh&Be M Nitrate Chloriae MW-4 T tr C ide ene
(lllti) €m,Al (ugj) Chlo · (~ (mg/I) (mg/I)
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-Ol 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 <l 6.2 47
10-0ct-07 2300 1.7 <l <l 6.2 45
26-Mar-08 2400 1.7 <l <1 5.8 42
25-Jun-08 2500 1.6 <l <1 6.09 42
10-Sep-08 1800 1.8 <l <1 6.36 35
15-0ct-08 2100 1.7 <1 <l 5.86 45
4-Mar-09 2200 1.5 <l <l 5.7 37
23-Jun-09 1800 1.3 <1 <l 5.2 34
14-Sep-09 2000 1.4 <l <l 5.3 43
Chloroform CarJ>on Chloromedt ne Mdaylene Nitra1e Chloride MW4 Tetr :chleride ( .. g/1~ (ilff'AI,\ (~) CM ~( g/J) (mg/I) (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
l l-Oct-10 1500 1.4 ND ND 4.9 41
23-Feb-1 l 1700 1.5 ND ND 4.6 40
l-Jun-11 1700 1.4 ND ND 4.9 35
17-Aug-l l 1700 1.1 ND ND 4.9 41
16-Nov-ll 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
ll-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
11-0ct-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
1 l-Dec-19 1370 ND ND ND 4.34 45.5
19-Feb-20 1230 ND ND ND 6.22 48.1
0
......
0 0 0
I\) 0 0 0
(ug/L)
(,J 0 0 0
""" 0 0 0
01 0 0 0
en 0 0 0
"'-I 0 0 0
Sep-99 --1-----+----+----+----+--....---+---+~~---1
Mar-00
Sep-00
Mar-01
Sep-01
Mar-02
Sep-02
Mar-03
~:~~~! I I I 71 Sep-04 t • . . .
Mar-05
Sep-OS
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
Sep-19
s: ~ ~ I
() ::r 0 a -0 -st 3
~ c (t)
r/)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ug/1) (ug/1)
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-Ol 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
3 l-Aug-05 2900 <10 <10 <10 9.8 NA
l-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 <l <l 9.4 47
28-Feb-07 1900 1.2 <1 <l 8.9 47
27-Jun-07 1900 1.4 <1 <l 9 45
15-Aug-07 2300 1.3 <l <1 8.4 43
10-0ct-07 2000 1.3 <l <1 7.8 43
26-Mar-08 2000 1.3 <l <l 7.6 39
25-Jun-08 1900 1.1 <l <l 8.68 39
10-Sep-08 1700 1.3 <l <l 8.15 35
15-0ct-08 1700 1.3 <l <l 9.3 41
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ug/1) (ug/1) ' I I
l l-Mar-09 1700 1.1 <l <1 7.5 37
24-Jun-09 1500 1 <l <1 6.9 37
15-Sep-09 1700 <1 <l <l 7.3 36
29-Dec-09 1400 <l <1 <l 6.8 41
3-Mar-10 1300 <l <l <l 7.1 35
15-Jun-JO 1600 1.2 <1 <l 6.8 40
24-Aug-10 1500 <l <1 <l 6.8 35
14-0ct-10 1500 <l <l <l 6.6 40
24-Feb-l l 1300 ND ND ND 6.6 41
l-Jun-11 1200 ND ND ND 7 35
l 8-Aug-11 1300 ND ND ND 6.8 36
29-Nov-l l 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.J
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
3 l-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
Chlo.-ofoi,m C3rbon Chloromethime Metb!lene Nitrate Chloride ·TW4-l (ugffl Tetrachloride (u_g/1) Chloride (mgll) (mg/I) (ug/1) (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
10-Dec-19 1070 ND ND ND 3.91 44.2
19-Feb-20 1190 ND ND ND 4.67 47.5
......
0 0 0 0
28-Jun-99
28-Dec-99
28-Jun-OO
28-Dec-OO
28-Jun-01
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
28-Dec-19
I\)
0 0 0
(ug/L)
(,J
0 0 0
.j:s,.
0 0 0
en 0 0 0
O')
0 0 0
......,
0 0 0
-f ~ .....
0 :::r
0 ~ §-
~ 3
< m c C'D fh
II Carbon Methylene
TW4-2 Chloroform Tetrachloride Chloromethane Chloride Nitrate Chloride
(ug/1) (u2'1) (ug/1) (u2'1) (mg/I) (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-Ol 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 <l <1 7.3 54
27-Jun-07 3000 2.5 <l <1 7.8 50
15-Aug-07 340 2.2 <l <l 7.3 49
10-0ct-07 3200 2.1 <1 <1 6.9 51
26-Mar-08 3300 2.3 <l <1 6.9 48
25-Jun-08 3100 2.2 <l <1 7.44 46
10-Sep-08 2800 2.4 <l <1 7.1 42
15-0ct-08 3200 2.4 <2 <2 7.99 47
ll-Mar-09 3100 2.2 <l <1 6.5 46
24-Jun-09 2800 2 <l <1 6.4 44
15-Sep-09 3000 2 <l <l 6.6 43
29-Dec-09 1600 2 <1 <l 6.4 46
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-2 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul!/1) (ul!/1)
3-Mar-10 2600 2 <1 <1 6.8 42
15-Jun-10 3300 2.6 <l <l 6.7 43
16-Aug-10 3300 2.5 <1 <1 6.6 43
14-0ct-10 3000 2.1 <I <1 6.5 41
24-Feb-l l 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-1 l 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
l 9-0ct-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 1-0ct-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
Chloroform Carbon Ch1oromethane Methylene Nitrate Chloride TW4-2 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul(/1) (ue/l)
IO-Dec-19 934 ND ND ND 3.40 41.5
19-Feb-20 1880 ND ND ND 6.07 42.1
0
.....
0 0 0
I\)
0 0 0
(ug/L)
(,J
0 0 0
.j::,,.
0 0 0
c.n g
0
C1)
0 0 0
-...J 0 0 0
1 O-Nov-99 +-----t-----+--..... =-it-----+----,r+-------t--------i
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
1O-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
10-May-16
10-Nov-16
10-May-17
10-Nov-17
10-May-18
10-Nov-18
10-May-19
~ii>~oO s_g~-a ff-,'< g.w
:::,ac:o-o 0 :::, -, 0 ii>., a. a -· o-c;<1>03. o~m-<_, ..,Qg?...,~
0 -, -· (l) .. -3 (/) (l) ..... :::, Sl) C: (/)
9~ai~gi
C) a.. ... g a.-18.
!!1. li5 i C) a. 0
(l) 0 < -, s· ~ ~ cc 55 "O ~ -· g (l) (/) a.
CJ)
1 O-Nov-19 L--~:::.t:::=,_.,.1-__ --1 ___ ...L __ ____JL_ __ .....L __ ___J
-t ! I I\)
0 :T o "'I 0 0 "'I 3
< m
C (I)
tn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-3 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
I (ue/1) (ue/1)
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-Ol 347 1.85
21-Jun-01 390 2.61
20-Sep-Ol 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 <1 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 <l 3.3 26
14-Jun-06 <1 <1 <1 <l 3.2 26
20-Jul-06 <1 <l 1.6 <l 2.9 26
8-Nov-06 <l <l <1 <l 1.5 23
28-Feb-07 <1 <1 <1 <1 3.1 22
27-Jun-07 <l <l <1 <l 3.3 23
15-Aug-07 <1 <1 <1 <1 3.1 24
10-0ct-07 <l <l <1 <1 2.8 27
26-Mar-08 <1 <1 <1 <l 2.8 21
25-Jun-08 <1 <l <1 <1 2.85 19
10-Sep-08 <l <1 <1 <l 2.66 19
15-0ct-08 <1 <1 <1 <1 2.63 22
4-Mar-09 <l <1 <1 <1 2.5 21
24-Jun-09 <l <l <1 <}. 2.9 20
15-Sep-09 <1 <1 <l <1 2.8 21
16-Dec-09 <1 <1 <l . <l 2.5 22
23-Feb-10 <1 <1 <1 <1 2.8 23
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-3 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul?/I) (ul?/I)
8-Jun-10 <l <l <1 <1 3 24
10-Aug-10 <I <1 <1 <1 3.1 22
5-0ct-10 <l <l <1 <l 3.3 26
15-Feb-l 1 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-l 1 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
11-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
IO-Oct-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
ll-Sep-19 ND ND ND ND 5.12 26.0
12-Dec-19 ND ND ND ND 5.91 28.0
17-Mar-20 ND ND ND ND 6.15 27.7
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
Dec-19
9 0
......
(}1 0 0 0 0 0 0 0
(ug/L)
...... I\) I\)
(}1 0 (}1
0 0 0 0 0 9 0 0 0
w 0 0 0 0
3~ -· ~ r1' I
u, w -· :::, ::::r n DJ tD u, s: c:T DJ tD
""' tD n :::,
::::r -N tD co : ... .... N :::J" 0 DJ 0 :::, w ....
