DRC-2020-016544 - 0901a06880d42434

ENERGY FUELS
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.energyfuels.com
Div of Waste Management and Radiation Control
AUG 1 9 2020
-OWL-2020-05100
August 14, 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 2nd 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 2nd 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,
PAL-a
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Paul Goranson
Logan Shumway
Scott Bakken
Terry Slade
August 14, 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
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.energyfuel .com
Re: Transmittal of 2nd 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 2nd 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,
°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
2nd Quarter
{April through June)
2020
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
August 14, 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 .............................................................................. 1
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 Hydrographs .............................................................................................. 20
4.1.4 Depth to Groundwater Measured and Groundwater Elevation ................. 20
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture ............................ 20
4.2 Review of Analytical Results ............................................................................ 25
4.2.1 Current Chloroform Isoconcentration Map .............................................. 25
4.2.2 Chloroform Concentration Trend Data and Graphs .................................. 25
4.2.3 Interpretation of Analytical Data .............................................................. 25
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND
TW4-4 OPERATIONS REPORT ..................................................................... 29
5.1 Introduction ....................................................................................................... 29
5.2 Pump Test Data Collection ............................................................................... 30
5.3 Water Level Measurements .............................................................................. 30
5.4 Pumping Rates and Volumes ............................................................................ 30
5.4.1 TW4-19 ............................................................................................................ 31
5.5 Mass Removed and Plume Residual Mass ....................................................... 31
5.6 Inspections ........................................................................................................ 32
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 ............................................... 33
7 .3 Disposal of Extracted Groundwater .................................................................. 33
7.4 Compliance Well Performance ......................................................................... 3 3
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 .............................................. 39
10.0 SIGNATURE AND CERTIFICATION ........................................................... 40
LIST OF TABLES
Table 1 Summary of Wells Sampling for the Period
ii
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture
Zone Details Map and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater
Elevations over Time for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells
over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QNQC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank Evaluations
I-7 QNQC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform lsoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs over
Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
Tab N Exceedance Notices for the Reporting Period
iii
1.0 INTRODUCTION
The presence of chloroform was initially identified in groundwater at the White Mesa Mill (the
"Mill") as a result of split sampling performed in May 1999. The discovery resulted in the
issuance of State of Utah Notice of Violation ("NOV") and Groundwater Corrective Action
Order ("CAO") State of Utah Department of Environmental Quality ("UDEQ"), Division of
Waste Management and Radiation Control ("DWMRC") Docket No. UGW-20-01, which
required that Energy Fuels Resources (USA) Inc. ("EFRI") submit a Contamination Investigation
Plan and Report pursuant to the provisions of UAC R317-6-6.15(D). In response to the NOV,
EFRI submitted a series of documents outlining plans for investigation of the chloroform
contamination. This plan of action and preliminary schedule was set out in EFRI submittals
dated: September 20, 1999; June 30, 2000; April 14, 2005; and November 29, 2006. EFRI
submitted a draft Groundwater Corrective Action Plan ("GCAP") dated August 22, 2007. The
draft GCAP was reviewed by the Director, who advised EFRI in 2013 that modifications were
required. In an effort to expedite and formalize active and continued remediation of the
chloroform plume, both parties have agreed to the GCAP found in Attachment 1, of the final
Stipulation and Consent Order ("SCO") dated September 14, 2015.
This is the Quarterly Chloroform Monitoring Report for the second 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 wen 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 wens 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 wens
• Piezometers P-1, P-2, P-3, P-4 and P-5
• MW-20 and MW-22
• Nitrate monitoring wens
• 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 'ampling conducted for chloroform .inve tigation
purposes has conformed to the general principles et out in the QAP, ome of the requiremenl 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% RPO) 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 ervice 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
l 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.
Three trip blanks were provided by AW AL and returned with the quarterly chloroform
monitoring samples.
Two rinsate blank samples were collected as indicated on Table 1. Rinsate samples were labeled
with the name of the subsequently purged well with a terminal letter "R" added (e.g. TW4-7R).
The results of these analyses are included with the routine analyses under Tab H.
In addition, one DIFB, while not required by the Chloroform QAP, was collected and analyzed
for the same constituents as the well samples and rinsate blank samples.
3.2 Adherence to Mill Sampling S0Ps
The QA Manager's review of Mill Personnel's adherence to the existing SOPs, confirmed that
the QA/QC requirements established in the QAP and Chloroform QAP were met.
3.3 Analyte Completeness Review
All analyses required by the GCAP for chloroform monitoring for the period were performed.
7
3.4 Data Validation
The QAP and GWDP identify the data validation steps and data QC checks required for the
chloroform monitoring program. Consistent with these requirements, the QA Manager performed
the following evaluations: a field data 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 confirm. tliat all depth measurements used for development of the
groundwater contour map 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%'RPD.
Purging a Well to Dryness and Stability of a Limited Li t of Field Parameters
Wells TW4-3, TW4-6, TW4-7, TW4-10, TW4-12, TW4-13, TW4-14, TW4-26, TW4-27, TW4-
28, TW4-29, TW4-30, TW4-31, TW4-33, TW4-34, TW4-35, TW4-36, and TW4-42 were
pumped to dryness before two casing volumes were evacuated. After well recovery, one set of
measurements of pH, conductivity and temperature were taken. The samples were then collected,
and another set of measurements of pH, conductivity and temperature were taken. Stabilization
of pH, conductivity and temperature are required within 10% RPO under the QAP. The QAP
requirements for stabilization were met.
Continuou ly Pumped Wells
Wells MW-4, TW4-1, TW4-2, TW4-4, TW4-ll, 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, TW4-24, 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 amples are Teguired to be preserved and arrive at the
laboratory with a pH le s than 2. A review of the laboratory data revealed that the volatiJe
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 tran port of
the samples. Trip blank check 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% unle the measured results are less than 5
time · the required detection limit. This standard i ba ed 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 RPO 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 RPO is greater than 20%. The additional
duplicate information is provided for information purposes.
Duplicate results were within a 20% RPO 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 TW4-3R had a reported chloroform detection of 3.05 ug/L. TW4-3 was
nondetect for chloroform. Rinsate blank sample TW 4-9R had a reported chloroform detection of
1.98 ug/L. TW4-9 had a chloroform detection of 55.1 ug/L. The rinsate blank results for TW4-3
were outside of acceptance limits for the rinsate blank results.
TW4-3R wa collected after decontamination and prior to the pump being u ed to collect any Q2
2020 chloroform samples. Because the pump was not used prior to the rin ·ate ample collection,
the detection is not the result of cross contamination. TW 4-9R was collected after the
decontamination was completed after purging well TW4-5 and prior to sampling TW4-9. TW4-
9 had a chloroform detection of 55.1 ug /L. The chloroform detection of 55.1 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 Q2 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
except as indicated in Tab I. The data recoveries and RPDs which are outside the laboratory
established acceptance limits do not affect the quality or usability of the data because the
recoveries and RPDs above or below the acceptance limits are indicative of matrix interference
most likely caused by other constituents in the samples. Matrix interferences are applicable to
the individual sample results only. The requirement in the QAP to analyze a MS/MSD pair with
each analytical batch was met and as such the data are compliant with the QAP.
11
The QAP specifies that surrogate compounds shall be employed for all organic analy e • but the
QAP does not specify acceptance limits for surrogate recoverie ·. The analytical data as. ociated
with the routine quarterly sampling met the requirement pecified in the QAP. The information
from the Laboratory QA/QC Summary Report indicates that the urrogate recoverie. for the
quarterly chloroform ampJes were within acceptable laboratory limit for the surrogate
compounds. The requirement in the QAP to analyze urrogate compound was met and the data
are compliant with the QAP. Fmthermore, 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 ·ample made and
carried through all analytical steps. For the Mill amples a method blank was prepared for the
analytical methods. Per the approved QAP, contamination detected in analysis of method blanks
will be u ed to evaluate any analytical laboratory contamination of environmental amples. The
QAP state that non-conformance condition will exist when contaminant level.s in the
samples( ) are not an order of magnitude greater than the blank result. There were no detections
in the method blanks in this quarter. Method blank result are included in Tab H.
The information from the Laboratory QA/QC Summary Reports indicates that the LCS
recoverie for the amples were within acceptable laboratory limit for the regulated compounds
as indicated in Tab I.
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 as ociated with the wildlife ponds locally change the generaJiy
outherly perched water flow pattern . For example, northea t of the Mill ite, mounding
associated with formerly used wildlife ponds is still evident and di rupts the generally
southwesterly flow pattern, to the extent that locally north-nortbwe terJy flow occurs near MW-
19 and PIEZ-1. The impact of the mounding associated with the northern pond , to which water
has not been delivered ince March 2012, i dimini hing and i expected to continue to dimini h
as the a sociated mound decays due to reduced recharge. The perched groundwater mound
associated with the . outhern wiJdlife pond is also diminishing due to reduced recharge at that
location.
Not only has recharge from the wildlife pond 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 ite, resulted in changing
conditions that were expected to impact constituent concentrations and migration rates witbio the
plumes. Specifically, past recharge from the northern ponds helped limit many constituent
12
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 well
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, con ·tHuent concentration were generaJly expected to jncrea. e in downgradient well
clo e to the ponds before increa e were detected in wells farther downgradient of the pond .
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 plume are under control. Ongoing mechani ms that can be expected to
inc1·ease constituent concentrations Jocally as a result of reduced wildlife pond recharge include
but are not limited to:
1) Reduced dilution -the nnxmg of low constituent concentration pond recharge into
existing perched groundwater will be reduced over time.
2) Reduced saturated thicknesses -dewatering of higher permeability layers rece1vmg
primarily low constituent concentration pond water will result in wells intercepting these
layers receiving a smaller proportion of the low constituent concentration water.
The combined impact of the above two mechanisms was anticipated to be more evident at
chloroform pumping wells MW-4, MW-26, TW4-4, TW4-I9, and TW4-20; nitrate pumping
13
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 TW 4-4 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
wells immediately south and southeast (downgradient) of TW4-4 resulting from TW4-4 pumping
were expected to be muted because TW 4-4 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.
14
Detecting water level d:rawdowns in wells immediately outh and outbea t of TW4-4 re ulting
from TW4-4 pumping ha also been complicated by a general, long-term increase in water levels
in this area that has been attributable to past wildlife pond recharge. Between the fourth quarter
of 2007 and the fourth quarter of 2009 (just prior to the start of 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 ce sation of water delivery to tbe wildlife ponds and pumping.
Although water levels at ome of the well marginal to the chloroform plume uch as TW4-14,
TW4-27, TW4-30 and TW4-31 were generally increa ing until about tbe first quarter of 2018,
these water levels now appear to be relatively stable.
The e patially variable water Jevel trends likely result from pumping condition , the
permeability distribution, and di. tance from the wildlife pond . Wells that are relatively
hydraulically isolated (due to completion in lower permeability materials or due to intervening
lower permeability materials) and that are more di rant 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 previou lack of a well-defined cone of depres ion associated with TW4-4 was also
influenced by the historically relatively low water level at non-pumping well TW 4-14, located
ea t of TW4-4 and TW4-6. Prior to 2018 although water level djfference among these three
well bad dimini bed, and TW4-4 ha been pumping jnce 2010, the water level at TW4-14 was
typically lower than the water level at TW4-6 and lower to an even greater extent than the water
level at TW4-4. For the current quarter, a during the previous quarter, the water level at TW4-
14 is higher than water levels at both TW4~4 and TW4-6: the water level at TW4-14
(approximately 5535.2 feet above mean sea level ["ft amsl"]) is 4.4 feet higher than the water
level at TW4-6 (approximately 5530.8 ft amsl) and nearly 2 feet higher than the water level at
TW4-4 (approximately 5533.2 ft amsl). This pattern i attributable to the cone of depre. ion
induced by pumping both TW 4-4 and TW 4-41.
The static water levels at wells TW4-14 and downgradient well TW4-27 (installed outh 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 po itioned 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
15
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).
Pr.ior to the in taJJation of TW4-27, the persi tently low water level at TW4-14 was considered
anomalou because it appeared to be downgraclient 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
(5529.1 feet amsl) is, however, lower than water levels at adjacent wells TW4-6 (5530.8 feet
amsl) and TW4-23 (5532.8 ft. amsl), as shown in the detail water level map under Tab C.
Hydraulic tests inclicate that the permeability at TW4-27 is an order of magnitude lower than at
TW4-6 and three order of magnitude lower than at TW4-4 ( ee Hydro Geo Chem, Inc. [HGC],
September 20, 2010: Hydraulic Te ting of TW4-4, TW4-6 and TW4-26, White Me a Uranium
Mill, July 2010; and HGC, November 28, 2011: In tallation, Hydraulic Te·ting, 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 e ti.mate at TW4-27, uggested that both well were completed in materials hav ing
Jower permeability than nearby well . The low permeability condition likely reduced the rate of
long-term water level increase at TW4-14 and TW4-27 compared to nearby well , yielding water
level 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 In tallation and Hydraulic Te ting of TW4-35 and TW4-36
White Mesa Uranium Mill Near Blanding, Utah [A -Built Report]). Hydraulic tests also indicate
that the permeability at TW 4-36 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 al TW4-27 (approximately 5528.9 ft. am 1) i more than 6 feet
lower than the water level at TW4-14 (5535.2 ft. amsl). Increases in water level difference
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 re ults primarily from: the relative
positions of the well · past water delivery to the northern wiJdlife pond ; 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 i elation of TW4-14 and
TW4-27 delayed responses at these locations. Until pumping tarted at TW4-41, water levels at
both these wells were consistently lower than in surrounding higher permeability material even
though water levels in surrounding materials were generally decrea ing 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
16
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 TW4-14, 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 TW 4-14, consistent with the lower rate of increase in water levels at TW 4-27,
and the earlier reduction in the rate of increase (since early 2014) as discussed above).
The low permeability at TW4-14 and TW4-27 is expected to retard the transport of chloroform
to these wells (compared to nearby wells). As will be discussed in Section 4.2.3, TW4-14 and
TW4-27 remain outside the plume with current quarter chloroform concentrations of
approximately 2.9 µg/L and 7.9 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 TW4-4 around
the low permeability zone defined by TW4-36, TW4-14, and TW4-27.
Chloroform during the current quarter was detected at approximately 65 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:
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
17
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 TW4-4.
3. Chloroform concentrations at TW4-26 exceeded 70 µg/L for the first time during the
second quarter of 2017. Chloroform at TW4-26 is bounded by concentrations below 70
µg/L at TW4-6 and TW4-23 (located up-to cross-gradient of TW4-26); and at TW4-34
(located cross-to downgradient of TW4-26). Chloroform ha not been detected at either
TW4-23 or TW4-34. Although chloroform exceeding 70 µg/L was detected at well TW4-
40, in tailed 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 bound · 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 ource. The decrease at
TW4-33 is expected to be faster than at TW4-29 becau:e TW4-33 is in clo er proximity to TW4-
4 pumping. Such behavior is expected by analogy with the temporary decrea es in chloroform
concentrations that occurred at TW4-6 and TW4-26 once TW4-4 pumping began (di cus ed 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
ugge t that chloroform migration has been arre ted at TW4-33 by TW4-4 (and TW4-41)
pumping and that increasing chloroform at downgradient we.U TW4-29 result from a remnant of
the plume that continues to migrate downgraclient (generally toward TW4-30 which bounds the
plume to the ea t). The influence of TW4-4 pumping at the di tal end of the pJume is consi tent
w.ith generally decrea i.ng water level 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 northem
ponds, is expected to impact water leveJ within and adjacent to thi portion of the plume.
Reduced wildlife pond seepage, in particular reduced eepage from the southern wildlife pond
likely contributes to decreasing water level trend at both wells ( ince about the fomth quarter of
2013); temporarily increa ed concentralions at TW4-6 subsequent to the first quarter of 2014;
and increased concentrations at TW4-26 since the third quarter of 2016.
As the groundwater mound associated with the southern pond decays, groundwater flow
direction in the southern extremity of the plume are likely to become more southerly, and plume
migration is likely to turn more to the south. An increasingly southerly direction of plume
migration is consistent with increased concentrations at TW 4-26.
In addition, generally decreasing concentrations at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 since the third quarter of 2016, suggest that TW4-
18
4 pumping has arrested chloroform migration between TW 4-4 and TW 4-6, and that increased
chloroform at TW4-26 results from a remnant of the plume that continues to migrate south from
TW4-6 to TW4-26. The enhancement of pumping in the vicinity of TW4-4 by the start-up of
TW4-41 pumping in the second quarter of 2018 is likely to increase this apparent separation and
to have resulted in concentrations at 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 TW 4-40.
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 first quarter of 2020, as submitted with the
Chloroform Monitoring Report for the first quarter of 2020, is attached under Tab E. A
comparison of the water table contour maps for the current quarter (second quarter of 2020) to
the water table contour maps for the previous quarter (first quarter of 2020) 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 similar to last quarter.
Drawdown patterns and overall capture associated with pumping of the original chloroform
pumping wells MW-4, MW-26, and TW4-19 have changed as additional groups of wells have
been added to the pumping network. A large expansion in capture occurred within a year of the
initiation of pumping at nitrate pumping wells TW4-22, TW4-24, TW4-25 and TWN-2 in the
first quarter of 2013. Additional large expansions occurred once chloroform pumping wells
TW4-1, TW4-2, TW4-11, TW4-21 and TW4-37 became operational in 2015, and once TW4-39
became operational in the fourth quarter of 2016. Significant expansion of capture to the south
has resulted from pumping of TW 4-41 since the second quarter of 2018 and from initiation of
pumping at TW4-40 during the second quarter of 2019.
The drawdown at chloroform pumping wells MW-4, TW4-20 and TW4-21 decreased by more
than 2 feet this quarter. However drawdowns at chloroform pumping wells MW-26, TW4-2,
TW4-37 , TW4-39 and TW4-41; and nitrate pumping wells TW4-24 and TWN-2 increased 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 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 TW4-1, TW4-2 and TW4-11
are below the depth of the Brushy Basin contact this quarter. Although both increases and
decreases in drawdown occurred in pumping wells, the overall apparent capture area of the
combined pumping system is similar to last quarter.
19
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 historical1y relatively low water level at adjacent well TW4-14.
The expanded cone of depression as ociated 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
outherly expan ion of total pumping sy tern capture. As discu ed above, southerly expan ion
of capmre was additionally enhanced in the second quarter of 2019 by the initiation of pumping
at TW4-40.
The reported water level decrease of 0.45 feet at Piezometer 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
0.53 feet at Piezometer 4 and 5 likely re ulted primarily from reduced recharge at the southern
wildlife pond. Reported water level decrease of approximately 0.3 and 0.35 feet respectively, at
TWN-1 and TWN-4 are consi tent with continuing decay of the northern groundwater mound.
The reported water levels at MW-20 and MW-37 decreased by approximately 2.6 and 7.1 feet,
respectively, compensating for increases 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 decrease of nearly 4.1 feet at MW-22 compensates for
the reported increase last quarter that likely resulted from measurement error.
As noted above, the reported water level at TW4-20 increased (drawdown decreased) compared
to last quarter. The reported drawdown decreased even though the pump control mechanism
failed, causing continuous pump operation and eventual pump failure due to almost total
dewatering of the well and exposure of the pump to air.
Mea urable water was not rep01ted at DR-22. Although DR-22 is typically dry, mea urable
water wa reported in the bottom of its casing between the econd quarter of 2015 and the third
quarter of 2016.
4.1.3 Hydrographs
Attached under Tab F are hydrographs showing groundwater elevation in each chloroform
contaminant investigation monitor well over time.
4.1.4 Depth to Groundwater Measured and Groundwater Elevation
Attached under Tab F are tables showing depth to groundwater measured and groundwater
elevation over time for each of the wells listed in Section 2.1.1 above.
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
20
fouith 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 upgraclient of TW 4-4 were cho en because 1) they were located in
areas of the perched zone having relatively high permeability and . aturated thickne , and 2)
high concentrations of chloroform were detected at these locations. The relatively high
transmissivity of the perched zone in the vicinity of the, e original pumping wells re, ulted in the
wells having a relatively high productivity. The combination of relatively high productivity and
high chloroform concentration allowed for a high rate of chlornform ma removal. TW4-4 and
TW4-41 are located in a downgradient area having relatively high chloroform concentrations but
relatively small saturated thickness, and at a tran ition from relatively high to relatively Jow
permeability conditions downgradient of TW4-4. As with the other chloroform pumping wells,
pumping TW4-4 and TW4-41 help 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 mall saturated thickne e , the permeability in the vicinity of TW 4-
40 (located ·outb of TW 4-26) is large enough to make pumping practical. TW 4-40 is valuable in
that it i · located within the downgradient ( outhern) 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 contom map 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 vicinitie of wells TW4-1 TW4-2,
and TW4-11 which began pumping during the fir ·t quarter of 2015. As di.cosed in Section
4.1.1, although chloroform pumping well TW4-4 became operational in 2010 the drawdown
associated with TW4-4 was likely less apparent due to variable permeability conditions near
TW4-4 and the per istently Low water level at adjacent well TW4-I4. However, pumping at
adjacent well TW4-41 since the econd quarter of 2018 has generally increased drawdowns in
th.is area; the third quarter of 2018 wa the first quader 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 expan ion 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 increa es and decrea es in water level occurred at njtrate and
chloroform pumping wells, although change in water levels in chloroform pumping well TW4-
1, TW4-4, TW4-11, TW4-I9 and TW4-40; and citrate pumping weUs TW4-22 and TW4-25
were less than two feet. Water level decreases occurred in chloroform pumping well MW-26
(nearly 12.6 feet); TW4-l (approximately 0.7 feet)· TW4-2 (approximately 2.1 feet)· TW4-4
(approximately 1.2 feet); TW4-ll (approximately 0.6 foot); TW4-37 (nearly 2.5 feet)· TW4-39
(approximately 3.9 feet); and TW4-41 (nearly 12 feet)· and in nitrate pumping weJJ . TW4-24
21
(approximately 5.3 feet); TW4-25 (approximately 0.3 feet); and TWN-2 (nearly 11 feet). Water
level increases occurred in chloroform pumping wells MW-4 (approximately 7.8 feet); TW4-19
(approximately 1.5 feet); TW4-20 (approximately 9 feet); TW4-21 (approximately 6.2 feet); and
TW4-40 (approximately 0.2 feet); and in nitrate pumping well TW4-22 (approximately 0.7 feet).
The overall apparent combined capture area of the nitrate and chloroform pumping systems is
similar to last quarter.
As noted in Section 4.1.2, the reported water level at TW4-20 increased (drawdown decreased)
compared to last quarter. The reported drawdown decreased even though the pump control
mechanism failed, causing continuous pump operation and eventual pump failure due to almost
total dewatering of the well and exposure of the pump to air.
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 6.3
gpm. This calculation is based on the total volume pumped by these wells over the 90 day
quarter (820,207 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 2.9
gpm or 85 %, and is considered adequate at the present time even with the reduced productivities
of some wells. In addition, because of continued reductions in saturated thicknesses and
hydraulic gradients resulting from reduced wildlife pond recharge, 'background' flow through
the plume is expected to continue to diminish, thereby reducing the pumping needed to control
the plume.
Chloroform concentrations at many locations have been or appear to be affected by changes
associated with reduced dilution from the wildlife ponds and nitrate pumping. For example,
22
increases in chloroform at TW4-22 and TW4-24 after these wells were converted to nitrate
pumping wells are attributable to we tward migration of chloroform from the vicinity of TW4-20
toward these wells. The increa e in concentration at TW4-8 from non-detect to 100 µg/L in the
fir t quarter of 2014 i Ukely related to reduced dilution. The concentration at TW4-8 remained
below 70 ug/L thi quarter after dropping below 70 µg/L la t quarter. In addition although the
chloroform concentration in TW4-6 generally decreased between the first quarter of 2015 and
the current quarter (and remain · out ide the plume) concentration· at TW4-6 increa ed from
approximately 6 µg/L in the fast quarter of 2014 to 1,180 µg/L in the fir t quru.ter of 2015 before
dropping to approximately 5 µg/L tbi quarter. The increa. e between the fir t quarter of 2014
and the fir t quarter of 20 J 5 was likely related to both reduced dilution and more westward flow
induced by nitrate pumping.
TW4-6 i · located immediately outh and historically cro -to downgradient of chloroform
pumping well TW4-4. TW4-6 ha been incorporated into the chloroform plume twice: from the
fir t quruter of 2009 through the third quarter of 2010; and from the third quarter of 2014 through
the econd quarter of 2018. Pumping of TW4-6 (and TW4-26) i impractical becau e of
relatively low permeability and relatively small saturated thickne·se . However, pumping at
more productive location upgradient of TW4-6 (s uch a TW4-4 and TW4-41) enhances ma
removal and lowers hydraulic gradient , thereby reducing the rate of downgradient chloroform
migration and allowing natural attenuation to be more effective. Pumping at TW4-4 was
implemented during the fir t quarter of 2010 to improve capture downgradient of TW4-4 to the
extent allowable by the lower productivity conditions present in thi area.
The beneficial effect of pumping TW 4-4 was demon trated by the net decrease in TW 4-6
chloroform concentrations from 1,000 µg/L to 10.3 µg/L, and jn TW4-26 from 13 µg/L to 4.2
µg/L, between the initiation of TW4-4 pumping and the second quruter of 2014. Concentration
at these wells decrea ed substantially even though they did not unambiguously appear to be
within the hydraulic capture of TW4-4. As discu ed in Section 4.1.1, however the decrease in
the long-term rate of water level rise at TW 4-6 after TW 4-4 began pumping does ugge t that
TW4-6 was within the hydraulic influence of TW4-4. The decline in water levels at TW4-6 since
the fourth quarter of 2013 likely reflects the additional influence · of ce sation of water delivery
to the wildlife ponds and the addition of chloroform pumping well TW4-1, TW4-2, TW4-11
and TW4-41. Regardless of whether TW4-6 was demon trably within the hydraulic capture of
TW4-4, pumping TW4-4 and relatively recently in tailed adjacent pumping well TW4-41, help
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 beneficiaJ 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 quru1er of 2005, and maintained concentration
below 70 µg/L until the econd quarter of 2014, even though TW4-16 appears to be beyond the
hydraulic capture of MW-26. Furthermore, the overall hydraulic capture of the chloroform
pumping ystem ha expanded ince initiation of pumping at wells TW4-1, TW4-2 TW4-J 1
TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 ince the beginning of 2015. In particular, the
23
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 quaiter of 2015. Chloroform at TW4-16 has been above and below 70 µg/L
since the second quarter of 2015 and was detected at 141 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 rustoric groundwater elevations in this area,
TW4-29 was positioned generally cross-gradient of TW4-4 and TW4-6. As di cussed 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 con i tent with chloroform exceeding 70 µg/L detected in the fourth quarter of 2013
at TW4-33, in talled 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 TW 4-29 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
TW 4-4 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.
A di cu sed in Section 4.1.1 generally decrea ing water level trends at TW4-6 and TW4-26
( ince about the fourth quarter of 2013), temporarily increa ed concenu·ations at TW4-6 (since
the fir t quarter of 2014) and iocrea ed concentrations at TW4-26 (since the third quarter of
2016), are also consistent with reduced wildlife pond seepage, in particular reduced seepage
from the southern wildlife pond. As the groundwater mound associated with the outhern 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
24
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 1,140 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 TW 4-6 to TW 4-26. 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 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 (as discussed in Section 4.2.3) demonstrate that
chloroform is bounded to the southeast of TW4-29; and chloroform analytical results from TW4-
36 indicate that when concentrations at TW4-8 exceed 70 µg/L, chloroform is bounded to the
east of TW 4-8.
4.2 Review of Analytical Results
4.2.1 Current Chloroform Isoconcentration Map
Included under Tab J of this Report is a current chloroform isoconcentration map for the Mill
site. Details of the gridding procedure used to generate the chloroform isoconcentration map
(consistent with Part III.B.2.a through Part III.B.2.c of the GCAP) are provided in Tab L.
4.2.2 Chloroform Concentration Trend Data and Graphs
Attached under Tab K are tables summarizing values for all required parameters, chloride,
nitrate/nitrite, carbon tetrachloride, chloroform, chloromethane, and methylene chloride, for each
well over time.
Attached under Tab K are graphs showing chloroform concentration trends in each monitor well
over time.
4.2.3 Interpretation of Analytical Data
Comparing the chloroform analytical results to those of the previous quarter, as summarized in
the tables included under Tab K, the following observations can be made:
a) Chloroform concentrations have increased by more than 20% in the following wells
compared to last quarter: MW-26, TW4-16, TW4-30 and TW4-39;
25
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: TW4-1, TW4-2, TW4-6, TW4-20 and TW4-22;
c) Chloroform concentrations have remained within 20% in the following wells compared
to last quarter: MW-4, TW4-4, TW4-5, TW4-7, TW4-8, TW4-9, TW4-10, TW4-11,
TW4-14, TW4-18, TW4-19, TW4-21, TW4-24, TW4-26, TW4-27, TW4-29, 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 well with detected chloroform were
within 20% of the values reported for the well during the previou quarter uggesting that
variations are within the range typical for sampling and analytical error. Well MW-26, TW4-1
TW4-2, TW4-6, TW4-16, TW4-20, TW4-22, TW4-30 and TW4-39 had changes in
concentration greater than 20%. Of these, MW-26, TW4-1, TW4-2, TW4-20 and TW4-39 are
chloroform pumping wells; and TW4-22 is a nitrate pumping well. TW4-6 is located adjacent to
chloroform pumping wells TW4-4 and TW4-41; TW4-16 is located just inside the plume
boundary; and TW4-30 is located just outside the downgradient extremity of the plume.
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, fluctuations in concentrations at wells such as TW 4-16 and TW 4-30 are expected
based on their locations near the plume margins.
Chloroform pumping wells TW4-l 1 (2,810 µg/L); TW4-19 (7,600 µg/L), TW4-20 (5,800 µg/L),
TW4-37 (11,700 µg/L) and TW4-39 (5,870 µg/L)-and nitrate pumping well TW4-22 (2 530
µg/L), had the highest detected chloroform concentrations. Since last quarter the chloroform
concentration in TW4-11 decreased from 2,990 to 2,810 µg/L; TW4-19 decreased from 8,720
to 7,600 µg/L; TW4-20 decreased from 14,300 µ.g/L to 5,800 µg/L; TW4-37 decrea ed from
12,000 µg/L to 11,700 µg/L; and TW4-39 increa ed from 812 to 5,870 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 decreased from 844 to 767 µg/L;
the concentration in nitrate pumping well TW4-22 decreased from 3,910 to 2,530 µg/L; and the
concentration in nitrate pumping well TW4-24 decreased from 61.7 to 49.4 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.
A noted ia Section 4.1.2, failure of the TW4-20 pump control mechanism caused continuou
pump operation and eventual pump failure due to almo t total dewatering of the well and
exposure of the pump to air. Pump failure mo. t likely resulted from overheating due to lack of
submersion of the pump beneath a ufficient column of water. Overheating which i expected to
have caused substantial volatilization of chloroform and a consequent reduction in chloroform
within the groundwater sampled in the well, is the likely cause of the reduction in reported TW4-
20 chloroform from 14,300 µg/L last quarter to 5,800 µg/L this quarter.
26
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decrea ed slightly from 55 µg/L to 53.8 µg/L, and remained outside the plume.
TW 4-8 is located immediately east of chloroform pumping well MW-4, where chloroform wa
detected at a concentration of 1,250 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 wa re-
incorporated into the plume between the first quarter of 2014 and the fourth qua1ter of 2019. The
occurrence of elevated chloroform at TW4-8 i likely related to its location along the ea tern
plume boundary immediately east of pumpjng well MW-4. Changes in the plume boundary near
TW4-8 are expected to re ult from changes in pumping and reduced dilution re ·ulting from
ce sation of water delivery to the northern wildlife pond . Chloroform at TW4-8 is bounded to
the north by TW4-3 and TW4-38 (both non-detect) to the northea t by TW4-13 (non-detect) to
the east by TW4-36 (non-detect), and to the outheast by TW4-14 (2.9 µg/L).
Chloroform at TW4-29 (located at the outbeastern extremity of the plume, to the east of TW4-
26 and to the south of TW4-27) increa ed from 652 µg/L to 686 µg/L and chloroform at TW4-
30, located immediately cross-to downgradient of TW4-29, increa ed from approximately 53
µg/L to approximately 65 µg/L. Chloroform at TW4-14 decreased lightly from 3 µg/L to 2.9
µg/L and chloroform at TW4-27 remained at approximately 8 µg/L. Concentration trends at
these weU · are generalJy con i tent with ongoing, but low, downgradient migration of
chloroform at these locations. Chloroform at TW4-29 i bounded to the north by TW4-27
(approximately 8 µg/L), to the east by TW4-30 (approximately 65 µg/L) to the outheast by
TW4-35 (non-detect), to the south by TW4-34 (non-detect), and to the we t-noithwe t by TW4-6
(approximately 5 µg/L) and TW4-23 (non-detect). As discus ed in Secti.on 4.1.1, general
increa ·e in concentrations at TW4-26 since the third quaner of 2016 are also consi tent with
continuing downgradient chloroform migration which is Jikely 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 94 µg/L to 90 µg/L. Chloroform at TW4-33 i bounded to
the north by TW4-14 (approximately 3 µg/L), to the east by TW4-27 (approximately 8 µg/L)
and to the west by TW4-6 (approximately 5 µg/L) and TW4-23 (non-detect). Recent increa es in
concentration at TW4-26 have widened the southeast extremity of the plume which hi todcally
was narrow compared to more upgradient locations.
The chloroform concentration in TW4-6 decrea. ed from approx.imately 7 µg/L to approximately
5 ~tg/L. TW4-6 has remained outside the chloroform plume since the third quarter of 2018.
In tailed in the econd quarter of 2000, TW4-6 wa the mo t downgradient temporary perched
well prior to in. tallation 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 condition and the effects of
upgradient chloroform removal by pumping, and 2) natural attenuation.TW4-6 was subsequently
incorporated into the plume twice: from the fir t quaiter of 2009 through the third quarter of
2010; and from the third quarter of 2014 through the second quarter of 2018. Between initiation
27
of pumping of TW4-4 in the first quarter of 2010 and the second quarter of 2014, concentrations
at TW4-6 hewed a net decrease from 1 000 µg/L to 10.3 µg/L.
The relatively slow rate of chloroform migration in the vicinity of TW4-6 in the past is
demonstrated by comparing the rate of increase in chloroform at this well to the rate of increase
in the nearest upgradient well TW4-4. Concentrations at TW4-4 increased from non-detect to
more than 2,200 µg/L within only two quarters whereas 16 quarters were required for
concentrations in TW4-6 to increase from non-detect to only 81 µg/L. Thi. behavior is consistent
with hydraulic te ts performed at TW4-4, TW4-6 and TW4-26 during the third quarter of 2010
that indicate a nearly two orders of magnitude decrea e in permeability outh (downgradient) of
TW4-4. Chloroform migration rates in the vicinitie. 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 TW4-4 pumping, chloroform concentrations at both TW4-29 and
TW 4-33 are expected to eventually trend downward.
Although changes in concentration have occurred in well with.in the chloroform plume the
boundaries of the plume have not changed significantly ince the la t quarter, except for a slight
expansion near TW4-9 and TW4-16, and a slight contraction near TW4-24. The chloroform
concentration decrease at TW4-24, from approximately 62 µg/L to 49 µg/L, shifted the plume
boundary to the wet away from TW4-24. The concenLration increa e at TW4-9 (from.
approximately 49 µg/L to 55 µg/L); and at TW4-16 (from approximately 113 µg/L to 141 µg/L
shifted the plume boundary sligbtJy to the east and southwe t, respectively. Similar to last
quarter, due primarily to decrea. es in concentrations at TW4-6 and TW4-33, the kriging
algolithm has pinched off the outhern extremity of the plume.
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 econd quarter of 2015 and reduced productivity at
TW4-24 (since the third quarter of 2014). Sub equent to the fir t quarter of 2014, generalJy
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 weJI . Th.is increa ·e was likely related to reduced dilution from ce ation of
water delivery to the northern wildlife pond and more westerly flow induced by nitrate
pumping. In addition, concentrations at TW4-6 are likely influenced by reduced recharge at the
outhern wildlife pond and the decay of the a sociated groundwater mound.
TW4-6 has remained outside the plume since the third quarter of 2018 due to the general
decrea e in chloroform concentrations ince the third quarter of 2015, while (as discussed in
28
Section 4.1.5) TW4-16 has been both within and outside the plume. This quarter, although TW4-
6 remains outside the plume, TW 4-16 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 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. This behavior is consistent with the apparent 'pinching-off' of the southern
extremity of the plume during the previous and current quarters. Regardless, pumping at TW 4-
41, located adjacent to TW4-4, and pumping at TW4-40, located just south (downgradient) of
TW4-26, is expected to reduce or halt plume expansion to the south.
Although the nitrate pumping system may redistribute chloroform within the plume and cause
changes in the chloroform plume boundaries, continued operation of the nitrate pumping system
is expected to enhance capture associated with the chloroform pumping system. Furthermore,
since the beginning of 2015, the addition of chloroform wells TW4-1, TW4-2, TW4-11, TW4-
21, TW4-37, TW4-39, TW4-40 and TW4-41, is expected to have a beneficial impact. Generally
reduced concentrations at TW4-6 (since the first quarter of 2015) and TW4-16 (since the fourth
quarter of 2014) after previous increases are likely the result of initiation of TW4-1, TW4-2, and
TW4-ll 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
OPERA TIO NS 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 TW4-1 l
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 TW4-41. Beginning in May 2019 EFRI began long term pumping of TW4-40.
The following information documents the operational activities during the quarter.
29
5.2 Pump Test Data Collection
The long term pump te t for MW-4 wa tarted 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
Augu t 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 fir t pha e
of the pump te l and collect the initial two days of monitoring data for MW-4. EFRI personnel
bave gathered subsequent water level and pumping data.
Analyses of hydraulic parameters and discussions of perched zone hydrogeology near MW-4 has
been provided by Hydro Geo Chem in a separate report, dated November 12, 2001, and in the
May 26, 2004 Final Report on the Long Term Pumping Test.
Data collected during the quarter included the following:
• Measurement of water levels at MW-4, TW4-1, TW4-2, TW4-4, TW4-ll, 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 TW4-1, TW4-2, TW4-11, TW4-21, TW4-22,
TW4-24, TW4-25, TW4-37, TW4-39, TW4-41, and TWN-2 have been measured weekly. Depth
to groundwater in all other chloroform contaminant inve ·tigation wells i monitored monthly.
Copies of the weekly Depth to Water monitoring sheet for MW-4 MW-26, TW4-1, TW4-2,
TW4-ll 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 well and the elected temporary
well and permanent monitoring well. are included under Tab C. Monthly depth to water
mea urement 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
ince the inception of the chloroform recovery program for the active pumping well . It i
imprntant to note that TWN-2 i a nitrate program well and is ampled only for nitrate and
30
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 well are . hown in Table G-3.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Unless specifically noted below, no operational problems were observed with the well or
pumping equipment during the quarter.
5.4.1 TW4-19
During the routine check on May 4, 2020, the pump in TW4-19 malfunctioned. All ancillary
systems and controllers were checked and it was determined tbat the pump wa the cause of the
issue. The pump was removed and replaced within 24 hours of discovery and as such no
notifications were necessary.
5.5 Mass Removed and Plume Residual Mass
Chloroform removal wa e timated as of the first uarter 2007. Since that e timation, the ma s
removed by well for each quarter has been compiled in Table G-2, which show. the pound of
c.Woroform that have been removed to date. The ma s of chloroform removed from the plume
this quarter is approximately 25.2 lb., which is approximately 33% larger than the approximately
18.9 lb. removed last quarter. The larger rate of mass removaJ is attributable prima.dly to the
increased concentrations at TW4-39 and the increase in the total gallons pumped from TW4-20
due to failure of the control mechanism that protected the well from pumping dry.
The residual mass of chloroform within the plume is estimated as 1,056 lb. using the
methodology de cribed in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 50 lb. smaller than last quarter's estimate of 1,106 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 1,056 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
31
located immediately upgradient of the chloroform plume. The increase in calculated mass results
from increa ed plume area and increased average concentrations within the plume. The increa. es
i_n both pJume area and average concenu·ation. are attributable to reduced dilution due to the
reduction in cbJoroform-free wildlife pond seepage.
The general decrease in the re idual mass e timates ince the second qt1arter of 2016 ugge t
stabilization. Although the re idual mass estimates are generally larger ince 2012, the rate of
ma removed per quarter by pumping is al o generalJy larger, in particular ince the addition of
8 new pumping well since the beginning of 2015. Furthermore, although the pumping sy tern i
not designed to hydraulically capture the entire plume, the proportion of the ma s of the plume
under capture ha historically been large. The proportion of the ma s of the plume under capture
during the fourth quarter of 2012, 2013 2014 2015, 2016 2017, 2018 and 2019 ranged from
approximateJy 84% to 99%. The approximate proportion of the mass of the plume under capture
this quarter i 99%, about the ame a last quarter's.
5.6 Inspections
All of the required inspections were completed and the inspection forms are included in Tab C.
5.7 Conditions That May Affect Water Levels in Piezometers
No water was added to the any of the wildlife ponds during the quarter.
6.0 CORRECTIVE ACTION REPORT
No corrective actions were necessary for the current reporting period.
6.1 Assessment of Previous Quarter's Corrective Actions
There were no corrective actions required during the previous quarters' monitoring period.
7.0 CURRENT COMPLIANCE STATUS
7.1 Long Term Chloroform Plume Control
The chloroform plume is currently entirely within the Mill prope1ty boundary and i bounded on
aJl ides by wells having chloroform concentrations that are either non-detect or le s than 70
µg/L (Tab J). The plume i bounded to the north by TW4-25 (non-detect)· to the we t and
southwe t by MW-31 (non-detect) MW-32 (non-detect), TW4-6 (approximately 5 µg/L), TW4-
23 (non-detect), and TW4-24 (approximately 49 µg/L); to the ea t by TW4-3 (non-detect), TW4-
5 (approximately 15 µg/L) TW4-8 (approximately 54 µg/L), TW4-9 (approximately 55 µg/L),
TW4-13 (non-detect), TW4-14. (approximately 3 µg/L), TW4-18 (approximately 58 µg/L),
TW4-27 (approximately 8 µg/L) TW4-30 (approximately 65 µg/L), TW4-36 (non-detect) and
TW4-38 (non-detect); to the outh by TW4-34 (non-detect) and TW4-42 (non-detect); and to the
southeast by TW4-35 (non-detect).
32
Becau e TW4-26 no longer bounded the chloroform plume to the outh-southw~ t, TW4-40 wa
installed south (downgradient) of TW4-26 during the fir t quarter of 2018. Becau e the econd
quarter of 2018 was the econd consecutive quarter that chloroform in TW4-40 exceeded 70
µg/L, the required Plan and Time Schedule wa. ubmitted and TW4-42 wa in tailed
approximately 200 feet south of TW4-40 during April, 2019. Chloroform ha not been detected
in TW4-42 indicating that TW4-42 bounds the plume immediately to the outh-southwe t.
Regardles MW-17 (non-detect) and MW-38 (non-detect) bound the plume to the far ·outbwest
(cro -gradient) and MW-22 (non-detect), MW-39 (non-detect) and MW-40 (non-detect) bound
the plume far to the south (cro -to downgradient). Data collected to date indicate there are
ufficient chloroform monitoring and pumping well 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
in talled during the quarter a well as all previously installed well were installed in accordance
with tbe GCAP requirement. The well were maintained and operated a required. Additional
detail regarding any pecific pumpfog well operations and maintenance i sues noted during the
quarter are discussed in Section 5.0 above.
7 .3 Disposal of Extracted Groundwater
Part II of the GCAP requires that all extracted groundwater be di posed of in the tailings
management system or fed in the Mill proces . All extracted groundwater was handled as
required by the GCAP.
7 .4 Compliance Well Performance
Part II.G of the GCAP state that an exceedance of the compliance well performance standard is
defined as the pre ence 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 report . The previously noted exceedances have been addressed in Plans and Time
Schedules. There are no new exceedances in thi 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 e timated a 1 056 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 50 lb. less than La ·t quarter s estimate of 1,106 lb. The mass of
chloroform removed from the plume this q11arter is approximately 25.2 lb., which i
33
approximately 33% larger than the approximately 18.9 lb. removed last quarter. The larger rate
of mass removal is attributable primarily to the increased concentrations at TW4-39 and the
increase in the total gallons pumped from TW4-20 due to failure of the control mechanism that
protected the well from pumping dry.
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 5 µg/L), TW4-
23 (non-detect), and TW4-24 (approximately 49 µg/L); to the east by TW4-3 (non-detect), TW4-
5 (approximately 15 µg/L), TW4-8 (approximately 54 µg/L), TW4-9 (approximately 55 µg/L),
TW4-13 (non-detect), TW4-14 (approximately 3 µg/L), TW4-18 (approximately 58 µg/L),
TW4-27 (approximately 8 µg/L), TW4-30 (approximately 65 µg/L), TW4-36 (non-detect) and
TW4-38 (non-detect); to the south by TW4-34 (non-detect) and TW4-42 (non-detect); and to the
southeast by TW4-35 (non-detect).
Because TW4-26 no longer bounded the chloroform plume to the south-southwest, TW4-40 was
installed south (downgradient) of TW4-26 during the first quarter of 2018. Because the second
quarter of 2018 was the second consecutive quarter that chloroform in TW4-40 exceeded 70
µg/L, the required Plan and Time Schedule was submitted and TW4-42 was installed
approximately 200 feet south of TW4-40 during April, 2019. Chloroform has not been detected
in TW4-42, indicating that TW4-42 bounds the plume immediately to the south-southwest.
Regardless, MW-17 (non-detect) and MW-38 (non-detect) bound the plume to the far southwest
(cross-gradient), and MW-22 (non-detect), MW-39 (non-detect) and MW-40 (non-detect) bound
the plume far to the south (cross-to downgradient). Data collected to date indicate there are
sufficient chloroform monitoring and pumping wells to effectively define, control, and monitor
the plume.
The water level contour maps for the 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-ll during the first quarter of 2015. Capture in the
northwestern portion of the plume was enhanced by start-up of chloroform pumping wells TW4-
21 and TW4-37 during the second quarter of 2015; and of TW4-39 during the fourth quarter of
2016. Capture in the southernmost portion of the plume was enhanced by start-up of pumping at
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 drawdowns
in this area since the second quarter of 2018, and development of a definable capture zone, is
attributable to pumping at adjacent well TW4-41.
The capture zone associated with TW4-4 was likely obscured prior to the second quarter of 2018
by the historically relatively low water level at adjacent well TW4-14 and the two orders of
34
magnitude decrease in permeability south of TW4-4. However a noted in previou report ·,
between the ffr t quarter of 2010 and the second quarter of 2014, decreases in chloroform
concentrations and the rate of water level rise at TW4-6 Oocated downgradient of TW4-4) likely
resulted from TW 4-4 pumping.
Cone · of depres ion as ociated with the nitrate pumping well became evident a of the fomth
quarter of 2013, and capture associated with the nitrate pumping i expected to continue to
develop. Overall the apparent capture area of the combined chloroform and nitrate pumping
ystems i smaUer than la t quarter, with capture decrea ing within the central and northern
portions of the pumping ystem due to decrea ed 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 Repo1t (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Me a 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, TW4-1 l, TW4-19, TW4-20, TW4-21 TW4-22,
TW4-24, TW4-37, TW4-39, TW4-40 and TW4-41) is approximately 6.3 gpm, which exceeds
the calculated background flow by 2.9 gpm or 85%, 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 previou · quarter, suggesting that variation are within the range
typical for ampling and analytical error. We11s MW-26, TW4-1, TW4-2, TW4-6 TW4-16,
TW4-20, TW4-22, TW4-30 and TW4-39 had change in concentration greater than 20%. Of
these, MW-26, TW4-1, TW4-2, TW4-20 and TW4-39 are chloroform pumping well ; and TW4-
22 is a nitrate pumping well. TW4-6 is located adjacent to chloroform pumping wells TW4-4 and
TW4-4I · TW4-16 is located just inside the plume boundary; and TW4-30 is located just outside
the downgradient extremity of the plume.
Fluctuations in concentrations at both chloroform and nitrate pumping wells and well adjacent
to pumping wel ls likely result in part from change in pumping. In addition, because TW4-I6
and TW4-30 are located just outside the plume boundary fluctuations in concentration at these
wells are expected based on their locations near the plume margins. Furthermore, changes in
concentrations at chloroform wells are expected to resu1t from con6nued operation of nitrate
pumping wells as the capture associated with nitrate pumping expands and flow directions
change locally.
Chloroform pumping well TW4-l l (2,810 µg/L); TW4-19 (7,600 µg/L), TW4-20 (5,800 µg/L)
TW4-37 (J 1,700 µg/L) and TW4-39 (5 870 µg/L; and nitrate pumping well TW4-22 (2,530
µg/L), bad the highe ·t detected chloroform concentration . Since last quarter, the chloroform
concentration in TW 4-11 decreased from 2,990 to 2,8 l O µg/L; TW 4-19 decreased from 8 720 to
7,600 µg/l; TW4-20 decreased from 14,300 µg/L to 5,800 µg/L-TW4-37 decrea. ed from
12,000 µg/L to 11 700 µg/L; and TW4-39 increa ed from 812 to 5,870 µg/L. In addition, the
chloroform concentration in chloroform pumping well TW4-21 decrea ed from 844 to 767 µg/L;
the concentration in nitrate pumping well TW4-22 decreased from 3,910 to 2,530 µg/L; and the
35
concentration in nitrate pumping well TW4-24 decreased from 61.7 to 49.4 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.
A noted in Section 4.1.2, failure of the TW4-20 pump control mechanism caused continuous
pump operation and eventual pump failure due to almost total dewatering of the well and
exposure of the pump to air. Pump failure most likely resulted from overheating due to lack of
ubmer ion of the pump beneath a ufficient column of water. Overheating, which is expected to
have caused substantial volatilization of chloroform and a consequent reduction in chloroform
within the groundwater sampled in the well, is the likely cause of the reduction in reported TW 4-
20 chloroform from 14,300 µg/L last quarter to 5,800 µg/L this quarter.
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased lightly from 55 µg/L to 53.8 µg/L, and remained outside the plume.
TW4-8 is located immediately east of chloroform pumping well MW-4, where chloroform was
detected at a concentration of 1,250 µg/L. Although tbe plume bot1ndary 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 the fourth quarter of 2019. The
occurrence of elevated chloroform at TW4-8 is likely related to its location along the eastern
plume boundary immediately east of pumping well MW-4. Changes in the plume boundary near
TW 4-8 are expected to result from changes in pumping and reduced dilution resulting from
cessation of water delivery to the northern wildlife pond . Chloroform at TW4-8 i 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 (2.9 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
slightly from approximately 3 µg/L to 2.9 µg/L and chloroform at TW4-27 remained at
approximately 8 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 652 µg/L to 686 µg/L, and
chloroform at TW4-30, located immediately cross-to downgradient of TW4-29, increased from
approximately 53 µg/L to approximately 65 µg/L. Concentration trends at the e wells are
generally consi tent with ongoing, but low, 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 65 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 5 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
36
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 94 µg/L to 90 µg/L. CWoroform at TW4-33 i bounded to
tbe north by TW4-14 (2.9 µg/), to the east by TW4-27 (app.roximateJy 8 µg/L) and to the we t
by TW4-6 (approximately 5 µg/L) and TW4-23 non-detect). Increa e 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 well witbjn the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for a slight
expansion near TW4-9 and TW4-16 and a slight contraction near TW4-24. The chloroform
concentration decrease at TW4-24, from approximately 62 µg/L to 49 µg/L, hifted the plume
boundary to the west away from TW4-24. The concentration increases at TW4-9 (from
approximately 49 µg/L to 55 µg/L); and at TW4-16 (from approximateJy 113 µg/L to 141 µg/L
shifted the plume boundary slightly to the ea t and southwest re pectively. Similar to last
quarter, due primarily to decrea e. in concentrations at TW4-6 and TW4-33, the kriging
algorithm has 'pinched off the southern extremity of the plume.
TW4-9 remained outside the plume this quarter. Chloroform concentrations at TW4-9 increased
from approximately 49 µg/L to 55 µg/L shifting the plume boundary lightly to the e t toward
TW4-38 (non-detect). TW4-9 wa incorporated into the plume from th.e fir t quarter of 2016
until the fir t quarter of 2019 due to increa ed concentrations atu-ibutable to reduced recharge
(and dilution) from the northern wildlife ponds. However, except for the fourth quarter of 2014,
TW4-9 was out ide the plume prior to the fir ·t quarter of 2016. TW4-38 was installed to the east-
southeast of TW 4-9 to serve as a bounding well when concentrations at TW 4-9 exceeded 70
µg/L.
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). Sub equent to the fir t quarter of 20J4, gene.rally
increased concentrations at TW4-6 and TW4-16 (both of which were within the chloroform
plume in the past), cau ·ed the plume boundary to migrate to the southwe t and temporarily re-
incorporate both wells. Increased concentration at the e well 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, concentration 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 out ide the plume~ whereas a decreasing trend in
chloroform concentration at TW 4-6 (since the third quarter of 2015) bas once again taken TW 4-
6 outside the plume. This quarter TW4-16 and TW4-6 remain within and outside the plume,
respectively.
37
The decreasing trend in chloroform concentration at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 ince the third qllarter of 2016 ugge t that TW4-
4 pumping has arrested chloroform migration between TW4-4 and TW4-6 and that the increased
chloroform at TW4-26 results from a remnant of the plume that continues to migrate outh
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 boundarie , continued operation of the nitrate pumping system
is expected to enJ1ance capture associated with the chloroform pumping system. Furthermore, the
addition of chloroform pumping wells TW4-1, TW4-2, TW4-ll, 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 third 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 well , regardles of any short-term fluctuation in concentrations
detected at the wells helps to reduce downgradient chloroform migration by removing
chloroform ma s and reducing hydraulic gradient , thereby allowing natural attenuation to be
more effective. Continued operation of chloroform pumping well TW4-4, augmented by
pumping at adjacent well TW4-41, is recommended to improve capture of chloroform to the
extent practical in the outhern portion of the plume. The overall decrea e in chJoroform
concentration at TW4-6 from l,000 µg/L in the fir t quarter of 2010 to 10.3 µg/L in the econd
quarter of 2014 i likely related to pumping at TW4-4. The decrease in the long-term rate of
water level rise at TW4-6 once TW4-4 pumping began, which suggests that TW4-6 i within the
hydraulic influence of TW4-4, is also consistent with the decrea e 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-l , TW4-2, TW4-11, TW4-21,
TW4-37, TW4-39, TW4-40 and TW4-41 is also recommended becau ·e pumping these wells has
increased overall capture and improved chloroform mass removal.
Furthermore, because of the influence of TW4-4 pumping (augmented by TW4-4J pumping
since the second quarter of 2018), and by analogy with the concentration decrea e 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,
concentration at TW4-33 appear to be relatively . table to decreasing, while, ince the third
quarter of 2014, concentrations at TW4-29 appear to be on an upward trend. The relatively stable
chloroform at TW4-33 and secent increa e in concentration at TW4-29 suggest that chloroform
migration bas 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
38
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 the e
decreasing trends in water levels and to augment the expected reduction in concentration in the
distal end of the plume. Continued evaluation of trend. at TW4-29 and TW4-33 will be provided
in subsequent quarters.
EFRI and its consultants have raised the issues and potential effect associated with cessation of
water delivery to the northern wildlife pond 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 gradient 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 concentration
within the plumes while reducing hydraulic gr tdient and rates of plume migration. Generally
increased chloroform concentrations at TW4-6 ( ince the fu" t 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 TW4-6 and TW4-8 have been trending downward ince the first quarter of
2015). As discussed above, increased concentration 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 i expected o be beneficial even though it is
also expected to re ult in higher concentration · that will per i t until continued ma s reduction
via pumping and natural attenuation ultimately reduce concentrations. Temporary increases in
chloroform concentrations are judged le s 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 ha provided to the Director an electronic copy of the laboratory results for groundwater
quality monitoring conducted under the chloroform contaminant inve. tigation during the quarter
in Comma Separated Value format. A copy of the transmittal e-mail is included under Tab M.
39
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc.
Energy Fuels Resources (USA) Inc.
By:
' Scott Bakken DigitallysignedbyScottBakken
Date: 2020.08.14 12:05: 13 -06'00'
Scott A. Bakken Date
Senior Director Regulatory Affairs
40
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 inti ,rmation submitted. Based on my inquiry of the
person or persons who manage the sy tern, or those person directly Jesponsible for gathering the
information the information submitted is, to the best of my .knowledge and belief, true accw-ate,
and complete. I am aware that there are significant penalties for submitting false information
including the possibility of fine and imprisonment for knowing violations.
SC Ott Ba kke n• .. Digit~lly signed by :co~t Bak~en,
; . Date. 2020.08.14 12.05.42 ·06 00
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
41
Tables
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 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
Table 1: Summary of Well Sampling for the Period
Well Sample Date Date of Lab Report
MW-04 5/27/2020 6/12/2020
TW4-0l 5/27/2020 6/12/2020
TW4-02 5/27/2020 6/12/2020
TW4-03 6/10/2020 6/29/2020
TW4-03R 6/9/2020 6/29/2020
TW4-04 5/27/2020 6/12/2020
TW4-05 6/11/2020 6/29/2020
TW4-06 6/11/2020 6/29/2020
TW4-07 6/12/2020 6/29/2020
TW4-08 6/12/2020 6/29/2020
TW4-09 6/12/2020 6/29/2020
TW4-09R 6/11/2020 6/29/2020
TW4-IO 6/12/2020 6/29/2020
TW4-ll 5/27/2020 6/12/2020
TW4-12 6/10/2020 6/29/2020
TW4-13 6/11/2020 6/29/2020
TW4-14 6/11/2020 6/29/2020
MW-26 5/27/2020 6/12/2020
TW4-16 6/12/2020 6/29/2020
MW-32 6/12/2020 6/29/2020
TW4-18 6/12/2020 6/29/2020
TW4-19 5/27/2020 6/12/2020
TW4-20 5/27/2020 6/12/2020
TW4-21 5/27/2020 6/12/2020
TW4-22 5/27/2020 6/12/2020
TW4-23 6/11/2020 6/29/2020
TW4-24 5/27/2020 6/12/2020
TW4-25 5/27/2020 6/12/2020
TW4-26 6/12/2020 6/29/2020
TW4-27 6/11/2020 6/29/2020
TW4-28 6/10/2020 6/29/2020
TW4-29 6/12/2020 6/29/2020
TW4-30 6/12/2020 6/29/2020
TW4-3J 6/11/2020 6/29/2020
TW4-32 6/10/2020 6/29/2020
TW4-33 6/12/2020 6/29/2020
TW4-34 6/11/2020 6/29/2020
TW4-35 6/11/2020 6/29/2020
TW4-36 6/11/2020 6/29/2020
TW4-37 5/27/2020 6/12/2020
TW4-38 6/11/2020 6/29/2020
TW4-39 5/27/2020 6/12/2020
TW4-40 5/27/2020 6/12/2020
TW4-41 5/27/2020 6/12/2020
TW4-42 6/10/2020 6/29/2020
TW4-60 5/27/2020 6/12/2020
TW4-65 6/10/2020 6/29/2020
TW4-70 6/12/2020 6/29/2020
TW4-75 6/12/2020 6/29/2020
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
TW4-09 and TW4-75 is a duplicate ofTW4-07.
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.
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 chloroform pumping well EB installed February 2018
TW4-19 perched chloroform or EB nitrate pumping well
MW-38
-¢-perched monitoring well installed
February 2018
MW-5 • perched monitoring well
TW4-12
0 temporary perched monitoring well
TWN-7 temporary perched nitrate monitoring ~ well
PIEZ-1 perched piezometer -1
RUIN SPRING
c!, seep or spring
HYDRO
GEO
CHEM,INC.
WHITE MESA SITE PLAN SHOWING LOCATIONS OF
PERCHED WELLS AND PIEZOMETERS
APPROVED DATE REFERENCE
H:/718000/aug19/Uwelloc1219.srf
FIGURE A-1
TabB
Order of Sampling and Field Data Worksheets
Order of Contamination for 2nd Quarter 2020 Chlorofonn Purging Event
Chloroform
Well Sample time Levels Rinsate date/time
TW4-03 Ut$'21) ~O"lfND 0 "1 '.:.5
TW4-42<,/10/zo ffl5 ND otS'.:l.
TW4-28 (,/Jo/@ ~ ND uZ05
TW4-32 bllo/,io O 8 J;l ND
TW4-12 t.J1ofz.D u 8.;;tl ND
TW4-13 C,111/2,.C'.> oc:,o~ ND
TW4-36 C)11/2:Q 0(:.10 ND
TW4-3l 1.:,/ll/',l..O QOO ND
TW4-34 /,,/11.'u; Q G.'2.3 ND
TW4-35 {,/Hf').f) Ob3b ND
TW4-23 Mll/lO D~'jg ND
-MW-32 r./12~ 11'10 ND
TW4-38 C,/ l/l;i.p Qc,5~ ND
TW4-25 S /'1.1/lo 0'\15 ND
TW4-14 (,/11/'J.O D101\ 2.98
TW4-06 t,(U(J.,c 011a 6.93
TW4-27 {,/11/'-0 t,"12'l 8.04
TW4-05 f,/n/a,Q Q"1'10 14.8
~ TW4-09 c,/12.1.2.o O'z2$ 48.9
TW4-30 C./1112,T> o'-'lg 53.1
TW4-08 r,./12/3-0 O b5& 55
TW4-18 6/ru:;i.p CtfO 57
TW4-24 5('l1(1b oq,S 61.7
TW4-33 (,/11./J.p o72"l 93.7
TW4-16 (,/12/20 0735 113
TW4-40 ~}21/')J) 11'\5 364
TW4-29 (,,/12/20 DJ% 652
TW4-07 'l'WD 0300 746
TW4-I0 ,,/,'l./:i.o N<l.:2. 798
TW4-39 'Sfl.1/)JJ IOC>:2... 812
TW4-21 Sf2.7(1P O't0.5 844
TW4-26 G/11/?..0 0 g;;..3 1090
TW4-04 Sh1 /1.0 t2,2.'2. 1100
MW-26 5/:11/2,0 101 0 1100
TW4-0I 5/1.1/'J-O ll.05 1190
TW4-41 5/21/')...() 12.l5 1200
MW-04 5/27 (ii) 1p 1 1230
TW4-02 51:J.,1 /:,.o IQ1g 1880
TW4-l 1 S/z"I /J.D !010 2990
TW4-22 ':,/2.1/1'0 O"l'.)5 3910
TW4-19 5/17110 08'i5 8720
TW4-37 51.1.1 /10 0'\~5 12000
TW4-20 5'11/).0 MS2. 14300
TW4-60 D.I. Blank S/J,.7 /:;.,o
TW4-65 Duplicate ic,/1Q_/'l.t)
TW4-70 Duplicate L(,.11./:W
TW4-75 Duplicate (,, I ['l:,/)...()
Comments:
1310
0135
0('...2,5
bl,00
Pe>st DI b / 12 / ).,O 1.0 O'f l.5
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 a O ow5· 120 ·--n,Jl~ -01:if!, _ 0 b) /20.J.: 0 I
92.5
125
137.5
112.5 Cont. Pumping
87.9
146.3
86 Cont. Pumping
93.5
120
111
120 Cont. Pumping
121 Cont. Pumping
86
112 Cont. Pumping
122.5 Cont. Pumping
110 Cont. Pumping
97.75 Cont. Pumping
124 Cont. Pumping
120 Cont. Pumping
100 Cont. Pumping
113.5 Cont. Pumping
125 Cont. Pumping
112 Cont. Pumping
106 Cont. Pumping
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
r' White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-04 Sampling Program Chloroform Monitoring
Field Sample ID MW-04 05272020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 10:36
Sample Date & Time 5/27/2020 10:37 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-02
Casing Volume (gal) 14.49
Calculated Casing Volumes Purge Duration O
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) 84.10
Conductivity Dissolved
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 10:36 1877 7.35 15.70 338 0 40.3
Pumping Rate Calculations
[volume of water purged O Flow Rate (Q = S/60) (gal/min) 4.0
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 90.24 Number of casing_ Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Anal'i!_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: I Arrived on site at 1033. Samples collected at 1037. Water was clear. Left site at 1039.
Signature of Field Technician
~l(.(...l'Ll'l.r~-
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan --e~·-' -. I ~ ~· /r ·_l,··. ~y~ White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-01 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-01 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 12:04
Sample Date & Time 5/27/2020 12:05 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 27
Purging Method 2 Casings Previous Well Sampled MW-04
Casing Volume (gal) 12.75
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) 91.77
Conductivity Dissolved
Date/Time Gallons Purged (um hos/cm) pH (pH Units) Temp (deg C) Redox(mV) Turbidity (NTU) Oxygen(%) Before/After
5/27/2020 12:04 2306 7.38 17.80 370 0 71.0
Pumping Rate Calculations
[volume of water p_urged (} Flow Rate (Q = S/60) (gal/min) 13.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to ~Witte_!.Jfeet) 108.35 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sameles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-mLHDPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 120D. Samples collected at 1205. Water was clear. Left site at 1207.
Signature of Field Technician
-:3 •Lo<-
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-02 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-02 05272020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 10:27
Sample Date & Time 5/27/2020 10:28 lsameler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-11
Casing Volume (gal) 19.85
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) 90.49
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
5/27/2020 10:27 3728 7.26 16.80 327 0 80.0
l~l_lJme of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 14.00
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 116.95 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laborator}'_
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: I Arrived on site at 1024. Samples collected at 1028. Water was clear. Left site at 1030.
Signature of Field Technician
~,,.,..-Al....._.,.,-/.,,~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~
--~1 -·· -,r
''---l /• . ~y~ White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03 Sampling Program Chloroform Monitoring
Field Sample ID TW4-03 06102020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/9/2020 12:31
Sample Date & Time 6/10/2020 7:35 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-03R
Casing Volume (gal) 50.18
Calculated Casing Volumes Purge Duration (min) 9.12
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) 63.44
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/9/2020 12:37
6/10/2020 7:34
6/10/2020 7:36
!Volume of water purged (gals)
[Final Depth to ~ater_(feet)
69.66
Name of Certified Analytical Laboratory
AWSL
Analytical Sameles Information
Type of Sample/Analysis
VOCs-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
1830
1817
1820
69.66
138.15
Sample
Collected? Matrix
y WATER
y WATER
y WATER
6.80 14.92 479 5.0 71.5
6.00 14.98
6.05 15.00
Pumping Rate Calculations
Flow Rate (Q = S/60} (gal/min)
Time to evacuate 2 Casing Volumes (min)
Number of casing Volumes
Volume, if well evacuated to dryness (gals)
Container Preservative
Number Type Sample Filtered? Type
3 40mlVOA u HCI (pH<2), 4 Deg C
1 500-ml Poly u None
1 250-ml HOPE u H2504 (pH<2), 4 Deg C
Arrived on site at 1227. Purge began at 1231. Purged well for a total of 6 minutes and 20 seconds. Purged well dry. Purge ended at 1237. Water was clear. Left site at 1240.
Arrived on site at 0731. De_eth to water was 63.75. Samples bailed and collected at 0735. Left site at 0738.
Signature of Field Technician
..:3cU'~M~
Before
After
11.00
6.33
1.38
69.66
Added?
y
N
y
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03R Sampling Pro_g_ram
Field Sample ID TW4-03R 06092020 Sampli_ng Event 2020 Q2 Chloroform
Purge Date & Time
Sample Date & Time 6/9/2020 10:00 [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 Casing_ Diameter ()
Specific Conductance () Depth t()_ W_c1ter Before Purgtng (ft)
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp {deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/9/2020 9:59 133.00 0 6.21 17.93 481 0 51.3
[volume of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/601 0
Time to evacuate 2 Casing Volumes () I Final Dep_th to Water (fee_!) Number of casing Volumes
Volume, if well evacuated to dryness ()
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 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-mlHDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Signature of Field Technician
~ ' ' ----:Ju.~· ~
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 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 12:19
Sample Date & Time 5/27/2020 12:22 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 27
Purging Method 2 Casings Previous Well Sampled TW4-41
Casing Volume O
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) 76.41
Dissolved
Date/Time Gallons Purged Conductivity (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 12:21 2369 7.43 17.29 343 0 103.0
[Ve>lume ~f water_purged Q
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 14.50
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 94.34 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?
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: I Arrived on site at 1218. Samples collected at 1222. Left site at 1224. Water was clear.
Signature of Field Technician
----... . ',: / --.____)u,-,.~~:46-;:,
Groundwater Discharge Permit ~..... ,._ .--~-· ·----E!· /;.. . . . .· . .• Y,F;IL.ee:, S
Groundwater Monitoring Quality Assurance Plan
__.....· ,. ~.-··· .·~
. ~ '
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-05 Sameling Program
Field Sample ID TW4-05 06112020 Sampling Event
Purge Date & Time 6/10/2020 15:04
Sample Date & Time 6/11/2020 7:40 [sameler
Purging Equipment Pump Weather Conditions
Pump Type Grundfos External Ambient Temperature (C)
Purging Method 2 Casings Previous Well Sampled
Casing Volume (gal) 33.28
Calculated Casing Volumes Purge Duration (min) 6.05
pH Buffer 7.0 7.0 Well Depth (ft)
pH Buffer 4.0 4.0 Well Casing Diameter (in)
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft)
Conduct1v1ty
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV)
6/10/2020 15:09 55.00 1562 6.66 15.61 395
6/10/2020 15:10 66.00 1557 6.66 15.60 396
6/10/2020 15:11 77.00 1537 6.66 15.60 396
6/10/2020 15:12 88.00 1526 6.66 15.59 397
Pumping Rate Calculations
[volume of watE!_I' purged (gals) 88.00 Flow Rate (Q = S/60) (gal/min)
Time to evacuate 2 Casing Volumes (min)
[ Final Depth to Water (feet) 73.42 Number of casing Volumes
Volume, if well evacuated to dryness()
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered?
VOCs-Chloroform y WATER 3 40ml VOA u
Chloride y WATER 1 500-ml Poly u
Nitrate/nitrite as N y WATER 1 250-ml HDPE u
Comments:
Arrived on site at 1500. Purge began at 1504. Purged well for a total of 8 minutes. Purge ended at 1512. Water was clear. Left site at 1514.
Arrived on site at 0736. Depth to water was 71 .14. Samples bailed and collected at 0740. Left site at 0742.
Signature of Field Technician
.:3~-rr;;.~
Chloroform Monitoring
2020 Q2 Chloroform
TH/DL
Sunny
25
TW4-27
121.85
4
70.88
Dissolved
Turbidity (NTU) Oxygen(%) Before/ After
2.1 64.3
2.0 64.3
1.9 63.4
1.9 63.0
11.00
8.00
2.00
0
Preservative
Type Added?
HCI (pH<2), 4 Deg C y
None N
H2S04 (pH<2), 4 Deg C y
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e~·-. ~I ,· ,·· . ' ;'' • ( l ~ . . ./'.. .• El'tJER/IG'Y~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-06 Sameling Program Chloroform Monitoring
Field Sample ID TW4-06 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 14:02
Sample Date & Time 6/11/2020 7:18 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-14
Casing Volume (gal) 14.01
Calculated Casing Volumes Purge Duration (min) 2.54
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) 78.14
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/10/2020 14:03 14.66 3909 7.00 15.94 358 33.0 60.0
6/11/2020 7:17 3936 6.61 12.25 Before
6/11/2020 7:19 3940 6.63 12.30 After
[volumE!_of water p1.1rged (gals) 14.66
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Trme to evacuate 2 Casing Volumes (min) 1.33
!Final Depth to Water (feet) 96.92 Number of casing Volumes 1.04
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Analytical Laboratory
AWSL
Analytical Sam.e_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 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:
Arrivedon site at 1358-:-Purge began at 1402. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Water was a little murky. Purge ended at 1403. Left site at 1406.
Arrived on site at 0714. Depth to water was 78.65. Samples bailed and collected at 0718. Left site at 0720.
Signature of Field Technician
~=~.,t-A-a'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-07 Sampling_ Pr_ogram Chloroform Monitoring
Field Sample ID TW4-07 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 13:20
Sample Date & Time 6/12/2020 8:00 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 28
Purging Method 2 Casings Previous Well Sampled TW4-29
Casing Volume (gal) 25.53
Calculated Casing Volumes Purge Duration (min) 4.64
pH Buffer 7.0 7.0 Well Depth (ft) 121.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 81.89
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 13:24 49.50 1670 6.54 15.17 356 6.3 48.0
6/12/2020 7:59 1669 7.22 15.13 Before
6/12/2020 8:02 1667 7.21 15.10 After
!Volume of water purged (gals)
Pumping_ Rate Calculations
49.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.50 I Final Depth to Water (feet) 118.95 Number of casing Volumes 1.93
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 1316. Purge began at 1320. Purged well for a total of 4 minutes and 30 seconds. Purged well dry. Purge ended at 1324. Water was clear. Left site at 1327.
Arrived on site at 0755. Depth to water was 84.66. Samples bailed and collected at 0800. Left site at 0803.
Signature of Field Technician
~ur~M -a;
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-08 Sampling_ Program
Field Sample ID TW4-08 06122020 Samplin_g Event
Purge Date & Time 6/11/2020 10:03
Sample Date & Time 6/12/2020 6:58 [sampler
Purging Equipment Pump Weather Conditions
Pump Type Grundfos External Ambient Temperature (C)
Purging Method 2 Casings Previous Well Sampled
Casing Volume (gal) 26.18
Calculated Casing Volumes Purge Duration (min) 4.76
pH Buffer 7.0 7.0 Well Depth (ft)
pH Buffer 4.0 4.0 Well Casing Diameter (in)
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft)
Conductivity
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV)
6/11/2020 10:05 22.00 4954 6.70 15.21 413
6/11/2020 10:06 33.00 4946 6.70 15.19 414
6/11/2020 10:07 44.00 4946 6.69 15.19 416
6/11/2020 10:08 55.00 4943 6.67 15.18 416
[v~lume of water purged (gals) 55.00
Pumpin_g_ Rate Calculations
Flow Rate (Q = S/60) (gal/min)
Time to evacuate 2 Casing Volumes (min)
[Final Depth to Water (feet) 95.45 Number of casing Volumes
Volume, if well evacuated to dryness()
Name of Certified Analytical Laboratory_
AWSL
Anal~ical Samples Information
Sample Container
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered?
