DRC-2021-006761 - 0901a06880e8cafd

11 ENERGY FUELS
Energy Fuels Resources (USA) Inc.
225 Union Blvd., Suite 600
Lakewood, CO, US, 80228
303 974 2140 NC, -2021 '0006 w ww.energy fuels.com
May 10, 2021
Sent VIA OVERNIGHT DELIVERY
Ms, Jalynn Knudsen
Interim Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
Salt Lake City, UT 84116
Re: Transmittal of 1st Quarter 2021 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Ms. Knudsen:
Div of Waste Management
and Radiation Control
MAY 1 2 2021
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 1st Quarter of
2021 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David Frydenlund
Logan Shumway
Scott Bakken
Terry Slade
May 10, 2021
Sent VIA OVERNIGHT DELIVERY
Ms. Jalynn Knudsen
Interim 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 1st Quarter 2021 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Ms. Knudsen:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 1st Quarter of
2021 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word earchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
t~i~
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David Frydenlund
Logan Shumway
Scott Bakken
Terry Slade
White Mesa Uranium Mill
Chloroform Monitoring Report
State of Utah
Stipulation and Consent Order Docket No. UGW-20-01
1st Quarter
(January through March)
2021
Prepared by:
&1!£RGY-LS
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
May 10, 2021
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 Mea<:ured and Groundwater Elevation ................. 21
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture ............................ 21
4.2 Review of Analytical Results ............................................................................ 25
4.2.1 Current Chloroform Isoconcentration Map .............................................. 25
4.2.2 Chloroform Concentration Trend Data and Graphs .................................. 25
4.2.3 Interpretation of Analytical Data .............................................................. 26
1
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 ............................................................................ 31
5.5 Mass Removed and Plume Residual Mass ........................................ .' .............. 31
5.6 Inspections ........................................................................................................ 32
5.7 Condition 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 ......................................................................... 34
7.5 Chloroform Plume Monitoring for We.lls within 500 Feet of the Property
Boundary .......................................................................................................... 34
8.0 CONCLUSIONS AND RECOMMENDATIONS ............................................ 34
9.0 ELECTRONIC DATA FILES AND FORMAT .............................................. 40
10.0 SIGNATURE AND CERTIFICATION ........................................................... 41
LIST OF TABLES
Table 1 Summary of Wells Sampling for the Period
11
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture
Zone Details Map and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater
Elevations over Time for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells
over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QA/QC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank Evaluations
I-7 QA/QC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform lsoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs over
Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
Tab N Exceedance Notices for the Reporting Period
Ill
1.0 INTRODUCTION
The pre ence of chloroform was jnitialJy identified jn groundwater at the White Mesa MilJ (the
"MilJ") as a re ult of split ampJi11g performed in May L999. The di ·covery 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 '), Divi ion of
Waste Management and Radiation Control ("DWMRC") Docket No. UGW-20-01, which
required that Energy Fuels Re ources (USA) Inc. ("EFRI") submit a Contamination Investigation
Plan and Report pursuant to the provision of UAC R317-6-6.15(D). In response to the NOV,
EFRI submitted a eries of documents outlining plan for inve tigation of the chloroform
contamination. This plan of action and preliminary chedule was et out in EFRJ submittal
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 acti ve and continued remediation of the
chloroform plume both parties have agreed to the GCAP found in Attachment 1, of the final
Stipulation and Con ent Order ( 'SCO") dated September 14, 2015.
Thj is the Quarterly Chloroform Monitoring Report for the fir t quarter of 2021 as required
under the SCO. Thi report al ·o include the Operation Report for MW-04, TW4-0l, TW4-04,
TW4-02, TW4-1 l TW4-19 TW4-21, MW-26, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39,
TW 4-40, and TW 4-41 for the quarter.
2.0 CHLOROFORM MONITORING
2.1 Samples and Measurements Taken During the Quarter
A map howing the location of all groundwater monitoring wells piezometer , exi ting wells
temporary chloroform contaminant inve tigation welL and temporary nitrate investigation wells
is attached under Tab A. Chloroform amples and mea ·urement taken during thi 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 TW4-28 TW4-37
TW4-1 TW4-10 TW4-19 TW4-29 TW4-38
TW4-2 TW4-11 TW4-21 TW4-30 TW4-39
TW4-3 TW4-12 TW4-22 TW4-31 TW4-40
TW4-4 TW4-13 TW4-23 TW4-32 TW4-41
TW4-5 TW4-14 TW4-24 TW4-33 TW4-42
TW4-6 MW-26 (formerly TW4-15) TW4-25 TW4-34
TW4-7 TW4-16 TW4-26 TW4-35
TW4-8 MW-32 (formerly TW4-17) TW4-27 TW4-36
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 ample were
collected from each well, and the date(s) when analytical data were received from the contract
laboratory. Table 1 also identifies equipment cin ate ·amples collected a well as ample
number 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
U. e of analytical methods i~ consi tent with the requirements of the Chloroform Investigation
Monitoring Quality Assurance Program (the "Chloroform QAP') attached a Appendix A lo the
White Me a Uranium Mill Groundwater Monitoring QAP Revi ion 7.6 dated August 22 2019.
2.1.3 Groundwater Head Monitoring
Depth to groundwater was measured in the following wells and/or piezometers, pursuant to Part
I.E.3 of the Groundwater Discharge Permit (the "GWDP"):
• The quarterly groundwater compliance monitoring wells
• Existing monitoring well MW-4 and all of the temporary chloroform investigation wells
• Piezometers P-1, P-2, P-3, P-4 and P-5
• MW-20 and MW-22
• Nitrate monitoring wells
• The DR piezometers that were installed during the Southwest Hydrologic Investigation
In addition to the above, depth to water measurements are routinely ob. erved in conjunction with
sampli11g events for all wells sampled during quarterly and accelerated effort regardless of the
sampling purpose.
Weekly and monthJy 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, TW4-21, TW4-37, TW4-39,
TW4-40, and TW4-41 and the nitrate pumping wells TW4-22, TW4-24 TW4-25, and TWN-02.
In addition, monthly water level measurements were taken in non-pumping wells MW-27, MW-
30, MW-31, TW4-21, TWN-1, TWN-3, TWN-4, TWN-7, and TWN-18.
2
2.2 Sampling Methodology and Equipment and Decontamination Procedures
EFRI completed, and transmitted to DWMRC on May 25, 2006, a revised QAP for sampling
under the Mill's GWDP. While the water sampling conducted for chloroform investigation
purposes has conformed to the general principles set out in the QAP, some of the requirements in
the QAP were not fully implemented prior to DWMRC's approval of the QAP, for reasons set
out in correspondence to DWMRC dated December 8, 2006. Subsequent to the delivery of the
December 8, 2006 letter, EFRI discussed the issues brought forward in the letter with DWMRC
and has received correspondence from DWMRC about those issues. In response to DWMRC's
letter and subsequent discussions with DWMRC, EFRI modified the chloroform Quality
Assurance ("QA") procedures within the Chloroform QAP. The Chloroform QAP describes the
requirements of the chloroform investigation program and identifies where they differ from the
Groundwater QAP. On June 20, 2009 the Chloroform QAP was modified to require that the
quarterly chloroform reports include additional items specific to EFRI's ongoing pump testing
and chloroform capture efforts. The Groundwater QAP as well as the Chloroform QAP were
revised again on June 6, 2012, August 15, 2017, July 23, 2018, May 14, 2019, and August 22,
2019. The revised Groundwater QAP and Chloroform QAP, Revision 7.6 were approved by
DWMRC on September 10, 2019.
The sampling methodology, equipment and decontamination procedures used in the chloroform
contaminant investigation, as summarized below, are consistent with the approved QAP and the
Chloroform QAP.
2.2.1 Decontamination Procedures
Non-dedicated sampling equipment is decontaminated prior to use as described in the DWMRC-
approved QAP and as summarized below.
The water level meter is decontaminated with a detergent/deionized ("DI") water mixture by
pouring the solutions over the water level indicator. The water level meter is then rinsed with DI
water.
The field measurement instrument probe is decontaminated by rinsing with DI water prior to
each calibration. The sample collection cup is washed with a detergent/DI water solution and
rinsed with fresh DI water prior to each calibration.
The non-dedicated purging pump is decontaminated after each use and prior to use at subsequent
sampling locations using the following procedures:
a) the pump is submerged into a 55-gallon drum of nonphosphate detergent/DI water mixture;
b) the detergent/DI water solution is pumped through the pump and pump outlet lines into the
drain line connected to Cell 1;
c) the pump is submerged into a 55-gallon drum of DI water;
3
d) the DI water solution is pumped through the pump and pump outlet lines into the drain line
connected to Cell 1;
2.2.2 Well Purging and Depth to Groundwater
The non-pumping wells are purged prior to sampling by means of a portable pump. A list of the
wells in order of increasing chloroform concentration is generated quarterly. The order for
purging the non-pumping wells is thus established. The list is included with the Field Data
Worksheets under Tab B. Mill personnel start purging with all of the non-detect wells and then
move to the wells with detectable chloroform concentrations staring with the lowest
concentration and proceeding to the wells with the highest concentration. One deviation to this
practice is made for the continuously pumping wells. These wells are sampled throughout the
sampling event and are not sampled in the order of contamination. This practice does not affect
the samples for this reason: the pumping wells have dedicated pumps and there will be no cross-
contamination resulting from the sampling order.