::::r
tD
a.
tD .... tD n .... -· 0 :::,
w .i:,.
(}1 0 0 0 0 0 0 0
i I w
0 :::T
0 a -0 ...
3
~
C C1)
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-4 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) II (ue:/1) (ue:/1)
6-Jun-00 0
2-Sep-00 0
28-Nov-OO 3.9
28-Mar-Ol 2260 1.02
20-Ju n-OI 3100 14.5
20-Sep-01 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
1-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 <1 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 <1 <1 9.2 43
25-Jun-08 2500 1.5 <1 <1 10.8 42
10-Sep-08 2200 1.4 <1 <1 8.83 39
15-0ct-08 2500 2 <2 <2 10.1 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
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-4 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ua/1) (ua/1)
17-Feb-10 1700 1 <1 <l 6.6 48
10-Jun-10 2000 1.2 <l <l 7.6 35
16-Aug-10 2100 1.3 <l <l 7.3 36
l l-Oct-10 1700 1.3 <l <1 7.1 38
23-Feb-1 l 1800 1.4 ND ND 7 41
l-Jun-11 1700 1.2 ND ND 7 35
17-Aug-11 1500 ND ND ND 6.6 40
16-Nov-11 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
11-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
ll-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
ll-Oct-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
I! Cllloroform Carbon Chloromethane MethyJene Nitrate Chloride TW4.;4 (ugll) Tetrachloride t~gtl) Ohloride (mgffl (mg/I) '1 (u2/I) .I (ue.m ~
10-Dec-19 1140 ND ND ND 6.51 40.4
19-Feb-20 1100 ND ND ND 4.58 43.4
"' Cl) :::,
'i >
E a.. 0 -0 a.. ..2 .c
0
o::t I o::t ~
.----,---,---,---,----,----,----,----,-----,-8l-J'BV',J-9 ~
oi-unr-B~
L~-das-ii
-v~-oaa-a
l ~ -Jd'v'-~
60-1nr-9
90-PO-O~
vo-uer-v~
~r--t-+-+--4---1---+---l ~Q-Jd'v'-6 ~
t-----1r------t----1----1-----i----t----+----t----t-86-1nr-vi
0 0 lO
"""
0 0 0
"""
0 0 lO C")
0 0 0 C")
0 0 lO C\I
0 0 0 C\I
(1J6n)
0 0 lO
0 0 0 ..--
0 0 lO
0
Chloroform Carbon Chlorornethane Methylene Nitrate Chloride TW4-S (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2'1) (u2'1)
20-Dec-99 29.5
15-Mar-OO 49.0
2-Sep-00 124
29-Nov-00 255
28-Mar-01 236
20-Jun-01 240
20-Sep-01 240
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
I-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 <l <l 6.7 54
8-Nov-06 47.1 <1 <1 <1 2.9 55
28-Feb-07 33.0 <1 <1 <1 7.8 57
27-Jun-07 26.0 <1 <1 <1 7 45
15-Aug-07 9.2 <1 <l <1 7.7 38
10-0ct-07 9.4 <1 <I <l 8.2 39
26-Mar-08 11.0 <1 <l <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 <1 <1 <1 8.3 48
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-S (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
22-Dec-09 8.5 <1 <1 <1 7.5 41
25-Feb-10 13.0 <l <l <l 6.8 43
9-Jun-10 12.0 <1 <1 <1 7.1 28
1 l-Aug-10 12.0 <1 <1 <1 7 38
13-0ct-10 11.0 <l <l <1 7.2 41
22-Feb-11 10.0 ND ND ND 7 34
26-May-1 l 9.0 ND ND ND 7.2 35
17-Aug-11 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
ll-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.l
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-1 5 13.8 ND ND ND 9.32 45.1
10-Jun-l 5 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
l 7-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-l 7 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
Ohloroform Cal'bon Chlor~eti.ane MethJlene Nitrate 0.hloride TW4-5 Tetrachlomde Chloride (bg/1) <uwO (ug/1) (u2'H {mgll) (mg/l)
11-Sep-19 14.6 ND ND ND 7.02 46.1
14-Dec-19 15.7 ND ND ND 6.97 53.1
17-Mar-20 14.8 ND ND ND 7.1 48.3
0 c.n 0
......
0 0
(ug/L)
...... c.n 0
I\) 0 0
I\) c.n 0
w 0 0
w c.n 0
24-Jul-98 +---------------;------+-----+-----1-------1
19-Apr-01
14-Jan-04
10-0ct-061 I I / I I I I I
06-Jul-09 1 ~ I I I I I I I I
01-Apr-12 1 1 /J I I I I I I
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 _._ ___ .__ __ ___. ___ __._ ___ ___._ ___ _,_ ___ _._ __ ____.
-t :e ~ I U1
0 ::::r
0 ...
0 -0 ...
3
< !. C CD u,
Cbloroto11m C Pb Chl:0110 fJhnne Hetibyli te-' ll!lte CM ide TW4~6 (ug/1) 'I aehl1GPidt (11-Wm<ll ~ {mgtl~ tW!IU {Mvl&i
6-Jun-00 0
2-Sep-00 0
28-Nov-00 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 <l <1 <1 1 30
20-Jul-06 11.0 <l <1 <1 0.6 37
8-Nov-06 42.8 <1 <l <1 1.4 65
28-Feb-07 46.0 <l <1 <l 1.5 32
27-Jun-07 11.0 <l <l <1 0.6 38
15-Aug-07 18.0 <1 <1 <l 0.7 36
10-0ct-07 18.0 <1 <l <1 0.8 38
26-Mar-08 52.0 <1 <1 <1 1.1 33
25-Jun-08 24.0 <1 <1 <1 0.9 35
10-Sep-08 39.0 <l <1 <1 1.14 35
15-0ct-08 37.0 <l <1 <l 1.01 33
11-Mar-09 81.0 <1 <1 <1 2.2 35
24-Jun-09 120 <1 <1 <1 2.7 37
15-Sep-09 280 <l <1 <l 5.0 37
22-Dec-09 250 <1 <l <l 6.1 41
25-Feb-10 1000 <1 <1 <1 1.6 45
IO-Jun-IO 590 <1 <l <l 2.5 33
12-Aug-10 630 <1 <1 <1 3.9 31
13-0ct-10 420 <1 <l <1 4.3 41
l.j-.Feb-11 47 NU NU ND 0.7 40
Ca bo Mie-_: Chloroform Chlo~ teth te Chloride TW4~6 (!Ug/,IJ) Tetnwh~de (~ -httiae tfflfdl, (mgf.l Jt11ml9 (.nail) ' :LIJ-May-11 lU NU J'IU ND 0.3 42
17-Aug-l l 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
ll-Sep-12 6.9 ND ND ND 0.1 21
3-0 cl-12 9.0 ND ND ND 0.2 41
13-Peb-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-1 4 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-1 4 723 ND ND ND 6.92 41.1
18-Mar-15 1180 ND ND ND 5.25 41.2
l 1-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
26-0cl-16 301 ND ND ND 3.74 46.1
16-Mar-17 288 ND ND ND 3.15 42.1
21-Juil-17 239 ND ND ND 2.42 42.6
3-Aug-17 129 ND ND ND 1.71 42.9
ll-Oct-17 121 ND ND ND 1.71 37.6
20-Mar-1 8 159 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
14-Dec-19 7.40 ND ND ND 0.244 45.7
17-Mar-20 6.93 ND ND ND 0.222 43.2
u,
Cl) :::,
cu >
E ...
0 -0 ...
.2 .c
0
U)
I ~
== I-
0 0 -.;f" ,....
/
oc-unr-~
L~-das-
...----t --i -._-t---+-~~~--J vkoaa-c
0 0 C\J ,....
0 0 0 ,....
0 g 0 0 <D
(1J6n)
0 0 -.;f"
0 0 C\J
0
G ~-JdV-~
60-1nr-9
90-lOQ-~
vo-uer-~
0 0 C\J I
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-7 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2'1.) (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-OI 1100 2.65
20-Sep-01 1200 3.38
8-Nov-OJ 1100 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 <l <1 4.6 49
28-Feb-07 1800 1.1 <1 <l 5 47
27-Jun-07 2600 1.5 <l <l 5. 1 45
14-Aug-07 2300 1.4 <1 <1 4.7 44
10-0ct-07 1900 1.2 <1 <1 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
l l -Mar-09 1800 1.2 <1 <1 3.7 35
24-Jun-09 1400 <1 <1 <1 3.8 37
15-Sep-09 1500 1.0 <1 <l 4.1 37
I Carbon Methylene Chloroform Chloromethane Nitrate Chloride TW4-7 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) I (uwl) (uwl)
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 <1 <1 3.9 36
13-0ct-10 1100 1.1 <1 <l 4 38
23-Feb-l 1 1300 ND ND ND 3.60 45
1-Jun-11 1200 ND ND ND 4.00 35
18-Aug-1 l 1200 ND ND ND 4.10 37
29-Nov-l L 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
13-Sep-l.2 870 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-l 3 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
l l-Jun-15 950 ND ND ND 2.62 42.1
IO-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
ll-Oct-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
Chlorofomi Carbon Chloromethane Me~ylene Nitrate Chloride TW4·7 (ugtl) Tetrachloride (ug/1~ Chlorlde ('mg/J) (mgtl~
I (u2/I') (W?/1)
12-Sep-19 801 ND ND ND 3.76 39.7
18-Dec-19 546 ND ND ND 3.11 47.2
18-Mar-20 746 ND ND ND 3.75 42.1
0
...