VOCs-Ch loroform y WATER 3 40ml VOA u
Chloride y WATER 1 500-ml Poly u
Nitrate/nitrite as N y WATER 1 250-ml HDPE u
Comments:
Arrived on site at 1000. Purge began at 1003. Purged well for a total of 5 minutes. Purge ended at 1008. Water was clear. Left site at 1011 .
Arrived on site at 0655. Depth to water was 86.30. Samples bailed and collected at 0658. Left site at 0700.
Signature of Field Technician
..::) .. ,~.,~~
Chloroform Monitoring
2020 Q2 Chloroform
TH/DL
Sunny
22
TW4-30
126.20
4
86.10
Dissolved
Turbidity (NTU) Oxygen(%) Before/ After
0 28.4
0 26.0
0 25.0
0 25.0
11.00
5.00
2.00
0
Preservative
Type Added?
HCI (pH<2), 4 Deg C y
None N
H2S04 (pH<2), 4 Deg C y
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 06122020 Sami>_lin_g_ Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 9:00
Sample Date & Time 6/12/2020 6:25 jsampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 19
Purging Method 2 Casings Previous Well Sampled TW4-09R
Casing Volume (gal) 33.38
Calculated Casing Volumes Purge Duration (min) 6.06
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) 68.98
Conductivity Dissolved
Date!Time Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 9:05 55.00 2489 6.73 15.19 358 23.5 11.5
6/11/2020 9:06 66.00 2484 6.73 15.17 357 25.0 10.3
6/11/2020 9:07 77.00 2483 6.73 15.15 357 26.0 10.0
6/11/2020 9:08 88.00 2479 6.72 15.14 356 27.0 9.8
Pumpi'!_g Rate Calculations
~lume of water_purg_ed (gals) 88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
jFinal_!)epth to Water (feet) 85.20 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical ~mples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Ch loroform 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 0857. Purge began at 0900. Purged well for a total of 8 minutes. Purge ended at 0908. Water was a little murky. Left site at 0910.
Arrived on site at 0621 . Depth to water was 68.98. Same_les bailed and collected at 0625. Left site at 0630.
Signature of Field Technician
-:.3~-M-~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e~. ,' · l r ""-...,.. .. · .i'r . . ~. ___ . /•--. . ~y~~c;;
'. •"-~~ ,''
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-09R Sampling Program
Field Sample ID TW4-09R 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time
Sample Date & Time 6/11/2020 8:45 [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 ()
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
6/11/2020 8:44 133.00 6.0 6.70 20.83 314 0 71.0
[volullle of water purged()
Pumpi!!,g Rate Calculations
Flow Rate (Q = S/60L(1
[Final Depth to Water (feet)
Time to evacuate 2 Casing Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness()
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Ch loroform 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
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-10 Sampling Program Chloroform Monitoring
Field Sample ID TW4-10 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 13:50
Sample Date & Time 6/12/2020 8:12 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 30
Purging Method 2 Casings Previous Well Sampled TW4-07
Casing Volume (gal) 29.24
Calculated Casing Volumes Purge Duration (min) 5.31
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) 68.42
Conductivity Dissolved
Date/Time Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 13:53 38.50 3090 6.00 15.34 416 6.8 47.5
6/12/2020 8:11 2424 6.95 15.55
6/12/2020 8:13 2427 6.95 15.50
Pumping Rate Calculations
!Volume of waterp1.1rged (gals) 38.50 Flow Rate (Q = S/60) (gal/min)
Time to evacuate 2 Casing Volumes (min)
!Final Depth to Water (feet) 111.87 Number of casing Volumes
Volume, if well evacuated to dryness (gals)
Name of Certified Analytical Laboratory_
AWSL
Analyt_ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C
Chloride y WATER 1 500-ml Poly u None
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C
Comments:
Arrived on site at 1346. Purge began at 1350. Purged well for a total of 3 minutes and 30 seconds. Purged well dry. Purge ended at 1353. Water was clear. Left site at 1356.
Arrived on site at 0808. Deeth to water was 68.44. Samples bailed and collected at 0812. Left site at 0814.
Signature of Field Technician
..=:).,_.·w ... c ..... ./1~,
Before
After
11.00
3.50
1.31
38.50
Added?
y
N
y
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-ll 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 10:19
Sample Date & Time 5/27/2020 10:20 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled MW-26
Casing Volume (gal) 6.69
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 102.40
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 92.15
Conductivity Dissolved
Date/rime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 10:19 3721 7.27 16.01 282 0 65.0
jvolume of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 100.18 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sameles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 1015. Samples collected at 1020. Water was clear. Left site at 1022.
Signature of Field Technician
~=~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ----e ·~-. ..-....,.. -' ~' --_ _.
y•.· I
' /',· .r~Y~S
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-12 Sampling Program Chloroform Monitoring
Field Sample ID TW4-12 06102020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/9/2020 15:02
Sample Date & Time 6/10/2020 8:21 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-32
Casing Volume (gal) 31.59
Calculated Casing Volumes Purge Duration (min) 5.74
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) 54.82
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/9/2020 15:06 38.50 1320 6.60 15.26 451 1.0 62.5
6/10/2020 8:20 1397 7.23 15.12 Before
6/10/2020 8:22 1398 7.22 15.10 After
[volume of watE!! purged (gals) 38.50
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.50
[ Final Depth ~_Vi_ater (feet) 101.13 Number of casing Volumes 1.21
Volume, if well evacuated to dryness (gals) 38.50
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 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 1458. Purge began at 1502. Purged well for a total of 3 minutes and 30 seconds. Purged well dry. Purge ended at 1505. Water was clear. Left site at 1510.
Arrived on site at 0817. Depth to water was 54.95_._ Samples bailed and collected at 0821 . Left site at 0823.
Signature of Field Technician
~.,_,vv~-Md~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e····~ . -"·· re;-:'-.,~ ~Y~
__ ,T l
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-13 Sampling Program Chloroform Monitoring
Field Sample ID TW4-13 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 9:04
Sample Date & Time 6/11/2020 6:02 !same_ler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 16
Purging Method 2 Casings Previous Well Sampled TW4-12
Casing Volume (gal) 32.29
Calculated Casing Volumes Purge Duration (min) 5.87
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) 56.25
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/10/2020 9:07 40.33 1970 6.93 15.36 391 2.6 71.0
6/11/2020 6:01 2020 7.04 16.03 Before
6/11/2020 6:03 2010 7.02 16.00 Aher
lvol_!lme of W<!~r pu!_ged (gals) 40.33
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes {min) 3.66
!Final D~pth to Water (feet) 103.43 Number of casing Volumes 1.24
Volume, if well evacuated to dryness (gals) 40.33
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 0900. Purge began at 0904. Purged well for a total of 3 minutes and 40 seconds. Purged well dry. Purge ended at 0908. Water was clear. Left site at 0911 .
Arrived on site at 0558. Depth to water was 56.33. ~_amples bailed and collected at 0602. Left site at 0605.
Signature of Field Technician
--=:)w~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~ --.,....~ .· y . -s ~e·· ,//~ ~YF'L ·~ . ~ . '
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-14 Sampling Program Chloroform Monitoring
Field Sample ID TW4-14 06112020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 13:34
Sample Date & Time 6/11/2020 7:08 jsameler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-38
Casing Volume (gal) 11.35
Calculated Casing Volumes Purge Duration (min) 2.06
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) 77.71
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 13:35 13.75 5300 7.18 16.10 355 23.0 70.5
6/11/2020 7:07 5316 6.50 13.82 Before
6/11/2020 7:09 5313 6.53 13.80 After
Pumping Rate Calculations -
[volume of water purged (gals) 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) 92.98 Number of casing Volumes 1.21
Volume, if well evacuated to dryness (gals) 13.75
Name of Certified Analytical Laboratory
AWSL
Anal}'t_ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 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 1330. Purge began at 1334. Purged well for a total of 1 minute and 15 seconds. Purged well dry. Purge ended at 1335. Water was a little murky. Left site at 1337.
Arrived on site at 0704. Depth to water was 77.78. Same_!es bailed and collected at 0708. Left site at 0710.
Signature of Field Technician
--=3w'J'LA--·f7'{-z:?~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e -~·· ~ _j
.,..---.// • . Y~S ~ ._ 1 · ~ , '
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-26 Sampling Prt>gram Chloroform Monitoring
Field Sample ID MW-26 05272020 Sameling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 10:09
Sample Date & Time 5/27/2020 10:10 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-39
Casing Volume (gal) 28.13
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) 78.25
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp(deg C) Redox (mV) Turbidity (NTU) Oxygen{%) Before/After
5/27/2020 10:09 3440 7.19 16.01 304 0 20.5
[volume of water purgE?~Q
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 10.0
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 90.47 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laborat~ry
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: I Arrived on site at 1007. Samples collected at 1010. Water was clear. Left site at 1012.
Signature of Field Technician
~=~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-16 Sampling Program Chloroform Monitoring
Field Sample ID TW4-16 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 12:14
Sample Date & Time 6/12/2020 7:35 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 26
Purging Method 2 Casings Previous Well Sampled TW4-33
Casing Volume (gal) 48.87
Calculated Casing Volumes Purge Duration (min) 8.88
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) 72.75
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/11/2020 12:21 77.00 3701 6.41 15.04 417 7.8 22.0
6/11/2020 12:22 88.00 3715 6.42 15.04 415 6.0 20.0
6/11/2020 12:23 99.00 3683 6.44 15.04 410 6.5 19.0
6/11/2020 12:24 110.00 3709 6.44 15.03 395 6.4 18.S
[';.folume of v.,ater purged (gals) 110.00
PumpJl'lg Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 10.00
[Final Dep_th to Water (feet) 125.78 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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 121 O. Purge began at 1214. Purged well for a total of 1 O minutes. Purge ended at 1224. Water was clear. Left site at 1227.
Arrived on site at 0732. Depth to water was 72.85. Samples bailed and collected at 0735. Left site at 0738.
Signature of Field Technician
-2>-~~
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 06122020 Sam_eling Event 2020 Q2 Chloroform
Purge Date & Time 6/12/2020 6:40
Sample Date & Time 6/12/2020 11:40 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type QED External Ambient Temperature (C) 17
Purging Method 2 Casings Previous Well Sampled TW4-26
Casing Volume (gal) 32.22
Calculated Casing Volumes Purge Duration (min) 297.00
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) 81.25
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/12/2020 11:37 64.44 3767 6.75 15.98 248 100.0 44.0
6/12/2020 11:38 64.66 3722 6.74 15.15 235 102.0 41.0
6/12/2020 11:39 64.88 3735 6.68 15.28 230 104.5 40.0
6/12/2020 11:40 65.10 3729 6.66 15.06 227 106.0 39.0
[volume of water purged (gc1_ls}
Pumein_g_ Rate Calculations
65.10 Flow Rate (Q = S/60) (gal/min) .217
Time to evacuate 2 Casing Volumes (min) 300.00
[Final Depth to Water (feet} 86.85 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical ~boratory
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 H2504 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0636. Purge_began at 0640. Purged well for a total of 300 minutes. Purge ended and samples collected at 1140. Water was murky with little bubbles surfacing. Left site at 1145.
Signature of Field Technician
~w'-'1~-M-d'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
~
~-.~·r'./ y . . . .... · .;.,1"'1·-•
'< , . ---~-:z: S' ---'. ~ ··~ ... . _i','
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-18 Sameling Program Chloroform Monitoring
Field Sample ID TW4-18 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 11:08
Sample Date & Time 6/12/2020 7:10 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-08
Casing Volume (gal) 42.30
Calculated Casing Volumes Purge Duration (min) 7.69
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) 72.12
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/11/2020 11:14 66.00 1990 6.23 15.65 431 15.8 24.0
6/11/2020 11:15 77.00 1965 6.23 15.65 431 16.1 22.0
6/11/2020 11:16 88.00 1930 6.23 15.65 430 16.2 20.1
6/11/2020 11:17 99.00 1890 6.23 15.65 430 16.1 21.0
Pumping Rate Calculations
[volume of water purged (gals) 99.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 9.00
[Ei_nal Del)th to Water (feet) 72.40 Number of casing Volumes 2.00
Volume, it well evacuated to dryness () 0
Name of Certified Analytica!!-aboratory
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 1105. Purge began at 1108. Purged well for a total of 9 minutes. Purge ended at 1117. Water was mostly clear. Left site at 1120.
Arrived on site at 0707. Depth to water was 72.08. Samples bailed and collected at 0710. Left site at 0712.
Signature of Field Technician
--.... ''//!/ -.____}a_,,""!_sv_,.;,c..-,M ~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-19 Sampling Program Chloroform Monitoring
Field Sample ID TW4-19 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 8:44
Sample Date & Time 5/27/2020 8:45 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 18
Purging Method 2 Casings Previous Well Sampled N/A
Casing Volume (gal) 33.63
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) 75.35
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 8:44 2501 6.51 16.36 391 2.0 30.0
[volume _of water purged Q
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 90.20 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?
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-mLHDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 0841 . Sal'l'l~les collected at 0845. Water was clear. Left site at 0849.
Signature of Field Technician
~~· ~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-20 Sampling Program Chloroform Monitoring
Field Sample ID TW4-20 05272020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:51
Sample Date & Time 5/27/2020 9:52 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-37
Casing Volume (gal) 17.20
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) 79.55
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 9:51 3769 6.90 17.20 318 4.0 24.6
Pumping Rate Calculations
[volume <>f water eurg_ed () Flow Rate (Q = S/60) (gal/min) 4.0
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 88.55 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived_ on site at 0948. Samples collect~d at 0952. Water was mostly clear. Left site at 0954.
Signature of Field Technician
-.:3=-vu~ve'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-21 Sampling Pro_g_ram Chloroform Monitoring
Field Sample ID TW4-21 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:02
Sample Date & Time 5/27/2020 9:05 !sampler TH/OL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 19
Purging Method 2 Casings Previous Well Sampled TW4-19
Casing Volume (gal) 29.24
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 118.80
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.02
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 9:04 2982 7.01 16.75 286 0 33.5
Pumping_ Rate Calculations -
[volume of water purged() Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 79.33 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sam1>_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 HDPE u H2504 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 0900. Samples collected at 0905. Water was clear. Left site at 0908.
Signature of Field Technician
~w~~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-22 Sampling Program Chloroform Monitoring
Field Sample ID TW4-22 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:34
Sample Date & Time 5/27/2020 9:35 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature {C) 22
Purging Method 2 Casings Previous Well Sampled TW4-24
Casing Volume (gal) 27.29
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 114.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 72.90
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 9:34 5326 7.24 16.48 348 0 90.3
Pumping Rate Calculations
[volume of water purged () Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes {)
[Final Depth to Water (feet) 105.64 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Labo!~toiy_
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 0931 . Samples collected at 0935. Water was clear. Left site at 0937.
Signature of Field Technician
~w~?7"~
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 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 12:23
Sample Date & Time 6/11/2020 6:48 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 22
Purging Method 2 Casings Previous Well Sampled TW4-35
Casing Volume (gal) 27.19
Calculated Casing Volumes Purge Duration (min) 4.94
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) 74.75
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/10/2020 12:28 55.00 3531 6.59 14.83 249 78.0 27.3
6/10/2020 12:29 66.00 3510 6.60 14.83 252 71.0 29.7
6/10/2020 12:30 77.00 3516 6.61 14.81 252 71.0 31.0
6/10/2020 12:31 88.00 3515 6.61 14.82 252 70.2 30.0
Pumping Rate Calculations
!volume of__!,later purged (gals) 88.00 Flow Rate (Q = S/60) {gal/min) 11.00
Time to evacuate 2 Casing Volumes {min) 8.00
[ Final Depth to Water (feet) 95.34 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
AnalY:tical ~~!l'ples 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 1219. Purge began at 1223. Purged well for a total of 8 minutes. Purge ended at 1231. Water has an orange coloration. Left site at 1233.
Arrived on site at 0645. Dee_th to water was 74.85. Samples bailed and collected at 0648. Left site at 0650.
Signature of Field Technician
~UJ~-r/L.,,~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-24 Sampling Program Chloroform Monitoring
Field Sample ID TW4-24 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:24
Sample Date & Time 5/27/2020 9:25 jsameler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled TW4-25
Casing Volume (gal) 28.66
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) 70.90
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 9:24 7951 7.08 16.00 347 25.0 19.4
Pumping Rate Calculations
[volume of water purged O Flow Rate (Q = S/60) (gal/min) 17.00
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) 78.23 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Anal~~c:_al 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 0920. Samples collected at 0925. Water was clear but had little bubbles surfacing. Left site at 0927.
Signature of Field Technician
~~,~-Md~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-25 Sampling Program Chloroform Monitoring
Field Sample ID TW4-25_05272020 Sam_eling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:13
Sample Date & Time 5/27/2020 9:15 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled TW4-21
Casing Volume (gal) 43.62
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) 69.89
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
5/27/2020 9:14 2514 7.12 16.05 311 0 42.0
[volume of water purged()
Pumpin_g Rate Calculations
Flow Rate (Q = S/60) (gal/min) 12.6
Time to evacuate 2 Casing Volumes ()
§nal Depth to Water (fee!) 89.23 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 0910. Samples collected at 0915. Water was clear. Left site at 0917.
Signature of Field Technician
2)w-VV-7-hf-t734_,
~ ----~,--<r -_,._ ~y~--z:s ~'-,,
---' J
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)
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-26 Sampling Program Chloroform Monitoring
TW4-26 06122020 Sampling Event 2020 Q2 Chloroform
6/11/2020 14:20
6/12/2020 8:23 [same_ler TH/DL
Pump Weather Conditions Sunny
Grundfos External Ambient Temperature (C) 30
2 Casings Previous Well Sampled TW4-10
9.71
1.76
7.0 Well Depth (ft) 87.70
4.0 Well Casing Diameter (in) 4
1000 Depth to Water Before Purging (ft) 72.83
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 14:21 11.00 4728 6.70 16.21 402 12.5 68.0
6/12/2020 8:22 4665 6.88 15.37 Before
6/12/2020 8:24 4670 6.89 15.35 After
~ume_of water purg_ecj_lg_als)
Pum_e_ing Rate Calculations
11.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
[!:Jnal Depth to w_ater (feet) 85.53 Number of casing Volumes 1.13
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Anal}'tical 4boratory
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 1416. Purge began at 1420. Purged well for a total of 1 minute. Purged well dry. Water was clear. Purge ended at 1421 . Left site at 1423.
Arrived on site at 0819. Depth to water was 73.15. Samples bailed and collected at 0823. Left site at 0825.
Signature of Field Technician
~u,~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e-----Wf:\ -j . ,----• ' f ,· -.~'" ~···· ,"{ -•; y~
. l '/~
. . •----
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-27 Sampling Program Chloroform Monitoring
Field Sample ID TW4-27 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 14:37
Sample Date & Time 6/11/2020 7:29 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 25
Purging Method 2 Casings Previous Well Sampled TW4-06
Casing Volume (gal) 10.92
Calculated Casing Volumes Purge Duration (min) 1.98
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) 79.02
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 14:38 11.00 5088 7.31 16.10 366 17.8 69.0
6/11/2020 7:28 5028 6.90 12.10 Before
6/11/2020 7:30 5027 6.91 12.15 After
Pumping Rate Calculations
!volume of water purged (gals) 11.00 Flow Rate (0 = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
!Final D_eptti_ to Wat~(feet) 93.39 Number of casing Volumes 1.00
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analyt_ical 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. Purge ended at 1438. Purged well dry. Water was mostly clear. Left site at 1441 .
Arrived on site at 0725. Depth to water was 79.51 . Samples bailed and collected at 0729. Left site at 0731 .
Signature of Field Technician
..=3 ... r~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e. ~' -,,-·' ,--~ . . ,
.· y . ~s: '~ ~· ~
I ~·"j
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-28 Sampling Program Chloroform Monitoring
Field Sample ID TW4-28 06102020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/9/2020 13:39
Sample Date & Time 6/10/2020 8:05 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 24
Purging Method 2 Casings Previous Well Sampled TW4-42
Casing Volume (gal) 39.42
Calculated Casing Volumes Purge Duration (min) 7.16
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 (f 48.11
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/9/2020 13:43 47.66 1365 6.97 15.60 446 9.2 72.5
6/10/2020 8:04 1598 7.07 14.40 Before
6/10/2020 8:06 1597 7.07 14.38 After
Pumping Rate Calculations
[volume of water purged (gal!>) 47.66 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 47.66
[final Depth to Water (feet) 106.47 Number of casing Volumes 1.20
Volume, if well evacuated to dryness (gals) 47.66
Name of Certified Analytical Laboratoiy
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 1335. Purge began at 1339. Purged well for a total of 4 minutes and 20 seconds. Purged well dry. Purge ended at 1443. Water was mostly clear. Left site at 1446.
Arrived on site at 0800. Depth to water was 48.30. Samples bailed and collected at 0805. Left site at 0807.
Signature of Field Technician
~uAn~u4~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan -a·~-. F-:--j • I, . . r
(____ /, -,-~YFL-:ZS ' 1 '
. • c" ~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-29 Sampling Program Chloroform Monitoring
Field Sample ID TW4-29 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 12:54
Sample Date & Time 6/12/2020 7:46 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 27
Purging Method 2 Casings Previous Well Sampled TW4-16
Casing Volume (gal) 10.97
Calculated Casing Volumes Purge Duration (min) 1.99
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) 77.68
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 12:55 11.00 4070 6.65 16.21 412 9.1 62.0
6/12/2020 7:45 4040 7.15 15.73
6/12/2020 7:47 4042 7.14 15.70
Pumping Rate Calculations
[volume o~ water J)U1'9_~(gals) 11.00 Flow Rate (Q = S/60) (gal/min)
Time to evacuate 2 Casing Volumes (min)
[ Final Depth to Water (feet) 92.09 Number of casing Volumes
Volume, if well evacuated to dryness (gals)
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C
Chloride y WATER 1 500-mL Poly u None
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C
Comments:
Arrived on site at 1250. Purge began at 1254. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1255. Water was clear. Left site at 1258.
Arrived on site at 0742. Depth to water was 77.67. Samples bailed and collected at 0746. Left site at 0748.
Signature of Field Technician
~~-J-.r~~
Before
After
11.00
1.00
1.00
11.00
Added?
y
N
y
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-30 Sampling Program Chloroform Monitoring
Field Sample ID TW4-30 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 9:35
Sample Date & Time 6/12/2020 6:48 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 19
Purging Method 2 Casings Previous Well Sampled TW4-09
Casing Volume (gal) 11.96
Calculated Casing Volumes Purge Duration (min) 2.17
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) 75.16
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/11/2020 9:36 14.66 4669 5.70 15.72 405 27.7 40.4
6/12/2020 6:47 4047 5.63 15.93 Before
6/12/2020 6:49 4050 5.65 15.90 After
[volume of water pur_g~ (gals) 14.66
Pumping Rate Calculations
Flow Rate (Q = S/60) {gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.33
[Final Depth to Water (feet) 91.25 Number of casing Volumes 1.22
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2}, 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0932. Purge began at 0935. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 0936. Water was a little murky. Left site at 0938.
Arrived on site at 0644. Depth to water was 75.17. Samples bailed and collected at 0648. Left site at 0650.
Signature of Field Technician
~~d~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-31 Sampling Pr~g_ram Chloroform Monitoring
Field Sample ID TW4-31 06112020 Samp!ir1g Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 10:09
Sample Date & Time 6/11/2020 6:20 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 20
Purging Method 2 Casings Previous Well Sampled TW4-36
Casing Volume (gal) 20.17
Calculated Casing Volumes Purge Duration (min) 3.66
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) 76.58
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 10:11 22.00 4004 6.95 15.51 337 62.0 63.7
6/11/2020 6:19 4001 7.00 13.52 Before
6/11/2020 6:21 4003 7.00 13.55 After
[volume of_water purged (gals) 22.00
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 2.00
[ Final Dep_th to Water (feet) 105.42 Number of casing Volumes 1.09
Volume, if well evacuated to dryness (gals) 22.00
Name of Certified Analytical Laboratory
AWSL
Analytical San,ples 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 1005. Purge began at 1009. Purged well for a total of 2 minutes. Purged well dry. Purge ended at 1011. Water was murky. Left site at 1013.
Arrived on site at 0616. De_eth to water was 76.62. Samples bailed and collected at 0620. Left site at 0623.
Signature of Field Technician
.-==:)....,~r-7~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-32 Samplin_g__Program Chloroform Monitoring
Field Sample ID TW4-32 06102020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/9/2020 14:21
Sample Date & Time 6/10/2020 8:12 [sameler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-28
Casing Volume (gal) 38.54
Calculated Casing Volumes Purge Duration (min) 7.00
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) 55.61
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
6/9/2020 14:26 55.00 6377 4.27 14.99 479 9.0 28.0
6/9/2020 14:27 66.00 6399 4.28 14.98 479 10.0 30.0
6/9/2020 14:28 77.00 6407 4.28 14.98 479 10.0 31.0
6/9/2020 14:29 88.00 6391 4.28 15.00 480 11.0 32.0
Pumping Rate Calculations
[volume of water purged (gals) 88.00 Flow Rate (Q = S/60) (gal/min} 11.00
Time to evacuate 2 Casing Volumes (min} 8.00
[ Final Depth to Wa~!Jfeet) 84.50 Number of casing Volumes 2.00
Volume, if well evacuated to dryness (} 0
Name of Certified Analytical t___aboratory
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 1417. Purge began at 1421 . Purged well for a total of 8 minutes. Purge ended at 1429. Water was mostly clear. Pump and hose had salt like crystals on them when pulled. Left site
at 1433. Arrived on site at 0808. Depth to water was 55.§_9. Sam_p_les bailed and collected at 0812. Left site at 0814.
Signature of Field Technician
~u_,V,LA:-,-M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-33 SampJing Program Chloroform Monitoring
Field Sample ID TW4-33 06122020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/11/2020 11:48
Sample Date & Time 6/12/2020 7:24 [sc!_mpler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 26
Purging Method 2 Casings Previous Well Sampled TW4-18
Casing Volume (gal) 5.94
Calculated Casing Volumes Purge Duration (min) 1.08
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 (f1 77.13
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/11/2020 11:49 5.5 5008 6.43 17.45 422 19.8 59.0
6/12/2020 7:23 4417 6.77 15.77 Before
6/12/2020 7:2.5 4428 6.80 15.73 After
[volume of water purged (gals)
Pumping_ Rate Calculations
5.5 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.50
(Fina! Depth _t~ Water (feet) 84.10 Number of casing Volumes 0.92
Volume, if well evacuated to dryness (gals) 5.5
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 11 44. Purge began at 1148. Purged well for a total of 30 seconds. Purged well dry. Purge ended at 1149. Water was mostly clear. Left site at 11 51 .
Arrived on site at 0720. Deptl1 to water _1Nas 77.41 ._ Samples bailed and collected at 0724. Left site at 0727.
Signature of Field Technician
-2}'°~--M-«'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-34 Sampling_Prog_ram Chloroform Monitoring
Field Sample ID TW4-34 06112020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 10:41
Sample Date & Time 6/11/2020 6:28 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C 20
Purging Method 2 Casings Previous Well Sampled TW4-31
Casing Volume (gal) 12.97
Calculated Casing Volumes Purge Duration (min) 2.35
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 75.87
Conductivity Dissolved
Date/Time Gallons Purged (gal) (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 10:42 16.50 3499 6.94 15.54 337 11.0 65.0
6/11/2020 6:27 3462 7.17 13.66 Before
6/11/2020 6:29 3465 7.17 13.61 After
Pumping Rate Calculations
~ume of water purged (gal~ 16.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.50
~inal Depth to Water (feet) 93.51 Number of casing Volumes 1.27
Volume, if well evacuated to dryness (gals) 16.50
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 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 1037. Purge began at 1041. Purged well for a total of 1 minute and 30 seconds. Purged well dry. Purge ended at 1042. Water was clear. Left site at 1045.
Arrived on site at 0624. Depth to water was 75.90. Samples bailed and collected at 0628. Left site at 0630.
Signature of Field Technician
~«A,,~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-35 Sampling Pro.9.ram Chloroform Monitoring
Field Sample ID TW4-35_06112020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 11:54
Sample Date & Time 6/11/2020 6:36 I sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 21
Purging Method 2 Casings Previous Well Sampled TW4-34
Casing Volume (gal) 7.42
Calculated Casing Volumes Purge Duration (min) 1.34
pH Buffer 7.0 7.0 Well Depth (ft) 86.50
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 75.13
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 11:55 7.33 4414 7.01 17.45 364 13.1 70.0
6/11/2020 6:35 4331 6.94 12.20 Before
6/11/2020 6:37 4340 6.93 12.31 After
!volume of wat_E!_r purged (gal~)
Pumpin9_ Rate Calculations
7.33
-
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.66
[ Final D~pth to Water (~et) 84.48 Number of casing Volumes 0.98
Volume, if well evacuated to dryness (gals) 7.33
Name of Certified Analyti~I Laboratory
AWSL
Analytical Sam_eles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 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 1150. Purge began at 1154. Purged well for a total of 40 seconds. Purged well dry. Purge ended at 1155. Water was clear. Left site at 1157.
Arrived on site at 0632. Depth to water was 75.19. Samples bailed and collected at 0636. Left site at 0638.
Signature of Field Technician
~u,.,_,,~-1,{4~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e ·~~···. / ' {·,, I •
.,,_ ' Ii • --r~ ' //~ i ~Y~IFZS
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-36 Sampling Program Chloroform Monitoring
Field Sample ID TW4-36 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 9:37
Sample Date & Time 6/11/2020 6:10 ~ampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 18
Purging Method 2 Casings Previous Well Sampled TW4-13
Casing Volume (gal) 27.20
Calculated Casing Volumes Purge Duration (min) 4.94
pH Buffer 7.0 7.0 Well Depth (ft) 99.41
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromho.s) 1000 Depth to Water Before Purging (ft) 57.75
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 9:40 33.00 2435 6.75 15.35 245 18.0 52.0
6/11/2020 6:09 2404 6.87 13.59 Before
6/11/2020 6:11 2407 6.87 13.60 After
jvolume of water pinged (gals)
Pumping Rate Calculations
33.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.00
[ Final Depth to Water (feet) 97.22 Number of casing Volumes 1.21
Volume, if well evacuated to dryness (gals) 33.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 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 0933. Purge began at 0937~Purged~well for a 3 minutes. Purgeended at 0940. Purged well dry. Water was clear. Left site at 0943.
Arrived on site at 0606. Depth to water was 58.58. Sam.eles bailed and collected at 0610. Left site at 0613.
Signature of Field Technician
-2>"-'~M.~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-37 Sampli_11__g Program Chloroform Monitoring
Field Sample ID TW4-37 05272020 Sameling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 9:43
Sample Date & Time 5/27/2020 9:45 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casings Previous Well Sampled TW4-22
Casing Volume (gal) 24.87
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 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) 75.63
Conductivity Dissolved
Date/Time Gallons Purged (um hos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 9:44 4452 7.25 16.80 347 0 61.3
Pumping Rate Calculations
!volume of \Yater !)urged_() Flow Rate (0 = S/60) (gal/min) 18.00
nme to evacuate 2 Casing Volumes ()
!Final Dee_th to Water (feet) 84.29 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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 0940. Samples collected at 0945. Water was clear. Left site at 0947.
Signature of Field Technician
2)=~M.«~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~~ ... -i.' . /y--. . t .--
',I'*.· ,i-· ~Y~1FZS
. .. "J ~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-38 Sampling Program Chloroform Monitoring
Field Sample ID TW4-38 06112020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/10/2020 12:59
Sample Date & Time 6/11/2020 6:58 [sampler TH/DL
Purging Eq~iement Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 23
Purging Method 2 Casin~s Previous Well Sampled TW4-23
Casing Volume (gal) 35.91
Calculated Casing Volumes Purge Duration (min) 6.53 ..... _....,
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) 58.92
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/10/2020 13:03 44.00 1862 6.67 14.89 345 22.0 58.6
6/10/2020 13:04 55.00 1885 6.68 14.88 347 18.5 57.4
6/10/2020 13:05 66.00 1804 6.67 14.95 347 20.0 56.1
6/10/2020 13:06 77.00 1820 6.68 14.90 347 19.0 56.0
Pumping Rate Calculations
[volume of water purged (galsl 77.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 7.00
[Final Depth to Water (feet) 91.20 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical SaJ1!ples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1255. Purge began at 1259. Purged well for a total of 7 minutes. Purge ended at 1306. Water was a little murky. Left site at 1309.
Arrived on site at 0654. Depth to water was 59.12. Samples bailed and collected at 0658. Left site at 0700.
Signature of Field Technician
~w~-M~
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 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 10:01
Sample Date & Time 5/27/2020 10:02 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-20
Casing Volume (gal) 23.34
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) 84.99
Conductivity Dissolved
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
5/27/2020 10:01 2280 7.04 16.40 279 0 55.0
Pumping Rate Calculations
~~urt1e of water purged () Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to \Yater (feet) 98.15 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 0~58. Samples collected at 1002. Water was clear. Left site at 1004.
Signature of Field Technician
-2>a~M~
Groundwater Discharge Permit
~~· ~~~~y~ Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-40 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-40 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 12:44
Sample Date & Time 5/27/2020 12:45 !sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 28
Purging Method 2 Casings Previous Well Sampled TW4-04
Casing Volume (gal) 9.20
Calculated Casing Volumes Purge Duration O
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) 71.90
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 12:44 3977 7.33 17.20 319 0 79.5
!Volume of water purged 0
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 18.0
Time to evacuate 2 Casing Volumes ()
jFinal Depth to Water (feet) 77.54 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analyt~al Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 1241 . Samples collected at 1245. Water was clear. Left site at 1248.
Signature of Field Technician
~u.,~-M~
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 05272020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 5/27/2020 12:14
Sample Date & Time 5/27/2020 12:15 !Sampler TH/0.L
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 27
Purging Method 2 Casings Previous Well Sampled TW4-01
Casing Volume (gal) 13.01
Calculated Casing Volumes Purge Duration O
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} 88.89
Conductivity Dissolved
Date!Time Gallons Purged (um hos/cm} pH (pH Units) Temp (deg C} Redox (mV} Turbidity (NTU) Oxygen(%) Before/After
5/27/2020 12:14 2617 7.46 18.01 382 0 95.1
Pumping Rate Calculations -
@olume of ~ter purged_() Flow Rate (Q = S/60) (gal/min) 5.0
Time to evacuate 2 Casing Volumes ()
jFinal Depth to Water (feet) 93.54 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 HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on ~te at 1211_.__§~mples collected at 1215. Water was clear. Left site at 1217.
Signature of Field Technician
~=~Md~
Groundwater Discharge Permit
SF-:-· r --. 1· r · ~
.,.. .r , '.·· /l--.-... -~ ...
,, ,.,., -~~
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-42 Sampling Program Chloroform Monitoring
Field Sample ID TW4-42 06102020 Sampling Event 2020 Q2 Chloroform
Purge Date & Time 6/9/2020 13:04
Sample Date & Time 6/10/2020 7:52 [sam_eler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 24
Purging Method 2 Casings Previous Well Sampled TW4-03
Casing Volume (gal) 11.48
Calculated Casing Volumes Purge Duration (min) 2.08
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) 68.41
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
6/9/2020 13:05 13.75 3611 6.66 15.80 465 0 56.0
6/10/2020 7:51 3449 6.97 14.89 Before
6/10/2020 7:53 3451 6.98 14.88 After
~h.1_1!1e of water p_urged (gals)
Pumpin_g_ 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) 84.01 Number of casing Volumes 1.19
Volume, if well evacuated to dryness (gals) 13.75
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 1301 . Purge began at 1304. Purged well for a total of 1 minute and 15 seconds. Purged well dry. Purge ended at 1305. Water was clear. Left site at 1309.
Arrived on site at 0748. Depth to water was 68.78. Samples bailed and collected at 0752. Left site at 0754.
Signature of Field Technician
..:3~Md:.:f,
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-60 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-60 05272020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time 5/27/202013:09
Sample Date & Time 5/27/2020 13:10 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 28
Purging Method 2 Casings Previous Well Sampled TW4-40
Casing Volume ()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7 .0 7.0 Well Depth {ft)
pH Buffer 4.0 4.0 Well Casing_ Diameter ()
Specific Conductance (micromhos) 1000 Dept_l'l_to Water Befor~urging (ft)
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5/27/2020 13:09 1.0 7.71 22.10 333 0 95.0
Pumping Rate Calculations
[vo~me of water purged() Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes () I Final Depth to Water (feet) Number of casing Volumes
Volume, if well evacuated to dryness (} 0
Name of Certified Anal~ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived in lab at 1305. Samples collected at 1310. Left site at 1312.
Signature of Field Technician
Location ID
Field Sample ID
Purge Date & Time
Sample Date & Time
Purging Equipment
Pump Type
Purging Method
Casing Volume()
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance O
Date/Time Gallons Purged
!volume of water purged_Q
[ Final Depth to Water(feet)
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Type of Sample/ Analysis
VOCs-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
[ Duplicate of TW4-03
Signature of Field Technician
~~M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-65 Sampling Program
TW4-65 06102020 Sampling Event
6/10/2020 7:35 !sampler
Weather Conditions
External Ambient Tempe~ture ()
Previous Well Sameled
Well Depth (ft)
Well Casing Diameter O
Depth to Water Before Purgi_l!g_(ft)
Conductivity pH Temp Redox Turbidity
Pumping Rate Calculations
Flow Rate (Q = S/60l__Q
Time to evacuate 2 Casing Volumes ()
Number of casing Volumes
Volume, if well evacuated to dryness ()
Sample Container
2020 Q2 Chloroform
TH/DL
Dissolved
Oxygen
Preservative
Before/ After
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
Groundwater Discharge Permit
----SF-::·· '-~ ,! .-_ . . YFUP?P'S' ,.,~ .. ''-""""""'-, ~ ~ .•
, '
White Mesa Mill
Field Data Worksheet For Groundwater
Groundwater Monitoring Quality Assurance Plan
Location ID TW4-70 Sampling Program
Field Sample ID TW4-70 06122020 Sampling_ Event 2020 Q2 Chloroform
Purge Date & Time
Sample Date & Time 6/12/2020 6:25 [sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sampled
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing Diameter _Q
Specific Conductance () Depth to Wate! Before Purging (ft)
Dissolved
Date/Time Gallons Purged Conductivity _e_H Temp Redox Turbidity Oxygen I Before/After
!volume of water purged O
Pumping_ Rate Calculations
Flow Rate (Q = S/60) ()
!Final Depth to Water (feet)
Time to evacuate 2 Casing Volumes ()
Number of casing_ Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Laboratory
AWSL
AnalY!_i_c_!I_ 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-mLHDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Duplicate of TW4-09
Signature of Field Technician
..:3~M~
Location ID
Field Sample ID
Purge Date & Time
Sample Date & Time
Purging Equipment
Pump Type
Purging Method
Casing Volume O
Calculated Casing Volumes Purge Duration O
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance O
Date/Time Gallons Purged
(yolume Ef water purged O
[Final (?epth to Water (feet)
Name of Certified AnalY!ical Laboratory
AWSL
AnalY!ical Sameles Information
Type of Sample/Analysis
VOCs-Chloroform
Chloride
Nitrate/nitrite as N
Comments: I Dui:>_licate of TW4-07
Signature of Field Technician
~"'~~r/'~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-75 Sampling__flrogram
TW4-75 06122020 Sampling Event
6/12/2020 8:00 [sampler
Weather Conditions
External Ambient Temperature ()
Previous Well Sampled
Well Depth _(ft)
Well Casing_ Diamete!_O
Depth to Water Before Purging (ft)
Conductivity pH Temp Redox Turbidity_
Pumping Rate Calculations
Flow Rate (Q = S/601 ()
Tfme to evacuate 2 Casing Volume~
Number of casin_g_ Volumes
Volume, if well evacuated to dryn~ss ()
Sample Container
2020 Q2 Chloroform
TH/DL
Dissolved
OlC}'gen
Preservative
Before/ After
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 HOPE u H2S04 (pH<2), 4 Deg C y
TabC
Weekly and Monthly Depth to Water Data
Monthly Depth Check Form .···· ..
Date :l f.J. L~Q ;;w. Name .D~" L~P'l,v• 1 ..,;. ... ,.er-Mo J/,JQ.(t . ,
Time Well Depth* Time Well Deeth* it
lQlQ MW-4 !!:L '2S l~ TWN-1 ~7 . .5.5
lQQ1 TW4-1 lQ2..t;5' Idol~ TWN-2 1!<. 1 10
IQ t S: TW4-2 l l I. i I 11D~ TWN-3 ~l~~
10.a3 TW4-3 la;} ,7, 11.11. TWN-4 b(J .'-l.5
lQQQ TW4-4 8'3. l~ 1:L.Ob TWN-7 fl 1-3 I
IQJ~ TW4-5 7/), ll ,~,~ TWN-18 ,1.15
oq,5 TW4-6 7711./~ 1.2.03 MW-27 .s,·. b.5
~ >
f Ql:J.. TW4-7 8~.i~ 1157 MW;..30 7~. 7'j_
lQ.21 TW4-8 s:<. ss:: ll5~ MW-31 b3.73
iQ~ I TW4-9 ~8.Q8
L0.3S TW4-10 (p, 7. ':1.. 6"
lQIS TW4-11 9.0.1~
Q9~1 TW4-12 S:=f,;J.3
OSLS TW4-13 s: ~. i; ~ og.2.5 TW4-28 ~1,2..&,
0'1.l l TW4-14 77,'I :2, QB~~ TW4-29 71,/J';J.
LQ':J.(. TW4-15 1'1., l2 OS3Q TW4-30 '1.4,(.l
lQ':J.;J.. TW4-16 7Z,S8 oa11 TW4-31 7,:,. l ~
ll);iJ TW4-17 iD ;,5 Q94f! TW4-32 s~. e.fl
j:i.;l.b TW4-1'8 ]/ .1.5 /JS.:Z Q TW4-33 -,,. '23
12.'i5 TW4-19 1.Q .,, 083~ TW4-34 Z2.,2i ·
Ln5.1 TW4-20 '1g, 11 "S'.3~ TW4-35 '2..~.~~
1~.1~ TW4-21 7 31 0 1 ogu; TW4-36 ~Z'J.'-1
11 'i 7 TW4-22 C.j ,bt; l0.2~ TW4-37 7'::1.. l'J.
O'J_~lJ TW4-23 7~.11, lQ~8 TW4-38 5.S • .2~
11 Li5 TW4-24 bl I gt:_ lQ2.0 TW4-39 1.2.,3~
122-1 TW4-25 10:-1.73 0939 TW4-40 1.J._. 0.3
09. L/ '.f. TW4-26 7l,'3..7 lQQ ,3 TW4-41 81,13
0823 TW4-27· 78, S:5: osu, TW4-42 ,1,98
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
Ti W II
Name--=06 .... -ktymM ~« 14a•;;;,;, -· : ·
/ System Operat1"a1 (If no note
D th* C ts bl / ·'
Date
me e 8DI ommen anx (!rO ems cottectlve actloris}
1)4,;' .:J MW-4 q~ '1'~ Flow 3. SJ ~ No
Meter .2."' q c.t q,; 1 o ~ "m No "' •·
/Jlf ~ ~ MW-26 9,1./.11 Flow 1n ~ 'm No
Meter"~ L/ ~ j ,,__ ro ~ No
IO'lt:;" TW4-19 ~q '13 Flow Jfl n "89 No
Meter ~ , n-t '-I 7 ~ < '* No
11q1~ TW4-20 r-~ f>,;" Flow LI n 'ta No
Meter ~ J t~ n '"" .,. r:r c:--· No
1100 7 TW4-4 ~ t;' qt;' Flow I 'i " .;
.._ No
Meter '°~ Lf I!. 7 .:z st ._ No
,,Of)/) TWN-2 r-.a ~n Flow J 7./-. Yim No
Meter 1~_su:. ~ ~~-~ -No
,1q,1 TW4-22 7:, /)ff Flow ,~ "1 Yea No
Meter ~ q ~ n 11 :1 7 Va No
ll)O/J~ TW4-24 ~~ 71 Flow JI./ 9: 'ms No
Meter 13 .1.~~1~. ~::, -No
/1ilt;°1 TW4-25 tit!LII Flow I 1 /,. VD No
Meter "" ":I. '1l. /_ ,; ~ .J. -· No
/J4'57 TW4-1 In~ tl~ Flow , ,., (J 'a, No
Meter ~ :> !19 o 1 l va. No
nt:1"i/. TW4-2 JI :J.. -y '"I Flow J 7 g, 'Me No
Meter -;7g~ .17 si ._ No
04 ~'f TW4-11 ~/l t.1 Flow ,~ ~ Y:ea No
Meter r..;; 1 'it "'q -,, "-No
I}«,..,~ TW4-21 71.~~ Flow J 7 /_.. Vas No .. Meter~ 1 iJ~~,-L 1 ~ Val No
lnq I st TW4-37 ~, ~"J Flow 1« n ¥ea No
Meter , -, 1 q ~ r. 1.1. '& 'lift No
"(? .:l iJ TW4-39 "1.:J. ,;~ Flow J~ n ~ No
Meter /,,, '1 ~ n D r;_ ~ 'aa, No
JDJ'-1 TW4-40 7/ /LI Flow /f;l,/)
.._ No
Meter a.11 r. , /~ -,,, _., 4( Va No
1nn:1 TW4-41 Qn.11 Flow t"A' !1 ~ No
Meter :::J. 7'141'.,:; '2i ~ ... 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 .
Ti W II
NameV~a, ~r: f/,,ft~~, · ' .:" 1
System Operatio~I {If no note
D th* C ts bl ·'
Date
me e 8DI ommen an~ Qro ems/corrective actions}
/7,;j'/I/ MW-4 ~L /c;' Flow L/ ~ 'is> No·
Meter ~ c; o t:. c; ~ q q~ ~ No , . ..
O'R.21 MW-26 c;l 2 l. :J Flow JI g )(a, No
Meter ""-"-:'.l n, -r Vs No
, nne:-TW4-19 7t"J. I./~ ·Flow /'ii 0 'e No
Meter ~. , , rA ~ ~ '-' r, va..No
t)~O~ TW4-20 /,, q ' '"f .;-Flow .2 ~ ¥8 No
Meter 3 3 ~ I./ 7 t,, :l 7 .._ No
oqnq TW4-4 7~ 1./L/ Flow 14. r.. .,, ~ No
Meter ,r,. q <:r 7 I':. , , ~ "-No
n7~2 TWN-2 ~l."3'-1 Flow / 7. /,. Qls No
Meter 1 :2 gq ".'.1 z;q IJ ~ No
--TW4-22 7; .77 Flow Jf)J I"") -No u r,r,.
Meter ~q4c;~ J. c; -No
l'l7r;'O TW4-24 t:_q I :J Flow J~. 7 \!a No
Meter , ~ ".'.1 7 J../.t;°7. ~q lte8 No
177-:il' .. TW4-25 71 '-II Flow I I, "i '19 No
Meter "J:" o ..:i , / • ~ SJ -No
IJ'J~S-f TW4-1 107.4. '?J Flow J :J. . I' ... ~ No
Meter ~ :2 ~ ~ .::tli. n .._No
17g~,:; TW4-2 JI~ ~ 1 Flow /:J ~ '6ft No
Meter 3 7q ~ ~ :2. (o W..,. No
n~"la TW4-11 qo,fU .. Flow JI",. ..., 'a No
Meter r,. 7,q ~l-1 ~ ~ '81--No
1?7~1) TW4-21 ,n 111 Flow \. J ~ '-I ~ No
Meter .21<14~4 J.~q -No
ln~n~ TW4-37 7"1 r...' Flow I~ 0 'Ma No
Meter I 7 ::I ~ I 2 , I mll' NO
l?'il I z;--TW4-39 "7 :J &; () Flow Jg () V. No
Meter ~ ~ ,: q q ~. ; v., No
nq~ TW4-40 ...,, / ... < Flow J 'i( (] ¥as No
Meter 1,./ .2 ~ ,-... ~ 1 , 1 t,, ._,. No
OIJl'JO TW4-41 ~1 .... qn Flow I./ I) ~ No
Meter .:> 7 "-1 ~ q ll ~ Vat 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 Name 72,ca G
System Operational {n: note
bl / ti 1' .• ) Ti W II D th* C ts me e 8D! ommen an~ ero ems correc ve act ons
lnQ'!)~ MW-4 ~~.~r::; Flow '1 < \wa No
Meterd..~J~q~'-1' ~~ Va& No .. ..
nqo1 MW-26 7t:.. 0 C, Flow JI. 'l, V... No
Meter "~ g J ,;-~. ,,, "-8 No ,n~~ TW4-19 7:J 1_,r;c Flow Hf fl :.. No
Meter :i 1 :::, '-I , .2 7 R ¥199-No
n~e; J TW4;,.20 'x I In Flow 'IC n "-' No . Meter ~ "' , I",. 1 /.,. ..,, r. 'MS. No
ll')q"/ 6, TW4-4 c.144 C 7 Flow It:. '-I .; .... No-
Meter r.,. r., r.. 7 ":f ~ I-/ ¥JD, No
/)7/;, TWN-2 t:.2 ./... I.,. Flow /~ /J ..._ No
Meter , .:1 c, , ::, 7 ~ /.. ..... No
109,lo/ I TW4-22 "1~ '=t 2 Flow J fl /J "Vm No
Meter c.tt:t~ 7t:tCJ. q ~ No
/)Q~(,, TW4-24 l'-'1 fl~ Flow JI'-1 -No
Meter 1 -,. ~ 1 !1 :>. ~ ,. 1./ :. No
071./K TW4-25 72. J::l Flow II /.. "-No
Meter ""c;r..~ ~ 1,q o '\ta, No
lnQ.:2-, TW4-1 J () ~ J.t;" Flow I '.:J l"A Yet No
Meter ~~ ~'/.; Lf ,.., ..... No
/}q J "2, TW4-2 q~ ~I~ Flow /I',, /) ~ No
Meter ~ t,. I) t .. , IL> ,;-.. No
oqnQ TW4-11 q1 II Flow I IA "'.2 ¥.el No
Meter£.~ 1 ~'"' -,, "-No
(J,.,,..., TW4-21 q~ l("',1 Flow ,~ ~ --No
Meter ..:2 "] n::z ~sr~ 7~ ~ No
n9.wr:,, TW4-37 71.(~ Flow ,c;r n ~ No
Meter , 7 ~ _, , ~ ~ _ ~ 6a No
111~,;"6, TW4-39 -,~. ~/} Flow Hl.D VIII No
Meter r, ~" 791J. ~ ~ No
h&lr: ~ TW4-40 ..,~ ."'7-:a. Flow I CJ 0 ~ No
Meter '"''2. 1 n Sl~. I~ ... No .. t!)q-,.., TW4-41 i(~. ":Iii'.. Flow ~ (Li .... No
Meter ~.77?j ti/ -: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.
Weekly Inspection Form
Namecz::::::?ea.k:',cme" z;::cze< f{,(1./£J' -··'· ·:··
~vstem Operatronal {If no note
Date ti-i,J-,U)
Time w ell Deoth* C omments anv oroblems/correctlve actions,
0 q &;,"J MW-4 ~~ q"' Flow 3. t;n "-No
Meter ..Jr:::;,~ r;~ ~n ~ No ," ..
nq.,,_n MW-26 70 .:J q Flow J/7 4 Yee No
Meter J.( 1 .... q q q () ., ¥111 No
, n1...., TW4-19 t;,q.~n Flow ,~ tJ -No
Meter ..J 1 ~ q .., ~ =>. ,;-¥:es No
n~1.1 &;' TW4-20 qn.11..1 Flow L/. !J Y!D No
Meter '1 r:; , 1 , ,;-i; 7 -No·
/{)In TW4-4 7q 9.n Flow ) ~ () *' Yes No
Meter ~ q 7 ~ t./ 4 ~ )ms No
l)IAJ l TWN-2 e;.., 'i\ 1 Flow /9, /) Yea No
Meter 1 ~ c, ~ 4 1 7 n r. No
osn~ TW4-22 ..., !l :7":I Flow I~ 0 .... No
Meter t:::ct~ ::i44 q -No
/)tr':1 l'A TW4-24 t"..q ~n Flow 1£. ~ b No
Meter , -,, ~ r; ,;-/J '{'. , n ~ No
/Jtf./"JI.{ TW4-25 7'A ~ i;-Flow J/) 4 'e No
Meter '-It..; 11)/J :J. /J Yet No
1/')q~ I{' TW4-1 1ni: -ro Flow ) ::J. '71 ¥ea No
Meter 3 ~ '1 J .l. , , ... No
/)q I./ tr TW4-2 11:l.. II Flow }/;, L( VD No
Meter 3~ 1 ~ ~L.J o "-' No
(]q~~ TW4-11 ~e,. '115"° Flow JI. st Ya No
Meter C.R ~ ,., 4 ~ No
tJ7&i7 TW4-21 7~ '.'.lt Flow JI,.. () ... No
Meter::, _j 1n7c;t;::,., WI No
n~"I n TW4-37 ilo Ii Flow IQ n ...... No
Meter , -, '2, ~ , -, q ::i 'Bllt No
108,;"{) TW4-39 '2'1.1../~ Flow 1t1.n .... No
Meter In "I I t; .r, ~ '7> V.. No
JntQ TW4-40 "7 I "1 '1 Flow JR n ¥o No
Meter "' '2, ~ ~ g "· 1 ~ 'to No
I DO"; TW4-41 'i( :t 12 Flow z;-: ~ --No
Meter~-,~~~ :l 1 c;-Wit 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
Name::D«rzq..,,, ::z;:;.,,c ~fl~ , '.
System Operatio :Hlf no n~te
Date
Ti me W II e D th* C ts bl I I ct eo ommen an)t'. (!ro ems correct ve a !one)
-. nq-:1 I MW-4 ~« '11l Flow L/ 0 ~ No·
Meter .:i t;" ~ ctn n -:i.« 1 .._ No ,-..
/)~&/~ MW-26 <;l.i;'". r. ~ Flow " ::l "8at, No
Meter .,., , .., q , •. "2.. ... No
/()If) TW4-19 ~q_/ ~ Flow -Yes a,
Meter ~,:) ~ ,7G.., Yes ~
ln~n« TW4-20 ~q CI/J Flow ;;)._' Ya No
Meter -:3 s-q'3 ot. /,.1> ._ No
f)441/ TW4-4 SI0_ "1i~ Flow //,. 0 ... 'cs No
Meter t: cur~ 1-., 1 ~ No
n« Ir;" TWN-2 ~~ .'HO Flow IC. I.{ -No
Meter,~"",,."'~, -a. ... No .
1/HI ~ c:t TW4-22 7tJ '.'.1 "l, Flow J'l' 0 Ya -No
Meter 7 on¥ CJ n sr -~ ·No
10~2 l TW4-24 /aq_ r;"J Flow '"' ~ ~ No
Meter 1 '3 ;q"Tzt...08 "99 No
I} ~na TW4-25 .,~_...,_i;-Flow J :I. • ,.., ¥ea No
Meter ""~--r "T ,;-t:'. "",;t ~ No
l)Q1., TW4-1 1n6. JL/ Flow J-:f. n -No
Meter~~'""~ ~ 'fl 7 ~ No
I) tJ Ii' .. TW4-2 Jl/1_~1 Flow NI> 2. -No
Meter ~~ :2 r-:, 1 n Yo No
/Jq I I? TW4-11 an /./J Flow J~.« Via No
Meter /.. ~"' ~ L < ~ No
IJ'Al'JI-I TW4-21 -,:i..,~ Flow ,,."'I '-No
Meter .::2 -.i. ,_'" -r 2 -r. n7 va No
/')9.'2.I! TW4-37 7~./ 7 Flow 1« I) V..--No
Meter, 71 Yt:J/ 1."I 'YIS No
l'J«U~ TW4-39 9.. t:;. (') <-Flow 1«.o Ya No
Meter c11"~ t:.2 . .., \ v.· No
no11::'~ TW4-40 -,, ..,.., Flow /t;I(./) ._ No
Meter 1./J.J t:;"7 2 ~ "l I:"' Yes No
nq1-r TW4-41 ~~-0!2. Flow L/ ~ ¥fll9 No
Meter .:1_7 Gt.; :J., .t/4. ~ No -..
Operational Problems (Please list well number): r I
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date g .. 11-2.a
•", ...
Name V«n G; ,4:x:men , ·
T" ,me W II e Dent h* C ommen ts
System Operational (lf,.no note ., anll 1Zroblems/correctlva ac:tlonsl
1nna MW-4 '"'" 1'1 Flow '-I. D YJm No ..
Meter -, <''=I~ -,,,,d..,.""' ~ No
lt>qt;" I MW-26 ..,. QI'.. Flow JI ~ ~ No
Meter If 7 :t ,; n u "l ._ No
JJ:J 1.41:( TW4-19 7 I &..I "1. Flow I f-.n 'e No
Meter ~ 1-,. ,rQ It:' n 'am> No
na1111 TW4-20 r..Q an Flow 2. _4-'e-No
Meter ~~ ._o q ... ,., ~ ~ No
,n~I'-TW4-4 i;z,: "'J""I Flow , ,,_ /') ... 'tslt No
Meter ., 1)/) 1 -, "2. .., -No
l11q1 fl TWN-2 t:0.1~ Flow )'-q 'ts No
Meter 1:::, r, t:t !:> qc:, ,_ \3 No
ll>Q .., a TW4-22 7 'R 1. ,:-Flow '"·n ~ No
Meter 7d'2 "l u _~ . I "ID No
/J (if-.:J &J TW4-24 7/ 7"1 Flow. }~."I YD No
Meter , :a" 1 ~ au n ,:-'tml No
l>flntr TW4-25 J:.Q,: ~ Flow ·'" r-'ta No
Meter u 71',,, ~ 77 u-, ~No
In 11::; TW4-1 in,_ '2.n Flow I ::J..-, 'ta· No .; Meter ~ :i ,; ,:;-, -, i::--'m, No
I tnnl./ TW4-2 111 ":l '7 Flow Jr,. "l Vo No
Meter ~ 'ii ~ ~ 1.1 1.1 ~ -No
/JQC!ll TW4-11 QI t)"J Flow 1r.... g 'a No
Meter 1:. ~ c:-/-· '=I "' '$ No
1,,q,.,.,.., TW4-21 7fZ. /1"1 Flow / '7 <It \Bl No
Meter ~ ~ ~ r-. g 7 I I n 'ms No
l.t')a':lr: TW4-37 .... ~ 14'4 Flow I 'IC t) Va& No
Meter , -r¥ 1,;:,""'-;. « 'fl!S No
l.nQLol ,::" TW4-39 au 1'-1'1 Flow Jff_O -No
Meter c. "I 7 ~ er ,_ '.:I '*=' No
i,n~ "'.l TW4-40 •u «« Flow I« .:n '-No
Meter .Mr" nu" . ,., ~ Vs No
1n-::1.1 TW4-41 a-, , I Flow 'c. 1 '11!9 No
Meter .!'.I <1 a q I I.( , a V. No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): -----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Name:::z:2,..ca ~,cmao . . ·, .··
System Operational (If no note
Date s::~ 18 _ aa
1· W II D th* ,me e eo C ts bl I I ctl ommen anl£ ero ems correct ve a ens}
lnq 1.1 .:l MW-4 (l() ()'.J Flow 4 . a ~ No· -Meter :ii; Lf'-1 ~ ~ 7. "3"-1 lt!iS No ~ ..
nGt1"1 MW-26 9Ci? '19.. Flow I /'J .:I. 'Ga No
Meter '-17 < ~ IJ q :1 ~ No
nc;o TW4-19 7::J n~ Flow JI. 0 'ul,· No
Meter .J 1 ~ , 9J .'.l. ~ 7 ._ No
1/Jq /) I;' TW4-20 C:Sf.t: ~ Flow I./ 17 .._ No
Meter 3 7 7 -; "" 1 "'"l 'e No
,nn9. TW4-4 S?~ 1../.z;" Flow I ::J. (,, ., 'tea No
Meter 7 /J 1 :2. q liJ , '5" ~ No
,., 42 -a. r"I TWN-2 , C<t. .7" Flow I~ () '*-No
Meter , ~ f'J o I'-, 7 o ~ No
in~<LI TW4-22 71 ~~ Flow I (I, 0 .._ No
Meter 7 n L.f , ~ r;. c;1 "(a> No
na i-4 r::' TW4-24 I'-. t? ~H-1 Flow I t;", :l ~ No
Meter , l 'i 7 r,,, In ,;i '-' ¥:es No
ln«-:.::i ~ TW4-25 7~ .o< Flow JOU ._ No
Meter '-/ g 2.. 1 sr ~ q t) ~ No .
I) q L./ 9, TW4-1 ,n~ ::2n Flow ,.., 0 ~ No
Meter ~ .:i r.. ::i q n 4 ~No
1,-,q·:u~ TW4-2 //J7./i /11 Flow Ii.~ .._ No . Meter ~ ~ I./" L/ ~ :J. Yl!s No
n4"2n TW4-11 Q()l./1 Flow J '7. /j -No
Meter ~~ 11 n -:; ~ No
(Hl I c::-' TW4-21 7Cf II Flow ,~ 1 'U1,. No
Meter ..2.2 ~ 4 S? 9 '1', ~.., ~ No
n<ICQ TW4-37 ...,. "'1, , ,;' r;-Flow Jg I) ~ No
Meter , -, 1-11,, 7.q l'o , ¥iD No
ft,q I I TW4-39 ,'(, /~ Flow I t;i D 'm No
Meter ~"' q ~ -J 'i , q ~ No
/Oil/ TW4-40 '71. 9. (J Flow j~ I) "-No
Meter "'1 .. n "3 o J q ,,_ --No
l)q,rq TW4-41 ~7. QI Flow In 0 'ta No -Meter ~«if .l I Ill~ , i ... No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date , .. ,4 -aa
Time Well Deoth*
System Operational (lf.no·note
Comments anv oroblems/correctlve attiansl
""Ci~ MW-4 c;rq. .Qn Flow ,., n 'to No ..
Meter :i e: e;-,, n ~ ., n '5' 'tS8 No
1742.-:t MW-26 <;l./J, Ji Flow J/J ~ ~ No
Meter ,.,, " "7 .,,, 7 ~. ~ Y9 No
IP~~ TW4-19 7 .!J ~ r.. Flow , 1 ... ~ -No
Meter "l Ir. l. ~ ..., ,, -:a, ltm No
lnq!J-:i TW4-20 caq Colt Flow ~ /,. 'is& No
Meter ~ tt 7 Q ., ".I ,_ ::::1 "83 No ,n,., TW4-4 'fl(.. (.~ Flow J '-I. '-( .,, lQa No
Meter ~" ~ '-'" 1 , \9 No
nClnn TWN-2 ~Cil ti.I Flow 1'7. r .. 'ta No
Meter , ~ 11 "1. '] :::i 1:t .., 'm No
lnq,~ TW4-22 72 .'\ ".l Flow J.., n "88 No
Meter -, n ,._ !3 n a ,A ._ No
/)(1/J~-TW4-24 "7n r:'O Flow JJ:. 'i:89. No ~ '·
Meter , ~ t:' .!J I';.. , -, "7" ~ No
.... ·-...,
In A··~ ·':\ TW4-25 r-ct "l."7 Flow / "'l ...-:. ~ No
Meter .., ,1n , r .. "1 "' ,: "Q:19 No
innn TW4-1 '(') t,. lUA Flow 1'."l ~ \!es No
Meter ~ ~-, a "7 ., ~ 'ms No
n"~" TW4-2 JI (J 1 .. ~ Flow J"' I) 't:es No
Meter '1«~ n,, ~ Ym No
tC nqu!J TW4-11 ~n -,,:-Flow ,r: Cjil ~ No
Meter. &a•~.1...~ ~ No
(jo..., ":l,. TW4-21 '7"1..1< Flow J/.. ~ ~ No
Meter ~ ~ u ~ ~ c .:i. Ill".,.. ~ No .
l'JO I <J. TW4-37 7" c;1n Flow ,« n ~ No
Meter I ""7 ~ "l ".l .. r. a 't9 No
ln,o-,c, TW4-39 «<. ,2c;' Flow 1'11 . I? V!ID No
Meter ,.<!1 ~ :1., ,; 'lea No
,n~ !I TW4-40 ""71 Q. Q Flow JtJC, /J '&I No
Meter~ 0:1.r. QI. "1 la 'm:, No
rnn-, TW4-41 iq ntl Flow l'A (1 Va No
Meter "l 4 ~ 1 ... 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.
Weekly Inspection Form
Ti W II
System Operatl::1 {lf,no note
D th.* C t bl t a '
Date 4-1-iO
me 8 &D ommen s amt: ero ems corrective ctlonsl
,n:1<1. MW-4 'St i:; .l.f c;-Flow '-1. /) "-' No , .. ..
Meter ..2 t;'z:;qe;-;i ~ ~~ Vea No
lt,qt;"~ MW-26 1/ i;'~ Flow I 0, t;J -No
Meter '-' 7 9. 7 11 ~ -No
I I &.I q TW4-19 7'.l &; ~ Flow ,.., n ... No
Meter :, , , "1 ~ "19.H ~ No
I nq .:J.q TW4-20 q<"', "0 Flow 1 ;..____ ;1 J../ n "-No
Meter ~Qc;-~ 1·~ 71 .... No
,nc..tt; TW4-4 Qt.I 11 Flow '~ l!l.«. .._. No
Meter 7 n ~ u n a ,;-' ._,. No
'/)fl,t1/ TWN-2 ~jl :JI Flow lt...tJ Ya No
Meter , ~ n t;" ~ 9 ~ , ~No
1/JQlfJ. TW4-22 l"n I{ ~-,,-Flow J -0. 11 .... No
Meter 7 n 7r.. , t:'"_ '7 ¥a No
I/JQ I .:J TW4-24 r,, 4 L./ 'J. Flow /,,,;..n ~ No
Meter , '\ c;-~-, /. 1 r:' l.f ~ No
... I>« ~&j' TW4-25 ~~ nr Flow II. 1 YiD, No
Meter .&1Q("'9i~'i?.q :1 . -No
Jn?.LI TW4-1 In~ /,.t:. Flow )~ i; (Yes) No
Meter ~ !I -, (,., L/ e:. :J C.. Yes) No ,n, ::J TW4-2 / /) /_ "'/) Flow JrA ~ "-No
Meter ":I « 1. Q 1. , , Va No
" Jn I) :J. TW4-11 qJ.O~ Flow I IA '-I 'ms> No
' Meter· ,;;&q 9 4. ii "81-No -'
'l?f?::J..., TW4-21 76/ ,rq Flow I/.,'-( ¥Bir No
Meter ~ .!> c n ~ "' :, g n YD No
nq~~ TW4-37 ,:./~ ~~ .Flow JR.n 'Ne No
Meler , .., ~ t:. 61 7 ::i -, ._. No
n<J&:(n TW4-39 t:. Q I-{ t:;" Flow J " /J ~ No
Meter.. 1 _ t; /./ /,, '1 ~ J '6D.. No
,or:~ TW4-40 -,, <r< Flow ,a l'1 ~ No
Meter 1-1 ;'-'1 /A~ t.., 5"'~ Ver No
1n-i.q TW4-41 SIi:". I~ Flow .er. :.:2 ... No
Meter ~ « ,.., In ., :J • /. n ~ 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 f,-'-/ _ ~O
Monthly Depth Check Form . , 1.,
Name8,a v:r, ~&(/,' "/
Time Well Depth* ;, t t Time Well Depth* ·
l33~ MW-4 H!:t.!Q ... ,, azaa TWN-1 1..1.,.-. •·· .. TW4-1 ~TWN-2 l3 .at lQ.&.I~ l '"l ~!t ~,.~~
l3 3 S: TW4-2 U21, at.I alo,;-TWN-3 ~:J.., u. ,. 115:2-TW4-3 -413,lS a1a9 TWN-4 I.fl... S:(-2
l32.I TW4-4 iS: • .15: 0.Iil!:/. TWN-7 sr.ga
,:11, 1~13 TW4-5 ZfJ.. f.tQ '2:Z:I !:f TWN-18 ,a.. Q~
a9!:i s: TW4-6 ::;z:7,9~ Ql19 MW-27 51.LQ ... ,. 13~ I TW4-7 !.1 .7../J. a13S: MW-30 IS:,0.3
"' « 13!:::l:Z TW4-8 !6:, 91 l~3Q MW-31 ,s.~n .. ~ (!:(Ilg TW4-9 iii, '-'2 . ,. l~)l TW4-10 {al.Q?a
l! !ii TW4-11 gQ, 11
aga.3 TW4-12 5'£1. Zl
'2!.ta TW4-13 s::.i:.3~ '29..Z:Z TW4-28 ~l.9~
agi3 TW4-14 21. ~&j" at .. LL TW4-29 :z :I I ~ s:::
i !:fa.a TW4-15 sa.3s: • a1ll TW4-30 l~f1~~
I '1 il.3 TW4-16 72,34 0B4'1 TW4-31 Z'1..~ I •
I ~ .:I.GI TW4-17 iQ,9:Z Q93Q TW4-32 i'-.~a.
#l l s:,s: TW4-18 71..:,, 08/lo TW4-33 11. (I I •
I S: .l...:t TW4-19 :13, '5..0. Q83J TW4-34 1'-(;. t..
l~~Q TW4-20 ZQ,Qt«_ t2S33 TW4-35 "2.~. 9.:X
l S:JQ TW4-21 "'?~, (a( tJ.,u~ TW4-36 2-l• ff
l'i.~S. TW4-22 u9, a:i-· i!:l.!:t~ TW4-37 :t.a. is
ag!f.;i TW4-23 2!1.,5:..i:-I !:i Q S:::: TW4-38 £8.·'25:
l!::iS:3 TW4-24 ~g.95: l~3I TW4-39 I& .. !2
I !i.l2 S:. TW4-25 '2la1ll og:3r TW4-40 ~L, att -· b!3S TW4-26 1.d. I ,; f;;' i3;LS: TW4-41 S,Q.ll
as.a a TW4-27 ll., s 7. QSl~ TW4-42 ~,..~,
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
I
Weekly Inspection Form
Ti w JI D th* C
System Operat1081 (ff• no',note
ts b1 , act ..
Date NameD,ro
me 8 eo· ommen an~ ero ems correctlvt Ions)
_, /)411'1 MW-4 ~~ 7« Flow "·'-/) ~ No I ., ••
Meter ~ ~ ,. /_ ~ q n q u "-No
-()fl&JI, MW-26 '"7~_ql;"' Flow '/) « "-No
Meter 'ltzn ~ "'~ o "-No
J J ",:;-TW4-19 -,~qq Flow J'tf n ¥es> No
Meter ~ , ',a~ a:;-q ~ 1. ~ No .. /1f j_/J TW4-20 7 J. C°D Flow ~ ., ·"' ._ No
Meter Al " "' , q ,. ~ 1 V. No
lllQ':1~ TW4-4 ~~ '7/'J Flow l'U n ... Y,o No
Meter 7;, ..,·u 1 -i 1.1 Yes No
n-,4J'7 TWN-2 ,:q I~ Flow I "7 ") Vea No
Meter 1 1 n 7 ~ ~ c1. i::-._ No
A«nn TW4-22 l',.q 'l2 Flow ltZ /} Va No
. Meter ., n a -, .,, r •. 7 ~ No
r>-rl:'C TW4-24 7 /,. I'. I'. Flow J~_q '-No
Meter , ':\ 1. o '"\ n.., "" Vs No
t'J7Ul TW4-25 ..., .:>. q (... Flow IJ /_ Ya No
Meter ~111 ~ ..., "-4j:I 1 ¥BB No
,.. ncu« TW4-1 flt...' "'1-:t Flow / D ct v.. No
Meter -i ~ 11 , <' 1.1 • 7 ~ No
l/7~c:< TW4-2 ~~.,~ Flow I~ L v.. No
Meter ~" -, -, 4i"'CJ ~ "-No
/Jt'J.,., I'. TW4-11 qo 01 Flow J L « "89 No
Meter~~ J 4 I'..~ Yes No
n "T ~ s:;-TW4-21 "iO. ~q Flow J/_ L ~ No
Meter ~ .., ~,;, ~ ~ "' <' .n 'it::t; No
IJ'l. It:' TW4-37 7!1..~/ Flow J'l n ~ No
Meter , ., /./)/.,..., ~ ¥a No
1n~:1,; TW4-39 -, I. ""f '"f Flow Hl.(} ~ No
Meter th ( ~ ~, ~ "' -No
117<:1 &.It:' TW4-40 ~l."7~ Flow / ff /J ~ No
Meter u<111cu .. ,a ~ 1 Y:fs No
nq~c TW4-41 ~'B ,~ Flow ,,c 0 'a No
Meter :1. ~ '-' 7 ~~. ,:;.::, 'Ml 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
NameM<t2 ~,mesa · ·· ;·
System Operational (lf,no.note
Date
Tl me W II D th* e 8D' C ts bl ommen an~ ero ems/corrective actfonsl
1101.1/r MW-4 SJq I~ Flow 1-./ n ~ No .,.,
Meter ') c: 7 ~ ~ /_ ~ ~ G. -No
t]q ~/) MW-26' st .r;-, , a, Flow ) {) /,, ._ No
Meter I-/~ '.'.I <2 " LI u ¥a-No
111..f~ TW4-19 7,;J ~ c;-Flow '-, ,1 Vee No
Meter ., .., n , o , n -Y V. No
• ln4a~ TW4-20 ct[) I'} -; Flow '.:l • ,_, "91P ·No
Meter LI,~ 1 c;i !I ,q ~·No
,nnQ TW4-4 ~Hl -,,;-Flow ''"' ~ ,; ~ No
Meter -,n r:; ~ :l, ~ ._ No
/'Ja. nn TWN-2 r~ 'f~ Flow /I"-st "-No
Meter ,~nq ~t:.. ~ ~ ~ No
'/)\? C: ,:-TW4-22 "7~.1"1 Flow I a ,1'J .... No
Meter ...,. 1 / z:-~ Q. c 'es No
IUHl"T TW4-24 /-.4 /,. -:J Flow ,-, ~ )wa No
Meter , -,, /_ LI LI~ /1 ""' q "--No
11r1~-... TW4-25 7~ "o Flow II .. "'I ~ No
Meter -~ ,n sr «~ o . .., 4 ~ No
nqr;n TW4-1 1111'1 :l_~ Flow I I. 9. ._ No
Meter 1 ~ lil q ~ \ ct '-No
/)Q~~ TW4-2 ,or;, 30 Flow I 1. 0 ~ No
Meter ~ ~ '.:l cz n,. ~ V.-No
nq'::l:i TW4-11 qi), 8/./ Flow J /;. ,;t Yet No
Meter ,;. q ') 7 o c;-~ No
/J 71./"7 TW4-21 7t:), t I Flow It:..~ Yea No
Meter ~ -, ~ ~ , , 1 .~ ~ .._ No
{)Q/1~ TW4-37 "11.q~-........ Elow I 'A I) ¥!Is No Meter , -, /-. ,:;-&11> Q .., ~ No
[/11:JI I/ TW4-39 ~er ".'.> &:" Flow I 4. /J ~ No . Meter ~~q,;~~.4 }6n No
1n-::1fl TW4-40 -,, ,i Flow ,~ n Va. No
Meter l-/o 7c:t, ~ . .., 1.1 Ya No
·nqt:~ TW4-41 'it LI 11;'" Flow LI a Yo No
Meter ~. 4 7 n LI /_ q "' -NQ
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 ~
T" W II D
Name :7:2.-cn ?~1auo :,;:;;;,w:: f/,,«,f5.:.