Samples are collected by means of disposable bailer(s) the day folJowing 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
pecific conductivity, turbidity, pH, redox potential, Di olved 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 ["RPO"])
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 i
considered sufficiently evacuated to immediately collect a sample; however, if a pumping well
has been out of service for 48 hours or more, EFRI will follow the purging requirements outlined
in Attachment 2-3 of the QAP. The dedicated pump is used to collect parameters and to collect
4
the samples as described below. If the well does not have a dedicated pump, a Grundfos pump
(9 -10 gpm pump) is then lowered to the screened interval in the well and purging is started.
The purge rate is measured for the well by using a calibrated 5 gallon bucket. This purging
process is repeated at each well location moving from least contaminated to the most
contaminated well. All wells are capped and secured prior to leaving the sampling location.
Wells with dedicated pumps are sampled when the pump is in the pumping mode. If the pump is
not pumping at the time of sampling, it is manually switched on by the Mill Personnel. The well
is pumped for approximately 5 to 10 minutes prior to the collection of the field parameters. Per
the approved QAP, one set of parameters is collected. Samples are collected following the
measurement of one set of field parameters. After sampling, the pump is turned off and allowed
to resume its timed schedule.
2.2.3 Sample Collection
Prior to sampling, a cooler with ice is prepared. The trip blank is also gathered at that time (the
trip blank for these events is provided by the analytical laboratory). Once Mill Personnel arrive
at the well sites, labels are filled out for the various samples to be collected. All personnel
involved with the collection of water and samples are then outfitted with disposable gloves.
Chloroform investigation samples are collected by means of disposable hailers.
Mill personnel use a disposable bailer to sample each well that does not have a dedicated pump.
The bailer is attached to a reel of approximately 150 feet of nylon rope and then lowered into the
well. After coming into contact with the water, the bailer is allowed to sink into the water in
order to fill. Once full, the bailer is reeled up out of the well and the sample bottles are filled as
follows:
• Volatile Organic Compound ("VOC") samples are collected first. This sample consists
of three 40 ml vials provided by the Analytical Laboratory. The VOC sample is not
filtered and is preserved with HCl;
• A sample for nitrate/nitrite is then collected. This sample consists of one 250 ml. bottle
that is provided by the Analytical Laboratory. The nitrate/nitrite sample is not filtered
and is preserved with H2S04;
• A sample for chloride is then collected. This sample consists of one 500 ml. bottle that is
provided by the Analytical Laboratory. The chloride sample is not filtered and is not
chemically preserved.
After the samples have been collected for a particular well, the bailer is disposed of and the
samples are placed into the cooler that contains ice. The well is then recapped and Mill personnel
proceed to the next well.
5
2.3 Field Data
Attached under Tab B are copies of the Field Data Worksheets that were completed during the
quarter for the chloroform contaminant investigation monitoring wells identified in paragraph
2.1.1 above, and Table 1.
2.4 Depth to Groundwater Data and Water Table Contour Map
Attached under Tab C are copies of the Depth to Water Sheets for the weekly monitoring of
MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-21, TW4-22, TW4-24, TW4-
25, TW4-37, TW4-39, TW4-40, TW4-41 and TWN-2 as well as the monthly depth to
groundwater data for the chloroform contaminant investigation wells and the non-pumped wells
measured during the quarter. Depth to groundwater measurements that were utilized for
groundwater contours are included on the Quarterly Depth to Water Worksheet at Tab D of this
report, along with the kriged groundwater contour map for the current quarter generated from
this data. A copy of the kriged groundwater contour map generated from the previous quarter's
data is provided under Tab E.
2.5 Laboratory Results
2.5.1 Copy of Laboratory Results
All analytical results were provided by American West Analytical Laboratory ("AWAL"). Table
1 lists the dates when analytical results were reported to the QA Manager for each sample.
Results from the analyses of samples collected for this quarter's chloroform contaminant
investigation are provided under Tab H of this Report. Also included under Tab H are the results
of the analyses for duplicate samples, the DIFB, and rinsate samples for this sampling effort, as
identified in Table 1, as well as results for trip blank analyses required by the Chloroform QAP.
2.5.2 Regulatory Framework
As discussed in Section 1.0 above, the SCO triggered a erie of actions on EFRI's part. In
addition to the monitoring program, EFRI has equipped one nitrate weJI and fifteen chloroform
wells with pump to recover impacted groundwater, and ha initiated recovery of chl.oroform
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 analysi 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 AWAL and returned with the quarterly chloroform
monitoring samples.
Two rinsate blank samples were collected as indicated on Table 1. Rinsate samples were labeled
with the name of the subsequently purged well with a terminal letter "R" added (e.g. TW4-7R).
The results of these analyses are included with the routine analyses under Tab H.
In addition, one DIFB, while not required by the Chloroform QAP, was collected and analyzed
for the same constituents as the well samples and rinsate blank samples.
3.2 Adherence to Mill Sampling SOPs
The QA Manager's review of Mill Personnel's adherence to the existing SOPs, confirmed that
the QA/QC requirements established in the QAP and Chloroform QAP were met.
3.3 Analyte Completeness Review
All analyses required by the GCAP for chloroform monitoring for the period were performed.
7
3.4 Data Validation
The QAP and GWDP identify the data validation steps and data QC checks required for the
chloroform monitoring program. Consistent with these requirements, the QA Manager performed
the following evaluations: a field data QA/QC evaluation, a holding time check, a receipt
temperature check, an analytical method check, a reporting limit evaluation, a trip blank check, a
QA/QC evaluation of sample duplicates, a QC Control Limit check for analyses and blanks
including the DIFB and a rinsate sample check. Each evaluation is discussed in the following
sections. Data check tables indicating the results of each test are provided under Tab I.
3.4.1 Field Data QA/QC Evaluation
The QA Manager performs a review of the field recorded parameters to assess their adherence
with QAP requirements. The assessment involved review of two sources of information: the
Field Data Sheets and the Quarterly Depth to Water summary sheet. Review of the Field Data
Sheets addresses well purging volumes and measurement of field parameters based on the
requirements discussed in section 2.2.1 above. The purging technique employed determines the
requirements for field parameter measurement and whether stability criteria are applied. Review
of the Depth to Water data confirms that all depth measurements used for development of the
groundwater contour maps were conducted within a five-day period as indicated by the
measurement dates in the summary sheet under Tab D. The results of this quarter's review of
field data are provided under Tab I.
Based upon the review of the field data sheets, the purging and field measurements were
completed in conformance with the QAP requirements. A summary of the purging techniques
employed and field measurements taken is described below:
Purging Two Ca ing Volumes with St, ble Field Parameters (within 10% RPD)
Wells TW4-5, TW4-8, TW4-9, TW4-16, MW-32, TW4-18, TW4-23, TW4-32, and TW4-38
were sampled after two casing volumes were removed. Field parameters (pH, specific
conductivity, turbidity, water temperature, DO, and redox potential) were measured during
purging. All field parameters for this requirement were stable within 10% RPD.
Purging a Well to Dryne. and Stability of a Limited Li t of Field Parameter
Wells TW4-3, TW4-6, TW4-7, TW4-10, TW4-12, TW4-13, TW4-14, TW4-26, TW4-27, TW4-
28, TW4-29, TW4-30, TW4-31, TW4-33, TW4-34, TW4-35, TW4-36, and TW4-42 were
pumped to dryness before two casing volumes were evacuated. After well recovery, one set of
measurements of pH, conductivity and temperature were taken. The samples were then collected,
and another set of measurements of pH, conductivity and temperature were taken. Stabilization
of pH, conductivity and temperature are required within 10% RPD under the QAP. The QAP
requirements for stabilization were met.
Continuou ly Pumped Wells
Wells MW-4, TW4-1, TW4-2, TW4-4, TW4-11, MW-26, TW4-19, TW4-21, 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, 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 tha volatile ampJes are required to be pre erved and arrive at the
laboratory with a pH le s than 2. A review of the laboratory data revealed that the volatile
arnpJe. were received at the laboratory with a pH less than 2.
3.4.7 Trip Blank Evaluation
Trip blank results were reviewed to identify any VOC contamination resulting from transport of
the samples. Trip blank checks are provided in Tab I. All of the trip blank samples were
non detect.
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 dupJicate and
original field ample i le · than or equal to 20% unl the mea ured result are Jess than 5
times the requfred detection limit. Thi tandard is 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 RPDs are calculated for the dupbcate pairs for aU analyte
regardle s of whether or not the reported concentrations are greater than 5 times the required
detection limits; however, data are considered noncompliant only when the results are greater
than 5 times the reported detection limit and the RPD is greater than 20%. The additional
duplicate information is provided for information purposes.
Duplicate results were within a 20% RPD in the quarterly samples. Duplicate results are included
in Tab I.
3.4.9 Rinsate Sample Check
Rinsate blank sample checks are provided in Tab I. The rinsate blank sample concentration
levels were compared to the QAP requirements i.e., that rinsate sample concentrations be one
order of magnitude lower than that of the actual well.
Rinsate blank sample TW4-3R had a reported chloroform detection of 1.69 ug/L. TW4-3 was
nondetect for chloroform. Rinsate blank sample TW 4-16R had a reported chloroform detection
of 11.6 ug/L. TW4-16 had a chloroform detection of 248 ug/L. The rinsate blank results for
TW4-3 were outside of acceptance limits for the rinsate blank results.