0 0 0
I\) 0 0 0
(ug/L)
~ 0 0
.i,.. 0 0 0
u,
0 0 0
0) 0 0 0
24-Jul-98 -t-----+----+------+--------+----+------4
19-Apr-01
14-Jan-04
10-0ct-06 I I • ,.-I I I
6-Jul-09 -1 I ~ I I I I
1-Apr-12 i /T I I I I I
!7-Dec-14
!2-Sep-17
18-Jun-20
15-Mar-23 ...._ ___ _._ ____ ...,__ ___ __,_ ____ ...J.._ ____ 1-___ _1
-t :e .,:::..
I .....,
0 :::r
0 ..
0 -0 ..
3
< m
C CD tn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-8 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2'1.) (u2'1.)
29-Nov-99 0
15-Mar-OO 21.8
2-Sep-00 102
29-Nov-00 107 ND
26-Mar-01 116 ND
20-Jun-Ol 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 <l 1.7 <1 <0.1 NA
30-Nov-05 <l <l <l <1 <0.1 NA
9-Mar-06 1.3 <1 2.1 <l 0.3 39
14-Jun-06 1.0 <l 1.8 <l <0.1 37
20-Jul-06 <1 <l <l <1 0.1 39
8-Nov-06 <1 <l <l <l <0.1 40
28-Feb-07 2.5 <1 <l <1 0.7 39
27-Jun-07 2.5 <l <1 <1 0.2 42
15-Aug-07 1.5 <l <1 <1 <0.1 42
10-0ct-07 3.5 <1 <l <l 0.5 43
26-Mar-08 <1 <1 <1 <l 0.1 46
25-Jun-08 <1 <l <l <l <0.05 45
10-Sep-08 <1 <l <l <1 <0.05 39
15-0ct-08 <1 <l <1 <l <0.05 44
4-Mar-09 <1 <l <l <l <0.1 42
24-Jun-09 <1 <l <1 <l <0.1 44
15-Sep-09 <1 <1 <l <l <1 44
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-8 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
17-Dec-09 <1 <1 <1 <1 <0.1 51
24-Feb-10 <1 <l <1 <1 <0.1 57
9-Jun-10 <1 <1 <l <1 <0.1 42
l l-Aug-10 <1 <l <l <1 <0.1 45
5-0ct-10 <1 <1 <1 <1 <0.1 46
16-Feb-11 ND ND ND ND ND 52
25-May-11 ND ND ND ND 0.1 45
16-Aug-l 1 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-17 359 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
Chloroform Carbon Chloromethane Metby,lene Nitrate Chloride ' TW4--8 Tetrachloride Chloride (ug/1) (ue/0 (ug/1) (:ue/1) (mg/I) (m,g/l),
19-Jun-19 96.0 ND ND ND 1.10 56.5
12-Sep-19 75.4 ND ND ND 0.999 52.0
18-Dec-19 84.4 ND ND ND 1.21 60.l
18-Mar-20 55.0 ND ND ND 1.04 53.8
0
I\)
0 0
.j::.
0 0
(ug/L)
O> g ex,
0 0
......
0 0 0
......
I\)
0 0
24-Jul-98 -1------+-----+------------1------+--------;
19-Apr-01
14-Jan-04
10-0ct-06 • I I I I I I I
6-Jul-09 t I I I I I I I
1-Apr-12 l \ I I I I I I
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 _.__ ___ __._ ____ _.__ ___ __,_ ____ ..__ ___ _._ ___ __.
-I ! I a,
0 J
0 ""I 0 -0 ""I 3
< !. C CD en
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-9 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (uwl) (uwl)
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
l 7-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 <l 2.9 <1 1.3 NA
l-Dec-05 <l <l <l <1 1.3 NA
9-Mar-06 <1 <l 2.6 <1 1.5 38 ' .
14-Jun-06 <l <l 2.7 <l 1.5 39
20-Jul-06 <l <1 <l <1 0.9 41
8-Nov-06 <1 <1 <l <I 0.7 44
28-Feb-07 <l <1 <l <l 0.6 44
27-Jun-07 21 <1 <1 <1 1.3 42
15-Aug-07 9.5 <1 <l <1 1.8 38
10-0ct-07 8.7 <1 <l <1 2 40
26-Mar-08 1.3 <l <l <1 2.1 35
25-Jun-08 1.0 <1 <1 <1 2.3 35
10-Sep-08 <l <1 <1 <1 2.79 28
15-0ct-08 <1 <1 <1 <1 1.99 58
4-Mar-09 <1 <1 <1 <1 2.5 30
24-Jun-09 <1 <1 <1 <1 2.3 30
15-Sep-09 <1 <l <l <1 2.5 30
Chloroform Carbon Chloromethane Methylene Nitrate Chloride
I TW4-9 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
17-Dec-09 <l <I <l <1 1.7 37
23-Feb-10 <1 <1 <1 <1 1.7 47
9-Jun-10 <1 <l <1 <l 1.5 33
l l-Aug-10 <I <l <1 <l 1.2 40
6-0ct-10 <l <l <1 <l 1.8 34
17-Feb-ll ND ND ND ND 1.3 41
25-May-l l ND ND ND ND 3.4 38
16-Aug-l l 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-1 2 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
28-0 ct-1 5 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.l
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-17 132 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
Chloroform ,Carlion CJi)oromethane Metby,Jene Nitrate Chloride 'FW4-9 Tetrachloride Chloride (ug/1) (:i12'1} (ug!.I) (U2'./l) (mg/lJ {mg/I)
11-Sep-19 66.0 ND ND ND 0.904 35.2
18-Dec-19 54.8 ND ND ND 0.744 40.1
18-Mar-20 48.9 ND ND ND 0.855 37.7
0
I\)
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0 OJ 0
(ug/L)
0 0 I\) 0
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24-Jul-98 -1-----1-----1---------------+---------+----1
19-Apr-01
14-Jan-04
10-0ct-06 ' .