Svsfem Operational llf~ote
h C ts bl · t lo
Date 4-,a-,o
1me e eot • ommen any: ero ems correc11ve act nsl
/)Q~r;' MW-4 st r: /) ,_ Flow '-I LI Vee. No .• • ~'-Meter :J ,;-.., q, ".1 ~ .!J~ v.· No
nq~:, MW-26 ,;t_/) UIJ Flow II.~ "89 No ~
Meter I/ R ~ -, C < ~ ._ No
Jf'-lc;" TW4-19 -, ~ « '=I Flow J~JJ . .. No
Meter .:1 1 t c.; 9 n a LI V. No
'/)q'J/l TW4-20 r..~ I 'T Flow .:] . 'it -No
Meter 4 ~ , 1 -, "1 &.JL.I 'tfa:, No
J/)IR TW4-4 0'-1 n ~ Flow JI. :l,. ' _. '-' No
Meter 7 o /_,-, ~ /..,_ -, -No
ln~IQ TWN-2 ~a Q/l Flow II':. £/ ._ No
~ Meter , '1 , n " 1.1 c: -, 'a No
I/Jqn ~ TW4-22 -u.. I I-/ Flow 1st n ~ No
Meter -, 1 ~ 4 -, tZ. c.-. .. No .
nqn~ TW4-24 t(,q_ ".l ~ Flow 16.. 'tJ .... No
Meter J 1 ~ g I'. 1. L. o <r .... No
nAJ~ TW4-25 "'7~_...,, Flow JI ~ ._ No
Meter 5" 1 i: '=I ~ Yf "2. ~ '-No
,nntr TW4-1 uu,. ~I .. Flow J!l. 0 Va No
Meter ~:i.q~, ~ _ ~ ._ No .
[/1Q'-/Q TW4-2 Jl":l ,~ Flow 11:.. n Va No
Meter 3flqi!J·7'-I ~ "--No
/)4-_I,.//) TW4-11 c:an. Q.2 Flow I/-~~ 'ta No
Meter I'.. ct·.1../ '.l h "1 ._ No
l~~n~ TW4-21 "?.,,, ,._ -:a. Flow ,r.... ~ . .._ No ~ Meter ,, ~ .., *-' n ··.., ., . n u .._ No
lnq I L4 TW4-37 , \ ".\n Flow HI n · ~ No
Meter , , 7tJO a .. ,._~ ~ No
l)Q '.l ,. TW4-39 /.. Q ,:-If' Flow I Cil. (') 'te:s No
Meter t'n~ "] ~ n,_ o ~ No
,n~"-TW4-40 ..,, ~< Flow Jt;i.,, ·*· No
Meter LJ~ ... ~ -=i 11. ,.,n ~ No
111 I~ TW4-41 "a ~n Flow <. /_ Via No
Meter ., . f'il t;1 ~ '1 n . n J./ ~ No
Operational Problems (Please list well number): ..
Corrective Actlon(s) Taken (Please 11st well number}: ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date G-a..q~;w Namen,.0 '"i-">••n= ~~.:: ·' '
System Oper80nal ,n nci~note
C t r bl t ., • T" W II D th* 1me e 8D ommen s an)l e o ems corrective actions)
,n:1&:' MW-4 t::JJ ~.~ ,Flow ". /'J Vo No ,.· ..
Meter ~ c; 'flt:. 4 :,s:r_ ~li" Yes, No
nt'.l~t: MW-26 ~t. r:'n Flow / /J .:z -No
Meter "" q r:: ,_,, t; Sl Q ... Nq
11-11n TW4-19 7::J 4~ Flow i 7. fl ':ea No
I Meter ., ~ A) /_ "'-,., /-,
.._. No
j/)ql./1) TW4-20 q~.7~ Flow ':I./.. "-No
Meter 4/ ~ Sl , ,_, , • n ~ ._ No
/7,4,;" TW4-4 r/1. C:L/ Flow I IA "" .,, ... No
Meter 7() ..,~ /J ~. q ... No
nq,~ TWN-2 ,;q DI Flow II',. A •• No·
Meter , ":I , -:1 t:. 11 tJ ~ < Yim No
lnq.:1 ,. TW4-22 C.i 4Q Flow I fl n -No
Meter ~ , I!' ., ~ .t:'. .., -No
ll)Q"l f\ .TW4-24 1,.q Cl(" Flow , ff ~ _._ No
Meter , ~ -, ~ -, , '1 /. ,_ ... No
/)qf)t,. TW4-25 c;t 2. .., n Flow IO "I 'ta No
Meter r; .!l 1 !> "7; ".l..q 'iD No
,~ -=In TW4-1 IJ')~ ~~ Flow '~ < ... No
Meter 3'3 o ~ 'f~. Q 'ValD-No
1n I "=I TW4-2 '" ~ D Flow, J&. n \{di' No·
\ Meter 1 q n~ 1 r:; /) -No
1nnt:: TW4-11 QI J.l() Flow I/. n .... No
Meter l.. q c; /,. fo' ~ ._ No
.....
nQnn TW4-21 i:l. ~·I Flow , ,. 'l ~ No.
Meter ~ .., Q I , -:r c '-I« .._. No
-
/}q'2.L( TW4-37 il.~.IA Flow JR n ~ No
Meter .. , .., ., "" '7 mo 2. )ra, No
(JQLJ~ TW4-39 /._q qq Flow I (I_ n ~ No
Meter /..L.r;'oQ ~~ z;-~ No
,~,:r; TW4-40 7 l '11 Flow J',1.,, *a& No
Meter r:: n j ~ ., ~ n<l ~ No
/ l 2-( .. TW4-41 t;(f/J t?~ Flow z:;-< ~No
Meter-.'.1 « q ,..._ ~ /.. , c, ~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. Tanner Mollidny
Date: 5/4/2020-5/5/2020
Depth lo Depth to
Dale Time Well Water (ft.) Date Time Well Water (ft.)
5/5/2020 1224 MW-01 64.51 5/4/2020 921 MW-04 88.70
5/5/2020 1453 MW-02 109.77 5/4/2020 927 TW4-0l 106.14
5/5/2020 1118 MW-03A 83.98 5/4/2020 916 TW4-02 110.21
5/5/2020 958 MW-05 108.21 5/4/2020 1106 TW4-03 63.31
5/5/2020 1040 MW-II 85.25 5/4/2020 944 TW4-04 80.33
5/5/2020 1001 MW-12 107.15 5/4/2020 1 I 15 TW4-05 70.55
5/5/2020 1030 MW-14 102.28 5/4/2020 1055 TW4-06 78.02
5/5/2020 1026 MW-15 105.31 5/4/2020 1058 TW4-07 82.78
5/5/2020 1100 MW-17 71.59 5/4/2020 1102 TW4-08 86.15
5/5/2020 1219 MW-18 73.26 5/4/2020 l 113 TW4-09 68.55
5/5/2020 1207 MW-19 64.63 5/4/2020 I 119 TW4-JO 67.97
5/5/2020 1310 MW-20 89.71 5/4/2020 910 TW4-ll 90.60
5/5/2020 1305 MW-22 66.49 5/4/2020 1038 TW4-12 54.78
5/5/2020 1459 MW-23 117.15 5/4/2020 1035 TW4-13 56.12
5/5/2020 1405 MW-24A 112.03 5/4/2020 1028 TW4-14 77.65
5/5/2020 1405 MW-24 I 10.94 5/4/2020 1123 TW4-16 72.40
5/5/2020 1035 MW-25 79.63 5/4/2020 l 130 TW4-18 71.60
5/5/2020 848 MW-26 85.63 5/4/2020 JOJO TW4-19 68.18
5/5/2020 1409 MW-27 57.17 5/4/2020 838 TW4-20 69.90
5/5/2020 1352 MW-28 74.70 5/4/2020 804 TW4-2l 72.12
5/5/2020 l 130 MW-29 107.75 5/4/2020 828 TW4-22 70.23
5/5/2020 1524 MW-30 75.23 5/4/2020 1052 TW4-23 74.61
5/5/2020 1519 MW-31 68.48 5/4/2020 821 TW4-24 69.51
5/5/2020 1515 MW-32 80.25 5/4/2020 809 TW4-25 72.45
5/5/2020 101 l MW-33 DRY 5/4/2020 1048 TW4-26 72.60
5/5/2020 1017 MW-34 107.61 5/4/2020 900 TW4-27 78.97
5/5/2020 1503 MW-35 l 12.38 5/4/2020 1041 TW4-28 47.99
5/5/2020 1506 MW-36 110.60 5/4/2020 1025 TW4-29 77.53
515/2020 1021 MW-37 I 13.55 5/4/2020 1015 TW4-30 75.08
5/5/2020 1319 MW-38 70.03 5/4/2020 904 TW4-31 76.57
5/5/2020 1315 MW-39 64.88 5/4/2020 1044 TW4-32 55.55
5/5/2020 1055 MW-40 80.15 5/4/2020 857 TW4-33 77.05
5/4/2020 1022 TW4-34 75.72
MW-26=TW4-15 5/4/2020 1018 TW4-35 75.07
Comments: MW-32 = TW4-17 5/4/2020 1032 TW4-36 57.65
5/4/2020 834 TW4-37 76.17
5/4/2020 ] ] JO TW4-38 58.79
5/4/2020 843 TW4-39 85.05
5/4/2020 952 TW4-40 71.77
5/4/2020 937 TW4-41 88.02
5/4/2020 853 TW4-42 68.60
Date Time
5/5/2020 121 l
5/5/2020 1203
5/5/2020 1429
5/5/2020 1044
5/5/2020 1049
5/5/2020 1445
5/5/2020 815
5/5/2020 1435
5/5/2020 1418
5/5/2020 1215
5/5/2020 1228
5/5/2020 1240
5/5/2020 1236
5/5/2020 1414
5/5/2020 1300
5/5/2020 1338
5/5/2020 1334
5/5/2020 1005
5/5/2020 1349
5/5/2020 1345
5/5/2020 1329
5/5/2020 l 113
5/5/2020 1109
5/5/2020 1104
5/5/2020 1355
5/5/2020 1324
5/5/2020 1359
5/5/2020 1403
5/5/2020 1420
5/5/2020 1425
5/5/2020 1408
5/5/2020 1430
5/5/2020 1412
Well
PIEZ-01
PIEZ-02
PIEZ-03A
PIEZ-04
PIEZ-05
TWN-01
TWN-02
TWN-03
TWN-04
TWN-06
TWN-07
TWN-14
TWN-16
TWN-18
TWN-19
DR-05
DR-06
DR-07
DR-08
DR-09
DR-10
DR-II
DR-12
DR-13
DR-14
DR-15
DR-17
DR-19
DR-20
DR-21
DR-22
DR-23
DR-24
Depth to
Water(ft.)
66.49
43.95
55.93
65.71
64.44
67.85
59.80
42.72
60.88
79.67
82.12
59.36
47.40
62.ll
53.79
82.77
94.23
91.34
51.52
86.43
78.25
98.41
91.56
69.20
75.75
92.36
64.78
63.20
55.51
100.16
DRY
70.38
44.00
@ estimated dry area
TW4-42 temporary perched monitoring well
¢ 5526 installed April, 2019 showing
elevation in feet amsl
MW-38 perched monitoring well
-Q-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::504 perched monitoring well showing
elevation in feet amsl
TW4-12 h d . . II 0 5569 temporary perc e momtonng we
showing elevation in feet amsl
TWN-7 h d . ·t . A 5567 temporary perc e nitrate mom onng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5589 elevation in feet amsl
RUIN SPRING & 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chlorofonn 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 2nd QUARTER, 2020 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE
H:n18000/aug20/WUUw10620.srf
FIGURE
D-1
estimated chloroform capture zone boundary
, ;;-stream tubes resulting from pumping. (note:
, , , combined capture shown for MW-4, TW4-1. I I I TW4-2, TW4-4, TW4-11 , TW4-40andTW4-41;
for MW-26. TW4-20 and TW4-37; and For
TW4-19, TW4-21 and TW4-39)
• @
TW4-42
¢5526
MW-38
"9" 5463
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
capture for nitrate pumping wells TW4-22,
TW4-24 and TW4-25 incorporated within
capture of chloroform pumping system)
estimated dry area
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
perched monitoring well
installed February, 2018 showing
elevation in feet amsl
TW4-40 temporary perched monitoring well -+-5526 installed February, 2018 showing
elevation in feet amsl
M;'-:504 perched monitoring well showing
:, elevation In feet amsl
TW4-12 . 0 5569 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 h . . . A 5567 temporary perc ed nitrate momtonng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
g 5589 elevation in feet amsl
RUIN SPRING A 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-\ TW4-2 and TW4-11 wate_r levels a!E!_ below tile base of !he Burro Canyon Formation
HYDRO
GEO
CHEM, INC.
KRIGED 2nd QUARTER, 2020 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
APPROVEO DATE REFERENCE
H:/718000/aug20/WL/Uwl0620cz2.srf
FIGURE
D-2
---,,, ,,,
II I
• TW4-42
¢ !j521>
TW4-40
+552.G
MW-25
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;
for MW-26, TW4-20 and TW4-37; and for
TW4-19, TW4-21 and TW4-39)
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
capture for nitrate pumping wells TW4-22,
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 e 5/:i3<J perched monitoring well showing
TW elevation in feet amsl 4-7 O ,-,::,,8 temporary perched monitoring well .. ,,,,., showing elevation in feet amsl
PIEZ-2 perched piezometer showing
<;i 5585 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 2nd QUARTER, 2020 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
detail ma CHEM, INC. APPROVED DATE REFERENCE
H:/718000/aug20/WL/Uwl0620cz.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
-¢-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;:504 perched monitoring well showing
elevation In feet amsl
TW4-12 0 5570 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 ch d . . . A temporary per e nitrate monitonng
v 5567 well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5589 elevation in feet amsl
RUIN SPRING 6 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 chlorofonn 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
E-1
TabF
Depths to Groundwater and Elevations and Hydrographs of Groundwater Elevations over Time for
Chloroform Monitoring Wells
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,527.63 09/25/79 94.70 93.14
5,527.63 10/10/79 94.70 93.14
5,528.43 01/10/80 93.90 92.34
5,529.93 03/20/80 92.40 90.84
5,528.03 06/17/80 94.30 92.74
5,528.03 09/15/80 94.30 92.74
5,527.93 10/08/80 94.40 92.84
5,527.93 02/12/81 94.40 92.84
5,525.93 09/01/84 96.40 94.84
5,528.33 12/01/84 94.00 92.44
5,528.13 02/01/85 94.20 92.64
5,528.33 06/01/85 94.00 92.44
5,528.93 09/01/85 93.40 91.84
5,528.93 10/01/85 93.40 91.84
5,528.93 11/01/85 93.40 91.84
5,528.83 12/01/85 93.50 91.94
5,512.33 03/01/86 110.00 108.44
5,528.91 06/19/86 93.42 91.86
5,528.83 09/01/86 93.50 91.94
5,529.16 12/01/86 93.17 91.61
5,526.66 02/20/87 95.67 94.J 1
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
5,533.63 05/04/20 88.70 87.14
Depth Below Measuring Point (ft.) .... -N 0 00 0\ .j:::,. N 0 0 0 0 0 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 -~
07/12/97 "1 c:,
11/24/98 ~ ~ -04/07/00 =-0
08/20/01 < ~ "1
01/02/03 ""'3 ...
05/16/04 a ~
09/28/05 --?
02/10/07 'r:::1" -06/24/08 a ~ '-"
11/06/09
03/21/1 l
08/02/12
12/15/13
04/29/15
09/10/16
01/23/18
06/07/19
10/19/20
03/03/22
~ 07/16/23
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.]4
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
5,512.44 05/04/20 106.14 105.12
--N -0 0
Depth Below Measuring Point (ft.) -8 I.O 0 00 0 -.l 0 O'I u-,
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 ""'3 01/05/06 ~ 06/04/06 ,&. 11/01/06 I ~ 03/31/07 ~ 08/28/07
01/25/08 """' ~ 06/23/08 ""1
11/20/08 ~
04/19/09 ~ ~
09/16/09 """' =--02/13/10 0 07/13/10 ~
12/10/10 ~ ""1 05/09/11 ""'3 10/06/11 .... a 03/04/12 ~
08/01/12 --12/29/12 ?
05/28/13 O" -10/25/13 a 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
08/14/21
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) Mouitoring (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
5,514.51 05/04/20 110.21 108.59
---w N -0 0 0
Depth Below Measuring Point (ft.) -8 \0 0 00 0 ....J 0 0\ 0 u.. 0
11/08/99
04/06/00
09/03/00
01/31/01
,_ 06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04
03/11/05
08/08/05 to-3 01/05/06 ~ 06/04/06 ...
11/01/06 I N 03/31/07 ~ 08/28/07
01/25/08 ""'" ~ 06/23/08 ~
11/20/08 ~
04/19/09 ~ -i:,
09/16/09 ;.
02/13/10 0 07/13/10 ~
12/l 0/10 ~ ~ 05/09/11 to-3 10/06/11 ...
03/04/12 a ~
08/01/12 --.
12/29/12 ?
05/28/13 O" -10/25/13 a 03/24/14 -i:,
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
08/14/21
Water Levels and Data over Time
White Mesa Mill-Well TW4-3
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) (L D) (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) (L D) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 l.02 140.:\0
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 W,!ll
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
5,568.92 05/04/20 63.31 62.29
-J V, -J 0
Depth Below Measuring Point (ft.)
O'I V, O'I 0
V, V, V, 0 +:>,
V,
+:>,
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 .,
12/11/08 e,
05/10/09 ~ "C
10/07/09 -=-03/06/10 0 08/03/10 < 12/31/10 ~ .,
05/30/11 ~ 10/27/11 -· 03/25/12 a ~
08/22/12 --01/19/13 ~
06/18/13 O"' -11/15/13 a 04/14/14 "C
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
09/04/21
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 1.184 114.5
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 1.184 114.5
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 I 1/16/04 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 Surl'ace 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
5,549.31 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
5,533.16 05/04/20 80.33 79.15
..... .....
0
.....
8
Depth Below Measuring Point (ft.)
\0 0 00 0 -..J 0 °' 0
u,
0
I • 4 , 1, '"t I I I r 05/25/00 1 ' ~ ~ ....._ 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
05/19/07
10/16/07
03/14/08
08/11/08
01/08/09
06/07/09
11/04/09
04/03/10
08/31/10
01/28/11
06/27/11
11/24/11
04/22/12
09/19/12
02/16/13
07/16/13
12/13/13
05/12/14
10/09/14
03/08/15
08/05/15
01/02/16
05/31/16
10/28/16
03/27/17
08/24/17
01/21/18
06/20/18
11/17/18
04/16/19
09/13/19
02/10/20
07/09/20
12/06/20 .._ ______ _._ _______ __._ _______ ..._ 05/05/21
~ ! I ~
~ ;-
"1
~ ~ ~
0 ~ ~ "1
~ .... a ~ ,-..,
?
"a"
! --
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 l.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 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.L D) Well
5,638.75 5,640.70 1.95 121.85
5,583.28 09/19/01 57.42 55.47
5,583.36 10/02/01 57.34 55.39
5,583.49 11/08/01 57.21 55.26
5,583.84 12/03/01 56.86 54.91
5,583.79 01/03/02 56.91 54.96
5,583.96 02/06/02 56.74 54.79
5,584.39 03/26/02 56.31 54.36
5,584.12 04/09/02 56.58 54.63
5,584.55 05/23/02 56.15 54.20
5,584.42 06/05/02 56.28 54.33
5,583.65 07/08/02 57.05 55.10
5,584.90 08/23/02 55.80 53.85
5,585.02 09/11/02 55.68 53.73
5,585.20 10/23/02 55.50 53.55
5,585.15 11/22/02 55.55 53.60
5,585.42 12/03/02 55.28 53.33
5,585.65 01/09/03 55.05 53.10
5,585.65 02/12/03 55.05 53.10
5,585.92 03/26/03 54.78 52.83
5,586.22 04/02/03 54.48 52.53
5,586.01 05/01/03 54.69 52.74
5,584.81 06/09/03 55.89 53.94
5,584.34 07/07/03 56.36 54.41
5,584.40 08/04/03 56.30 54.35
5,583.88 09/11/03 56.82 54.87
5,583.57 10/02/03 57.13 55.18
5,583.39 11/07/03 57.31 55.36
5,583.97 12/03/03 56.73 54.78
5,585.28 01/15/04 55.42 53.47
5,585.50 02/10/04 55.20 53.25
5,585.87 03/28/04 54.83 52.88
5,586.20 04/12/04 54.50 52.55
5,586.45 05/13/04 54.25 52.30
5,586.50 06/18/04 54.20 52.25
5,587.13 07/28/04 53.57 51.62
5,586.22 08/30/04 54.48 52.53
5,585.69 09/16/04 55.01 53.06
5,585.17 10/11/04 55.53 53.58
5,584.64 11/16/04 56.06 54.11
5,584.77 12/22/04 55.93 53.98
5,584.65 01/18/05 56.05 54.10
5,584.98 02/28/05 55.72 53.77
5,585.15 03/15/05 55.55 53.60
5,586.25 04/26/05 54.45 52.50
5,586.79 05/24/05 53.91 51.96
5,586.52 06/30/05 54.18 52.23
Water Levels and Data over Time
White Mesa Mill -Well 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) (L D) (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
5,570.15 05/04/20 70.55 68.60
-J VI -J 0
Depth Below Measuring Point (ft.)
0\ VI 0\ 0 VI
VI
VI
0
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 Ul
~ ~ ~ "1
0 ~ "CS ~ =-0 < ~ "1
~ ... e ~ --?
O"' -e "CS '-'
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) O,lw.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
5,530.76 05/04/20 78.02 76.57
Depth Below Measuring Point (ft.)
l,O 00 00 --.J --.J 0\ 0\ Ul Ul
0 Vl 0 Vl 0 Vl 0 Vl 0
05/25/00
10/22/00
03/21/01
08/18/01
01/15/02
06/14/02
11/11/02
04/10/03
09/07/03
02/04/04
07/03/04
11/30/04
04/29/05
09/26/05
02/23/06 ~
07/23/06 ~
12/20/06 ~ I
05/19/07 O"I
10/16/07 ~ 03/14/08 -08/11/08 ~ ""1
01/08/09 t:,
06/07/09 ~ "O
11/04/09 -=-04/03/10 0 08/31/10 <
01/28/11 ~ ""1
06/27/11 ~
11/24/11 ....
9 04/22/12 ~
09/19/12 ---02/16/13 ?
07/16/13 C" -12/13/13 9
05/12/14 "O '-"
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)
5,6 19.87 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 6)9.87 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
5,538.29 05/04/20 82.78 81.58
00 V, 00 0
Depth Below Measuring Point (ft.)
-J V, -J 0 °' V, °' 0 V, V, V, 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 1-3 01/26/06 ~ 06/25/06 ,I;:.. 11/22/06 I -...,l
04/21/07 ~ 09/18/07
02/15/08 """ ~ 07/14/08 "'1
12/11/08 0
05/10/09 ~ "C
10/07/09 e,
03/06/10 0 08/03/10 < 12/31/10 ~ "'1 05/30/11 1-3 10/27/11 ....
03/25/12 a ~
08/22/12 ,-....
01/19/13 ?
06/18/13 C" -11/15/13 a 04/14/14 "C
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
09/04/21
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
5,535.25 05/04/20 86.15 81.55
....
8 \0 0 00 0
Depth Below Measuring Point (ft.)
-.J 0 0\ 0
v,
0
.i:,..
0
(.J.)
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 ,&:;;..
11/22/06 I 00 04/21/07 ~ 09/18/07
02/15/08 """' ~ 07/14/08 "1
12/11/08 0
05/10/09 ~ ~ 10/07/09 """' ::r 03/06/10 0 08/03/10 < 12/31/10 ~ "1 05/30/11 ~ 10/27/11 -· 03/25/12 9 ~
08/22/12 ,,-....
01/19/13 ?
06/18/13 'r:r'
11/15/13 -9 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
09/04/21
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.l
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
5,569.04 05/04/20 68.55 67.07
-.J 0 O'\ 00 O'\ O'\
Depth Below Measuring Point (ft.)
i O'\ tv ~ Vl 00 Vl
O'\
Vl +'" Vl tv Vl 0
12/20/99
05/18/00
10/15/00
03/14/01
08/11/01
01/08/02
06/07/02
11/04/02
04/03/03
08/31/03
01/28/04
06/26/04
•· 11/23/04
04/22/05
09/19/05
02/16/06 ~
07/16/06 ~
12/13/06 ~ I
05/12/07 "° 10/09/07 ~ 03/07/08 -08/04/08 ~ ~
01/01/09 ~ 05/31/09 ~
10/28/09 "'C -03/27/10 =-
08/24/10 0
01/21/11 < ~
06/20/11 ~
~ 11/17/11 ...
04/15/12 9
09/12/12 ~ --02/09/13 ?
07/09/13 C"' 12/06/13 -05/05/14 9 "'C 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
09/25/21
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
5,566.27 05/04/20 67.97 65.72
00 0 -...I 0 °' 0
Depth Below Measuring Point (ft.)
v,
0 .j::.. 0 w 0 N 0 -0 0
01/03/02
06/02/02
10/30/02
03/29/03
08/26/03
01/23/04
06/21/04
11/18/04
04/17/05
09/14/05
02/11/06
07/11/06
12/08/06 ~ 05/07/07 ! 10/04/07
03/02/08 I
~
07/30/08 Q
12/27/08 ~ 05/26/09 ""' ~
10/23/09 ~
03/22/10 C,
~ 08/19/10 ~ ""' 01/16/11 =-
06/15/11 0
11/12/11 ~ ~
04/10/12 ~
~ 09/07/12 -· 02/04/13 a ~
07/04/13 --12/01/13 ?
04/30/14 C" -09/27/14 a ~
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) Monitoring (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.Ql
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 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
5,529.85 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
5,533.02 05/04/20 90.60 88.90
.....
8 \0 V, \0 0
Depth Below Measuring Point (ft.)
00 V, 00 0 -..J V, -..J 0 0\ V, 0\ 0
V,
V,
V,
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 ~
07/30/08 ~
12/27/08 ~ 05/26/09 ""'" ~
10/23/09 ""'l
03/22/10 0 ~
08/19/10 ~ ""'" 01/16/11 =r"
06/15/11 0
11/12/11 <l ~
04/10/12 ""'l
~ 09/07/12 ...
9 02/04/13 ~
07/04/13 --12/01/13 ?
"a' 04/30/14 -09/27/14 9 ~
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 4-12
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) Monitorin; (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 TW4-12
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) Monitorin; (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) Monitorin~ (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
5,569.45 05/04/20 54.78 52.93
Ul
\0
Ul
""'"
Depth Below Measuring Point (ft.)
""'" \0 t (.>)
\0
v)
""'" 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 1--l N 03/19/09 ~ 08/16/09
01/13/10 ""'" tt)
06/12/10 "1
~ 11/09/10 tt)
"t::, 04/08/11 ""'" =-09/05/11 0 02/02/12 <
07/01/12 tt)
"1
11/28/12 ~ ...
04/27/13 a
09/24/13 tt) --02/21/14 ?
07/21/14 a" -12/18/14 a
05/17/15 "t::,
'-'
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
07/14/21
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
5,53 I .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
5,563.82 05/04/20 56.12 54.27
...... 0 0 '° 0
Depth Below Measuring Point (ft.)
00 0 -..J 0 0\ 0 Vl 0 ~ 0
08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07 ~
12/25/07 ~
05/23/08 .&;.
I
10/20/08 """" ~
03/19/09 ~ 08/16/09 l'°t"
01/13/10 t,
"1
06/12/10 ~
11/09/10 t,
"Cl
04/08/11 ~
09/05/11 0
02/02/12 ~ t,
07/01/12 "1
11/28/12 ~ ...
04/27/13 a t,
09/24/13 --02/21/14 ?
07/21/14 a" -12/18/14 a
05/17/15 "Cl ..._,
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
07/14/21
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.l
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.l
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
5,535.12 05/04/20 77.65 75.8
.....
8
~ ., \0 0
• •
~. •
• • • • •
••
••
0
~
~
•
00 0
• • • • • •
•
' . •• • • • ••
0 •• 0
Depth Below Measuring Point (ft.)
-.l
0 g V, 0 .i::,. 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 ~ 12/25/07 ! 05/23/08 I
10/20/08 ""'6 ....
03/19/09 i 08/16/09
01/13/10 ~ ~ "1 06/12/10 ~ 11/09/10 ~ ~ 04/08/11 ~ =-09/05/11 0 02/02/12 <
07/01/12 ~ ,.,
11/28/12 ~ -· 04/27/13 e
09/24/13 ~ .-..
02/21/14 ?
07/21/14 O" -12/18/14 e
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
07/14/21
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
5,539.82 05/04/20 85 .63 84.33
.....
8 8
Depth Below Measuring Point (ft.)
00 0 -.J 0 °' 0 Vl 0 ~
f-------+----+-----1-----+----.i----+ 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 .___ __________ __,_ ___ __._ ___ __._ _________ ..._07/14/21
~ N O'\
~ ;-
"1
~ ~ "'C ~
0 ~ "1
t-3 -· a ~ --?
O" -a "'C --
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,562.91 08/23/02 61.11 57.74
5,563.45 09/11/02 60.57 57.20
5,563.75 10/23/02 60.27 56.90
5,563.68 11/22/02 60.34 56.97
5,563.68 12/03/02 60.34 56.97
5,564.16 01/09/03 59.86 56.49
5,564.25 02/12/03 59.77 56.40
5,564.53 03/26/03 59.49 56.12
5,564.46 04/02/03 59.56 56.19
5,564.79 05/01/03 59.23 55.86
5,564.31 06/09/03 59.71 56.34
5,563.29 07/07/03 60.73 57.36
5,562.76 08/04/03 61.26 57.89
5,561.73 09/11/03 62.29 58.92
5,561.04 10/02/03 62.98 59.61
5,560.39 11/07/03 63.63 60.26
5,559.79 12/03/03 64.23 60.86
5,561.02 01/15/04 63.00 59.63
5,561.75 02/10/04 62.27 58.90
5,562.98 03/28/04 61.04 57.67
5,563.29 04/12/04 60.73 57.36
5,564.03 05/13/04 59.99 56.62
5,564.09 06/18/04 59.93 56.56
5,565.08 07/28/04 58.94 55.57
5,564.56 08/30/04 59.46 56.09
5,563.55 09/16/04 60.47 57.10
5,561.79 10/11/04 62.23 58.86
5,560.38 11/16/04 63.64 60.27
5,559.71 12/22/04 64.31 60.94
5,559.14 01/18/05 64.88 61.51
5,558.65 02/28/05 65.37 62.00
5,558.54 03/15/05 65.48 62.11
5,558.22 04/26/05 65.80 62.43
5,558.54 05/24/05 65.48 62.11
5,559.24 06/30/05 64.78 61.41
5,559.38 07/29/05 64.64 61.27
5,559.23 09/12/05 64.79 61.42
5,557.67 12/07/05 66.35 62.98
5,557.92 03/08/06 66.10 62.73
5,558.47 06/13/06 65.55 62.18
5,558.42 07/18/06 65.60 62.23
5,558.09 11/07/06 65.93 62.56
5,557.34 02/27/07 66.68 63.31
Water Levels and Data over Time
White Mesa Mill -Well 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
5,547.11 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 72.00 68.63
5,556.25 05/04/20 72.40 69.03
00 V, 00 0
Depth Below Measuring Point (ft.)
-..J V, -..J 0 0-. V, 0-. 0
V, V,
V, 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..
I
10/20/08 ~ ~ 03/19/09 ~ 08/16/09
01/13/10 -~ "'1 06/12/10 t:,
11/09/10 ~ ~ 04/08/11 -=-09/05/11 0 02/02/12 <
07/01/12 ~ "'1
11/28/12 ~ ....
04/27/13 9
09/24/13 ~ --02/21/14 ?
07/21/14 C" -12/18/14 9
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
07/14/21
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) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5,542.17 08/23/02 83.07 81.24
5,542.39 09/11/02 82.85 81.02
5,542.61 10/23/02 82.63 80.80
5,542.49 11/22/02 82.75 80.92
5,542.82 12/03/02 82.42 80.59
5,543.03 01/09/03 82.21 80.38
5,543.04 02/12/03 82.20 80.37
5,543.41 03/26/03 81.83 80.00
5,543.69 04/02/03 81.55 79.72
5,543.77 05/01/03 81.47 79.64
5,544.01 06/09/03 81.23 79.40
5,544.05 07/07/03 81.19 79.36
5,543.99 08/04/03 81.25 79.42
5,544.17 09/11/03 81.07 79.24
5,544.06 10/02/03 81.18 79.35
5,544.03 11/07 /03 81.21 79.38
5,543.94 12/03/03 81.30 79.47
5,543.98 01/15/04 81.26 79.43
5,543.85 02/10/04 81.39 79.56
5,544.05 03/28/04 81.19 79.36
5,544.33 04/12/04 80.91 79 .08
5,544.55 05/13/04 80.69 78.86
5,544.59 06/18/04 80.65 78.82
5,545.08 07/28/04 80.16 78.33
5,545.26 08/30/04 79.98 78.15
5,545.48 09/16/04 79.76 77.93
5,545.61 10/11/04 79.63 77.80
5,545.46 11/16/04 79.78 77.95
5,545.66 12/22/04 79.58 77.75
5,545.33 01/18/05 79.91 78.08
5,545.51 02/28/05 79.73 77.90
5,545.57 03/15/05 79.67 77.84
5,545.46 04/26/05 79.78 77.95
5,545.45 05/24/05 79.79 77.96
5,545.33 06/30/05 79.91 78.08
5,545.16 07/29/05 80.08 78.25
5,545.54 09/12/05 79.70 77.87
5,545.77 12/07/05 79.47 77.64
5,546.09 03/08/06 79.15 77.32
5,545.94 06/13/06 79.30 77.47
5,545.94 07/18/06 79.30 77.47
5,546.24 11/07/06 79.00 77.17
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) Monitorin!? (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 bhv.l\llP) (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
5,544.99 05/05/20 80.25 78.42
00 +'-00 N
Depth Below Measuring Point (ft.)
00 0 -:i 00 -:i
O'I
-:i +'--:i 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 ~
10/20/08 ~ N
03/19/09 ~ 08/16/09
01/13/10 -('I)
06/12/10 ~ e:,
11/09/10 ('I)
04/08/11 "'O -09/05/11 =-0 02/02/12 <
07/01/12 ('I)
~
11/28/12 ~ ...
04/27/13 a
09/24/13 ('I)
,-....
02/21/14 ~
07/21/14 -a--12/18/14 a
05/17/15 "'O '-'
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
07/14/21
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 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
5,585.15 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
5,569.68 05/04/20 71.60 69.45
00 0 --..) 0 0\ 0
Depth Below Measuring Point (ft.)
VI 0 ~ 0 w 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 I
10/20/08 """"' 00 03/19/09 ~ 08/16/09
01/13/10 f"'I'-~
06/12/10 "1
t:::,
11/09/10 ~ "'Cl 04/08/11 ~ 09/05/11 0 02/02/12 <
07/01/12 ~ "1
11/28/12 ""'3 ...
04/27/13 e
09/24/13 ~ -02/21/14 ?
07/21/14 'a' -12/18/14 e
05/17/15 "'Cl '-'
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
07/14/21
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 (q 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) Monitoring (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
5,563.21 05/04/20 68.18 66.32
-8 \Ci 0
Depth Below Measuring Point (ft.)
00 0 --..l 0 °' 0 Vl """ 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
10/10/06 ""'3
03/09/07 ~
08/06/07 ,&;;:..
I
01/03/08 i,...
~
06/01/08 ~ 10/29/08
03/28/09 -('D
08/25/09
.,
e,
01/22/10 ('D
06/21/10 "t:S -11/18/10 =-
04/17/11 0 < 09/14/11 ('D .,
02/11/12 ""'3 07/10/12 ... a 12/07/12 ('D
05/06/13 -.. ~ 10/03/13 .
03/02/14 ~ -07/30/14 a
12/27/14 "t:S '-'
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
07/23/21
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
5,559.63 05/04/20 69.90 68.89
Depth Below Measuring Point (ft.)
-0 \0 00 -...J °' V, .j::..
0 0 0 0 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
09/06109 ~
02/03/10 ~ I
07/03/10 N = 11/30/10 ~ 04/29/11 """ ~
09/26/11 l"I
C,
02/23/12 ~ "'Q
07/22/12 """ =r"
12/19/[2 0 ~
05/18/13 ~ l"I
· 10/15/13 ~ ...
03/14/14 a ~
08/11/14 --?
01/08/15 er -06/07/15 a "'Q
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
[2/13/19
05/11/20
[0/08/20
03/07/21
Water Levels and Data over Time
White Mesa Mill -Well TW4-21
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.20 5,639.35 1.15 118.8
5,582.98 07/29/05 56.37 55.22
5,583.43 08/30/05 55.92 54.77
5,581.87 09/12/05 57.48 56.33
5,580.50 12/07/05 58.85 57.70
5,583.64 03/08/06 55.71 54.56
5,580.55 06/13/06 58.80 57.65
5,578.95 07/18/06 60.40 59.25
5,578.47 11/07/06 60.88 59.73
5,579.53 02/27/07 59.82 58.67
5,578.07 05/02/07 61.28 60.13
5,583.41 08/15/07 55.94 54.79
5,583.45 10/10/07 55.90 54.75
5,586.47 03/26/08 52.88 51.73
5,579.16 06/24/08 60.19 59.04
5,579.92 08/26/08 59.43 58.28
5,577.37 10/14/08 61.98 60.83
5,578.00 03/10/09 61.35 60.20
5,580.14 06/24/09 59.21 58.06
5,578.72 09/10/09 60.63 59.48
5,579.99 12/11/09 59.36 58.21
5,582.81 03/11/10 56.54 55.39
5,582.23 05/11/10 57.12 55.97
5,576.60 09/29/10 62.75 61.60
5,581.14 12/21/10 58.21 57.06
5,579.53 02/28/11 59.82 58.67
5,584.17 06/21/11 55.18 54.03
5,584.80 09/20/11 54.55 53.40
5,585.68 12/21/11 53.67 52.52
5,585.24 03/27/12 54.11 52.96
5,585.26 06/28/12 54.09 52.94
5,585.16 09/27/12 54.19 53.04
5,585.25 12/28/12 54.10 52.95
5,582.84 03/28/13 56.51 55.36
5,581.79 06/27/13 57.56 56.41
5,580.89 09/27/13 58.46 57.31
5,577.45 12/20/13 61.90 60.75
5,576.01 03/27/14 63.34 62.19
5,574.08 06/25/14 65.27 64.12
5,573.20 09/25/14 66.15 65.00
5,576.13 12/17/14 63.22 62.07
5,578.19 03/26/15 61.16 60.01
5,574.85 06/22/15 64.50 63.35
Water Levels and Data over Time
White Mesa Mill -Well TW4-21
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.20 5,639.35 1.15 118.8
5,573.05 09/30/15 66.30 65.15
5,569.88 12/02/15 69.47 68.32
5,571.81 03/30/16 67.54 66.39
5,571.86 06/30/16 67.49 66.34
5,570.82 09/29/16 68.53 67.38
5,570.45 12/21/16 68.90 67.75
5,574.53 03/30/17 64.82 63.67
5,569.91 06/27/17 69.44 68.29
5,569.49 09/28/17 69.86 68.71
5,566.87 11/30/17 72.48 71.33
5,568.10 03/28/18 71.25 70.10
5,568.17 06/22/18 71.18 70.03
5,567.50 09/24/18 71.85 70.70
5,554.80 12/17/18 84.55 83.40
5,560.92 03/25/19 78.43 77.28
5,561.49 06/24/19 77.86 76.71
5,564.17 08/12/19 75.18 74.03
5,555.91 11/18/19 83.44 82.29
5,561.05 02/10/20 78.30 77.15
5,567.23 05/04/20 72.12 70.97
8 00 0 --.J 0
Depth Below Measuring Point (ft.)
~ V,
0 t v:,
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
04/29/1 I
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 t,J
~
~ ;-
~
~ ~ ~ ;.
0 < ~ ~
~ -· e ~ --?
a--e ~ '-'
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
5,558.77 05/04/20 70.23 69.06
......
8 \0 0 00 0
Depth Below Measuring Point (ft.)
-.I 0 ~ Vl 0
.i:,..
0
u.)
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
,l;;I,,.
I N
11/30/10 N
04/29/11 ~ -09/26/11 ~ ""1
02/23/12 ~ ~
07/22/12 "'C
12/19/12 ~
0 05/18/13 < ~
10/15/13 ""1
03/14/14 ~ ... = 08/11/14 ~ --01/08/15 ?
06/07/15 O"' -11/04/15 = "'C
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 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
5,538.89 09/13/07 68.48 66.88
5,538.80 10/10/07 68.57 66.97
5,539.25 11/30/07 68.12 66.52
5,539.49 12/11/07 67.88 66.28
5,539.19 01/08/08 68.18 66.58
5,539.44 02/18/08 67.93 66.33
5,539.54 03/26/08 67.83 66.23
5,539.71 04/23/08 67.66 66.06
5539.48 05/30/08 67.89 66.29
5,539.53 06/24/08 67.84 66.24
5,539.44 07/16/08 67.93 66.33
5,539.68 08/26/08 67.69 66.09
5,541.18 09/10/08 66.19 64.59
5,539.57 10/14/08 67.80 66.20
5,539.29 11/26/08 68.08 66.48
5,539.55 12/29/08 67.82 66.22
5,540.15 01/26/09 67.22 65.62
5,539.74 02/24/09 67.63 66.03
5,539.86 03/06/09 67.51 65.91
5,539.72 04/07/09 67.65 66.05
5,539.84 05/29/09 67.53 65.93
5,540.12 06/30/09 67.25 65.65
5,540.12 07/31/09 67.25 65.65
5,540.27 08/31/09 67.10 65.50
5,540.13 09/10/09 67.24 65.64
5,540.64 12/11/09 66.73 65.13
5,541.15 03/11/10 66.22 64.62
5,541.61 05/11/10 65.76 64.16
5,541.47 09/29/10 65.90 64.30
5,541.54 12/21/10 65.83 64.23
5,541.54 02/28/11 65.83 64.23
5,541.98 06/21/11 65 .39 63 .79
5,541.90 09/20/11 65.47 63.87
5,542.58 12/21/11 64.79 63.19
5,542.59 03/27/12 64.78 63.18
5,542.61 06/28/12 64.76 63.16
5,542.92 09/27/12 64.45 62.85
5,542.61 12/28/12 64.76 63.16
5,543.48 03/28/13 63.89 62.29
5,543.23 06/27/13 64.14 62.54
5,543.12 09/27/13 64.25 62.65
5,542.96 12/20/13 64.41 62.81
Water Levels and Data over Time
White Mesa Mill -Well TW4-23
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) {blw.LSD) Well
5,605.77 5,607.37 1.60 116.4
5,542.35 03/27/14 65.02 63.42
5,541.42 06/25/14 65.95 64.35
5,540.65 09/25/14 66.72 65.12
5,540.34 12/17/14 67.03 65.43
5,539.47 03/26/15 67 .90 66.30
5,539.22 06/22/15 68 .15 66.55
5,538.82 09/30/15 68.55 66.95
5,538.28 12/02/15 69.09 67.49
5,538.29 03/30/16 69.08 67.48
5,537 .60 06/30/16 69.77 68 .17
5,537.07 09/29/16 70.30 68.70
5,536.86 12/21/16 70.51 68.91
5,536.91 03/30/17 70.46 68.86
5,536.49 06/27/17 70.88 69 .28
5,536.18 09/28/17 71.19 69.59
5,535 .72 11/30/17 71.65 70.05
5,535.62 03/28/18 71.75 70.15
5,535.34 06/22/18 72.03 70.43
5,534.93 09/25/18 72.44 70.84
5,534.64 12/17/18 72.73 71.13
5,534.23 03/25/19 73.14 71.54
5,534.22 06/24/19 73.15 71.55
5,534.01 08/12/19 73.36 71.76
5,533.51 11/18/19 73 .86 72.26
5,533.26 02/10/20 74.11 72.51
5,532.76 05/04/20 74.61 73.01
-.l 0\ -.l .j:,..
Depth Below Measuring Point (ft.)
-.l N -.l 0 0\ 00 0\ 0\ 0\ 0\ .j::,. N
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10
05/25/11 ~
10/22/11 ~ I
03/20/12 N ~
08/17/12 ~ -01/14/13 t'D "1
06/13/13 ~ t'D
11/10/13 "Cl -=-04/09/14 0 -id
09/06/14 t'D "1
02/03/15 ~ ....
07/03/15 = t'D ,-..
11/30/15 ~
04/28/16 Q"' -
09/25/16 = "Cl -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
04/02/21
Water Levels and Data over Time
White Mesa Mill -Well TW4-24
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.70 5,627.83 2.13 114.8
5,570.61 09/13/07 57.22 55.09
5,570.53 10/10/07 57.30 55.17
5,571.16 11/30/07 56.67 54.54
5,571.30 12/11/07 56.53 54.40
5,571.03 01/08/08 56.80 54.67
5,571.22 02/18/08 56.61 54.48
5,571.43 03/26/08 56.40 54.27
5,571.68 04/23/08 56.15 54.02
5571.52 05/30/08 56.31 54.18
5,571.34 06/24/08 56.49 54.36
5,571.28 07/16/08 56.55 54.42
5,571.34 08/26/08 56.49 54.36
5,571.23 09/10/08 56.60 54.47
5,571.12 10/14/08 56.71 54.58
5,570.95 11/26/08 56.88 54.75
5,570.92 12/29/08 56.91 54.78
5,571.65 01/26/09 56.18 54.05
5,571.31 02/24/09 56.52 54.39
5,571.37 03/06/09 56.46 54.33
5,571.21 04/07/09 56.62 54.49
5,571.23 05/29/09 56.60 54.47
5,571.42 06/30/09 56.41 54.28
5,571.38 07/31/09 56.45 54.32
5,571.48 08/31/09 56.35 54.22
5,571.28 09/10/09 56.55 54.42
5,571.64 12/11/09 56.19 54.06
5,571.86 03/11/10 55.97 53.84
5,571.91 05/11/10 55.92 53.79
5,572.18 09/29/10 55 .65 53.52
5,571.86 12/21/10 55.97 53.84
5,571.78 02/28/11 56.05 53.92
5,572.40 06/21/11 55.43 53.30
5,572.19 09/20/11 55.64 53.51
5,573.02 12/21/11 54.81 52.68
5,573.03 03/27/12 54.80 52.67
5,573.02 06/28/12 54.81 52.68
5,573.13 09/27/12 54.70 52.57
5,573.05 12/28/12 54.78 52.65
5,566.53 03/28/13 61.30 59.17
5,564.63 06/27/13 63.20 61.07
5,570.01 09/27/13 57.82 55.69
5,566.85 12/20/13 60.98 58.85
5,562.33 03/27/14 65.50 63.37
Water Levels and Data over Time
White Mesa Mill -Well TW4-24
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.70 5,627.83 2.13 114.8
5,563.43 06/25/14 64.40 62.27
5,563.43 09/25/14 64.40 62.27
5,560.97 12/17/14 66.86 64.73
5,561.95 03/26/15 65.88 63.75
5,565.38 06/22/15 62.45 60.32
5,562.61 09/30/15 65.22 63.09
5,560.91 12/02/15 66.92 64.79
5,563.69 03/30/16 64.14 62.01
5,565.64 06/30/16 62.19 60.06
5,565.35 09/29/16 62.48 60.35
5,563.33 12/21/16 64.50 62.37
5,565.27 03/30/17 62.56 60.43
5,565.86 06/27/17 61.97 59.84
5,565.21 09/28/17 62.62 60.49
5,559.24 11/30/17 68.59 66.46
5,564.78 03/28/18 63.05 60.92
5,564.83 06/22/18 63.00 60.87
5,565.47 09/24/18 62.36 60.23
5,549.72 12/17/18 78.11 75.98
5,559.52 03/25/19 68.31 66.18
5,546.68 06/24/19 81.15 79.02
5,549.54 08/12/19 78.29 76.16
5,554.44 11/18/19 73.39 71.26
5,563.62 02/10/20 64.21 62.08
5,558.32 05/04/20 69.51 67.38
\Ci 0 0
00 0 0 " 0 0
Depth Below Measuring Point (ft.)
°' 0 0
V, 0
0
~ 0
0
t,;)
0 0
Iv 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 lo-3 ~ 10/22/11 ,&;..
I
03/20/12 N ,&;..
08/17/12 ~ """ 01/14/13 ~ "1
06/13/13 ~ ~
11/10/13 "Cl """ =-04/09/14 0 ~ 09/06/14 ~ "1
02/03/15 lo-3 ...
07/03/15 9 ~ ----11/30/15 ?
04/28/16 a' -
09/25/16 9 "Cl --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
04/02/21
Water Levels and Data over Time
White Mesa Mill-Well TW4-25
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,642.82 5,644.91 2.09 136.7
5,601.86 09/13/07 43.05 40.96
5,601.89 10/10/07 43.02 40.93
5,602.57 11/30/07 42.34 40.25
5,602.82 12/11/07 42.09 40.00
5,601.94 01/08/08 42.97 40.88
5,599.13 02/18/08 45.78 43.69
5,597.11 03/26/08 47.80 45.71
5,595 .51 04/23/08 49.40 47.31
5594.42 05/30/08 50.49 48.40
5,594.26 06/24/08 50.65 48.56
5,586.67 07/16/08 58.24 56.15
5,594.17 08/26/08 50.74 48.65
5,594.23 09/10/08 50.68 48.59
5,594.12 10/14/08 50.79 48.70
5,594.06 11/26/08 50.85 48.76
5,594.87 12/29/08 50.04 47.95
5,595.89 01/26/09 49.02 46.93
5,596.27 02/24/09 48.64 46.55
5,596.47 03/06/09 48.44 46.35
5,596.74 04/07/09 48.17 46.08
5,597.55 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 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
5,584.79 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 09/29116 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
5,572.46 05/04/20 72.45 70.36
Depth Below Measuring Point (ft.) --N 0 00 0\ ~ N 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 1--3 ~ 10/22/11 ,&;:,..
I
03/20/12 N !.II
08/17/12 ~ -01/14/13 ~ "'1
06/13/13 ~ ~
11/10/13 ~ -=-04/09/14 0 < 09/06/14 ~ "'1
02/03/15 1--3 ...
07/03/15 e ~ --11/30/15 ?
04/28/16 'a' -
09/25/16 a ~ '-'
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
04/02/21
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
5,529.08 05/04/20 72.60 70.90
-.J .j::,.
8
-.J N
8
Depth Below Measuring Point (ft.)
-.J 0
0 0
0\ 00
8
0\ 0\
0 0
i 0\ 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
05/06/13 N °'
10/03/13 ~ -03/02/14 ~ "1
~ 07/30/14 ~ "O
12/27/14 e,
0
05/26/15 < ~ "1
10/23/15 ~ .... a
03/21/16 ~ --08/18/16 ?
a' -01/15/17 a "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
02/23/21
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
5,528.97 05/04/20 78.97 77.22
I.Cl N b 0
I.Cl 0 b 0
Depth Below Measuring Point (ft.)
00 00 b 0
00 a,
b 0
00 .i,.
b 0
00 N b 0
00 0 b 0
.......
00
b 0
04/17/11
09/14/11
02/11/12
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
~
07/30/14 ~ ,I;;..
I
12/27/14 N -...l
05/26/15 ~
'""'" ~
10/23/15 ~
0 ~
03/21/16 ~
'""'" =-
08/18/16 0 < ~ ~ 01/15/17 ~ -· 06/14/17 a ~ --11/11/17 ?
O" -04/10/18 a ~ ..._,
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 TW4-28
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
5,569.01 05/04/20 47.99 44.51
O'I 0
8
Vo 0 g
Depth Below Measuring Point (ft.)
~ W N 0 0 0 o o o 0 0 0
••
•
••
0
•
~
••
p
•
'
0
•
••
•
0
·~
~
•
0
~
......
0 0
8 g
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
~
12/27/14 ~ .a;.
I N
05/26/15 QC
10/23/15 ~ """ ~ "'1
03/21/16 ~ ~ "O """ 08/18/16 =-0 -l!!l
01/15/17 ~ "'1
~ ....
06/14/17 9 ~ ,-._
11/11/17 ?
'Q" -04/10/18 9 "O '-"
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 TW4-29
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
5,528.51 05/04/20 77.53 74.05
-..J I.O 0 0
-..J 00
0 0
Depth Below Measuring Point (ft.) -J -..J -..J -..J -..J
-..J 0-. VI ~ W o o o o o 0 0 0 0 0
-..J N 8
-..J -8
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
~
12/27/14 ~ I N
05/26/15 \C
~ 10/23/15 -~
""'
03/21/16 c:,
~ ~ -=-08/18/16 0 ~ ~ 01/15/17 ""' ~ -· 06/14/17 a ~ -..
11/11/17 ?
a' -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 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
5,527.73 05/04/20 75.08 71.6
-.J 00
VI 0
-.J 00
0 0
Depth Below Measuring Point (ft.)
-.J -.J
VI 0
-.J -.J
8
-.J
O'I
VI 0
-.J O'I
8
-.J VI
VI 0
-.J VI
8
-.J .i:..
VI 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~ ~ 12/27/14 ~ I ~ = 05/26/15 ~
"""" 10/23/15 ~ "'1
~
03/21/16 ~ "'C
"""" ::r
08/18/16 0 -id ~
01/15/17 "'1
~ -· 06/14/17 9 ~ ---~ 11/11/17 .
'r:f' -04/10/18 9 "'C ..._,,
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
5,528.01 05/04/20 76.57 73.09
00 0\
8
00 ~
8
Depth Below Measuring Point (ft.)
00 N
8
00 0
8
-.I 00
8
-.I -.I 0\ ~
0 0 0 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
~
07/30/14 ~ .&;.
I ~ 12/27/14 ~
05/26/15 ~
"""' n> "1
10/23/15 ~ n> "'O
03/21/16 ~
0
08/18/16 < n> "1
01/15/17 ~ ...
9 n>
06/14/17 ---?
11/11/17 C" -9
04/10/18 "'O '-'
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
5,556.29 05/04/20 55.55 53.91
Vl
°' 8
\.J\ Vl 0 0
Vl ~
8
Depth Below Measuring Point (ft.)
Vl w
8
Vl N
8
Vl -0 0
Vl
0
8
~ I.O
8
~ 00
0 0
~ -.J
0 0
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 tM N
~ ;-
"'1
~ ~ ~ g.
0 < ~ "'1
~ .... = ~ ,-..,
?
C" 9 ~ "-'
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
5,529.68 05/04/20 77.05 75.52
-..J 00
0 0
-.l -..J
8
-..J 0\
8
Depth Below Measuring Point (ft.)
-..J VI
8
-..J
""" 0 0
-..J w
8
-..J N 8
-..J ......
0 0
-..J 0\ 0 I.Cl
0 8 0
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 CM CM
~ -~ "1
0 ~ "'C ;.
0 ~ "1
~ -· a ~ --?
O" §"
"'C '-'
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) (L D) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,601.60 5,603.34 1.74 95.74
5,534.04 09/27/13 69.30 67.56
5,534.14 12/20/13 69.20 67.46
5,533.89 03/27/14 69.45 67.71
5,533.32 06/25/14 70.02 68.28
5,532.94 09/25/14 70.40 68.66
5,532.99 12/17/14 70.35 68.61
5,532.37 03/26/15 70.97 69.23
5,532.24 06/22/15 71.10 69.36
5,532.08 09/30/15 71.26 69.52
5,531.79 12/02/15 71.55 69.81
5,531.80 03/30/16 71.54 69.80
5,531.28 06/30/16 72.06 70.32
5,530.87 09/29/16 72.47 70.73
5,530.74 12/21/16 72.60 70.86
5,530.79 03/30/17 72.55 70.81
5,530.43 06/27/17 72.91 71.17
5,530.12 09/28/17 73.22 71.48
5,530.01 11/29/17 73.33 71.59
5,529.84 03/28/18 73.50 71.76
5,529.64 06/21/18 73.70 71.96
5,529.39 09/25/18 73.95 72.21
5,529.23 12/17/18 74.11 72.37
5,528.83 03/25/19 74.51 72.77
5,528.84 06/24/19 74.50 72.76
5,528.75 08/12/19 74.59 72.85
5,528.30 11/18/19 75.04 73.30
5,528.18 02/10/20 75.16 73.42
5,527.62 05/04/20 75.72 73.98
OZ/8I/90
61/170/ZO -C. e -~
~ "-"
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0 ..= -C. ~ 91/0l/~O ~ s.. ~ -~
~ ~ I i 171/LZ/ZI
~
£1/171/80
Zl/10/170
0 0 8 0 8 0 0 ~ 0 0 ~ ~ ~ ~ 0 0 0
00 0\ 0 ..... N (") ~ V) \0 r-.: \0 \0 r:--r-r-r-r-r:--r-r-
(":JJ) lll!Od ~uµnsugw Mopg qldgQ
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
5,524.80 05/04/20 75.07 73.87
OZ/81/90
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171/LZ/ZI
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0 0 0 0 0 0 0 0 0 ~ 00 0 N -.:I" ID 00 C: ~
C<) C<) ...,j-...,j-...,j-...,j-...,j-on on r--r--r--r--r--r--r--r--r--
(·:y) lU!Od iuµnsl?:lw: MOPS: qld~a
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
5,558.94 05/04/20 57.65 56.24
OZ/81/90
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171/LZ/ZI
£1/171/80
0 0 0 0 0 0 0 0 0 0 0 00 0 N s::t" \D 00 C: <"! ~ ~ 00
l/') \C) \C) \C) \C) \C) r--r--r--: r--r--: l/') l/') l/') l/') l/') l/') l/') l/') l/') l/') l/')
('1;J) lll~Od ~uµnsugw MOJ;}S: qldgQ
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
5,555.68 05/04/20 76.17 74.45
..... N 0 g
.....
8 g
Depth Below Measuring Point (ft.)
00 0 0 0
0\ 0 g
,is.. 0 g ~ 0 0
0 g
1------+------+------+----~----+------t-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
06/18/20
.__ ________ __._ ___ __._ ___ _... ___________ _._ 01/04/21
~ ~ ... I ~ -..,l
1 """ ~ "1
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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) Monitoring (blw.MP) (blw.LSD) Well
5,628.82 5,629.99 1.17 113.92
5,576.59 12/21/16 53.40 52.23
5,576.62 03/30/17 53.37 52.20
5,576.07 06/27/17 53.92 52.75
5,577.49 09/28/17 52.50 51.33
5,575.68 11/30/17 54.31 53.14
5,574.69 03/28/18 55.30 54.13
5,574.25 06/22/18 55.74 54.57
5,573.63 09/25/18 56.36 55.19
5,572.31 12/17/18 57.68 56.51
5,572.51 03/25/19 57.48 56.31
5,572.53 06/24/19 57.46 56.29
5,572.31 08/12/19 57.68 56.51
5,571.90 11/18/19 58.09 56.92
5,571.67 02/10/20 58.32 57.15
5,571.20 05/04/20 58.79 57.62
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
5,544.51 05/04/20 85.05 84.31
OZ/81/90
61/IO/Zl
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Q
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O'\ ~ I ~ ~ E-4 LI/ZZ/60
LI/90/£0
91/81/80
0 0 0 0 0 0 8 0 0 0 0 0 0 ci 0 ci ci ci ci ci N 'tj-\0 00 0 N
(":y) lll!Od .8uµnsu~w MOPS: q1d~a --
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
5,525.81 05/04/20 71.77 69.85
--Q. e -,,Q
~ --~ e .... E-4 .. ~ ;;.
0
..d ..... Q.
~ ~ .. ~ ~
0 "1' I "1' ~ E-4
OZ/OZ/£0
6l/Z:Z/01
611s;vs;o
8I/9Z/ZI
8l/6ZILO
00
\0 0 r--r-N r-
Water Levels and Data over Time
White Mesa Mill -Well TW4-41
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,613.31 5,614.96 1.65 97.8
5,539.24 03/28/18 75.72 74.07
5,526.18 06/22/18 88.78 87.13
5,513.86 09/24/18 101.10 99.45
5,536.53 12/17/18 78.43 76.78
5,521.88 03/25/19 93.08 91.43
5,527.89 06/24/19 87.07 85.42
5,530.75 08/12/19 84.21 82.56
5,536.69 11/18/19 78.27 76.62
5,538.67 02/10/20 76.29 74.64
5,526.94 05/04/20 88.02 86.37
,-.,
Q. s -,.c.
4:! ..._,
~ s ·-~
~ ~ ~ 0
-= Q.
~ ~
~ ~ ...,_
~
~ ~ I ~ ~ ~
OZ/OZ/£0
6l/ZZ/0I
6I/~Z/~O
8l/9Z/ZI
8I/6Z/l0
0 0 N 0 00 0 0 -
Water Levels and Data over Time
White Mesa Mill-Well TW4-42
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) Monitorin~ (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
5,526.10 05/04/20 68.60 66.29
--~ e -,.Q
ct: "-"
~ e ... ~ • ~ ,...
0 ..= .....
~ ~ ~ • ~ ..... ;
N ~ I ~ ~ ~
OZ/OZ/£0
61/ZZ/Ol
61/~Z/~O
8I/9Z/Zl
8I/6Z/LO
\0 \0 00 \0 N t"--00 t"--
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 (Connerly MW;.U)
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 614911 100 615 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
Ql 2009 90710 2200 343337.4 755342170 755 l.7 52970 950 200491.5 190466878 190 0.4
Q2 2009 450040 1800 1703401.4 3066122520 3066 6.8 58050 410 219719.3 90084892.5 90 0.2
Q3 2009 90420 2000 342239.7 684479400 684 l.5 57610 850 218053.9 185345773 185 0.4
Q4 2009 322380 1800 1220208.3 2196374940 2196 4.8 61960 1100 234518.6 257970460 258 0.6
QI 2010 68125 1600 257853.1 412565000 413 0.9 61320 780 232096.2 181035036 181 0.4
Q2 2010 84005.33 2100 317960.2 667716366 668 l.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 51121 4591 Sil l. l 60180 970 227781.3 220947861 221 0.5
Ql 2011 76247.6 1700 288597.2 490615182 491 l.l 55 130 450 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 l.2 65618 720 248364.l 178822174 179 0.4
Q4 2011 89735.0 1600 339647.0 543435160 543 l.2 50191.3 1800 189974.1 341953327 342 0.8
Ql 2012 90376.4 1500 342074.7 513112011 513 l.l 31440.1 2400 11 9000.8 285601868 286 0.6
Q2 2012 90916.5 1400 344118.8 481766269 482 l.l 26701.2 3000 101064.1 303192353 303 0.7
Q3 2012 9 1607.0 1500 346732.5 520098743 520 I.I 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
QI 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.l 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 l.O 21042.0 2350 79644.0 187163330 187 0.4
Q4 2015 99633.4 1200 377112.4 452534903 453 1.0 19355.6 2680 73260.9 196339335 196 0.4
QI 2016 90882.1 1240 343988.7 426546048 427 0.9 19150.8 2650 72485.8 192087312 192 0.4
Q2 2016 96540.5 1580 365405.8 577341152 577 1.3 22105.7 2220 83670. I 185747565 186 0.4
Q3 2016 79786.4 1430 301 991.5 431847879 432 l.O 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
Ql 2017 76642.3 1450 290091.1 420632103 421 0.9 26107.0 1290 988 15.0 127471344 127 0.3
Q2 2017 72299.8 1430 273654.7 391326282 391 0.9 25921.8 2450 981 14.0 240379332 240 0.5
Q3 2017 95349.3 1400 360897.l 505255941 505 l.l 27489.9 1230 104049.3 127980604 128 0.3
Q4 2017 106679.8 1320 403783.0 532993617 533 1.2 26445.8 2570 100097.4 257250197 257 0.6
Table G-1
................ _. .... ,_.._..,u , .. ,.,...,o '-"' '-JOll'l,•o-.,&'-10 111 ,, .... ,.,....,,. .... SU. UIO._. &'UL<;41 .. ,.11Ul ll .... '"'I Y'O Ul.'-'1 I 1,ll&l~"-'
~-4 TW4=1S (formerl:fMW-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 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 I.I 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 I.I 23791.3 1480 90050.1 133274104 133 0.3
Ql 2019 111746.9 1190 422962.0 503324800 503 1.1 26798.5 11 I 0 101432.3 112589878 113 0.2
Q2 2019 94540.7 1300 357836.5 465187514 465 1.0 24050.2 1280 91030.0 116518409 117 0.3
Q3 2019 95517.7 1180 361534.5 426610704 427 0.9 24181.1 1360 91525.5 124474630 124 0.3
Q4 2019 99220.8 1370 375550.9 514504705 515 I. I 22384.8 1390 84726.5 117769791 118 0.3
QI 2020 102597.0 1230 388329.6 477645370 478 1.1 24J07.0 1100 91245.0 100369495 100 0.2
Q2 2020 101850.7 1250 385504.9 481881077 482 l.l 25418.4 1610 96208.6 154895917 155 0.3
Totals 6461424.28 105.4 2861673.7 37.1
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)
QI 2007 6768986 2660 25620612.0 68150827947 68151 150.2 642290 16240 2431067.7 3.9481E+IO 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
Q4 2007 334350 1100 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 11. I 51030 13000 193148.6 2510931150 251 I 5.5
Q4 2009 454205 4700 1719165.9 8080079848 8080 17.8 208790 15000 790270.2 l.1854E+IO 11 854 26.1
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
Q22011 159238.9 4000 602719.2 2410876946 2411 5.3 67907.7 8100 257030.6 2081948220 2082 4.6
Q32011 141542.6 970 535738.7 519666578.8 520 I.I 72311.2 6800 273697.9 1861145666 1861 4.1
Q4 2011 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 74681.8 2001473178 2001 4.4
Q4 2013 403974 942 1529041.6 1440357178 1440 3.2 19280.2 15700 72975.6 1145716245 1146 2.5
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 I 126643.1 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 I 6341.8 23300 61853.7 1441191513 1441 3.2
QI 2015 60553.0 4660 229193.1 1068039869 1068 2.4 15744.7 19900 59593.7 1185914421 1186 2.6
Q2 2015 75102.8 1570 284264.1 446294633.9 446 1.0 18754.1 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 I 136 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
QI 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 I 12626.4 8840 426290.9 3768411768 3768 8.3 14556.8 27600 55097.5 1520690669 1521 3.4
Q4 2017 108891.2 129 412153.2 53167761.77 53 0.1 14271.0 11600 54015.7 626582526 627 1.4
Table G-1
~ ..... -.--.. ---·---·----.....-·· .... -· ............. ~-..................... _.. ...................... ..................................... ,,11.,.r ........
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.l 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 l.l
04 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 51 4 I. I
Q2 2020 136619.7 7600 517105.6 3930002290 3930 8.7 100713.8 5800 381201.6 2210969393 2211 4.9
Totals 19262306.43 439.6 2569921.69 296.2
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
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 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.l 1700 328810.9 558978527 .5 559 1.2 NA NA NA NA NA NA
QI 2011 73360.0 1800 277667.6 499801680 500 I. I NA NA NA NA NA NA
Q22011 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 l .4 NA NA NA NA NA NA
QI 2012 101616.8 1200 384619.6 461543505.6 462 1.0 NA NA NA NA NA NA
Q2 2012 87759.1 1500 332168.2 498252290.3 498 l.l NA NA NA NA NA NA
Q3 2012 80006.0 1600 302822.7 484516336 485 I.I NA NA NA NA NA NA
Q4 2012 71596 1400 270990.9 379387204 379 0.8 NA NA NA NA NA NA
QI 2013 58716.8 1460 222243.1 324474908.5 324 0.7 l 6677.4 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.l 1256106224.1 1256.1 2.8
QI 2014 58992.9 1260 223288.1 281343039.4 281 0.6 24532.0 12100 92853.6 1123528802.0 1123.5 2.5
Q2 2014 60235.3 1220 227990.6 278148544.8 278 0.6 24193.9 12400 91573.9 J 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 11 24.4 2.5
QI 2015 36941.3 1350 139822.8 188760807.7 189 0.4 22046.9 12700 83447.5 I 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. I 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. I 258 0.6 24517.8 6070 92799.9 563295229.1 563.3 J.2
Q2 2016 61378.0 1780 232315.7 413521999.4 414 0.9 26506.3 8570 100326.3 859796780.9 859.8 1.9
Q3 2016 50104.2 1380 189644.4 261709267.9 262 0.6 22144.1 5840 83815.4 489482044.0 489.5 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
._....._ • ..__., ........... ,_ ... , ....... ,...,,, ...,, _,,, .. .,, ..... ,~010 1 .,_.010"-'T""" ..... 'U.11 .... a ............ T ............... V'' ............. & .... I ii ~
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)
01 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
Q22019 14311.9 1070 54170.5 579624 79 .41 58 0.1 23073.l 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
Ql 2020 14439.2 1100 54652.4 60117609.2 60 0.1 24746.1 3910 93664.0 366226195.0 366.2 0.8
Q2 2020 15347.0 1140 58088.4 66220770.3 66 0.1 25295.3 2530 95742.7 242229057.6 242.2 0.5
Totals 2134896.7 25.6 717172.1 42.0
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-24 TW4-25 -
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
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
QI 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q220!0 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 20 11 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
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.l 0.0 469858.9 0.0 0.0 0.0
Q4 2015 107799.l 25.3 408019.6 10322895.7 10.3 0.023 116420.1 0.0 440650.1 0.0 0.0 0.0
QI 2016 100063.2 22.8 378739.2 8635254.0 8.6 0.019 115483.2 0.0 437103.9 0.0 0.0 0.0
Q2 2016 65233.6 69.6 246909.2 17184878.6 17.2 0.038 125606.0 0.0 475418.7 0.0 0.0 0.0
Q3 2016 51765.8 17.8 195933.6 3487617.2 3.5 0.008 104983.6 0.0 397362.9 0.0 0.0 0.0
Q4 2016 99522.5 20.8 376692.7 7835207.4 7.8 0.017 98681.2 0.0 373508.3 0.0 0.0 0.0
QI 2017 99117.4 18.3 375159.4 6865416.3 6.9 0.015 161.2 l.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 11673 l.9 0.0 441830.2 0.0 0.0 0.0
Table G-1
.._.._.._ .. _. •• _...,.,_,..,._. .. ,.._,,, ....,, -111..,,,,,.._.,,,,, a, .... 01 1..,,,._,,a ._.,, ..... •'\JLO.LI 'I' V l ... 1 1.1 ..... V I 00 1;.f.\. ..... l I '-'101..IV'L.a
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 28.1 369798.3 10391331.8 10.4 0.023 90789.5 0.0 343638.3 0.0 0.0 0.0
Q2 2019 53197.3 28.8 201351.8 5798931.3 5.8 0.013 88302.0 0.0 334223.1 0.0 0.0 0.0
Q3 2019 54445.7 31.l 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
QI 2020 86344.38 61.7 326813.5 20164391.6 20.2 0.044 85049.47 0.0 321912.2 0.0 0.0 0.0
Q2 2020 57634.7 49.4 218147.3 10776478.6 10.8 0.024 90767.9 0.0 343556.6 0.0 0.0 0.0
Totals 3414414.0 1.089 3181696.9 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
QI 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
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
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 20ll NA NA NA NA NA NA NA NA NA NA NA NA
QI 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2015 24569.2 1130 92994.4 I 05083696.9 105.1 0.23 24156.7 1840 91433.1 168236921.5 168.2 0.37
Q2 2015 23989.9 1260 90801.8 114410232.l 114.4 0.25 22029.9 1650 83383.2 137582233.0 137.6 0.30
Q3 2015 23652.0 1060 89522.8 94894189.2 94.9 0.21 21586.9 1310 81706.4 107035405.6 107.0 0.24
Q4 2015 20764.3 1040 78592.9 81736590.5 81.7 0.18 21769.8 2070 82398.7 170565294.5 170.6 0.38
Qi 2016 19255.6 974 72882.4 70987502.4 71.0 0.16 20944.6 1970 79275.3 156172362.7 156.2 0.34
Q2 2016 19588.2 1140 74141.3 84521124.2 84.5 0.19 20624.0 2070 78061.8 161588008.8 161.6 0.36
Q3 2016 15613.5 ll60 59097.1 68552633.1 68.6 0.15 17487.4 1780 66189.8 I 17817860.0 117.8 0.26
Q4 2016 16756.8 1330 63424.5 84354569.0 84.4 0.19 19740.6 1600 74718.2 119549073.6 119.5 0.26
QI 2017 16931.8 519 64086.9 33261081.9 33.3 0.07 19869.7 1570 75206.8 118074698.8 118.1 0.26
Q2 2017 18200.2 977 68887.8 67303338.6 67.3 0.15 18716.7 1940 70842.7 13 7 4 34856.4 137.4 0.30
Q3 2017 17413.6 958 65910.5 63142236.0 63.l 0.14 19338.8 1310 73197.4 95888539.0 95.9 0.21
Q4 2017 14089.8 556 53329.9 29651420.5 29.7 0.07 17327.6 1610 65585.0 105591795.3 105.6 0.23
Table G-1
__ ... ._ .. _ ......... ~ ...................... • ........ ...,.."''''' ........... ...,. ............................. _, • y ., ............. ··-·-· ..............