TW4-3R was collected after decontamination and prior to the pump being used to collect any Ql
2021 chloroform samples. Because the pump was not used prior to the rinsate sample collection,
the detection is not the result of cross contamination. TW 4-16R was collected after the
decontamination was completed after purging well TW4-30 and prior to sampling TW4-16.
TW 4-9 had a chloroform detection of 248 ug IL. The chloroform detection of 248 ug/L in TW 4-
16 is within the historic range of detections and is not likely the result of cross contamination.
10
Prior to the Ql 2021 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 TW4-16 are usable as reported. Even if there were contribution of
chloroform to the sample results, it would bias the data high and would result in a more
conservative data application. EFRI does not believe the data quality has been affected.
3.4.10 Other Laboratory QA/QC
Section 9 .2 of the QAP requires that the laboratory's QNQC 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 QNQC 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 QNQC 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 analyses, but the
QAP does not specify acceptance limits for surrogate recoveries. The analytical data associated
with the routine quarterly sampling met ·the requirement specified in the QAP. The information
from the Laboratory QA/QC Summary Reports indicates that the surrogate recoveries for the
quaiterly chloroform samples were within acceptable laboratory limits for the surrogate
compounds. The requirement in the QAP to analyze surrogate compounds was met and the data
are compliant with the QAP. Furthermore, there are no QAP requirements for surrogate
recoveries.
The QAP, Section 8.1.2 requires that each analytical batch shall be accompanied by a method
blank. The analytical batches routinely contain a blank, which is a blank sample made and
carried through all analytical steps. For the Mill samples, a method blank was prepared for the
analytical methods. Per the approved QAP, contamination detected in analysis of method blanks
will be used to evaluate any analytical laboratory contamination of environmental samples. The
QAP states that non-conformance conditions will exist when contaminant levels in the
samples(s) are not an order of magnitude greater than the blank result. The laboratory reported
that a method blank reported concentrations of methylene chloride below the RL. The method
blank results did not affect any sample results and no further actions are necessary. Method
blank results are included in Tab H.
The information from the Laboratory QA/QC Summary Reports indicates that the LCS
recoveries for the samples were within acceptable laboratory limits for the regulated compounds
as indicated in Tab I. ·
4.0 INTERPRETATION OF DATA
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.
4.1.1 Current Site Groundwater Contour Map
The water level contour maps (See Tab D) indicate that perched water flow ranges from
generally southwesterly beneath the Mill site and tailings cells to generally southerly along the
eastern and western margins of White Mesa south of the tailings cells.
Perched water mounding associated with the wildlife ponds locally changes the generally
southerly perched water flow patterns. For example, northeast of the Mill site, mounding
associated with formerly used wildlife ponds is still evident and disrupts the generally
southwesterly flow pattern, to the extent that locally north-northwesterly flow occurs near MW-
19 and PIEZ-1. The impact of the mounding associated with the northern ponds, to which water
has not been delivered since March 2012, is diminishing and is expected to continue to diminish
as the associated mound decays due to reduced recharge. The perched groundwater mound
associated with the southern wildlife pond is also diminishing due to reduced recharge at that
location.
Not only has recharge from the wildlife ponds impacted perched water elevations and flow
directions at the site, but the cessation of water delivery to the northern ponds, which are
generally upgradient of the nitrate and chloroform plumes at the site, resulted in changing
12
conditions that were expected to impact constituent concentrations and migration rates within the
plumes. Specifically, past recharge from the northern ponds helped limit many constituent
concentrations within the plumes by dilution while the associated groundwater mounding
increased hydraulic gradients and contributed to plume migration. Since use of the northern
ponds was discontinued in March 2012, increases in constituent concentrations in many wells,
and decreases in hydraulic gradients within the plumes, are attributable to reduced recharge and
the decay of the associated groundwater mound. EFRI and its consultants anticipated these
changes and discussed these and other potential effects with DWMRC in March 2012 and May
2013.
The impacts associated with cessation of water delivery to the northern ponds were expected to
propagate downgradient (south and southwest) over time. Wells close to the ponds were
generally expected to be impacted sooner than wells farther downgradient of the ponds.
Therefore, constituent concentrations were generally expected to increase in downgradient wells
close to the ponds before increases were detected in wells farther downgradient of the ponds.
Although such increases were anticipated to result from reduced dilution, the magnitude and
timing of the increases were anticipated to be, and have been, difficult to predict due to the
complex permeability distribution at the site and factors such as pumping and the rate of decay of
the groundwater mound. Because of these complicating factors, some wells completed in higher
permeability materials were expected to be impacted sooner than other wells completed in lower
permeability materials even though the wells completed in lower permeability materials were
closer to the ponds.
In general, chloroform and nitrate concentrations within and in the vicinity of the chloroform
plume appear to have been impacted to a greater extent than nitrate concentrations within and
adjacent to the nitrate plume. This behavior is reasonable considering that the chloroform plume
is generally more directly downgradient of and more hydraulically connected (via higher
permeability materials) to the northern wildlife ponds.
In addition, the southern wildlife pond is in relatively close proximity to the downgradient
(southern) extremity of the chloroform plume. Reduced recharge at the southern pond, and decay
of the associated groundwater mound, can be expected to impact water level behavior and
chloroform and nitrate concentrations in wells within this portion of the chloroform plume.
Localized increases in concentrations of constituents such as chloroform and nitrate within and
near the chloroform plume, and of nitrate and chloride within and near the nitrate plume, may
occur even when these plumes are under control. Ongoing mechanisms that can be expected to
increase constituent concentrations locally as a result of reduced wildlife pond recharge include
but are not limited to:
1) Reduced dilution -the rruxmg 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 prop01tion of the low constituent concentration water.
13
The combined impact of the above two mechanisms was anticipated to be more evident at
cbJoroform pumping wells MW-4, MW-26, TW4-4, TW4-19, and TW4-20 (now abandoned);
nitrate pumping well TW4-22, TW4-24 TW4-25, and TWN-2; and non-pumped wells adjacent
to the pumped wells. Impacts were al o expected to occur over time at wells subsequently added
to the chloroform pumping network: TW4-l TW4-2, TW4-l l , 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 overalJ
impact wa expected to be generally higher constituent concentration in the e wells over time
unti] mas reduction re ulting from pumping and natural attenuation eventually reduces
concentrations. Sh01t-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
well except TW4-4 and TW4-37 which began pumping in the fir t quarter of 2010 and the
second quarter of 2015 re pectively. The third quarter of 2018 wa the fir t quarter that a well-
defined cone of depression was a sociated with TW4-4, primarily the re ult of pumping at
adjacent well TW4-41.
The lack of well-defined capture associated with chloroform pumping well TW4-4 was
con i tent prior to the third quarter of 2018, even though pumping since the first quarter of 2010
has depre sed the water table in the vicinity of this well. The lack of a well-defined cone of
depression near TW4-4 likely resulted from l) variable permeability conditions in the vicinity of
TW4-4 and 2) hi torical relatively low water levels at adjacent well TW4-14.
Nitrate pumping well TW4-22, TW4-24, TW4-25 and TWN-2 tarted pumping during the fir t
quarter of 2013. By the fourth quarter of 2013, operation of the nitrate pumping y tem had
produced well-defined impact on water level . Water level impacts of the nitrate and chloroforn1
pumping y tern overlap· however the long-term interaction between the nitrate and chloroform
pumpjng y terns is evolving and change 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 condition Likely contributed to the lack of a well-
defined cone of depression near chloroform pumping well TW4-4. Change in water level. at
wells immediately south and southeast (downgraclient) ofTW4-4 resulting from TW4-4 pumping
were expected to be muted because TW4-4 is located at a tran ition from relatively high to
relatively low permeability conditions south and southeast of TW 4-4. As will be di cussed
below, the permeability of the perched zone at TW4-6, TW4-26, TW4-29, TW4-30, TW4-31,
14
TW4-33, TW4-34, and TW4-35 is one to two orders of magnitude lower than at TW4-4, and the
permeability at TW4-27 is approximately three orders of magnitude lower than at TW4-4.
Detecting water level drawdowns in wells immediately south and southeast of TW4-4 resulting
from TW4-4 pumping has also been complicated by a general, long-term increase in water levels
in this area that has been attributable to past wildlife pond recharge. Between the fourth quarter
of 2007 and the fourth quarter of 2009 Uust 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 stait 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 TW4-6 is within the hydraulic influence of TW4-4.
Except for TW4-30, which is within the plume again this quarter, water levels in 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 TW 4-6 (remaining outside the plume again this quarter) has also trended
downward since the fourth quarter of 2013. Downward trends are attributable to both the
cessation of water delivery to the wildlife ponds and pumping. Although water levels at some of
the wells marginal to the chloroform plume such as TW4-14, TW4-27 and TW4-31 were
generally increasing until about the first quarter of 2018, these water levels now appear to be
relatively stable. Water level trends at TW4-30, which was incorporated into the chloroform
plume during the fourth quarter of 2020, have been similar to those at TW4-27.
These spatially variable water level trends likely result from pumping conditions, the
permeability distribution, and distance from the wildlife ponds. Wells that are relatively
hydraulically isolated (due to completion in lower permeability materials or due to intervening
lower permeability materials) and that are more distant from pumping wells and the wildlife
ponds, are expected to respond more slowly to pumping and reduced recharge than wells that are
less hydraulically isolated and are closer to pumping wells and the wildlife ponds. Wells that are
more hydraulically isolated will also respond more slowly to changes in pumping.