6-Jul-09 t \ I I I I I I I
1-Apr-12 I I \ I I I I I I
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 _.__ __ ....__ __ ....__ __ _._ __ __,_ __ __,_ __ ~--~--~--__,
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-10 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
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
I-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 <1 <1 1 7.6 62
27-Jun-07 350 <1 <l 1 5.1 54
15-Aug-07 660 <1 <1 1 7.3 59
10-0ct-07 470 <1 <l 1 6.7 59
26-Mar-08 620 <1 <I 1 7.3 55
25-Jun-08 720 <1 <l 1 9.91 58
10-Sep-08 680 <l <l 1 9.23 51
15-0ct-08 1200 <2 <2 2 10.5 61
11-Mar-09 1100 <1 <1 1 11.6 64
24-Jun-09 1200 <l <1 1 9.8 62
15-Sep-09 910 <l <1 1 8.1 51
22-Dec-09 300 <l <l <l 3.5 51
3-Mar-10 460 <l <1 <l 5 49
10-Jun-10 220 <l <1 <l 1.6 42
12-Aug-10 100 <l <1 <l 0.8 38
13-0ct-10 1100 <l <1 <l 11 52
23-Feb-11 620 ND ND ND 9 62
1-Jun-11 280 ND ND ND 3.3 42
[I Cld ,~rm· Carben Chi Dmdb ·---Nitmte CIIlorite TWtl-18. €ugai) T F li): id'e (ug(AJ) ChJe,:,i (~ (nttJll)
11 ,€tt;d }: ·(imzrll~·
17-Aug-1 1 180 ND ND ND 1.9 41
16-Nov-1 1 110 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 49.1
13-Jun-13 486 ND ND ND 5.6 51.5
I 2-Sep-13 1160 ND ND ND 13 .0 67.9
14-Nov-13 1380 ND ND ND 16.0 70.9
5-Feb-l4 1260 5.16 ND ND 16.8 73
23-May-14 lllO ND ND ND 13 .9 77.3 11
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
1 O-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
27-0 ct-1 6 1290 ND ND ND 14.8 84.4
2 1-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
l 1-0ct-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
18-Dec-19 768 ND ND ND 6.89 62.0
18-Mar-20 798 ND ND ND 7.83 53.5
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Chloroform Carbon Chlorometbane Methylene Nitrate Chloride TW4-11 Tetrachloride (ug/1) (ut!/1) (ug/1) Chloride (ug/1) (mg/I) (mg/I)
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
1-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 <1 1.6 10.1 54
27-Jun-07 3800 1.6 <1 1.1 10.6 53
15-Aug-07 4500 1.7 <] 1.1 10.2 53
10-0ct-07 4400 1.6 <1 1.2 9.8 53
26-Mar-08 340 <1 . <1 <1 7.7 63
25-Jun-08 640 <1 <l <1 7.28 46
10-Sep-08 900 <1 <1 <1 7.93 42
15-0ct-08 1000 <2 <2 <2 9.46 47
11-Mar-09 1100 <1 <1 <1 7.3 49
24-Jun-09 980 <1 <1 <1 6.8 44
15-Sep-09 1000 <1 <1 <1 7 49
29-Dec-09 860 <1 <1 <1 6.6 46
3-Mar-10 820 <1 <1 <] 6.8 42
10-Jun-10 820 <1 <1 <l 6.9 40
12-Aug-10 800 <1 <1 <1 6.7 43
13-0ct-10 720 <1 <1 <1 6.4 49
23-Feb-11 1000 ND ND ND 6.5 46
l-Jun-11 930 ND ND ND 7.3 49
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-11 Tetrachloride (ug/1) (ul?/1) (ug/1) Chloride ( ug/1) (mg/I) (mg/I)
17-Aug-ll 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-l 7 3370 1.83 ND ND 7.92 51.4
26-Jul-17 3290 1.81 ND ND 7.78 51.0
11-0ct-l 7 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
10-Dec-19 3250 ND ND ND 7.14 49.0
19-Feb-20 2990 ND ND ND 7.07 51.9
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Carbon I Methylene Chloroform Chloromethane Nitrate Chloride TW4-12 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (U21)) (u2'1)
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
l 7-Sep-04 0 1.24
17-Nov-04 0 1.5
16-Mar-05 0 1.4
25-May-05 <l NA NA NA 1.6 NA
31-Aug-05 <1 <1 5.8 <1 1.5 NA
l-Dec-05 <1 <1 1.9 <2 1.4 NA
9-Mar-06 <l <1 2.6 <l 1.3 19
14-Jun-06 <1 <l 1.4 <l 1.4 16
20-Jul-06 <1 <1 <1 <1 1.4 16
8-Nov-06 <1 <l <1 <l 1.4 16
28-Feb-07 <l <l <1 <1 1.5 16
27-Jun-07 <l <l <l <1 1,5 18
15-Aug-07 <l <1 <l <l 1.4 29
10-0ct-07 <1 <1 <l <l 1.4 16
26-Mar-08 <1 <1 <l <1 1.6 16
25-Jun-08 <1 <l <l <1 2.69 19
10-Sep-08 <l <1 <l <1 2.65 18
15-0ct-08 <l <1 <1 <1 2.47 22
4-Mar-09 <1 <1 <1 <1 2.4 23
24-Jun-09 <l <l <l <1 3.8 22
15-Sep-09 <l <1 <l <l 5.1 22
16-Dec-09 <l <1 <1 <l 3.6 23
23-Feb-10 <l <1 <l <l 4 22
8-Jun-10 <l <l <l <l 11 29
10-Aug-10 <l <l <l <1 9 35
5-0ct-10 <1 <1 <1 <I 8 31
15-Feb-l 1 ND ND ND ND 6.5 31
25-May-l 1 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
I CMhe Methylene
TW4-12 I Ohh>l'ot61'ffl etracbtoJti• Chlo eflbane 1 Cblnrfde Nitrate Oderhie'
(i.1wJ). I {Ufd(') (~) I (~~'
(mg/I) (mw)))
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
11-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-l9 ND ND ND ND 10.1 50.8
13-Jun-19 ND ND ND ND 8.31 55.3
LJ-Sep-1 9 ND ND ND ND 8.88 52.6
14-Dec-19 ND ND ND ND 8.04 58.0
17-Mar-20 ND ND ND ND 6.39 53.0
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Chloroform Carbon Chlorometbane Methylene Nitrate Chloride TW4-13 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
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 <I <I 3.1 <1 4.60 NA
I-Dec-05 <l <I <l <I 4.30 NA
9-Mar-06 <l <I 1.7 <1 4.20 o7.0
14-Jun-06 <l <1 1.4 <l 4.90 66.0
20-Jul-06 <1 <I <I <I 4.30 65 .0
8-Nov-06 <1 <1 <I <1 0.80 33.0
28-Feb-07 <1 <1 <I <l 4.00 59.0
27-Jun-07 <1 <I <1 <l 4.60 59.0
15-Aug-07 <1 <l <1 <l 4.40 58.0
I 0-0ct-07 <1 <l <1 <l 4.10 58.0
26-Mar-08 <l <I <I <l 3.80 54.0
25-Jun-08 <1 <I <I <I 4.24 58.0
10-Sep-08 <1 <I <I <l 4.26 50.0
15-0ct-08 <1 <l <l <1 4.63 58.0
4-Mar-09 <1 <1 <l <l 3.70 58.0
24-Jun-09 <1 <l <l <l 1.20 57.0
15-Sep-09 <1 <1 <1 <1 4.70 63.0
16-Dec-09 <1 <1 <1 <1 4.10 60.0
24-Feb-10 <1 <1 <l <l 4.30 53.0
8-Jun-10 <I <I <1 <l 5.20 52.0
10-Aug-10 <l <1 <l <1 5.ou 55 .0
5-0ct-10 <l <l <l <l 5.80 55.0
15-Feb-l 1 ND ND ND ND 5.50 60.0
25-May-ll ND ND ND ND 5.40 56.0
16-Aug-11 ND ND ND ND 5.20 60.0
15-Nov-ll 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
CJdorofo m CaJ!\h-cm CI\J,eromethruie eih Jene N. ife Cbleride TW4-i3 I 'o (11glij Tetrachloride (u;lt) Clde.ride mgt't) (mt,l)
r fuel!' I tu@Jl),
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
23-0 ct-1 4 ND ND ND ND 6.28 66.1
l 1-Mar-1 5 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
14-Dec-19 ND ND ND ND 5.17 68.7
17-Mar-20 ND ND ND ND 5.50 63.9
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
Dec-1 9
Mar-20
0
0
•• ••
' ' •• .. ..