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 20[8 [2505.7 70.4 47334.1 3332318.8 3.3 0.01 16232.3 764 61439.3 46939591.2 46.9 0.10
Q2 2018 10814.8 942 40934.0 38559845.0 38.6 0.09 16051.4 949 60754.5 57656067.0 57.7 0.13
Q3 2018 9727.3 1010 36817.8 37186008.8 37.2 0.08 14927.2 980 56499.5 55369463.0 55.4 0.12
Q4 2018 9836.7 752 37231.9 27998395.9 28.0 0.06 15464.1 822 58531.6 48112990.4 48.1 0.11
QI 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 9734.1 894 36843.6 32938150.2 32.94 0.07 14106.9 797 53394.6 42555509.4 42.56 0.09
Q4 201 9 9184.3 1070 34762.6 37195955.8 37.20 0.08 14220.9 934 53826.1 50273583.5 50.27 0.11
QI 2020 8796.7 1190 33295.5 39621656.3 39.62 0.09 13162.1 1880 49818.5 93658871 .2 93.66 0.21
Q2 2020 9600.2 499 36336.8 18132041.7 18.13 0.04 14155.6 1070 53578.9 57329472.2 57.33 0.13
Totals 331022.2 2.59 391976.8 4.8 1
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-11 -TW:4-21 -
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
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
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
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q22012 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 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.l 47538600.8 47.5 0.10 132248.7 545 500561.3 272805924.6 272.8 0.60
Q3 2016 2953.8 3200 11180.1 35776425.6 35.8 0.08 110381.9 456 417795.5 190514744.1 190.5 0.42
Q4 2016 3050.2 3180 11545.0 36713122.3 36.7 0.08 130311.3 434 493228.3 214061069.4 214.1 0.47
Ql 2017 2984.2 3310 l 1295.2 37387102.1 37.4 0.08 54333.5 598 205652.3 122980073.9 123.0 0.27
Q2 2017 2845.9 3370 1077 l.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.l 223108736.4 223.1 0.49
Table G-1
"'-._.._.,,. L'-U O _..._._ . ._., ........... 11 'VI ....... 11 ..... 0 "-'1",'I Ill ., .... 111 .................. <Ull"-1 I ..... U,,0~ """''"''·· .... ~I •• U.t.."'I • YIII'"'""''"'
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)
OJ 2018 2571.0 3090 9731.2 30069516.2 30.1 0.07 117832.0 421 445994.1 187763524.5 187.8 0.41
Q2 2018 2513.5 2800 9513.6 26638073.0 26.6 0.06 116681.0 532 441637.6 234951195.2 235.0 0.52
Q3 2018 2170.2 3050 8214.2 2505333 l.4 25.J 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
QI 2019 2342.4 2820 8866.0 25002074.9 25.00 0.1 123264 323 466554.6 150697141.8 150.70 0.3
Q22019 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
Q42019 1983.9 3250 7509.1 24404449.9 24.40 0.1 116167.55 794 439694.2 349117176.3 349.1 0.8
QI 2020 1947.4 2990 7370.9 22039017.9 22.04 0.0 106622.01 844 403564.3 340608275.8 340.6 0.8
Q2 2020 2003.9 2810 7584.8 21313179.8 21.31 0.0 110999.13 767 420131.7 322241019.3 322.2 0.7
Totals 69703.0 1.64 2289451.1 9.80
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) (po~ds) (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
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
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q42011 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 201 2 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 201 2 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
Q l 20 15 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2015 29206.0 30200 11 0544.7 3338450242.0 3338.5 7.4 NA NA NA NA NA NA
Q3 2015 118063.9 19100 446871.9 8535252554.7 8535.3 18.8 NA NA NA NA NA NA
Q4 2015 111737.5 19500 422926.4 8247065531.3 8247.1 18.2 NA NA NA NA NA NA
QI 2016 111591.0 17500 422371.9 7391508862.5 7391.5 16.3 NA NA NA NA NA NA
Q2 2016 119241.2 16200 451327.9 7311512660.4 7311.5 16.1 NA NA NA NA NA NA
Q3 2016 98377.6 15900 372359 5920511534.4 5920.5 13.1 NA NA NA NA NA NA
Q42016 101949.l 16400 385877 6328388433.4 6328.4 14.0 3598.3 2800 13620 38134783.4 38.1 0.1
QI 2017 97071.7 18000 367416 6613494921.0 6613.5 14.6 103117.8 6460 390301 2521343639.6 2521.3 5.56
Q2 201 7 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 I 1.3 68180.2 552 258062 142450255.5 142.5 0.3
Table G-1
..._.. ... ..,.,.._._.,' _.._._,_._.,L& .. 1~1t ..._... _,,,,._..,..,_...,.....,, ••• .. , ..... 11n.•• ......... "611.._. O ...,, ... u..1 Y ~11,011,,.., ""' r• 1.11.,V • UIII """-'
1:W4-3? 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.l 16200 245836.l 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. I 593.4 1.3
Q4 2019 66732.4 13100 252582.1 3308825955.4 3308.8 7.3 51808.6 1650 196095.6 323557659.2 323.6 0.7
QI 2020 65554.2 12000 248122.6 2977471764.0 2977.5 6.6 43169.3 812 163395.8 132677390.0 132.7 0.3
Q2 2020 65163.8 11700 246645.0 2885746301.1 2885.7 6.4 37352.7 5870 141380.0 829900421.0 829.9 1.8
Totals 1779423.7 234.5 667464.0 25.5
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)
QI 2007 NA NA NA NA NA NA NA NA NA NA NA NA 286.9 9648896.0
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA 4.0 904550.0
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA 9.0 559220.0
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 550560.0
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA 13.8 503034.0
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA 14.8 527290.0
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA 26.8 724960.0
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA 22.7 786870.0
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
QI 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
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA 10.8 468706.3
QI 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 3 l.I 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
QI 2015 NA NA NA NA NA NA NA NA NA NA NA NA 9.9 458271.4
Q2 2015 NA NA NA NA NA NA NA NA NA NA NA NA 15.3 539592.9
Q3 2015 NA NA NA NA NA NA NA NA NA NA NA NA 33.4 816299.8
Q4 2015 NA NA NA NA NA NA NA NA NA NA NA NA 32.3 847567.8
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 754250.1
Q4 2017 NA NA NA NA NA NA NA NA NA NA NA NA 16.9 841953.7
Table G-1
"-""'"'"" •• _ _..,_a.a • .,. ... ...,,,.,,, .....,,,,...,,...,,...,,,,, ,,_.,_,,...,.v,, ,-.,,.,.. .l' .,.., ...... 1 • ~,.._,,, ...... ....,, ,,.,. .. _, • ._.,,, .,v.,..
TW4-40 TW4-41
Total Total Total Total rrotal 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)
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.l 803034.5
Q3 2018 NA NA NA NA NA NA 44981.6 1390 170255 236654734.4 236.7 0.5 17.6 733435.6
Q4 2018 NA NA NA NA NA NA 35431.6 1320 134108 177023110.1 177.0 0.4 20.8 800443.6
QI 2019 NA NA NA NA NA NA 31904 1220 120755.1 147321253.7 147.3 0.3 16.2 811589.4
Q2 2019 81762.7 263 309471.8 81391088.5 81.4 0.18 25146.5 1320 95179.5 125636943.3 125.6 0.3 26.2 750139.6
Q3 2019 116414.2 380 440627.7 167438543.9 167.4 0.37 24045.6 1190 91012.6 108304989.2 108.3 0.2 18.3 794827.4
Q4 2019 108281.89 314 409847.0 128691943.4 128.7 0.28 21186.4 1410 80)90.5 113068638.8 113.1 0.2 13.0 844887.9
QI 2020 102021.51 364 386151.4 140559115.2 140.6 0.31 17289.9 1200 65442.3 78530725.8 78.5 0.2 18.9 802209.2
Q2 2020 100757.13 367 381365.7 139961225.5 140.0 0.3 1 17294.9 1220 65461.1 79862567.4 79.9 0.2 25.2 910974.8
Totals 509237.4 1.45 290991.2 3.2 1230.3 46423537.9
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
o.-rter* Obs.) Obs.J (lbs.) (lbs.J {lbs.) (lbs.} (lbs.) (lbs.) (lbsJ (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) Totals (lbs.)
01 2007 36.8 12.9 150.2 87.0 NA NA NA NA NA NA NA NA NA NA NA NA 286.9
022007 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 l.O 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 32 9.9 NA NA NA NA NA NA NA NA NA NA NA NA 14.8
03 2008 1.2 0.3 15.9 9.3 NA NA NA NA NA NA NA NA NA NA NA NA 26.8
Q4 2008 1.3 0.3 20.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 22.7
OJ 2009 1.7 0.4 4.3 3.6 NA NA NA NA NA NA NA NA NA NA NA NA 10.0
02 2009 6.8 0.2 3.7 2.8 NA NA NA NA NA NA NA NA NA NA NA NA I 3.5
03 2009 1.5 0.4 II.I 5.5 NA NA NA NA NA NA NA NA NA NA NA NA 18.5
04 2009 4.8 0.6 17.8 26.1 NA NA NA NA NA NA NA NA NA NA NA NA 49.4
01 2010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 4.5
Q2 2010 1.5 1.0 6.8 5.9 1.4 NA NA NA NA NA NA NA NA NA NA NA 16.5
Q3 2010 1.3 l.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA NA NA NA 10.6
042010 I.I 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA NA NA NA 17.9
Of 2011 1.1 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
Q32011 1.2 0.4 I.I 4.1 1.2 NA NA NA NA NA NA NA NA NA NA NA 8.1
042011 1.2 0.8 2.7 4.8 1.4 NA NA NA NA NA NA NA NA NA NA NA 10.8
QI 2012 I.I 0.6 0.8 7.0 1.0 NA NA NA NA NA NA NA NA NA NA NA 10_6
Q2 2012 I.I 0.7 0.7 6.9 I.I NA NA NA NA NA NA NA NA NA NA NA 10.4
-03 2012 1.1 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 3.2 0.8 NA NA NA NA NA NA NA NA NA NA NA 7.2
QI 2013 0.9 0.4 7.4 2.8 0.7 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
032013 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
042013 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
012014 0.8 0_3 1.5 2.8 0.6 2.5 0.2 0.0 NA NA NA NA NA NA NA NA 8.6
Q2 2014 0.8 0.4 2.0 3.4 0.6 2.5 0.1 0.0 NA NA NA NA NA NA NA NA 9.9
, 3 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
, 4 2014 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
, l 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
)2 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
)3 2015 1.0 0.4 7.6 2.5 0.7 L6 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
Ql 2016 0.9 0.4 7.6 2.6 0.6 1.2 0.02 0.0 0.16 0.34 0.08 0.41 16.3 NA NA NA 30.6
Q2 2016 1.3 0.4 13.0 4.4 0.9 1.9 0.04 0.0 0.19 0.36 0.10 0.60 16.J NA NA NA 39.4
03 2016 1.0 0.5 5.2 2.4 0.6 LI 0.01 0.0 0.15 0.26 0.08 0.42 13.1 NA NA NA 24.7
Q42016 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
Ql 2017 0.9 0.3 I.I 2.6 0.3 1.1 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
03 2017 I.I 0.3 8.3 3.4 0.3 I.I 0.008 0.0 0.14 0.21 0.08 0.54 10.2 2.9 NA NA 28.5
04 2017 1.2 0.6 0.1 1.4 0.2 0.9 0.014 0.0 0.07 0.23 0.06 0.49 11.3 0.3 NA NA 16.9
QI 2018 1.2 0.3 2.4 1.8 0.2 0.9 0.020 o.o 0.01 0,10 0.07 0.41 9.1 1.4 NA NA 18.0
02 2018 I.I 0.4 2.8 1.3 0.2 0.6 0.022 0.0 0.09 0.13 0.06 0.52 JO.I 2.0 NA 0.9 20.1
03 2018 LO 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
Q42018 1.1 0.3 4.7 1.0 0.1 0.5 0.018 0.0 0.06 0.11 0.06 0.59 9.7 2.0 NA 0.4 20.8
OJ 2019 I.I 0.2 2.0 1.9 0.1 0.9 0.023 o.o O.Ol 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
03 2019 0.9 0.3 5.6 1.2 O.l 0.7 0.014 0.0 O.D7 0.09 o.o 0.5 6.7 1.3 0.37 0.2 18.3
Q42019 I.I 0.3 0.5 0.6 0.1 0.8 0.037 o.o 0.08 0.11 0.1 0.8 7.3 0.7 0.28 0.2 13.0
QI 2020 1.1 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
Q2 2020 I.I 0.3 8.7 4.9 0.1 0.5 0.024 0.0 0.04 0.13 0.0 0.7 6.4 1.8 0.3 1 0.2 25.2
Well Totals 105.4 37.1 439.6 296.2 25.6 42.0 1.089 0.0 2.59 4.81 1.64 9.80 234.5 25.5 1.45 3.2 1230.3
• QI 2007 represents the cumulative total prior to and including Ql 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 101850.7 4.0
MW-26 25418.4 11.0
TW4-19 136619.7 17.2
TW4-20 100713.8 3.2
TW4-4 15347.0 14.7
TWN-2 30078.9 16.7
TW4-22 25295.3 18.0
TW4-24 57634.7 16.3
TW4-25 90767.9 11.6
TW4-0l 9600.2 12.8
TW4-02 14155.6 16.1
TW4-11 2003.9 16.5
TW4-21 110999.1 16.7
TW4-37 65163.8 18.0
TW4-39 37352.7 18.0
TW4-40 100757.1 18.0
TW4-41 17294.9 5.4
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9 9 9
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t 01 2015
02 2015
03 2015
04 2015
01 2016
02 2016
03 2016
04 2016
01 2017
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01 2015
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
02 2020
0
0 0
Chlorofo~ Removed (~8unds)
0 _.
01 0
0 ~ !=' _.
01
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MW-26 Mass of Chloroform Removed by Quarter (lbs.)
14.0 .....----------------------------------------------,
12.0 ~------------------------------------------1
10.0 rr-----------------------------------_J
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0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
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TabH
Laboratory Analytical Reports
3440 South 700 West
Mt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-0IOC
Client Sample ID: MW-04_05272020
Collection Date: 5/27/2020 1037h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/3/2020 820h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20
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 20.0 1,250
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
---------------
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,020
987
983
1,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 1256h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 102 72-151
1,000 98.7 80-152
1,000 98.3 72-135
1,000 IOI 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 50.5 50.00 IOI 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.1 50.00 98.2 80-152
Surr: Dibromofluoromethane 1868-53-7 49.4 50.00 98.9 72-135
Surr: Toluene-d8 2037-26-5 49.8 50.00 99.7 80-124
Report Date: 6/12/2020 Page 32 of 48
All analyses applicable to lhe CW A. SDW A. and RCRA are performed in accordance to NE LAC protocols Per1inenl sampling information is located on Lhe attached COC. Confidential Business Information: This report is provided for the exclush e use of the
~ddressee Pri,·ile~es o!sub ... seq~enl ~1~e of Lhe ~:";'e of this .co~pany or any ~~ber of ils staIT, or reproduclio~ ~fthis repo~ in ~on~eclion .. with the a~,,ertisement, P~?motio.n or ~aJe of~~: ~rod~cl or P~?cess, ~r in ~onrn;_c~ion ,,·~lh th~ r~·publication of this report
American West ANALYTICAL LABORATORI ES
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: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2005695-010
Client Sample ID: MW-04_05272020
Collection Date: 5/27/2020 1037h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1906h
6/1/2020 1431h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 40.7
E353.2 0.100 5.04
Report Date: 6/12/2020 Page 15 of 48
All anal) ses applicable lo lhe CW A, SOWA. and RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on the altached COC. Confidential Business Information: This report is provided for the exclusi, e use of the
~ddressee, Pri,·ile~es orsub,_seq~1ent ~1;-e oflhe ~?1:°e or this .co1~pany or fill) ~mber olits slalT, or reproduclio~ ~f lhis repo~ in ~o~ec1ion .. "-ilb the a~, ertisement, P~?moti~n ~r saJe of ~!).frod~ct or P~?cess, ~r in ~nn~c!ion w~th th~ r:-publication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-008C
American West Client Sample ID: TW4-0l_05272020
ANALvr1cAL LA00RAT0R1Es Collection Date: 5/27/2020 1205h
Contact: Tanner Holliday
Received Date: 5/29/2020 1050h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 6/2/2020 1215h
Units: µg/L
Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
CAS Result Amount Spiked %REC
17060-07-0 509 500.0 102
460-00-4 489 500.0 97.8
1868-53-7 493 500.0 98.7
2037-26-5 506 500.0 101
--The reporting limits were raised due lo high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 317h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor: Method:
CAS Reporting
Number Limit
56-23-5 1.00
74-87-3 1.00
75-09-2 1.00
CAS Result Amount Spiked %REC
17060-07-0 52.2 50.00 104
460-00-4 49.6 50.00 99.3
1868-53-7 50.5 50.00 101
2037-26-5 50.5 50.00 101
SW8260D
Analytical
Result Qual
499
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: 6/12/2020 Page 30 of 48
All o.naJyses appl1coblc: I the CWA. SOW A. ruld RCRA are perfom-.ed in accordance to NELAC protocols. P~ninc:nt s(lrnplint,'informa:tion is localed on the attached COC. Confidentlal Business lnfonniltion: This repon is pro,·ided for the c.'Cc-hKh-~ use of lhe
~ddressee. Prl\·ile~ t>,r1u~~1ent .u~e of the~~ or lhis .co1~pillly or nny r~mber of its staff, or reproductH~! ~hhis rtp,o~ in ~on~cclio.~ with the a~,·ertise~enl, P~?motio.n ~r saJe of ~!Y ~rodl~cl or p~ocess, ~r in ~nn~c!ion w!th 1~ r~·p:ubllc.11th'm or 1his report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-008
Client Sample ID: TW4-01_05272020
Collection Date: 5/27/2020 1205h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1833h
6/1/2020 1446h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 46.4
E353.2 0.100 0.443
Report Date: 6/12/2020 Page 13 of 48
All analyses applicable to lhe CWA, SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the ollached COC Conlidentiol Business Information; This repor1 is provided for the exclusi,·e use of the
~ddressee Pri, ile~es o_f su~se<1~ent ~~e of the ~?';le or this .con;ipany or &1) 1~1;1be1 or its staff, or reproduclio.~ ?.f this repo~ in .co~ection~ \\llh the a~vertisement, p~omoti~ or saJe of ?J!~ rrod~ct or P~?Cess, ~r in ~onn~c~ion w!th th~ r~-publication 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-01 lC
Client Sample ID: TW4-02_05272020
Collection Date: 5/27/2020 1028h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/3/2020 921h Extracted:
Units: µg/L Dilution Factor:
Compound
Chloroform
Surrogate Units: µg/L CAS
Surr: I ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
20
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 20.0 1,070
Result Amount Spiked %REC Limits Qual
1,030 1,000 103 72-151
1,020 1,000 102 80-152
982 1,000 98.2 72-135
1,020 1,000 102 80-124
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 1316h Extracted:
Units: µg/L Dilution Factor: 1 Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 < 1.00
Chloromethane 74-87-3 1.00 < 1.00
Methylene chloride 75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 51.6 50.00 103 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.2 50.00 98.5 80-152
Surr: Dibromofluoromethane 1868-53-7 50.5 50.00 101 72-135
Surr: Toluene-d8 2037-26-5 50.7 50.00 101 80-124
Report Date: 6/12/2020 Page 33 of 48
All analyses applicable to lhe CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling information is located on the allached COC. Conlidenlial Business [nformation: This repon is provided for1he exclusi, e use of the
~ddressee. Pri,•ile~es or sub~seq~ent ~?e of the ~?1;1e of this .co1~pany or an) 1~~ber of its staff, or reproductio~ ~f this repo~ in ~m1;1eclion~ \\ilh the a~, ertisemenl, P~?moti~n or sale of ?1!Y prod~cl or p~ocess, ~r in ~nn~!ion '''!lh th~ r~-p~blicntion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (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: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2005695-011
Client Sample ID: TW4-02_05272020
Collection Date: 5/27/2020 1028h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1923h
6/1/2020 1432h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 40.6
E353.2 0.100 3.62 ----
Report Date: 6/12/2020 Page 16 of 48
All anal) ses applicil.ble to the CW A. SOW A. and RCRA are perfonned in accordance to NE LAC protocols Peninenl sampling i11forma1ion is located on the au ached COC Confidential Business rnrormu1ion: This repon is provided for the e.~clusi, e use of 1he
~ddressee,. Pri, ile~es of' sub .. seq~enl ~~e or the ~:u:ne of this _con:ipo.ny or M) ~mbe1 of its slaJT, or reproduclio~ ~f this repo~ in _con~1ection .. wilh the a~vertisement, P~?molio.n or ~ale of ?-'!Y, ~rodi~cl or p1.ocess, ~r in ~nn:c~ion w!lh th~ ri;-publication or this repon
American West
ANALYTICAL LABORATORlfS
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-002C
Client Sample ID: TW4-03_06102020
Collection Date: 6/10/2020 735h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 203 lh
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 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
54.0 50.00 108 72-151
51.7 50.00 103 80-152
46.9 50.00 93.8 72-135
52.3 50,00 105 80-124
Report Date: 6/29/2020 Page 27 of53
All analyses applicable lo the CW A. SOWA. and RCRA are performed in accordance lo NELAC prolocols Per1inenl sampling informalion is located on lhe auached COC Confidential Business Jnrormalion: This report is pro,•ided for the exclusi,·e use of the
~ddressee Pri\'ile~es o.r su~seq~ent ~:'e of the ~~e of I his .con;,pany or an) ~'!1be1' of'ils slaff, or reproduclio~ ~f this repo~ in .co~ection~ with the ~~ertisemenl, P~?moti~n ~r sale of~!). ~rodl~cl or p1.?cess, ~r in ~nnt;c!ion w!1h th~ r1;-publication of I his 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-002
Client Sample ID: TW4-03_06I02020
Collection Date: 6/10/2020 735h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1202h
6/15/2020 826h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 26.2
E353.2 0.100 6.53
Report Date: 6/29/2020 Page 8 of 53
All analyses applicable lo the CWA SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the altached COC Conlidential Business Jnformalion: This report is proyided for the exclusiYe use of1he
'!ddressee. Prh ile~es o.r sub~seq~enl ~·~e or the ~~e of I his .co1~pany or any ~mbe1 of its staff, or reproduclio~ ~f this repo~ in .con~eclion~ with the a~vertisement, P~?motio.n ~r ~aJe of :11f ~rod~cl or P~?cess, ~r in ~onn~c~ion w(lh th~ r1;:-p~blication of lhis report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-00lC
Client Sample ID: TW4-03R_06092020
Collection Date: 6/9/2020 1 OOOh
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 1930h
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 3.05
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 53.5 50.00 107 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.0 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 49.2 50.00 98.4 72-135
Surr: Toluene-d8 2037-26-5 52.0 50.00 104 80-124
Report Date: 6/29/2020 Page 26 of 53
All analyses applicable lo lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling information is located on the altached COC. Conridenlial Business Information: This report is pr°'•ided f'orthe exclusin use of the
~ddressee. Pririle~es o_f sub__seq~1enl ~~e of the ~?1,"e of I his .co~pany or nny ~I!1ber of its staff, or reproduclio~ ~f this repo~ in .co~ecl10n .. with the u~vertisement, P~?moti~n or sale of ~!Y ~rod~cl or p~ocess, ~r in ~nrn:c,lion ,,·!lh th~ r~-publicaJion of this repon
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-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-001
Client Sample ID: TW4-03R_06092020
Collection Date: 6/9/2020 1 OOOh
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1145h
6/15/2020 825h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 6/29/2020 Page 7 of 53
All anal) ses applicable to the CW A, SDW A. and RCRA are i:ierformed in accordance lo NELAC protocols. Pertinent sampling information is localed on lhe attached COC Confidenti:il Business Information: This report is provided for the exclusi, e use of the
~ddressee Pri,·ile~es o:sub ... seq~enl ~1~e of the ~?1,'le of lhis .con:ipany or any ~mber of its slaff, or reproductio~ ~f this repo~ in .con~1eclion ... WiU1 the n~vertisement, P~?motio.n or saJe of ~!Y ~rodl~cl or p~ocess, ~r in ~nn:c~ion w!Lh th~ r:-publication of lhis repon
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-006C
Client Sample ID: TW4-04_05272020
Collection Date: 5/27/2020 1222h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/2/2020 1134h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 20
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 20.0 1,140
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
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
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
1,010
983
984
1,020
--The reporting limits were raised due lo high analyte concentrations.
Analyzed: 6/2/2020 236h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 IOI 72-151
1,000 98.3 80-152
1,000 98.4 72-135
1,000 102 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Surr: l,2-Dichloroethane-d4 17060-07-0 50.6 50.00 IOI 72-151
Surr: 4-Bromofluorobenzene 460-00-4 49.2 50.00 98.4 80-152
Surr: Dibromofluoromethane 1868-53-7 49.2 50.00 98.5 72-135
Surr: Toluene-d8 2037-26-5 49.9 50.00 99.8 80-124
Report Date: 6/12/2020 Page 28 of 48
All analyses applicable to lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols. Per1inenl sampling i11formalion is localed on the attached COC Conf1den1ial Business Jnforrnation: This repor1 is prO\•ided for 1he e.xclusi,-e use oflhe
~ddressee Pri, ile~es o_f sub~seq~1enl ~1~e or lhe ~?1:11e or lhis .co~pany or M) ~mbe1 or ils slaIT, or reproductio~ ~[this repo~ in ~o°!"'ection~ \\ilh the 11~~'ertise1~enl, P~?molio.n ~r sn.le or ?1!): ~rod~cl or P~?Cess, ~r in ~onn:c!ion w!lh th~ r~·publicaJion of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-006
Client Sample ID: TW4-04_05272020
Collection Date: 5/27/2020 1222h
Received Date: 5/29/2020 I 050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1742h
6/1/2020 1426h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 46.1
E353.2 0.100 7.26
Report Date: 6/12/2020 Page 11 of 48
All analyses applicable to lhe CWA, SOWA_ and RCRA are perfonned in accordance to NELAC prolocols Pertinenl sampling information is locuted on Lhe attached COC. Confidenlial Business rnformation: This report is prm•ided for the exclusi,·e use of the
~ddressee. Pri,·ile~es o.f sub,_5eq~enl ~~e of lhe ~~e of I his .co~pany or nn) ~~ber of ils slaff, or reproduclio~ ~~this repo~ in ~o~ecllon,. \\ilh lhe a~~ertise~enl, P~?molio.n ~r ~a1e of~!). ~rod~ct or P~?cess, ~r in ~onm_:c~ion \\'!th lh~ n~-publicalion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-018C
Client Sample ID: TW4-05_06112020
t.NALvr1cAL LAaouroR1es Collection Date: 6/11/2020 740h
3440 South 700 West
,alt Lake City, UT 84119
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1422h
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 15.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
54.9 50.00 110 72-151
52.9 50.00 106 80-152
48.0 50.00 96.0 72-135
52.2 50.00 104 80-124
Report Date: 6/29/2020 Page 43 of 53
All analyses applicable to lhe CWA. SOWA. and RCRA are performed in accordance lo NELAC prolocols Pertineni sampling information is located on the au ached COC Confidenli:il Business Informnlion: This repon is pro"ided for lhe e..,-clush"e use of lhe
~ddressee Prh ile~es o,r sub..5eq~ent ~~e of the ~:11:°e of this .co":1pany or nny '!!:mbe, of its slaff, or reproduclio~ ~f lhis repo~ in ~o~ection~ wilh the a<!~ertisement P~?molio.n or sale of~]} ~rod~ct or p•:?Ces1,, ~r in ~nn:c~ion w!th th~ r~-publico1ion or this report
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
2nd Quarter Chloroform 2020
2006384-018
Client Sample ID: TW4-05 06112020
ANALYTICAL LA00RAT0R1Es Collection Date: 6/l l/2020 740h
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: 6/12/2020 1010h
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
6/22/2020 1844h E300.0 l.00 49.5
6/15/2020 859h E353.2 0.100 7.83
Report Date: 6/29/2020 Page 24 of 53
All analyses applicable lo the CWA. SOWA. and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling informa1ion is localed on lhe auached COC Conliden1iol Business lnformolion: This report is pro,·ided for 1he exclusiYe use of the
~ddressee Pri, ile~es o_f su~seq~nt ~e of lhe ~?':"e of this .con_1JX1ny or M) ~mber of ils slafT, or reproductio~ ~f this repo~ in .co~ection .. with the ~~ertise~enL. P~?molio.n °!' sale of :i'!Y ~rod~cl or p~~s, ~r in ~nn';C~ion with lh~ r;-publicalion of this report
American West
ANALYTICAL LABORATOR I ES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-016C
Client Sample ID: TW4-06_06112020
Collection Date: 6/11/2020 718h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1341h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 4.86
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 54.1 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.8 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 46.4 50.00 92.8 72-135
Surr: Toluene-d8 2037-26-5 51.8 50.00 104 80-124
Report Date: 6/29/2020 Page 41 of 53
All analyses applicable to lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols. Per1inenl sampling information is located on the aUached COC. Confidential Business 1nforma1ion: This report is prm•ided for the exclusi,·e use of the
!ddressee Pri, ile~es o.f sub~seq~enl ~~e of the ~?',11e or1his .con_1pany or an) ~mber of its staff, or reproduclio~ ~~ this repo~ in ~o~eclion .. with the ~vertise~enl, P~?motio.n ~r saJe of:"!) ~rod~ct or p1:?cess, ~r in ~nn1;.c~ion w!lh th~ r:-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-016
Client Sample ID: TW4-06_06112020
Collection Date: 6/11/2020 718h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 18 !0h
6/15/2020 856h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 42.4
E353 .2 0.100 0.205
Report Date: 6/29/2020 Page 22 of 53
All analyses applicable to lhe CWA, SOWA_ and RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is localed on the attached COC Conlidenti::il Business lnformnlion: This report is pro,•ided for the exclusi,·e use of lhe
!ddressee. Pri,·ile~es or sub~seq~enl ~;e of the ~?',11e or this .con:ipany or an) ~mber of its slaff, or reproduclio~ ~f this repo~ in ~o~eclion~ with the n~vertisement, P~?motio.n ~r sale of :U!). ~rod~cl or p1:ocess, ~r in ~nn~c~ion w~th th~ r:-publication of lhis report
American West
ANALYTICAL LABORATORIES
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2006426-009C
Client Sample ID: TW4-07_06122020
Collection Date: 6/12/2020 800h
Contact: Tanner Holliday
Received Date: 6/16/2020 I OOOh
Analytical Results
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 6/17/2020 1337h
Units: µg/L
Compound
Chlorofonn
Phone: (80 I) 263-8686 Surrogate Units: µg/L
foll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
--------
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor: IO Method:
CAS Reporting
Number Limit
67-66-3 10.0
CAS Result Amount Spiked %REC
17060-07-0 558 500.0 112
460-00-4 526 500.0 105
1868-53-7 510 500.0 102
2037-26-5 524 500.0 105
--The rep orting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/17/2020 1056h
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: Dibromotluoromethane
Surr: Toluene-dB
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 55.4 50.00 Ill
460-00-4 51.9 50.00 104
1868-53-7 50.6 50.00 IOI
2037-26-5 52.8 50.00 106
SW8260D
Analytical
Result Qual
864
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: 6/29/2020 Page 27 of 41
All anal)ses applicable 10 lhe CWA. SOWA. and RCRA are performed in accordance to NELAC prolocols, Per1inent sampling information is localed on 1he attached COC. Conlirlentlol Business Jnformntion: This report is pro\'ided for 1he exclusi, e use of lhe
~ddressee Pri, ile~es o_r sub ... seq~enl ~~e of lhe ~~e of this .con;1pnny or M) ~mber of its staff, or reproductio~ ~f this repo~ in ~0~1ection .. wilh the a~,•ertise~ent, P~?motio.n '!r sale of~!) ~rod~cl or p1:ocess, ~r in 7onn:_c~ion w/th th~ r:-publicetion of I his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-009
Client Sample ID: TW4-07 _06122020
Collection Date: 6/12/2020 800h
Received Date: 6/16/2020 1 OOOh
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
612 4/2020 300h
6/16/2020 I 245h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 44.1
E353.2 0.100 4.06
Report Date: 6/29/2020 Page 14 of 41
All anal) ses applicable to lhe CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is locoted on the all ached COC Confidential Business Jnform.ition: This report is pro\lided for lhe exclush·e use of 1he
~ddressee Pri, ilef!es o~ su~seq~enl ~!e of the ~~le of lhis ,co1~p1llly or any ~mbet of ils Slaff, or reproductio~ ~r this repo~ in ~eel ion~ \\ilh the a~~'er1ise~enl, P~?motio.n o_r ~ale of~!). ~rod~cl or p~ocess, ~r in ~nn~!ion ,,·1th th~ r~-p~blication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-004C
Client Sample ID: TW4-08_06122020
Collection Date: 6/12/2020 658h
Received Date: 6/16/2020 I OOOh
Analytical Results
Analyzed: 6/17/2020 834h
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 53.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
55.6
53.7
51.5
53.0
50.00 Ill 72-151
50.00 107 80-152
50.00 103 72-135
50.00 106 80-124
Report Date: 6/29/2020 Page 22 of 41
All anal, ses applicable to lhe CWA. SOWA, and RCRA are perfom1ed in accordance lo NE LAC protocols Pertinent sampling information is Jocoted on the nlleched COC Confidentinl Business (nformalion: This repon is pro"ided for the exclush-e use of !he
~dressee Pri, ile~es o.r sub~seq~enl ~~e of lhe ~~le of this .co1~pony or any ~mber of its stalT, or reproductio!~ ~~ this repo~ in ~o~eclion .. "ilh the n~,•ertisemenl, P~?motio
1
n ~r :ale of~!). ~rod~ct or p~ocess, ~r in ~nm;.c~ion w/lh lh~ r~-p~blication of !his report
American West
ANALYTICAL LABOAATORieS
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-004
Client Sample ID: TW4-08_06122020
Collection Date: 6/12/2020 658h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 030h
6/16/2020 1240h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 56.9
E353.2 0.100 1.06
Report Date: 6/29/2020 Page 9 of 41
All analyses applicable lo lhe CWA. SOWA. and RCRA are perfonned in accordance lo NELAC prolocols Pertinent sampling information is locllted on lhe auached COC Conridential Business Jnformation: This repon is prO\·ided for 1he exclusi\·e use of the
~ddressee Pri\·ile~es o.r subpseq~I ~~e of the ~~1e of !his .con;ipany or any ,~mber of ils slaff, or reproduccio~ ~f lhis repo~ in ~eel ion~ ,,~th the ~~er1ise1~enl. P~?moli~ ~r sale of ~!Y ~rod~ct or p~ocess, ~r in ?>nn~~ion w/lh lh~ r:-publicalion of I.his repon
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-002C
Client Sample ID: TW4-09 _06122020
Collection Date: 6/12/2020 625h
Received Date: 6/16/2020 1000h
Analytical Results
Analyzed: 6/16/2020 1525h
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 55.1
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
50.4 50.00 101 80-152
48.4 50.00 96.9 72-135
51.2 50.00 102 80-124
Report Date: 6/29/2020 Page 20 of 41
All anal~ ses applicable to lhe CW A. SDW A. and RCRA are performed in accordance to NE LAC prolocols Peninent sampling information is located on lhe auached COC Confidential Business Jnformalion: This repon is prO\•ided for the exclusi, e use of the
~ddressee Pri, ile~es or sub .. seq~enl !1~e of lhe ~~e of this .con_1pany or any ~mber of ils staIT, or reproductio~ ~f this repo~ in ~o~ec1ion .. \\ith the n~,,ertisement.. P~?molio.n ~r sale of ?'!Y ~1 odl~CI or P~?cess, ~r in ~onnc;.c~ion w!th 1h~ r1;:-publicatio11 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-002
Client Sample ID: TW4-09 _06l22020
Collection Date: 6/12/2020 625h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride rng/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/23/2020 2323h
6/16/2020 1237h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 39.5
E353.2 0.100 0.990
Report Date: 6/29/2020 Page 7 of 41
All ,lllalyses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols, Pertinent sampling information is localed on lhe atlached COC Conl'idential Business Information: This report is provided for the exclusi, e useof1he
~ddressee Pri, ile~es arsub~seq~ent ~~e of the ~:1':'1e of this .con.1pany or any ~mbe1 ofils staff, or reproductio~ ~! lhis repo~ in ~Ol~ection~ wilh the a~~·ertisemenl, P~?nlolio.n ~r sale of~!) ~rod~cl or p~ocess, ~r in ~nn~c~io11 w!th th~ r~-publicnlion of this repon
American West
ANALYTICAL LAB0AATOA1E6
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-019C
Client Sample ID: TW4-09R_06112020
Collection Date: 6/11/2020 845h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 1950h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 1.98
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 53.8 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 53.3 50.00 107 80-152
Surr: Dibromofluoromethane 1868-53-7 48.2 50.00 96.5 72-135
Surr: Toluene-d8 2037-26-5 52.1 50.00 104 80-124
Report Date: 6/29/2020 Page 44 of 53
All analyses applicable to lhe CWA, SDWA. and RCRA are perfom1ed in accordance lo NELAC protocols, Peninenl sampling infonnation is loct11ed on the attached COC ronfidentlol Business Jnformwlion: This repon is provided ror the esclusi\·e use of the
~ddressee. Privile~es o.f sub ... seq~enl ~~e of !he ~~e of this .co~pany or any ~mber of ils stalT, or reproduclio~ ~~this repo~ in ~o~eclion~ with the a~~er1isemenl, P~?moti<>;n ~r sale of ?'!Y ~rod.~cl or p~~s, ~r in ~nn~~ion \\'!lh th~ r:publicalion 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-019
Client Sample ID: TW4-09R_061 l2020
Collection Date: 6/11/2020 845h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 I 900h
6/15/2020 900h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 6/29/2020 Page 25 of 53
All anal~ ses applicable lo lhe CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinenl sampling informal ion is localed on the au ached COC Confidentlnl Business lnform;:ilion: This repon is prol'ided for 1he exclusi, e use or the
~ddressee Pri,·ile~es or sub__seq~nl ~;e of the ~?1."e of this .co~pany or anr ~'!1be1 of ils slaff, or reproduclio~ ~~this repo~ in ~oc1?eclion .. \\·ith the tu!ver1isement, P~?moli~n ~r ~ale of?'!~: ~rod~cl or p~ocess, ~r in ~nn~!ion '''!lh lh~ r~-publicaJion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-0IOC
Client Sample ID: TW4-10_06122020
ANALYTICAL LAeoRAToR1Es Collection Date: 6/12/2020 812h
Contact: Tanner Holliday
Received Date: 6/16/2020 1000h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 6/17/2020 1357h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
---------------
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
544
522
499
508
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/17/2020 1116h
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
109
104
99.8
102
Method:
Reporting
Limit
1.00
1.00
1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: 1,2-Dichloroethane-d4 17060-07-0 54.8 50.00 110
Surr: 4-Bromotluorobenzene 460-00-4 51.8 50.00 104
Surr: Dibromotluoromethane 1868-53-7 50.2 50.00 101
Surr: Toluene-dB 2037-26-5 50.7 50.00 101
SW8260D
Analytical
Result Qual
928
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: 6/29/2020 Page 28 of 41
All annlyses applicable 10 the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinenl sampling inrormution is located on the attached COC Conlidentlnl Business lnfonnation: This repori is provided for the exclusi\'e use oCthe
~ddressee Pri\ ile~es o.rsub .. seq~enl ~1~e of the ~?1;1e or lhis.con:1pnny or nny ~mbe1 of its staJT, or reproduclio~ ~fthis repo~ in ~o~ection .. ,\~th the n~~·ertise~ent. P~?moli~ ~r sale of !ll!~. prod~ct or p1:ocess, ~r in ~nn~c!ion ,,·11h th~ r~-p~blico.tion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-010
Client Sample ID: TW4-I0_06122020
Collection Date: 6/12/2020 812h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 3 I 7h
6/16/2020 1252h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 60.1
E353.2 0.100 8.13
Report Date: 6/29/2020 Page 15 of 41
All annb ses applicable to the CWA. SDWA_ and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the altached COC Confidenlinl Business [nformation: This report is pro"ided for the exclusi,·e use of the
~ddressee Pri, ile~es o.f sub .. seq~ent ~~e of the ~~e of this .co~pany or nny ·~l;lber of its slalT, or reproductio~ ~f this repo~ in .con~eclion ... ,,~th the n~~1ertise1~ent, P~?moli~ or sale of~;). ~rod~cl or p~ocess, ~r in ~nn~~ion w~th th~ r1;-publication or lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-012C
American West Client Sample ID: TW4-I I_05272020
ANAL vr,c AL L Aeo R Aro R, Es Collection Date: 5/27/2020 1020h
Received Date: 5/29/2020 I 050h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 6/3/2020 941h
Units: µg/L Dilution Factor: 50 Method: SW8260D
3440 South 700 West
;alt Lake City, UT 84119 Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate -----------Units: µg/L
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 50.0 2,810
Result Amount Spiked %REC Limits Qual
2,590 2,500 104 72-151
2,580 2,500 103 80-152
2,460 2,500 98.4 72-135
2,570 2,500 103 80-124
--The reporting limits were raised due lo high analyte concenlrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 1337h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer 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
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 1.37
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
51.3 50.00 103 72-151
48.2 50.00 96.3 80-152
48.9 50.00 97,8 72-135
49.7 50.00 99.5 80-124
Report Date: 6/12/2020 Page 34 of 48
All analyses applicable to lhe CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Per1inent sflmpling information is locn1ed on the allached CDC Confirlenlinl Business Information: This 1epor1 is provided for the exclusi\ e use of the
~ddressee Pri, ile~es or su~seq~1enl ~~e of the ~~le of !his .co~pany or an~· ·~~ber of its Slaff, or reproductio~ ~f this repo~ in ~"!1eclionA with lhe (t~\'enisef!ienl, p~~>nlOti~n ~r ~ale of ~!Y ~rod~cl Of p~ocess, ~r in ~""~!ion \V!lh th~ r~-publicalion of lhis repon
3440 South 700 West
;alt Lake City, UT 841 1 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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-012
Client Sample ID: TW4-l 1_05272020
Collection Date: 5/27/2020 1020h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1940h
6/1/2020 1433h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 48.6
E353.2 0.100 7.56
Report Date: 6/12/2020 Page 17 of 48
All anal) ses applicable lo lhe CWA. SOWA, and RCRA are perfom1ed in accordance to NELAC prolocols. Pertinenl sampling information is located on lhe aUached COC, Confidential Business lnform.:llion: This repor1 is prm·ided for lhe exclusi, e use of lhe
~ddressee Pri, ile~es o~ sub,_seq~ent ~;e of the ~~e of this
0
Co",1pnny or an~· ~mber of its staff, or reproductio~ ~f this repo~ in ~on~ection~ wilh the ~~ertise~enl, P~?lllolio.n m sale 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 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-006C
Client Sample ID: TW4-12_06102020
Collection Date: 6/10/2020 82 lh
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2153h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 54.0 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 53.6 50.00 107 80-152
Surr: Dibromofluoromethane 1868-53-7 47.0 50.00 94.0 72-135
S urr: Toi uene-d8 2037-26-5 52.2 50.00 104 80-124
Report Date: 6/29/2020 Page 31 of 53
All analyses applicable to the CWA, SOWA. and RCRA are performed in accordance 10 NELAC protocols. Pertinenl sampling information is located on the allached COC Conlidential Business Information: This report is provided for 1he exclusi\e use of the
~ddressee Pri, ile~es o_f sub~seq~ent ~~e or lhe ~~e or this .co";pany or ru1y ~':"ber or its slaff, or reproduclio~ ~~ I his repo~ in .co~eclion,. with the ~vertisemenl, p~omolio.n or saJe of :"!Y ~rod~ct or p~ocess, ~r in ~onn!c~ion w~lh th~ r~-publication of this repon
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-006
Client Sample ID: TW4-12_06102020
Collection Date: 6/10/2020 82 lh
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1342h
6/15/2020 839h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 51.7
E353.2 0.100 4.95
Report Date: 6/29/2020 Page 12 of 53
All analyses applicable to the CWA. SOWA. and RCRA are perfonned in accordance to NELAC prolocols Pertinent sampling infom,ation is located on the nllached COC. Confidenlial Business Jnformalion: This report is provided for the esclusiYe use of the
~ddressee Pri, ile~es or su~seq~enl ~~e of the ~~e of lhis _co~pany or any ~mber of ils staff, or reproductio~ ~f this repo~ in ~o~ection ... wilh the ~,,ertise~enl, p~~molio.n or sale of~!)~ ~roch~ct or p•:?Cess, ~r in ~nn:c~ion w~th th~ r:·publication or !his repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-008C
Client Sample ID: TW4-13_06112020
Collection Date: 6/11/2020 602h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2234h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 54.5 50.00 109 72-151
Surr: 4-Bromotluorobenzene 460-00-4 53.6 50.00 107 80-152
Surr: Dibromotluoromethane 1868-53-7 47.3 50.00 94.5 72-135
Surr: Toluene-d8 2037-26-5 52.8 50.00 106 80-124
Report Date: 6/29/2020 Page 33 of 53
All analyses applicable to lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on lhe attached COC. Confidenrinf Business Information: This report is proyided for the exclusi, e use of the
!ddressee. Pri, ile~es o_f sub,_seq~enl ~~e of lhe ~~e of 1his .con_1pany or any ~'I'ber of ils staff, or reproduclio~ ~r lhis repo~ in .co~ecLion~ \\ilh the o~vertise1~enl, P~?moli~ or sale of~!) ~rod1~cl or P~?cess, ~r in ~onn:c~ion w!lh lh~ r:-publicalion 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-008
Client Sample ID: TW4-13_06112020
Collection Date: 6/11/2020 602h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1449h
6/15/2020 841h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 62.7
E353.2 0.100 5.96
Report Date: 6/29/2020 Page 14 of53
All analyses applicable lo lhe CWA SOWA, and RCRA are performed in accordance lo NELAC prolocols, Pertinent sampling informalion is located on lhe a1tached COC Confidential Business Lnformalion: This report is provided for lhe exclush e use of the
~ddressee Pri, ile~es o.f sub ... seq~enl ~~e of the ~?1:11e of I his .co~pany or any 1~mbe1 of ils sln.ff, or reproduclio~ ~f Lhis repo~ in ~o~ection,.. ,\~Lh the a~ver1isement, P~?motio_n ~r ~ale of~!). ~rod~cl or p~ocess, ~r in ~nn~c!ion w!lh 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-015C
Client Sample ID: TW4-14_06112020
Collection Date: 6/11/2020 708h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1320h
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 2.87
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55.3 50.00 Ill 72-151
53.6 50.00 107 80-152
47.7 50.00 95.5 72-135
52.4 50.00 105 80-124
Report Date: 6/29/2020 Page 40 of 53
All analyses applicable lo the CWA. SOW A, and RCRA are perfonned in accordance to NE LAC protocols Pertinent sampling information is localed on Lhe allached COC Confidential Business Jnformalion: This report is pro,•ided for lhe exclusi, e use of the
~ddressee. Pri, ile~es of sub .. seq~1enl ~~e of the ~?',11e of this .co~pany or any ~mbe1 ofils slaIT, or reproductio~ ~fthis repo~ in .con~eclion ... ,\~lh lhe u~renisemenl, p~~motio.n ~r sale of ~lY ~roch~cl or p~ocess, ~r in ';°nn:,c~ion w~lh lh~ n;_-publicaJ.ion of lhis report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-015
Client Sample ID: TW4-14_06112020
ANALYTICAL LAeoRAToR1Es Collection Date: 6/11/2020 708h
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: 6/12/2020 1010h
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
6/22/2020 1753h E300.0 1.00 47.6
6/15/2020 849h E353.2 0.100 6.57
Report Date: 6/29/2020 Page 21 of 53
All analyses applicable to the CWA. SOWA. and RCRA are performed in accordance lo NELAC prolocols~ Pertinent sampling infonnalion is located on the attached COC Confidenllol Business lnformotion; This report is pro,•ided for 1he exclusi,e use of the
!ddressee Pri,·ile~es or su~eq~nl ~~e of lhe ~?1.'1e of this .con:ipany or an) ~mbel' of ils s111rr, or reproductio~ ~f this repo~ in ~o~ection~ with the a<!~·er1ise1'?enl, P~?molio.n ~r ~e of?'!)~ ~rod~I or p1.ocess, ~r in ?>""~c!ion w!th 1h~ r~-p~blicntion of lhis repoI1
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-007C
Client Sample ID: MW-26_05272020
Collection Date: 5/27/2020 1010h
Contact: Tanner Holliday
Received Date: 5/29/2020 1050h
Analytical Results
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
~alt Lake City, UT 84119
Analyzed: 6/2/2020 1154h
Units: µg/L
Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate ------------Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 50 Method:
CAS Reporting
Number Limit
67-66-3 50.0
CAS Result Amount Spiked %REC
17060-07-0 2,520 2,500 IOI
460-00-4 2,440 2,500 97.7
1868-53-7 2,460 2,500 98.2
2037-26-5 2,520 2,500 101
--The reporting limits were raised due Lo high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 257h
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:
CAS Reporting
Number Limit
56-23-5 1.00
74-87-3 1.00
75-09-2 1.00
CAS Result Amount Spiked %REC
17060-07-0 50.8 50.00 102
460-00-4 49.0 50.00 98.0
1868-53-7 50.2 50.00 JOI
2037-26-5 49.4 50.00 98.7
SW8260D
Analytical
Result Qual
1,610
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
3.92
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 6/12/2020 Page 29 of 48
All annlyses applicnble to lhe CWA. SDW A. and RCRA are perfomled in accordance to NELAC protocols Pertinent sampling information is located on lhe attached COC ('onridenlial Business Jnformation: This repon is provided for1he exclusi,·e use of the
~ddressee Pri, ile~es of su~seq~nt ~~ of the ~!1'?1e of lhis .cor:ipan~· or any ~mbe1 of ils staff, or reproduclio~ ~~ lhis repo~ in ~on~eclion~ wilh lhe a<!~ertisement, P~?moti~n ~r sale of :11!), ~rod~cl or p~ocess, ~r in ~nn~!ion \\'!lh th~ r~-publication of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2005695-007
Client Sample ID: MW-26_05272020
Collection Date: 5/27/2020 10 I Oh
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1652h
6/l /2020 1427h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 77.6
E353.2 0.100 2.93
Report Date: 6/12/2020 Page 12 of 48
All analyses applicable lo the CW A. SOW A. and RCRA are performed in accordance to NELAC prolocols Pertinenl sampling information is located on lhe auached COC Conridenrial Business Information: This report is prOl•ided for lhe e.'-clusi, e use of the
~ddressee Pri \ ile~es o,r sub .. seq~ent ~;e of lhe ~?1,11e or lhis .cor~pany or anr ~mber of its staIT, or reproducli~ ~r this repo~ in ~o~ection~ \\ith the a~~ertise1!1enl, P~?moli~ ~r sale of~!) ~rod~t or P~?cess, ~r in ~onn:_c~ion w~lh th~ r~-publication 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-007C
Client Sample ID: TW4-16_06122020
Collection Date: 6/12/2020 735h
Received Date: 6/16/2020 1000h
Analytical Results
Analyzed: 6/17/2020 935h
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 1.00 141
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
55 .9
53.5
51.7
52.1
50.00 112 72-151
50.00 107 80-152
50.00 103 72-135
50.00 104 80-124
Report Date: 6/29/2020 Page 25 of 41
All am:ibses applicable to lhe CWA. SDWA. and RCRA ore perform~d in accordance 10 NELAC prolocols. Per1inen1 sampling inforinalion is locoted on lhe attached COC Confiden1ial Business Information: This repon is provided for the e:'l'.clusi,·e use of the
~ddressee Prh ile~es or sub .. seq~enl ~e of lhe ~!1':"e of I his ,con_,pany or any ~'!1ber of ils Slaff, or reproducli<>!~ ~f this repo~ in ~o~eclion~ w:ilh the a~:er1ise~n1, p~~mo1ia;n o.r saJe of~!) ~rod~cl or p,.ocess, ~r in ~nn~c!ion \\'!lh lh~ r~-p~blicruion of !his report
INORGANIC ANALYTICAL REPORT
3440 South 700 West
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-007
Client Sample ID: TW4-I6_06122020
Collection Date: 6/12/2020 735h
Received Date: 6/16/2020 I OOOh
Analytical Results
Compound Units
Date
Prepared
;a]t 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
6/24/2020 I 03h
6/16/2020 1243h
Contact: Tanner Holliday
Method
Used
E300.0
E353.2
Reporting
Limit
1.00
0.100
Analytical
Result
79.7
4.44
Qual
Report Date: 6/29/2020 Page 12 of 41
All anal) ses applicable to the CWA. SOW A. and RCRA are performed in accordance to NE LAC protocols Pertinenl sampling informalion is located on lhe au ached COC Confidential Business (nform.ition: This report is provided for !he exclush e use of the
~ddressee Pri, ile~es o,r su~seq~enl ~1~e of lhe ~~e or lhis .cor~pany or any ~mber of its slnff, or reproducli~ ?.'. this repo~ in ~o~eclion~ \\~Lh the n<!"er1ise~ent. P~?motio.n o.r sale of~~) ~rod~cl or P~?cess, ~r in ~onn~c~ion w!th th~ r~-publication of lhis report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-00lC
Client Sample ID: MW-32_06122020
Collection Date: 6/12/2020 1140h
Received Date: 6/16/2020 1 OOOh
Analytical Results
Analyzed: 6/16/2020 1504h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 54.9 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.6 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 48.3 50.00 96.6 72-135
Surr: Toluene-d8 2037-26-5 51.7 50.00 103 80-124
Report Date: 6/29/2020 Page 19 of 41
All analrses applicable to the CWA. SDWA. and RCRA are performed in accordance 10 NELAC prolocols Pertinenl sampling information is located on the auached COC Confidential Business Informalion: This report is provided for the exclusi, e use of the
~ddressee. Pri\'ile~es or sub,_seq~enl ~~e of lhe ~?1!1e of lhis .con:1pany or any ~';1ber of its staff, or reproductio~ ~~this repo~ in ~o~eclion ... with the ac_!;1ertise~enL P~?motio,n ~r ~ale of ?1!Y~ rrod~cl or P~?cess, ~r in ~onn~c.lion w!lh th~ r:-p~blication of I his repor1
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: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2006426-001
Client Sample ID: MW-32_06122020
Collection Date: 6/12/2020 1140h
Received Date: 6/16/2020 I OOOh
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/23/2020 2306h
6/16/2020 1234h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 35.6
E353.2 0.100 < 0.100
Report Date: 6/29/2020 Page 6 of 41
All amdyses applicable to the CW~ SOWA. and RCRA are perfonned in accordance lo NELAC prolocols, Pertinent sampling information is localed Oil lhe attached COC. Confldential Business Informalion: This report is pro\'ided for the exclusi, e use of the
~ddressee, Pri, ile~es Of' sub~seq~enl ~~e of the ~~e of this 0Con:1pany or M)" 1~mber of ils slarf, or reproduclior! ~f this repo~ in ;on?ection .. \\~th the ~~1ertisemenl, P~?motio.n ~r sale of ~y ~rod~cl or p~ocess, ~r in ~nn:c~ion w!th th~ re;-publicalion of lhis report
American West
ANALYTICAL LAOORATORIEB
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-005C
Client Sample ID: TW4-18_06122020
Collection Date: 6/12/2020 710h
Received Date: 6/16/2020 1000h
Analytical Results
Analyzed: 6/17/2020 85 5h Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L CAS
Surr: l ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
Contact: Tanner Holliday
Test Code: 8260D-W-DENI00
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 58.2
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
54.7 50.00 109 72-151
51.4 50.00 103 80-152
50.2 50.00 JOO 72.135
51.7 50.00 103 80-124
Report Date: 6/29/2020 Page 23 of 4 l
All anol~ ses applicable to 1he CWA. SOWA, and RCRA are perfom1ed in R.Ccordance 10 NE LAC prolocols. Peninent s11mpling information is locnted on the nUached COC. Confidenlinl Business lnformalion: This report is provided for 1he exclush e use of the
~ddressee Pri, ile~es o_f su~eq~enl ?:e of lhe ~~e of !his .con:,pony or rmy ~mber of ilS staff, or reproducli<>!! ~f lhis repo~ in ~o"?eclion .. with the ~~ertise1~enl, P~?molio.n ~r sale of~ ~rod~cl or p,.ocess, ~r in ~M~!ion \\'!lh 1h~ r~-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: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2006426-005
Client Sample ID: TW4-18_06122020
Collection Date: 6/12/2020 710h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 153h
6/16/2020 1241h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 41.4
E353.2 0.100 3.62
Report Date: 6/29/2020 Page IO of 41
All analyses applicable to the CWA. SOWA. and RCRA are performed in accordance lo NELAC protocols. Pertinent sampling information is located on the altached COC. Confidential Business Jnformatlon: This report is provided for the exclusi\ e use of lhe
~ddressee Pri, ile~es o_r sub .. seq~enl ~1~e of the ~?1:'1e of this .co~pany or an~ ~mber or its staff, or reproductio~ ~f this repo~ in .c~ection ... with the rn!venisemenl, p~~motio.n ~r sale of :U!Y ~rod~cl or p~ocess, ~r in ~onn~~ion w!th th~ r~~publication of this report
ORGANIC ANALYTICAL REPORT
3440 South 700 West
;alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-014C
Client Sample ID: TW4-l 9 _ 05272020
Collection Date: 5/27/2020 845h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/3/2020 1022h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
CAS 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
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 7,600
Result Amount Spiked %REC Limits Qual
5,100 5,000 102 72-151
4,950 5,000 99.0 80-152
4,910 5,000 98.3 72-135
5,160 5,000 103 80-124
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 1417h
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
17060-07-0
460-00-4
1868-53-7
2037-26-5
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 10.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qua!
51.4 50.00 103 72-151
49.1 50.00 98.3 80-152
49.4 50.00 98.7 72-135
50.0 50.00 100 80-124
Report Date: 6/12/2020 Page 36 of 48
All an::il) ses applicable to 1he CW A. SOW A. and RCRA nre perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnformotion: This repon is pro\'ided ror 1he exclusire use of the
!ddressee Pril'ile~es o.f su~seq~ent ~~e of the ~~1e of rhis .co~pany or nny ~'!'ber of its slnff, or reproductio~ ~f this repo~ in ~on)1eclion ... n-ilh 1he n<!~·er1isemenl. P~?moli~n ~r sale of ?1!) ~n>d~cl or p~ocess, ~r in ?>nn~~ion w!lh lh~ r~-publicaJion of I.his 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-014
Client Sample ID: TW4-I 9 _ 05272020
Collection Date: 5/27/2020 845h
Received Date: 5/29/2020 I 050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 2013h
6/1 /2020 I435h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 147
E353.2 0.100 1.14 ------
Report Date: 6/12/2020 Page 19 of 48
All amilyses applicable to lhe CWA. SDWA, and RCRA are performed in accordance 10 NELAC protocols Pertinent sampling information is located on the aUached COC Confidential Business lnformalion: This report is provided for the e..xclush·e use of the
~ddressee Pri,·ile¥es of sub .. seq~enl ~~e or the ~?1:11e of this .con:ipany or any ~':1ber of its slaff, or reproduclio~ ~f lhis repo~ in ~o~ection ... wilh the o.~~1ertisemenl. P~?motio.n or sale of :"~Y ~rod~cl or P~?ces;, ~r in ~onn:c~ion w!lh th~ r~-publicarion oflhis repor,
3440 South 700 West
;;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-016C
Client Sample ID: TW4-20_05272020
Collection Date: 5/27/2020 952h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/3/2020 1103h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 5,800
Phone: [phone] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
----
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,080
5,160
4,760
5,050
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 1503h Extracted:
Units: µg/L Dilution Factor:
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
5,000 102 72-151
5,000 103 80-152
5,000 95.1 72-135
5,000 101 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 6.74
1.00 1.30
1.00 12.3
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.7 50.00 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.6 50.00 97.1 80-152
Surr: Dibromofluoromethane 1868-53-7 49.8 50.00 99.7 72-135
Surr: Toluene-d8 2037-26-5 49.9 50.00 99.8 80-124
Report Date: 6/12/2020 Page 38 of 48
All anal) ses applicable lo the CWA. SOWA. and RCRA nre perfom,ed in accordance 10 NELAC protocols Pertinent sampling i11rormation is locuted on lhe allached COC. Confidential Business (nformation: This report is provided for the exclusi, e use of the
~ddressee Prh·ile~es o_f sub,_seq~enl ~1;e of the ~:u:71e of lhis .co~pany or nny 11_!:mber of its sin.ff, or reproduclio~ ~r this repo~ in ~on?eclion,. ,,i1h lhe a~~enise~ent, P~?moti~ or sale of !LI!~ ~rod~cl or P~?Cess, ~r in ~onn:_c!ion w~lh th~ r~-publication of lhis repor1
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
2nd Quarter Chloroform 2020
2005695-016
Client Sample ID: TW4-20 05272020
Collection Date: 5/27/2020 952h
Received Date: 5/29/2020 I 050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 2228h
6/1/2020 1443h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 301
E353.2 0.100 7.23
Report Date: 6/12/2020 Page 21 of 48
All analyses applicable to the CW A. SOWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling infommlion is localed on lhe au ached COC Confidential Business Information: This repon is provided for the exclusiYe use of lhe
!ddressee Pri,·i\e~es o[ sub~seq~enl ~~e of the ~~e or lhis .con:ipany or 311) 1~'!1ber of ils staJT, or reproducli~ ~r this repo~ in ~o~eclion ... \\ith lhe a~vertisement. P~?rnolio.n ~r sale of ~~Y ~rod~ct or P~?Cess, ~r in ~nn:_c~ion w!th th~ r1;-publicalion or this report
American West
ANAlYTICAl LABORATORICS
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-005C
Client Sample ID: TW4-21_05272020
Collection Date: 5/27/2020 905h
Contact: Tanner Holliday
Received Date:
Analytical Results
5/29/2020 1050h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 6/2/2020 1113h Extracted:
Units: µg/L Dilution Factor: 20 Method:
CAS Reporting
Compound Number Limit
Chloroform 67-66-3 20.0
Surrogate Units: µg/L CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4 17060-07-0 1,010 1,000 IOI
Surr: 4-Bromofluorobenzene 460-00-4 971 1,000 97.1
Surr: Dibromofluoromethane 1868-53-7 985 1,000 98.5
Surr: Toluene-d8 2037-26-5 1,000 t,000 100
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 216h
Units: µg/L
Compound
Extracted:
Dilution Factor: Method:
CAS Reporting
Number Limit
SW8260D
Analytical
Result Qual
767
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
1.00 < 1.00
1.00 < 1.00
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
75-09-2
Result Amount Spiked
50.6 50.00
49.9 50.00
SO.I 50.00
50.9 50.00
1.00 < 1.00
%REC Limits Qual
IOI 72-151
99.9 80-152
100 72-135
102 80-124
Report Date: 6/12/2020 Page 27 of 48
All analyses applicable to 1he CW A, SOW A. and RCRA are performed in accordance to NE LAC protocols. Pertinent sampling information is locnled on the allached COC Confidenlfrll Business (nformntion: This report is provided for the c,..,cduth'o u~ of the
~ddressee Pri, ilc~es o_f sub .. seq~ent ~~e of lhe ~?1,'le of this .cor~pany or an) ~mber of ils staff, or reproduclio~ ~f I.his repo~ in ~on~eclion,. wilh t.he a~~ertise1"!1enL, P~?motio.n ~r ~ale of~!)~ -~rod~ct or P~?cess, ~r in ~onn~c!ion w!lh th~ r~-public:iaiou o(lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-005
Client Sample ID: TW4-21_05272020
Collection Date: 5/27/2020 905h
Received Date: 5/29/2020 I 050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1635h
6/1/2020 1420h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 353
E353.2 0.200 15.4
Report Date: 6/12/2020 Page IO of 48
All analyses applicable lo lhe CWA. SOWA, and RCRA are performed in accordance to NELAC profocols Pertinent sampling informalion is localed on the altad1ed COC Confidenlinl Business Informrilion: This report is provided for the exdusiYe use of lhe
~ddressee. Pri, ile~es of sub,_5eq~1enl ~~e of lhe ~~e of this .con:1pw1y or any 1~'!1ber of ils staff, or reproduclio~ ~f this repo~ in ~o°-?ection ... with lhe ~~·ertise~enl, P~?motio.n ~r sale of ?'!Y ~rod~cl or p~ocess, ~r in 7011n~c~ion w!lh th~ r~-p~blicalion of lhis report
ORGANIC ANALYTICAL REPORT
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-013C
Client Sample ID: TW4-22_05272020
Collection Date: 5/27/2020 935h
Received Date: 5/29/2020 I 050h
Analytical Results
Analyzed: 6/3/2020 1001h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 50
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 50.0 2,530
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-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
2,570
2,620
2,410
2,600
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 1357h
Units: µg/L
Comp':mnd
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
2,500 103 72-151
2,500 105 80-152
2,500 96.4 72-135
2,500 104 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua!