The previous lack of a well-defined cone of depression associated with TW4-4 was also
influenced by the historically relatively low water level at non-pumping well TW4-14, located
east of TW4-4 and TW4-6. Prior to 2018, although water level differences among these three
wells had diminished, and TW 4-4 has been pumping since 2010, the water level at TW 4-14 was
typically lower than the water level at TW 4-6 and lower to an even greater extent than the water
level at TW4-4. However, since the first quarter of 2018, as a result of pumping at TW4-
4l(adjacent to TW4-4), and declining water levels at TW4-6, the water level at TW4-14 was
typically higher than the water levels at both TW4-4 and TW4-6. During the current quarter the
water level at TW4-14 (approximately 5535.6 feet above mean sea level ["ft amsl"]) is more than
5 feet higher than the water level at TW4-6 (approximately 5530.2 ft amsl), and is nearly 1.6 feet
higher than the water level at TW4-4 (approximately 5534 ft. amsl).
The static water levels at wells TW4-14 and downgradient well TW4-27 (installed south of
TW4-14 in the fourth quarter of 2011) were similar (within 1 to 2 feet) until the third quarter of
2014; both appeared anomalously low. TW4-27 was positioned at a location considered likely to
15
detect any chloroform present and/or to bound the chloroform plume to the southeast and east
(respectively) of TW4-4 and TW4-6. As will be discussed below, groundwater data collected
since installation indicates that TW4-27 does indeed bound the chloroform plume to the
southeast and east of TW4-4 and TW4-6 (respectively); however, chloroform exceeding 70 µg/L
has been detected at more recently installed temporary perched wells TW 4-29 (located south of
TW4-27) and TW4-33 (located between TW4-4 and TW4-29).
Prior to the installation of TW4-27, the persistently low water level at TW4-14 was considered
anomalous because it appeared to be downgradient of all three wells TW 4-4, TW 4-6, and TW 4-
26, yet chloroform had not been detected at TW4-14. Chloroform had apparently migrated from
TW4-4 to TW4-6 and from TW4-6 to TW4-26. This suggested that TW4-26 was actually
downgradient of TW4-6, and TW4-6 was actually 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
(5528.4 feet amsl) is, however, lower than water levels at adjacent wells TW4-6 (5530.2 and
TW4-23 (5532.3 ft. amsl), as shown in the detail water level map under Tab D.
Hydraulic tests indicate that the perineability at TW4-27 is an order of magnitude lower than at
TW4-6 and three orders of magnitude lower than at TW4-4 (see Hydro Geo Chem, Inc. [HGC],
September 20, 2010: Hydraulic Testing of TW4-4, TW4-6, and TW4-26, White Mesa Uranium
Mill, July 2010; and HGC, November 28, 2011: Installation, Hydraulic Testing, and Perched
Zone Hydrogeology of Perched Monitoring Well TW4-27, White Mesa Uranium Mill Near
Blanding, Utah). Past similarity of water levels at TW4-14 and TW4-27, and the low
permeability estimate at TW4-27, suggested that both wells were completed in materials having
lower permeability than nearby wells. The low permeability condition likely reduced the rate of
long-term water level increase at TW4-14 and TW4-27 compared to nearby wells, yielding water
levels that appeared anomalously low. This behavior is consistent with hydraulic test data
collected from more recently installed wells TW4-29, TW4-30, TW4-31, TW4-33, TW4-34 and
TW4-35, which indicate that the permeability of these wells is one to two orders of magnitude
higher than the permeability of TW4-27 (see: HGC, January 23, 2014, Contamination
Investigation Report, TW4-12 and TW4-27 Areas, White Mesa Uranium Mill Near Blanding,
Utah; and HGC, July 1, 2014, Installation and Hydraulic Testing of TW4-35 and TW4-36,
White Mesa Uranium Mill Near Blanding, Utah [As-Built Report]). Hydraulic tests also indicate
that the permeability at 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 at TW4-27 (approximately 5529.2 ft. amsl) is more than 6 feet
lower than the water level at TW4-14 (5535.6 ft. amsl) Increases in water level differences
between TW4-14 and TW4-27 since 2013 are attributable to more rapid increases in water levels
at TW4-14 compared to TW4-27. This behavior likely results primarily from: the relative
positions of the wells; past water delivery to the northern wildlife ponds; and the permeability
distribution. Past seepage from the ponds caused propagation of water level increases in all
directions including downgradient to the south. The relative hydraulic isolation of TW4-14 and
TW4-27 delayed responses at these locations. Until pumping started at TW4-41, water levels at
both these wells were consistently lower than in surrounding higher permeability materials even
though water levels in surrounding materials were generally decreasing due to reduced pond
16
seepage and pumping. Although water levels at TW4-14 and TW4-27 appear to have stabilized,
the previous rate of increase was higher at TW4-14 due to factors that include: closer proximity
to the northern pond seepage source; and a smaller thickness of low permeability materials
separating TW 4-14 from surrounding higher permeability materials. In addition, hydraulic
gradients between TW 4-14 and surrounding higher permeability materials were relatively large
and were consistently directed toward TW4-14 prior to TW4-41 pumping. Slowing of the rates
of water level increase at TW4-14 (since 2015) and TW4-27 (since early 2014), and relative
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-I4 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 TW4-I4, consistent with the lower rate of increase in water levels at TW4-27,
and the earlier reduction in the rate of increase (since early 2014) as discussed above).
The low permeability at TW4-14 and TW4-27 is expected to retard the transport of chloroform
to these wells (compared to nearby wells). As will be discussed in Section 4.2.3, TW4-14 and
TW 4-27 remain outside the plume with current quarter chloroform concentrations of
approximately 1.8 µg/L and 4.7 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 at TW4-30 (located east and cross-to downgradient of TW4-29) exceeded 70 µg/L
for the first time during the previous quarter and was detected at nearly 75 µg/L this quarter.
Consequently, TW4-30 does not bound the plume immediately to the east. However, chloroform.
was not detected at wells TW4-31 (located east of TW4-27), TW4-34 (located south and cross-
to downgradient of TW4-29), nor TW4-35 (located southeast and generally downgradient of
TW4-29).
Data from wells within and adjacent to the southern portion of the chloroform plume indicate
that:
17
1. Chloroform exceeding 70 µg/L at TW4-29 is bounded by concentrations below 70 µg/L at
wells TW4-6, TW4-23, TW4-27, TW4-34, TW4-35 and TW4-42; however, as discussed
above, TW4-30 does not bound the plume immediately to the east. TW4-30 is cross-to
downgradient of TW4-29; TW4-6, TW4-23 and TW4-27 are generally cross-to
upgradient of TW4-29; TW4-34 is generally cross-to downgradient of TW4-29; TW4-42
is generally cross-gradient of TW4-29; and TW4-35 is generally downgradient of TW4-
29.
2. Chloroform concentrations at TW4-33 that are lower than concentrations at TW4-29, and
the likelihood that a pathway exists from TW4-4 to TW4-33 to TW4-29, suggest that
concentrations in the vicinity of TW4-33 were likely higher prior to initiation of TW4-4
pumping, and that lower concentrations currently detected at TW4-33 are due to its closer
proximity to TW4-4.
3. Chloroform concentrations at TW4-26 exceeded 70 µg/L for the first time during the
second quarter of 2017. Chloroform at TW 4-26 is bounded by concentrations below 70
µg/L at TW4-6 and TW4-23 (located up-to cross-gradient of TW4-26); and at TW4-34
(located cross-to downgradient of TW4-26). Chloroform has not been detected at either
TW4-23 or TW4-34. Although chloroform exceeding 70 µg/L was detected at well TW4-
40, installed approximately 200 feet south of TW4-26 in February, 2018, chloroform has
not been detected at TW4-42, installed approximately 200 feet south of TW4-40 in April,
2019. TW4-42 is generally downgradient of both TW4-26 and TW4-40 and bounds the
chloroform plume to the south.
Eventually, TW4-4 pumping, enhanced by operation of adjacent pumping well TW4-41, is likely
to reduce chloroform at both TW4-33 and TW4-29 by cutting off the source. The decrease at
TW4-33 is expected to be faster than at TW4-29 because TW4-33 is in closer proximity to TW4-
4 pumping. Such behavior is expected by analogy with the temporary decreases in chloroform
concentrations that occurred at TW4-6 and TW4-26 once TW4-4 pumping began (discussed in
Section 4.2.3). Since installation in 2013, however, concentrations at TW4-33 appear to be
relatively stable to decreasing; since the third quarter of 2014, concentrations at TW4-29 appear
to be generally increasing (although they appear to have generally stabilized and decreased since
the second quarter of 2020).
Relatively stable to decreasing chloroform at TW4-33 and generally increasing to stable
concentrations at TW4-29 suggest that chloroform migration has been arrested at TW4-33 by
TW4-4 (and TW4-41) pumping and that increased chloroform at downgradient well TW4-29
resulted from a remnant of the plume that continues to migrate downgradient (generally toward
TW4-30, which, until the current quarter, bounded the plume to the east). The influence of TW4-
4 pumping at the distal end of the plume is consistent with generally decreasing water levels at
both TW4-29 and TW4-33. Pumping at TW4-41 since the second quarter of 2018 is expected to
help maintain or enhance this decline.