0
•• 0
0
•• ••
l~
0
0
0
0
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11 Carbon Methylene
II TW4-14 Chloroform Tetrachloride Chloromethane Chloride Nitrate Chloride
(ug/1) (owl) (ug/1) (uwl) (mg/I) (mg/I)
8-Nov-06 <I <l <l <1 2.40 37.0
28-Feb-07 <1 <l <1 <1 2.30 38.0
27-Jun-07 <1 <1 <1 <1 1.40 38.0
15-Aug-07 <1 <l <l <l 1.10 36.0
10-0ct-07 <1 <1 <1 <1 0.80 36.0
26-Mar-08 <1 <1 <1 <1 0.04 57.0
25-Jun-08 <1 <1 <l <1 1.56 35.0
10-Sep-08 <l <1 <l <1 1.34 34.0
15-0ct-08 <l <1 <I <l 0.76 40.0
4-Mar-09 <1 <1 <l <l 1.60 35.0
24-Jun-09 <1 <1 <1 <1 1.40 36.0
15-Sep-09 <1 <l <l <l 1.50 38.0
16-Dec-09 <l <1 <l <l 1.40 34.0
3-Mar-10 <l <l <1 <1 2.50 33.0
8-Jun-10 <1 <1 <1 <l 2.90 49.0
10-Aug-10 <1 <1 <l <l 2.80 35.0
6-0ct-10 <l <l <l <l 2.90 29.0
15-Feb-ll ND ND ND ND 1.80 25.0
16-Aug-ll 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 s:oo ND ND 1.80 2.88 42.4
Clrlmrof,erm Oarbe.n dhl9;emeth:ane Mellbylene Nitrate Chh)mle 1, TW4•14 TetJtaddmdi Odeliide :1 (lfWI) (~ (mg/I) ~) {uall) (ud}
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-l 7 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
11-Sep-19 6.08 ND ND ND 4.77 45.4
14-Dec-19 3.83 ND ND ND 4.76 49.4
17-Mar-20 2.98 ND ND ND 6.17 48.4
tn G) ::::,
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ci
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0 0
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~hloroform Carija CM ometh bylene Nitrate ride MW-26 Trfflacldmde C:M 'de '
(ug/1) (,a•· (qg{li) {u;lll<I(), (mg/{) {~)
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
1-Dec-05 1000 <50 <50 <50 0.3 NA
9-Mar-06 llOO <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 <l 2.8 0.3 54
28-Feb-07 570 <l <l 5.5 0.5 56
27-Jun-07 300 <l <1 13 0.4 49
15-Aug-07 1400 <l <1 36 1 57
10-0ct-07 2000 <1 <l 14 0.6 57
26-Mar-08 930 <l <l 40 0.1 49
25-Jun-08 1300 <l <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 llOO <1 <1 40 2.3 60
17-Feb-10 780 <1 <l 19 0.2 57
9-Jun-10 1900 <1 <1 28 1.1 58
16-Aug-10 2200 <l <1 21 0.6 49
11-0ct-10 970 <1 <l 6.5 0.7 65
23-Feb-11 450 ND ND 3.6 0.5 57
Ca11ban M -~
Olil{l)r,.ofo!(JD· adol"omdhaa-e "'"' ilrate OMoride MW-26 (ng?!I) Tew •ldo 1t e (agll) 8:A !,1 (uigll) (~ /I 1fuwll ''(Qt!Affi
31-May-11 1800 ND ND 1.3 0.4 88
17-Aug-11 720 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
l l-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
19-0 ct-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-17 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-1 8 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
10-Dec-1 9 f390 ND ND 1.78 0.977 83.2
19-Feb-20 1100 ND ND ND 1.170 88.9
u,
Cl) :::, cu >
E II.,
0 -0 II.,
.2 .c 0
CD
C\I I
== :il5
0 0 LO '<:I"
0 0 0 '<:I"
0 0 LO C')
0 0 0 C')
0 0 LO C\I
(1J6n)
0 0 0 C\I
0 0 LO
0 0 0
0 0 LO
oi-unr-8~
L~-das-ii
v~-oaa-a
G ~ -Jdy-~
60-1nr-9
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0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
II (u2'D (u2'D
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 <1 3.2 43 <0.1 NA
l-Dec-05 14 <2.5 2.6 5.9 1.4 NA
9-Mar-06 39 <I 1.1 21 3 60
14-Jun-06 13 <l 2.4 8.9 1.9 55
20-Jul-06 5.2 <1 <] 2.7 2.7 60
8-Nov-06 13.6 <1 <I 9.2 5.6 62
28-Feb-07 8.7 <1 <I 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 <I <1 4.4 69
26-Mar-08 11 <1 <] 26 ND 52
25-Jun-08 <l <1 <l <1 1.46 58
10-Sep-08 10 <1 <1 14 10.5 71
15-0ct-08 3.9 <I <1 6.6 9.82 89
4-Mar-09 <1 <1 <1 <1 9.6 78
24-Jun-09 <1 <l <l <l 8.9 76
15-Sep-09 <I <l <I <1 8.8 79
17-Dec-09 <1 <I <l <1 5.2 76
24-Feb-10 <1 <I <1 <1 4.2 77
9-Jun-10 2.1 <l <1 <1 4.7 64
24-Aug-10 4.3 <l <I <1 4.6 72
6-0ct-10 3 <1 <l <1 3.3 72
22-Feb-ll 15 ND ND ND 7 86
26-May-Il 16 ND ND ND 5 81
17-Aug-ll 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
Ii Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 Tetrachloride Chloride (ug/1) (u2'1) (ug/1) (u2'1) (mg/I) (mg/I)
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.l
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
ll-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
18-Dec-19 94.3 ND ND ND 3.37 88.6
18-Mar-20 113.0 ND ND ND 3.91 76.2
t/J
G) ::, ca >
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0 0 <O
0 0 LO
0 0
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(1J6n)
0 0 C\J
0 0 .... 0
oc-unr-a~
L~-das-cc
v~-oaa-LG
U-JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride MW-32 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (02/1) (owl)
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 <1 <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 <l <1 <1 <0.1 32
27-Jun-07 <1 <1 <1 <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 <l <1 <l <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-l 1 ND ND ND ND ND 31
16-Aug-11 ND ND ND ND ND 33
6-Dec-11 ND ND ND ND ND 32
Cbfer0. orm C rbn jzJdQr th ne M.teth I n
' ~-Cklc»i MW-32 ~eUlaffl101i6' Clderidl ,uwA, f:.md'II (11~ ,(.11•, i (mgll~ miJI,
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
l 1-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
18-Dec-19 ND ND ND ND ND 36.3
18-Mar-20 ND ND ND ND ND 36.0
(1J6n)
CX)
ci
<D
ci
C\J
ci
oi-unr-s~ ' . •• ~
0
0
• • ' . ' .
~ L~-das-cc
' . 0
•
•
~ • 0 v~-oaa-a
0
0
•
0
0
0
H • • 0
0
0 60-1nr-9
0
0
0
•l 90-PO-O~ 0
0 ..
• •
•• .. vo-uer-v~ ·~ 0
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-18 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (uwl) (uwl)
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
3 l-Aug-05 39 <1 2.8 <l 13.3 NA
l-Dec-05 14 <1 1.1 <l 7 .3 NA
9-Mar-06 12.0 <l 1.1 <l 5.9 5.9
14-Jun-06 12.0 <1 1.6 <l 4.7 35
20-Jul-06 10.8 <1 2.7 <] 6.1 35
8-Nov-06 139 <l <1 <1 8.7 34
28-Feb-07 9.2 <1 <1 <l 5.1 30
27-Jun-07 8.0 <l <1 <I 4.9 28
15-Aug-07 8.9 <l <l <l 5 32
10-0ct-07 7.4 <I <l <l 4.4 27
26-Mar-08 6.4 <l <1 <l 0.7 23
25-Jun-08 5.7 <I <I <I 4.55 23
1 O-Sep-08 8.0 <1 <1 <l 4.68 26
15-0ct-08 9.4 <1 <I <I 5,15 30
4-Mar-09 11.0 <1 <l <l 5.2 29
24-Jun-09 16.0 <I <1 <l 6.2 30
15-Sep-09 13 .0 <l <l <1 5.9 26
22-Dec-09 8.2 <1 <l <1 5.4 30
24-Feb-10 69.0 <l <l <l 5.1 41
9-Jun-10 29.0 <l <l <l 9 35
12-Aug-10 29.0 <l <I <I 9 37
13-0ct-10 30.0 <l <I <I 10 50
22-Feb-l 1 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
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-18 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (m!/1) (ue/1)
13-Jun-12 24.0 ND ND ND 6.6 30
11-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-1 3 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
l l-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-l 7 63.8 ND ND ND 4.5 41.6
3-Aug-17 62.8 ND ND ND 4.24 40.4
10-0ct-l 7 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
ll-Sep-1 9 56.2 ND ND ND 3.25 36.8
18-Dec-19 62.0 ND ND ND 3.02 42.7
18-Mar-20 57.0 ND ND ND 3.71 39.4
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Carbon Chloromethane Methylene Nitrate Chloride TW4-19 Tetrachloride Chloride (ug/1) (ue/1) (ug/1) (ue/1) (mg/I) (mg/I)
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 <I <I 4 133
27-Jun-07 1800 2.3
15-Aug-07 1100 1.9 <l <I 4.1 129
IO-Oct-07 1100 1.9 <l <l 4 132
26-Mar-08 1800 2.9 <l <l 2.2 131
25-Jun-08 1000 1 <I <l 2.81 128
10-Sep-08 3600 8.6 <l <l 36.2 113
15-0ct-08 4200 12 <1 <l 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <l 2.4 132
15-Sep-09 6600 15 <1 <l 0.1 43
14-Dec-09 4700 16 <l <l 26.7 124
17-Feb-10 940 1.3 <1 <I 2 144
9-Jun-10 1800 4.2 <1 <l 4.4 132
16-Aug-10 2000 4.9 <1 <l 5.9 142
II Carbon Methylene
II TW4-19 Chloroform Tetrachloride Chloromethane Chloride Nitrate Chloride
(ug/1) (ue/1) (ug/1) (ue/1) (mg/I) (mg/I)
ll-Oct-10 1200 1.3 <1 <I 2.7 146
17-Feb-11 3400 17 ND ND 17 135
7-Jun-11 4000 8.3 ND ND 12 148
17-Aug-11 910 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
ll-Feb-13 4210 5.15 ND ND 7.99 164
5-Jun-13 2070 5.15 ND ND 2.95 I48