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
50.9
49.0
49.5
49.5
50.00 102 72-151
50.00 98.0 80-152
50.00 99.1 72-135
50.00 99.0 80-124
Report Date: 6/12/2020 Page 35 of 48
All anal~ ses applicable to the CW A, SOWA. and RCRA are perfomied in accordance to NE LAC prolocols Pertinent sampling informalion is located on the attached COC Confidential Business lnfonm1lion: This report is pro,•ided for lhe e:-.clusi, e use of lhe
~ddressee Prfrile~es of sub~seq~ent ~·~e of the ~~e of lhis .con.1pony or M) ~mber ofils staff, or reproduclio~ ~f lhis repo~ in ~o"!"'eclion~ '"'ilh 1he n~~ertise~enl, P~?motio.n ':r sale of~!~ ~rodl~ct or Pt;?Cess, ~r in ~nn:_c~ion w(lh th~ r:-publication or this report
3440 South 700 West
;aitLakeCity,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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-013
Client Sample ID: TW4-22_05272020
Collection Date: 5/27/2020 935h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1956h
6/1/2020 1434h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 578
E353.2 0.500 60.5
Report Date: 6/12/2020 Page 18 of 48
All anai)Ses applicable lo the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling informal.ion is located on the allached COC Confidential Business lnformalion: This report is provided for 1he exclusive use of the
~ddressee. Prh i\e~es o_f sub~seq~enl ~~e of lhe ~?1;1e of this .cor1:1pany or M) ~mber of ils staff, or reproductio~ ~f this repm; in ~~ection~ \\ilh I.he n~~ertise~enl, P~?motio.n ~r ~ale of ?1~Y .. ~rod~ct or p1:?cess, ~r in ~onn~c~ion w!lh th~ r~-publicillion of this repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-013C
Client Sample ID: TW4-23_06112020
ANALYTICAL LAB0RAT0R 1Es Collection Date: 6/11/2020 648h
3440 South 700 West
;alt Lake City, UT 84119
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1239h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN I 00
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-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
56.0 50.00 112 72-151
53.4 50.00 107 80-152
48.4 50.00 96.8 72-135
53.2 50.00 106 80-124
Report Date: 6/29/2020 Page 38 of 53
All anal~ ses applicable to lhe CWA. SOWA. and RCRA are perfomied in accordance lo NELAC prolocols Pertinenl sampling information is localed on the auached COC, Confidential Business Information: This repon is provided for 1he exclusi, e use of 1he
~ddressee Pri,·ile~es o_f su~seq~enl ~~e of I.he ~~e of this .co1~pany or any ~mber or its staJT, or reproduclio~ ~~\his repo~ in .co~eclion ... \\ilh 1he ~~~er1ise1!1enl, P~?molio.n '!r saJe of ~!Y ~rocl~ct or p1:ocess, ~r in ~nn:_c!ion w!th lh~ r:-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2006384-013
Client Sample ID: TW4-23_06I 12020
Collection Date: 6/11/2020 648h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1646h
6/15/2020 846h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 49.0
E353.2 0.100 < 0.100
Report Date: 6/29/2020 Page 19 of 53
All analyses applicable lo lhe CWA. SOWA. and RCRA ore performed in accordance to NELAC protocols, Pertinent sampling information is located on lhe attached COC Confiden1ial Business lnforrnalion: This reporl is provided for 1he exclusiYe use of1he
~ddressee Prh ile~es o,r sub,.3eq~enl ~~e of lhe ~?1!1e of this .co~pany or f\11)' ~mber of its slaff, or reproduclio~ ~f lhis repo~ in ~~ection~ ,,~th the a~vertisemenl, P~?molio.n ~r sale of ~!Y ~rod~cl or p~occss, ~r in ~nn~c!ion w!lh th~ r~·publication of this report
3440 South 700 West
;alt Lake City, UT 84 I 19
Phone:[phone]
foll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-002C
Client Sample ID: TW4-24_05272020
Collection Date: 5/27/2020 925h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/2/2020 115h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENJOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 49.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
I 868-53-7
2037-26-5
51.8 50.00
48.9 50.00
50.3 50.00
50.2 50.00
104 72-151
97.8 80-152
101 72-135
100 80-124
Report Date: 6/12/2020 Page 24 of48
All analyses applicable 10 the CWA, SOW A. and RCRA are performed in accordance Lo NELAC protocols. Pertinent sampling information is loc.ited on the attached COC. Con(identi.11 Business Information: This repon is prm•ided for the ~~Tush c use of the
~ddressee Privile~es or sub .. seq~enl ~~e of lhe ~~e of this .con:ipany or an) ~mber of its slaff, or reproducLio~ ~f this repo~ in .co~eclion~ \\ill, the a~\'ertisement. P~?motio.n or sale of~!): ~rod~ct or p1.?ces11, ~r in ~onn:_c~ion w!th th~ r~-pul:tlk:ntlt'ln or this report
3440 South 700 West
:;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-002
Client Sample ID: TW4-24_05272020
Collection Date: 5/27/2020 925h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite ( as N) mg/L ---
Date
Analyzed
6/9/2020 1512h
6/1 /2020 1416h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 1,060
E353.2 0.500 41.7 -----
Report Date: 6/12/2020 Page 7 of 48
All analyses applicable lo the CW A. SOWA. Md RCRA are performed in accordance to NELAC prolocols Pertinenl sampling information is located on the altached COC Confidential Business Information: This report is provided ro, ltlt! t.~C'lu,·th (' uJe or the
~ddressee Plirile~es o~ su~seq~ent ~~e of lhe ~~e of this.co~pany or M) ~mber of its staff, or reproducli~ ~f this repo~ in .con~eclion .. \\ith the a~vertise~enl, P~?moti~ or ~ale of ~!Y._~rod~cl or P~?cess, ~r in 7onn:c~io11 w~th ,h~ r1;:·publicntioH or this report
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-00 IC
Client Sample ID: TW4-25_05272020
Collection Date: 5/27/2020 915h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/2/2020 054h
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 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
51.7 50.00 103 72-151
49.3 50.00 98.6 80-152
49.5 50.00 99.0 72-135
51.0 50.00 102 80-124
Report Date: 6/12/2020 Page 23 of 48
All am1lyses applicable to the CWA. SOW A, and RCRA nre perfom1ed in accordance to NELAC prolocols. Per1inent sampling information is located on lhe auached COC ConlidenLial Business lnformalion: This report is provided for lhe exclusi, e use of the
~ddrcssee. Pri, ile~es o_f subpseq~enl ~?e or the ~:1',11e or this .con_ipany or any 1~mbe1 of its slaff, or reproduclio.~ ~'. I his repo~ in 7°°!1ection~ wilh the n~~ertisement, P~?moli~ or saJe of ~y ~rod~ct or P~?cess, ~r in ~nn:_c~ion w~lh 1h~ r~-publicalion of this report
American West ANALYTICAL LABORATORIE8
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-001
Client Sample ID: TW4-25_05272020
Collection Date: 5/27/2020 915h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1455h
6/1/2020 1413h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 2.00 76.8
E353.2 0.100 0.851
Report Date: 6/12/2020 Page 6 of 48
All analyses applicable to lhe CWA, SDW A. and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling information is localed on the auached COC. Conlidential Business Jnformalion: This report is provided for the exclush e use of the
~ddressee Pri\•ile~es a: sub .. seq~enl ~~e of the ~~e of this .cor,:1pany or nil) ~mber of its staff, or reproduct10~ ~f this repo~ in ~o~ecLion .. with the o~ver1ise1~en1, p~~motio.n ~r ~a1e of ~Y. ~rod~cl or P~?cess, ~r in 7011n:c~ion w!lh lh~ r~-publication or this report
American West ANALYTICAi LABORATORIES
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-01 lC
Client Sample ID: TW4-26_06122020
Collection Date: 6/12/2020 823h
Contact: Tanner Holliday
Received Date: 6/16/2020 1 OOOh
Analytical Results
Test Code: 8260D-W-DENI00
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 6/17/2020 1418h
Units: µg/L
Compound
Chlorofonn
Phone: (80 l) 263-8686 Surrogate Units: µg/L
foll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
CAS Result Amount Spiked %REC
17060-07-0 556 500.0 Ill
460-00-4 528 500.0 !06
1868-53-7 506 500.0 IOI
2037-26-5 524 500.0 105
SW8260D
Analytical
Result Qual
1,140
Limits Qual
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: 6/17/2020 1136h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: I ,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
SW8260D
Analytical
Result Qua(
< 1.00
< 1.00
< 1.00
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 55.8 50.00 112 72-151
460-00-4 51.1 50.00 102 80-152
1868-53-7 52.0 50.00 !04 72-135
2037-26-5 51.8 50.00 104 80-124
Report Date: 6/29/2020 Page 29 of 41
All anal) ses applicable to lhe CWA. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COC Confidential Business lnformation: This report is provided for lhe exclusi, e use of the
~ddressee. Pri, ile~es o.r su~seg~ent ~~e of 1he ~~e of this .con:1pany or M) ~~be1· of ils staff. or reproductio~ ~f this repo~ in .con~ec1ion .. with the a~\'erlise'!lent, p~~motio.n ~r !ale of?'!) ~rod~ct or P~?cess, ~r in ~nn!c!ion w!th th~ r1;-p~blication of this report
3440 South 700 West
ialt 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-011
Client Sample ID: TW4-26_06122020
Collection Date: 6/12/2020 823h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 334h
6/16/2020 1253h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300,0 1.00 35.1
E353.2 0.100 11.1
Report Date: 6/29/2020 Page 16 of 41
All analyses applicable to lhe CWA, SOWA, and RCRA are performed in accordance to NELAC prolocols Pertinenl sampling information is located on lhe auached COC. Confidential Business lnformalion: This report is pro,·ided for thee:xclusiYe use of the
~dressee_ Prl\ ile~es o,r sub .. seq~ent ~~e of the ~~e of this .con;ipany or any ~7~be1 of its stnff, or reproductio1~ ~:this repo~ in .con~eclion ... \\~th the ~vertisemenl, P~?moti~ or saJe of ~.f ~rod~ct or P~?Ccs;, ~r in ~nm;_c~ion w~lh th~ ri;-publication 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-0I 7C
Client Sample ID: TW4-27_06112020
Collection Date: 6/11/2020 729h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1401h
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 7.92
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
52.6
46.8
51.9
50.00 108 72-151
50.00 105 80-152
50.00 93.6 72-135
50.00 104 80-124
Report Date: 6/29/2020 Page 42 of 53
All analyses applicable to lhe CW A. SOWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on lhe allached COC Conridenlial Business Information: This report is pro\'ided for the exclusi, e use of the
~ddressee Pri, ile~es o_f sub~seq~enl ~1~e of the ~~e of lhis .co11,1pany or nny ~mber of its staff, or reproducti~! ~rthis repo~ in ~on~ection ... \\ith the ~~1ertise~enl, P~?moti~n ~r sale of ~!Y ~rod1~l or p1:ocess, ~r in ~nn~c!ion w!lh th~ r~-publication 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-017
Client Sample ID: TW4-27_06112020
Collection Date: 6/11/2020 729h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1827h
6/15/2020 850h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 28.0
E353.2 0.500 21.5
Report Date: 6/29/2020 Page 23 of 53
All analyses applicable to lhe CWA, SOWA. and RCRA are perrormed in accordance to NELAC prolocols Pertinenl sampling information is located on the attached COC Confidenlial Business lnformation: This repor1 is provided (or 1hc.exclwive use of the
~ddressee P,1\•i\e~es o.r sub~seq~ent ~~e of the ~~e of this .con;ipany or any ~'!1be1 of ils slaff. or reproductio~ ~r 1his repo~ in ;or1~eclion,, wilh the 3C;~·ertisement, P~?moli~n ~r sale of~) ~rod~cl or p1:?ces1,, ~r in ~nn:c~ion w!lh ti~ r:pYblication of lhis report
3440 South 700 West
;alt Lake City, UT 84 I I 9
Phone:[phone]
foll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-004C
Client Sample ID: TW4-28_06102020
Collection Date: 6/10/2020 805h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2112h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 53.9 50.00 108 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.6 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 46.9 50.00 93.8 72-135
Surr: Toluene-d8 2037-26-5 52.6 50.00 105 80-124
Report Date: 6/29/2020 Page 29 of 53
All analyses applicable 10 the CW A. SOWA, and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling informal ion is loco.led on lhe au ached COC, Confidentilll Business lnform::ilion: This report is prm·ided for lhe exclusi\·e use of the
~ddressee Pri, ile~es Of' sub~seq~enl ~;e of the ~~e of this _con:ipany or nny ~mbe1 of its slaff, or reproductio~ ~f this repo~ in .con~eclion" ,vith the a~~·ertisemenl, P~?molio.n ~r ~ale of~!~~ ~rod~l or p1.ocess, ~r in ~nn:c!ion w!th th~ r:-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
falt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-004
Client Sample ID: TW4-28_06102020
Collection Date: 6/10/2020 805h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1309h
6/15/2020 829h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 49.8
E353.2 0.100 9.55
Report Date: 6/29/2020 Page IO of 53
All an:,lyses applicable lo the CW A. SOWA. and RCRA are performed in accordance to NELAC protocols. Per1inenl sampling informalion is lociJted on the al1ached COC Confidential Business Jnfonnolion: This report is pro\'ided for the e.\'.clusi\·e use of lhe
!ddressee. Pri, ile~es o.r su~eq~nl ~;e of lhe ~~e of this .co,~pany or rut~ ~mber of its slaff, or repmducfior~ ~f this repo~ in ~eel ion ... with lhe a<!vertisemenl. P~?molio.n or safe of ~Y ~rod~I or P~?Cess, ~r in ~nn~c!ion w(th th~ r~-publication of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-008C
American West Client Sample ID: TW4-29_06122020
AN.At vr1 cA L L .. e oRAToR IE s Collection Date: 6/12/2020 746h
Received Date: 6/16/2020 1000h
Analytical Results
Analyzed: 6/17/2020 13 17h Extracted:
Units: µg/L Dilution Factor:
3440 South 700 West
falt Lake City, UT 84119 Compound
Chloroform
Phone: [phone] Surrogate Units: µg/L CAS
Toll Free: [phone] Surr: l ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Fax: [phone] Surr: Dibromofluoromethane 1868-53-7
:-mail: [e-mail] Surr: Toluene-d8 2037-26-5
10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENJOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 686
Result Amount Spiked %REC Limits Qual
548 500.0 110 72-151
523 500.0 105 80-152
510 500.0 102 72-135
515 500.0 103 80-124
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/17/2020 1036h
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
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 54.8 50.00 110 72-151
460-00-4 51.2 50.00 102 80-152
1868-53-7 51.1 50.00 102 72-135
2037-26-5 51.5 50.00 103 80-124
Report Date: 6/29/2020 Page 26 of 41
All Mill) ses applicable lo lhe CWA. SDWA, and RCRA are perfom,ed in accordance to NELAC prot~s Pertinent sampling informatim\ is located on the attached COC. Conrideotial Business Information; This report is prorided for lhe e.'l:clusi\'e use oflhe
~ddressee Pri, ile~es o,r su~eq~1enl ~1~e of lhe ~~e of lhis .co1~pany or any ~mberof its s1aIT, or reproductio!) ~f this repo~ in ~~1eccion ... with the a~~·er1isemenl, P~?molici;n ~r sale of ~!Y ~rod~ct or pr.ocess, ~r in ?'""~c!ion \\'!lh 1h~ r~publication of rhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
foll Free: [phone]
Fax: (80 l) 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-008
Client Sample ID: TW4-29 _06122020
Collection Date: 6/12/2020 746h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 244h
6/16/2020 1244h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 42.2
E353 .2 0.100 3.18
Report Date: 6/29/2020 Page 13 of 41
All anal) ses applicable to lhe CW A. SOW A. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is localed on lhe auached COC Confiden!ial Business Information: This report is pro,,ided for the exclusil'e use of 1he
~ddressee. Pri\file~es or sub...5eq~enl ~~e of the ~'.1':"e or this .cor,:ip::my or M) ~mber of its staff, or reproduclio~ ~f this repo~ in ~o°-?eclion,. wiLl1 the a~,•ertisement, P~?moti~n o_r ~ale of~!~. ~rod~cl or p~~cess, ~r in ~nn:_c~ion w!lh th~ r~-p~blication of this 1epor1
American West
ANALYTICAL LABORATOR IES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-003C
Client Sample ID: TW4-30_06122020
Collection Date: 6/12/2020 648h
Received Date: 6/16/2020 1 OOOh
Analytical Results
Analyzed: 6/17/2020 814h
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
I 7060-07-0
460-00-4
1868-53-7
2037-26-5
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 65.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55.6 50.00 Ill 72-151
52.4 50.00 105 80-152
51.8 50.00 104 72-135
52.2 50.00 104 80-124
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 6/29/2020 Page 21 of 4 I
All anal)ses applicable lo 1he CWA. SDWA. and RCRA are perfomled in accordance to NE LAC protocols. Per1inent sampling information is located on the au ached COC Confidenliol Business lnformolion: This report is pro\'ided for the exclusi\·e use of the
~ddressee Pri, ile~es o; sub_seq~ent ~~e of lhe ~~1e of lhis .co1~pany or any ~mber of its slaff, or reproduclio!) ~~lhis repo~ in ~on?ection .. ,\'ith the ~'.'ertise~nl, P~?moli~ or sale of ~!Y ~rod~cl Of P~?cess, ~r in ?'""~!ion \\'!lh lh~ r!·publicnlion of 1his repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2006426-003
Client Sample ID: TW4-30_06122020
Collection Date: 6/12/2020 648h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 013h
6/16/2020 1238h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.6
E353.2 0.100 3.69
Report Date: 6/29/2020 Page 8 of 41
All an:il}ses applicable to the CW A. SOWA. and RCRA are 11erformed in accordance to NELAC protocols Pertinent sampling information is located on the auached COC Confidential Business lnform:ition: This report is pro"ided for lhe exclusiye use of the
~ddressee Pri, ile~es o,r sub .. seq~enl ~~e of the ~~e of this .co1~pany or any l~1J1be1 of its sln.ff, or reproduclio~ ~f Lhis repo~ in ~o"?eclion,. wilh the °'!"ertise1:1enl, p~~molio.n ~r sale of~!) ~rod~ct or P~?cess, ~r in ~01m~c!io11 w!lh th~ r~-publicalion or this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-0lOC
Client Sample ID: TW4-31_06112020
ANALvr1cAL LAeoRAroR 1Es Collection Date: 6/11/2020 620h
3440 South 700 West
Mt Lake City, UT 84119
Received Date: 6/12/2020 101 Oh
Analytical Results
Analyzed: 6/13/2020 1138h
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 < l.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 54.9
460-00-4 51.8
1868-53-7 47.4
2037-26-5 52.7
50.00 110 72-151
50.00 104 80-152
50.00 94.7 72-135
50.00 105 80-124
Report Date: 6/29/2020 Page 35 of 53
All an.ii) ses applicable to lhe CWA, SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling information is localed on the al1ached COC. Conlidentiul Business Information: This report is provided for the exclusi\'e use of lhe
~ddressee Pri, ile~es o_f sub .. seq~enl ~~e of the ~~e of this .con:ipany or an)' 1~1;1ber of ils staff, or reproduclio~ ~! this repo~ in ~o~ection .. with the n~~1ertise~ent, p~~molio.n or sale of ~;y.~rod~ct or P~?cess, ~r in ~nn:c~ion w\th th~ r~-publication of this reporl
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-010
Client Sample ID: TW4-31_06I 12020
Collection Date: 6/11/2020 620h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1613h
6/15/2020 843h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 36.7
E353.2 0.100 0.569
Report Date: 6/29/2020 Page 16 of 53
All anal)ses applicable to the CW A, SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling informal ion is located on !he au ached COC Confidential Business lnformotion; This report is pro\'ided ror the exclusi,·e use or the
~ddressee Pri, ile~es o.f su~eq~enl ~~e of lhe ~?1:'1e of this .co1~pany or M) ,~mber of its staff or reproducti~ ~f this repo~ in ~~ection .. \\ilh the ~\'ertise"?enl, P~?moli~ ~r :aJe of~)~ ~rod~I or p~ocess, ~r in ~~!ion \\'!lh lh~ r~-pubJication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-005C
Client Sample ID: TW4-32_06102020
ANALvT1cAL LAeonATon1Es Collection Date: 6/10/2020 812h
3440 South 700 West
)alt Lake City, UT 84119
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2133h
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 < l.00
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0 53.7
460-00-4 52.3
1868-53-7 47.1
2037-26-5 51.8
50.00 107 72-151
50.00 105 80-152
50.00 94.3 72-135
50.00 104 80-124
Report Date: 6/29/2020 Page 30 of 53
All analyses applicable lo the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols. Pertinenl sampling informalion is located on the anached COC Conridential Business Information: This report is pro\1ided for 1he exclusi\e use of the
~ddressee. Prl\"ile~es o~ su~eq~enl ~~e of the ~!1':"e ollhis .con:ipany or any ~mber of its slaff, or reproductio!~ ~f lhis repo~ in ~on~eclio".. wilh lhe ~vertisement. P~?moli~n ~r sale of~~. ~rod~t or p~ocess, ~r in ~nn~!ion \\'!lh th~ r~-p~blication of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
Mt Lake City, UT 84119
Phone: (80 l) 263-8686
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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-005
Client Sample ID: TW4-32_06102020
Collection Date: 6/10/2020 812h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1326h
6/15/2020 830h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 57.0
E353.2 0.100 2.19
Report Date: 6/29/2020 Page 11 of 53
All anal) ses applicable 1o the CWA. SOW A. and RCRA are perfonned in accordance to NELAC protocols Pertinenl sampling informalion is localed on lhe attached COC Confidenlial Business Information: This repon is provided for lhe exclusi,·e use of lhe
!ddressee, Pri,·ile~es o.f su~eq~enl ~,~e or the ~~e of this .co~ixiny or an) ~mber of its Slaff, or reproductio~ ~f 1.his repo~ in ~~ection__ wilh the a'!_,1ertisemenl, p~~moli°!1 ~r sale of?'!>. ~rod~I or p~ocess, ~r in ?1""~c!ion w!lh th~ r~-publication of this repor1
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-006C
Client Sample ID: TW4-33_06122020
ANALrncA1. LA00RAT0R1Es Collection Date: 6/12/2020 724h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 6/16/2020 1 OOOh
Analytical Results
Analyzed: 6/17/2020 915h
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-DENI00
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 90.1
74-87-3 1.00 < l.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55.2 50.00 110 72-151
51.7 50.00 103 80-152
50.8 50.00 102 72-135
51.0 50.00 102 80-124
Report Date: 6/29/2020 Page 24 of 41
All anal, ses applicable lo the CWA, SOWA. and RCRA .1re perfom1ed in accordance to NELAC protocols Peninenl samplin~ in(ormolion is localed on lhe allached COC Confidential Business Cnformnlion: This repon is provided for 1he exdush e use of the
~ddressee Pri, ile~es o! sub,_seq~enl ~1~e or the ~~e of this ,con_ipany or any "2:'!'ber of ils stnff, or reproducli~ ~f this repo~ in .co"!1ection,. with the ~~ertise~enl, P~?motio.n ':r ~ale of ~!Y ~rod~cl or P~?Cess, ~r in ~nn~c!ion w!th th~ r~-publicalion of this report
American West
ANALYTICAi LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
2nd Quarter Chlorofonn 2020
2006426-006
Client Sample ID: TW4-33 06122020
Collection Date: 6/12/2020 724h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 046h
6/16/2020 1242h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 48.9
E353.2 0.100 3.26
Report Date: 6/29/2020 Page 11 of 41
All analyses applicable to lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinenl sampling information is localed on the aUached COC. Confidential Business lnforrm1lion: This repon is pro,1ided for lhe exclusi,·e use of the
~ddressee Pri, ile~es or sub ... seq~enl ~1~e of the ~~e of lhis .cor1;pnny or M) ~1!1ber of ils slaff, or reproduclio~ ~rthis repo~ in ~on~eclion~ with the a~~ertisemenL P~?molio.n or sale of ::U~Y, ~rod~ct or P~?Cess, ~r in ~nn~c!ion w!lh lh? r:·publicalion of lhis repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-01 lC
Client Sample ID: TW4-34_06112020
ANALYTICAL LAD0RAT0R 1Es Collection Date: 6/11 /2020 628h
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: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1158h
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-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55.5 50.00 Ill 72-151
52.5 50.00 105 80-152
47.5 50.00 95.0 72-135
52.9 50.00 106 80-124
Report Date: 6/29/2020 Page 36 of 53
All analyses applicable lo lhe CWA, SOWA. and RCRA :ire performed in accordance lo NE LAC prolocols.. Pertinent sampling i11formalion is localed on the au ached COC Confidenlinl Business lnformnlion: This repon is provided for !he exclusi, e use of 1he
!ddressee Pri, ile~es o: sub,_seq~ent ~;e or the ~?1,11e of lhis .con;ipany or M)' 1~~be1 of ils staff. or reproductio~ ~r lhis repo~ in .con~eclion .. with the n~~ertisemenl, P~?molio.n t:r ~ale of~~~ ~rod~cl or p~ocess, ~r in ~nn~c!ion \\'!lh lh? r~-publicalion of lhis report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-011
Client Sample ID: TW4-34_06112020
ANALvr1cAL LAeoRAroR1Es Collection Date: 6/11/2020 628h
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: 6/12/2020 1010h
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
6/22/2020 1556h E300.0 1.00 20.9
6/15/2020 844h E353.2 0.100 1.24
Report Date: 6/29/2020 Page 17 of 53
All anah ses applicable to lhe CWA. SOWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the auached COC. Confidential Business Information: This report is provided for the exclw;ire use of lhe
~ddressee P1il'ile~es or sub..5eq~enl ~~e of the ~'.1';1e of this .con:1pnny or any ~~her of its staff, or reproductio~ ~f this repo~ in .co~ection .. with the n~vertisemenl, P~?motio.n or ~ale of ?-1!~~ ~rod~cl or P~?cess, ~r in ~nn!c~ion ,,·~Lh th~ r~-publicalion of this repon
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-012C
Client Sample ID: TW4-35 _06112020
Collection Date: 6/11/2020 636h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/13/2020 1219h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
54.9
52.7
48.0
52.4
50.00 110 72-151
50.00 105 80-152
50.00 96.1 72-135
50.00 105 80-124
Report Date: 6/29/2020 Page 3 7 of 53
All analyses applicable lo the CWA, SOW A. and RCRA are performed in accordance 10 NE LAC prolocols, Pertinent sampling information is localed on the altached COC Confidential Business Jnformalion: This report is provided for 1he e..'i.tlush <! tne of the
~ddressee, Pri,•i\e~es or subnseq~enl ~~e of lhe ~?1,11e of this .con:pany or M) ~mber of ils staJT, or reproducLio~ ~f lhis repo~ in ,co~eclion,. wilh lhe ~\•ertise1~ent. P~?molio.n ~r ~ale of ?1!Y .. ~rod~ct or P~?cess, ~r in ~M~C!ion w!lh th~ r~-publicntlOu of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-012
Client Sample ID: TW4-35_06112020
Collection Date: 6/11/2020 636h
Received Date: 6/12/2020 l O 10h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1630h
6/15/2020 845h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 34.0
E353.2 0.100 0.699 -----
Report Date: 6/29/2020 Page I 8 of 53
All anal~ ses applicable to lhe CWA. SDWA. and RCRA are performed in accordance to NELAC prolocols Pertinent sampling information is located on I.he allached COC, Confidenlial Business lnfonnnlion: This reporl is pro\'ided for the exclusiYe use of the
~ddressee Prfrile~es o.f sub~seq~enl ~~e of lhe ~?'!'e of I his .con:ipany or any ~~bc1 of its staff, or reproduclio~ ~~ this repo~ in ~o~ection,. \\ith the a~,•ertisement, P~?motio.n a._r ~ale of ?1!), ~rod~ct or p~ocess, ~r in ~nm;c~ion w~lh lh~ r~-publicat.ion 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-009C
Client Sample ID: TW4-36_06112020
Collection Date: 6/11/2020 610h
Received Date: 6/12/2020 10 IOh
Analytical Results
Analyzed: 6/13/2020 813h Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L CAS
---
Surr: l,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-dB 2037-26-5
1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
----
Result Amount Spiked %REC Limits Qual
54.0 50.00 108 72-151
51.1 50.00 102 80-152
47.8 50.00 95.5 72-135
51.6 50.00 103 80-124
Report Date: 6/29/2020 Page 34 of 53
All analyses applicable to lhe CW A. SOWA, and RCRA are i:ierformed in accordance to NELAC protocols. Pertinent sampling information is localed on lhe altached COC Confidenlial Business Informal ion: This repon is provided for lhe exclusive use of lhe
~ddressee. Pri, ile~es o.rsub .. seq~ent ~~e of the ~?1,lle of lhis .co~pany or nny ~~be1 of its slaff, or reproduclio~ ~!this repo~ in ~o~eclion_. ,,ilh lhe n~,•ertisemenL P~?moti~n ~r sale of!"!~. ~rod~cl or p1
0
oces•;, ~r in ';°nm:c~ion w!th th~ r~-publicnlion of this repon
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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-009
Client Sample ID: TW4-36_06l 12020
Collection Date: 6/11 /2020 610h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1506h
6/15/2020 831 h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 67.0
E353.2 0.100 < 0.100
Report Date: 6/29/2020 Page 15 of 53
All analyses applicable to the CW A. SOWA. and RCRA are perfom1ed in accordance lo NELAC prolocols Pertinent sampling informalion is located on lhe altached COC. Conlidential Business Information: This repon is provided for the exclusi,·e use o[the
!ddressee Pri, ile~es o_r sub .. seq~enl ~~e of the ~?1:'e of this .cot~pany or an) ~mber or its slnff, or reproductio!! ~f this repo~ in .con~eclionp with the a~~·ertisement, P~?motio.n or sale of ?-1!Y ~rod~cl or P~?cess, ~r in ~nn!c~ion w!lh th~ r~-publication of I his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: (80 l) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-015C
Client Sample ID: TW4-37_05272020
Collection Date: 5/27/2020 945h
Contact: Tanner Holliday
Received Date: 5/29/2020 1050h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 6/3/2020 1042h
Units: µg/L
Compound
Chloroform
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 100 Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua\
67-66-3 100 11,700
-----------
CAS Result Amount Spiked %REC Limits Qual ---
17060-07-0 5,190 5,000 104 72-151
460-00-4 5,160 5,000 103 80-152
1868-53-7 4,940 5,000 98.9 72-135
2037-26-5 5,200 5,000 104 80-124
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 1438h Extracted:
Units: µg/L Dilution Factor: Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 11.8
Chloromethane 74-87-3 1.00 1.44
Methylene chloride 75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.8 50.00 102 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.0 50.00 96.0 80-152
Surr: Dibromofluoromethane 1868-53-7 49.4 50.00 98.9 72-135
Surr: Toluene-d8 2037-26-5 50.0 50.00 100 80-124
Report Date: 6/12/2020 Page 37 of 48
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance 10 NELAC prolocols Per1inenl sampling information is localed on lhe attached COC Conlidential Business Information: This report is provided for the I.\Xc:lush.c use or the
~ddressee Pri, il~es of sub .. seq~1ent ~!e of lhe ~~e of this .co1:1po11y or nn~ 1~mber of i1s staIT, or reproduclio~ ~f 1his repo~ in .con~1ection .. ,\ith lhe a~vertise~enl, P~?moti°:"' ~r ~aJe of ~!Y. -~rod~cl or P~?Cess, ~r in ~nn~c!ion w~lh th~ r~-p~bliC.:ulun or1his 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-015
Client Sample ID: TW4-37_05272020
Collection Date: 5/27/2020 945h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 221 lh
6/1/2020 1437h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 321
E353.2 0.200 28.3
Report Date: 6/12/2020 Page 20 of 48
All anal) ses applicnble to the CWA. SDW A. and RCRA are performed in accordance to NELAC prolocols Pertinent sampling information is located on the aUached COC Conridentlnl Business Jnformohon: This report is pro\'ided for the c.u ·lu:Sihc:-use of the
~ddressee Pri, ile~es o_f su~seq~tent ~~e of the ~~e of I his .co~p:iny or M) ~mbet· of its s1afT, or reproduclio~ ~f this repo~ in ~~eclion~ with the ~vertisemenl, P~?motio.n or saJe of ?"!Y ~rod~L or p1.~es1;, ~r in ~cmn:_c!ion w!Lh th~ r:_-p~blicnli.an or lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-014C
Client Sample ID: TW4-38_06112020
ANALYTICAL 1A00AAT0R1Es Collection Date: 6/11/2020 658h
3440 South 700 West
~alt Lake City, UT 84119
Received Date: 6/12/2020 IO 1 Oh
Analytical Results
Analyzed: 6/13/2020 1300h
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]
ToJI Free: [phone]
Fax: [phone]
:-mail: [e-mail] Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0 53.7
460-00-4 SO.I
1868-53-7 46.1
2037-26-5 51.6
----
50.00 107 72-151
50.00 100 80-152
50.00 92.2 72-135
50.00 103 80-124
Report Date: 6/29/2020 Page 39 of 53
All anill)ses applicable lo 1he CWA, SDWA, and RCRA are performed in accordance to NELAC protocols, Per1inen1 sampling information is localed on the attached COC. Confideolial Business lnformalion; This repon is pro\'ided for the exclusi\·e use of1he
~ddressee Pri, ile~es of su~seq~ent ~,;e or the ~~e of this .co~pnny or anr ~mber of ils slalT, or reproducli~! ~f fhis repo~ in ~~eclion~ wilh lhe a<!~·ertisemenl, P~?moli~ o_r sale of !11;). ~rod~ct or pr:ocess, ~r in ~onn~c!ion w!lh th~ r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84 I 19
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-014
Client Sample ID: TW4-38_06112020
Collection Date: 6/11/2020 658h
Received Date: 6/12/2020 IO JOh
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1703h
6/15/2020 84 7h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 34.9
E353.2 0.100 9.00 ----
Report Date: 6/29/2020 Page 20 of 53
All analyses applicable to the CWA SDWA and RCRA are performed in accordance to NELAC prolocols. Pertinenl sampling informalion is located on lhe altached COC Confidenliul Business [nformntion: This report is provided for the exclusi\e use of1he
~ddressee. Pri, ile~es o_f su~seq~enl .u~e of the ~?1:'e of lhis .co".1pany or an) ~'!Iber of its staff, or reproductio~ ~f this repo~ in ~o~eclion .. with lhe n~vertisement, P~?motio.n or sale of ~Y. prodl~ct or p~ocess, ~r in ~onn~c~ion w\lh th~ r~-p~blication of this repon
American West ANALYTICAL LABORATORIES
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-004C
Client Sample ID: TW4-39 _ 05272020
Collection Date: 5/27/2020 1002h
Contact: Tanner Holliday
Received Date:
Analytical Results
5/29/2020 1050h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 6/2/2020 1053h
Units: µg/L
Compound
Chloroform
Phone: [phone] Surrogate Units: µg/L
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 100 Method:
CAS Reporting
Number Limit
67-66-3 100
CAS Result Amount Spiked %REC
17060-07-0 4,960 5,000 99.1
460-00-4 4,980 5,000 99.5
1868-53-7 4,820 5,000 96.5
2037-26-5 5,090 5,000 102
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/2/2020 155h
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:
CAS Reporting
Number Limit
56-23-5 1.00
74-87-3 1.00
75-09-2 1.00
CAS Result Amount Spiked %REC
17060-07-0 50.6 50.00 101
460-00-4 49.I 50.00 98.1
1868-53-7 50.1 50.00 100
2037-26-5 49.9 50.00 99.8
SW8260D
Analytical
Result Qual
5,870
Limits Qual
72-151
80-152
72-135
80-124
SW8260D
Analytical
Result Qual
7.56
< 1.00
< 1.00
Limits Qual
72-151
80-152
72-135
80-124
Report Date: 6/12/2020 Page 26 of 48
All analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the nllached COC Confidential Business lnformotion: This repon is pro\'ided for lhe e~clusi\'e use of the
~ddressee Pri, ile~es or sub .. seq~ent ~·~e of lhe ~~e or this .con_ipany or fill) '':1:~be, of ils staff, or reproductio~ ~f I.his repo~ in .co~ection~ "ilh the a~~ertise1~ent, P~?motio.n or sale of '.31~). ~rod~cl or P~?cess, ~r in ':°nn!c~ion w!lh th? r~~publiclllion of this report
American West ANALYTICAL LABORATORlfS
3440 South 700 West
;alt Lake City, UT 84 I 19
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-004
Client Sample ID: TW4-39 _05272020
Collection Date: 5/27/2020 I 002h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1619h
6/1/2020 1419h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 88.5
E353.2 0.100 5.01
Report Date: 6/12/2020 Page 9 of 48
All analyses applicable to lhe CWA. SOW A. and RCRA are performed in accordance to NELAC prolocols. Pertinent sampling i11formalion is located on Lhe auached COC Confidential Business Information: This repon is provided fnrthOt''\"hl~l\t' use of1he
!ddressee Pri\·ile~es o~ su~seq~enl ~~ of the ~~e or I his .co~pany or anr ~mber of ils stall, or reproducli~ ~~this repo~ in ~~eel ion~ \\.ith 1he a~~1er1ise~n1, P~?motio_n ~r ~aJe or ~2Y._~rodl~l or P~?cess, ~r in ~onn~c.tion ,,·!th 11!~ r:"p~blic:1lon ar this report
3440 South 700 West
:;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chlorofonn 2020
Lab Sample ID: 2005695-003C
Client Sample ID: TW4-40_05272020
Collection Date: 5/27/2020 1245h
Received Date: 5/29/2020 1050h
Analytical Results
Analyzed: 6/2/2020 91 lh
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 367
-----
CAS Result Amount Spiked %REC Limits Qual ----Phone: [phone] Surrogate ------------Units: µg/L
foll Free: [phone]
Fax:[phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
498
488
487
502
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 135h Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
---
500.0 99.6 72-151
500.0 97.6 80-152
500.0 97.5 72-135
500.0 100 80-124
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 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 17060-07-0 51.l 50.00 102 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.9 50.00 97.9 80-152
Surr: Dibromofluoromethane 1868-53-7 49.4 50.00 98.8 72-135
Surr: Toluene-d8 2037-26-5 50.4 50.00 101 80-124
Report Date: 6/12/2020 Page 25 of 48
All analyses applicable to lhe CWA, SOWA. and RCRA are perfonned in accordance to NE LAC prolocols Per1inent sampling informalion is located on the attached COC Confidential Business Information: This repon is provided for the o,:dUSl,·e ~ of the
~cldressee Pri,·ile~es of sub .. seq~ent ~e of the ~~e of lhis .co~J),'.lny or M)" '~r.!1ber of its slaff, or reproductio~ ~fthis repo~ in .co~1eclion .. \\·ilh the ~vertise1~I. P~?molio.n ~r ~e of ~!),~.prod~cl or P~?cess, ~r in ~nn~cJion \\'!lh th~ r:-p~blltC111o.i, or1his report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-003
Client Sample ID: TW4-40_05272020
Collection Date: 5/27/2020 1245h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 1528h
6/1/2020 1418h ---
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 36.5
E353.2 0.100 2.91
Report Date: 6/12/2020 Page 8 of 48
All analyses npP.l,cable to lhe CWA. SOWA. and R.CRA are perfonned in accordance to NELAC ITf010C-olJ. 'Peninml sn.mplinu inromt:11 Oil\ is located on the attached COC. Conlickntiol Business lnfonn.111on: This report is provided for 1hoc.~clu~lw?, use of the
~ddressce. Pri,·1!C'~es o_f sub~seq~ent ~~e of 1he !~~~c or1his .co".1pany or any ~mber of its slaff, or rcproductu.w) ~f 1his 1q><>J! in ~on~lot11on .. \\ith the at!vertisement, P~?moli~ ~ ~c of ~!r. ~rod~t <>r-JJt;~ess. ~r in ~nn:cJion w!lh lh~ r:pubHtmlon of !his report
American West
ANALYTICAL I ABORATORIES
3440 South 700 West
;alt Lake City, UT 84 I I 9
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-009C
Client Sample ID: TW4-41_05272020
Collection Date: 5/27/2020 1215h
Received Date: 5/29/2020 l 050h
Analytical Results
Analyzed: 6/2/2020 1235h
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 Qual
67-66-3 20.0 1,220
Phone: (80 I) 263-8686 Surrogate --------------CAS Result Amount Spiked %REC Limits Units: µg/1.. Qual
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
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethanc
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,020
978
994
1,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 6/2/2020 337h Extracted:
Units: µg/L Dilution Factor: 1
CAS
Compound Number
Carbon tetrachloride 56-23-5
Chloromethane 74-87-3
Methylene chloride 75-09-2
1,000 102 72-151
1,000 97.8 80-152
1,000 99.4 72-135
1,000 IOI 80-124
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/1.. CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.7 50.00 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.5 50.00 97.0 80-152
Surr: Dibromofluoromethane 1868-53-7 50.4 50.00 101 72-135
Surr: Toluene-d8 2037-26-5 50.1 50.00 100 80-124
Report Date: 6/12/2020 Page 31 of 48
All analyses applictible lo lhe CWA. SOWA and RCRA are perfonned in accordance to NELAC prolocols Pertinenl sampling information is located on lhe au ached COC Conridenti.o.l Business (nformation; This report is provided for the e.~clusi, e use of the
~ddressee Pridle~es Of' sub,.seq~enl ~~e of the ~~e or lhis .con:1pa11y or M)' ·~1!1ber or its staff, or reproduclio~ ~f I his repo~ in ~on~ection~ with the a~vertisemenL P~?motio.n or sale of ~!Y rrodL~cL or p•:?Cess, ~r in ~nn:_c~ion w!th th~ r~-publication or this report
American West ANALYTICAL LABORATORIES
3440 South 700 West
>alt Lake City, UT 84 I 19
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-009
Client Sample ID: TW4-4I_05272020
Collection Date: 5/27/2020 1215h
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 I 849h
6/1/2020 1430h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 41.7
E353.2 0.100 6.78
Report Date: 6/12/2020 Page 14 of 48
All anal) ses applicable lo lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Per1inenl sampling informo.tion is located on the au ached COC. Confidential Business Jnform:llion: This report is provided for the exclusi, e use of lhe
~ddressee Pri,•i\e~es o: sub~seq~ent ~1~e or the ~~e or !his .con,1pany or M) 1~mber of its slaIT, or reproduclio~ ~~this repo~ in .cm1?ection~ wi1h lhe .i~:er1isemenl, P~?moti~n or ~aJe of ~!Y. ~rod~cl or p~ocess, ~r in ~nn~c~ion w~lh 1h~ r~-publicalion of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-003C
Client Sample ID: TW4-42_06I02020
ANAtvT1cAL LAB0RAT0R1Es Collection Date: 6/10/2020 752h
3440 South 700 West
>alt Lake City, UT 84119
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2052h Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L CAS
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
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 l.00 < 1.00
Result Amount Spiked %REC Limits Qual
54.2 50.00 108 72-151
51.9 50.00 104 80-152
47.5 50.00 95.0 72-135
53.1 50.00 106 80-124
Report Date: 6/29/2020 Page 28 of 53
All analyses applicable to lhe CW A. SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on lhe altached COC Conlidentiol Business Information: This repon is provided for 1he C.Xdusi,·t u~e or the
~ddressee. Pri,·ile~es of sub .. seq~enl ~·~e of the ~?1:"e of this .con:ipany or any 1~mber of ils slaff, or reproduclio~ ~f this repo~ in .co~1eclionr ,,-i1h the a~vertisemenl, P~?molio.n ~r ~aJe of~!). ~rod~cl or p~oces1;, ~r in ~nn~c~ion w!lh lh~ r~-p~bl 1:::llfon er I his 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: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-003
Client Sample ID: TW4-42_06I02020
Collection Date: 6/10/2020 7 52h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1219h
6/15/2020 827h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 23.1
E353.2 0.100 3.23
Report Date: 6/29/2020 Page 9 of 53
All analyses applicable to the CW A,. SDWA0 and RCRA are performed in accordance to NELAC prolocols, Pertinent sampling information is localed on the allached COC Confidential Business information: This report is pro,•ided for the exclusi, e use of the
~ddressee Pri, ile~es o.r sub ... seq~enl ~~e or the ~?':11e or this .co~pany or any ~mbe1· of its stafT, or reproductio~ ~f 1his repo~ in fO~eclion ... with the a~vertisemenl, P~?motio.n ~r saJe of~~-~rod~ct or P~?ccss, ~r in :-°nn:c~ion w!th th~ r~-publication or this repon
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-017C
Client Sample ID: TW4-60_05272020
Collection Date: 5/27/2020 13 !0h
Received Date: 5/29/2020 I 050h
Analytical Results
Analyzed: 6/2/2020 1033h
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 < l.00
74-87-3 1.00 < l.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
50.6
48.5
48.6
50.3
50.00 101 72-151
50.00 96.9 80-152
50.00 97.1 72-135
50.00 101 80-124
Report Date: 6/12/2020 Page 39 of 48
All annl) ses applicable 1o lhe CW A. SDWA. and RCRA are perfom1ed in accordance to NE LAC prolocols_ Pertinent sampling information is located on lhe attached COC Confidential Business Information: This report is prm•ided for the crwi:clo:5:h c U:fe or the
~ctdressee Pri,•i\e~es o_f sub .. seq~enl ~~e or the ~~e of lhis .cm~pany or an~ ~mber of ils staff, or reproductio~ ~f this repo~ in .co~eclion .. "~lh lhe ~vertisement, P~?molio.n ~r sale of~!)_ ~rod~ct or p~ocesi;, ~r in ~nn~c~ion w~th th~ r1;-puhlicaiitm or this report
American West
ANAIVTICAL LAB0RATOR1f8
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2005695-017
Client Sample ID: TW4-60_05272020
Collection Date: 5/27/2020 131 Oh
Received Date: 5/29/2020 1050h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/9/2020 2301 h
6/1/2020 1444h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 6/12/2020 Page 22 of 48
All analyses applicable lo the CWA SOWA, and RCRA are perfonned in accordance to NELAC prolocols Pertinenl sampling information is localed on the allached COC, Confidential Business Information: This report is pro"ided for 1he e.~clusi, e use or the
~ddressee. Pri, ile~es orsub,_seq~ent ~~e of the ~~e of lhis .con_ipany or any ~mber ofils staff, or reproduclio,~ ~'.!his repo~ in ~o"!'eclion ... '"ill1 the a~~ertisemenl, P~?moti~n or sale of ~y ~rod~cl or P~?Cess, ~r in c::onn~c!ion w~Lh th~ r1;-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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-007C
Client Sample ID: TW4-65_06102020
Collection Date: 6/10/2020 735h
Received Date: 6/12/2020 1010h
Analytical Results
Analyzed: 6/12/2020 2213h
Units: µg/L
Extracted:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Dilution Factor:
----
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
54.4
53.6
46.8
52.I
----
50.00 109 72-151
50.00 107 80-152
50.00 93.7 72-135
50.00 104 80-124
Report Date: 6/29/2020 Page 32 of 53
All anal) ses applicable to lhe CWA. SOWA, and RCRA are performed in accordance 10 NELAC protocols Pertinenl sampling infonna1ion is located on the atlached COC Conlidential Business lnformalion: This repon is provided for the t';,(dusi\o J.Se of the
~ddressee Pri, ile~es o[ sub,,seq~ent ~~e of the ~?1:"e or this .con:ipany or any 1~mber of its slaIT, or reproductio~ ~~this repo~ in .co~ection,. wlth the a<!~·crtise~enl, P~?mofio.n ~r sale of ~!Y. ~rod~ct or P~?cess, ~r in ~nn~c!ion w!lh 1h~ r~-publicrulo11 or lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006384-007
Client Sample ID: TW4-65_06102020
Collection Date: 6/10/2020 735h
Received Date: 6/12/2020 1010h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/22/2020 1433h
6/15/2020 840h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 26.7
E353.2 0.100 6.63
Report Date: 6/29/2020 Page 13 of 53
All analyses applicable lo lhe CW A.. SOW A, and RCRA are performed in accordance to NELAC protocols, Pertinent sampling informalion is located on the all ached COC Confidential Business Jnforrnalion: This report is provided for the e.-.;clusi, e use of the
~ddressee Pri, ile~es o[ su~seq~enl ~:e of lhe ~?1;1e of this .co~pany or nn) ~mber of ils staff, or reproduclio~ ~!this repo~ in ~on~ection~ \\ilh the n~vertisemenl, P~?mo1io.n o.r sale of?'!~ ~rod~ct or p~ocess, ~r in ~onn:c~ion w!th th~ r:-p~blication of this repon
3440 South 700 West
Mt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: [phone]
!·mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-012C
Client Sample ID: TW4-70_06122020
Collection Date: 6/12/2020 625h
Received Date: 6/16/2020 I OOOh
Analytical Results
Analyzed: 6/17/2020 1156h
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 56.4
74-87-3 1.00 < 1.00
75-09-2 1.00 < l.00
Result Amount Spiked %REC Limits Qual ----
55.4 50.00 111 72-151
51.4 50.00 103 80-152
50.2 50.00 100 72-135
52.0 50.00 104 80-124
Report Date: 6/29/2020 Page 30 of 41
All analyses applicnble to the CW A. SOWA. and RCRA are performed in accordance lo NELAC protocols Pertinent sampling information is localed on lhe altached COC Confidenlial Business Tnformation; This report is provided for the e.'iclum·c l,l$e of the
~ddressee Pri, ile~es o,r sub~seq~enl ~~e of lhe ~~e of this .con:ipnny or any 1~~ber or ils staff, or reproduclio~ ~r I his repo~ in .co~eclionr wilh the a~vertise~ent, p~~motio.n ~r ~ale or ?-1!): .rrod~cl or P~?ce~s, ~r in ~nn:c~ion w!lh th~ r~-p~blic111io11 of lhis report
3440 South 700 West
:;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-012
Client Sample ID: TW4-70_06122020
Collection Date: 6/12/2020 625h
Received Date: 6/16/2020 1000h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 35 lh
6/16/2020 1254h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 39.6
E353.2 0.100 1.01 ----
Report Date: 6/29/2020 Page 17 of 41
All analyses applicable to lhe CWA, SOWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infonnation is located on the nu ached COC Conlidentiol Business Jnfonnation: This report is proYided for the exclusiYe use of the
~dressee. Pri\ i\e~es o,r subnseq~ent ~~e of the ~?1;1e of this .co~pany or any ~mber of its staff, or reproducli°!! ~f this repo~ in ~o~ection .. with the ~~·ertise~enl, p~~mo1io.n ~r sale of~~: -~rod~I or P~?Cess, ~r in ~nn~!ion w!th lh~ r~-publication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-013C
Client Sample ID: TW4-75_06I22020
ANALvr,cAL LAB0RAT0R1Es Collection Date: 6/12/2020 800h
Contact: Tanner Holliday
Received Date:
Analytical Results
6/16/2020 1000h Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 6/17/2020 1438h
Units: µg/L
Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate ----------Units: µg/L
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 10 Method:
CAS Reporting
Number Limit
67-66-3 10.0
CAS Result Amount Spiked %REC ----
17060-07-0 549 500.0 110
460-00-4 524 500.0 105
1868-53-7 498 500.0 99.5
2037-26-5 522 500.0 104
--The reporting limits were raised due lo high analyte concentrations.
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Analyzed: 6/17/2020 1217h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: I ,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 55.1 50.00 110
460-00-4 53.4 50.00 107
1868-53-7 50.5 50.00 101
2037-26-5 52.7 50.00 105
SW8260D
Analytical
Result Qual
871
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: 6/29/2020 Page 31 of 41
All analyses applicrible lo the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling informnlion is located on the allachL'<i COC. Confidential Business Information: This report is provided ror the ~du.sh c me of the
~ddressee Pri, ile~es o_f sub .. seq~ent ~~e of the ~?';le of lhis .con:ipany or M) ~mber of ilS staff. or reproductio~ ?,f this repo~ in ~on?ection .. ,,-i1h lhe .i~vertisemenl, P~?motio.n or saJe of~!!~ ~rod~cl or p1:oces';, ~r in ~nn~c!ion w~th lh~ r~-publir.ntlon or I his report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 2nd Quarter Chloroform 2020
Lab Sample ID: 2006426-013
Client Sample ID: TW4-75 _06122020
Collection Date: 6/12/2020 800h
Received Date: 6/16/2020 I OOOh
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
6/24/2020 407h
6/16/2020 1259h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 43.1
E353.2 0.100 4.19 ---
Report Date: 6/29/2020 Page I 8 of 4 I
All anal~ ses applicable lo lhe CWA. SOWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on lhe attached COC Conlidential Business lnformnlion: This report is provided for the exclusi,e use of the
~ddressee, Pri,•ile~es or sub .. seq~enl ~e or the ~~e of this .co~pany or rut) ~1!1be1 of its Slaff. or reproduclio~ ~f this repo~ in ~o~eclion .. wilh the n~vertise~ent, P~?molio.n ~r sa1e of ?1~r -~rod~cl or p1:?cess, ~r in ~nn~c!ion "'!Lh th~ r~-publicalion of Lhis report
American West ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
foll 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.
2nd Quarter Chloroform 2020
2005695-018A
Client Sample ID: Trip Blank
Collection Date: 5/27/2020
Received Date: 5/29/2020
Analytical Results
Analyzed: 6/2/2020 1012h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
845h
1050h
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 Qua!
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
SO.I 50.00
49.8 50.00
48.3 50.00
50.4 50.00
----
100 72-151
99.6 80-152
96.7 72-135
101 80-124
Report Date: 6/12/2020 Page 40 of 48
All analyses applicable lo lhe CWA, SDW A, and RCRA are perfom1ed in accordance 10 NELAC protocols Pertinent sampling information is located on the au ached COC Conlidenlia.l Business Information: This report is provided for the e."<clud\"CI use or the
~ddressee Pri, ile~es of su~eq~enl ~~ of lhe ~:u:"e of this.co"?pany or any ~'?1be, of ils staff, or reproducti~! ~f this repo~ in .co~eclion~ \\-ith the a~~er1ise1~ent, P~?moti~ ~r ~aJe of ~!Y. ~rod~cl or P~?cess, ~r in ~nn:cJi011 w!th th~ r;-publkntlon of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
2nd Quarter Chloroform 2020
2006384-020A
Client Sample ID: Trip Blank
Collection Date: 6/9/2020
Received Date: 6/12/2020
Analytical Results
Analyzed: 6/12/2020 201 lh
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
1000h
1010h
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
53.6 50.00 107 72-151
51.1 50.00 102 80-152
47.4 50.00 94.9 72-135
51.9 50.00 104 80-124
Report Date: 6/29/2020 Page 45 of 53
All an.ii~ ses applic.ible to the CWA, SOW A. and RCRA rue perfom1ed in accordance lo NE LAC protocols Pertinent sampling information is localed on the all ached COC. Confidential Business Information: This report is provided for the e"i.clusi, e use of the
~ddressee Prfrile~es o,r sub~seq~enl ~~e of the ~~e of lhis .cm~pany or any ~mber of its sla.lT, or reproduclio~ ~r I his repo~ in ~o~eclion,.. \\'ith lhe °"!~ertise~enl, P~?motio;n or sale of ~;y ~rod~L or P~?cess, ~r in ~nn~c!ion w!lh th~ r~-publicalion of this report
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
2nd Quarter Chloroform 2020
2006426-014A
Client Sample ID: Trip Blank
Collection Date: 6/12/2020
Received Date: 6/16/2020
Analytical Results
Analyzed: 6/17/2020 1237h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
625h
1000h
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 ---
54.8 50.00 110 72-151
52.7 50.00 105 80-152
49.4 50.00 98.8 72-135
51.9 50.00 104 80-124
Report Date: 6/29/2020 Page 32 of 41
All anal)ses applicable to lhe CWA, SDWA. and RCRA are perfonned in accordance 10 NELAC prolocols Pcr1inent sampling information is located on the attached COC. Confidential Business lnformalion: This repon. is proYided forllto exclusive use of1he
~ddressee. Pri,·ile~es o_f sub .. seq~enl ~~e of the ~~e of lhis .corr;ipany or fill) ~mber of ilS slaff, or reproductio.~ ~~ this repo~ in ~on?ection~ with the ~vertisemenl, p~~motio.n or saJe of :U!Y ~rod~ct or P~?ces!;, ~r in ';°nn~c!ion w~lh th~ r~~µ,ublication of lhis repon
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
American West Blanding, UT 84511
ANALYTICAL LABORATOR IES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
TEL: [phone]
RE: 2nd Quarter Chloroform 2020
Dear Tanner Holliday: Lab Set ID: 2005695
American West Analytical Laboratories received sample(s) on 5/29/2020 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 2020.06.12
12:29:22 -06'00'
Laboratory Director or designee
Report Date: 6/12/2020 Page I of 48
All anal) ses applicable lo the CW A. SOWA. and RCRA are performed in accordance to NELAC prolocols. Pertinent sampling information is located on the allached COC Confidential Business Information: This report is prm•ided ror 1h~. exclusiYe use oflhe
~ddressee Pri, ile~es o.f sub~seq~enl ~~e of lhe ~?','le of this .con:ipany or M) 1~mber of its staff, or reproduclio~ ~f this repo~ in ~on!1ection .. with the a~~·ertise~ent, P~?motio.n or sale of ~!Y ~rod~ct or p1,~ces1;, ~r in ~onn:c~ion w!th l~ rC;"publicalion of lhis repon
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANALYTICAL LABORATORlfS Project: 2nd Quarter Chloroform 2020
Lab Set ID: 2005695
Date Received: 5/29/2020 I 050h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2005695-00 IA TW4-25 05272020 5/27/2020 915h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2005695-00 I B TW4-25 05272020 5/27/2020 915h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-00IC TW4-25_05272020 5/27/2020 915h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 2005695-002A TW4-24 05272020 5/27/2020 925h Aqueous Anions, E300.0
2005695-0028 TW4-24 05272020 5/27/2020 925h Aqueous Nitrite/Nitrate (as N), E353.2 Toll Free: [phone] 2005695-002C TW4-24 05272020 5/27/2020 925h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260D/5030C
:-mail: [e-mail] 2005695-003A TW4-40 05272020 5/27/2020 1245h Aqueous Anions, E300.0
2005695-003B TW4-40 05272020 5/27/2020 1245h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-Jabs.com 2005695-003C TW4-40 05272020 5/27/2020 1245h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-004A TW4-39 05272020 5/27/2020 1002h Aqueous Anions, E300.0
Kyle F. Gross 2005695-004B TW4-39 05272020 5/27/2020 1002h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-004C TW4-39 05272020 5/27/2020 1002h Aqueous VOA by GC/MS Method Laboratory Director 8260D/5030C
2005695-005A TW4-21 05272020 5/27/2020 905h Aqueous Anions, E300.0
Jose Rocha 2005695-005B TW4-2 I 05272020 5/27/2020 905h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2005695-005C TW4-2 I 05272020 5/27/2020 905h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-006A TW4-04 05272020 5/27/2020 1222h Aqueous Anions, E300.0
2005695-006B TW4-04 05272020 5/27/2020 1222h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-006C TW4-04 05272020 5/27/2020 1222h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-007 A MW-26 05272020 5/27/2020 1010h Aqueous Anions, E300.0
2005695-007B MW-26 05272020 5/27/2020 1010h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-007C MW-26 05272020 5/27/2020 1010h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-00SA TW4-01 05272020 5/27/2020 1205h Aqueous Anions, E300.0
2005695-008B TW4-0I 05272020 5/27/2020 1205h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-00&C TW4-0I 05272020 5/27/2020 1205h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-009A TW4-41 05272020 5/27/2020 1215h Aqueous Anions, E300.0
2005695-009B TW4-41_05272020 5/27/2020 1215h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-009C TW4-41 05272020 5/27/2020 1215h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-01 OA MW-04 05272020 5/27/2020 1037h Aqueous Anions, E300.0
Report Date: 6/12/2020 Page 2 of 48
All analyses applicable to lhe CW A. SOW A. and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is located on lhe attached COC Confidential Business Information: This report is provided for lhe exclusi, e use of the
~ddressee Pri,·ile~es o_f sub,.seq~1enl ~·?e of lhe ~?-1:11e of I his 1C01~pany or nn~ 1~mbe1 of its staff, or reproductio~ ~f this repo~ in ~o~eclion,.,. ,vith the ~vertise~ent, P~?molio.n or saJe of~!)" ~rodl~Cl or p~ocess, ~r in ~nn:_c~ion w~lh lh~ r:-publication of this report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 2nd Quarter Chloroform 2020
American West Lab Set ID: 2005695
ANALYTICAL LABORATORIES Date Received: 5/29/2020 1050h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2005695-0IOB MW-04 05272020 5/27/2020 1037h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2005695-01 OC MW-04 05272020 5/27/2020 1037h Aqueous VOA by GC/MS Method
8260D/5030C
;aJt Lake City, UT 841 19 2005695-01 lA TW4-02 05272020 5/27/2020 1028h Aqueous Anions, E300.0
2005695-01 IB TW4-02 05272020 5/27/2020 1028h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-011 C TW4-02 05272020 5/27/2020 1028h Aqueous VOA by GC/MS Method
Phone: [phone]D/5030C
2005695-012A TW4-ll 05272020 5/27/2020 1020h Aqueous Anions, E300.0
Toll Free: [phone] 2005695-0 l 2B TW4-ll 05272020 5/27/2020 1020h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: (80 I) 263-8687 2005695-012C TW4-ll 05272020 5/27/2020 1020h Aqueous VOA by GC/MS Method
:-mail: [e-mail] 8260D/5030C
2005695-0BA TW4-22 05272020 5/27/2020 935h Aqueous Anions, E300.0
web: www.awal-labs.com 2005695-0 l 3B TW4-22 05272020 5/27/2020 935h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-0 l 3C TW4-22 05272020 5/27/2020 935h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-014A TW4-19_05272020 5/27/2020 845h Aqueous Anions, E300.0 Kyle F. Gross 2005695-0148 TW4-19 05272020 5/27/2020 845h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2005695-0 l 4C TW4-19_05272020 5/27/2020 845h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2005695-015A TW4-37 05272020 5/27/2020 945h Aqueous Anions, E300.0
QA Officer 2005695-0 l 5B TW4-37 05272020 5/27/2020 945h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-0 l 5C TW4-37 05272020 5/27/2020 945h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-016A TW4-20 05272020 5/27/2020 952h Aqueous Anions, E300.0
2005695-0168 TW4-20 05272020 5/27/2020 952h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-0 l 6C TW4-20 05272020 5/27/2020 952h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-017 A TW4-60 05272020 5/27/2020 1310h Aqueous Anions, E300.0
2005695-0178 TW4-60 05272020 5/27/2020 1310h Aqueous Nitrite/Nitrate (as N), E353.2
2005695-0l 7C TW4-60 05272020 5/27/2020 1310h Aqueous VOA by GC/MS Method
8260D/5030C
2005695-018A Trip Blank 5/27/2020 845h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 6/12/2020 Page 3 of 48
All analyses applicnble to lhe CWA. SOWA. and RCRA ore perfomled in RCcordance to NE LAC prolocols Pertinent sampling information is located on Lhe au ached COC Confidentinl Business Information: This report is provided for the t'.~Cl~isi,'r: u,ci of lhe
~ddressee. Pri\·ile~es o,r su~seq~ent ~~e of lhe ~~e or lhis .co1~pany or MY ,~~ber of its slali, or reproductio1~ ~f this repo~ in .con~eclion~ ,,-ith the n~venise~ent, P~?moli~n ~r ~ale of~!~: ~rodl~t or p•:~s, ~r in ';'Onni;c~ion w!lh th~ r::-publkruio11 or1his report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic 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:
2nd Quarter Chloroform 2020
2005695
5/29/2020
5/27/2020
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, 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 l 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: 6/12/2020 Page 4 of 48
All anal)ses applicnble to lhe CWA. SOWA_ and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnformalion: This report is pro"ided for the exclusive use of the
~ddressee Pri,·i\e~es o[sub~seq~enl ~~e of the ~~e of lhis .con_1pany or an)' 1~mber of its slaff, or reproductio.~ ~~this repo~ in ~o~ection~ with lhe o~'.'ertisemenl, P~?molio.n or sale of ?1!) ~rod~cl or p~~cess, ~r in ~onn~c!ion w~lh th~ r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
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:
2nd Quarter Chloroform 2020
2005695
5/29/2020
5/27/2020
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. 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, with the
following exceptions: the MS and MSD percent recoveries for Chloroform on
sample 2005695-0lOC were outside of the control limits due to sample matrix
interference.
Surrogates: All surrogate recoveries were within established limits.
Corrective Action: None required.
Report Date: 6/12/2020 Page S of 48
All anal) ses applicable lo lhe CWA. SOWA. and RCRA are performed in accordance lo NELAC prolocols Pertinent sampling information is locnted on I.he attached COC Confidential Business lnformalion: This report is provided for lhe exclusi, e use of the
~ddressee Pri,·ile~es of sub ... seq~enl ~~e of the ~~e of lhis .con:ipany or nn) ~mbe1 of ils staff, or reproductio~ ~f this repo~ in ~on~ecl1on~ "ith the n~vertisement, P~?motio.n or sale of~) ~rod~cl or p~ocess, ~r in ~nn~c!ion w~th th~ r~-p~blication of this report
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
Project: 2nd 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-Rl39685 Date Analyzed: 06/09/2020 1438h
Test Code: 300.0-W
Chloride 5.20 mg/L E300.0 0.0565 0.100 5.000 0 104
Lab Sample ID: LCS-Rl39343 Date Analyzed: 06/01/2020 1401h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.05 mg/L E353,2 0.00494 0.0100 1.000 0 105
Limits
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
-----
RPD Ref.
Amt %RPO
RPD
Limit Qual
Report Date: 6/12/2020 Page 41 of 48
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business 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 connectlon 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: 2005695
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: MB-RI39685 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-RI39343 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Tanner Holliday
Dept: WC
QC Type: MBLK
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
06/09/2020 142th
mg/L E300.0 0.0565 0.100
06/01/2020 1400h
---
mg/L E353.2 0.00494 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 6/12/2020 Page 42 of 48
analyses applicable to the CWA, SOWA, and RCRA are perfom1ed 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: 2005695
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2005695-00JAMS Date Analyzed:
Test Code: 300.0-W
Chloride 86.9
Lab Sample ID: 2005695-006AMS Date Analyzed:
Test Code: 300.0-W
Chloride 94.7
Lab Sample ID: 2005695-00IBMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.82
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
Units Method MDL Limit
06/09/2020 I 545h
mg/L E300.0 0.565 1.00 50.00
06/09/2020 1759h
mg/L E300.0 0.565 1.00 50.00
06/01/2020 1414h
mg/L E353.2 0.00494 0.0100 1.000
Tanner Holliday
WC
MS
Spike Ref.
Amount %REC
36.5 101
46.1 97.2
0.851 97.2
Limits
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 6/12/2020 Page 43 of 48
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC, Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
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:
Tanner Holliday
WC
Project: 2nd Quarter Chloroform 2020 QC Type: MSD
Analyte
Lab Sample ID: 2005695-00JAMSD
Test Code: 300.0-W
Chloride
Lab Sample ID: 2005695-006AMSD
Test Code: 300.0-W
Chloride
Lab Sample ID: 2005695-00IBMSD
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N)
Result Units Method
Date Analyzed: 06/09/2020 1602h
86.9 mg/L E300.0
Date Analyzed: 06/09/2020 1816h
95.8 mg/L E300.0
Date Analyzed: 06/01/2020 1415h
1.82 mg/L E353.2
MDL
0.565
0.565
0.00494
Reporting
Limit
1.00
1.00
0.0100
Amount Spiked Spike Ref.
Amount %REC
50.00 36.5 IOI
50.00 46.1 99.4
1.000 0.851 96.8
Limits
90 • 110
90 • 110
90 • 110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPD
86.9 0.0629 20
94.7 1.12 20
1.82 0.220 10
Qual
Report Date: 6/12/2020 Page 44 of 48
analyses applicable to the CW A, SOW A, 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 Wlll be granted only on contact. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: LCS VOC-1 060120A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 22.2
Chloroform 22.1
Chloromethane 18.3
Methylene chloride 24.2
Surr: l ,2-Dichloroethane-d4 51.8
Surr: 4-Bromofluorobenzene 49.2
Surr: Dibromofluoromethane 50.6
Surr: Toluene-d8 50.8
Lab Sample ID: LCS VOC-1 060220A Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 21.4
Chloroform 21.1
Chloromethane 16.4
Methylene chloride 22.7
Surr: l ,2-Dichloroethane-d4 50.6
Surr: 4-Bromofluorobenzene 47.4
Surr: Dibromofluoromethane 49.6
Surr: Toluene-d8 50.9
Lab Sample ID: LCS VOC-1060320A Date Analyzed:
Test Code: 8260D-W-DENLOO
Chloroform 21.3
Surr: 1,2-Dichloroethane-d4 49.6
Surr: 4-Bromotluorobenzene 51.l
Surr: Dibromofluoromethane 48.8
Surr: Toluene-d8 51.2
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
06/01/2020 1947h
-
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
06/02/2020 717h
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 l.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
06/03/2020 719h
µg/L SW8260D 0.166 1.00 20.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
µg/L SW8260D 50.00
Tanner Holliday
MSVOA
LCS
Spike Ref.
Amount %REC
0 111
0 110
0 91.7
0 121
104
98.4
101
102
0 107
0 105
0 82.0
0 113
101
94.8
99.2
102
0 106
99.3
102
97.5
102
Limits
---
66 -143
83 -119
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
66 -143
83 -l 19
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
83 -119
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt %RPO Limit Qual
Report Date: 6/12/2020 Page 45 of 48
nnlllySdi applicable to the CWA, SOWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidentia1 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 connectlon with the re-publication of this report for any purpose other than for the addressee will be b'Tanted only on contact This
American West
ANALYTICA L LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
Project: 2nd 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:
QC Type:
Tanner Holliday
MSVOA
MBLK
Reporting
Limit
Amount Spiked Spike Ref.
Method MDL Amount %REC
Lab Sample ID: MB VOC-1 06010A Date Analyzed: 06/01/2020 2007h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-1 060220A
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toi uene-d8
Lab Sample ID: MB VOC-1 060320A
Test Code: 8260D-W-DENIOO
Chloroform
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
51.5
49.6
49.0
50.9
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
51.0
48.6
48.9
49.4
Date Analyzed:
< 1.00
50.7
50.3
48.1
52.1
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
06/02/2020 737h
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
06/03/2020 739h
µg/L SW8260D 0.166
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
1.00
1.00
1.00
1.00
1.00
1.00
1.00
1.00
1.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
103
99.2
98.0
102
102
97.2
97.8
98.8
101
101
96.1
104
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPD
Limit Amt %RPO Qual
Report Date: 6/12/2020 Page 46 of 48
analyses applicable to the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infonnatlon 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 tJ-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with there-publication of this report for any purpose other than for the addressee will be granted only on contact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
Project: 2nd Quarter Chlorofonn 2020
Analyte Result
Lab Sample ID: 2005695-00JCMS Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 228
Chloroform 582
Chloromethane 159
Methylene chloride 240
Sure: l ,2-Dichloroethane-d4 492
Sure: 4-Bromofluorobenzene 488
Sure: Dibromofluoromethane 497
Sure: Toluene-d8 504
Lab Sample ID: 2005695-0lOCMS Date Analyzed:
Test Code: 8260D-W-DEN100
Chloroform 1,540
Sure: l,2-Dichloroethane-d4 1,010
Sure: 4-Bromofluorobenzene 1,030
Sure: Dibromofluoromethane 981
Sure: Toluene-d8 1,040
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
06/02/2020 93 lh
----
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
µg/L SW8260D 500.0
µg/L SW8260D 500.0
06/03/2020 840h
µg/L SW8260D 3.32 20.0 400.0
µg/L SW8260D 1,000
µg/L SW8260D 1,000
µg/L SW8260D 1,000
µg/L SW8260D 1,000
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
0 114
367 108
0 79.5
0 120
98.3
97.5
99.4
IOI
1250 74.0
101
103
98.1
104
' -Matrix spike recovery indicates matrix interference. The method is. in control as indicated by the LCS.
Limits
66 -143
83 -119
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
83 -119
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
Report Date: 6/12/2020 Page 4 7 of 48
analyses applicable to the CW A, SOW A, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infom1ation 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 tt-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be ,b'Tanted only on contact-This
American West ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2005695
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2005695-00JCMSD Date Analyzed:
Test Code: 8260D-W-DENI00
Carbon tetrachloride 211
Chloroform 546
Chloromethane 152
Methylene chloride 228
Surr: l ,2-Dichloroethane-d4 493
Surr: 4-Bromofluorobenzene 491
Surr: Dibromofluoromethane 491
Surr: Toluene-d8 505
Lab Sample ID: 2005695-0 lOCMSD Date Analyzed:
Test Code: 8260D-W-DEN100
Chloroform 1,500
Surr: 1,2-Dichloroethane-d4 1,000
Surr: 4-Bromofluorobenzene 1,010
Surr: Dibromofluoromethane 973
Surr: Toluene-d8 1,020
3440 South 700 West
Salt Lake City, UT 841 I 9
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
06/02/2020 952h
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
µg/L SW8260D 500.0
µg/L SW8260D 500.0
06/03/2020 900h
µg/L SW8260D 3.32 20.0 400.0
µg/L SW8260D 1,000
µg/L SW8260D 1,000
µg/L SW8260D 1,000
µg/L SW8260D 1,000
Tanner Holliday
MSVOA
MSD
Spike Ref.
Amount %REC
0 106
367 89.8
0 75.8
0 114
98.5
98.3
98.2
101
1250 64.7
100
101
97.3
102
' -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
66 -143
83 -119
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
83 -119
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt %RPO Limit
228 7.79 35
582 6.33 35
159 4.76 35
240 5.17 35
1540 2.45 35
Qual
Report Date: 6/12/2020 Page 48 of 48
analyses applicable to the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampfo1g information is located on the attached COC. ConfidentiaJ Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftt-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisemenL 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
American West Analytical Laboratories Rpt Emailed:
WORK ORDER Summary
Client:
Client ID:
Project:
Energy Fuels Resources, Inc.
ENE300
2nd Quarter Chloroform 2020
Contact: Tanner Holliday
QC Level: III
Work Order: 2005695
Due Date: 6/12/2020
WO Type: Project
Comments: QC 3 (no chromatograms). EDD-Denison. CC [e-mail]; Do not use "*R_" samples as MS/MSD.;
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Set Storage
2005695-00IA TW4-25_05272020 5/27/2020 0915h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-00IB N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
2005695--00lC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENIOO; # of Analytes: 41# ofSurr: 4
2005695-002A TW 4-24 _ 05272020 5/27/2020 0925h 5/29/2020 1050h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2005695-00ZB N02/N03-W-3S3.2 df-no2/no3
I SEL Analytes: N03N02N
2005695-002C 8260D-W-DEN100 VOCFridge
Test Group; 8260D-W-DENJOO; # of AnalJ,1fes: 41 # of Surr: 4
2005695-00JA TW4-40_:os212020 5/27/2020 1245h 5/29/2020 1050h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2005695-00JB N02/N03-W-3S3.2 df-no2/no3
1 SEL Analftes: N03N02N
2005695-00JC 8260DcW-DENI00 VOCFridge
Test Group: 8260D-W-DENIOO; # of Analytes: 41# o[Surr: 4
2005695-004A TW4-39_05272020 5/27/2020 1002h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-004B N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
2005695-004C 8260D-W-DENI00 VOCFridge
Test Group: 8260D-W-DEN100; /!_<JLAnalytes: 41 # of Surr: 4
2005695-005A TW4-21_0S272020 5/27/2020 0905h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-005B N02/N03-W-3S3.2 df-no2/no3
1 SEL Analytes: N03N02N
2005695-00SC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENI 00; # of Analytes: 41 # of Surr: 4
UL
Denison
Page 1 of 4
3
3
3
3
3
Printed: 05/29/20 13:38 LABORATORY CHECK: %M D RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed~----
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
2005695-006A TW4-04_05272020
2005695-006B
2005695-006C
2005695-007A l\iW-26_05272020
2005695-007B
2005695-007C
2005695-00SA TW4-01_05272020
2005695-00SB
2005695-00SC
2005695-009A TW4-4l_OS272020
2005695-009B
'2005695-009C
2005695-0lOA l\iW-04_05272020
2005695-0lOB
2005695-01 OC
2005695-0llA TW4-02_05272020
2005695-0 l lB
2005695-011 C
Work Order: 2005695
Due Date: 6/12/2020
Collected Date Received Date Test Code Matrix Set Storage
5(27/2020 1222h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
5/27/2020 1010h 5/29/2020 1050h 300.0-W Aqueous df. we
1 SEL Analytes: CL
N02/N03-W-353.2 df -no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEN 100; //_El_ Analytes: 41 # of Surr: 4
5f27f2020 1205h 5(29/2020 1050h 300.0-W Aqueous df. WC
I SEL Anaiztes: CL
N02/N03-W-353.2 df • no2/no3
I SEL 4.nalytes: N03N02N
8260D-W-DEN100 VOCFridge
·' :: .. Test Group: 8260D-W-[_)ENJOO; # of Anizly{e.s:-41.#_ of Surr: 4
5/27/2020 1215h 5(29/2020 1050h 300.0-W Aqueous df-wc
1 SEL Anal}'tes: CL
N02/N03-W-353.2 df. no2/no3
1 SEL Analytes: N03N02N
8260D-W•DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
5/27/2020 1037h 5/29/2020 1050h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df. no2/no3
I SEL Ana12tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4/# ofSurr: 4
5f27/2020 1028h 5/29/2020 1050h 300.0-W Aqueous df-wc
l SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana12tes: N03N02N
8260D-W-DEN100 VOCFridge
TestGrouE_: 8260D-W-DENJOO; # of Analytes: 41# ofSurr: 4
Page2 of4
3
3
3
3
3
3
Printed: 05/29/20 13:38 LABORATORY CHECK: %M D RT O CN O TAT O QC D LUO D HOK ___ HOK __ _ HOK___ COC Emailed. ____ _
WORK ORDER Summary Work Order: 2005695 Page3 of4
Client: Energy Fuels Resources, Inc. Due Date: 6/12/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2005695-012A TW4-11_05272020 5/27/2020 1020h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-012B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2005695-012C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Su": 4
2005695-0BA TW4-22_05272020 5/27/2020 0935h 5/29/2020 1050h 300.0-W Aqueous elf-we
I SELAnalytes: CL
2005695-0BB N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2005695-0BC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Su": 4
2005695-0I4A TW4-19_05272020 5/27/2020 0845h 5/29/2020 1050h 300.0-W Aqueous elf-we
I SEL Analytes: CL
2005695-014B N02/N03-W-353.2 df. uo2/no3
I SEL Analytes: N03N02N
:2005695-0I4C :·:...: -. 8260D-W-DEN.O.O • , VOCl:ridge 3
..: •• :,. I ( -Test-Group: 8260D-W-DENJ 00; # of Analytes: 4 / # oJSurr: 4 ._ -. \. ...
2005695-015A TW4-37_05272020 5/27/2020 0945h 5/29/2020 I050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-0ISB N02/N03-W-353.2 df. no2/uo3
I SEL Analytes: N03N02N
2005695-015C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Surr: 4
2005695-016A TW4-20_05272020 5/27/2020 0952h 5/29/2020 1050h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2005695-016B N02/N03-W-353.2 df. uo2/no3
I SEL Analytes: N03N02N
2005695-0 I 6C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 1 # ofSurr: 4
2005695-0I 7A TW 4-60 _ 05272020 5/27/2020 1310h 5/29/2020 1050h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2005695-0l 7B N02/N03-W-353.2 df-uo2/no3
I SEL Analytes: N03N02N
Printed: 05/29/20 13:38 LABORATORY CHECK: %M 0 RT 0 CNO TAT 0 aco LUOO HOK __ HOK __ HOK __ COG Emailed_
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
2005695-017C T\V4-60_05272020
2005695-0l&A Trip Blank
Work Order: 2005695
Due Date: 6/12/2020
Collected Date Received Date Test Code Matrix Sel Storage
5/27/2020 1310h S/29/2020 1050h 8260D-W-DEN100 Aqueous VOCFridge
Test Graup: 8260D-W-DENJOO; # of Ana/y!es: 41 # of_Surr: 4
5/27/2020 0845h 5/29/2020 1050h 8260D-W-DEN100 Aqueous VOCFridge
Test Group: 8260D-W-DENJ 00; # of AIIQ/ytes: 41 # of Surr: 4
Page4 of4
3
3
Printed: 05/29/20 13:38 LABORATORY CHECK: %M D RT O CN O TAT O QC O LUO 0 HOK~~ HOK~~ HOK___ COC Emailed,..._ ___ _
American West
Analytic~! Laboratories
463 W. 3600 S. Salt Lake City, lJT 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
Blanding, UT 84511
Contact: Tanner Holliday
Phone#: [phone] Cell#:
~els.com;KWeliiol@enerc:,fuel..com;
Email: tholli~&Dfilel.a.CGlll
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samole ID: Samoled
TW4-25_05272020 5/27/2020
, TW4-24_05272020 5/27/2020
1 TW4-40_05272020 5/27/2020
4 TW4-39_05272020 5/27/2020
TW4-21_05272020 5/27/2020
0 1 TW4-04_05272020 5/27/2020
MW-26_05272020 5/27/2020
8 1 TW4-01_05272020 5/27/2020
1 TW4-41_05272020 5/27/2020
~ MW-04_05272020 5/27/2020
1 TW4-02_05272020 5/27/2020
z TW4-11_05272020 5/27/2020
l TW4-22_05272020 5/27/2020
:rby: ..:Jh .. ··-fJ.../1 L 1/ Colo:
~
l [l lmt:
Prinl Name: Tu,.,.rl'.ol""-1100
Relinquished by: Date:
Slaaat.i,e
fTlme:
Print.Name:
Relinquished by: Date:
islanature
fT1me:
Prtnl Name:
Rell'""'ishedby: 0811:e:
islonature
Tlme:
PrintNlmo:
Time
Samoled
915
925
1245
1002
905
1222
1010
1205
1215
1037
1028
1020
935
Received by:
"lgnalure
PrlntName:
Rocuvtd by:
Sianatum
PrlntNamo:
l{ecelved by:
Slanalllre
Prin!Name:
Received by:
Slaoature
F>rintName:
I
CHAIN OF CUSTODY
All analy,ls wtll be conducted using NELAP accredited methods and all deta wtll be reported using AW/u:s standard analyte lists and reporting
limits (POL) untoos epedflcally n,quested oihefwioe on this Chain of custody and/or attached dorumenlation.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed reports wtll 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
o' D NLLAP ~ c::i D Non.Compliance 1;i 0 U' D Other.
!2. "' I!! )( .. 0 Cl) 0 \() C :s Cl) ~ tll i 0 C'l :a; 0 ~ Known Hazards l/) 0 " ...... ::t. • t) C. N t) & 0 E g u g tll Samole Comments * (/J
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 iW X X X
5 K'I 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:
lime:
2 (]~Cc· ?:S
AWAL Lab Sample Set #
Page 1 of 2
Due Date:
Laboratory Use Only
SamplesWere:i.J... ~5
1 e hand dollv..-od
2 AmbooolorE)
3 T~ ~·c
4 Received Brokenll-ing
(Jmprope~y Sealod0 y N
5 d[ly Prosorved y N
od .. berd>
y N
6 Received Wittlin
~111!Times N
coc Tape Was;
1 ~ on Outer Package
Y N NA
2 Gbroken on Outer Package
Y N NA
3 PrasentonSample c3 y N
4 Unbroken on Sample {: )
Y N \_NA
Discrepancies Between Semple
y N
Labels and COC Record?~
~ 1,//,,, 'LL. / Dato· :i h 51579, Z.(i
See the Analytical Scope of Work for Reponing Limits and voe
analyte list.