Decreasing water level trends at TW4-29 and TW4-33 are also consistent with reduced wildlife
pond seepage. The decay of the groundwater mound associated with the southern wildlife pond,
which is 3 to 4 times closer to the southern extremity of the chloroform plume than the northern
ponds, is expected to impact water levels within and adjacent to this portion of the plume.
Reduced wildlife pond seepage, in particular, reduced seepage from the southern wildlife pond,
18
likely contributes to decreasing water level trends at both well ( ince about the fourth quarter of
2013); temporarily increased concentrations at TW4-6 ub equent 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
directions in the southern extremity of the plume are likely to become more southerly, and plume
migration is likely to turn more to the south. An increasingly southerly direction of plume
migration is consistent with increased concentrations at TW4-26.
In addition, generally decreasing concentrations at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 since the third quarter of 2016 . ugge t that TW4-
4 pumping has arrested chloroform migration between TW4-4 and TW4-6 and that increa ed
chloroform at TW4-26 results from a remnant of the plume that continue to migrate south from
TW4-6 to TW4-26. The enhancement of pumpjng in the vicinity of TW4-4 by the tart-up of
TW4-41 pumping in the second quarter of 2018 i likely to increase thi apparent separation and
to have resulted in concentrations at TW 4-6 dropping below 70 µg/L after the second quarter of
2018. Furthermore, the initiation of pumping at TW4-40 during the second quarter of 2019 is
expected to reduce or prevent chloroform migration to the south of TW4-40.
Detectable chloroform concentrations at TW4-14 (since the fourth quarter of 20 J 4) and TW4-27
(since the third quarter of 2015) suggest ongoing, but Jow, downgradient migration of
chloroform from the southeastern extremity of the plume (near TW4-29 and TW4-33) into the
low permeability materials penetrated by TW4-14 and TW4-27. Pumping at TW4-41 is expected
to reduce or prevent future migration of chloroform toward these wells.
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater Contour
Maps for Previous Quarter
The groundwater contour map for the Mill site for the fourth quarter of 2020, as submitted with
the Chloroform Monitoring Report for the fourth quarter of 2020, is attached under Tab E. A
compari on of the water table contour maps for the current quarter (first quarter of 2021) to the
water table contour maps for the previous quarter (fourth quarter of 2020) indicates the
following: water level changes at the majority of site wells were small ( < 1 foot); water level
contours have not changed significantly except in the vicinities of many of the nitrate and
chloroform pumping wells. Overall, total pumping capture is smaller than last quarter.
Drawdown patterns and overall capture associated with pumping of the original chloroform
pumping wells MW-4 MW-26 and TW4-19 have changed a 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 nit.rate pumping welt TW4-22 TW4-24, TW4-25 and TWN-2 in the
first quarter of 2013. Additional large expan ion occurred once chloroform pumping weU
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 expan ion of capture to the south
has resulted from pumping of TW4-41 since the ·econd quarter of 2018 and from initiation of
pumping at TW 4-40 during the second quarter of 2019.
19
The drawdowns at chloroform pumping wells MW-4, TW4-19, TW4-21, TW4-39 and TW4-40;
and nitrate pumping well TWN-2, decreased by more than 2 feet this quarter. However
drawdowns at chloroform pumping wells TW4-1, TW4-2, TW4-4 and TW4-41; and nitrate
pumping well TW4-22 increa. ed by more than 2 feet this quarter. Water level changes at other
nitrate and chloroform pumping wells were 2 fo!t or less, although both increases (decreases in
drawdown) and decreases (increases in drawdown) occurred. Water level fluctuations at
pumping wells typically occur in part becau e of fluctuations in pumping conditions just prior to
and at the time the measurements are taken. The reported water level for chloroform pumping
wells TW4-1, TW4-2 and TW4-11 are is below the depth of the Brushy Basin contact this
quarter. Although both increases and decreases in drawdown occurred in pumping wells, the
overall apparent capture area of the combined pumping system is smaller than last quarter.
As discussed in Section 4.1.1, pumping at chloroform well TW 4-4, which began in the first
quarter of 2010, depressed the water table near TW4-4, but a well-defined cone of depression
was not clearly evident until the third quarter of 2018, likely due to variable permeability
conditions near TW4-4 and the historically relatively low water level at adjacent well TW4-14.
The expanded cone of depression 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 expansion of total pumping system capture. As discussed above, southerly expansion
of capture wa additionally enhanced in the second quarter of 2019 by the initiation of pumping
at TW4-40.
Water levels at Piezometers 2 and 3A were relatively unchanged this quarter; past decreases
likely resulted from cessation of water delivery to the northern wildlife ponds as discussed in
Section 4.1.1 and the consequent continuing decay of the a ociated perched water mound.
Reported water level decreases of approximately 0.03 and 0.05 feet, respectively, at TWN-1 and
TWN-4 are also consistent with continuing decay of the northern groundwater mound. The
reported water level decrease of 0.05 feet at Piezometer 4 UkeJy re ult primarily from reduced
recharge at the southern wildlife pond.
The reported water level at MW-20 increased by more than 2.4 feet. Water level variability at
this well likely results from low permeability and variable intervals between purging/sampling
and water level measurement. The reported water level increase at MW-20 partially compensates
for the reported decrease last quarter.
Measurable water was not reported at DR-22. Although DR-22 is typically dry, measurable
water was reported in the bottom of its casing between the second quarter of 2015 and the third
quarter of 2016.
4.1.3 Hydrographs
Attached under Tab F are hydrographs showing groundwater elevation in each chloroform
contaminant investigation monitor well over time.
20
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; TW4-4 since 2010; TW4-l,
TW4-2, TW4-l 1, TW4-21 and TW4-37 since 2015; TW4-39 since the fourth quarter of 2016;
TW4-41 since the second quarter of 2018; and TW4-40 since the second quarter of 2019. TW4-
20 was also operated as a pumping well from 2005 until August, 2020 when it collapsed and was
subsequently abandoned. The primary purpose of pumping the above wells is to reduce total
chloroform mass in the perched zone as rapidly as is practical.
The original pumping wells up gradient of TW 4-4 were chosen because 1) they were located in
areas of the perched zone having relatively high permeability and saturated thickness, and 2)
high concentrations of chloroform were detected at these locations. The relatively high
transmissivity of the perched zone in the vicinity of these original pumping wells resulted in the
wells having a relatively high productivity. The combination of relatively high productivity and
high chloroform concentrations allowed for a high rate of chloroform mass removal. TW 4-4 and
TW4-41 are located in a downgradient area having reJatively high chloroform concentration but
relatively small saturated thickness, and at a tran sition from relatively high to relatively low
permeability conditions downgradient of TW 4-4. As with the other chloroform pumping wells,
pumping TW4-4 and TW4-41 helps to reduce the rate of chloroform migration in downgradient
portions of the plume.
Although pumping of TW 4-6 and TW 4-26 (located south of TW 4-4 and TW 4-41) is impractical
due to low permeability and small saturated thicknesses, the permeability in the vicinity of TW 4-
40 (located south of TW4-26) is large enough to make pumping practical. TW4-40 is valuable in
that it is located within the downgradient (southern) toe of the plume and is relatively productive.
Pumping of TW4-40 is likely to more effectively reduce or prevent further downgradient plume
migration than can be expected by pumping at the more upgradient locations.
The impact of chloroform pumping is indicated by the water level contour 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. Except for TW4-20, which collapsed in August, 2020 and was abandoned in October,
2020 these well continue to remove ignificant quantities of chloroform from the perched zone.
Relatively Jarge cone · of depression have developed in the vicinities of well. TW4-1, TW4-2
and TW4-l l which began pumping during the first quarter of 2015. A di cussed in Section
4.1.1, although chloroform pumping well TW 4-4 became operational in 2010, the draw down
associated with TW4-4 was likely less apparent due to variable permeability conditions near
TW4-4 and the persi tently low water Jevel at adjacent well TW4-14. However, pumping at
adjacent well TW4-41 since the econd quarter of 2018 has generally increased drawdowns in
this area; the third quarter of 2018 wa the first quarter that a weU-defined cone of depre sion
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
21
contributed to southerly expansion of total pumping system capture. Overall, the water level
contour maps indicate effective capture of water containing high chloroform concentrations in
the vicinities of the pumping wells.
Compared to last quarter, both increases and decreases in water levels occurred at nitrate and
chloroform pumping wells, although changes in water levels in chloroform pumping wells MW-
26, TW4-11 and TW4-37; and nitrate pumping wells TW4-24 and TW4-25 were less than two
feet. Water level decreases occurred in chloroform pumping wells TW4-1 (approximately 6.9
feet); TW4-2 (nearly 7.7 feet); TW4-4 (nearly 2.6 feet); TW4-37 (approximately 0.7 feet); and
TW4-41 (nearly 2.7 feet); and in nitrate pumping well TW4-22 (approximately 4.5 feet). Water
level increases occurred in chloroform pumping wells MW-4 (nearly 4.4 feet); MW-26 (0.04
feet); TW4-11 (0.03 feet); TW4-19 (nearly 3.3 feet); TW4-21 (nearly 6.2 feet); TW4-39
(approximately 3.6 feet); and TW4-40 (nearly 3.1 feet); and in nitrate pumping wells TW4-24
(approximately 1.1 feet); TW4-25 (nearly 0.5 feet); and TWN-2 (approximately 6.1 feet). The
overall apparent combined capture area of the nitrate and chloroform pumping systems is smaller
than last quarter; capture decreased within the northern and southern portions of the combined
pumping system due primarily to decreased drawdowns at TW4-19, TW4-21, TW4-39, TW4-40
and TWN-2.