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
1 l-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-l 7 8840 13.0 ND ND 1.12 218
1 l-Oct-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
10-Dec-19 551 ND ND ND 0.535 147
19-Feb-20 8720 13.7 5.41 ND 10.100 205
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'I Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-20 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u211) (u2'1)
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 <l 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 <l 1.2 7.96 191
10-Sep-08 21000 15 <l 3.7 4.44 156
15-0ct-08 NA NA NA NA 5.51 166
4-Mar-09 8200 5.7 <l 5.2 5.1 164
24-Jun-09 6800 4.9 <2 4.2 2.9 154
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 <l 3.2 2 179
14-Jun-10 18000 11 <l 3.7 5.6 200
16-Aug-10 15000 12 <1 2.2 5.3 196
11-0ct-10 24000 20 <l 5.5 4.6 203
23-Feb-l l 31000 27 ND 19 4.4 220
l-Jun-11 8100 10 ND 2.1 4.8 177
17-Aug-ll 6800 7.3 ND 3.1 6.5 207
16-Nov-ll 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
ll-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
I l-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
Chloroform Carbon Chlmromethane Methylene Nitrate Chloride TW4-20 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) ' (uwl)
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
19-0 ct-15 17000 14.5 10.8 1 6.23 293
9-Mar-J6 21600 20.2 4.09 1.16 10.3 293
23-May-16 33700 40.6 ND ND 11.2 318
25-Ju l-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-1 7 18100 23.4 ND ND 9.76 281
26-Jul-17 27600 25.0 ND ND 10.8 292
12-0 ct-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-J 8 10500 9.85 4.98 ND 8.14 282
28-Nov-18 9500 8.32 15.6 ND 9.72 295
8-Mar-1 9 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
10-Dec-19 8790 5.92 2.67 ND 9.75 307
19-Feb-20 14300 8.60 10.7 ND 9.81 310
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-21 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul?/l) (ul?/l)
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 <I <1 8.7 296
28-Feb-07 160 1.8 <l <1 8.7 306
27-Jun-07 300 5.8 <l <1 8.6 327
15-Aug-07 140 <l <l <1 8.6 300
10-0ct-07 120 <l <l <l 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 <l 7.57 244
15-0ct-08 170 2 <1 <2 8.00 284
l l-Mar-09 180 <l <l <1 8.3 279
24-Jun-09 200 <l <l <1 8.1 291
15-Sep-09 140 <l <1 <1 9.2 281
22-Dec-09 160 <l <1 <1 8.4 256
25-Feb-10 170 <1 <1 <1 8.4 228
10-Jun-10 210 1.2 <l <1 12 266
12-Aug-10 390 9.2 <l <1 14 278
13-0ct-10 200 1.2 <l <1 7 210
22-Feb-11 230 1.2 ND ND 9 303
28-Jun-l 1 290 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
II Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-21 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) ,, (owl) (02'1)
12-Mar-15 292 1.75 ND ND 10.9 255
8-Jun-15 366 1.92 ND ND 13.1 494
31-Aug-1 5 281 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
J 2-0ct-16 434 ND ND ND I 1.4 301
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
l l-Oct-17 466 ND ND ND 16.9 378
12-Mar-J 8 421 ND ND ND 15.8 447
8-Jun-l 8 532 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-1 9 596 ND ND ND 14.7 478
JO-Dec-19 794 ND ND ND 5.73 339
19-Feb-20 844 ND 2.58 ND 8.93 446
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Ii Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-22 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
Ill (uwl) (uwl)
25-May-05 340 NA NA NA 18.2 NA
31-Aug-05 290 <5 <5 <5 15.7 NA
I-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 <l 1.6 <l 15.9 236
28-Feb-07 440 <1 <l <1 20.9 347
27-Jun-07 740 <l <1 <l 19.3 273
15-Aug-07 530 <I <l <l 19.3 259
10-0ct-07 440 <1 <1 <l 18.8 238
26-Mar-08 1400 <I <1 <l 39.1 519
25-Jun-08 1200 <1 <1 <1 41.9 271
10-Sep-08 6300 1.3 <l <l 38.7 524
15-0ct-08 630 <2 <2 <2 36.3 539
l l-Mar-09 390 <l <l <1 20:7 177
24-Jun-09 730 <1 <1 <1 20.6 177
15-Sep-09 2300 <I <1 <1 40.3 391
29-Dec-09 380 <l <1 <1 17.8 175
3-Mar-10 2200 <I <1 <1 36.6 427
IS-Jun-IO 540 <1 <1 <I 19 134
24-Aug-10 340 <I <1 <1 15 130
13-0ct-10 340 <1 <1 <1 16 134
23-Feb-l 1 1300 ND ND ND 18 114
l-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
ll-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 I2400 6.65 ND ND 47.2 614
l 1-Aug-14 12400 1.9 40 ND 41.5 540
21-0ct-14 12400 3.32 1.61 ND 54.9 596
Chloroform Carbon Chloromethane Methylene Nitrate Chloride II TW4-22 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (owl) (uwl)
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
19-0 ct,.]5 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-1 6 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
11-0ct-l 7 4770 ND ND ND 80.1 600
L2-Mar-l 8 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
10-Dec-19 3820 ND ND ND 59.9 608
19-Feb-20 3910 ND ND ND 57.7 606
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Chloroform Carbon Chlorometbane Methylene Nitrate Chloride TW4-23 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (m!/1) ' (u2/l)
27-Jun-07 <] <1 <l <l <0.1 47
15-Aug-07 <1 <l <l <I <0.1 46
lO-Oct-07 <1 <1 <l <l <0.1 43
26-Mar-08 <l <l <1 <1 <0.1 41
25-Jun-08 <1 <1 <1 <1 <0.05 41
10-Sep-08 <1 <1 <l <1 <0.05 35
JS-Oct-08 <2 <2 <2 <2 <0.05 51
4-Mar-09 <1 <1 <1 <I <0.1 41
24-Jun-09 <1 <1 <l <l <0.1 43
15-Sep-09 <1 <l <1 <l <0.1 43
16-Dec-09 <l <I <I <l <0.1 37
24-Feb-10 <l <l <l <1 <0.1 45
8-Jun-JO <1 <l <l <l <0.1 40
10-Aug-lO <1 <l <l <I <0.1 40
5-0 ct-10 <l <1 <1 <1 <0.1 34
16-Feb-1 l ND ND ND ND ND 44
25-May-11 ND ND ND ND ND 44
I 6-Aug-11 ND ND ND ND ND 41
15-Nov-l I ND ND ND ND ND 43
17-Jan-1 2 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-1 4 ND ND ND ND ND 44.6
2 1-May-14 ND ND ND ND ND 42.3
13-Aug-14 ND ND ND ND ND 46.0
28-0 ct-14 ND ND ND ND ND 46.8
12-Mar-15 ND ND ND ND ND 47.3
10-Jun-15 ND ND ND ND ND 48.4
3-Sep-15 ND ND ND ND ND 54.1
28-0cr-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
Chloroform Camon Chrotiome11liane Methylene Nitrate Chto:cicle TW4,.23 (ug(l) Tetraehloridi (ugff) Obloride (mgtl) (mdt) II (11;1dl:) (uef,t),
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
14-Dec-19 ND ND ND ND ND 54.4
17-Mar-20 ND ND ND ND ND 50.0
(ug/L)
0 0 0 0 0
~~~~~~ t I I I I I I I I I
Dec-07
Mar-08 I
Jun-08
Sep-08 :
Dec-08
Mar-09 I 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
~:~~~; ! Mar-14
Jun-14
Sep-14
Dec-14
Mar-15 1 Jun-15
Sep-15
Dec-15
Mar-16 %
Jun-16
Sep-16 •
Dec-16
Mar-17 l Jun-17
Sep-17
Dec-17
Mar-18 t
Jun-18 %
Sep-18
Dec-18
Mar-19
Jun-19
Sep-19
Dec-19
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Chloroform Carbon Chloromethane Methylene , Nitrate Chloride TW4-24 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) I (ue/1) (ue/1) I
27-Jun-07 2.6 <1 <1 <1 26.1 770
15-Aug-07 2.2 <1 <l <1 29 791
10-0ct-07 1.5 <1 <l <1 24.7 692
26-Mar-08 1.5 <1 <1 <1 24.4 740
25-Jun-08 1.4 <1 <1 <l 45.3 834
10-Sep-08 2.9 <l <1 <l 38.4 1180
15-0ct-08 <2 <2 <2 <2 44.6 1130
4-Mar-09 1.4 <l <1 <l 30.5 1010
24-Jun-09 1.5 <l <1 <1 30.4 759
15-Sep-09 1.4 <l <1 <1 30.7 618
17-Dec-09 1.2 <l <1 <1 28.3 1080
25-Feb-10 1.3 <1 <l <1 33.1 896
9-Jun-10 1.7 <1 <l <1 30 639
24-Aug-10 1.8 <1 <1 <l 31 587
6-0ct-10 1.4 <1 <l <l 31 522
17-Feb-ll 1.8 ND ND ND 31 1100
26-May-11 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
ll-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-Ju1-16 17.8 ND ND ND 34.4 1180
12-0ct-16 20.8 ND ND ND 31.9 1010
Chloroform Cu-bon Clfl(i)rom.e'llltane l\lletih I ne Nitrate Chloride TW4-24 Tetraehlo.ride Cbhride (ug/1) '{o~n (11gil) (tt1.!A~ (mg/I~ (mgA)
8-Mar-17 18.3 ND ND ND 41.3 1090
I 3-Jun-17 17.2 ND ND ND 39.9 1080
26-Jul-17 17.8 ND ND ND 40.0 1230
ll-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-1 8 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
10-Dec-19 43.3 ND ND ND 33.8 1090
19-Feb-20 61.7 ND ND ND 37.1 1010
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-25 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