;,-/i,_, -~/i.s,..._~ Tme: I 051\ ,. ./ Oate:
Time:
Date:
Time:
I
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# (801) 263~686 Toll Free# (868) 26~86
_L-~ Fax# (801) 2~7 Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Tanner HoWday
Phone#: [phone] Cell#:
[e-mail]; [e-mail];
Email: th.ollidaJ(li)eerl!!!!da.com
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samole ID: Samoled
1 TW4-19_05272020 5/27/2020
, TW4-37 _0527202_0 5/27/2020
TW4-20_05272020 5/27/2020
i TW4-60_05272020 5/27/2020
TRIP BLAl'IK 5/27/2020
I
I
I
0
I
2
s
t<llllf'q.A-by: "-\A.,u,u fl /~L,y" Doto:
;-.... S,,a/2010
1111no:
,.,..Name: T11m,..HaUid,w 1100
by: Dalo:
~
mme:
~Namo:
by: 0-
lsianotLo,,
mmo:
"""'Nmno:
..... inquighod by: Oato:
IS!anoturn
Tlmo:
PrlntNilme:
I
Time
Samoled
845
945
952
1310
845
Received by:
Signature
Print Name:
CHAIN OF CUSTODY
All analysis v.11 be conducted using NELAP a<credited methods and ell dale will be reported using AWM.'s standard aRalyte llsts end reporting
!knits (POL) unless spocifocaly requested oU>erMse on !his Chaln of Cuetody and/or attached documentation
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed reports 'MN be emailed by 5:00 pm on
3 Standard U,e day they era due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
D NELAP
D RCRA
D CWA
D SOWA
D EL.AP / A2I.A
o' D NU.AP
C'i' 0 D Non-Compliance ei C CJ D Other. "1 I!! !2. .. C " )( 0 IC C: ·c: (') Jg .; ~ c::, C'l
C: ::;; ~ ~ Known Hazards 0 " .... :t. • (.) a. N t.) & 'o E g u g .. Sample Comments .. "'
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:
Time:
'.Z GO 5 G 't'S-
AWAI. Lab Sample Set#
Page 2 of 2
1·"· .... I
Laboratory Use Only
~•rrrptes Wo,,,: t /"' ;5 e.\100~,.-
2 ArrrblO(ll~ei)
3 T""1j)O<Uluro ..!...:.!?__ "C
4 Reoeived Broken/1.eakr,g
(Improperly Sealed) -.
y v
S cI:Y Preserved V N
C od at bench
y N
6 Received Within
Holding Times cJ N
COCTepeWas;.
1 ant on 01.ter Package
N NA
2~ on Otter Pod<age
Y N NA
3 Present on Sample 6 y N
4 Unbroken on Sample 6 y N
Discrepancies Between Semple
labels ;nd COC Recordd
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analyte list.
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Recetved by: I !Pate:
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Recetved by: Pate:
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Prlrt Name:
Analysis
Ammonia
COD
Cyanide
Metals
NOi/N03
O&G
Phenols
Sulfide
TKN
TP04
CrVI+
Procedure:
Frequency:
Preservation Check Sheet
s jamp le Set Ext,
Preservative I )_ J L/ .,.--& ,.J
oH<2H2S04
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pH<2H2S04
pH>9NaOH,
Zn Acetate
pH<2H2S04
oH <2 H2S04
pH>9
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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
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i/,, s ,
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2)
3)
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If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
£.
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH> __ due to the sample matrix interference .
Lab Set ID: 2 0 0-5(9 'j'S
pH Lot#: ~l 9 /
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f7'
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
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84 511
TEL: ( 435) 678-2221
RE: 2nd Quarter Chloroform 2020
Dear Tanner Holliday: Lab Set ID: 2006384
American West Analytical Laboratories received sample(s) on 6/12/2020 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,
Approved by:
J G Digitally signed 059 . by Jose G.
Rocha Rocha Date: 2020.06.29
14:31 :49 -06'00'
Laboratory Director or designee
Report Date: 6/29/2020 Page I of 53
All analyses applicable 10 the CW A. SDW A. and RCRA are perfonned in accordance 10 NELAC prolocols. Per1inenl sampling informalion is localed on the altached COC Confidenlial Business Information: This repon is pro\'ided for the exclusfre use or1he
~ddressee Pri, ile~es o.r sub ... seq~1ent ~1~e of lhe ,~~e of this .co~p:iny or an) ~mber of its staff, or reproduclio~ ~f this repo~ in ~o~ection ... \\ilh the a~"ertisement. P~?moli~n o_r sale of~!) ~rod~cl or p~ocess, ~r in ~onn~c~ion w!lh lh~ r~-p~blication of this repor\
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANALYTICAL LAOORATORI ES Project: 2nd Quarter Chloroform 2020
Lab Set ID: 2006384
Date Received: 6/12/2020 1010h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2006384-001 A TW4-03R 06092020 6/9/2020 1000h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2006384-001 B TW4-03R 06092020 6/9/2020 1000h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-001 C TW4-03R 06092020 6/9/2020 1000h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 2006384-002A TW4-03 06102020 6/10/2020 735h Aqueous Anions, E300.0
2006384-002B TW4-03 06102020 6/10/2020 735h Aqueous Nitrite/Nitrate (as N), E353.2 Toll Free: [phone] 2006384-002C TW4-03 06102020 6/10/2020 735h Aqueous VOA by GC/MS Method
Fax: [phone]D/5030C
:-mail: [e-mail] 2006384-003A TW4-42 06102020 6/10/2020 752h Aqueous Anions, E300.0
2006384-003B TW4-42 06102020 6/10/2020 752h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2006384-003C TW4-42 06102020 6/10/2020 752h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-004A TW4-28 06102020 6/10/2020 805h Aqueous Anions, E300.0
Kyle F. Gross 20063 84-004 B TW4-28 06102020 6/10/2020 805h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-004C TW4-28 06102020 6/10/2020 805h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2006384-00SA TW4-32 06102020 6/10/2020 812h Aqueous Anions, E300.0
Jose Rocha 2006384-00SB TW4-32 06102020 6/10/2020 812h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2006384-00SC TW4-32 06102020 6/10/2020 812h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-006A TW4-12 06102020 6/10/2020 821h Aqueous Anions, E300.0
2006384-006B TW4-12 06102020 6/10/2020 821h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-006C TW4-12 06102020 6/10/2020 821h Aqueous VOA by GC/MS Method
8260D/5030C
20063 84-007 A TW4-65 06102020 6/10/2020 735h Aqueous Anions, E300.0
2006384-007B TW4-65_06102020 6/10/2020 735h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-007C TW4-65 06102020 6/10/2020 735h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-008A TW4-13 06112020 6/11/2020 602h Aqueous Anions, E300.0
2006384-008B TW4-13 06112020 6/11/2020 602h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-008C TW4-13 06112020 6/11/2020 602h Aqueous VOA by GC/MS Method
8260D/5030C
20063 84-009 A TW4-36_06112020 6/11/2020 610h Aqueous Anions, E300.0
2006384-009B TW4-36 06112020 6/11/2020 610h Aqueous Nitrite/Nitrate (as N), E353.2
20063 84-009C TW4-36 06112020 6/11/2020 610h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-01 OA TW4-31 06112020 6/11/2020 620h Aqueous Anions, E300.0
Report Date: 6/29/2020 Page 2 of 53
All anal) ses applicable to lhe CWA SDW A. and RCRA nre performed in accord1U1ce lo NE LAC prolocols Pertinenl sampling informalion is located on the allached COC Confidential Business lnformalion: This report is prm•ided for the exclusirn use of the
~ddressee, Pri, ile~es o! sub,_seq~ent ~~e of the ~~1e of this.co1~pnny or nil) 1~1!1ber of its staff, or reproduclio~ ~! I his repo~ in ~o~eclion ... ,,ith the a~vertisemenl, p~omotio.n ~r ~ale of :U!). rrodl~ct or P~?cess, ~r in ~onn~c~ion w~th th~ r~-p~blication of lhis report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 2nd Quarter Chloroform 2020
American West Lab Set ID: 2006384
ANALYTICAL LAOORATORIES Date Received: 6/12/2020 1010h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2006384-0lOB TW4-3 l 06112020 6/11/2020 620h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2006384-01 oc TW4-3 l 06112020 6/11/2020 620h Aqueous VOA by GC/MS Method
8260D/5030C
:1alt Lake City, UT 841 J 9 2006384-01 lA TW4-34 06112020 6/11/2020 628h Aqueous Anions, E300.0
2006384-011 B TW4-34 06112020 6/11/2020 628h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-01 lC TW4-34 06112020 6/11/2020 628h Aqueous VOA by GC/MS Method
Phone:[phone]D/5030C
2006384-012A TW4-35 06112020 6/11/2020 636h Aqueous Anions, E300.0
Toll Free: [phone] 20063 84-0 l 2B TW4-35 06112020 6/11/2020 636h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 84-0 l 2C TW4-35 06112020 6/11/2020 636h Aqueous VOA by GC/MS Method
~-mail: [e-mail] 8260D/5030C
2006384-0BA TW4-23 06112020 6/11/2020 648h Aqueous Anions, E300.0
web: www.awal-labs.com 2006384-013 B TW4-23 06112020 6/11/2020 648h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-0BC TW4-23 06112020 6/11/2020 648h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-014A TW4-38 06112020 6/11/2020 658h Aqueous Anions, E300.0 Kyle F. Gross 2006384-0148 TW4-38 06112020 6/11/2020 658h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 20063 84-0 l 4C TW4-38 06112020 6/11/2020 658h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2006384-0lSA TW4-14 06112020 6/11/2020 708h Aqueous Anions, E300.0
QA Officer 20063 84-0 l 5B TW4-14 06112020 6/11/2020 708h Aqueous Nitrite/Nitrate (as N), E353.2
20063 84-0 l 5C TW4-14 06112020 6/11 /2020 708h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-016A TW4-06 06112020 6/11/2020 718h Aqueous Anions, E300.0
20063 84-0 l 6B TW4-06_06112020 6/11/2020 718h Aqueous Nitrite/Nitrate (as N), E353.2
20063 84-0 I 6C TW4-06_06112020 6/11/2020 718h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-017 A TW4-27 06112020 6/11/2020 729h Aqueous Anions, E300.0
2006384-017B TW4-27 06112020 6/11/2020 729h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-0l 7C TW4-27 _06112020 6/11/2020 729h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-018A TW4-05 06112020 6/11/2020 740h Aqueous Anions, E300.0
20063 84-0 l 8B TW4-05 06112020 6/11/2020 740h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-018C TW4-05 06112020 6/11/2020 740h Aqueous VOA by GC/MS Method
8260D/5030C
2006384-019A TW4-09R 06112020 6/11/2020 845h Aqueous Anions, E300.0
20063 84-0 l 9B TW4-09R_06112020 6/11/2020 845h Aqueous Nitrite/Nitrate (as N), E353.2
2006384-019C TW4-09R 06112020 6/11/2020 845h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 6/29/2020 Page 3 of 53
All analyses applicable 1o lhe CWA, SOWA, and RCRA are perfonned in accordance 10 NELAC prolocols Penineot sampling information is localed on the allached COC ConCidenlial Business lnformalion: This report is provided for the r:.~chKh'r use of the
~ddressee Pri, ile~es o,' sub~seq~ent ~~e or the ~~e of I his .con:1pany or an) ~mber of ils slaff, or reproduclio~ ~f this repo~ in ~o~ection~ \\~th the~' ertisemenl, P~?moti~ ~r sale of~!~. ~rod~ct or p~oces:;, ~r in ~nn:_c~ion w!lh th~ r:_-pu~liaulOn or this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Client:
Project:
Lab Set ID:
Energy Fuels Resources, Inc.
2nd Quarter Chloroform 2020
2006384
Date Received: 6/12/2020 1010h
Lab Sample ID Client Sample ID Date Collected
2006384-020A Trip Blank 6/9/2020 1000h
Contact: Tanner Holliday
Matrix Analysis
Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 6/29/2020 Page 4 of 53
All analyses applicable to the CWA. SDWA. and RCRA nre performed in accordance to NELAC protocols. Pertinent sampling infonnntion is localed on the allached COC Confidenlial Business lnformalioo: This report is prO\'ided for the e.xchisi\·e use of the
~ddressce Pri, ile~es o_(su~seq~enl ~~e of the ~~e of this .con_1pn.ny or any ~'!1ber of its Slaff, or reproductio.~ ~! lhis repo~ in ~~eel ion .. \\·ilh the ~~·ertisemenl, P~?mo1io.n or sale of~) ~rod~ct or p~~s. ~r in ~nn~~on w!lh th~ r~-publication of this refX)rt
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:
2nd Quarter Chloroform 2020
2006384
6/12/2020
6/9-6/11/2020
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, 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: 6/29/2020 Page 5 of 53
All analyses applicable to lhe CWA. SOWA. and RCRA me performed in accordance 10 NELAC prolocols Pertinent sampling information is localed on lhe allached COC Conndential Business Information: This report is provided ror 1hc exclusirn use of the
~ddressee Pri,·ile~es o_f sub .. seq~1enl ~1~e of the ~?1,11e of lhis .con:ipany or any ~mber of its slafT, or reprocluctio~ ~~this repo~ in ~on~ection-,,~th lhe a~~1ertise1'!1ent, P~?motio.n ~r ~ale of ~!Y. ~rod~ct or P~?Cess, ~r in ~nn~c!ion w!lh 1~ r~·IJublication of this report
American West
ANALYTICAL LABORATORltS
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
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:
2nd Quarter Chloroform 2020
2006384
6/12/2020
6/9-6/11 /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. 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: 6/29/2020 Page 6 of 53
All analyses applicable to the CWA. SOW A. and RCRA .ire performed in accordance to NELAC protocols, Per1inenl sampling informalion is located on the attached COC. Conridentinl Business Information: This report is provided for the exclusi\"e use of the
~ddressee Pri, ile~es o,rsub;eq~enl ~~e of lhe ~~e of this .co~pany or nn~· ~mber ofils slaff, or reproducli~ ~f this repo~ in ;o~eclion~ ,vith the o~~ertisement, P~?moti~ or sale of ~!Y ~rod~cl or p~ocess, ~r in ~nn:_c!io11 w!lh th~ r:-publicalion of 1his report
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd Quarter Chloroform 2020
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa": [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
Tanner Holliday
WC
Method MDL
Reporting
Limit
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS-Rl40166 Date Analyzed: 06/22/2020 1128h
Test Code: 300.0-W
Chloride 4.86 mg/L E3000 0.0565 0.100 5.000 0 97.1
Lab Sample ID: LCS-Rl39820 Date Analyzed: 06/15/2020 824h
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
RPD Ref. RPD
Limit Amt %RPD Qual
Report Date: 6/29/2020 Page 46 of 53
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: TI1is report is provided for the excllJSive use of the addressee Privileges of subsequent use oft~
11e 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 ~or any purpose other than for the addressee will be granted only on contact This
American West
A~AlYTICAl LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd Quarter Chlorofonn 2020
Analyte Result
Lab Sample ID: MB-Rl40166 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-RI39820 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
06/22/2020 1112h
mg/L E300.0 0.0565 0.100 -06/15/2020 823h
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. RPO
Amt %RPO Limit Qual
Report Date: 6/29/2020 Page 4 7 of 53
analyses applicable to the CWA. SOWA, and RCR/\ nrc perfonm:d. in accordance to NELAC protocols Pertinent sampling infonnation 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 e:onnec!tmn with the advertisement. promotion or sale of any product or process. or in connection with the re-publ;cation of this report for any purpose other than for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2006384-00JAMS Date Analyzed:
Test Code: 300.0-W -
Chloride 71.1
Lab Sample ID: 2006384-0 HAMS Date Analyzed:
Test Code: 300.0-W
Chloride 67.8
Lab Sample ID: 2006384-009BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.14
Lab Sample ID: 2006384-016BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.26
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa'C: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
06/22/2020 1235h
mg/L E300.0 0.565 1.00 50.00
06/22/2020 1523h
--
mg/L E300 0 0.565 1.00 50.00
06/15/2020 832h
mg/L E353.2 0.00494 0.0100 1.000
06/15/2020 857h
mg/L E353 2 0.00494 0.0100 1.000
Tanner Holliday
WC
MS
Spike Ref.
Amount %REC
23.1 95.9
20.9 93.8
0.0958 104
0.205 105
Limits
90 -110
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 6/29/2020 Page 48 of 53
anulyses applicahte IU the CWA, SOWA, and RCRA are performed in accordance to NE LAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tl-
ucofthis 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 wlth the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
ANALYTICAL LABORATORIES ""C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 2006384 Dept: WC
Project: 2nd Quarter Chloroform 2020 QC Type: MSD
Reporting Amount Spiked Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: 2006384-00JAMSD Date Analyzed: 06/22/2020 1252h
Test Code: 300.0-W -----
Chloride 71.2 mg/L E300.0 0.565 1.00 50.00 23.1 96.2 90 -110 71.1 0.179 20
Lab Sample ID: 2006384-01 lAMSD Date Analyzed: 06/22/2020 1540h
Test Code: 300.0-W -----
Chloride 69.1 mg/L E300.0 0.565 1.00 50.00 20.9 96.4 90 -110 67.8 1.85 20
Lab Sample ID: 2006384-009BMSD Date Analyzed: 06/15/2020 833h
Test Code: N02/N03-W-353.2 --
Nitrate/Nitrite (as N) 1.15 mg/L E353.2 0.00494 0.0100 1.000 0.0958 106 90 -110 1.14 1.31 10
Lab Sample ID: 2006384-016BMSD Date Analyzed: 06/15/2020 858h
Test Code: N02/N03-W-353.2 ------
Nitrate/Nitrite (as N) 1.23 mg/L E353.2 0.00494 0.0100 1.000 0.205 102 90 -110 1.26 2.25 10
Report Date: 6/29/2020 Page 49 of 53
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NE LAC protocols Pertinent samphng information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tl-
ne of this company or any member of its staff, or reproduction of this repmt in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd 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
_QC SUMMARY REPORT
Contact:
Dept:
Tanner Holliday
MSVOA
Method MDL
Reporting
Limit
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-1 061220B Date Analyzed: 06/12/2020 1431h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-1 061320A
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
20.5 µg/L SW8260D
20.4 µg/L SW8260D
15.6 µg/L SW8260D
20.6 µg/L SW8260D
52.2 µg/L SW8260D
52.9 µg/L SW8260D
45.3 µg/L SW8260D
53.1 µg/L SW8260D
Date Analyzed: 06/13/2020 712h
20.5 µg/L SW8260D
19.8 µg/L SW8260D
14.0 µg/L SW8260D
19.4 µg/L SW8260D
53.4 µg/L SW8260D
52.3 µg/L SW8260D
47.7 µg/L SW8260D
52.6 µg/L SW8260D
0.859 1.00 20.00 0 102
0.166 1.00 20.00 0 102
0.802 1.00 20.00 0 78.2
0.381 1.00 20.00 0 103
50.00 104
50.00 106
50.00 90.7
50.00 106
0.859 1.00 20.00 0 102
0.166 1.00 20.00 0 99.2
0.802 1.00 20.00 0 69.8
0.381 1.00 20.00 0 96.8
50.00 107
50.00 105
50.00 95.3
50.00 105
Limits
66 -143
79 -124
30 -149
65 • 154
80 • 136
85 • 121
78 • 132
81 -123
66 • 143
79 • 124
30 • 149
65 • 154
80 -136
85 • 121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 6/29/2020 Page 50 of 53
analyses applie:lble 10 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 ~,e exclusive use of the addressee Privileges of subsequent use oft~
ne of this comp:iny or uny member of its staff, or reproduction of this report in connection wlth 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: 2006384
Project: 2nd 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:
QC Type:
Tanner Holliday
MSVOA
MBLK
Reporting
Limit
Amount Spiked Spike Ref.
Method MDL Amount %REC
Lab Sample ID: MB VOC-1 0612208 Date Analyzed: 06/12/2020 1451h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-1 061320A
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
53.1
50.9
46.3
51.5
Date Analyzed:
-
< 1.00
< 1.00
< 1.00
< 1.00
53.5
52.1
46.9
51.6
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 50.00 106
µg/L SW8260D 50.00 102
µg/L SW8260D 50.00 92.7
µg/L SW8260D 50.00 103
06/13/2020 733h
-
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 50.00 107
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 93.9
µg/L SW8260D 50.00 103
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Limit Amt %RPO Qual
Report Date: 6/29/2020 Page 51 of 53
analyses applicable to the CWA, SDWA, and RCRA are perfom,ed in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftt
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 producr or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2006384-009CMS Date Analyzed:
Test Code: 82600-W-DENl 00
Carbon tetrachloride 21.4
Chloroform 20.4
Chloromethane 14.9
Methylene chloride 20.3
Surr: l ,2-Dichloroethane-d4 53.3
Surr: 4-Bromofluorobenzene 53.7
Surr: Dibromofluoromethane 46.7
Surr: Toluene-d8 53.1
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 REPORT
Contact: Tanner Holliday
Dept: MSVOA
QC Type: MS
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
06/13/2020 915h
µg/L SW8260D 0.859 1.00 20.00 0 107
µg/L SW8260D 0.166 1.00 20.00 0 102
µg/L SW8260D 0.802 1.00 20.00 0 74.4
µg/L SW8260D 0.381 1.00 20.00 0 102
µg/L SW8260D 50.00 107
µg/L SW8260D 50.00 107
µg/L SW8260D 50.00 93.4
µg/L SW8260D 50.00 106
Limits
66 -143
79 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 6/29/2020 Page 52 of 53
analyses applicable to the CWA, SOWA, and RCRA are perfonnC!d in accordance to NEL1\C protocols Pertinent samphng information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with ihe advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other th.an for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006384
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2006384-009CMSD Date Analyzed:
Test Code: 8260D-W-DENIOO -
Carbon tetrachloride 18.9
Chloroform 18.9
Chloromethane 14.2
Methylene chloride 18.6
Surr: 1,2-Dichloroethane-d4 52.2
Surr: 4-Bromofluorobenzene 52.0
Surr: Dibromofluoromethane 45.5
Surr: Toluene-d8 53.0
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
MSD
Spike Ref.
Amount %REC
06/13/2020 935h
µg/L SW8260D 0.859 1.00 20.00 0 94.4
µg/L SW8260D 0.166 1.00 20.00 0 94.7
µg/L SW8260D 0.802 1.00 20.00 0 70.9
µg/L SW8260D 0.381 1.00 20.00 0 92.8
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 91.0
µg/L SW8260D 50.00 106
Limits
66 -143
79 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit
21.4 12.2 35
20.4 7.62 35
14.9 4.96 35
20.3 9.15 35
Qual
Report Date: 6/29/2020 Page 53 of 53
analyses applicable to the CWA, SDWA, and RCRA are pcrfonnod in accordon<~ 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 tf
ne of this company or any member of its staff. or reproduction of this report in connec:mon with the advertisement. promotion or sale of any product or process. or ln connection with the re-publication of this report for any purpose other than for the addressee will be b,l'fanted only on contact This
-,,.,..· ...
American West Analytical Laboratories Rpt Emailed:
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Client ID: ENE300
Project: 2nd Quarter Chloroform 2020
Comments: QC 3 (no chromatograms). EDD-Denison.
Sample ID Client Sample ID
20063 84-00 lA 1W 4-03R_ 06092020
2006384-00lB
2006384-00lC
2006384-002A 1W 4-03 _ 06102020
2006384-002B
2006384-002C-
-2006384-00JA : • -TW4-42::_06102020 ·. . . • ... i
2006384-00JB
. 2006384-00JC
--
2006384-004A 1W4-28_06102020
2006384-004B
2006384-004C
2006384-00SA 1W4-32_06102020
2006384-00SB
2006384-00SC
Work Order: 2006384
Due Date: 6/26/2020
Contact: Tanner Holliday
QC Level: III WO Type: Project
CC [e-mail];. Do not use "*R_" samples as MS/MSD.;
Collected Date Received Date Test Code Matrix Sel Storage
6/9/2020 1000h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Ana'l_tes: N03N02N
82600-W-DENIOO VOCFridge
Test Group_: 8260D-W-DENJOO; # of Ana{ytes: 4/# of Surr: 4
6/10/2020 0735h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SEL Anal}l__tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 • VOCFridgc: . ,
Test Group: 8260D-W-DENJ 00; # of Analyres: 4 I# of Surr: 4
6/10/2020 0752h: -6/12/2020.IOIOh 300.0-W Aqueous .. .... <!fc we. · ...
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
,o•'\ Test Group_: 8260D-W-DENJ 00; # of Analytes: 4 I # of Surr: 4
6/10/2020 0805h 6/12/2020 1010h 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-DENI()_O; # of Analytes: 4 I# ofSurr: 4
6/10/2020 0812h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SEL Anal)l_tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anal:y_tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group_: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
UL
Denison
Page 1 of4
~·
•. 3 -.
3
3
3
Printed: 06/12/20 12:05 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK!.<?Y HOK~~ HOK___ coc Emailed._......1...:...........__~
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Sample ID Client Sample ID
2006384-006A T\V4-12_06102020
2006384-006B
2006384-006C
20063 84-007 A T\V 4-65 _ 06102020
2006384-007B
2006384-007C
2006384-00&A T\V4-13_06112020
2006384-00SB
2006384-00SC
., , ..... -• ~ J .
2006384-009A T\V 4-36 _ 06112020
2006384-009B
i006384-009C
2006384-0lOA T\V4-31_06112020
2006384-0IOB
2006384-0lOC
2006384-01 lA T\V4-34_06112020
2006384-0llB
2006384-0llC
Collected Date Received Date Test Code
6/10/2020 0821h 6/12/2020 1010h 300.0-W
1 SEL Analytes: CL
NOl/NOJ-W-353.2
1 SEL Ana/ytes: N03N02N
8260D-W-DEN100
Matrix
Aqueous
Work Order: 2006384
Due Date: 6/26/2020
Sel Storage
elf-we
df-no2/no3
VOCFridge
Test GrouE_: 8260D-W-DENJOO; # of Analytes: 4/#ofSu": 4
6/10/2020 0735h 6/12/2020 1010h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
N02/N03-W-353.2 elf-no2/no3
1 SEL Ana/ytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Analytes: 4/# of Su": 4
6/11/2020 0602h 6/12/2020 1010h 300.0-W Aqueous elf-we
I SEL Analj,_tes: CL
N02/N03-W-353.2 elf-no2/no3
Page 2 of 4
3
1 SELAna/ytes: N03N02N •.•...•.. ,:,,, ...
8260D-W-DEN100 VOCFridge 3
i . ·. ':• · • Tes(Gro1ijJ: 8260D-W-DENJOO; # 'of Analytes: 47-#'of Surr:'il' · · ,. · · · · ,, ··, . ' ..:--,
. -. ' . . ~-, .
6/11/2020 061 Oh 6/12/2020 1010h 300.0-W Aqueous elf-we
1 SELAnalytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL AnalJites: N03N02N
8260D-W--DEN100 VOCFridge 3
Test Group: 8260D-W-DEN J 00; # of Ana/ytes: 4 I# of Surr: 4
6/11/2020 0620h 6/12/2020 1010h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
N02/N03-W-353.2 elf-no2/no3
1 SELAnalytes: N03N02N
8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
6/11/2020 0628h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SEL Ana/ytes: CL
N02/N03-W-353.2 df-no2/no3
J SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge 3
Test GroUJ)_: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
Printed: 06/12/20 12:05 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed. ____ _
WORK ORDER Summary Work Order: 2006384
Due Date: 6/26/2020
Page3 of4
Client:
Sample ID
2006384-012A
2006384-0128
2006384-012C
2006384-0BA
2006384-0138
2006384-013C
2006384-014A
2006384-0148
2006384-014C
2006384-0lSA
2006384-0158
20063 84-0 l SC
2006384-016A
2006384-0168
2006384-016C
2006384-0l?A
2006384-0178
Printed; 06/12/20 17:52
Energy Fuels Resources, Inc.
Client Sample ID Collected Date Received Date Test Code Matrix Set Storage
TW4-35_06112020 6/11/2020 0636h 6/12/2020 1010h 300.0-W Aqueous [~J df-wc
_ 1 Sf!_~Analytes: <;!:____ _ ---·-
N02/N03-W-353.2 \v'] df -no2/no3
_______ 1S._'E_LA_n_alytes:lV03lV02lV_~------·-----· ------8260D-W-DEN100 [~ VOCFridge 3
!_est Group: ~260D-W-DENJOO: #of AnaJytes: 4 /# !!fSurr: 4
TW4-23_06112020 6/11/2020 0648h 6/12/2020 I010h 300.0-W Aqueous ~ df-wc
1 SEL Analytes_.:_<;_L
N02/N03-W-353.2 ~l df-no2/no3
I SEL A.11alyies: NOJN02N ·-----
8260D-W-DEN100 [v'] VOCFridge 3
Te!.~<z!.~!P: 8260D-W-DEN10p;_ #of A11alytes: 4 /#of Su!~: 4
TV\14-38_06112020 6/11/2020 0658h 6/12/2020 1010h 300.0-W Aqueous ~ df-wc
_l_SEL Analj!_t!_!: CL
N02/N03-W-353.2 Iv'! df-no2/no3
________ l_S_'EL_Analytes: ND_3_"!Q2_lV _____________ _
8260D-W-DEN100 ~ VOCFridge 3
Test Group: 8260D-W-DENJOO: # of Analytes: 4 I# oj!urr: 4
TW4-14_06112020 6/11/2020 0708h 6/12/2020 1010h 300.0-W Aqueous l\f] df-we
-----------·· --------------·~ ·-·-------------l SEL 11liafytes: CL ____ _
·-
TV\14-06_06112020 6/11/2020 0718h
TV\14-27 _06112020 6/11/2020 0729h
---·
N02/N03-W-353.2
____ I_ SEL Analytes: lV03N02f:!_
8260D-W-DEN100
Te_st Group: 8260D-W-DENJOO_.·_# ofAnaj;11es: 4 I# of_~lfrr: 4
6/12/2020 lOIOh 300.0-W Aqueous
_____ J__S§L Analytes: CL
N02/N03-W-353.2
---· 1 SELAnalytes: lV03'!_(_)2N
8260D-W-DEN100
\;,J df -no2/no3
-·--J,jj VOCFridge 3
Iv'] df-wc
J,iJ df-no2/no3
-----[~ VOCFridge 3
Test Group:_ 8260D-W-DENJOO; # of A'!_a_lytf!S: 4 I # ofSurr: 4
6/12/2020 101 Oh 300.0-W Aqueous l~ df-wc
__ I SEL Analytes: CL
N02/N03-W-353.2 Rl df-no2/no3
1 SE~A'!aly_tes: N03N02N
LABORATORY CHECK: %M [J RT [J CN [J TAT O QC [l LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed~----
WORK ORDER Summary Work Order: 2006384 Page4of4
Client: Energy Fuels Resources, Inc. Due Date: 6/26/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2006384-017C T\V4-27_06112020 6/11/2020 0729h 6/12/2020 I 010h 8260D-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
2006384-0lSA T\V~5_06112020 6/11/2020 0740h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
2006384-0lSB N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006384-0lSC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 /# ofSurr: 4
2006384-019A T\V 4-09R _ 06112020 6/11/2020 0845h 6/12/2020 1010h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2006384-019B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006384-019C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DEN 100; # of AJ1t1lytes: 41 # of Surr: 4
20()6384-020A Trip Blank 6/9/2020 1 OOOh · 6/12/2020 1010h 8260D-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260D-W-DENJOO; #of Analytes: 4/#ofSu": 4 .... .......
, . . . ~ .-:
I
Printed: 06/12/20 12:05 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO D HOK ___ HOK __ _ HOK___ CDC Emailed,._ ___ _
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake 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] Cell#:
Email: [e-mail]; [e-mail].
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Samoled
TW4-03R_0609202b 6/9/2020
TW4-03_06102020 6/10/2020
TW4-42_06102020 6/10/2020
TW4-28_06102020 6/10/2020
TW4-32_06102020 6/10/2020
TW4-12_06102020 6/10/2020
TW4-65_06102020 6/10/2020
TW4-13_06112020 6/11/2020
TW4-36_06112020 6/11/2020
10 > TW4-31_06112020 6/11/2020
II TW4-34_06112020 6/11/2020
I TW4-35_06112020 6/11/2020
1 TW4-23_06112020 6/11/2020 ~1
""'JnqulsMdl>'f: _\ /rd/ L_../ taltt:
Slanaturo -.n ,1/U ~-' ----8111/2020
// limo:
Pttm"'-. Tamer Hoilidav 111X
Rolinqulshad by: Date:
SiQnawra
ITTme:
PrlntName:
Relinquished by: Date:
lsiaoature
Time:
PrfntName:
R•l/nqulshedby: Date;
lsianature
rnme:
l<>.lnlName-:
Time
Samoled
1000
735
752
805
812
821
735
602
610
620
626
636
648
Rocaived by:
Slanature
Print Name:
CHAIN OF CUSTODY
All analysi& "'111 be conduded u&ing NEl.AP accredited methods and all data v.11 be reported using AWAf.'s standani analylo llsts and reporting
ttmits (POL) unl<>ss spec!flCSJly requested otherMse on this Chain of Custody and/or attached documentation.
QC Level: Turn Around Time: Unless other arrangements have been made,
signed reports will be emalled by 5:00 pm on
3 Standard tho day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field FUtered For.
For Compliance With:
D NELAP
D RCRA -D CWA
D SDWA
D ELAP/A2LA
o' D NLLAP ~ c D Non-Compliance l;i 0 u' D otl1er:
£2. "' 11 )( .. 0 a, C) \0 .~ ·c (') 1ii i 0 ""' !'l :::;; Q ~ Known Hazards C It) 0 " ...... :t. II u a. N t) & 'o E g 0 g .. Samole Comments .. (I)
5 w X X X
5 w X X X
5 w X X X
6 w X X X
6 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
Date: Special Instructions:
'llme:
-
zoo Co 3 rsc.;
AWAL Lab Sample Set#
Page 1 of 2 r ...... I
Laboratory Use Only
Samples Were:
1 Shipped haPd delivered
2 Ambient CIIIU
3 Temperatll'e f.J/ ·c
4 Received eroken/1.oaklng
(Jmproperty Sealed)
y ~
5 ~Prosarved ~ N at bench
y N
6 R9C8ived Within
6ir,gTime&
N
Kx)c Tap& Wos:
1 ~ntonOulorPaclcage
Y N NA
2dbrokon on Oulor Pad<ago
Y N NA
3 Pro&ant on Seml)le \
' ' ~ 4 Unbroken on Sample
Y N NA
Discrepancies Between Sample
y N
Lobals end COC Roa>r<l?c]
Roooivod by: Ji. ,/ -;::;.J s . ~ . 7 Olll"'G,7/.1,/L() See the Analytical Scope of Work for Reporting Limits and voe
analyte list.
Print Homo: z_ / ,.,_._v., 1-L '~, ./ Time: /()I {!
Received by: 7 I Date:
~ianature
ITime:
Prtnt Name:
Received by: Date:
SJanatura
Tlme:
PrtntName:
American West
Analytical Laboratories
463 W. 3600 S. Saltlake City, UT 84115
Phone# [phone] Toll Free# [phone] L~ Fax# (801) 263~687 Email [e-mail]
www.awal~labs.com
Client: Energy Fut.els Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Tanner Holliday
Phone#: [phone] CeU#:
Emal: [e-mail]; [e-mail]
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Sampled
1 TW4-38_06112020 6/11/2020
r TW4-l:4_06112020 6/11/2020
t TW4-06_06112020 6/11/2020
r TW4-27_06~12020 6/11/2020
I TW4-05_06112020 6/11/2020
, TW4-09R_06112020 6/11/2020
~ TRIP BLANK 6/9/2020
I
I
g
I
2
l~by: )1;A..tn ... J/t-//,L _ Date:
6111/2/l?fl
~ Tlme:
Print Name: Tannm Hollldav 1100
Rollnqulshad by: Date:
Signature
Tone:
PrinlName:
Relinquished by: Date:
SlgnatuJe
Tlme:
Print Name:
Reinqulshed by: P~te:
Sionature
Time:
Prlnt.Nama:
Time
Sampled
658
708
718
729
740
845
1000
Reooived by:
SignBlllre
Prfnt Name:
Received by:
s
PrtntName:
Received by:
s1nnmure
Prirt Name:
Received by:
SjnnAfnre
Pl'IDtName:
I
CHAIN OF CUSTODY
AJ analysts wUI be conducted using NElAP accredHed methods and all data will be reported using AWAJ...·s standard analyte lls1s end reporting
limits (POL) unless specifically requested ottte,v,;se on this Chain of Custody and/or attaclled doromentalioo.
QC Level: I Turn Around Time: Unlees other arrangements have been made,
signed reports will be emailed by 5:00 pm on
3 Standard the day !hoy en, due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAP/A2l.A
c' 0 NLLAP ~ 0 0 Non-Compliance
r,1 0 G' D Other. ('J
e! ~ .. C " X 0 \0 C: :s "' Jg .. g 0 C'l :; 0 ~ Known Hazards C: lt) 0 CD ...... ::t. • <.) ii ~ t.) & 0 E 0 a g .. Iii; Sample Comments .. V,
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:
jnme:
/
260~~
AWAL Lab Sample Set#
Page "-of 2
'Due Date: I
Laboratory Use Only
Samples Were:
1 Shipped~
2 Ambleme) ., ·Y 3 Tompon,lure ~~~-·c
4 Received Broken/Leaking
(Improperly Sealed)
y ~
6 ~PIOSMVod y N .. -y N
6 Received Within
8dlngTimes N
lcoc Tape WB5:
1 Present cm Outer Package (:j N NA
'2 (jbroken on outer Package
Y N NA
3 Present on Sample y N G
4 Unbroken on Sample (: J Y N NA
Discrepancies Between Sample
Labels and COC Raco~
y N
~ ,,uJ.. nl. ..d. Date· Cc/; _h . · ll Zil See the Analytical Scope of Work for Reporting Limits and VOC
enalyte list. LI n,,._ (f-4. ./ ,.:...__/ tTime: IJ !Cl
I Date:
Time:
Date:
Time:
Analysis
Ammonia
COD
Cyanide
Metals
N02/N03
O&G
Phenols
Sulfide
TKN
TP04
Cr VI+
Procedure:
Frequency:
Preservation Check Sheet
s amn le Set E
Preservative I ;?.. 3 C/ <:-..J
pH<2 H2S04
oH<2 H2S04
oH>12NaOH
pH<2HN03
oH<2H2S04 ~< ll« Y~ I V.:s-Jts
oH<2 HCL I
oH<2 H2S04
pH>9NaOH,
Zn Acetate
pH<2 H2S04
oH<2H2S04
pH>9
(NH4hS04
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
Co
~( ,
duH
7 2" 1
t/, ~< ,/...,-
/0 II
I/. r It{
r -,
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client ifrequested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
~
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH> __ due to the sample matrix interference .
Lab Set ID: z.. 0 0 CJ 3. 'fr'-/
pH Lot #: U 2. '=t'f
/2... 0 I lf /S I~ 17 ('if' ,,
\t ( 1L, Jtr 1£, ~s IL 1/..._ >t
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
Ta1U1er Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 2nd Quarter Chloroform 2020
Dear Ta1U1er Holliday: Lab Set ID: 2006426
American West Analytical Laboratories received sample(s) on 6/16/2020 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:
J G Digitally signed 058 . by Jose G.
Rocha Rocha Date: 2020.06.29
14:29:33 -06'00'
Laboratory Director or designee
Report Date: 6/29/2020 Page I of 41
All analyses applicable to the CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Pertinenl sampling information is located on the allached COC Confidential Business lnformalion: This report is prm·ided for 1he exclusi, e use of lhe
~ddressee Pri, ile~es o}' sub .. seq~enl ~~e of the ~?'?e of this .con:1pany or nny "2:mber of its slafT. or reproduclio~ ~~this repo~ in .co~eclion~ ,\ith lhe o~~ertisemenl. P~?molio.n or sale of ?-1!~ ~rodl~Cl or P~?Cess, ~r in ~onn:c~ion w~lh th~ n;:·publicnlion of this repor\
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANALYTICAL LABORATORl[S Project: 2nd Quarter Chloroform 2020
Lab Set ID: 2006426
Date Received: 6/16/2020 1 OOOh
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West 2006426-001 A MW-32 06122020 6/12/2020 1140h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2006426-001B MW-32 06122020 6/12/2020 1140h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-001 C MW-32_06122020 6/12/2020 1140h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 2006426-002A TW4-09 06122020 6/12/2020 625h Aqueous Anions, E300.0
2006426-002B TW4-09 06122020 6/12/2020 625h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 2006426-002C TW4-09 06122020 6/12/2020 625h Aqueous VOA by GC/MS Method
Fax:[phone]D/5030C
:-mail: [e-mail] 2006426-00JA TW4-30 06122020 6/12/2020 648h Aqueous Anions, E300.0
2006426-00JB TW4-30 06122020 6/12/2020 648h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2006426-00JC TW4-30 06122020 6/12/2020 648h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-004A TW4-08 06122020 6/12/2020 658h Aqueous Anions, E300.0
Kyle F. Gross 2006426-0048 TW4-08 06122020 6/12/2020 658h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-004C TW4-08 06122020 6/12/2020 658h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2006426-00SA TW4-18 06122020 6/12/2020 710h Aqueous Anions, E300.0
Jose Rocha 2006426-00SB TW4-18 06122020 6/12/2020 710h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2006426-00SC TW4-18 06122020 6/12/2020 710h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-006A TW4-33 06122020 6/12/2020 724h Aqueous Anions, E300.0
2006426-0068 TW4-33 06122020 6/12/2020 724h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-006C TW4-33 06122020 6/12/2020 724h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-007 A TW4-16 06122020 6/12/2020 735h Aqueous Anions, E300.0
2006426-0078 TW4-16_06122020 6/12/2020 735h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-007C TW4-16_06122020 6/12/2020 735h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-008A TW4-29 06122020 6/12/2020 746h Aqueous Anions, E300.0
2006426-0088 TW4-29 06122020 6/12/2020 746h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-008C TW4-29 _06122020 6/12/2020 746h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-009A TW4-07_06122020 6/12/2020 800h Aqueous Anions, E300.0
2006426-0098 TW4-07 06122020 6/12/2020 800h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-009C TW4-07 06122020 6/12/2020 800h Aqueous VOA by GC/MS Method
8260D/5030C
2006426-01 OA TW4-10_06122020 6/12/2020 812h Aqueous Anions, E300.0
Report Date: 6/29/2020 Page 2 of 41
All anal) ses applicable to the CW A. SOWA. and RCRA are perfonned in accordance to NELAC prolocols Pertinenl sampling information is located on 1he au ached COC Confidenlial Business Cnformation: This report is pro,·ided for the exclusi\"e use of the
~ddressee Pri, ile~es or su~seq~enl ~?e of the ~~e of I his .co~pany or any ~mbe1 of iLs staff; or reproduclio!~ ~f this repo~ in ~on~ection~ ,\ith the ~~·ertisement, P~?motio.n ~r sale or~!) ~rod~cl or pi:ocess, ~r in ~onn~c~ion w!lh 1h~ r1;-publication or lhis report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 2nd Quarter Chloroform 2020
Lab Set ID: 2006426
ANAi YTICAL LABORATOR IES Date Received: 6/16/2020 1000h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2006426-01 OB TW4-I0 06122020 6/12/2020 812h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2006426-0 J oc TW4-10 06122020 6/12/2020 812h Aqueous VOA by GC/MS Method
8260D/5030C
;alt Lake City, UT 84119 2006426-01 lA TW4-26 06122020 6/12/2020 823h Aqueous Anions, E300.0
2006426-0 l lB TW4-26 06122020 6/12/2020 823h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-01 lC TW4-26 06122020 6/12/2020 823h Aqueous VOA by GC/MS Method
Phone:[phone]D/5030C
2006426-012A TW4-70 06122020 6/12/2020 625h Aqueous Anions, E300.0
Toll Free: [phone] 2006426-012B TW4-70 06122020 6/12/2020 625h Aqueous Nitrite/Nitrate (as N), E353.2
Fax:[phone] 2006426-012C TW4-70 06122020 6/12/2020 625h Aqueous VOA by GC/MS Method
:-mail: [e-mail] 8260D/5030C
2006426-013A TW4-75 06122020 6/12/2020 800h Aqueous Anions, E300.0
web: www.awal-labs.com 2006426-0BB TW4-75 06122020 6/12/2020 800h Aqueous Nitrite/Nitrate (as N), E353.2
2006426-013C TW4-75 06122020 6/12/2020 800h Aqueous VOA by GC/MS Method
8260D/5030C
Kyle F. Gross 2006426-0!4A Trip Blank 6/12/2020 625h Aqueous VOA by GC/MS Method
8260D/5030C
Laboratory Director 2006426-015A Post DI 6/12/2020 915h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha
QA Officer
Report Date: 6/29/2020 Page 3 of 41
All analyses applicable to lhe CW A. SOWA, and RCRA are perfom1ed in accordance to NELAC prolocols Pertinent sampling information is located on the allached COC Confidential Business lnformalion: This report is pr°''ided for the exclusi, e use of the
~ddressee Pri\'ile~es o.r sub .. seq~ent ~~e of the ~~e of this .con_ipcmy or anr ~i:ibe1 or its staff. or reproductio~ ~f this repo~ in .co~echon~ with the ~~·ertisement, P~?moti~n ~r ~ale of ?1!r -~rod~ct or P~?cess, ~r in :°nn:c~ion w~th 1h~ r~-publicalion of this report
3440 South 700 West
;alt Lake City, UT 84 I I 9
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web : www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
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:
2nd Quarter Chloroform 2020
2006426
6/16/2020
6/12/2020
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: 6/29/2020 Page 4 of 41
All annlrses applicable to the CWA. SOWA, and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is located on the attached COC. Conlidenti::il Business lnformal1on: This report is provided for the exclusi, e use of1he
~dressee Pri,·ile~es o.r su~seq~1ent ~,~e or the ~~e or lhis .co~pany or any ~mbe1 of its staff, or reproduclio~ ~! this repo~ in .con~echon .. with the ~vertise~enl, P~?moLio.n or saJe of ?1!Y rrod~ct or p1:ocess, ~r in ~onn!c~ion w!lh th~ r~-p~blication of Lhis report
American West
ANAIVTICAL LABORATOR IES
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
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, lnc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
2nd Quarter Chloroform 2020
2006426
6/16/2020
6/12/2020
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. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPO, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicate (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, with the
following exceptions: the MS and MSD percent recoveries for Chloroform on
sample 2006426-003C were outside of the control limits due to sample matrix
interference.
Surrogates: All surrogate recoveries were within established limits.
Corrective Action: None required.
Report Date: 6/29/2020 Page 5 of 41
All anal)ses applic.tble to 1he CWA, SDWA and RCRA are perfomled in accordance to NELAC protocols Per1inent sampling informal ion is located on the all ached COC Confidential Business Information: This report is pro\'ided for lhe exclusi, e use of the
~ddressee Pri, ile~es o.r su~seq~ent ~~e of the ~~e of lhis .co1~pany or an)' ~mber of its Slaff, or reproduclio~ ~f this repo~ in ~o~ection~ \\ilh the ~vertisemenl, P~?moti°:" or sale of ?1!~ ~rod~\ or p~ocess, ~r in ~nn~c!ion ,,·!th th~ r~~p~blication of I.his report
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd 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-R140197 Date Analyzed: 06/23/2020 2249h
Test Code: 300.0-W
Chloride 4.99 mg/L E300.0 0.0565 0.100 5.000 0 99.7
Lab Sample ID: LCS-Rl39881 Date Analyzed: 06/16/2020 1115h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.07 mg/L E353.2 0.00494 0.0100 1.000 0 107
Limits
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Limit Amt %RPO Qual
-------~-----
Report Date: 6/29/2020 Page 34 of 41
analyses applicable to the CWA. SDWA, and RCRA rue pcrformc-d in accordnncc to NELAC pn:11ocols 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 1his report in connec.tion wnh rh~ 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
ANALYTIC.Al
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: MB-RI40197 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-RI39881 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
06/23/2020 2232h
mg/L E300.0 0.0565 0.100
06/16/2020 1114h
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
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 6/29/2020 Page 35 of 41
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. ConfidentiaJ 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 stafl or reproduction of this report in connection with the advertisement, promotion or sale of any product or process, or ln connection with the re-publication of this repon for any purpose other than for the addressee will be granted only on contact. This
American West
ANALYTICAL LABORATORIES
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
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Dept: WC Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte Result Units Method
Lab Sample ID: 2006426-002AMS Date Analyzed: 06/23/2020 2339h
Test Code: 300.0-W
Chloride 87.9 mg/L E300.0
Lab Sample ID: 2006426-00SAMS Date Analyzed: 06/24/2020 210h
Test Code: 300.0-W
Chloride 90.8 mg/L E300.0
Lab Sample ID: 2006426-00IBMS Date Analyzed: 06/16/2020 1235h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.960 mg/L E353.2
MDL
0.565
0.565
0.00494
Reporting
Limit
1.00
1.00
0.0100
QCType: MS
Amount Spiked Spike Ref.
Amount %REC
50.00 39.5 96.9
50.00 41.4 98.9
1.000 0.0539 90.6
Limits
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 6/29/2020 Page 36 of 41
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 oftf
ne of this company or any member of \ts staff7 or reproduction of thjs report in connection with the advertisement; promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample JD: 2006426-002AMSD Date Analyzed:
Test Code: 300.0-W
Chloride 87.5
Lab Sample ID: 2006426-00SAMSD Date Analyzed:
Test Code: 300.0-W
Chloride 90.0
Lab Sample ID: 2006426-00IBMSD Date Analyzed:
Test Code: N02/N03-W-353.2 --
Nitrate/Nitrite (as N) 0.959
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
Dept: WC
QCType: MSD
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
06/23/2020 2356h
mg/L E300,0 0.565 1.00 50.00 39.5 96.0
06/24/2020 227h
mg/L E300.0 0.565 1.00 50.00 41.4 97.3
06/16/2020 1236h
mg/L E353.2 0.00494 0.0100 1.000 0.0539 90.5
Limits
90 -110
90 -110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPO
Amt %RPO Limit
87.9 0.506 20
90.8 0.856 20
0.96 0.0417 10
Qual
Report Date: 6/29/2020 Page 37 of 41
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 tl-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotlon 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 win be granted only on contact This
LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd 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
MSVOA
Method MDL
Reporting
Limit
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-1 061620A Date Analyzed: 06/16/2020 728h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-1 061720A
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
16.9 µg/L SW8260D
18.2 µg/L SW8260D
15.0 µg/L SW8260D
19.4 µg/L SW8260D
52.1 µg/L SW8260D
51.0 µg/L SW8260D
46.7 µg/L SW8260D
52.4 µg/L SW8260D
Date Analyzed: 06/17/2020 734h
18.2 µg/L SW8260D
18.9 µg/L SW8260D
16.3 µg/L SW8260D
21.7 µg/L SW8260D
54.1 µg/L SW8260D
53.3 µg/L SW8260D
52.9 µg/L SW8260D
53.5 µg/L SW8260D
0.859 1.00 20.00 0 84.6
0.166 1.00 20.00 0 90.8
0.802 1.00 20.00 0 75 .0
0.381 1.00 20.00 0 96.9
50.00 104
50.00 102
50.00 93.3
50.00 105
0.859 1.00 20.00 0 91.2
0.166 1.00 20.00 0 94.4
0.802 1.00 20.00 0 81.4
0.381 1.00 20.00 0 108
50.00 108
50.00 107
50.00 106
50.00 107
Limits
66 -143
79 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
66 -143
79 -124
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 6/29/2020 Page 38 of 41
analyses applicable to the CWA. SOWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Bus;ness 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 thls report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], fa,c [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact:
Dept:
QC Type:
Tanner Holliday
MSVOA
MBLK
Reporting
Limit
Amount Spiked Spike Ref.
Method MDL Amount %REC
Lab Sample ID: MB VOC-1 061620A Date Analyzed: 06/16/2020 837h
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 061720A
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
53.5
53.2
49.0
53.1
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
55.1
50.7
51.5
51.9
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 50.00 107
µg/L SW8260D 50.00 106
µg/L SW8260D 50.00 98.0
µg/L SW8260D 50.00 106
06/17/2020 754h
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 50.00 110
µg/L SW8260D 50.00 IOI
µg/L SW8260D 50.00 103
µg/L SW8260D 50.00 104
Limits
80 -136
85 -121
78 -132
81 -123
80-136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 6/29/2020 Page 39 of 41
analyses applicable to the CWA. SOWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Jnfmmation: 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 reppublication of this repon for any purpose other than for the addressee will be granted only on contacL This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte Result
Lab Sample ID: 2006426-003CMS Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 26.4
Chloroform 90.8
Chloromethane 22.3
Methylene chloride 25.1
Surr: l ,2-Dichloroethane-d4 53.6
Surr: 4-Bromofluorobenzene 52.1
Surr: Dibromofluoromethane 48.1
Surr: Toluene-d8 53.2
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
MS
Spike Ref.
Amount %REC
06/17/2020 955h
-
µg/L SW8260D 0.859 1.00 20.00 0 132
µg/L SW8260D 0.166 1.00 20.00 65.4 127
µg/L SW8260D 0.802 1.00 20.00 0 111
µg/L SW8260D 0.381 1.00 20.00 0 126
µg/L SW8260D 50.00 107
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 96.2
µg/L SW8260D 50.00 106
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
66 -143
79 -124
30 -149
65 -154
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: 6/29/2020 Page 40 of 41
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 Informal ion: This report is provided for the exclusive use of tl1e 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 ln connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2006426
Project: 2nd Quarter Chloroform 2020
Analyte
Lab Sample ID: 2006426-00JCMSD
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Result
Date Analyzed:
24.1
90.6
20.2
22.9
54.5
51.2
49.8
53. I
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
MSD
Spike Ref.
Amount %REC
06/17/2020 1015h
--
µg/L SW8260D 0.859 1.00 20.00 0 120
µg/L SW8260D 0.166 1.00 20.00 65.4 126
µg/L SW8260D 0.802 1.00 20.00 0 IOI
µg/L SW8260D 0.381 1.00 20.00 0 115
µg/L SW8260D 50.00 109
µg/L SW8260D 50.00 102
µg/L SW8260D 50.00 99.6
µg/L SW8260D 50.00 106
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
66 -143
79 -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
26.4 9.15 35
90.8 0.254 35
22.3 9.50 35
25.1 9.28 35
Qual
Report Date: 6/29/2020 Page 41 of 41
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 oftt-
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
·i.•
American West Analytical Laboratories Rpt Emailed:
WORK ORDER Summary Work Order: 2006426
Due Date: 6/30/2020 Client: Energy Fuels Resources, Inc.
Client ID: ENE300 Contact: Tanner Holliday
Project: 2nd Quarter Chloroform 2020 QC Level: III WO Type: Project
Comments: QC 3 (no chromatograms). EDD-Denison. CC [e-mail]; Do not use "*R_" samples as MS/MSD.; -t
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Set Storage
2006426-00lA MW-32_06122020 6/12/2020 1140h 6/16/2020 1000h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2006426-00lB N02/NOJ.W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2006426-00 IC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; # of Ana/ytes: 4/# ofSurr: 4
2006426-002A TW 4-09 _ 06122020 6/12/2020 0625h 6/16/2020 1000h 300.0-W Aqueous df-wc
I SEL Ana!y_tes: CL
2006426-002B N02/N03-W-353.2 df-nq2/no3
1 SELAna[ytes: N03N02N
2006426-002C .. ··;:• 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DE1!_I 00; # ofA111:!_/y_les: 4 I# of Surr: 4 -·· . ··-
2006426•003A .. TW4-30_'.06122020 ,. ·· 6/12/2020 0648h . . 6/16/2020 rDOOh 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2006426.-00JB N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2006426-00JC 8260DsW-DEN100 VOCFridge
Test Group: 8260D-W~DENI 00; # of Analj,tes: 4 I# ofSurr: 4
2006426-004A TW4-08_06122020 6/12/2020 0658h 6/16/2020 1000h 300.0-W Aqueous df-wc
1 SELAnaly!es: CL
2006426-004B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006426-004C 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJ 00; /j__<)f Ana/ytes: 4 I #_E[Surr: 4
2006426-00SA TW4-I8_06l22020 6/12/2020 0710h 6/16/2020 IOOOh 300.0-W Aqueous df ·wc
I SEL Analytes: CL
2006426-00SB N02/N03-W-353.2 df-no2/no3
I SELAnalj_tes: N03N02N
2006426-00SC 8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DEl!_I00; # of Analytes: 4 I# of Surr: 4
UL
Denison
Page I of3
3
!··
3
3
Printed: 06/16/20 11:33 LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK~~-HOK~~-HOK__ COC Emailed Q: 114!(2--({l...C ,.J'
WORK ORDER Summary Work Order: 2006426 Page2 of3
Client: Energy Fuels Resources, Inc. Due Date: 6/30/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Set Storage
2006426-006A 1W4-33_06122020 6/12/2020 0724h 6/16/2020 1000h 300.0-W Aqueous elf-we
I SEL Analytes: CL
2006426-006B N02/N03-W-353.2 elf-no2/no3
I SELAnalytes: N03N02N
2006426-006C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# ofSurr: 4
2006426-007 A 1W4-16_06122020 6/12/2020 0735h 6/16/2020 IOOOh 300.0-W Aqueous df-we
I SEL Analytes: CL
2006426-007B N02/N03-W -353.2 elf-no2/no3
I SEL Analytes: N03N02N
2006426-007C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI00; # of Analytes: 4/#ofSurr: 4
2006426-00SA 1W4-29_06122020 6/12/2020 0746h 6/16/2020 1000h 300.0-W Aqueous elf-we
I SEL Analytes: CL
2006426-00SB N02/N03-W-353.2 df-no2/no3
1 SEL A11alytes: N03N02N
2006426-00SC 8260D-W-DEN100 VOCFridge 3
-. ... Test Group: 8260D-W-DENJOO; #..ofAnalytes;.4/ # ofSw:r; ti. ....... r-_ • ..:..,, • ,._. ·-· :·•
2006426-009A 1W4--07_06122020 6/12/2020 0800h 6/16/2020 IOOOh 300.0-W Aqueous df-we
1 SEL Ana/ytes: CL
2006426-009B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2006426-009C .. ,,· & •• 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI00; # of Analytes: 4/# of Su": 4
2006426-0 l OA 1W4-10_06122020 6/12/2020 0812h 6/16/2020 1000h 300.0-W Aqueous df-we
I SEL Analytes: CL
2006426-0lOB N02/N03-W-353.2 elf-no2/no3
I SEL Analytes: N03N02N
2006426-0 lOC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Ana/ytes: 41 # of Surr: 4
2006426-0llA 1W4-26_06122020 6/12/2020 0823h 6/16/2020 1000h 300.0-W Aqueous elf-we
I SELAnalytes: CL
2006426-0llB N02/NOJ..W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006426-01 lC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI00; # of Ana/ytes: 4/# ofSurr: 4
Printed: 06/16/20 11:33 LABORATORY CHECK: %M D RT D CNO TAT D aco LUDO HOK __ HOK __ HOK __ COG Emailed
WORK ORDER Summary Work Order: 2006426 Page 3 of3
Client: Energy Fuels Resources, Inc. Due Date: 6/30/2020
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2006426-012A T\V4-70_06122020 6/12/2020 0625h 6/16/2020 1000h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2006426-0l2B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006426-012C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 /# o/Surr: 4
2006426-0BA T\\'4-75_06122020 6/12/2020 0800h 6/16/2020 1000h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2006426-0 l3B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2006426-0BC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI 00; # of Analytes: 41 # of Surr: 4
2006426-014A Trip Blank 6/12/2020 0625h 6/16/2020 1000h 8260D-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 41 # of Su": 4
2006426-0lSA ··Post DI :·v·. :•; . 6/12/2020 091 Sh 6/16/2020 iOOOh 8260D-W~DEN100 Aqueous VOCFridge 3
Test Group: 8260D-W-DEN I 00; # of Analytes: 41 # of Surr: 4 -. ·~~ -.
-r , I • • • .._,, •.-J ' :..:,..;..
.. ~· ...
Printed: 06/16/20 11:33 LABORATORY CHECK: %M O RT D 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] ~ Fax# (801) 263~687 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] Cell#:
Email: [e-mail]; thollidaY@eDer&Yfuels.com
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samole ID: Samoled
JrlW-32_06122020 6/12/2020
TW4-09_06122020 6/12/2020
1 TW4-30_06122020 6/12/2020
4 TW4-08_06122020 6/12/2020
, TW4-18_06122020 6/12/2020
1 TW4-33_06122020 6/12/2020
TW4-16_06122020 6/12/2020
8 1 TW4-29_06122020 6/12/2020
g 1 TW4-07_06122020 6/12/2020
l TW4-10_06122020 6/12/2020
I TW4-26_06122020 6/12/2020
! TW4-70_06122020 6/12/2020
3 TW4-75_06122020 6/12/2020
F<elinqUlMod by: ..:::J ~ //,./.. ~ DIIIO: --/j~"'-,·, 811
V Timo:
"""'Namor: TOIUl&rHolM<rv 11°'
Sellnqulshed by: 10ate:
lslnnAture
tTime:
PrintNeme:
Relinquished by: Date:
Sloos\ure
mme:
Prlnt.Narna.:
Relinquished by: Date:
'"''"aal!JJ8 mme:
Print Name:
I
Time
Samoled
1140
625
648
658
710
724
735
746
800
812
823
625
800
Received by:
Print Name:
CHAIN OF CUSTODY
All analysls will be conducted using NELAP acaadited methods and all data will be reported using AWAL's standard anelyte llsls and reporting
limits (PQL) unless speclflcally requested otherwise on thls Chain of Custody and/or attached documentation.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed r&pc,rts will be emelled by 5:00 pm on
3 Standard the day they are due..
X Include EDD:
LOCUS UPLOAD
EXCEL
Field FIitered For:
For Compliance With:
D NELAP
0 RCRA
0 CWA
0 SDWA
D ELAP/A2LA
o' D NLLAP
~ D Non-Compliance c:i f;i c:, D' D Other: "1 t!! ~ ... .. >< C) f5 C ·c t'> ·;;; ai 0 c:, ~ i: :::; c:, Known Hazards I!: lJ) 0 Q) ...... :?. .. () C. N t.) & 'o E 0 t) g ., Sample Comments .. IJ) I!:
5 w X X X
5 w X X X
5 w X X X
s w X X X
s 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
s w X X X
s w X X X
Oete: Special Instructions:
Time: ,
A 6 (.\(c, l( z. (o
AWAL Lab Sample Set#
Page 1 of 2
r•DM,c I
Laboratory Use Only
S!m,pjeo Wore: l{ pS
,eochonddtllvorod 2 Amblon!-6 •
3 Tomporature ~ ·c
4 Received Broken/leaking
C){r:::JN~C ) tr,,.,r..._
5 Propony Prosoovod
~ecked ·at bench N
y N
6 Received Within
GdingTimes
N
COC Tepe Wes:
1 Prt on Outer Package
(' N NA
2 Unbroken on Outer Pac*age <:_! N NA
3 Present on Sample
y N (5
4 Unbroken on Sample E\ y N
Dfsatipancie& Between Sample
Labels ;nd COC Recordc)
Rocoiv~~f 10..:..;.im, 1 8·1. _J L. '/ D/Jt•ea h UJ lu1 See the Analytical Scope of Work for Reporting Limits and VOC
Pru,I NBm<>: ~·/11.. '.J, . . ,._ _/
analyte list.
Time: If. or\
!Received by: I Date:
lsicneture
mme:
PrtntName:
Received by: Date:
Signature
Time:
Pm Name;
8
10 I
I 11
12 !
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Toll Free# {888) 263-8686
~ 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] Cell#:
Email: [e-mail]; thollida:,@eDer&Yfuels.com
Project Name: 2nd Quarter Chloroform 2020
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Samole ID: Samoled
TRIP BLANK 6/12/2020
Post DI 6/12/2020
13 I TW4-75_06122020
l~=by. -.:::::)h~.IAw" . )h///! --~ Cato:
1111= .,. Tlme:
::,..rntNamc: Tamar Hollfd,.,.., 11"'
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I"""'"'""'
Time:
PmlNnmo:
Rtllnq,.;6"odt,y. !)ala;
1., ....... _.
Time:
Print Name:
Rollncµsl!ed bi: Date:
l"'"""'uro
1nme:
IPrintName:
I
.
Time
Samcled
625
915
Received by:
Sl<,nature
Print Name:
CHAIN OF CUSTODY
All analysis will be conducted using NELAP accredited methods and all data wlll be reported using AWAL1s standard analyte lists end reporting
limits (PQL) unless speclncally reQU86'ted otherwise on this Chain of Custody and/or attached documentation.
QC Level: I Tum Around Time: Unless other arrangements have beer, made,
signed reports wlU 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 SDWA
0 ELAP/A2LA
c' D NLLAP
~ ci D Non-Compliance ~ c:, D' 0 Other: "l I!! ~ .. c:, CD )( 0 IC .s :s I') c:, C"l . .!!! 111 0 :;; c:, ~ Known Hazards C: I;!: l/) 0 a, .... :t. .. u C. C'I C) & 'o E 0 t) g 111 Samole Comments .. Cl) I;!:
3 w X
5 w X
Oale: Special Instructions:
Tirne:
I
;z.cC! Ccl/2ee
AWAL Lab Sample Set#
Page 2 of 2 r ...... I
Laboratory Use Only
S.mp'nw .... (ln
, ~ hand dotivonid
2 Ambionlat~
3 Tomporoturo ~ -C
4 Received Broken/Leaking m-) C:) ;,/ i ' .,. ~· ... I F'Q_ L,
s Prooorved ~ ~;;; ~ N 'Vu,
edotbondl
y N
6 Received Within
Holding Tlm8S
~ N
COC Tape Was:
1 Pr988ffl on Outer Package
() N NA
2 ~broken on Outer Pack-C N NA
3 Present on Sample y N e
4 Unbroken on Sample f.
y N NAJ
lni.nepandes -Sample
Labels and CDC Record?
y (J
~~1 SloNJI " _//l -r:;l.k.,, ~ 0Z j/(r, h..,11 See the Analytical Scope of Work for Reporting Limits and VOC
?riliName; ·s lb +R.. / Tme' /~ UG analyte list.
Received by: I , Date:
Slonature
rnme:
PrtntNeme:
Received by: Date:
Slqnature
11me:
Prird.Nama.'.
Analysis
Ammonia
COD
Cyanide
Metals
NOz/N03
O&G
Phenols
Sulfide
TKN
TP04
Cr VI+
Procedure:
Frequency:
Preservation Check Sheet
s amn le Set E
Preservative J J.... .~ l/ 'j
pH<2 H2S04
pH<2H2S04
oH>12NaOH
pH<2HN03
0H<2H2S04 v., II .• is 1/,~ v:.
pH<2HCL r / r /
oH<2 H2S04
pH>9NaOH,
Zn Acetate
pH<2 H2S04
pH<2H2S04
pH>9
(NH4)2S04
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
&
i/~
duB
Q &--q
IL ,f_.,s 1,l,
/0 II
1/., ,/.c
/' "'
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+ ..
#
•
The sample required additional preservative upon receipt
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH> __ due to the sample matrix interference .
/2...
72c
'
Lab Set ID:
pH Lot#:
/ 2,
~r
~ (10 c;; {.~
{i~
Tab I
Quality Assurance and Data Validation Tables
1-1 : Field ONQC Evaluatio
1x Casing 2x Casing Dissolved
Location Volume Volume Pumped Volume Volume Check Conductivity RPO PH RPO Temperature RPO Redox RPO Turbidity RPO Oxygen RPO
MW-04 NA Continuously Pumped well --1877 NC 7.35 NC 15.70 NC 338 NC 0 NC 40.3 NC
TW4-01 NA Continueuslv Pumped well --2306 NC 7.38 NC 17.80 NC 370 NC 0 NC 71 .0 !';JC
TWH>2 NA Centlnueusly Pumpe.d well -· 3728 NC 7.26 NG 16.80 NC 327 NC 0 NC 80.0 NC
:'.I\YY~-. -~,.·---c..· -.. mfl.Q.0::---foo:36 _ li JPl:lfflgW:1::uv, ~1817" b_ 1820 oi;16 . 6.00 I, •• _ M~HK, o:as-_ -1tt9jl IL 1_5:00_ , r 1).13---·--· "'_ -..:NM. -• I J~~< Nt.a -.N~---~"NM··_ . N'3 ,~ ~ . . ~ .11
TW4-04 NA Continuously Pumped well --2369 NC 7.43 NC 17.29 NC 343 NC 0 NC 103.0 NG
TW4-05 33.28 88.00 66.56 okay 1537 1526 0.72 6.66 6.66 0.00 15.60 15.59 0.06 396 397 0.25 1.9 1.9 0.00 63.4 63.0 0.63
r I•. .'l411:ll"" il:41~,. ~02 ~EllY. ~ 31MD :--(!!:101-· --..... :..6.61 '~flll ~~ .0.3Q 1.2,26 . 12.aa ·-· ~'I! :_j{M -_ ............. --NU: --__ NM .::: ,J ,g NM .. NC . -~ . ·-: JW~07 "IL 25.53 II • ~ :.5,.~1;ee:: . 11 -166Z_ -ll1.!: 7.22 7.211 15.:13 15.10. -
l,f; ~--,_. ]\16> .., ~ --N, C NM ' . .,f'.QmDillNi1~ :~Jll:W-. ~ I-'--'0!20 ---"~ rr Nu
TW4-08 26.18 55.00 52.36 okay 4946 4943 0.06 6.69 6.67 0.30 15.19 15.18 0.07 416 416 0.00 0 0 0.00 25.0 25.0 0.00
TW4-09 33.38 88.00 66.76 okay 2483 2479 0.16 6.73 6.72 0.15 15.15 15.14 0.07 357 356 0.28 26.0 27.0 3.77 10.0 9.8 2.02
1\W'~10, 29.24_ -:_ _ =ae.se;_ ,. _'1:)§iml' --i4!1lmJ;l&D:E>~· -,28 -1,. 2427 0~12 .9;Q5.. ---6.95 I iaraq -· ---1.9;66_ 15:&0 ·:.082 I\M I~ NC _., .. NN1. .-NC _:N .: --NG; t" , ,, ~ -~. 11 ,_ --
TW4-11 NA Continuously Pumped well --3721 NC 7.27 NC: 16.01 NC 282 NC 0 NC 65.0 NC .. ,.--I; .• TW4-i2° :,a1IU: ~ -.:HB.i.18 . ;Rt;imped;,ll>W 1 ·1S9'l _-... ::.1398 ·= =-OJP~ .71i23 • 7.::Zi 'Q.d•' 15.12 1'6ftl!): .. 0.13.: ~ .NM cc= ~-NM ' . Ui -' -NM _ ,· .N.Q~ .. lijWJSi~ :: 32,29 . 40~ 64.5a ' _;f!l.u_m~;OI\Y w..::u • : 1 ... ---w.10; -, ,~ Oi50 _ ,_. ~i~_ °l'.",U'.l, •.1:1~8 16..03 16.0Q. ':.Qill\:I NM 11 NC --N M:_ I e I 'NMi Ne; -~ • 11 ' -----"'
I! IW 4'1:4' f'.1.86,, 1$1~ '22.7 P~lfef.l Qrv_ 5316 . 5313~ ' 0;I:16: _6.§.0 1' •. eu,.a I O,iffl ,'13.82 1a.6.Q -0;1~_ NM . _N~ NM e;:' NM_ NC . .----
MW-26 NA Gontinueusly Pumped well --3440 NC 7.19 NC 16.01 NC 304 NC 0 NC 20.5 NC
TW4-16 48.87 110.00 97.74 okay 3683 3709 0.70 6.44 6.44 0.00 15.04 15.03 0.07 410 395 3.73 6.5 6.4 1.55 19.0 18.5 2.67
MW-32 32.22 65.10 64.44 okay 3735 3729 0.16 6.68 6.66 0.30 15.28 15.06 1.45 230 227 1.31 104.5 106.0 1.43 40.0 39.0 2.53
TW4-18 42.30 99.00 84.6 okay 1930 1890 2.09 6.23 6.23 0.00 15.65 15.65 0.00 430 430 0.00 16.2 16.1 0.62 20.1 21 .0 4.38
TW4-19 NA Continuously Pumped well -2501 NC 6.51 NC 16.36 NG 391 NC 2.0 NC 30.0 NC
TW4-20 NA Contlnu0usly Pumped well .. 3769 NC 6.90 NC 17.20 NC 318 NC 4.0 NC 24.6 NC
TW4-21 NA Centinuqusly Pumped well -2982 NC 7.01 NC 16.75 NC 286 NC 0 NC 33.5 NC
TW4-22 NA Continuously Pumped well -5326 NC 7.24 NC 16.48 NC 346 NC 0 NC 90.3 NC
TW4-23 27.19 88.00 54.38 okay 3516 3515 0.03 6.61 6.61 0.00 14.81 14.82 0.07 252 252 0.00 71 .0 70.2 1.13 31.0 30.0 3.28
TW4-24 NA Centinuou.sly Pumped well ·-7951 NC 7.08 NC 16.00 NC 347 NC 25.0 NC 19.4 NC
TW4-25 NA C0ntinu0usly Pumped well -· 2514 NC 7.12 NC 16.05 NG 311 NC 0 NC 42.0 NC ,-liW4~26 e:~_1' II j:jl08_ ---t9~2 et. ~J;JIY.· 4Uti:i'.. ' :=· 2'67Q. _. I•-_,l)iTI --1·, -8188· 6.e.9" _ 0115 ... 11 -15.37 I• 1§';3&,:· 0 ... 13 NM = . NC ::~ --NM NC NM' NC ----· -. .
,~. ,T.W~27 ., •ton _ 1" .. :i .~el!r ~ . .,. . _21'..8'1---: ·5oga_-:--_,-.~7 .• _0;02 6'.90 5i91 O.':ltt: fitl W-_ 12:10 . ~ JW 11 • -_N&t __ N_C~--1:L: :N~ i",!C NM, -N.0 . -. ---
1W4-281 atf::lfl?'.' I I~ . -(j e.Q~l -.-~ ~-I 1597 II .:OB 11r 7!0:, [I 7.0, ,·~ o:oo, -::. I!'.~_ 14lair-0; ~ -·NM, NE: -~M -NG_ NM'..,,.:. ,Ni .. -. -,---• 1:0~0:: -. . I
TW4!-29 . 1.2..97 c;, -•.· -1,-.~--40:4.Q _·:~: .. , __ Q.YQ' ,. , 7',J5; ?.l4 -"Q~~,._ _-15._13 ~· 15.'Z<t ~-0, 9 ,:NM NG_ ··N -NC. = NM NG: ----' ' ,_ -
_ TW.+30· ·, =1l.!m' -1: • jlrJ. 23.:i2. 1·Ra.,,, .... • ~7r F40i([ I ..-.,f;p~~ ::-5.63 ,. -~,, --=·0!35 -!11!i!H3 -: 15.90-_ I ,,0.,191 ~NM NC: -_, 1::-,; _N :c -.-=...,.. .t-J~ ~ It ---NM ---I NG----.