The capture associated with nitrate pumping wells and chloroform pumping wells added since
the beginning of 2015 is expected to generally increase over time as water levels continue to
decline due to cessation of water delivery to the northern wildlife ponds and continued pumping.
Slow development of hydraulic capture in the vicinities of many wells is consistent with and
expected based on the relatively low permeability of the perched zone at the site.
The hydraulic capture effectiveness of both chloroform and nitrate pumping systems depends to
some extent on the continued productivity of chloroform and nitrate pumping wells. Decreases in
productivity since the third quarter of 2014 have been noted in chloroform pumping well TW 4-
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, TW4-21,
TW4-22, TW4-24, TW4-37, TW4-39, TW4-40 and TW4-41) is approximately 5.2 gpm.
Pumping from TW4-20 is not included as it was abandoned in October, 2020.
The pumping calculation is based on the total volume pumped by the above wells over the 90
day quarter (679,538 gallons) and accounts for times that the pumps are off due to insufficient
22
water columns in the wells. Pumping from these wells exceeds the calculated background flow
by 1.8 gpm or 53 %, and is considered adequate at the present time even with the reduced
productivities of some wells. In addition, because of continued reductions in saturated
thicknesses and hydraulic gradients resulting from reduced wildlife pond recharge, 'background'
flow through the plume is expected to continue to diminish, thereby reducing the pumping
needed to control the plume.
Chloroform concentrations at many locations have been or appear to be affected by changes
associated with reduced dilution from the wildlife ponds and nitrate pumping. For example,
increases in chloroform at TW4-22 and TW4-24 after these wells were converted to nitrate
pumping wells are attributable to westward migration of chloroform from the vicinity of TW 4-20
toward these wells. The increase in concentration at TW 4-8 from non-detect to 100 µg/L in the
first quarter of 2014 is likely related to reduced dilution. The concentration at TW4-8 remained
below 70 ug/L this quarter after dropping below 70 µg/L during the first quarter of 2020. In
addition, although the chloroform concentration in TW4-6 generally decreased between the first
quarter of 2015 and the current quarter (and remains outside the plume), concentrations at TW4-
6 increased from approximately 6 µg/L in the first quarter of 2014 to 1,180 µg/L in the first
quarter of 2015 before dropping to 3.8 µg/L this quarter. The increase between the first quarter
of 2014 and the first quarter of 2015 was likely related to both reduced dilution and more
westward flow induced by nitrate pumping.
TW 4-6 is located immediately south and historically cross-to downgradient of chloroform
pumping well TW 4-4. TW 4-6 has been incorporated into the chloroform plume twice: from the
first quarter of 2009 through the third quarter of 2010; and from the third quarter of 2014 through
the second quarter of 2018. Pumping of TW4-6 (and TW4-26) is impractical because of
relatively low permeability and relatively small saturated thicknesses. However, pumping at
more productive locations upgradient of TW4-6 (such as TW4-4 and TW4-41) enhances mass
removal and lowers hydraulic gradients, thereby reducing the rate of downgradient chloroform
migration and allowing natural attenuation to be more effective. Pumping at TW4-4 was
implemented during the first quarter of 2010 to improve capture downgradient of TW4-4 to the
extent allowable by the lower productivity conditions present in this area.
The beneficial effect of pumping TW 4-4 was demonstrated by the net decreases in TW 4-6
chloroform concentrations from 1,000 µg/L to 10.3 µg/L, and in TW4-26 from 13 µg/L to 4.2
µg/L, between the initiation of TW4-4 pumping and the second quarter of 2014. Concentrations
at these wells decreased substantially even though they did not unambiguously appear to be
within the hydraulic capture of TW 4-4. As discussed in Section 4.1.1, however, the decrease in
the long-term rate of water level rise at TW 4-6 after TW 4-4 began pumping does suggest that
TW 4-6 was within the hydraulic influence of TW 4-4. The decline in water levels at TW 4-6 since
the fourth quarter of 2013 likely reflects the additional influences of cessation of water delivery
to the wildlife ponds and the addition of chloroform pumping wells TW4-1, TW4-2, TW4-11
and TW4-41. Regardless of whether TW4-6 was demonstrably within the hydraulic capture of
TW4-4, pumping TW4-4, and relatively recently installed adjacent pumping well TW4-41, helps
to reduce chloroform migration to TW4-6, TW4-26, and other downgradient locations by the
mechanisms discussed above.
23
Likewise, pumping at other productive upgradient locations has a beneficial impact on
downgradient chloroform even if the downgradient chloroform is not completely within the
hydraulic capture of the productive upgradient well(s). For example, pumping at MW-26 likely
reduced chloroform concentrations at TW 4-16 from a maximum of 530 µg/L in the second
quarter of 2004 to less than 70 µg/L by the fourth quarter of 2005, and maintained concentrations
below 70 µg/L until the second quarter of 2014, even though TW4-16 appears to be beyond the
hydraulic capture of MW-26. Furthermore, the overall hydraulic capture of the chloroform
pumping system has expanded since initiation of pumping at wells TW4-1, TW4-2, TW4-ll
TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 since the beginning of 2015. In particular, the
addition of wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-37 and TW4-39 likely halted the
mid-2013 to end of 2014 increase in concentration at TW4-16 from non-detect to 387 µg/L.
Concentrations at TW4-16 dropped from 387 µg/L in the fourth quarter of 2014 to less than 70
µg/L by the second quarter of 2015. Although chloroform at TW4-16 has been above and below
70 µg/L since 2014, and was detected at 248 µg/L this quarter, concentrations have generally
increased since 2018, likely in response to reduced dilution.
Chloroform exceeding 70 µg/L was detected in the second quarter of 2013 at TW4-29, installed
during the first quarter of 2013 and located south of TW4-27 and east of TW4-26. With respect
to historic groundwater flow directions implied by historic groundwater elevations in this area,
TW4-29 was positioned generally cross-gradient of TW4-4 and TW4-6. As discussed in Section
4.1.1, chloroform detected at TW4-29 may have migrated around the low permeability area
defined by TW4-27, TW4-14 ru1d TW4-36. The apparent migration pathway from TW4-4 to
TW4-29 i con i tent with chloroform exceeding 70 µg/L detected in the fourth quarter of 2013
at TW4-33, installed during the third quarter of 2013 and located between TW4-4 and TW4-29.
Chloroform concentrations at TW4-33 that are lower than concentrations at TW4-29, and the
likelihood that a pathway exists from TW4-4 to TW4-33 to TW4-29, suggest that concentrations
in the vicinity of TW 4-33 were likely higher prior to initiation of TW 4-4 pumping.
TW4-4 pumping (augmented by pumping at adjacent well TW4-41) is likely to eventually
reduce cbJorofonn at both TW4-33 and TW4-29 by cutting off the ource. The impact at TW4-
33 i expected to be greater than at TW4-29 becau e TW4-33 is in closer proximHy 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. Since the third quarter of 2014 concentrations at TW4-29 have
increased, although since the second quarter of 2020 they appear stable to decreasing. As
discussed in Section 4.1.1, although decreasing concentration trends at both wells are eventually
expected to occur, relatively stable to decreasing chloroform at TW 4-33 and increased to stable
concentrations 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 to stable
chloroform at downgradient well TW4-29 results from a remnant of the plume that continues to
migrate downgradient (toward TW4-30, which, until the fourth quarter of 2020, bounded the
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
24
is 3 to 4 times closer to the southern extremity of the chloroform plume than the northern ponds,
is likely to have an impact on water levels within and adjacent to this portion of the plume.
As discussed in Section 4.1.1, generally decreasing water level trends at TW4-6 and TW4-26
(since about the fourth quarter of 2013), temporarily increased concentrations at TW4-6 (since
the first quarter of 2014) and increased 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 southern pond
decays, groundwater flow directions in the southern extremity of the plume are likely to become
more southerly, and plume migration is likely to turn more to the south. An increasingly
southerly direction of plume migration is consistent with increased concentrations at TW4-26
(from less than 10 µg/L in the third quarter of 2016 to 1,030 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 TW 4-4 by the start-up of TW 4-41 pumping in the second quarter of
2018 is likely to increase this apparent separation and to have resulted in concentrations at TW4-
6 dropping below 70 µg/L beginning in the third quarter of 2018.
Furthermore, detectable chloroform concentrations at TW 4-14 (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. From 2014 through 2019 chloroform
concentrations at TW4-8 exceeded 70 µg/L and TW4-36 (non-detect for chloroform) served as
an eastern bounding well. However, chloroform at TW 4-8 remained below 70 µg/L during 2020
and continues to bound the chloroform plume to the east.
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 111.B.2.a through Part 111.B.2.c of the GCAP) are provided in Tab L.
4.2.2 Chloroform Concentration Trend Data and Graphs
Attached under Tab K are tables summarizing values for all required parameters, chloride,
nitrate/nitrite, carbon tetrachloride, chloroform, chloromethane, and methylene chloride, for each
well over time.
25
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, TW4-19, TW4-22, TW4-24, TW4-39 and TW4-40;
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: TW4-8, TW4-10, TW4-14, TW4-21 and TW4-27;
c) Chloroform concentrations have remained within 20% in the following wells compared
to last quarter: MW-4, TW4-1, TW4-2, TW4-4, TW4-5, TW4-6, TW4-7, TW4-9, TW4-
11, TW4-16, TW4-18, TW4-26, TW4-29, TW4-30, TW4-33, TW4-37 and TW4-41; and
d) Chloroform concentrations have remained non-detect in the following wells: MW-32,
TW4-3, TW4-12, TW4-13, TW4-23, TW4-25, TW4-28, TW4-31, TW4-32, TW4-34,
TW4-35, TW4-36, TW4-38 and TW4-42.