27-Jun-07 <1 <l <l <] 17.1 395
15-Aug-07 <1 <l <1 <l 16.7 382
10-0ct-07 <l <l <1 <l 17 356
26-Mar-08 <1 <1 <1 <1 18.7 374
25-Jun-08 <1 <1 <1 <1 22.1 344
10-Sep-08 <l <1 <1 <1 18.8 333
15-0ct-08 <2 <2 <2 <2 21.3 366
4-Mar-09 <1 <1 <l <1 15.3 332
24-Jun-09 <l <1 <l <1 15.3 328
15-Sep-09 <l <l <l <l 3.3 328
16-Dec-09 <l <l <l <l 14.2 371
23-Feb-10 <1 <l <1 <1 14.4 296
8-Jun-10 <1 <l <1 <l 16 306
10-Aug-.10 <1 <1 <1 <l 14 250
5-0ct-10 <l <l <1 <l 15 312
16-Feb-l 1 ND ND ND ND 15 315
25-May-11 ND ND ND ND 16 321
16-Aug-11 ND ND ND ND 16 276
15-Nov-11 ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 ND ND ND ND 16 287
l 1-Sep-12 ND ND ND ND 17 334
3-0ct-12 ND ND ND ND 17 338
1 l-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
Chloroform Carbon Chlo,ramethaue Meflllylene Nitrate Chloride TW4-2:S (ug/1) Treuachlerlde (11g1jl) Oooruie (mgAn ~git) .I (111?tl), {us/t)
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
10-Dec-19 ND ND ND ND 0.841 73.1
19-Feb-20 ND ND ND ND 0.607 86.0
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-1
Jun-1
Sep-1
Dec-1
Mar-1
Jun-1
Sep-1
Dec-1
Mar-1
Jun-1
Sep-1
Dec-1
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TW4-26 Tetrachloride Chloromethane Chloride Nitrate Chloride
I
(ug/1) (ue/1.) (ug/1) (ue/1.) (mg/I) (mg/I)
I I
15-Jun-10 13 <l <l <l 7.9 33
l l-Aug-10 5 <1 <1 <1 9 17
6-0ct-10 5.4 <1 <1 <1 9.6 22
22-Feb-11 2.0 ND ND ND 10 30
26-May-l l 2.9 ND ND ND 10 15
l 7-Aug-11 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
l 1-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
11-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
18-Dec-19 1070 ND ND ND 10.3 38.3
18-Mar-20 1090 ND ND ND 11.9 36.3
Jun-10
Oct-10
Feb-11
Jun-11
Oct-11
Feb-12
Jun-12
Oct-12
Feb-13
Jun-13
Oct-13
Feb-14
Jun-14
Oct-14
Feb-15
Jun-15
Oct-15
Feb-16
Jun-16
Oct-16
Feb-17
Jun-17
Oct-17
Feb-18
Jun-18
Oct-18
Feb-19
Jun-19
Oct-19
Feb-20
N 0 0 0
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-27 Tetrachloride (ug/1) (ue/1) (ug/1) Chloride (ug/1) (mg/I) (mg/I)
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
l 1-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.l 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
14-Dec-19 7.97 ND ND ND 22.0 27.4
17-Mar-20 8.04 ND ND ND 23.6 27.6
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-28 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (uwl) (uwl)
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 l-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-l 7 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
ll-Sep-19 ND ND ND ND 10.2 49.0
12-Dec-19 ND ND ND ND 9.48 50.0
l 7-Mar-20 ND ND ND ND 9.87 52.1
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
Dec-19
Mar-20
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19-Jun-13 242 ND ND ND 4.63 44.8
11-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
1 l-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
l 9-Jun-19 537 ND ND ND 2.56 39.4
12-Sep-19 549 ND ND ND 2.55 38.0
18-Dec-19 630 ND ND ND 2.58 44.8
18-Mar-20 652 ND ND ND 3.1 41.0
0 0 "
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Cid :efunn € l'bon Chlumnet!fume M~lette Niirait.e Chi ~ TW4-30 (llfMI} Tet'r. :&toritle'Q ~ug:'A~ Ch:loride .ga) (ug/A)) (u;l!{4.)1 ,l!tmJAl)
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
ll-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
18-Dec-19 44.9 ND ND ND 3.62 39.1
17-Mar-20 53.1 ND ND ND 3.85 37.5
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
Dec-19
Mar-20
0
0
0
0
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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-1 4 ND ND ND ND 1.1 30
28-0 ct-14 ND ND ND ND 1.23 30
ll-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
2 1-0 ct-1 5 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
lO-Oct-1 7 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
11-Sep-19 ND ND ND ND 0.610 35.8
14-Dec-19 ND ND ND ND 0.583 40.6
17-Mar-20 ND ND ND ND 0.572 38.2
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
Oct-19
Dec-19
Feb-20
0
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-32 Tetrachloride (ug/1) (uwl) (ug/1) Chloride ( ug/1) (mg/I) (mg/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 1-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
14-Dec-19 ND ND ND ND 1.89 64.7
17-Mar-20 ND ND ND ND 1.97 59.7
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
Nov-19
Jan-20
Mar-20
0 0 0 0 . ~
••
••
•• ·~
••
·~
·~ ••
-
•
0
••
' .
0
0
0
0
0
0
0
0
0
;.
0
0
(ug/L)
0
0
:::J"'
0
"'"' 0 _..,
0
"'"' 3
:::J"'
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(/)
::,
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UI
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-33 Tetrachloride (ug/1) (ue/1) (ug/1) Chloride ( ug/1) (mg/I) (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-16 109 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
l 1-0ct-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
18-Dec-19 117 ND ND ND 1.86 48.8
18-Mar-20 94 ND ND ND 2.44 45.3
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
Nov-19
Jan-20
Mar-20
I\)
0 0
'
.i,.. 0
a,
0
(ug/L}
CX)
0
......
0 0
......
I\)
0
......
.i,.. 0
a,
0
-I :e ~ I w w
0 :::r
0 a -0 ""I 3
< !. C (D
tn
CJJJofff Pmi Carhn C or(!) dkaoe Md&,tene Nitrate ChltnPlde TW4-34 (ug/l) Tetr· ohtoride (ug/A) Cid de (mg/I) (mgM) (u,ml\ (udil
14-Nov-13 ND ND ND ND 1.64 19.2
23-Jan-14 ND ND ND ND 1.94 20.4
21-May-1 4 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
11-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
20-0 ct-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-19 ND ND ND ND 0.994 20.1
ll-Sep-19 ND ND ND ND 0.934 17.8
14-Dec-19 ND ND ND ND 1.07 21.4
17-Mar-20 ND ND ND ND 1.09 20.1
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
Nov-19
Jan-20
Mar-20
0 ..
'.
••
••
••
i•
~~
0
0
~.
0
0
0
0
0
0
0
0 ..
0
0
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••
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0 0 0 0
I
(ug/L)
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0
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CD
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3
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C CD 0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-35 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul?/1) (mun I
27-Aug-14 ND ND ND ND 0.2 34
28-0ct-14 ND ND ND ND 0.351 34.1
I 1-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-17 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
l 2-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
l l-Sep-19 ND ND ND ND 0.525 31.7
14-Dec-19 ND ND ND ND 0.524 37.4
I 7-Mar-20 ND ND ND ND 0.595 34.5
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
Oct-19
Dec-19
Feb-20
0
•
••
'.
•
• •
• '.
•
•
•
•
• i•
i•
i•
i•
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it
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(ug/L)
0 0 0 0 _,_
0 ::::r
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0 -0 --,:
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(D
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-36 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u,vl) (ue/1)
27-Aug-14 ND ND ND ND ND 65
23-0ct-14 ND ND ND ND ND 67.3
1 :t-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-1 6 ND ND ND ND ND 69.4
20-0 ct-16 ND ND ND ND ND 73.8
15-Mar-17 ND ND ND ND ND 60.2
I 5-Jun-17 ND ND ND ND ND 71.3
2-Aug-17 ND ND ND ND ND 69.6
10-0ct-l 7 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
14-Dec-19 ND ND ND ND ND 73.7
17-Mar-20 ND ND ND ND ND 69.1
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
Oct-19
Dec-19
Feb-20
0
••
••
0
••
•• ••
••
••
;
0
0
0
'
0
0
0
0
0
0
0
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{ug/L)
0 0 0 0 ......