I ,_ TW.M.a1.. ~ 20j~ -;-----'~ ~KM! 'RQM Ii>,, :40011 --~3 =_J, o.~., 11~ 7~00 . ~00--:-.moo· .,. -13152 fltiiS'~ 0.22 '.NMt ' • ·-. · NE:, ! J=~ ,_N I ~,--: NC NM NC ---~ -
TW4-32 38.54 88.00 77.08 okay 6407 6391 0.25 4.28 4.28 0.00 14.98 15.00 0.13 479 480 0.21 10.0 11.0 9.52 31.0 32.0 3.17
~ TW~as-ss s,;a-11.88 P.UrtiPJdJ).1 --*~ 4428 --JJ.n I• 6;.801 o .. ~4.. If r1:.5.Tl 1:6~73 0.25:. -C '.NM. -C N<i: NM~ -I ~c. NM NG ~ ·mzo:-.• -...... .
I TW4:3,4 12.97 I • ~ = _ :u:t11Q1: ~iijJ!,, ~-P.um tea OJ --~ .~r ]S466-.-.0,~ _·1 ~71.:'lll' II 1.17 1~ ·;Q .• Ob. 1~ _-_t3.1:1,r 13:ti,£_ -0:37 'i.NM, ·-11 _Ne ·,:NM! _ :,. NC . -.NM --N(;;: :..
II lW4·a5: 77,.4~· --' ~:,,,.:__ -~ -{/''a~---14;9_41 ff.ilm -4331 :4341:1'; 0.21 • 6.94· ,6,W '"Of.H i -1~-28. -' .=11 2i~-'.; --0~0·. •NMI NG ,.... NM: --'-NC NM· -'NGf Ii ---
'.JWk35 a 27,20 aa:oo -'5ilk:4. . P.!ffei jlij"l:J] ~ I ;~--2407 •• 0;!1:Z -.6.87. I•' 6.8Z' 0.00 -=-~sg· ·ttaGO I '.L _0..07: NM' _11 N~ I -'~_NM. -,: N~ ·NM '.'1 L:NC_ _ ---.
TW4-37 NA C0ntinuously Pumped well -4452 NC 7.25 NC 16.80 NC 347 NC 0 NC 61 .3 NC
TW4-38 35.91 77.00 71.82 okay 1804 1820 0.88 6.67 6.68 0.15 14.95 14.90 0.34 347 347 0.00 20.0 19,0 5.13 56.1 56.0 0.18
TW4-39 NA Continuously Purriped well .. 2280 NC 7.04 NC 16.40 NC 279 NC 0 NC 55.0 NG
TW4-40 NA Continuously Pumpe<:f well .. 3977 NC 7.33 NC 17.20 NC 319 NC 0 NC 79.5 NC
TW4-41 NA Continuously Pumped well -2617 NC 7.46 NC 18.01 NC 382 NC 0 NC 95.1 NC . liW:.J;:,42 _ ~·11.'.48. _ 13.'ZS· . _ --'22.96 I[. P.-·----·~--~ -3@9 J $4.$1 O,QB 1'~9?-' 6._98_ ~nf:: 14.8!) l 1J:se·, 0.07 NM N~: NM---, N.C. -NM .. _ NC_ -. I
MW-04, MW-26, TW4-01 , TW4-02, TW4-04, TW4-11 , TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41 are contmually pumped wells.
03 1iW4-6 '4-07 TW4-10, 4-12, TW4-13 TW4-14 TW4-26, TW4-27, TW4-28 TW4'-29, TW4'-30, TW4-31, TW4;33 TW4-34 TW4-35, TW4-36, TW4-42were Qum eddrY,,....,,,..=..::.=""'"'""'-='-'~ .... ......._,,___ ____________________________ _
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 5/27/2020 6/2/2020 6 14 OK
Trip Blank Chloroform 5/27/2020 6/2/2020 6 14 OK
Trip Blank Chloromethane 5/27/2020 6/2/2020 6 14 OK
Trip Blank Methylene chloride 5/27/2020 6/2/2020 6 14 OK
Trip Blank Chloroform 6/3/2020 6/8/2020 5 14 OK
Trip Blank Methylene chloride 6/3/2020 6/8/2020 5 14 OK
Trip Blank Carbon tetrachloride 6/9/2020 6/12/2020 3 14 OK
Trip Blank Chloroform 6/9/2020 6/12/2020 3 14 OK
Trip Blank Chloromethane 6/9/2020 6/12/2020 3 14 OK
Trip Blank Methylene chloride 6/9/2020 6/12/2020 3 14 OK
Trip Blank Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
Trip Blank Chloroform 6/12/2020 6/17/2020 5 14 OK
Trip Blank Chloromethane 6/12/2020 6/17/2020 5 14 OK
Trip Blank Methylene chloride 6/12/2020 6/17/2020 5 14 OK
MW-04 Chloride 5/27/2020 6/9/2020 13 28 OK
MW-04 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
MW-04 Chloroform 5/27/2020 6/3/2020 7 14 OK
MW-04 Chloromethane 5/27/2020 6/2/2020 6 14 OK
MW-04 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
MW-04 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-0l Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-01 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-01 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-01 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-01 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-01 Nitrate/Nitrite ( as N) 5/27/2020 6/1/2020 5 28 OK
TW4-02 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-02 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-02 Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-02 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-02 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-02 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-03 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-03 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-03 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-03 Chloromethane 6/10/2020 6/12/2020 2 14 OK
TW4-03 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-03 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-03R Chloride 6/9/2020 6/22/2020 13 28 OK
TW4-03R Carbon tetrachloride 6/9/2020 6/12/2020 3 14 OK
TW4-03R Chloroform 6/9/2020 6/12/2020 3 14 OK
TW4-03R Chloromethane 6/9/2020 6/12/2020 3 14 OK
TW4-03R Methylene chloride 6/9/2020 6/12/2020 3 14 OK
TW4-03 Nitrate/Nitrite (as N) 6/9/2020 6/15/2020 6 28 OK
TW4-04 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-04 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-04 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-04 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-04 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-04 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-05 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-05 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-05 Chloroform 6/11/2020 6/13/2020 2 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
TW4-05 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-05 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-05 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-06 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-06 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-06 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-06 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-06 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-06 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-07 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-07 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-07 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-07 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-07 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-07 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-08 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-08 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-08 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-08 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-08 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-08 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-09 Chloride 6/12/2020 6/23/2020 11 28 OK
TW4-09 Carbon tetrachloride 6/12/2020 6/16/2020 4 14 OK
TW4-09 Chloroform 6/12/2020 6/16/2020 4 14 OK
TW4-09 Chloromethane 6/12/2020 6/16/2020 4 14 OK
TW4-09 Methylene chloride 6/12/2020 6/16/2020 4 14 OK
TW4-09 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-09R Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-09R Carbon tetrachloride 6/11/2020 6/12/2020 1 14 OK
TW4-09R Chloroform 6/11/2020 6/12/2020 1 14 OK
TW4-09R Chloromethane 6/11/2020 6/12/2020 1 14 OK
TW4-09R Methylene chloride 6/11/2020 6/12/2020 1 14 OK
TW4-09R Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-I0 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-I0 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-I0 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-I0 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-10 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-10 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-l l Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-ll Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-ll Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-ll Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-l l Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-ll Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-12 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-12 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-12 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-12 Chloromethane 6/10/2020 6/12/2020 2 14 OK
TW4-12 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-12 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-13 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-13 Carbon tetrachloride 6/11/2020 6/12/2020 1 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
TW4-13 Chloroform 6/l l/2020 6/12/2020 1 14 OK
TW4-13 Chloromethane 6/1 l/2020 6/12/2020 1 14 OK
TW4-13 Methylene chloride 6/l l/2020 6/12/2020 1 14 OK
TW4-13 Nitrate/Nitrite (as N) 6/l l/2020 6/15/2020 4 28 OK
TW4-14 Chloride 6/1 l/2020 6/22/2020 11 28 OK
TW4-14 Carbon tetrachloride 6/1 l/2020 6/13/2020 2 14 OK
TW4-14 Chloroform 6/1 l/2020 6/13/2020 2 14 OK
TW4-14 Chloromethane 6/1 l/2020 6/13/2020 2 14 OK
TW4-14 Methylene chloride 6/l l/2020 6/13/2020 2 14 OK
TW4-14 Nitrate/Nitrite (as N) 6/1 l/2020 6/15/2020 4 28 OK
MW-26 Chloride 5/27/2020 6/9/2020 13 28 OK
MW-26 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
MW-26 Chloroform 5/27/2020 6/2/2020 6 14 OK
MW-26 Chloromethane 5/27/2020 6/2/2020 6 14 OK
MW-26 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
MW-26 Nitrate/Nitrite (as N) 5/27/2020 6/l/2020 5 28 OK
TW4-16 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-16 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-16 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-16 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-16 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-16 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
MW-32 Chloride 6/12/2020 6/23/2020 11 28 OK
MW-32 Carbon tetrachloride 6/12/2020 6/16/2020 4 14 OK
MW-32 Chloroform 6/12/2020 6/16/2020 4 14 OK
MW-32 Chloromethane 6/12/2020 6/16/2020 4 14 OK
MW-32 Methylene chloride 6/12/2020 6/16/2020 4 14 OK
MW-32 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-18 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-18 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-18 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-18 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-18 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-18 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-19 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-19 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-19 Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-19 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-19 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-19 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-20 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-20 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-20 Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-20 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-20 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-20 Nitrate/Nitrite (as N) 5/27/2020 6/l/2020 5 28 OK
TW4-21 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-21 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-21 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-21 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-21 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-21 Nitrate/Nitrite (as N) 5/27/2020 6/l/2020 5 28 OK
TW4-22 Chloride 5/27/2020 6/9/2020 13 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
TW4-22 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-22 Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-22 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-22 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-22 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-23 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-23 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-23 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-23 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-23 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-23 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-24 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-24 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-24 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-24 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-24 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-24 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-25 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-25 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-25 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-25 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-25 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-25 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-26 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-26 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-26 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-26 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-26 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-26 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-27 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-27 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-27 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-27 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-27 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-27 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-28 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-28 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-28 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-28 Chloromethane 6/10/2020 6/12/2020 2 14 OK
TW4-28 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-28 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-29 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-29 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-29 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-29 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-29 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-29 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-30 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-30 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-30 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-30 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-30 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-30 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 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
TW4-31 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-31 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-31 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-31 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-31 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-31 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-32 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-32 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-32 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-32 Chloromethane 6/10/2020 6/12/2020 2 14 OK
TW4-32 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-32 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-33 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-33 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-33 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-33 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-33 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-33 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-34 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-34 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-34 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-34 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-34 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-34 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-35 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-35 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-35 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-35 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-35 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-35 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-36 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-36 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-36 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-36 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-36 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-36 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-37 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-37 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-37 Chloroform 5/27/2020 6/3/2020 7 14 OK
TW4-37 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-37 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-37 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-38 Chloride 6/11/2020 6/22/2020 11 28 OK
TW4-38 Carbon tetrachloride 6/11/2020 6/13/2020 2 14 OK
TW4-38 Chloroform 6/11/2020 6/13/2020 2 14 OK
TW4-38 Chloromethane 6/11/2020 6/13/2020 2 14 OK
TW4-38 Methylene chloride 6/11/2020 6/13/2020 2 14 OK
TW4-38 Nitrate/Nitrite (as N) 6/11/2020 6/15/2020 4 28 OK
TW4-39 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-39 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-39 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-39 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-39 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
I-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-39 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-40 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-40 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-40 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-40 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-40 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-40 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-41 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-41 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-41 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-41 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-41 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-41 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-42 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-42 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-42 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-42 Chloromethane 6/10/2020 6/12/2020 2 14 OK
TW4-42 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-42 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-60 Chloride 5/27/2020 6/9/2020 13 28 OK
TW4-60 Carbon tetrachloride 5/27/2020 6/2/2020 6 14 OK
TW4-60 Chloroform 5/27/2020 6/2/2020 6 14 OK
TW4-60 Chloromethane 5/27/2020 6/2/2020 6 14 OK
TW4-60 Methylene chloride 5/27/2020 6/2/2020 6 14 OK
TW4-60 Nitrate/Nitrite (as N) 5/27/2020 6/1/2020 5 28 OK
TW4-65 Chloride 6/10/2020 6/22/2020 12 28 OK
TW4-65 Carbon tetrachloride 6/10/2020 6/12/2020 2 14 OK
TW4-65 Chloroform 6/10/2020 6/12/2020 2 14 OK
TW4-65 Ch loromethane 6/10/2020 6/12/2020 2 14 OK
TW4-65 Methylene chloride 6/10/2020 6/12/2020 2 14 OK
TW4-65 Nitrate/Nitrite (as N) 6/10/2020 6/15/2020 5 28 OK
TW4-70 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-70 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-70 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-70 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-70 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-70 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
TW4-75 Chloride 6/12/2020 6/24/2020 12 28 OK
TW4-75 Carbon tetrachloride 6/12/2020 6/17/2020 5 14 OK
TW4-75 Chloroform 6/12/2020 6/17/2020 5 14 OK
TW4-75 Chloromethane 6/12/2020 6/17/2020 5 14 OK
TW4-75 Methylene chloride 6/12/2020 6/17/2020 5 14 OK
TW4-75 Nitrate/Nitrite (as N) 6/12/2020 6/16/2020 4 28 OK
Table 1-3 Recipt Temperature Check
Sample Batch Wells in Batch Temperature
MW-04, TW4-0l, TW4-02, TW4-04, TW4-ll, MW-26, TW4-19, TW4-20,
2005695 TW4-21, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41, l.0°C
TW4-60, Trip Blank
TW4-03, TW4-03R, TW4-05, TW4-06, TW4-09R, TW4-12, TW4-13, TW4-14,
2006384 TW4-23, TW4-27, TW4-28, TW4-31, TW4-32, TW4-34, TW4-35, TW4-36, l.4°C
TW4-38, TW4-42, TW4-65, Trip Blank
2006426 TW4-07, TW4-08, TW4-09, TW4-I0, TW4-16, MW-32, TW4-18, TW4-26, l.4°C TW4-29, TW4-30, TW4-33, TW4-70, TW4-75, Trip Blank
1-4 Analytical Method Check
Parameter Method Method Used by Lab
SW8260B,
Carbon Tetrachloride SW8260C or SW8260D
SW8260D
A4500-Cl B or
Chloride A4500-Cl E or E300.0
E300.0
SW8260B,
Chloroform SW8260C or SW8260D
SW8260D
SW8260B,
Chloromethane SW8260C or SW8260D
SW8260D
SW8260B,
Methylene chloride SW8260C or SW8260D
SW8260D
Nitrogen E353.1 or E353.2 E353.2
All parameters were analyzed using the reporting method specificied in the QAP
I 5 R -eportrng 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 I 1 OK
Trip Blank Chloroform 1 ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u I 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u I 1 OK
Trip Blank Methylene chloride 1 ug/L u I 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 I 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 I ug/L u 1 1 OK
MW-04 Chloroform 20 ug/L 20 1 OK
MW-04 Chloromethane 1 ug/L u 1 1 OK
MW-04 Methylene chloride 1 ug/L u 1 1 OK
MW-04 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-01 Chloride 1 mg/L 5 1 OK
TW4-0l Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-0l Chloroform 10 ug/L 10 1 OK
TW4-01 Chloromethane 1 ug/L u 1 1 OK
TW4-01 Methylene chloride 1 ug/L u 1 1 OK
TW4-01 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-02 Chloride 1 mg/L 5 1 OK
TW4-02 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-02 Chloroform 20 ug/L 20 1 OK
TW4-02 Chloromethane 1 ug/L u 1 1 OK
TW4-02 Methylene chloride 1 ug/L u 1 1 OK
TW4-02 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-03 Chloride 1 mg/L 5 I 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 1 OK
TW4-03R Chloromethane 1 ug/L u 1 1 OK
TW4-03R Methylene chloride 1 ug/L u 1 1 OK
TW4-03R Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-04 Chloride 1 mg/L 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 1 ug/L u 1 1 OK
I 5 R -epornng 1m1t ec L .. Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-05 Methylene chloride 1 ug/L u l l OK
TW4-05 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-06 Chloride 1 mg/L 5 I OK
TW4-06 Carbon tetrachloride l ug/L u 1 l OK
TW4-06 Chloroform 1 ug/L 1 I OK
TW4-06 Chloromethane 1 ug/L u I l OK
TW4-06 Methylene chloride 1 ug/L u l I OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 1 O. l 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 5 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 I 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 l mg/L 5 1 OK
TW4-09 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-09 Chloroform 1 ug/L 1 I OK
TW4-09 Chloromethane 1 ug/L u 1 I 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 I 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
TW4-1 l Chloride 1 mg/L 10 1 OK
TW4-l l Carbon tetrachloride 1 ug/L 1 1 OK
TW4-l 1 Chloroform 50 ug/L 50 1 OK
TW4-l 1 Chloromethane 1 ug/L u 1 1 OK
TW4-l 1 Methylene chloride 1 ug/L u 1 1 OK
TW4-l l Nitrate/Nitrite (as N) 0.1 mg/L 5 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) 0.1 mg/L 10 0.1 OK
TW4-13 Chloride 1 mg/L 10 1 OK
TW4-13 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-13 Chloroform 1 ug/L u 1 1 OK
TW4-13 Chloromethane 1 ug/L u 1 1 OK
-eponmg 1m1t ec I 5 R L .. Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-13 Methylene chloride 1 ug/L u I 1 OK
TW4-13 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 I I OK
TW4-14 Chloromethane 1 ug/L u 1 1 OK
TW4-14 Methylene chloride 1 ug/L u I I 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 50 ug/L 50 1 OK
MW-26 Chloromethane 1 ug/L u I 1 OK
MW-26 Methylene chloride J ug/L 1 1 OK
MW-26 Nitrate/Nitrite (as N) 0.1 mg/L 2 0.1 OK
TW4-16 Chloride I mg/L 10 1 OK
TW4-16 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-16 Chloroform 1 ug/L 1 I 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 5 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 I I 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 I OK
TW4-18 Chloroform 1 ug/L I 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 5 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 u 1 1 OK
TW4-19 Methylene chloride l ug/L u 1 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.1 mg/L 2 0.1 OK
TW4-20 Chloride 5 mg/L 50 1 OK
TW4-20 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-20 Chloroform 100 ug/L JOO 1 OK
TW4-20 Chloromethane 1 ug/L 1 1 OK
TW4-20 Methylene chloride 1 ug/L 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 u 1 1 OK
TW4-21 Methylene chloride 1 ug/L u 1 1 OK
TW4-21 Nitrate/Nitrite (as N) 0.2 mg/L 20 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 50 ug/L 50 1 OK
TW4-22 Chloromethane 1 ug/L u 1 1 OK
I 5 R -eporltnP. 1m1t ec L' . Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-22 Methylene chloride 1 ug/L u I 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
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 I 1 OK
TW4-24 Chloroform I ug/L I 1 OK
TW4-24 Chloromethane I ug/L u l 1 OK
TW4-24 Methylene chloride 1 ug/L u 1 1 OK
TW4-24 Nitrate/Nitrite (as N) 0.5 mg/L 50 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 I 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 10 ug/L 10 1 OK
TW4-26 Chloromethane 1 ug/L u 1 1 OK
TW4-26 Methylene chloride 1 ug/L u I 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) 0.5 mg/L 50 0.1 OK
TW4-28 Chloride 1 mg/L 10 I OK
TW4-28 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-28 Chloroform l ug/L u 1 1 OK
TW4-28 Chloromethane 1 ug/L u 1 1 OK
TW4-28 Methylene chloride 1 ug/L u 1 1 OK
TW4-28 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-29 Chloride 1 mg/L 5 I OK
TW4-29 Carbon tetrachloride I 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 2 0.1 OK
TW4-30 Chloride I mg/L 5 1 OK
TW4-30 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-30 Chloroform 1 ug/L 1 1 OK
TW4-30 Chloromethane l 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 5 0.1 OK
TW4-31 Chloride l 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
I 5 R -eportmg 1m1t ec L' . Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-31 Methylene chloride I ug/L u 1 1 OK
TW4-31 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 I ug/L u I 1 OK
TW4-32 Chloromethane 1 ug/L u 1 1 OK
TW4-32 Methylene chloride 1 ug/L u 1 I OK
TW4-32 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-33 Chloride 1 m2/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 1 1 OK
TW4-33 Nitrate/Nitrite (as N) 0.1 mg/L 2 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 I 1 OK
TW4-34 Chloromethane 1 ug/L u I 1 OK
TW4-34 Methylene chloride I ug/L u I I OK
TW4-34 Nitrate/Nitrite (as N) 0.1 mg/L I 0.1 OK
TW4-35 Chloride 1 m2/L 5 I OK
TW4-35 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-35 Chloroform 1 ug/L u 1 1 OK
TW4-35 Chloromethane 1 ug/L u I 1 OK
TW4-35 Methylene chloride 1 u2/L u 1 1 OK
TW4-35 Nitrate/Nitrite (as N) 0.1 m2/L I 0.1 OK
TW4-36 Chloride 1 mg/L 10 1 OK
TW4-36 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-36 Chloroform 1 u2/L u I 1 OK
TW4-36 Chloromethane 1 ug/L u 1 I OK
TW4-36 Methylene chloride 1 ug/L u 1 I OK
TW4-36 Nitrate/Nitrite (as N) 0.1 mg/L u I 0.1 OK
TW4-37 Chloride 5 mg/L 50 1 OK
TW4-37 Carbon tetrachloride 1 u2/L 1 1 OK
TW4-37 Chloroform 100 ug/L 100 1 OK
TW4-37 Chloromethane 1 ug/L I I OK
TW4-37 Methylene chloride 1 ug/L u 1 I OK
TW4-37 Nitrate/Nitrite (as N) 0.2 m2/L 20 0.1 OK
TW4-38 Chloride 1 m_g/L 5 I OK
TW4-38 Carbon tetrachloride I ug/L u 1 1 OK
TW4-38 Chloroform 1 ug/L u 1 1 OK
TW4-38 Chloromethane 1 ug/L u 1 1 OK
TW4-38 Methylene chloride 1 u2/L u I I OK
TW4-38 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-39 Chloride 1 mg/L 10 1 OK
TW4-39 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-39 Chloroform 100 ug/L 100 1 OK
TW4-39 Chloromethane 1 u_g/L u 1 1 OK
TW4-39 Methylene chloride 1 u_g/L u 1 1 OK
TW4-39 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-40 Chloride 1 mg/L 5 1 OK
TW4-40 Carbon tetrachloride 1 u_g/L u 1 1 OK
TW4-40 Chloroform 10 ug/L 10 I OK
TW4-40 Chloromethane 1 ug/L u 1 1 OK
I 5 R -eporung lffill ec L' . Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-40 Methylene chloride 1 ug/L u 1 1 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 l ug/L u l 1 OK
TW4-41 Methylene chloride l ug/L u l l OK
TW4-41 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-42 Chloride 1 mg/L 5 1 OK
TW4-42 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-42 Chloroform 1 ug/L u I I OK
TW4-42 Chloromethane I ug/L u 1 l OK
TW4-42 Methylene chloride 1 ug/L u 1 I OK
TW4-42 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-60 Chloride 1 mg/L u 1 1 OK
TW4-60 Carbon tetrachloride I ug/L u 1 1 OK
TW4-60 Chloroform 1 ug/L u 1 1 OK
TW4-60 Chloromethane 1 ug/L u 1 1 OK
TW4-60 Methylene chloride I ug/L u 1 I OK
TW4-60 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-65 Chloride 1 mg/L 10 1 OK
TW4-65 Carbon tetrachloride 1 ug/L u l 1 OK
TW4-65 Chloroform 1 ug/L u 1 1 OK
TW4-65 Chloromethane 1 ug/L u 1 1 OK
TW4-65 Methylene chloride 1 ug/L u 1 1 OK
TW4-65 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-70 Chloride l mg/L 10 l OK
TW4-70 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-70 Chloroform 1 ug/L I 1 OK
TW4-70 Chloromethane 1 ug/L u 1 1 OK
TW4-70 Methylene chloride I ug/L u 1 1 OK
TW4-70 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-75 Chloride l mg/L 10 1 OK
TW4-75 Carbon tetrachloride I ug/L u 1 1 OK
TW4-75 Chloroform 10 ug/L 10 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 10 0.1 OK
1-6 Trip Blank Evaluation
Lab Report Constituent Result
Carbon tetrachloride ND ug/L
2005695 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
2006384 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
2006426 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)
RPO= Relative Percent Difference
ND = The analyte was not detected
TW4-03
26.2
6.53
ND
ND
ND
ND
TW4-09
39.5
0.990
ND
55.1
ND
ND
TW4-07
44.1
4.06
ND
864
ND
ND
TW4-65 %RPD
26.7 1.9
6.63 1.5
ND NC
ND NC
ND NC
ND NC
TW4-70 %RPD
39.6 0.3
I.OJ 2.0
ND NC
56.4 2.3
ND NC
ND NC
TW4-75 %RPD
43.l 2.3
4.19 3.2
ND NC
871 0.8
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
MS MSD %REC RPD
Lab Repol:lt Lab Sample ID Well Analyte %REC %REC Range RPD Range
2006426 2006426-003 TW4-30 Chloroform 127 126 79-124 0.25 35
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
RciH8fl!e
l~llil -ate Re .,1Jlillt
''Slrutnwl'e ~o!llL'$lii).e1let (~~::PL) '!Prevj~vus 'We1 I ®alJll1pfod
TW4-03R Chloroform 3.05 NA
TW4-09R Chloroform 1.98 TW4-05 (15.4)
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
MW-24A installed during December, 2019
......_ 70 kriged chloroform isocon and label
TW4-42
¢ND
temporary perched monitoring well
installed April, 201 9 showing
concentration in µg/L
TW4-40 temporary perched monitoring well
•367 installed February, 2018 showing
concentration in µg/L
MW-38
"9-ND
MW-32
e ND
TW4-7
0 864
TWN-1
~NS
PIEZ-1
"1 NS
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)
' 1 mile
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 2nd QUARTER, 2020 CHLOROFORM (µg/L)
WHITE MESA SITE
APPROVED DATE REFERENCE
H:/718000/aug20/chloroform/Uchl0620 .srf
FIGURE
J-1
......
NS = not sampled; ND = not detected
~ .. o
TW4-42
¢ND
TW4-40
... 367
MW-32
.ND
TW4-7
0 864
PIEZ-2
GI 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 2nd QUARTER, 2020 CHLOROFORM (µg/L)
WHITE MESA SITE
APPROVED DATE
(detail map)
REFERENCE H/718000/aug20/
chloroform/Uchl0620det.srf
FIGURE
J-2
NS = not sampled; ND= not detected
~70
TW4-42
¢ND
TW4-40
... 367
MW-32 e No
TW4-7
0 864
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.
1st QUARTER, 2020 CHLOROFORM
GREATER THAN OR EQUAL TO 70 µg/L GRID
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/aug20/
ch loroform/Uchl0620ge 70.srf
FIGURE
J-3
TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
Chier f(t CaFbon CbleFometlha e Met&rt. Nitrate Chloride MW-4 'l'etraehloria
II (~ iumi:\, ( ... ~ Chfmid.e (ug/1) (mgll) (mg/I)
28-Sep-99 6200
28-Sep-99 5820
28-Sep-99 6020 I
15-Mar-OO 5520
15-Mar-OO 5430
2-Sep-00 5420 9.63
30-Nov-00 6470 9.37
29-Mar-Ol 4360 8.77
22-Jun-Ol 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 <l 6.4 50
28-Feb-07 2300 1.6 <l <l 6.3 47
27-Jun-07 2000 1.8 <l <l 7 45
15-Aug-07 2600 1.9 <1 <l 6.2 47
10-0ct-07 2300 1.7 <l <l 6.2 45
26-Mar-08 2400 1.7 <l <l 5.8 42
25-Jun-08 2500 1.6 <1 <l 6.09 42
10-Sep-08 1800 1.8 <l <l 6.36 35
15-0ct-08 2100 1.7 <l <l 5.86 45
4-Mar-09 2200 1.5 <1 <l 5.7 37
23-Jun-09 1800 1.3 <1 <l 5.2 34
14-Sep-09 2000 1.4 <1 <l 5.3 43
Chhirof-0rm Car~ n Chlo ethane Melrytene Nitrate Chlol'ide MW-4 Tetrachl: ride (ug(I) {ua4!} (ugll) Chloride ,(,ug4) (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-l l 1700 1.5 ND ND 4.6 40
1-Jun-11 1700 1.4 ND ND 4.9 35
17-Aug-ll 1700 1.1 ND ND 4.9 41
16-Nov-11 1600 1.3 ND ND 5.1 40
23-Jan-12 1500 1 ND ND 4.8 41
6-Jun-12 1400 1.2 ND ND 4.9 39
4-Sep-12 1500 1.5 ND ND 5 41
4-0ct-12 1300 1 ND ND 4.8 42
l l-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.l
27-Jan-14 1390 4.15 ND ND 4.7 38.5
19-May-14 1390 5.21 ND ND 4.08 39.9
24-Aug-14 1490 ND 7.6 ND 3.7 41
21-0ct-14 1440 ND ND ND 5.07 41.5
9-Mar-15 1400 1.26 ND ND 5.75 40.7
8-Jun-15 1300 ND ND ND 2.53 43.1
31-Aug-15 1290 ND ND ND 4.79 44.3
19-0ct-15 1200 ND ND ND 4.43 40.8
9-Mar-16 1240 ND ND ND 5.15 42.2
23-May-16 1580 1.44 ND ND 4.54 43.7
25-Jul-16 1430 ND ND ND 4.95 42.5
12-0ct-16 1470 1.24 ND ND 4.88 44.8
8-Mar-17 1450 1.22 ND ND 4.99 43.3
13-Jun-17 1430 1.15 ND ND 4.88 44.0
26-Jul-17 1400 1.15 ND ND 4.59 43.8
ll-Oct-17 1320 ND ND ND 5.25 43.8
12-Mar-18 1320 1.07 ND ND 4.47 46.2
8-Jun-18 1240 ND ND ND 4.64 43.5
22-Aug-18 1300 ND ND ND 4.55 48.5
28-Nov-18 1330 ND ND ND 4.44 43.1
8-Mar-19 1190 ND ND ND 5.05 41.5
5-Jun-19 1300 ND ND ND 5.16 40.6
4-Sep-19 1180 ND ND ND 4.69 41.9
l l-Dec-19 1370 ND ND ND 4.34 45.5
19-Feb-20 1230 ND ND ND 6.22 48.1
27-May-20 1250 ND ND ND 5.04 40.7
0
_.
0 0 0
I\)
0 0 0
(ug/L)
c.> 0 0 0
.i::. 0 0 0
c.n 0 0 0
0) 0 0 0
-...J 0 0 0
Sep-99 +----t----1-----t----1----,.-----i---~,...~---;
Mar-00
Sep-00
Mar-01
Sep-01
Mar-02
Sep-02
Mar-03
~:~~!1 I I t r 1
Sep-04 1 r / : ..
Mar-05 •
Sep-05
Mar-06
Sep-06
Mar-07
Sep-07
Mar-08
Sep-08
Mar-09
Sep-09
Mar-10
Sep-10
Mar-11
Sep-11
Mar-12
Sep-12
Mar-13
Sep-13
Mar-14
Sep-14
Mar-15
Sep-15
Mar-16
Sep-16
Mar-17
Sep-17
Mar-18
Sep-18
Mar-19
Sep-19
Mar-20 ._~-~----~~--~--~---~--~---.....
s::: ~ ~ I
() :::r
0
0 0
3
~
C <D (/)
Chlorofomi Carbaa Qlufflllethne Mdh~lene Nitrate CliduPnle I 'FW4-1 Tetr eride Cldorirm (ug/1) (ug¢1) (ug,<I) (uwt) (mg.ti) (mgtl)
28-Jun-99 1700 7.2
10-Nov-99 5.8
15-Mar-00 1100
10-Apr-OO 1490
6-Jun-00 1530
2-Sep-00 2320 5.58
30-Nov-OO 3440 7.79
29-Mar-01 2340 7.15
22-Jun-01 6000 8.81
20-Sep-01 12.8
8-Nov-01 3200 12.4
26-Mar-02 3200 13.1
22-May-02 2800 12.7
12-Sep-02 3300 12.8
24-Nov-02 3500 13.6
28-Mar-03 3000 12.4
23-Jun-03 3600 12.5
12-Sep-03 2700 12.5
8-Nov-03 3400 11.8
29-Mar-04 3200 11
22-Jun-04 3100 8.78
17-Sep-04 2800 10.8
17-Nov-04 3000 11.1
16-Mar-05 2700 9.1
25-May-05 3080 NA NA NA 10.6 NA
31-Aug-05 2900 <10 <10 <10 9.8 NA
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 <1 <1 9.4 47
28-Feb-07 1900 1.2 <1 <1 8.9 47
27-Jun-07 1900 1.4 <1 <1 9 45
15-Aug-07 2300 1.3 <1 <1 8.4 43
10-0ct-07 2000 1.3 <1 <1 7.8 43
26-Mar-08 · 2000 1.3 <l <l 7.6 39
25-Jun-08 1900 1.1 <1 <l 8.68 39
10-Sep-08 1700 1.3 <1 <l 8.15 35
15-0ct-08 1700 1.3 <1 <1 9.3 41
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
II (ug/1) (ug/1)
11-Mar-09 1700 1.1 <1 <1 7.5 37
24-Jun-09 1500 1 <l <l 6.9 37
15-Sep-09 1700 <1 <] <1 7.3 36
29-Dec-09 1400 <1 <l <1 6.8 41
3-Mar-10 1300 <l <l <1 7.1 35
15-Jun-10 1600 1.2 <1 <l 6.8 40
24-Aug-10 1500 <1 <1 <1 6.8 35
14-0ct-10 1500 <l <l <I 6.6 40
24-Feb-l l 1300 ND ND ND 6.6 41
1-Jun-11 1200 ND ND ND 7 35
18-Aug-11 1300 ND ND ND 6.8 36
29-Nov-11 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 llOO ND ND ND 6.87 39.1
12-Sep-13 1150 ND ND ND 7.12 37.6
14-Nov-13 1280 ND ND ND 7.08 36.5
5-Feb-14 1090 5.47 ND ND 7.74 38.9
23-May-14 1020 4.77 ND ND 6.93 37.4
27-Aug-14 845 ND 1.4 ND 4.8 38
29-0ct-14 ll40 ND ND ND 6.31 38.7
9-Mar-15 1130 ND ND ND 7.06 38.3
8-Jun-15 1260 ND ND ND 6.07 40.3
31-Aug-15 1060 ND ND ND 6.28 45.9
19-0ct-15 1040 ND ND ND 1.55 38.5
9-Mar-16 974 ND ND ND 0.148 41.7
23-May-16 1140 ND ND ND 0.138 44.4
25-Jul-16 1160 ND ND ND 5.49 44.7
13-0ct-16 1330 ND ND ND 0.746 44.2
8-Mar-17 519 ND ND ND 4.44 41.5
13-Jun-17 977 ND ND ND 5.74 41.8
26-Jul-17 958 ND ND ND 5.04 42.8
l l-Oct-17 556 ND ND ND 5.78 38.5
12-Mar-18 70.4 ND ND ND 4.84 45.8
8-Jun-18 942 ND ND ND 4.38 42.0
22-Aug-18 1010 ND ND ND 4.30 47.3
Chloroform Carbon CDhlor.omethane Methflene Nitrat~ Chloride TW4·1 (Ug/1~ Tetrachloride (ug/0 Chloride {mg/I) (mg/I) Gug/1) I (ug/1) I
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
27-May-20 499 ND ND ND 0.443 46.4
.....
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
28-0ec-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)
w 0 0 0
.j::,,.
0 0 0
01 0 0 0
O> 0 0 0
""" 0 0 0
-I =E .,::..
I -0 :::r
0 ""'I 2. 0 ""'I
3
< !.
C C'D u,
Chloi,oform Carm Cblocomeihane Metltylene Nitrate CldGride TW4·2 (Ug/1) Tetradlfu (ug/1, Chlvide {mglt) (~ (lll!II} (umn
10-Nov-99 2510
2-Sep-00 5220
28-Nov-00 4220 10.7
29-Mar-01 3890 10.2
22-Jun-01 5500 9.67
20-Sep-01 4900 11.4
8-Nov-01 5300 10.1
26-Mar-02 5100 9.98
23-May-02 4700 9.78
12-Sep-02 6000 9.44
24-Nov-02 5400 10.4
28-Mar-03 4700 9.5
23-Jun-03 5100 9.6
12-Sep-03 3200 8.6
8-Nov-03 4700 9.7
29-Mar-04 4200 9.14
22-Jun-04 4300 8.22
17-Sep-04 4100 8.4
17-Nov-04 4500 8.6
16-Mar-05 3700 7.7
25-May-05 3750 8.6
31-Aug-05 3900 <10 <10 <10 8 NA
1-Dec-05 3500 <50 <50 <50 7.8 NA
9-Mar-06 3800 <50 <50 <50 7.5 56
14-Jun-06 3200 <50 <50 <50 7.1 56
20-Jul-06 4120 <50 <50 <50 7.4 54
8-Nov-06 3420 2.3 <1 <1 7.6 55
28-Feb-07 2900 1.8 <1 <1 7.3 54
27-Jun-07 3000 2.5 <1 <1 7.8 50
15-Aug-07 340 2.2 <l <l 7.3 49
10-0ct-07 3200 2.1 <1 <1 6.9 51
26-Mar-08 3300 2.3 <l <I 6.9 48
25-Jun-08 3100 2.2 <1 <I 7.44 46
10-Sep-08 2800 2.4 <1 <l 7.1 42
15-0ct-08 3200 2.4 <2 <2 7.99 47
11-Mar-09 3100 2.2 <1 <1 6.5 46
24-Jun-09 2800 2 <1 <1 6.4 44
15-Sep-09 3000 2 <1 <1 6.6 43
29-Dec-09 1600 2 <1 <1 6.4 46
€'&bcm ~ene. ~
TW4•2 Chloroform 1'etrac· · .. Chloromethan Chlu ide Nitrate Odm de
II (ug/1) (ui!LO (ug(,f) (ueffi (mg/}) (m.gl,t)
II
3-Mar-10 2600 2 <1 <1 6.8 42
15-Jun-10 3300 2.6 <1 <1 6.7 43
16-Aug-10 3300 2.5 <1 <1 6.6 43
14-0ct-10 3000 2.1 <1 <1 6.5 41
24-Feb-11 3100 2.4 ND ND 7 46
2-Jun-11 3000 2.2 ND ND 6.8 42
17-Aug-11 2400 1.6 ND ND 6 48
29-Nov-11 3900 2.8 ND ND 7 49
24-Jan-12 2500 2 ND ND 7.1 49
14-Jun-12 2500 2.1 ND ND 7.7 52
13-Sep-12 2900 1.8 ND ND 4 76
4-0ct-12 3100 2 ND ND 7.6 49
13-Feb-13 3580 5.17 ND ND 8.1 46
19-Jun-13 3110 2.65 ND ND 7.51 46.9
12-Sep-13 3480 2.41 ND ND 9.3 44.9
14-Nov-13 3740 3.15 ND ND 8.39 43.9
6-Feb-14 3180 7.1 ND ND 7.87 45.9
23-May-14 2930 6.05 ND ND 9.11 45.4
27-Aug-14 3170 1.4 3.6 ND 6.2 45
30-0ct-14 3580 2.6 ND ND 8.45 45.5
9-Mar-15 1840 1.44 ND ND 5.32 44.9
8-Jun-15 1650 ND ND ND 4.3 48.1
31-Aug-15 1310 ND ND ND 3.76 50.0
19-0ct-15 2070 ND ND ND 5.18 41.9
9-Mar-16 1970 1.20 ND ND 5.30 43.4
23-May-16 2070 1.49 ND ND 5.67 43.8
25-Jul-16 1780 ND ND ND 4.07 42.9
12-0ct-16 1600 ND ND ND 6.07 44.3
8-Mar-17 1570 ND ND ND 4.74 43.1
13-Jun-17 1940 ND ND ND 4.90 43.6
26-Jul-17 1310 ND ND ND 5.08 43.2
l l-Oct-17 1610 ND ND ND 3.28 43.5
12-Mar-18 764 ND ND ND 2.94 44.4
8-Jun-18 949 ND ND ND 3.50 41.3
22-Aug-18 980 ND ND ND 4.83 44.3
28-Nov-18 822 ND ND ND 3.52 41.7
8-Mar-19 1040 ND ND ND 3.92 40.4
5-Jun-19 1360 ND ND ND 4.38 39.8
4-Sep-19 797 ND ND ND 4.79 40.8
Chloroform Garbon Chlorometbane Methylene Nitra~e Oblorlde TW4-2 Tetrachlo,ride Chloride (ug/1) (ue/1) (ug/1) (ue/1) (mg/I) (mg()}
I
10-Dec-19 934 ND ND ND 3.40 41.5
19-Feb-20 1880 ND ND ND 6.07 42.1
27-May-20 1070 ND ND ND 3.62 40.6
0
.....
0 0 0
I\)
0 0 0
(ug/L)
(,J
0 0 0
~ 0 0 0
c.n 0 8
0)
0 0 0
'-I 0 0 0
1 O-Nov-99 ;-----t----t--.._=-l-----+----...+----+----1
10-May-OO
10-Nov-OO
1 O-May-01
10-Nov-01
10-May-02
10-Nov-02
10-May-03
10-Nov-03
10-May-04
10-Nov-04
10-May-05
10-Nov-05
10-May-06
10-Nov-06
10-May-07
10-Nov-07
10-May-08
10-Nov-08
10-May-09
10-Nov-09
10-May-10
10-Nov-10
10-May-11
10-Nov-11
10-May-12
10-Nov-12
10-May-13
10-Nov-13
10-May-14
10-Nov-14
10-May-15
10-Nov-15
10-May-16
10-Nov-16
10-May-17
10-Nov-17
10-May-18
10-Nov-18
10-May-19
10-Nov-19
Q.,iii" ~ o O cO"CD _Ill =--Q'<!ll 5i g ea. C: g "t) ~ Q ~ cl Q.
o'<CDo;:?. o~m-<m ... 0 (/l ... "t)
Q. ... [ ~ m
..... ::, Ill C: (/l
92-cii1;f~
(") C.. -g C.-i~
!!1. ai i (") a. 0 CD.-+<::; :::!. O Ill CD ::, -en
<O ai "t)
:T iii" g CD C. (/l
1 O-May-20 -------..-,,===---....L,_ __ _i ___ _L ___ ..L_ __ _J_ __ __J
-4 =e ~ I N
(') :::r 0 ""I 2. 0 ""I
3
< m
C CD u,
Cliloroform II' Carb~ 0d iJ"DlilWdl . re Me'tltylene Nitrate a .. hle TW4·3 TeilF dlleride Cllmriite (ug/l) ind) (~ (IQ!A) ,, (mg/0 (m.glt)
28-Jun-99 3500 7.6
29-Nov-99 702
15-Mar-OO 834
2-Sep-00 836 1.56
29-Nov-00 836 1.97
27-Mar-01 347 1.85
21-Jun-Ol 390 2.61
20-Sep-01 300 3.06
7-Nov-01 170 3.6
26-Mar-02 11 3.87
21-May-02 204 4.34
12-Sep-02 203 4.32
24-Nov-02 102 4.9
28-Mar-03 0 4.6
23-Jun-03 0 4.8
12-Sep-03 0 4.3
8-Nov-03 0 4.8
29-Mar-04 0 4.48
22-Jun-04 0 3.68
17-Sep-04 0 3.88
17-Nov-04 0 4.1
16-Mar-05 0 3.5
25-May-05 <1 NA NA NA 3.7 NA
31-Aug-05 <1 <1 6.4 <I 3.5 NA
l-Dec-05 <I <l 2.3 <1 3.3 NA
9-Mar-06 <1 <1 2.2 <1 3.3 26
14-Jun-06 <1 <I <I <1 J.2 26
20-Jul-06 <l <1 1.6 <1 2.9 26
8-Nov-06 <l <l <l <1 1.5 23
28-Feb-07 <1 <l <l <l 3.1 22
27-Jun-07 <1 <1 <1 <1 3.3 23
15-Aug-07 <1 <I <1 <1 3.1 24
10-0ct-07 <1 <l <l <l 2.8 27
26-Mar-08 <1 <1 <1 <1 2.8 21
25-Jun-08 <1 <1 <l <1 2.85 19
10-Sep-08 <1 <1 <l <1 2.66 19
15-0ct-08 <1 <l <l <1 2.63 22
4-Mar-09 <1 <1 <l <1 2.5 21
24-Jun-09 <1 <I <l <1 2.9 20
15-Sep-09 <1 <1 <l <1 2.8 21
16-Dec-09 <l <l <l <I 2.5 22
23-Feb-10 <1 <l <1 <1 2.8 23
Chlo ee CarJ>:o Chiu methane Metbylen :Nikrafe Chloride TW4-3 Tekaebler..id CM ide (~ '{111!.R)1 (11-J fttd)i (m.gffl (ntglll)
8-Jun-10 <1 <l <l <1 3 24
10-Aug-10 <1 <l <l <l 3.1 22
5-0ct-10 <l <l <1 <l 3.3 26
15-Feb-ll ND ND ND ND 3.5 23
25-May-11 ND ND ND ND 3.7 23
16-Aug-1 l ND ND ND ND 4 23
15-Nov-l 1 ND ND ND ND 4.4 23
l 7-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
10-0ct-17 ND ND ND ND 6.32 25.9
14-Mar-18 ND ND ND ND 6.46 29.8
12-Jun-18 ND ND ND ND 6.52 26.1
29-Aug-18 ND ND ND ND 5.53 31.0
30-Nov-18 ND ND ND ND 5.85 27.4
13-Mar-19 ND ND ND ND 5.82 25.5
13-Jun-19 ND ND ND ND 6.68 27.4
11-Sep-19 ND ND ND ND 5.12 26.0
12-Dec-19 ND ND ND ND 5.91 28.0
17-Mar-20 ND ND ND ND 6.15 27.7
10-Jun-20 ND ND ND ND 6.53 26.2
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
Jun-20
0
0
_..
c.n 0 0 0 0 0
0 0
(ug/L)
_.. N N c.n 0 c.n 0 0 0 0 0 0
0 0 0
(.u
0 0 0
0
= -I 3 :: -· ~ r+ I
"' w -· ::::J :::r n QJ tD "' S: CT
QJ tD ... tD n ::::J
:::r -N tD
()Q ~ ...
r+ :::r
tD
Q.
tD r+ tD n r+ -· 0
::::J
(.u .i,.. c.n 0 0 0 0 0
0 0
-t ! I w
0 :::r
0 2. 0 ...
3
< I»
C CD tn
ChloJ!'Ofol'III Cali'hon Chkwom,ethane Metby,lene Nitrate Otronh TW4~4 (ug/1) 'Fetr eftk>ride (u.gJl) a-rich (mg/I) .. (mgAI) (ovJj)' (ue/lll' I
6-Jun-00 0
2-Sep-00 0
28-Nov-OO 3.9
28-Mar-01 2260 1.02
20-Jun-01 3100 14.5
20-Sep-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 <l <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 <l <1 9.5 45
10-0ct-07 2500 1.5 <l <1 9.5 47
26-Mar-08 2800 1.6 <l <1 9.2 43
25-Jun-08 2500 1.5 <1 <1 10.8 42
10-Sep-08 2200 1.4 <1 <1 8.83 39
15-0ct-08 2500 2 <2 <2 10.1 44
4-Mar-09 2200 1.2 <1 <1 10.2 37
24-Jun-09 1800 1.2 <l <l 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
~Ql'Bl Carb Cbl•r0m:etllane ~ Narate €ltbwide TW4-4 'fetradtlvide €hl'O:ri6 (llg/f) tud): (odi) (us/Ii) {mgtl) (mglt)
17-Feb-10 1700 1 <1 <I 6.6 48
10-Jun-10 2000 1.2 <1 <I 7.6 35
16-Aug-10 2100 1.3 <1 <1 7.3 36
1 l-Oct-10 1700 1.3 <1 <1 7.1 38
23-Feb-l 1 1800 1.4 ND ND 7 41
1-Jun-11 1700 1.2 ND ND 7 35
17-Aug-ll 1500 ND ND ND 6.6 40
16-Nov-l l 1500 1 ND ND 7 39
23-Jan-12 1200 ND ND ND 7.1 38
6-Jun-12 1500 ND ND ND 7.1 43
4-Sep-12 1600 1.2 ND ND 7.1 39
3-0ct-12 1400 1 ND ND 7 38
ll-Feb-13 1460 1.12 ND ND 7.36 39
5-Jun-13 1330 ND ND ND 6.3 39.6
3-Sep-13 1380 ND ND ND 7.22 38.8
29-0ct-13 1360 5.3 ND ND 7.84 43.9
27-Jan-14 1260 3.88 ND ND 7.28 37.4
19-May-14 1220 5 ND ND 5.91 47.5
11-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
11-0ct-17 1290 ND ND ND 6.90 40.7
12-Mar-18 1160 ND ND ND 6.12 42.2
8-Jun-18 1050 ND ND ND 6.34 39.0
22-Aug-18 1030 ND ND ND 6.34 39.0
28-Nov-18 1140 ND ND ND 6.02 41.4
8-Mar-19 1050 ND ND ND 7.26 38.3
5-Jun-19 1070 ND ND ND 10.40 38.5
4-Sep-19 989 ND ND ND 6.32 39.8
11 Chloroform Carbon <Dhloromethane Methylene Nimtte Chloride II TW4-4 Tetrachloride <C:hlorid (ug/1) (,ul!/l1) {ug/1) (ul!/f.) (mg/I) (mg/I)
10-Dec-19 1140 ND ND ND 6.52 40.4
19-Feb-20 1100 ND ND ND 4.58 43.4
27-May-20 1140 ND ND ND 7.26 46.1
u,
Cl)
::I
co >
E ... 0 -0 ...
..2 .c 0
"11::1' I
"11::1' 3: I-
0 0 I!) 'V
0 0 0 'V
0 0 I!) C')
0 0 0 C')
0 0 I!)
C\l
0 0 0 C\l
(1J6n)
0 0 I!) ....
0 0 0 ....
0 0 I!)
0
oi-unr-e~
L~-das-cc
v~-oaa-a
c ~ -Jd'v'-~
60-1nr-9
90-PO·O~
vo-u·eir-v ~
Cblo1toform C h:on C&lo1'eme1hane Methyilene NJmte Cldmle TW4•5 ~ug/1) Vewadllvij {191) Cbhtrfde (mgft) (mg/I) (ueffi (11etf~,
20-Dec-99 29.5
15-Mar-00 49.0
2-Sep-00 124
29-Nov-OO 255
28-Mar-Ol 236
20-Jun-Ol 240
20-Sep-Ol 240
7-Nov-01 260
26-Mar-02 260
22-May-02 300
12-Sep-02 330
24-Nov-02 260
28-Mar-03 240
23-Jun-03 290
12-Sep-03 200
8-Nov-03 240
29-Mar-04 210
22-Jun-04 200
17-Sep-04 150
17-Nov-04 180
16-Mar-05 120
25-May-05 113 NA NA NA 3.7 NA
31-Aug-05 82.0 <2.5 5.8 <2.5 6 NA
l-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 <1 6.7 54
8-Nov-06 47.1 <1 <l <1 2.9 55
28-Feb-07 33.0 <l <l <l 7.8 57
27-Jun-07 26.0 <1 <l <1 7 45
15-Aug-07 9.2 <1 <1 <1 7.7 38
10-0ct-07 9.4 <l <1 <1 8.2 39
26-Mar-08 11.0 <l <l <l 7.4 36
25-Jun-08 9.3 <l <l <l 8.7 37
10-Sep-08 11.0 <l <1 <1 7.91 34
15-0ct-08 10.0 <l <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
1, Cttbo 1'!Iet& re ' Chi I' Clar ~e . -...•.
TW4-S mu Tetra 00 Chle • e a ·--
(~ (uQ/U (uglt) ~m?JI) (mgjl) (mg(l)
22-Dec-09 8.5 <1 <1 <l 7.5 41
25-Feb-10 13.0 <1 <1 <l 6.8 43
9-Jun-10 12.0 <l <1 <1 7.1 28
1 l-Aug-10 12.0 <l <1 <1 7 38
13-0ct-10 11.0 <1 <l <1 7.2 41
22-Feb-11 10.0 ND ND ND 7 34
26-May-l 1 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
1 l-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-15 13.8 ND ND ND 9.32 45.1
10-Jun-15 13.3 ND 1.07 ND 7.08 47.3
3-Sep-15 12.9 ND ND ND 8.1 52.2
28-0ct-15 11.0 ND ND ND 8.03 43.6
17-Mar-16 11.0 ND ND ND 10.2 44.7
26-May-16 13.6 ND ND ND 8.98 45.9
25-Jul-16 10.8 ND ND ND 8.49 44.6
26-0ct-16 10.8 ND ND ND 8.32 47.8
15-Mar-17 12.6 ND ND ND 8.49 44.7
15-Jun-17 14.6 ND ND ND 8.52 47.3
2-Aug-17 14.6 ND ND ND 8.52 48.6
10-0ct-17 13.8 ND ND ND 8.57 42.5
15-Mar-18 15.2 ND ND ND 8.36 51.2
13-Jun-18 13.9 ND ND ND 9.24 47.4
30-Aug-18 15.4 ND ND ND 7.34 54.7
12-Dec-18 15.6 ND ND ND 7.67 49.8
16-Mar-19 14.1 ND ND ND 7.38 47.6
13-Jun-19 15.8 ND ND ND 7.62 49.3
Chlorol!~rm Carbon <Cliloromethane Metliylene Nitrate Chloricle II TW4-S Te'trachloridt Chloride
II (Ug/1) (UP'nl (ug/1) (ue/1) (mg/I) (mg/I)
ll-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
l 1-Jun-20 15.4 ND ND ND 7.83 49.5
0 CJ1 0
.....
0 0
(ug/L)
.....
CJ1 0
I\)
0 0
I\)
CJ1 0
c..:> 0 0
c..:> CJ1 0
24-Jul-98 -t----t----+----+----+------1'-----+----1
19-Apr-01
14-Jan-04 -
10-0ct-06 1 I I / I I I I I
06-Jul-09 1 t I I I I I I I I
01-Apr-12 1 1 /I I I I I I I
27-0ec-14
22-Sep-17
18-Jun-20
15-Mar-23 _._ ___ _..__ ___ ..__ __ __.. ___ ~---~-----'-----'
-4 =E .s:i,
I (.11
0 :::r
0 "'I 0 -0 "'I
3
< m
C CD "'
Chloroform Carb• Cklorometh ne Methylene Nitl'afe Chloride TW4-6 (ug(l) Tetrachlmde (lig/1) Qlori e (mg/I) (mgtl) lu11LI:) (q/U
6-Jun-00 0
2-Sep-00 0
28-Nov-OO 0 ND
26-Mar-01 0 0.13
20-Jun-01 0 ND
20-Sep-01 4 ND
7-Nov-01 I 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
1-Dec-05 17.0 <1 1.3 <1 0.9 NA
9-Mar-06 31.0 <1 <1 <1 1.2 31
14-Jun-06 19.0 <1 <1 <1 1 30
20-Jul-06 I 1.0 <1 <1 <1 0.6 37
8-Nov-06 42.8 <1 <1 <1 1.4 65
28-Feb-07 46.0 <1 <1 <1 1.5 32
27-Jun-07 11.0 <1 <1 <l 0.6 38
15-Aug-07 18.0 <1 <1 <1 0.7 36
10-0ct-07 18.0 <1 <1 <l 0.8 38
26-Mar-08 52.0 <l <1 <l 1.1 33
25-Jun-08 24.0 <l <l <1 0.9 35
10-Sep-08 39.0 <1 <1 <1 1.14 35
15-0ct-08 37.0 <1 <1 <1 1.01 33
ll-Mar-09 81.0 <1 <1 <l 2.2 35
24-Jun-09 120 <l <1 <1 2.7 37
15-Sep-09 280 <1 <1 <1 5.0 37
22-Dec-09 250 <l <1 <1 6.1 41
25-Feb-10 1000 <1 <1 <l 1.6 45
10-Jun-10 590 <1 <1 <1 2.5 33
12-Aug-10 630 <1 <1 <1 3.9 31
13-0ct-10 420 <1 <l <1 4.3 41
23-Feb-l l 47 ND ND NU 0.7 40
Chloroform Ca:rboD Cim>r methan Mtthyle e j ,ate Chloride TW4-6 Tetrachlori e Cldoi,ide ' (ug/1) (.u.e/1) (ug/t) (uflll) (mg/I~ (q/1)
.to-May-I I 10 ND ND ND 0.3 42
17-Aug-ll 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
l l-Sep-12 6.9 ND ND ND 0.1 21
3-0ct-12 9.0 ND ND ND 0.2 41
13-Feb-13 6.9 ND ND ND 0.154 40.4
13-Jun-J 3 4.9 ND ND ND 0.155 37.9
5-Sep-13 5.9 ND ND ND 0.157 40.6
13-Nov-13 5.5 ND ND ND 1.52 40.2
29-Jan-14 5.7 ND ND ND 0.184 40.6
22-May-14 10.3 ND ND ND 0.312 37
14-Aug-14 202 ND ND ND 4.2 40
24-Sep-14 260 ND ND ND NIA NIA
29-0ct-14 723 ND ND ND 6.92 41.1
18-Mar-15 1180 ND ND ND 5.25 41.2
ll-Jun-15 1040 ND ND ND 5.87 41.6
10-Sep-15 1040 ND ND ND 6.75 47.0
29-0ct-15 843 ND ND ND 5.61 40.2
22-Mar-16 834 ND ND ND 6.79 42.0
8-Jun-16 486 ND ND ND 3.19 44.1
4-Aug-16 433 ND ND ND 3.85 42.2
26-0ct-16 301 ND ND ND 3.74 46.1
16-Mar-17 288 ND ND ND 3.15 42.1
21-Jun-l 7 239 ND ND ND 2.42 42.6
3-Aug-17 129 ND ND ND 1.71 42.9
l l-Oct-17 121 ND ND ND 1.71 37.6
20-Mar-18 159 ND ND ND 1.96 43.1
14-Jun-18 74.9 ND ND ND 1.48 40.2
5-Sep-18 53 .2 ND ND ND 1.18 44.0
12-Dec-18 37.0 ND ND ND 0.900 20.0
19-Mar-19 23.2 ND ND ND 0.755 41.0
13-Jun-19 15 .8 ND ND ND 0.484 38.1
ll-Sep-19 15 .8 ND ND ND 0.412 39.7
14-Dec-19 7.40 ND ND ND 0.244 45.7
17-Mar-20 6.93 ND ND ND 0.222 43.2
ll-Jun-20 4.86 ND ND ND 0.205 42.4
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0 0 0 ,-
0 0 (X)
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Chmro M'ID C btl> a nmethane Methi).ll'e Nitrate CfdGmte TW4-7, (ug/1} Tetr ride ( A> 11 Cbleri e (mg/I) (m,g;l) tuekt I Gul!.lt);
29-Nov-99 256
15-Mar-OO 616
2-Sep-00 698
29-Nov-00 684 1.99
28-Mar-01 747 2.46
20-Jun-Ol 1100 2.65
20-Sep-Ol 1200 3.38
8-Nov-01 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
1-Dec-05 2500 <50 <50 <50 5.3 NA
9-Mar-06 1900 <50 <50 <50 1 48
14-Jun-06 2200 <50 <50 <50 4.5 47
20-Jul-06 2140 <50 <50 <50 4.7 51
8-Nov-06 2160 1.5 <1 <l 4.6 49
28-Feb-07 1800 1.1 <1 <1 5 47
27-Jun-07 2600 1.5 <1 <1 5.1 45
14-Aug-07 2300 1.4 <1 <1 4.7 44
10-0ct-07 1900 1.2 <1 <1 4.7 45
26-Mar-08 2200 1.3 <1 <1 4.2 43
25-Jun-08 1800 1.3 <l <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
ll-Mar-09 1800 1.2 <l <1 3.7 35
24-Jun-09 1400 <1 <1 <1 3.8 37
15-Sep-09 1500 1.0 <1 <1 4.1 37
Cldor0. 'oflll Carken CW~:tJimue' M~l . Nitrate Qloride 1'W~1 (~ Tetii '81' (ugA (CJ O •• (mgJI) (mgl,f) 11 (u~ (W!/iJi}l
29-Dec-09 1300 <l <1 <l 4.2 37
3-Mar-10 1200 <1 <1 <1 3.8 36
10-Jun-10 1100 <l <1 <1 3.9 31
18-Aug-10 1500 1. I <l <1 3.9 36
13-0ct-10 1100 1.1 <1 <1 4 38
23-Feb-l 1 1300 ND ND ND 3.60 45
l-Jun-11 1200 ND ND ND 4.00 35
18-Aug-l l 1200 ND ND ND 4.10 37
29-Nov-l 1 1000 ND ND ND 3.80 37
l 9-Jan-12 1000 ND ND ND 3.90 37
14-Jun-12 790 ND ND ND 4.00 41
13-Sep-12 870 ND ND ND 3.80 40
4-0ct-12 940 ND ND ND 3.80 41
13-Feb-13 1080 3.51 ND ND 3.90 37.7
18-Jun-13 953 ND ND ND 4.04 39.3
12-Sep-13 1040 ND ND ND 4.17 36.4
14-Nov-13 1050 ND ND ND 4.13 37.2
5-Feb-14 946 5.41 ND ND 4.24 38.2
23-May-14 847 4.78 ND ND 4.19 37.7
27-Aug-14 857 ND 1.5 ND 2.90 39
30-0ct-14 926 ND ND ND 3.68 40.2
18-Mar-15 942 ND ND ND 4.25 40.4
11-Jun-15 950 ND ND ND 2.62 42.1
10-Sep-15 897 ND ND ND 4.72 46.7
29-0ct-15 847 ND ND ND 3.49 40.6
22-Mar-16 834 ND ND ND 4.43 42.4
8-Jun-16 909 ND ND ND 3.75 44.l
4-Aug-16 1000 ND ND ND 4.21 42.3
27-0ct-16 886 ND ND ND 4.33 45.8
21-Mar-17 986 ND ND ND 3.87 40.5
21-Jun-17 968 ND ND ND 4.15 43.3
4-Aug-17 1070 ND ND ND 4.20 44.7
11-0ct-17 884 ND ND ND 4.35 43.7
21-Mar-18 721 ND ND ND 3.96 44.5
14-Jun-18 751 ND ND ND 4.45 41.5
5-Sep-18 781 ND ND ND 4.34 48.5
13-Dec-18 838 ND ND ND 3.98 42.8
20-Mar-19 736 ND ND ND 4.01 41.3
19-Jun-19 862 ND ND ND 4.19 43.0
Ghlol'oform Carbon Chlorom~hane Methylene Nitrate Chloride Tw4i..7 Tetrachloride Chloride (ug/1) (ue/1) (ug/1) (ul!/1) ~gll) (lllg/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
12-Jun-20 864 ND ND ND 4.06 44.1
(ug/L)
..... I\) w .j::. 01 0) 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
24-Jul-98
19-Apr-01
14-Jan-04
10-0ct-06 I . ,..--4 =E .,:a.
I ......
0
~
I I I I 0 6-Jul-09 1 I -=i-... 0 -0 ... 3
< e!.
I I C 1-Apr-12i .t'i I I I I CD 0
~7-Dec-14
~2-Sep-17
18-Jun-20
15-Mar-23 _,__ ___ ___,_ ____ _.._ ___ ___. ____ __.._ ____ ._ ___ _,
Chloroform1 Cubfm ~ Met/hflme Nitrate Chloride TW4-.8 Tetrachloride -•1 ••
(ug/1) (ug/1) ,e (mg/I) ~m~) (~ I (otdi1)·
29-Nov-99 0
15-Mar-OO 21.8
2-Sep-00 102
29-Nov-OO 107 ND
26-Mar-01 116 ND
20-Jun-01 180 ND
20-Sep-01 180 0.35
7-Nov-01 180 ND
26-Mar-02 190 0.62
22-May-02 210 0.77
12-Sep-02 300 ND
24-Nov-02 450 ND
28-Mar-03 320 0.8
23-Jun-03 420 ND
12-Sep-03 66.0 ND
8-Nov-03 21.0 0.1
29-Mar-04 24.0 0.65
22-Jun-04 110 0.52
17-Sep-04 120 ND
17-Nov-04 120 ND
16-Mar-05 10.0 ND
25-May-05 <l NA NA NA 0.2 NA
31-Aug-05 1.1 <1 1.7 <1 <0.1 NA
30-Nov-05 <1 <1 <l <1 <0.1 NA
9-Mar-06 1.3 <1 2.1 <1 0.3 39
14-Jun-06 1.0 <1 1.8 <1 <0.1 37
20-Jul-06 <1 <1 <l <1 0.1 39
8-Nov-06 <1 <1 <l <1 <0.1 40
28-Feb-07 2.5 <1 <1 <1 0.7 39
27-Jun-07 2.5 <1 <1 <1 0.2 42
15-Aug-07 1.5 <l <1 <1 <0.1 42
10-0ct-07 3.5 <l <l <1 0.5 43
26-Mar-08 <1 <l <1 <1 0.1 46
25-Jun-08 <1 <l <1 <1 <0.05 45
10-Sep-08 <l <l <1 <1 <0.05 39
15-0ct-08 <l <1 <l <1 <0.05 44
4-Mar-09 <1 <l <1 <1 <0.1 42
24-Jun-09 <1 <l <1 <1 <0.1 44
15-Sep-09 <1 <1 <1 <1 <l 44
Cld.oro'form Carbo CfdGFGmetJl M~en Nitrate Chle>:llide TW4-8 ~-tF Morid Cld'O,mle (ug/t, (wrtll\ ' gffl'. ht~): (mg/I) (mg/I)
II
17-Dec-09 <1 <1 <1 <1 <0.1 51
24-Feb-10 <l <1 <l <1 <0.1 57
9-Jun-10 <l <1 <1 <1 <0.1 42
ll-Aug-10 <1 <1 <1 <1 <0.1 45
5-0ct-10 <1 <1 <l <1 <0.1 46
16-Feb-ll ND ND ND ND ND 52
25-May-11 ND ND ND ND 0.1 45
16-Aug-ll 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
11-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
l 1-0ct-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 Ca"Tbon Cblol'omefh ne Methylene Nit-rate Chloride TW4•8 (ug/1>, Tetrachloride (ug/1) €bloride (mg/I) (mg/1) (tue/1) (u~)
19-Jun-19 96.0 ND ND ND I.IO 56.5
12-Sep-19 75.4 ND ND ND 0.999 52.0
18-Dec-19 84.4 ND ND ND 1.21 60.1
18-Mar-20 55.0 ND ND ND 1.04 53.8
12-Jun-20 53.8 ND ND ND 1.06 56.9
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0 0 0 ..-
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0 0 "<t"
0 0 C\I
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TW4-9 €hloro1'0FIB T~uacW · · Otil'~'Re OblQmfe Nitra1e ~ide
(ug/1) {U1'f11), {uglt) (ud"> (mwJ) (ol§l)J)
20-Dec-99 4.2
15-Mar-00 1.9
2-Sep-00 14.2
29-Nov-OO 39.4 ND
27-Mar-01 43.6 ND
20-Jun-01 59.0 0.15
20-Sep-Ol 19.0 0.4
7-Nov-01 49.0 0.1
26-Mar-02 41.0 0.5
22-May-02 38.0 0.65
12-Sep-02 49.0 0.2
24-Nov-02 51.0 0.6
28-Mar-03 34.0 0.6
23-Jun-03 33.0 0.8
12-Sep-03 32.0 1.1
8-Nov-03 46.0 1.1
29-Mar-04 48.0 0.82
22-Jun-04 48.0 0.75
17-Sep-04 39.0 0.81
17-Nov-04 26.0 1.2
16-Mar-05 3.8 1.3
25-May-05 1.2 NA NA NA 1.3 NA
31-Aug-05 <1 <1 2.9 <1 1.3 NA
1-Dec-05 <1 <1 <1 <1 1.3 NA
9-Mar-06 <1 <l 2.6 <l 1.5 38
14-Jun-06 <l <1 2.7 <l 1.5 39
20-Jul-06 <1 <1 <1 <1 0.9 41
8-Nov-06 <l <1 <1 <l 0.7 44
28-Feb-07 <l <l <l <1 0.6 44
27-Jun-07 21 <1 <1 <1 1.3 42
15-Aug-07 9.5 <1 <1 <1 1.8 38
10-0ct-07 8.7 <1 <1 <l 2 40
26-Mar-08 1.3 <1 <l <1 2.1 35
25-Jun-08 1.0 <1 <l <1 2.3 35
10-Sep-08 <I <1 <l <l 2.79 28
15-0ct-08 <1 <1 <l <1 1.99 58
4-Mar-09 <1 <1 <1 <1 2.5 30
24-Jun-09 <I <1 <1 <1 2.3 30
15-Sep-09 <1 <1 <1 <1 2.5 30
fflllorofenn Carl: Chloro :thne Mdlylen Niff3te Chlwi'lfe TW4-9 < WI) Tetmdtmrid'e ( g!l) Chlmicle (ragtl} (mgffl ~} fimA)
17-Dec-09 <1 <1 <1 <1 1.7 37
23-Feb-10 <1 <1 <1 <1 1.7 47
9-Jun-10 <1 <1 <1 <1 1.5 33
11-Aug-10 <1 <l <1 <1 1.2 40
6-0ct-10 <l <l <1 <1 1.8 34
17-Feb-1 l ND ND ND ND 1.3 41
25-May-11 ND ND ND ND 3.4 38
16-Aug-11 ND ND ND ND 4 21
7-Dec-11 ND ND ND ND 2.3 38
18-Jan-12 ND ND ND ND 2.3 28
31-May-12 ND ND ND ND 4 23
30-Aug-12 ND ND ND ND 3.9 22
3-0ct-12 ND ND ND ND 3.8 21
7-Feb-13 ND ND ND ND 4.12 20.6
30-May-13 ND ND ND ND 4.49 21.4
5-Sep-13 ND ND ND ND 4.03 22.7
7-Nov-13 ND ND ND ND 4.87 23.6
29-Jan-14 ND ND ND ND 4.36 22
21-May-14 6.9 ND ND ND 3.44 24
14-Aug-14 46.9 ND ND ND 2.7 27
29-0ct-14 101 ND ND ND 4.27 25
12-Mar-15 53.5 ND ND ND 3.28 29.5
ll-Jun-15 35.1 ND ND ND 1.83 35.3
3-Sep-15 48.2 ND ND ND 1.44 39.5
28-0ct-15 68.4 ND ND ND 2.89 29.2
17-Mar-16 74.3 ND ND ND 2.51 33.6
8-Jun-16 76.2 ND ND ND 2.16 35.1
3-Aug-16 76.8 ND ND ND 2.11 33.6
26-0ct-16 76 ND ND ND 2.24 37.4
16-Mar-17 113 ND ND ND 2.18 34.5
21-Jun-17 113 ND ND ND 1.92 35.9
3-Aug-17 118 ND ND ND 1.90 37.0
11-0ct-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
II Carbon ~thylene Chlorof-orm Chlorometbane Nitrate Chloride
II TW4-9 (ug/1) Tetrachloride (ugtl) Chloride (mg/I~ (mg/I~ {u211;) '(U2/l)'
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
12-Jun-20 55.1 ND ND ND 0.990 39.5
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Chloroform Can.'Gtl C . Metlly,le e Nitram Cllhtride W4-@ Tetm orm I 11 -.• -
(ug/1) liJ ' (ugJI) (m'WI) (mg,11) {WIR}i (ud,
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
1-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 <1 1 5.1 54
15-Aug-07 660 <1 <1 1 7.3 59
10-0ct-07 470 <1 <1 1 6.7 59
26-Mar-08 620 <1 <l 1 7.3 55
25-Jun-08 720 <1 <1 1 9.91 58
10-Sep-08 680 <1 <1 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 <1 <1 1 9.8 62
15-Sep-09 9f0 <1 <1 1 8.1 51
22-Dec-09 300 <l <1 <1 3.5 51
3-Mar-10 460 <l <1 <1 5 49
10-Jun-10 220 <l <1 <1 1.6 42
12-Aug-10 100 <l <1 <1 0.8 38
13-0ct-10 1100 <1 <1 <1 11 52
23-Feb-ll 620 ND ND ND 9 62
l-Jun-11 280 ND ND ND 3.3 42
Chloroform Carbon Chlff(fflNthane Methp, Ni'ffa e Chloride TW4-10: (ugl)) T 11 tdmide ( wJl) ride (mg/.11) (mw)) (witl1 (mdfl
17-Aug-11 180 ND ND ND 1.9 41
16-Nov-l 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.l
13-Jun-13 486 ND ND ND 5.6 51.5
12-Sep-13 1160 ND ND ND 13.0 67.9
14-Nov-13 1380 ND ND ND 16.0 70.9
5-Feb-14 1260 5.16 ND ND 16.8 73
23-May-14 1110 ND ND ND 13.9 77.3
27-Aug-14 1060 ND 1.5 ND 9.8 74
30-0ct-14 1220 ND ND ND 13.2 75.2
18-Mar-15 1210 ND ND ND 15.0 78.6
ll-Jun-15 1240 ND ND ND 11.4 75
10-Sep-15 1280 ND ND ND 14.0 89.5
29-0ct-15 1350 ND ND ND 13.5 79.9
22-Mar-16 1430 ND ND ND 17.3 84.l
8-Jun-16 1510 ND ND ND 14.9 89.5
4-Aug-16 1500 ND ND ND 14.9 85.3
27-0ct-16 1290 ND ND ND 14.8 84.4
21-Mar-17 1260 ND ND ND 13.0 74.6
21-Jun-17 1140 ND ND ND 13.0 73.1
4-Aug-17 1320 ND ND ND 13.4 77.0
11-0ct-17 1150 ND ND ND 12.9 70.0
21-Mar-18 1240 ND ND ND 11.1 72.7
14-Jun-18 914 ND ND ND 11.2 64.5
5-Sep-18 911 ND ND ND 10.1 73.5
13-Dec-18 1070 ND ND ND 10.6 63.5
20-Mar-19 869 ND ND ND 9.34 59.3
19-Jun-19 799 ND ND ND 8.86 58.7
12-Sep-19 734 ND ND ND 7.79 55.8
18-Dec-19 768 ND ND ND 6.89 62.0
18-Mar-20 798 ND ND ND 7.83 53.5
12-Jun-20 928 ND ND ND 8.13 60.1
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0 ,....