As indicated, chloroform concentrations at many of the wells with detected chloroform were
within 20% of the values reported for the wells during the previous quarter, suggesting that
variations are within the range typical for sampling and analytical error. Wells MW-26, TW4-8,
TW4-10, TW4-14, TW4-19, TW4-21, TW4-22, TW4-24, TW4-27, TW4-39 and TW4-40 had
changes in concentration greater than 20%. Of these, MW-26, TW4-19, TW4-21, TW4-39, and
TW4-40 are chloroform pumping wells; and TW4-22 and TW4-24 are nitrate pumping wells.
TW 4-8 is located adjacent to chloroform pumping well MW-4; TW 4-10 is located adjacent to
chloroform pumping wells MW-26 and TW4-11; TW4-14 is located adjacent to chloroform
pumping wells TW4-4 and TW4-41; and TW4-27 is located just outside the plume boundary.
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 TW4-14 and TW4-27 are expected based on their locations near
the plume margins.
Chloroform pumping wells MW-26 (3,060 µg/L); TW4-11 (2,750 µg/L); TW4-19 (6,660 µg/L);
TW4-37 (9,380 µg/L); and TW4-39 (2,970 µg/L); and nitrate pumping well TW4-22 (5,100
µg/L), had the highest detected chloroform concentrations. Although pumping well TW4-20,
formerly located between pumping wells TW4-19 and TW4-37, would typically be distinguished
as having one of the highest concentrations, TW4-20 collapsed during August, 2020 and was
abandoned in October, 2020.
Since last quarter, the chloroform concentrations in MW-26 increased from 866 to 3,060 µg/L;
TW4-11 increased from 2,670 to 2,750 µg/L; TW4-19 increased from 660 to 6,660 µg/L; TW4-
37 decreased from 10,300 µg/L to 9,380 µg/L; and TW4-39 increased from 648 to 2,970 µg/L. In
addition, the chloroform concentration in chloroform pumping well TW4-21 decreased from 948
26
to 400 µg/L; the concentration in nitrate pumping well TW4-22 increased from 3,640 to 5,100
µg/L; and the concentration in nitrate pumping well TW4-24 increased from 72.6 to 96.2 µg/L,
remaining just within the plume boundary this quarter. Nitrate pumping well TW4-25 remained
non-detect. TW4-25, located north of TW4-21, bounds the chloroform plume to the north.
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased from 51.3 µg/L to 26.9 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 1,150 µg/L. Although the plume boundary remained between MW-
4 and TW4-8 from the first quarter of 2005 through the fourth quarter of 2013, TW4-8 was re-
incorporated into the plume between the first quarter of 2014 and the fourth quarter of 2019.
Elevated chloroform at TW4-8 was 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 (which has remained below 10 µg/L). Although previously elevated, TW4-
8 remained outside of and bounded the plume during 2020, and remains outside of and bounds
the plume this quarter. Changes in the plume boundary near TW 4-8 are expected to result from
changes in pumping and reduced dilution resulting from cessation of water delivery to the
northern wildlife ponds.
Chloroform at TW4-29 (located at the southeastern extremity of the plume, to the east of TW4-
26 and to the south of TW4-27) decreased from 671 µg/L to 577 µg/L; and chloroform at TW4-
30, located immediately cross-to downgradient of TW4-29, decreased from nearly 83 µg/L to
nearly 75 µg/L, remaining within the plume. Chloroform at TW4-14 decreased from
approximately 2.7 µg/L to 1.8 µg/L and chloroform at TW4-27 decreased from approximately
7.8 µg/L to 4.7 µg/L. Concentration trends at these wells are generally consistent with ongoing,
but slow, downgradient migration of chloroform at these locations. For example, it took more
than 51 quarters for detectable chloroform at TW4-4 to migrate approximately 400 feet
downgradient to TW4-14; and it took more than 30 quarters for chloroform exceeding 70 µg/L at
TW4-29 to migrate approximately 160 feet downgradient to TW4-30.
In addition, as discussed in Section 4.1.1, general increases in concentrations at TW4-26 since
the third quarter of 2016 are also consistent with continuing downgradient chloroform migration
which is likely enhanced by the decay of the groundwater mound associated with the southern
wildlife pond. Recent increases in concentration at TW4-26 have widened the southeast
extremity of the plume which historically was narrow compared to more upgradient locations.
Chloroform at TW4-29 is bounded to the north by TW4-27 (approximately 4.7µg/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 3.8 µg/L) and TW4-23 (non-detect). As a consequence of
the increase at TW4-30 last quarter, TW4-30 does not bound the plume immediately to the east.
Chloroform at TW4-33 (located between TW4-4 and TW4-29) showed a decrease in
concentration, from less than 81 µg/L to less than 65 µg/L. Chloroform at TW4-33 is bounded
to the north by TW4-14 (approximately 1.8 µg/L), to the east by TW4-27 (approximately 4.7
µg/L), and to the west by TW4-6 (approximately 3.8 µg/L) and TW4-23 (non-detect).
27
The chloroform concentration in TW4-6 decreased from approximately 4.6 µg/L to 3.8 µg/L.
TW 4-6 has remained outside the chloroform plume since the third quarter of 2018. Installed in
the second quarter of 2000, TW4-6 was the most downgradient temporary perched well prior to
installation of TW4-23 in 2007 and TW4-26 in the second quarter of 2010. TW4-6 remained
outside the chloroform plume between installation in the second quarter of 2000 and the fourth
quarter of 2008 likely due to a combination of 1) slow rates of downgradient chloroform
migration in this area due to low permeability conditions and the effects of upgradient
chloroform removal by pumping, and 2) natural attenuation. TW4-6 was subsequently
incorporated into the plume twice: from the first quarter of 2009 through the third quarter of
2010; and from the third quarter of 2014 through the second quarter of 2018. Between initiation
of pumping of TW4-4 in the first quarter of 2010 and the second quarter of 2014, concentrations
at TW4-6 showed a net decrease from 1,000 µg/L to 10.3 µg/L.
The relatively slow rate of chloroform migration in the vicinity of TW 4-6 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 TW 4-6 to increase from non-detect to only 81 µg/L. This behavior is consistent
with hydraulic tests performed at TW4-4, TW4-6, and TW4-26 during the third quarter of 2010
that indicate a nearly two orders of magnitude decrease in permeability south (downgradient) of
TW4-4. Chloroform migration rates in the vicinities of wells TW4-26, TW4-29 and TW4-33
have been expected to be relatively slow due to upgradient pumping and relatively low
permeability conditions. By analogy with the decreases in concentration at TW4-6 and TW4-26
that occurred after initiation of TW4-4 pumping, chloroform concentrations at both TW4-29 and
TW4-33 are expected to eventually trend downward.
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for slight
contractions near TW4-8, TW4-16 and TW4-21; and slight expansion near TW4-24. The
chloroform concentration increase at TW4-24, from approximately 72.6 µg/L to 96.2 µg/L
caused slight expansion of the plume boundary to the west of TW4-24. The concentration
decreases at TW4-8 (from approximately 51 µg/L to 27 µg/L); at TW4-16 (from approximately
270 µg/L to 248 µg/L); and at TW4-21 (from approximately 948 µg/L to 400 µg/L); caused
slight contractions of the plume boundary. Similar to the last four quarters, due primarily to
decreases 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. TW4-9 was incorporated into the plume from
the first quarter of 2016 until the first quarter of 2019 due to increased concentrations attributable
to reduced recharge (and dilution) from the northern wildlife ponds. 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 is again just within the plume this quarter.
TW4-24 likely remained primarily outside the plume since 2014 due to initiation of TW4-37
28
pumping in the second quarter of 2015 and reduced productivity at TW4-24 (since the third
quarter of 2014). Subsequent to the first quarter of 2014, generally higher concentrations at
TW4-6 and TW4-16 (both of which were within the chloroform plume in the past) caused the
plume boundary to migrate to the southwest and temporarily re-incorporate both wells. This
increase was likely related to reduced dilution from cessation of water delivery to the northern
wildlife ponds and more westerly flow induced by nitrate pumping. fu addition, concentrations at
TW 4-6 are likely influenced by reduced recharge at the southern wildlife pond and the decay of
the associated groundwater mound.
TW4-6 has remained outside the plume since the third quarter of 2018 due to the general
decrease in chloroform concentrations since the third quarter of 2015, while (as discussed in
Section 4.1.5) TW4-16 has been both within and outside the plume. This quarter, although TW4-
6 remains outside the plume, 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 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
TW 4-6 to TW 4-26. This behavior is consistent with the apparent 'pinching-off of the southern
extremity of the plume since the end of 2019. Regardless, pumping at TW4-41, located adjacent
to TW 4-4, and pumping at TW 4-40, located just south ( downgradient) of TW 4-26, 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 like I y the result of initiation of TW 4-1, TW 4-2, and
TW4-11 pumping during 2015. Maintaining reduced concentrations at TW4-6 is anticipated to
result from pumping at TW 4-41.