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Odo,ofomu Carle Ckl~r~etlaa Metl.,Iene Nitrate Chlnride TW'4-37 Teetir. hloride Clmride ~ugi'l) fnd) (ag,ll} t,udl). (lng/lJ (mg/I)
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 1, 16 ND ND 31.2 281
26-Jul-l 7 15000 15.1 ND ND 30.5 277
ll-Oct-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
10-Dec-19 13100 8.8 3.12 ND 25.5 220
19-Feb-20 12000 8.5 12.30 ND 28.3 236
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
Oct-19
Dec-19
0
01 0 0 0
....
0 0 0 0
Feb-20 -
@ (ug/L)
0 0
I\)
0 0 0 0
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c,.:, 0 0 0 0
c,.:, 01 0 0 0
-I ! I w .....
0 :r
0 "'I ~ "'I 3
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0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW~38 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) fue/1} (usr./.1)
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 IO.I 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
14-Dec-19 ND ND ND ND 7.51 36.0
17-Mar-20 ND ND ND ND 8.11 33.4
(ug/L)
0 0 0 0 0 ...... ...... ...... ......
Nov-16 ---1----1----1-----+---+-----.1-------+------l
Feb-17
t May-17
Aug-17
Nov-17
I I I I I I I I I I
Feb-18 ~ I I I I I I I I I ~ ~ I w 0)
0
May-18 1 I I I I I I I I I I
:::r
0 ... a 0 ...
Aug-18 1 I I I I I I I I I I 3
< !. C (1)
Nov-18 I I I I I I I I 0
Feb-19
May-19
t
Aug-19
Nov-19
Feb-20
Chloroform Carbon Cble omethane Mdbykme Nitrate ~htoride TW4-39 Tetr.acbloride Cblf:>r.ide (ug(I) (u;g/.l) € ~) (netf.a (mg/l) (JJWf}
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 13"2
ll-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
10-Dec-19 1650 1.14 ND ND 0.948 74.7
19-Feb-20 812 ND ND ND 0.792 76.5
oi-qa.::1
6~-AON
6~-onv
6 ~ -A'E!V\I
B~-AON
UJ Cl) ::::,
'ii > 8 ~-onv E ...
0 -0 ...
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a,
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I -.::I' B ~-qa.::1 3:: I-
L~-AON
L~-onv
L ~ -li'BV\I
L ~-qa.::1
9~-AON
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
C\I 0 (X) CD s:t" C\I .... ....
(110n)
Chloroform Cat!bo, ChlOl!omeduute M$y1 ne Nitrate Chloride TW4-40 (ug/1) Tetrdl&•ide (ilg/1) Clooride (mg/t) (mgll') (11mn /,no;l,I'.\
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
10-Dec-19 314 ND ND ND 2.89 36.7
19-Feb-20 364 ND ND ND 2.98 38.5
tn Q) ::::, ca >
E ...
0 -0 ...
.2 .c
0
0 "'=" I "'=" 3: I-
0 0 '<:I"
0 I()
('I)
0 0 ('I)
0 I()
C\I
(1J6n)
0 I() 0 0
T""
0 I() 0
Oc-JBV\1-0 ~
6~-oaa-~
6~-5nv-8c
6 ~ -A'BV\1-9 ~
6~-qa.:1-v
8~-PO-LG
ehloroform Carbon Chloromethane Methylene Chloride TWr4-41 (ug/1) Tetrachloride ~ug/1) Chloride Nitrate '(~g/1) (mgll) (ue/1), Cue/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
10-Dec-19 1410 ND ND ND 6.11 42.1
19-Feb-20 1200 ND ND ND 6.12 44.4
UJ G) :::,
'ii >
E ...
0 -0 ...
.2 .c 0
T"'"
'111:1' I
'111:1' 3: I-
0 I{)
"'" T""
0 0
"'" T""
0 LO C")
T""
0 g
T""
(1J6n)
0 LO C\I
T""
0 0 C\I
T""
0 LO
T""
T""
Oc-JBV\1-0 ~
6 ~-oaa-~
6 ~ -6n'v'-£G
6 ~ -li'E!V\1-9 ~
6~-qa.:J-17
B~-PO-LG
Chlo11ofolllll Car:bon Cbloromethane Methy.Jene Nitrate 'Chloride TW.t .. ll2 Tetrachloride Chloride (ug/1) (uwi) (ug/1) (ug/1) (mg/I) (mg/I)
19-Jun-19 ND ND ND ND 2.57 23.3
11-Sep-19 ND ND ND ND 2.75 20.6
12-Dec-19 ND ND ND ND 2.82 22.6
17-Mar-20 ND ND ND ND 2.88 23.2
u,
G) ::::,
'ii >
E ...
0 -e
.2 .c
0
N -.:t' I !
.
0
(1/6n)
0
Oc-JBV'J-O ~
••
6 ~-oaa-~
0
6 ~ -6nv-£c
'.
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_Q1_20.xls
Gridding details:
1) kriging parameters: SURFER™ default parameters (point kriging, linear
variogram, slope= 1, no anisotropy [anisotropy= l], no search constraints [all data
used])
2) minx, 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) Q4, 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, MW-23, MW-27 through
MW-29, MW-35 (all non-detect).
Chloroform residual mass estimate kriged grid files {ascii format):
Ucm1Q20wl.grd: first quarter, 2020 Water Level Grid (ft amsl)
Ucm1Q20bb.grd: first quarter, 2020 Aquifer Base Grid (ft amsl)
Ucm1Q20sat.grd: first quarter, 2020 Saturated Thickness Grid (ft)
Ucm1Q20logchl.grd: first quarter, 2020 log of chloroform grid (log of ug/L)
Ucm1Q20chl.grd: first quarter, 2020 Chloroform Concentration Grid (ug/L)
Ucm1Q20ge70.grd: first quarter, 2020 Chloroform Concentration GE 70 Grid (ug/L)
Ucm1Q20volm3.grd: first quarter, 2020 Groundwater Volume Grid (m3)
Ucm1Q20masslb.grd: first quarter, 2020 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format):
Ucm1Q20wl.dat: first quarter, 2020 Water Level Grid XYZ file (ft amsl)
Ucm1Q20bb.dat: first quarter, 2020 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm1Q20sat.dat: first quarter, 2020 Saturated Thickness Grid XYZ file (ft)
Ucm1Q20logchl.dat: first quarter, 2020 log of chloroform grid XYZ file (log of ug/L)
Ucm1Q20chl.dat: first quarter, 2020 Chloroform Concentration Grid XYZ file (ug/L)
Ucm1Q20ge70.dat: first quarter, 2020 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm1Q20volm3.dat: first quarter, 2020 Groundwater Volume Grid XYZ file (m3)
Ucm1Q20masslb.dat: first quarter, 2020 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate file: Ucm1Q20result.xls
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
01 17 1271
0217 1372
0317 1948
0417 884
0118 1271
0218 1271
0318 1208
0418 1107
01 19 833
0219 1408
0319 1050
0419 770
01 20 1106
Notes:
lbs= pounds
H:\718000\may20\chloroform\masscalc\FL.l_resid_chl_mass_1Q20.xls: Table L.1
:ii" =-cu .... Ill E t;
1M
"' "' Ill ~
E .. .E 0 .. 0 ::i: u
iii :I "C ui cu a:
2400
2200
2000
1800
1600
1400
1200
1000
800
600
400
200
0
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ &~ ~~ ~~ ~~ &~ ~~ ~~ ~~ &~ ~~ ~~ ~~ &~ ~~ ~~ ~~ &~ ~~ ~~
~ mass estimate
-~ Linear (mass estimate)
HYDRO
GEO
CHEM, INC.
TIME SERIES OF RESIDUAL CHLOROFORM MASS
ESTIMATES
Approved I Date
SJS
Author I Date
SJS
File Name !Figure
MNSEstTimeSeries.zls L.1
H:\718000\may20\chloroform\masscalc\FL.1_resid_chl_mass_ 1020.xls: FL.1 Resid CHL Mass
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Wednesday, May 13, 2020 1 :02 PM
Phillip Goble
Dean Henderson; David Frydenlund; Terry Slade; Scott Bakken; Logan Shumway; Paul
Goranson
Transmittal of CSV Files White Mesa Mill 2020 Q1 Chloroform Monitoring
2002488-report-EDD.csv; 2003454-report-EDD.csv; Q1 2020 Chloroform Field Data.csv;
Q1 2020 DTW all programs.csv
Attached to this e-mail is an electronic copy of laboratory results for chloroform monitoring conducted at the White
Mesa Mill during the first quarter of 2020, 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
eF -·-· Energy Fuels Resources (USA) Inc.
Kathy W einel
Quality Assurance Manager
t: 303.389.4134 If: 303.389.4125
225 Union Blvd., Suite 600
Lakewood, CO 80228
http://www.energyfuels.com
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TabN
Exceedance Notices for the Reporting Period
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