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0 0 co ....
0 0 -.:t" ....
0 0 C\J ....
0 0 0 ....
0 0 00
0 0 co
(1J6n)
0 0 C\J
0
oi-unr-B~
L~-das-ii
v~-oaa-a
G ~ -JdV-~
60-1nr-9
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II Chlorofom1 Carbon Cl6romethane et" itrate ir'~•-=de II
II TW4•11 Tetracblol'kle ,,,...r-
(ug/1), {~l (ulM Oltal'ide (ug;lry (mg/I) €mgt10
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 <IO 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 <l 1.6 10.1 54
27-Jun-07 3800 1.6 <1 1.1 10.6 53
15-Aug-07 4500 1.7 <1 1.1 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 <1 <1 7.28 46
10-Sep-08 900 <1 <1 <1 7.93 42
15-0ct-08 1000 <2 <2 <2 9.46 47
1 l-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 <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
Chlo.rt ,r CCa!"I CAiero _., Methyl Nitrate Cblol'ide ' 'I TW+ll Tetracblori e
I (ug/1) (ug/1) Chloride (ug/J} (mg/1) (mg/I) i (ud)
17-Aug-11 820 ND ND ND 7.1 48
16-Nov-11 1500 ND ND ND 7.1 46
24-Jan-12 610 ND ND ND 6.8 43
13-Jun-12 660 ND ND ND 6.7 52
13-Sep-12 740 ND ND ND 3 49
4-0ct-12 730 ND ND ND 7 50
13-Feb-13 867 3.23 ND ND 6.83 47.3
18-Jun-13 788 ND ND ND 7.42 49.7
12-Sep-13 865 ND ND ND 7.8 46.6
13-Nov-13 874 ND ND ND 8.01 46.7
5-Feb-14 785 5.19 ND ND 8.47 48.5
23-May-14 751 ND ND ND 6.92 51.6
27-Aug-14 719 ND 1.2 ND 5.4 48
29-0ct-14 803 ND ND ND 7.33 56.4
9-Mar-15 2450 1.24 ND ND 8.72 49.8
8-Jun-15 2710 ND ND ND 8.48 62.2
31-Aug-15 1120 ND 1.62 ND 9.61 73.1
19-0ct-15 2730 ND ND ND 7.5 55.3
9-Mar-16 2660 1.2 ND ND 7.13 55.5
23-May-16 3340 2.19 ND ND 7.81 56.4
25-Jul-16 3200 ND ND ND 8.83 55.3
12-0ct-16 3180 1.58 ND ND 8.92 57.2
8-Mar-17 3310 1.71 ND ND 8.12 49.8
13-Jun-17 3370 1.83 ND ND 7.92 51.4
26-Jul-17 3290 1.81 ND ND 7.78 51.0
ll-Oct-17 2880 1.48 ND ND 7.79 49.7
12-Mar-18 3090 1.82 ND ND 7.89 54.0
8-Jun-18 2800 1.34 ND ND 7.51 52.6
22-Aug-18 3050 1.47 ND ND 7.15 53.3
28-Nov-18 2930 1.33 ND ND 6.85 45.4
8-Mar-19 2820 1.48 ND ND 7.50 46.8
5-Jun-19 2970 1.52 1.40 ND 8.30 45.3
4-Sep-19 2790 ND ND ND 7.15 48.8
10-Dec-19 3250 ND ND ND 7.14 49.0
19-Feb-20 2990 ND ND ND 7.07 51.9
27-May-20 2810 1.37 ND ND 7.56 48.6
U) a,
.2 cu >
E i... 0 -e
.2 .c
CJ ,... ,...
I -~ 3: I-
0 0 0 I'-
0 0 0 co
0 0 0 lO
0 0 0 v
0 0 0 ('t)
(1J6n)
0 0 0 C\J
0 0 0 ,-
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60-1nr-9
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C:hlorofonn Carb Cblorometh Meiti,',l,ne Nitrate Qderide
1 TW4-12 {ug/1) Tetracbloride (UgA!} Chltlrid.e (mg/I~ (mg/4~ I (umb II i (11f!A) ' 12-Sep-02 2 2.54
24-Nov-02 0 2.2
28-Mar-03 0 1.9
23-Jun-03 0 1.8
12-Sep-03 0 1.8
9-Nov-03 0 1.6
29-Mar-04 0 1.58
22-Jun-04 0 1.4
17-Sep-04 0 1.24
17-Nov-04 0 1.5
16-Mar-05 0 1.4
25-May-05 <1 NA NA NA 1.6 NA
31-Aug-05 <1 <1 5.8 <1 1.5 NA
1-Dec-05 <1 <1 1.9 <2 1.4 NA
9-Mar-06 <l <1 2.6 <l 1.3 19
14-Jun-06 <l <1 1.4 <l 1.4 16
20-Jul-06 <1 <1 <l <l 1.4 16
8-Nov-06 <1 <1 <1 <1 1.4 16
28-Feb-07 <1 <l <1 <1 1.5 16
27-Jun-07 <1 <l <1 <1 1,5 18
15-Aug-07 <1 <l <1 <1 1.4 29
10-0ct-07 <1 <l <1 <1 1.4 16
26-Mar-08 <1 <l <l <1 1.6 16 1,
25-Jun-08 <1 <1 <l <1 2.69 19
10-Sep-08 <1 <1 <l <1 2.65 18
15-0ct-08 <1 <1 <1 <1 2.47 22
4-Mar-09 <l <1 <l <1 2.4 23
24-Jun-09 <1 <1 <1 <1 3.8 22
15-Sep-09 <l <1 <l <1 5.1 22
16-Dec-09 <l <1 <l <1 3.6 23
23-Feb-10 <l <1 <l <1 4 22
8-Jun-10 <l <1 <1 <1 11 29
10-Aug-10 <1 <1 <l <1 9 35
5-0ct-10 <1 <1 <1 <1 8 31
15-Feb-11 ND ND ND ND 6.5 31
25-May-11 ND ND ND ND 7 32
16-Aug-ll ND ND ND ND 6.8 31
15-Nov-ll ND ND ND ND 8 30
17-Jan-12 ND ND ND ND 7.7 28
Chloroform tarb@n Cbloxemedtane-Methylene Nitrate fflllom:le TW4-12 ,, ~ Chloride (ugll) ,(~4) (qglt) fud) (mg/I) (mg/I
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-19 ND ND ND ND 10.1 50.8
13-Jun-19 ND ND ND ND 8.31 55.3
11-Sep-19 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
10-Jun-20 ND ND ND ND 4.95 51.7
19-Apr-01
14-Jan-04
10-0ct-06
6-Jul-09
1-Apr-12
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23
9 0
• •• :
•• •• ••
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0
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~J'01r , Carbo Cblormeft.'lflfte ~n N•te Cbl~t?ide TW4-13 Tetradll.mde ,f"ll ~ ..
(u-) tlf/i) ----,._---{;m-(mgM)
II l:u@tfJ (mdl),
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
l 7-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 <l <l 3.1 <l 4.60 NA
l-Dec-05 <l <1 <l <l 4.30 NA
9-Mar-06 <l <l 1.7 <l 4.20 67.0
14-Jun-06 <l <l 1.4 <l 4.90 66.0
20-Jul-06 <1 <l <1 <I 4.30 65.0
8-Nov-06 <1 <l <I <I 0.80 33.0
28-Feb-07 <l <l <I <1 4.00 59.0
27-Jun-07 <l <1 <1 <I 4.60 59.0
15-Aug-07 <1 <l <l <1 4.40 58.0
10-0ct-07 <1 <1 <1 <1 4.10 58.0
26-Mar-08 <1 <l <1 <l 3.80 54.0
25-Jun-08 <1 <l <I <1 4.24 58.0
10-Sep-08 <1 <1 <I <l 4.26 50.0
15-0ct-08 <1 <l <1 <l 4.63 58.0
4-Mar-09 <1 <l <l <l 3.70 58.0
24-Jun-09 <1 <1 <I <1 1.20 57.0
15-Sep-09 <1 <1 <1 <1 4.70 63.0
16-Dec-09 <1 <1 <1 <l 4.10 60.0
24-Feb-10 <1 <l <l <1 4.30 53.0
8-Jun-10 <1 <1 <1 <1 5.20 52.0
10-Aug-10 <l <1 <1 <l 5.60 55.0
5-0ct-10 <1 <1 <l <1 5.80 55.0
15-Feb-l l ND ND ND ND 5.50 60.0
25-May-11 ND ND ND ND 5.40 56.0
16-Aug-11 ND ND ND ND 5.20 60.0
15-Nov-l 1 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
Chloroform (arbon Clll9rometha Met,byJene .Nitl'ate Chloride 11 TW4-13 Tetrachloride Chlorid (ugAI) (Md) (uw,f) (ud) (~ (mgll)
7-Feb-13 ND ND ND ND 6.31 59.3
29-May-13 ND ND ND ND 6.84 56
29-Aug-13 ND ND ND ND 7.16 63.5
6-Nov-13 ND ND ND ND 6.48 58.5
22-Jan-14 ND ND ND ND 7.09 63.1
21-May-14 ND ND ND ND 5.99 56.1
13-Aug-14 ND ND ND ND 4.80 62
23-0ct-14 ND ND ND ND 6.28 66.1
ll-Mar-15 ND ND ND ND 7.09 66.4
10-Jun-15 ND ND ND ND 6.32 70.3
2-Sep-15 ND ND ND ND 5.70 76.5
21-0ct-15 ND ND ND ND 5.78 65.5
16-Mar-16 ND ND ND ND 7.97 69.4
25-May-16 ND ND ND ND 5.87 71.8
28-Jul-16 ND ND ND ND 6.14 69.3
19-0ct-16 ND ND ND ND 6.20 70.9
15-Mar-17 ND ND ND ND 6.05 66.0
15-Jun-17 ND ND ND ND 6.49 70.4
2-Aug-17 ND ND ND ND 6.15 70.5
10-0ct-17 ND ND ND ND 6.17 60.9
14-Mar-18 ND ND ND ND 5.76 71.0
12-Jun-18 ND ND ND ND 6.24 65.0
29-Aug-18 ND ND ND ND 5.13 73.7
30-Nov-18 ND ND ND ND 5.29 64.5
16-Mar-19 ND ND ND ND 5.74 61.6
13-Jun-19 ND ND ND ND 6.56 65.4
13-Sep-19 ND ND ND ND 5.19 65.3
14-Dec-19 ND ND ND ND 5.17 68.7
17-Mar-20 ND ND ND ND 5.50 63.9
1 l-Jun-20 ND ND ND ND 5.96 62.7
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-19
Mar-20 Jun-20
0
' .
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• I
0
0
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0
0
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0
0
0
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Chl91i'ofornt Carboo t::;bloirwmth oe MetJ¥eue Nitrate Qaferide II TW4-14 Tetrachl~e CJ oride (ugll) (wiJU (ugM?, Cllfl/1 £mgl)) (mg4)
8-Nov-06 <l <l <l <l 2.40 37.0
28-Feb-07 <l <l <l <l 2.30 38.0
27-Jun-07 <1 <l <l <l 1.40 38.0
15-Aug-07 <l <1 <1 <l I.IO 36.0
IO-Oct-07 <1 <1 <1 <l 0.80 36.0
26-Mar-08 <l <l <1 <l 0.04 57.0
25-Jun-08 <l <l <l <1 1.56 35.0
10-Sep-08 <l <l <1 <l 1.34 34.0
15-0ct-08 <1 <l <l <l 0.76 40.0
4-Mar-09 <1 <1 <l <1 1.60 35.0
24-Jun-09 <1 <1 <l <l 1.40 36.0
15-Sep-09 <1 <l <l <l 1.50 38.0
16-Dec-09 <l <l <l <l 1.40 34.0
3-Mar-10 <1 <1 <l <l 2.50 33.0
8-Jun-10 <l <l <l <l 2.90 49.0
IO-Aug-IO <1 <l <l <l 2.80 35.0
6-0ct-10 <l <l <1 <l 2.90 29.0
15-Feb-l 1 ND ND ND ND 1.80 25.0
16-Aug-11 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.IO 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 3.1 8 2.45 43.6
28-Jul-16 5.00 ND ND 1.80 2.88 42.4
Chloroform Carbon Chloromethane Methylene itrat Chloride 'FW4-14 tug/I) Tetrachloride (ug/1) Ohlollide (mg/I) (mg/I) (Ju2/1} (uS!/1)
20-0ct-16 7.02 ND ND 1.59 2.86 45.6
15-Mar-17 6.45 ND ND ND 4.36 45.4
15-Jun-17 6.85 ND ND ND 5.12 46.9
2-Aug-17 6.14 ND ND ND 4.84 46.4
10-0ct-17 6.13 ND ND ND 4.73 42.5
15-Mar-18 5.80 ND ND ND 5.67 51.5
13-Jun-18 5.12 ND ND ND 6.36 46.9
30-Aug-18 4.76 ND ND ND 5.34 54.1
12-Dec-18 4.41 ND ND ND 5.85 48.7
16-Mar-19 4.08 ND ND ND 6.16 48.7
13-Jun-19 4.18 ND ND ND 5.86 48.3
1 l-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
11-Jun-20 2.87 ND ND ND 6.57 47.6
0 0 cci
0 0 r-..:
0 ~
(0
0 0
LO
0 0 -<i
0 0 (')
(1J6n)
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C\J
0 0 0 0 ci
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I
Chlotoform Ca Chloro etha M lene Nibate Chloride MW-26 Tmadd Ide Qloi'itle (ug/1) fuea) (ug/lO: (wrJI' {mgti~ (mw,f)
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
I-Dec-05 1000 <50 <50 <50 0.3 NA
9-Mar-06 1100 <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 <1 <1 13 0.4 49
15-Aug-07 1400 <1 <l 36 I 57
10-0ct-07 2000 <l <1 14 0.6 57
26-Mar-08 930 <l <1 40 0.1 49
25-Jun-08 1300 <1 <l 53 0.56 57
10-Sep-08 630 <1 <l 24 0.24 44
15-0ct-08 1700 <l <l 100 0.65 64
4-Mar-09 950 <1 <l 51 0.4 49
24-Jun-09 410 <l <l 12 0.2 48
15-Sep-09 850 <1 <l 30 O.I 46
14-Dec-09 1100 <1 <l 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 <1 <l 21 0.6 49
11-0ct-10 970 <1 <1 6.5 0.7 65
23-Feb-ll 450 ND ND 3.6 0.5 57
-Ow&o Me1hylene
MW-26 Cb1oroform Tet .. -... Ch~r eltane Chhmde Nitrate Chloride
(ugM) .... e (ug/1) (mg/lJ (mg/I) (aw/iii\· (q/1).
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
11-Feb-13 2120 ND ND 9.34 2.27 81.9
5-Jun-13 4030 ND ND 52.4 2.11 77.9
3-Sep-13 2940 ND ND 33.2 1.18 60.5
29-0ct-13 1410 ND ND 4.03 1.38 72.3
27-Jan-14 1400 ND ND 13.8 0.549 59.4
19-May-14 1960 ND ND 15.4 0.928 53.4
11-Aug-14 2120 ND 8.7 26 0.7 59
21-0ct-14 2090 ND ND 23.2 0.934 60.1
9-Mar-15 1980 ND ND 27.4 0.732 56.5
8-Jun-15 1980 ND ND 11.2 0.419 62
31-Aug-15 2350 ND 4.05 11.6 0.684 69.6
19-0ct-15 2680 ND 1.32 8.28 0.991 62.6
9-Mar-16 2650 ND 1.32 4.66 1.45 68.3
23-May-16 2220 ND ND 4.57 1.12 66.2
25-Jul-16 3190 ND ND 7.81 1.57 66.4
12-0ct-16 2510 ND ND 4.31 1.18 66.2
8-Mar-17 1290 ND ND 7.65 0.768 58.4
13-Jun-17 2450 ND ND 7.59 0.922 64.3
26-Jul-17 1230 ND ND 5.26 1.56 61.4
11-0ct-l 7 2570 ND ND 7.83 1.18 62.2
12-Mar-18 1210 ND ND 2.14 1.57 60.3
8-Jun-18 1870 ND ND 9.19 0.901 58.7
22-Aug-18 1680 ND ND ND 2.80 91.4
28-Nov-18 1480 ND ND ND 1.96 85.5
8-Mar-19 1110 ND ND 2.20 1.85 69.9
5-Jun-19 1280 ND ND 1.19 2.83 80.7
4-Sep-19 1360 ND ND 1.93 3.08 76.2
10-Dec-19 1390 ND ND 1.78 0.977 83.2
19-Feb-20 1100 ND ND ND 1.17 88.9
27-May-20 1610 ND ND 3.92 2.93 77.6
.----......----.-----.----.---~---,------,-----.------,-€c-rev,J-9 ~
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vo-uer-v~
~Q-Jd'v'-6 ~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 LO 0 LO 0 LO 0 LO 0 LO 'st 'st C') C') C\J C\J .... ....
(1J6n)
Chlorof onn Carhu Cllvom.ethane hylen Nitrate Cid&.
TW4-16 Tetr eh:km QI .
(bg/1) (JlwE\ (ngli) (-1), (mg/I) (mg(j)
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 <1 1.1 21 3 60
14-Jun-06 13 <1 2.4 8.9 1.9 55
20-Jul-06 5.2 <1 <1 2.7 2.7 60
8-Nov-06 13.6 <1 <1 9.2 5.6 62
28-Feb-07 8.7 <1 <l 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 SA 66
10-0ct-07 1.4 <1 <1 <1 4.4 69
26-Mar-08 11 <l <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 <1 <1 6.6 9.82 89
4-Mar-09 <l <1 <1 <1 9.6 78
24-Jun-09 <l <l <l <1 8.9 76
15-Sep-09 <1 <1 <1 <1 8.8 79
17-Dec-09 <1 <1 <1 <1 5.2 76
24-Feb-10 <1 <1 <l <1 4.2 77
9-Jun-10 2.1 <1 <1 <1 4.7 64
24-Aug-10 4.3 <1 <l <1 4.6 72
6-0ct-10 3 <1 <1 <1 3.3 72
22-Feb-Il 15 ND ND ND 7 86
26-May-ll 16 ND ND ND 5 81
17-Aug-ll 9.2 ND ND ND 1.7 63
16-Nov-11 ND ND ND 1.4 0.4 38
18-Jan-12 ND ND ND 1.7 0.1 48
Chlonform C•h Chloromethane Methyl Nitrate Chforide TW4 .. 16 Te& mlodde .CJdo • (ug/1) (ad); (ng/tt) Jilldf) (mgtl) (mflll}
31-May-12 ND ND ND ND ND 53
30-Aug-12 ND ND ND ND ND 59
3-0ct-12 ND ND ND 3 ND 53
7-Feb-13 ND ND ND 3 ND 58.1
30-May-13 ND ND ND 4.21 ND 49.8
5-Sep-13 ND ND ND ND ND 54.4
7-Nov-13 13.4 ND ND ND 1.37 56.6
29-Jan-14 6.9 ND ND ND 3.16 66.8
22-May-14 14.6 ND ND ND 4.94 80.7
14-Aug-14 229 ND ND ND 5.1 80
24-Sep-14 371 ND ND ND NIA NIA
29-0ct-14 387 ND ND ND 8.40 92.1
12-Mar-15 153 ND ND ND 4.30 65.3
l 1-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
l l-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
l 9-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 ND ND ND 3.91 76.2
12-Jun-20 141 ND ND ND 4.44 79.7
"' Cl) ::::,
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0 0 (0
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0 0 ... 0
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v~-oaa-a
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60-1nr-9
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Chlo~oform Qlrb D C D :edlane M~ene Nitrate ~ MW-32 Te ehlomle Chh>dd (uglt) (ue'A)J (og/1) l~ I (mg;ll) ( ~
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 <1 <1 <1 <0.1 32
27-Jun-07 <1 <1 <1 <1 <0.1 32
15-Aug-07 <1 <1 <l <1 <0.1 31
10-0ct-07 <1 <1 <1 <1 <0.1 32
26-Mar-08 <1 <1 <1 <1 <0.1 31
25-Jun-08 <1 <1 <1 <1 <0.05 29
10-Sep-08 <1 <1 <1 <1 <0.05 30
15-0ct-08 <1 <1 <1 <1 <0.05 26
4-Mar-09 <1 <1 <l <1 <0.1 30
24-Jun-09 <1 <1 <l <1 <0.1 31
15-Sep-09 <1 <1 <l <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-ll ND ND ND ND ND 40
25-May-l l ND ND ND ND ND 31
16-Aug-11 ND ND ND ND ND 33
6-Dec-11 ND ND ND ND ND 32
C.blorofonn Carbo Cltlerometlmne Mettllt1 . e itrate Chloride MW-32 (ug/1) Tctraclderkle (uw,I} Chlo e (mg/I) (mg/I) (u/1) (:WlA)
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
1 l-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
12-Jun-20 ND ND ND ND ND 35.6
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(1J6n)
co 0
(0
0
C\I 0 0
Chlo11oform Carb4n Cklvomdh M~tlaJI e Nitrate 0 ri. TW4-18 1' traddfflde CJrhr •
(ug'/1) tu,u/0 (vwl,) (\'.UlJI') {mg/I) (mgff)
12-Sep-02 440 1.49
24-Nov-02 240 13.3
28-Mar-03 160 13.1
23-Jun-03 llO 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.I
25-May-05 29.8 NA NA NA 12.9 NA
31-Aug-05 39 <l 2.8 <l 13.3 NA
1-Dec-05 14 <1 1.1 <l 7.3 NA
9-Mar-06 12.0 <1 1.1 <I 5.9 5.9
14-Jun-06 12.0 <1 1.6 <I 4.7 35
20-Jul-06 10.8 <1 2.7 <I 6.1 35
8-Nov-06 139 <1 <l <1 8.7 34
28-Feb-07 9.2 <1 <1 <1 5.1 30
27-Jun-07 8.0 <1 <1 <1 4.9 28
15-Aug-07 8.9 <1 <1 <1 5 32
10-0ct-07 7.4 <1 <l <l 4.4 27
26-Mar-08 6.4 <l <l <1 0.7 23
25-Jun-08 5.7 <l <1 <l 4.55 23
10-Sep-08 8.0 <l <1 <1 4.68 26
15-0ct-08 9.4 <l <1 <1 5,15 30
4-Mar-09 11.0 <1 <1 <l 5.2 29
24-Jun-09 16.0 <1 <1 <1 6.2 30
15-Sep-09 13.0 <1 <1 <1 5.9 26
22-Dec-09 8.2 <1 <1 <1 5.4 30
24-Feb-10 69.0 <1 <1 <l 5.1 41
9-Jun-10 29.0 <1 <l <1 9 35
12-Aug-10 29.0 <1 <1 <1 9 37
13-0ct-10 30.0 <1 <1 <1 10 50
22-Feb-ll 39.0 ND ND ND 10 52
26-May-11 26.0 ND ND ND 9 36
17-Aug-ll 29.0 ND ND ND 4.6 23
7-Dec-ll 28.0 ND ND ND 6.3 23
19-Jan-12 25.0 ND ND ND 4.4 18
Cid I', €al'b:o Cbto,rometha , thyle e Nifratte Cid ride TW4-18 orm Tetradtlori , e :0 de (ugt.l) (dB) (ug!Q fu/0 (mg/A) (mg/l)
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-13 44.3 ND ND ND 14.2 37.1
30-Jan-14 38.9 ND ND ND 12.8 40.9
22-May-14 34.8 ND ND ND 12.2 47
14-Aug-14 32.8 ND ND ND 9.8 49
28-0ct-14 33.0 ND ND ND 11.1 40.8
12-Mar-15 32.0 ND ND ND 11.7 41.6
11-Jun-15 30.5 ND ND ND 9.69 43.5
3-Sep-15 28.7 ND ND ND 15.7 47.6
28-0ct-15 52.9 ND ND ND 6.24 39.4
17-Mar-16 56.6 ND ND ND 5.96 40.7
8-Jun-16 60.0 ND ND ND 5.43 43.8
3-Aug-16 56.3 ND ND ND 5.79 40.7
26-0ct-16 60.1 ND ND ND 5.24 43.9
16-Mar-17 62.0 ND ND ND 4.47 39.4
20-Jun-17 63.8 ND ND ND 4.5 41.6
3-Aug-17 62.8 ND ND ND 4.24 40.4
10-0ct-17 62.9 ND ND ND 4.43 37.1
15-Mar-18 62.3 ND ND ND 4.32 44.3
13-Jun-18 59.9 ND ND ND 4.09 39.5
30-Aug-18 56.2 ND ND ND 3.51 45.6
13-Dec-18 57.6 ND ND ND 3.60 38.2
19-Mar-19 52.8 ND ND ND 3.85 37.6
19-Jun-19 54.2 ND ND ND 4.01 39.5
11-Sep-19 56.2 ND ND ND 3.25 36.8
18-Dec-19 62.0 ND ND ND 3.02 42.7
18-Mar-20 57.0 ND ND ND 3.71 39.4
12-Jun-20 58.2 ND ND ND 3.62 41.4
ti)
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E ... 0 0 ...
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0 LO "Q"
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0 0 C')
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Chi ftmn Carbon Ottor. ·etltan 1 M ~ e Nitra1ie ChJerkfe
II TW4-19 (uw}) Te: cheride (ugM)) Qlmide ( gff) (mg/I) II (ue/,f) (tmtl) II
12-Sep-02 7700 47.6
24-Nov-02 5400 42
28-Mar-03 4200 61.4
15-May-03 4700 NA
23-Jun-03 4500 11.4
15-Jul-03 2400 6.8
15-Aug-03 2600 4
12-Sep-03 2500 5.7
25-Sep-03 4600 9.2
29-0ct-03 4600 7.7
9-Nov-03 2600 4.8
29-Mar-04 NA NA
22-Jun-04 NA NA
16-Aug-04 7100 9.91
17-Sep-04 2600 4.5
17-Nov-04 1800 3.6
16-Mar-05 2200 5.3
25-May-05 1200 5.7
31-Aug-05 1400 <5 <5 <5 4.6 NA
1-Dec-05 2800 <50 <50 <50 <0.1 NA
9-Mar-06 1200 <50 <50 <50 4 86
14-Jun-06 1100 <50 <50 <50 5.2 116
20-Jul-06 1120 <50 <50 <50 4.3 123
8-Nov-06 1050 1.6 2.6 <1 4.6 134
28-Feb-07 1200 1.3 <1 <1 4 133
27-Jun-07 1800 2.3
15-Aug-07 1100 1.9 <1 <1 4.1 129
10-0ct-07 1100 1.9 <1 <1 4 132
26-Mar-08 1800 2.9 <1 <1 2.2 131
25-Jun-08 1000 1 <1 <1 2.81 128
10-Sep-08 3600 8.6 <1 <1 36.2 113
15-0ct-08 4200 12 <1 <l 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <1 2.4 132
15-Sep-09 6600 15 <1 <1 0.1 43
14-Dec-09 4700 16 <1 <1 26.7 124
17-Feb-10 940 1.3 <l <1 2 144
9-Jun-10 1800 4.2 <l <1 4.4 132
16-Aug-10 2000 4.9 <1 <1 5.9 142
Chlor@fe m Carbo . Chlo etha e Methylen Nitrate CM ..
TW,4-19 (ug/1) 'F traoomi,id (ug{!, Chlm,Me (mg/JO i,, (mg/I, (ufllj), (aid)
l 1-0ct-10 1200 1.3 <1 <l 2.7 146
17-Feb-ll 3400 17 ND ND 17 135
7-Jun-11 4000 8.3 ND ND 12 148
17-Aug-11 970 2.1 ND ND 3 148
5-Dec-11 2200 5.4 ND ND 5 148
23-Jan-12 650 1.5 ND ND 0.6 138
6-Jun-12 460 1.1 ND ND 2.4 149
5-Sep-12 950 3.5 ND ND 2.5 149
3-0ct-12 1500 4 ND ND 4.1 150
ll-Feb-13 4210 5.15 ND ND 7.99 164
5-Jun-13 2070 5.15 ND ND 2.95 148
3-Sep-13 8100 20.7 ND ND 17.6 179
29-0ct-13 942 6.42 ND ND 4.7 134
27-Jan-14 586 4.05 ND ND 1.62 134
19-May-14 810 5.51 ND ND 1.34 152
11-Aug-14 1410 1.9 8.3 ND 1.6 140
21-0ct-14 4310 4.8 ND ND 4.72 130
9-Mar-15 4660 8.92 ND ND 8.56 238
8-Jun-15 1570 2.62 ND ND 0.916 180
4-Sep-15 7860 7.78 ND ND 11.6 326
19-0ct-15 7840 12.2 5.46 ND 10.6 252
9-Mar-16 7780 13.5 1.40 ND 15.7 276
23-May-16 12600 23.1 ND ND 1.27 204
25-Jul-16 6040 9.89 ND ND 10.5 214
25-Jul-16 6040 9.89 ND ND 10.5 214
13-0ct-16 6640 10.8 ND ND 10.0 200
8-Mar-17 1240 3.06 ND ND 11.1 461
13-Jun-l 7 510 1.35 ND ND 0.243 135
26-Jul-17 8840 13.0 ND ND 1.12 218
l 1-0ct-17 129 ND ND ND 0.377 139
12-Mar-18 2640 1.36 ND ND 8.61 193
8-Jun-18 2980 3.45 ND ND 0.494 138
22-Aug-18 1910 2.03 ND ND 2.55 166
28-Nov-18 5270 6.18 ND ND 0.233 140
8-Mar-19 2050 2.43 ND ND 6.58 197
5-Jun-19 11500 15.90 ND ND 8.96 160
4-Sep-19 6670 10.10 ND ND 0.332 153
10-Dec-19 551 ND ND ND 0.535 147
19-Feb-20 8720 13.7 5.41 ND 10.1 205
Chloroform Carb9n Ghloromethane MethJlene Nitrate Chloride TW4-19 Tetrachloride ,€h]oride (ug/1) Cuwl) ~ug/1) (utrll) QDg(l) fmgll~
27-May-20 7600 10.4 ND ND I. 14 147
oi-unr-a ~
v~-oaa-a
u,
Cl)
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0 -0 ...
0 ::2
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W-Jd'v'-6~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 .._,. C\J 0 co (0 .._,. C\J ..... ..... .....
(1J6n)
Cl eform,, Carbon Chh>romefllane Mdbyle • ate €1~4e TW4·21 Tutraddorid.e Cb .
(ugll) fu,t/.J,) (uglf) fwdll {mw)) (mg{.~
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 <1 1.1 4.2 124
27-Jun-07 1800 2.2 <1 <1 2.3 112
15-Aug-07 5200 3.5 <1 1.8 2.1 117
10-0ct-07 9000 6.8 <l 1.9 5.6 170
26-Mar-08 13000 9 <l 1.5 0.9 132
25-Jun-08 30000 13 <1 1.2 7.96 191
IO-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 <1 5.2 5.1 164
24-Jun-09 6800 4.9 <2 4.2 2.9 164
15-Sep-09 13000 8.4 <2 4.4 3.3 153
14-Dec-09 15000 14 <1 3 5.3 187
17-Feb-10 3500 2.7 <1 3.2 2 179
14-Jun-10 18000 11 <1 3.7 5.6 200
16-Aug-10 15000 12 <1 2.2 5.3 196
11-0ct-10 24000 20 <1 5.5 4.6 203
23-Feb-ll 31000 27 ND 19 4.4 220
1-Jun-11 8100 10 ND 2.1 4.8 177
17-Aug-11 6800 7.3 ND 3.1 6.5 207
16-Nov-11 7900 7.2 ND 2.5 4.2 186
23-Jan-12 11000 10 ND 1.3 7.9 207
6-Jun-12 36000 33 ND ND 11 262
4-Sep-12 13000 26 ND ND 10.8 289
3-0ct-12 19000 22 ND ND 11 302
l 1-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
1 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
Chlo: ofimu Cat"bon Ch1oro dl:ane Methylene Nikate Chloride TW4-20 Tm M.o . Choride
I (ugffl e (agt,f) (mg/I). (m,Jl) CuetJ), :{ud)·
9-Mar-15 19900 20.8 4.85 1.38 9.8 290
8-Jun-15 17600 16.2 13.4 1.73 5.76 296
31-Aug-15 17000 15.1 12.3 ND 9.27 365
19-0ct-15 17000 14.5 10.8 1 6.23 293
9-Mar-16 21600 20.2 4.09 1.16 10.3 293
23-May-16 33700 40.6 ND ND 11.2 318
25-Jul-16 23600 26.6 ND ND 11.3 307
12-0ct-16 21300 24.4 ND ND 11.4 301
8-Mar-17 23400 23.5 ND ND 12 290
13-Jun-17 18100 23.4 ND ND 9.76 281
26-Jul-17 27600 25.0 ND ND 10.8 292
12-0ct-l 7 11600 11.2 2.34 ND 8.91 293
12-Mar-18 15400 15.9 1.77 2.36 9.5 289
14-Jun-18 12000 ND ND 7.77 10.4 258
22-Aug-18 10500 9.85 4.98 ND 8.14 282
28-Nov-18 9500 8.32 15.6 ND 9.72 295
8-Mar-19 15600 15.40 ND ND 6.70 272
5-Jun-19 13700 10.10 ND ND 9.59 279
4-Sep-19 10500 8.39 ND ND 10.2 286
10-Dec-19 8790 5.92 2.67 ND 9.75 307
19-Feb-20 14300 8.60 10.7 ND 9.81 310
27-May-20 5800 6.74 1.30 12.3 7.23 301
oi-unr-a~
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E ... 0 -0 ... 0 U-JdV-~ :c
0
0 N I
'111:t'
== I-
60-1nr-9
90-ioo-o~
vo-uer-v~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I'-co I() 'q" ('I) C\I ...
(1J6n)
Chlo.110.tonn Cehon Chlo cmtdtane Meth~e ~ Chloride TW4 .. 21 Tev hrldi CllivMe
I
(ug/t) (ud) (ug11) {U~· (mgffl (mg/l)
25-May-05 192 NA NA NA 14.6 NA
31-Aug-05 78 <5 <5 <5 IO.I NA
1-Dec-05 86 <1 1.0 <1 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 <1 <1 8.7 296
28-Feb-07 160 1.8 <1 <l 8.7 306
27-Jun-07 300 5.8 <1 <1 8.6 327
15-Aug-07 140 <1 <1 <l 8.6 300
10-0ct-07 120 <1 <1 <1 8.3 288
26-Mar-08 380 7 <1 <1 14.3 331
25-Jun-08 160 1.7 <1 <1 8.81 271
10-Sep-08 120 1.6 <1 <1 7.57 244
15-0ct-08 170 2 <1 <2 8.00 284
11-Mar-09 180 <1 <1 <1 8.3 279
24-Jun-09 200 <1 <1 <1 8.1 291
15-Sep-09 140 <1 <1 <1 9.2 281
22-Dec-09 160 <1 <1 <1 8.4 256
25-Feb-10 170 <1 <1 <1 8.4 228
IO-Jun-IO 210 1.2 <1 <1 12 266
12-Aug-10 390 9.2 <1 <1 14 278
13-0ct-10 200 1.2 <1 <1 7 210
22-Feb-11 230 1.2 ND ND 9 303
28-Jun-11 290 4.8 ND ND 12 290
17-Aug-11 460 6.3 ND ND 14 287
7-Dec-11 390 6.7 ND ND 13 276
19-Jan-12 420 6.4 ND ND 15 228
13-Jun-12 400 5.4 ND ND 11 285
13-Sep-12 410 6 ND ND 13 142
4-0ct-12 390 7 ND ND 14 270
13-Jan-13 282 5.25 ND ND 11.8 221
18-Jun-13 328 3.49 ND ND 13.8 243
12-Sep-13 244 2.13 ND ND 10.3 207
13-Nov-13 204 ND ND ND 9 206
5-Feb-14 220 6.23 ND ND 11.4 200
22-May-14 240 4.73 ND ND 11.5 243
27-Aug-14 204 ND ND ND 7.1 230
29-0ct-14 229 1.04 ND ND 10 252
Chloroform Carbon CldDl'ome6.ane ~eihyletle Nitrate Chloride TW4-21 ('Ug/t) Tetraehlwide (1Jglll CM@ride (mg/t) (mgtl)
I b1.w)I) '(lid)
12-Mar-15 292 1.75 ND ND 10.9 255
8-Jun-15 366 1.92 ND ND 13.1 494
31-Aug-15 281 ND ND ND 14.7 499
19-0ct-15 339 ND ND ND 14.3 413
9-Mar-16 390 ND ND ND 14.6 452
23-May-16 545 ND ND ND 13.1 425
25-Jul-16 456 ND ND ND 16.5 457
12-0ct-16 434 ND ND ND 11.4 301
12-0ct-16 434 ND ND ND 11.4 301
8-Mar-17 598 2.36 ND ND 12.0 290
13-Jun-17 224 1.16 ND ND 9.53 309
26-Jul-17 537 1.05 ND ND 18.2 447
11-0ct-17 466 ND ND ND 16.9 378
12-Mar-18 421 ND ND ND 15.8 447
8-Jun-18 532 ND ND ND 14.1 387
22-Aug-18 476 ND ND ND 0.236 182
22-0ct-18 585 ND ND ND 15.2 392
8-Mar-19 323 ND ND ND 8.99 180
5-Jun-19 734 ND ND ND 17.5 456
4-Sep-19 596 ND ND ND 14.7 478
10-Dec-19 794 ND ND ND 5.73 339
19-Feb-20 844 ND 2.58 ND 8.93 446
27-May-20 767 ND ND ND 15.40 353
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ehJQrolorm Carbon CMenmetlan M$1lykna Mb-ate 11·0hloride TW4-22 T~ ~ tug/I;) '(tlW,Q (ugll) (udl~ (ntglf)' (m,g/1)
25-May-05 340 NA NA NA 18.2 NA
31-Aug-05 290 <5 <5 <5 15.7 NA
1-Dec-05 320 <5 <5 <5 15.1 NA
9-Mar-06 390 <10 <10 <10 15.3 236
14-Jun-06 280 <10 <10 <10 14.3 221
20-Jul-06 864 <10 <10 <10 14.5 221
8-Nov-06 350 <1 1.6 <1 15.9 236
28-Feb-07 440 <1 <1 <1 20.9 347
27-Jun-07 740 <1 <1 <1 19.3 273
15-Aug-07 530 <1 <l <l 19.3 259
10-0ct-07 440 <1 <1 <1 18.8 238
26-Mar-08 1400 <1 <1 <1 39.1 519
25-Jun-08 1200 <l <l <l 41.9 271
10-Sep-08 6300 1.3 <1 <1 38.7 524
15-0ct-08 630 <2 <2 <2 36.3 539
l 1-Mar-09 390 <l <l <l 20.7 177
24-Jun-09 730 <l <l <l 20.6 177
15-Sep-09 2300 <l <l <1 40.3 391
29-Dec-09 380 <l <1 <1 17.8 175
3-Mar-10 2200 <1 <1 <1 36.6 427
15-Jun-10 540 <1 <1 <1 19 134
24-Aug-10 340 <1 <l <1 15 130
13-0ct-10 340 <1 <1 <1 16 134
23-Feb-11 1300 ND ND ND 18 114
1-Jun-11 210 ND ND ND 17 138
17-Aug-11 450 ND ND ND 15 120
7-Dec-11 400 ND ND ND 19 174
19-Jan-12 200 ND ND ND 14 36
13-Jun-12 120 ND ND ND 12.8 35
12-Sep-12 940 ND ND ND 7 121
4-0ct-12 330 ND ND ND 14 130
11-Feb-13 10600 3.24 ND ND 58 635
5-Jun-13 12500 3.35 ND ND 50.2 586
3-Sep-13 9640 3.25 ND ND 29.7 487
29-0ct-13 13300 8.09 ND ND 45.2 501
27-Jan-14 12100 6.06 ND 2.83 54.6 598
19-May-14 12400 6.65 ND ND 47.2 614
ll-Aug-14 12400 1.9 40 ND 41.5 540
21-0ct-14 12400 3.32 1.61 ND 54.9 596
Chloroform Carbo Chloromethane Meth~ene Nifr Chloride TW4-Z2 (ugll) l'ctr cbluide (u,vl) adol'I (mwl) (mg/I} (uwd,) I fu4'.dfi
9-Mar-15 12700 3.77 4.31 ND 69.2 675
8-Jun-15 8050 2.42 3.42 ND 47.1 390
31-Aug-15 7810 ND 5.47 ND 64.7 557
19-0ct-15 7530 ND 5.1 ND 56.1 567
9-Mar-16 6070 ND ND ND 31.1 583
23-May-16 8570 2.64 ND ND 58.4 598
25-Jul-16 5840 ND ND ND 61.3 619
12-0ct-16 3370 1.08 ND ND 61.5 588
8-Mar-17 5320 1.56 ND ND 69.8 566
13-Jun-17 3670 1.21 ND ND 70.8 572
26-Jul-17 5150 ND ND ND 66.1 391
11-0ct-17 4770 ND ND ND 80.1 600
12-Mar-18 4530 ND ND ND 62.3 607
8-Jun-18 3010 ND ND ND 72.5 580
22-Aug-18 3600 ND ND ND 55.4 613
28-Nov-18 2680 ND ND ND 75.7 567
8-Mar-19 4310 1.02 ND ND 71.9 528
5-Jun-19 4690 ND 1.13 ND 83.9 662
4-Sep-19 3460 ND ND ND 72.5 588
10-Dec-19 3820 ND ND ND 59.9 608
19-Feb-20 3910 ND ND ND 57.7 606
27-May-20 2530 ND ND ND 60.5 578
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Chi oferm1 Cubon Chh>N.nmtl'l Methylen Nitrate Cb1Gride TW4-23 1'etradd . e CM rid II ~) (ugiff) (mg/l) (mgll)
1: £W!/t) lust),
27-Jun-07 <1 <1 <1 <1 <0.1 47
15-Aug-07 <1 <1 <1 <1 <0.1 46
10-0ct-07 <1 <1 <1 <1 <0.1 43
26-Mar-08 <1 <1 <1 <1 <0.1 41
25-Jun-08 <1 <l <1 <l <0.05 41
10-Sep-08 <1 <1 <1 <l <0.05 35
15-0ct-08 <2 <2 <2 <2 <0.05 51
4-Mar-09 <1 <1 <l <l <0.1 41
24-Jun-09 <1 <l <l <l <0.l 43
15-Sep-09 <1 <l <l <1 <0.1 43
16-Dec-09 <l <l <l <1 <0.1 37
24-Feb-10 <l <l <1 <1 <0.1 45
8-Jun-10 <l <l <1 <1 <0.1 40
10-Aug-10 <1 <1 <1 <1 <0.1 40
5-0ct-10 <1 <1 <1 <1 <0.1 34
16-Feb-ll ND ND ND ND ND 44
25-May-l 1 ND ND ND ND ND 44
16-Aug-11 ND ND ND ND ND 41
15-Nov-11 ND ND ND ND ND 43
17-Jan-12 ND ND ND ND ND 40
31-May-12 ND ND ND ND ND 44
29-Aug-12 ND ND ND ND ND 46
3-0ct-12 ND ND ND ND ND 45
7-Feb-13 ND ND ND ND ND 43.6
30-May-13 ND ND ND ND 0.116 44.7
5-Sep-13 ND ND ND ND ND 48.0
7-Nov-13 ND ND ND ND ND 43.0
23-Jan-14 ND ND ND ND ND 44.6
21-May-14 ND ND ND ND ND 42.3
13-Aug-14 ND ND ND ND ND 46.0
28-0ct-14 ND ND ND ND ND 46.8
12-Mar-15 ND ND ND ND ND 47.3
10-Jun-15 ND ND ND ND ND 48.4
3-Sep-15 ND ND ND ND ND 54.1
28-0ct-15 ND ND ND ND ND 46.4
16-Mar-16 ND ND ND ND ND 49.1
26-May-16 ND ND ND ND ND 50.4
3-Aug-16 ND ND ND ND ND 49.6
20-0ct-16 ND ND ND ND ND 52.1
<Chloro1orm Carba Cbloromethane Methylene Nitrate Chlol!ide TW4-23 (ugffl Tetradlloride. (ug11~ €hloride (mg/I) {mg{l) (ue/1'} (mr/1),
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-l 7 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
11-Jun-20 ND ND ND ND ND 49.0
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-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
Jun-20
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CMo eform Cawon Cldorometh Medlylene Nitrate Ckleride TW,4-24 Tetraclduide etdctricle (qtl1) Cud) (ug/1) f,ue:/4),, (mgJI) (niglii)
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 <l 24.7 692
26-Mar-08 1.5 <1 <l <l 24.4 740
25-Jun-08 1.4 <l <l <l 45.3 834
10-Sep-08 2.9 <1 <1 <1 38.4 1180
15-0ct-08 <2 <2 <2 <2 44.6 1130
4-Mar-09 1.4 <1 <1 <1 30.5 1010
24-Jun-09 1.5 <1 <1 <1 30.4 759
15-Sep-09 1.4 <1 <1 <l 30.7 618
17-Dec-09 1.2 <l <l <l 28.3 1080
25-Feb-10 1.3 <1 <1 <1 33.1 896
9-Jun-10 1.7 <1 <1 <1 30 639
24-Aug-10 1.8 <1 <1 <1 31 587
6-0ct-10 1.4 <1 <l <1 31 522
17-Feb-ll 1.8 ND ND ND 31 1100
26-May-11 1.1 ND ND ND 35 1110
17-Aug-ll 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
I 9-0ct-15 25.3 ND ND ND 29.6 909
9-Mar-16 22.8 ND ND ND 29.1 989
23-May-16 69.6 ND ND ND 24.2 771
25-Jul-16 17.8 ND ND ND 34.4 1180
12-0ct-16 20.8 ND ND ND 31.9 1010
Chlorofonn CarhMI Chlorome(lhane Methylene Nit-rate ~ TW4·24 (ug/l) Tetradderic!le (uglit) Chloride (mg/I) (mgil) («e/i) lumD.
8-Mar-17 18.3 ND ND ND 41.3 1090
13-Jun-17 17.2 ND ND ND 39.9 1080
26-Jul-l 7 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-18 21.0 ND ND ND 38.4 1100
8-Mar-19 28.1 ND ND ND 39.3 1040
5-Jun-19 28.8 ND ND ND 33.2 1020
4-Sep-19 31.1 ND ND ND 36.4 1130
10-Dec-19 43.3 ND ND ND 33.8 1090
19-Feb-20 61.7 ND ND ND 37.1 1010
27-May-20 49.4 ND ND ND 41.7 1060
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• Clluofenn Carb Odo:romethne Methylene Nitrate Cfllarifk TW4-2S ~ I! Tet~~ (uglll) Chlo de fmg/1) (mg/t} (lldl)i (ullll)
27-Jun-07 <l <l <1 <1 17.1 395
15-Aug-07 <1 <1 <1 <1 16.7 382
10-0ct-07 <1 <1 <1 <l 17 356
26-Mar-08 <l <l <l <l 18.7 374
25-Jun-08 <l <l <l <1 22.1 344
10-Sep-08 <l <l <l <l 18.8 333
15-0ct-08 <2 <2 <2 <2 21.3 366
4-Mar-09 <l <l <l <1 15.3 332
24-Jun-09 <l <l <l <1 15.3 328
15-Sep-09 <l <l <1 <l 3.3 328
16-Dec-09 <l <1 <1 <1 14.2 371
23-Feb-10 <l <1 <1 <1 14.4 296
8-Jun-10 <l <1 <l <l 16 306
10-Aug-10 <l <1 <l <l 14 250
5-0ct-10 <l <1 <l <l 15 312
16-Feb-ll ND ND ND ND 15 315
25-May-ll ND ND ND ND 16 321
16-Aug-ll ND ND ND ND 16 276
15-Nov-ll ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 ND ND ND ND 16 287
ll-Sep-12 ND ND ND ND 17 334
3-0ct-12 ND ND ND ND 17 338
ll-Feb-13 ND ND ND ND 9.04 190
5-Jun-13 ND ND ND ND 5.24 136
3-Sep-13 ND ND ND ND 5.69 119
29-0ct-13 ND ND ND ND 6.1 88.6
27-Jan-14 ND ND ND ND 2.16 85.7
19-May-14 ND ND ND ND 1.21 51.1
ll-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 Ch1oromethane Methylene Nitrate Chloride TW4-25 (ug/1) Tetrachlo"l'ide (ug/1)' Chloride (mg/I) (mg/)) II (mdD (ue/1)
8-Mar-17 1 ND ND ND 17 285
13-Jun-17 ND ND ND ND 0.976 69.8
26-Jul-17 ND ND ND ND 1.23 70.l
11-0ct-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
27-May-20 ND ND ND ND 0.851 76.8
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-19
Mar-20
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Chlor-oform Chtuome -e · ate Chi ~·d -TW4-26 (ug/1) etradllorlde J (ugjl) CM · (mgtl) (~ iu,Jl). fu;f!!,f~
15-Jun-10 13 <l <1 <l 7.9 33
1 l-Aug-10 5 <l <l <1 9 17
6-0ct-10 5.4 <1 <1 <1 9.6 22
22-Feb-1 l 2.0 ND ND ND 10 30
26-May-l 1 2.9 ND ND ND 10 15
17-Aug-ll 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
ll-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
1 l-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
12-Jun-20 1140 ND ND ND 11.1 35.1
0
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Jun-10 -r---11---1 ----,-----.-----,------.
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 en n :::r 0 ... 0 -0 ... 3
< DJ c 111 Ill
TW4-27 e thy ne Mtir
C o . (u~) (mg/ii)
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
11-Mar-15 ND ND ND ND 26.5 26.2
10-Jun-15 ND ND ND ND 24.0 26.8
2-Sep-15 1.30 ND ND ND 20.9 26.8
28-0ct-15 1.60 ND ND ND 23.5 26.2
16-Mar-16 2.11 ND ND ND 25.0 28.0
26-May-16 3.16 ND ND ND 21.2 28.7
3-Aug-16 2.78 ND ND ND 21.8 27.1
20-0ct-16 3.80 ND ND ND 19.3 29.4
15-Mar-17 4.33 ND ND ND 22.2 28.3
15-Jun-17 5.65 ND ND ND 23.8 27.9
2-Aug-17 6.05 ND ND ND 20.0 29.5
10-0ct-17 5.91 ND ND ND 21.5 26.3
14-Mar-18 6.95 ND ND ND 19.5 30.3
13-Jun-18 5.95 ND ND ND 22.0 28.3
30-Aug-18 7.32 ND ND ND 18.1 31.4
12-Dec-18 7.70 ND ND ND 20.8 28.2
16-Mar-19 6.54 ND ND ND 21.5 26.2
13-Jun-19 8.24 ND ND ND 22.3 28.6
11-Sep-19 7.58 ND ND ND 21.2 25.3
14-Dec-19 7.97 ND ND ND 22.0 27.4
17-Mar-20 8.04 ND ND ND 23.6 27.6
ll-Jun-20 7.92 ND ND ND 21.5 28.0
Jan-12
Mar-12
May-12
Jul-12
Sep-12
Nov-12
Jan-13
Mar-13
May-13
Jul-13
Sep-13
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
May-20
0 I-' N w ~
(ug/1)
V, en -.J 00 \D I-' 0
i I N ...... n :::r
0 0 o' ""I 3
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Ill
Chloroform Carbon Chlorome Jlethyl e Nitrate Chloride TW4•28 Tetrachloride Cbloritie (ilgM) {ud) (ug4) ~ud) (mg/I) (mg/I)
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
11-Mar-15 ND ND ND ND 19 52.2
IO-Jun-15 ND ND ND ND 19 56.4
2-Sep-15 ND ND ND ND 17.8 61.4
21-0ct-15 ND ND ND ND 18.7 52.7
15-Mar-16 ND ND ND ND 34.0 61.6
25-May-16 ND ND ND ND 29.0 67.1
27-Jul-16 ND ND ND ND 31.3 70.1
19-0ct-16 ND ND ND ND 25.5 70.9
14-Mar-17 ND ND ND ND 24.4 64.2
14-Jun-17 ND ND ND ND 26.0 68.6
27-Jul-17 ND ND ND ND 24.8 67.1
10-0ct-17 ND ND ND ND 24.8 57.4
14-Mar-18 ND ND ND ND 17.2 65.0
12-Jun-18 ND ND ND ND 19.0 55.7
29-Aug-18 ND ND ND ND 16.0 63.8
30-Nov-18 ND ND ND ND 17.7 52.4
16-Mar-19 ND ND ND ND 17.2 51.7
13-Jun-19 ND ND ND ND 15.0 51.8
1 l-Sep-19 ND ND ND ND 10.2 49.0
12-Dec-19 ND ND ND ND 9.48 50.0
17-Mar-20 ND ND ND ND 9.87 52.1
10-Jun-20 ND ND ND ND 9.55 49.8
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
Jun-20
0
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0
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0
0
0
0
0
0
0
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~hlorotorm €nu ChhmJmetlre Methylene Nitnitie Cfdorie TW4·2? ~tracht~ -'•. ~-(ug/1) fugl) ~I (mg/I) (~) tufYt), ~),,
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
l 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
11-0ct-l 7 466 ND ND ND 2.45 37.7
21-Mar-18 533 ND ND ND 2.44 43.1
14-Jun-18 474 ND ND ND 2.67 40.1
5-Sep-18 454 ND ND ND 2.52 45.9
13-Dec-18 521 ND ND ND 2.50 40.9
20-Mar-19 507 ND ND ND 2.67 39.9
19-Jun-19 537 ND ND ND 2.56 39.4
12-Sep-19 549 ND ND ND 2.55 38.0
18-Dec-19 630 ND ND ND 2.58 44.8
18-Mar-20 652 ND ND ND 3.1 41.0
12-Jun-20 686 ND ND ND 3.18 42.2
Ill QJ ::::,
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Chlo..roform {1 en DliorODledtane Methylene Nitrate OdDride TW4-30 (ug/1) T~adi&rlde .(llgA~' Cliloride (mgll) (mglt), twtA) tuwl)
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-l 7 15.2 ND ND ND 2.95 37.8
3-Aug-17 15.7 ND ND ND 3.11 39.8
10-0ct-l 7 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
l 1-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
12-Jun-20 65.4 ND ND ND 3.69 38.6
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
Jun-20
9 0
0 0
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(ug/L)
c,J
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€hloroform (Carbo GhlOl'Omethane Methylene Niclra Chlerldc TW4-31 (ug/1) ~ tradderide (ogll) Cltl0ri {mg/I) (m,gl-0 (um'I) (wdl)
19-Jun-13 ND ND ND ND 1.26 28.4
5-Sep-13 ND ND ND ND 1.1 29.4
7-Nov-13 ND ND ND ND 1.33 28
23-Jan-14 ND ND ND ND 1.32 28.5
21-May-14 ND ND ND ND 1.22 26.3
13-Aug-14 ND ND ND ND 1.1 30
28-0ct-14 ND ND ND ND 1.23 30
l 1-Mar-15 ND ND ND ND 1.33 30.6
10-Jun-15 ND ND ND ND 1.19 31.1
2-Sep-15 ND ND ND ND 0.916 30.4
21-0ct-15 ND ND ND ND 0.953 29.1
16-Mar-16 ND ND ND ND 1.84 31.5
25-May-16 ND ND ND ND 1.36 32.5
28-Jul-16 ND ND ND ND 1.41 30.6
20-0ct-16 ND ND ND ND 1.14 34.0
15-Mar-17 ND ND ND ND 1.19 31.3
15-Jun-l 7 ND ND ND ND 1.21 33.4
2-Aug-17 ND ND ND ND 1.11 33.0
10-0ct-17 ND ND ND ND 1.04 30.9
14-Mar-18 ND ND ND ND 0.916 38.8
12-Jun-18 ND ND ND ND 0.948 34.4
29-Aug-18 ND ND ND ND 0.710 40.3
12-Dec-18 ND ND ND ND 0.766 35.2
16-Mar-19 ND ND ND ND 0.754 35.0
13-Jun-19 ND ND ND ND 0.713 36.9
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
11-Jun-20 ND ND ND ND 0.569 36.7
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
Jun-20
0
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Chloroform Carbo CIUoromethaae Me$yl ue Nitrate Cfthm. TW4-32 Tetra-e otride (ugM) (u~) Gug/0 Chlo ·de €11~) Qng/1) (mgll)
-
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
1 l-Mar-15 ND ND ND ND 2.46 64.2
10-Jun-15 ND ND ND ND 1.21 62.7
2-Sep-15 ND ND ND ND 5.09 59.6
21-0ct-15 ND ND ND ND 1.19 55.1
15-Mar-16 ND ND ND ND 4.48 64.2
25-May-16 ND ND ND ND 3.16 71.8
28-Jul-16 ND ND ND ND 3.44 64.4
19-0ct-16 ND ND ND ND 2.87 66.0
14-Mar-17 ND ND ND ND 2.82 62.8
15-Jun-l 7 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
10-Jun-20 ND ND ND ND 2.19 57.0
Nov-1
Jan-1
Mar-1
May-1
Jul-1
Sep-1
Nov-1
Jan-1
Mar-1
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
May-20
0 0 0 0
0
0
0
0
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0
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Chloroform CarlMm c:: ___ eJliaane hyl'ep Nitrate 'CJ. .
TW4-33 Tetrachloride e
(ug/l) (ua/t} (llgJi) Chlft (agll) (mg/I) mg11,
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
1 l-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
11-0ct-17 97.1 ND ND ND 2.09 42.5
15-Mar-18 128 ND ND ND 1.94 49.2
13-Jun-18 88 ND ND ND 2.13 44.0
5-Sep-18 113 ND ND ND 1.82 50.0
13-Dec-18 141 ND ND ND 2.01 43.2
20-Mar-19 86.2 ND ND ND 2.00 47.2
19-Jun-19 121 ND ND ND 2.16 43.4
12-Sep-19 101 ND ND ND 1.61 41.1
18-Dec-19 117 ND ND ND 1.86 48.8
18-Mar-20 94 ND ND ND 2.44 45.3
12-Jun-20 90 ND ND ND 3.26 48.9
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
May-20
0
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CMoref&rm Carbtm Cbfon ane M hyhme . te <Jhloride TW4-34 (ug/1) Tetrac ,e (ug/1) oride (mgtl) {mg/I) (11ml) ' (u9M'I·
14-Nov-13 ND ND ND ND 1.64 19.2
23-Jan-14 ND ND ND ND 1.94 20.4
21-May-14 ND ND ND ND 1.69 17.9
13-Aug-14 ND ND ND ND 1.1 18
28-0ct-14 ND ND ND ND 1.16 17.5
1 l-Mar-15 ND ND ND ND 1.21 17.7
10-Jun-15 ND ND ND ND 0.868 17.4
3-Sep-15 ND ND ND ND 0.458 15.1
21-0ct-15 ND ND ND ND 0.368 15.8
16-Mar-16 ND ND ND ND 0.925 17.3
26-May-16 ND ND ND ND 0.605 18
26-May-16 ND ND ND ND 0.605 18
3-Aug-16 ND ND ND ND 0.726 17.2
20-0ct-16 ND ND ND ND 0.612 19.0
15-Mar-17 ND ND ND ND 0.674 18.0
15-Jun-17 ND ND ND ND 0.727 15.7
2-Aug-17 ND ND ND ND 0.733 19.8
10-0ct-17 ND ND ND ND 0.774 18.5
14-Mar-18 ND ND ND ND 0.737 19.1
13-Jun-18 ND ND ND ND 0.877 19.5
29-Aug-18 ND ND ND ND 0.736 23.8
12-Dec-18 ND ND ND ND 0.889 18.5
16-Mar-19 ND ND ND ND 0.859 17.9
13-Jun-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
l 1-Jun-20 ND ND ND ND 1.24 20.9
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
May-20
0
0
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;
1
l
0
0
0
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Chloroform Carbon C.blorem dume Meth,rleae Nitrate Obloride TW4-3S (uglt) Tetradrloride
' git)
Chleritle (mg/I) (mg/I) {u2'1~ :l (ue/1!}
27-Aug-14 ND ND ND ND 0.2 34
28-0ct-14 ND ND ND ND 0.351 34.1
l l-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.l
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
12-Dec-18 ND ND ND ND 0.559 43.0
16-Mar-19 ND ND ND ND 0.574 33.5
13-Jun-19 ND ND ND ND 0.670 35.5
ll-Sep-19 ND ND ND ND 0.525 31.7
14-Dec-19 ND ND ND ND 0.524 37.4
17-Mar-20 ND ND ND ND 0.595 34.5
11-Jun-20 ND ND ND ND 0.699 34.0
Aug
Oct
Dec
Feb
Apr
Jun
Aug-
Oct-
Dec-
Feb-
Apr-
Jun-
Aug-
Oct-
Dec-
Feb-1
Apr-1
Jun-1
Aug-1
Oct-1
Dec-1
Feb-1
Apr-1
Jun-1
Aug-1
Oct-18
Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
Oct-19
Dec-19
Feb-20
Apr-20
Jun-20
0
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Chloroform Carb&n ChJevo -~ Methylene I it,rate. Chloride TW4·36 (ug/,t)) Tetraeltl•rhle (ag{,I} Qleride (mg/l) (mgtl) ' (IQ!/t) Cu
27-Aug-14 ND ND ND ND ND 65
23-0ct-14 ND ND ND ND ND 67.3
l 1-Mar-15 ND ND ND ND ND 67.2
10-Jun-15 ND ND ND ND ND 69.3
3-Sep-15 ND ND ND ND ND 76.4
21-0ct-15 ND ND ND ND ND 64.5
16-Mar-16 ND ND ND ND ND 67.1
25-May-16 ND ND ND ND ND 72.3
27-Jul-16 ND ND ND ND ND 69.4
20-0ct-16 ND ND ND ND ND 73.8
15-Mar-17 ND ND ND ND ND 60.2
15-Jun-17 ND ND ND ND ND 71.3
2-Aug-17 ND ND ND ND ND 69.6
10-0ct-17 ND ND ND ND 0.104 62.9
14-Mar-18 ND ND ND ND ND 73.8
12-Jun-18 ND ND ND ND ND 64.3
29-Aug-18 ND ND ND ND ND 76.4
12-Dec-18 ND ND ND ND 0.123 65.8
16-Mar-19 ND ND ND ND 0.116 65.0
13-Jun-19 ND ND ND ND ND 71.5
11-Sep-19 ND ND ND ND ND 69.6
14-Dec-19 ND ND ND ND ND 73.7
17-Mar-20 ND ND ND ND ND 69.1
1 l-Jun-20 ND ND ND ND ND 67.0
Aug-1
Oct-1
Dec-1
Feb-1
Apr-1
Jun-1
Aug-1
Oct-1
Dec-1
Feb-1
Apr-1
Jun-1
Aug-1
Oct-1
Dec-1
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
Apr-20
Jun-20
0
0
0
0
0
0
0
0
0
0
0
0
0
0
0
••
••
••
••
0
••
••
••
••
••
(ug/L)
0 0 0 0
() -=s-
0
"'""" 0 -h 0
"'""" 3
-=s-
Pl en
::,
0 -O"
CD
CD ::,
a.
CD -CD
() -CD a. -· ::,
--f ~ ~ I w O')
_. _.
-t ~ I w a,
0 ::::T
0 2. 0 "'I 3
< !. C CD tn
Carbon -, Methylene Chl~rofonn Chloro.methane NitJ1ate Chloride TW14 .. J'7 Te_trachlorlde, Clilomde ~ug1,I) <.111rli~ .(uw.I~ filein (lllg/l) (ing/1)
8-Jun-15 30200 18 16 2 35 345
31-Aug-15 19100 17 14 1.04 32 374
19-0ct-15 19500 13 9 1.17 35 399
9-Mar-16 17500 16 4 1.34 28.4 332
23-May-16 16200 14 ND 1.17 27.9 389
25-Jul-16 15900 17 ND ND 33.4 294
12-0ct-16 16400 16 ND ND 26.1 304
8-Mar-17 18000 15 ND ND 32.3 305
13-Jun-17 15800 16 ND ND 31.2 281
26-Jul-17 15000 15.1 ND ND 30.5 277
11-0ct-17 15500 12.6 2.47 ND 30.6 255
12-Mar-18 12900 12.8 1.14 ND 30.0 263
8-Jun-18 14400 10.6 ND ND 28.6 275
22-Aug-18 14100 12.1 6.20 ND 25.4 387
28-Nov-18 15200 11.3 19.8 ND 27.3 264
8-Mar-19 13300 13.8 1.2 ND 30.1 209
5-Jun-19 16200 14.6 ND ND 31.2 250
4-Sep-19 11900 10.7 1.90 ND 25.8 228
10-Dec-19 13100 8.8 3.12 ND 25.5 220
19-Feb-20 12000 8.5 12.30 ND 28.3 236
27-May-20 11700 11.8 1.44 ND 28.3 321
u,
0 0 0 0
...L. 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
Apr-20
......
0 0 0 0
@ (ug/L)
0 0
I\)
0 0 0 0
I\) u,
0 0 0
w 0 0 0 0
w u,
0 0 0
-4 i I w ......
0 :::r
0
0 -0 ...
3
< !..
C: CD rn
Chloroform Carbon Chloromethane Methyl~ne Nitrate Chloride TW~38 Tetrachloride Chloride (UW)) {,W!/1) (ug/1) (U'f!/1) (mg/I) (mg/I)
10-Nov-16 ND ND ND ND 11.2 40.0
15-Mar-17 ND ND ND ND 10.6 35.7
15-Jun-17 ND ND ND ND 10.8 36.2
2-Aug-17 ND ND ND ND 10.1 36.9
10-0ct-17 ND ND ND ND 10.3 31.3
14-Mar-18 ND ND ND ND 9.34 36.5
13-Jun-18 ND ND ND ND 9.48 33.1
30-Aug-18 ND ND ND ND 7.77 39.2
12-Dec-18 ND ND ND ND 8.48 35.0
16-Mar-19 ND ND ND ND 8.96 33.5
13-Jun-19 ND ND ND ND 8.53 33.7
11-Sep-19 ND ND ND ND 7.61 31.6
14-Dec-19 ND ND ND ND 7.51 36.0
17-Mar-20 ND ND ND ND 8.11 33.4
l 1-Jun-20 ND ND ND ND 9.00 34.9
(ug/L)
0 0 0 0 0 _. _. _. _.
Nov-16 ._--+--+---t---+----t--+---1----r---r---,
Feb-17 t
May-17
Aug-17
Nov-17
Feb-18 1
May-18 1
Aug-18 1
Nov-18
Feb-19
May-19
t
Aug-19
Nov-19
Feb-20
May-20
I I I
I I I
I I
I I I I I I I
I I I I I I I
I I I I I I
-t ~ ~ I w (X)
0 ::::r
0 ""I 0 -0 ""I
3
< D> 2' Cl)
fl>
Ohlo.roform Carbon Chlorometbane Methylene Nitrate Chloride TW4-39 (ug{l) Tetrachloride (ug/1) €hloride (mg/I) (:mg/I) (iJg/f) (ul?/I)
10-Nov-16 2800 ND ND ND 20.7 68.9
8-Mar-17 6460 8.15 ND 1.35 6.44 130
13-Jun-17 5560 8.20 ND 1.31 6.25 120
26-Jul-17 10000 14.40 ND 1.50 7.74 132
11-0ct-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
27-May-20 5870 7.56 ND ND 5.010 88.5
(ug/L)
...... ......
I\) .i::,. O') (X) 0 I\)
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
Nov-16
Feb-17
May-17
Aug-17
Nov-17
Feb-18 -1 I '-I I I I I I -I :e .1:1,, I w
May-18 i I I ---i-..__ I I I co
0 ::,-
0 .,
I 0 Aug-18 i I I 1-i.. -0 .,
3
<
Nov-18 ~ I I I I / I I I D)
i: CD 0
I -----rr I I I I Feb-19
May-19
Aug-19
Nov-19
Feb-20
May-20 .__ ___ _.__ ___ _._ __ --=,,,....----'------'------'
Chloroform Carbon Cliloromethane Methylene Nitrate Chloride TW440 (ug/1) Teb!achloride (ug/1) C,hlorlde (mg/l) (lng/l) 'Cu11m (ug/1)
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
27-May-20 367 ND ND ND 2.91 36.5
en a,
:I cu >
E ... 0 -0 ...
.2 .c 0
Q
'111:t' I
'111:t' 3: I-
0 0 -.:I'
0 Lt)
('I)
0 0 ('I)
0 Lt)
C\I
0 0 C\I
(1/6n)
0 Lt) .... 0 0 .... 0 Lt) 0
oi-unr-B~
oc-Je~-o~
6~-oaa-~
6 ~ -6n\f-£c
6 ~-lie~-s ~
6kqa.:i-v
B~·lOO·LG
Chloroform €arbon Chloromethane Methylene Chloride TW441 Tetraeltloride Chlorkle Nitrate (mgll) (ug/1) tui!II) (ugll) ;{urun (irng/1)
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
27-May-20 1220 ND ND ND 6.78 41.7
U)
Cl)
::::J
'ii >
E ... 0 -0 ... .2 .c 0
,-
-.::I' I -.::I' 3: I-
0 LO s:t ,-
0 0 s:t ,-
0 LO (") ,-
0 0 (")
(1J6n)
0 LO C\I ,-
0 0 C\I ,-
0 LO
oc::-unr-a~
OC::-JBV\1-0 ~
6~-oao-~
6~-5nV-8C::
6 ~ -ABV\1-9 ~
6~-qa.:1-v
a ~-ioo-a
8~-JdV-O~
c_hloroform Qarbon Chloroinethane Meth,Iene Nitrate <CbJo,ide TW4-42 Tet.rachloride Chloride (ug/J) (u2'1) (ug/1) (_rmdn, {mg/I~ (mg/I)
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
17-Mar-20 ND ND ND ND 3.23 23.1
ti)
Cl) :::,
m >
E ...
0 -0 ...
.2 .c 0
N oi::t' I !
..-0 0
{1/6n)
.~
OG-JBIIIJ-O ~
oi-uer-oi
••
6 ~-oaa-~
i•
6k5nv-8i
..
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_Q2_20.xls
Gridding details:
1) kriging parameters: SURFER™ default parameters (point kriging, linear
variogram, slope= 1, no anisotropy [anisotropy= 1], no search constraints [all data
used])
2) 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) Ql, 2020 (previous quarter) data used at wells: none
Chloroform residual mass es timate kriged grid files (ascii format):
Ucm2Q20wl.grd: second quarter, 2020 Water Level Grid (ft amsl)
Ucm2Q20bb.grd: second quarter, 2020 Aquifer Base Grid (ft amsl)
Ucm2Q20sat.grd: second quarter, 2020 Saturated Thickness Grid (ft)
Ucm2Q20logchl.grd: second quarter, 2020 log of chloroform grid (log of ug/L)
Ucm2Q20chl.grd: second quarter, 2020 Chloroform Concentration Grid (ug/L)
Ucm2Q20ge70.grd: second quarter, 2020 Chloroform Concentration GE 70 Grid (ug/L)
Ucm2Q20volm3.grd: second quarter, 2020 Groundwater Volume Grid (m3)
Ucm2Q20masslb.grd: second quarter, 2020 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format):
Ucm2Q20wl.dat: second quarter, 2020 Water Level Grid XYZ file (ft amsl)
Ucm2Q20bb.dat: second quarter, 2020 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm2Q20sat.dat: second quarter, 2020 Saturated Thickness Grid XYZ file (ft)
Ucm2Q20logchl.dat: second quarter, 2020 log of chloroform grid XYZ file (log of ug/L)
Ucm2Q20chl.dat: second quarter, 2020 Chloroform Concentration Grid XYZ file (ug/L)
Ucm2Q20ge70.dat: second quarter, 2020 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm2Q20volm3.dat: second quarter, 2020 Groundwater Volume Grid XYZ file (m3)
Ucm2Q20masslb.dat: second quarter, 2020 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plwne mass estimate file: Ucm2Q20result.xls
2400
2200
2000
1800
:ii'
:::. 1600 a, .. RI E = w
Ill Ill RI ~
E ...
.E 0 ... 0 J: u
RI :::,
't, ·;;; a, a::
1400
1200
1000
800
600
400
200
0
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~ ~~
,-.-mass estimate
--Linear (mass estimate)
H:\718000\aug20\chloroform\masscalc\FL.1_resid_chl_mass_2Q20.xls: FL.1 Resid CHL Mass
HYDRO
GEO
CHEM,INC.
TIME SERIES OF RESIDUAL CHLOROFORM MASS
ESTIMATES
File Name I Figure
Mll.W•&IT~x19 L.1
Approved I Date
SJS
Author I Date
SJS
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
01 18 1271
0218 1271
0318 1208
0418 1107
01 19 833
0219 1408
0319 1050
0419 770
01 20 1106
0220 1056
Notes:
lbs= pounds
H:\718000\aug20\chloroform\masscalc\FL.l_resid_chl_mass_2Q20.xls: Table L.1
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Friday, August 14, 2020 12:52 PM
Phillip Goble
'Dean Henderson'; David Frydenlund; Terry Slade; Scott Bakken; Logan Shumway; Paul
Goranson
Transmittal of CSV Files White Mesa Mill 2020 Q2 Chloroform Monitoring
2005695-report-EDD.csv; 2006384-report-EDD.csv; 2006426-report-EDD.csv; Q2 2020
DTW all programs.csv; Q2 2020 Field Data.csv
Attached to this e-mail is an electronic copy of laboratory results for chloroform monitoring conducted at the White
Mesa Mill during the second 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 Weinel
Quality Assurance Manager
t: 303.389.4134 It: 303.389.4125
225 Union Blvd., Suite 600
Lakewood, CO 80228
http://www.energyfuels.com
This e-mail is intended for the exclusive use of person(s) mentioned as the recipient(s). This message and any attached files with it are confidential and may
contain privileged or proprietary information. If you are not the intended recipient(s) please delete this message and notify the sender. You may not use, distribute
print or copy this message if you are not the intended recipient(s).
1
TabN
Exceedance Notices for the Reporting Period
This attachment has been deliberately left blank.