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND TW4-4
OPERATIONS REPORT
5.1 Introduction
As a part of the investigation of chloroform contamination at the Mill site, EFRI has been
conducting a Long Term Pump Test on MW-4, TW4-19, MW-26, and TW4-20, and, since
January 31, 2010, TW4-4. The purpose of the test is to serve as an interim action that will
remove a significant amount of chloroform-contaminated water while gathering additional data
on hydraulic properties in the area of investigation. TW4-20 collapsed in August of 2020 and
was abandoned in October 2020.
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
29
(the "SCO") dated December 12, 2012. Because wells TW4-22, TW4-24, and TW4-25 are
chloroform program wells, they are included in this report and any chloroform removal realized
as part of this pumping is calculated and included in the chloroform quarterly reports.
Beginning on January 14, 2015, EFRI began long term pumping of TW4-1, TW4-2, and TW4-11
and began long term pumping of TW4-21 and TW4-37 on June 9, 2015. Beginning in December
2016 EFRI began long term pumping of TW4-39. Beginning in April 2018 EFRI began long
term pumping of TW 4-41. Beginning in May 2019 EFRI began long term pumping of TW 4-40.
The following information documents the operational activities during the quarter.
5.2 Pump Test Data Collection
The long term pump test for MW-4 was started on April 14, 2003, followed by the start of
pumping from TW4-19 on April 30, 2003, from MW-26 on August 8, 2003, from TW4-20 on
August 4, 2005, from TW4-4 on January 31, 2010, and from TW4-22, TW4-24, and TW4-25 on
January 26, 2013. Personnel from Hydro Geo Chem, Inc. were on site to conduct the first phase
of the pump test and collect the initial two days of monitoring data for MW-4. EFRI personnel
have gathered subsequent water level and pumping data.
Analyses of hydraulic parameters and discussions of perched zone hydro geology 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-l 1, TW4-
19, MW-26, 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, and regularly after
March 1, 2010 for TW4-4, water levels in these wells have been measured weekly. From
commencement of pumping, water levels in wells TW 4-1, TW 4-2, TW 4-11, TW 4-21, TW 4-22,
TW4-24, TW4-25, TW4-37, TW4-39, TW4-41, and TWN-2 have been measured weekly. Depth
to groundwater in all other chloroform contaminant investigation wells is monitored monthly.
Copies of the weekly Depth to Water monitoring sheets for MW-4, MW-26, TW4-1, TW4-2,
30
TW4-11, TW4-19, TW4-21, TW4-4, TW4-22, TW4-24, TW4-25, TW4-37, TW4-39, TW4-40
(beginning May 2019), TW4-41 and TWN-2 and the monthly Depth to Water monitoring sheets
for the chloroform contaminant investigation wells and the selected temporary wells and
permanent monitoring wells are included under Tab C. Monthly depth to water measurements
for the quarter are recorded in the Field Data Worksheets included under Tab C.
5.4 Pumping Rates and Volumes
Table G-2 summarizes the recovered mass of chloroform by well per quarter and historically
since the inception of the chloroform recovery program for the active pumping wells. It is
important to note that TWN-2 is a nitrate program well and is sampled only for nitrate and
chloride as required by the nitrate program. Because TWN-2 is not sampled or analyzed for
chloroform, the mass of chloroform recovered is not calculated.
The pumping wells do not pump continuously, but are on a delay device. The wells purge for a
set amount of time and then shut off to allow the well to recharge. Water from the pumping
wells is transferred to a holding tank. The water in the holding tank is used in the Mill processes.
The pumping rates and volumes for each of the pumping wells are shown in Table G-3.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Specific operational problems observed with the well or pumping equipment which occurred
during the quarter are noted for each well below.
Unless specifically noted below, no operational problems were observed with the well or
pumping equipment during the quarter.
5.5 Mass Removed and Plume Residual Mass
Chloroform removal was estimated as of the first quarter 2007. Since that estimation, the mass
removed by well for each quarter has been compiled in Table G-2, which shows the pounds of
chloroform that have been removed to date. The mass of chloroform removed from the plume
this quarter is approximately 16.8 lb., which is 75% larger than the approximately 9.6 lb.
removed last quarter. The larger rate of mass removal is attributable primarily to the increased
concentrations at TW4-19 and TW4-39.
The residual mass of chloroform within the plume is estimated as 1,273 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 558 lb. larger than last quarter's estimate of 715 lb. As per Part
111.B.2 of the GCAP, electronic files used in calculating the mass estimate are provided with this
report. Details of the procedure are provided in Tab L.
The residual mass is plotted in Figure L.1. Since the third quarter of 2015 the trend is downward;
the current quarter's estimate of 1,273 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
31
the trendline updated as per Part 111.B.3 of the GCAP.
As discussed in the CACME Report, the calculated chloroform mass is larger since the cessation
of water delivery to the two northern wildlife ponds in the first quarter of 2012. These ponds are
located immediately upgradient of the chloroform plume. The increase in calculated mass results
from increased plume area and increased average concentrations within the plume. The increases
in both plume area and average concentrations are attributable to reduced dilution due to the
reduction in chloroform-free wildlife pond seepage.
The general decrease in the residual mass estimates since the second quarter of 2016 suggests
stabilization. Although the residual mass estimates are generally larger since 2012, the rate of
mass removed per quarter by pumping is also generally larger. Mass removal rates were
particularly enhanced after the addition of 5 new pumping wells in 2015; and the subsequent
addition of 3 additional pumping wells has helped maintain mass removal rates. Furthermore,
although the pumping system is not designed to hydraulically capture the entire plume, the
proportion of the mass of the plume under capture has historically been large. The proportion of
the mass of the plume under capture during the fourth quarters of 2012, 2013, 2014, 2015, 2016,
2017, 2018, 2019 and 2020 ranged from approximately 84% to 99%. The approximate
proportion of the mass of the plume under capture this quarter is 89%, about the same as last
quarter, even though overall capture is smaller than last quarter.
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 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), except at the location of TW4-30. As discussed in Section 2.4.3, TW4-30 does not
bound the plume immediately to the east this quarter due to the increase in concentration last
quarter that brought TW4-30 into the plume for the first time.
32
However, the plume is bounded to the north by TW4-25 (non-detect); to the west and southwest
by MW-28 (non-detect), MW-31 (non-detect), MW-32 (non-detect), TW4-6 (approximately 3.8
µg/L) and TW4-23 (non-detect); to the east by TW4-3 (non-detect), TW4-5 (nearly 13 µg/L),
TW4-8 (nearly 27 µg/L), TW4-9 (approximately 39 µg/L), TW4-13 (non-detect), TW4-14
(approximately 1.8 µg/L), TW4-18 (approximately 52 µg/L), TW4-27 (nearly 4.7 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).
Except for TW4-30, located in the southeastern extremity of the plume, data collected to date
indicate there are sufficient chloroform monitoring and pumping wells to effectively define,
control, and monitor the plume. Subsequent data will determine whether or not TW4-30 remains
within the plume and can serve (as in the past) as a bounding well. Regardless of whether or not
TW4-30 remains within the plume, site water level data indicate that perched groundwater flow
to the east of TW 4-30, along the eastern site property boundary, is to the south-southwest;
therefore it is unlikely that any chloroform within this portion of the plume could ever migrate
across the eastern property boundary. In addition, chloroform in the vicinity of TW4-30 is
migrating relatively slowly; it took more than 30 quarters for chloroform exceeding 70 µg/L at
TW4-29 to migrate approximately 160 feet to TW4-30. Furthermore, hydraulic gradients from
TW4-29 to TW4-30 that are now nearly non-existent as a result of long-term decline is expected
to reduce chloroform migrations rates in this area.
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 wells were maintained and
operated as required. Additional details regarding any specific pumping well operations and
maintenance issues noted during the quarter are discussed in Section 5.0 above.
7.3 Disposal of Extracted Groundwater
Part II of the GCAP requires that all extracted groundwater be disposed of in the tailings
management system or fed in the Mill process. All extracted groundwater was handled as
required by the GCAP.
33
7.4 Compliance Well Performance
Part 11.G of the GCAP states that an exceedance of the compliance well performance standard is
defined as the presence of chloroform in any compliance monitoring well in excess of 70 ug/L
for two or more quarters.
The compliance well chloroform concentrations were below the 70 ug/L except for TW4-30. As
noted above, an exceedance is defined as the presence of chloroform in any compliance
monitoring well in excess of 70 ug/L for two or more quarters. The previously reported
chloroform concentration for TW4-30 was 82.8 ug/L and the current concentration is 74.8 ug/L.
Because an exceedance of chloroform in TW 4-30 has been reported two or more consecutive
quarters, an Exceedance Notice and Plan and Time Schedule are required and will be submitted
in accordance with the schedule required by the GCAP. A copy of the Exceedance Notice is
included in Tab N.
7.5 Chloroform Plume Monitoring for Wells within 500 Feet of the Property Boundary
Currently there are no compliance wells within 500 feet of the property boundary.
8.0 CONCLUSIONS AND RECOMMENDATIONS
The residual mass of chloroform within the plume is estimated as 1,273 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 558 lb. more than last quarter's estimate of 715 lb.
The mass of chloroform removed from the plume this quarter by pumping, approximately 16.8
lb., is 75 % larger than the mass removed last quarter (approximately 9.6 lb.). The larger mass
removal is attributable primarily to the increased concentrations at TW4-19 and TW4-39.
The chloroform plume is entirely contained 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) except at the location of TW4-30. As discussed in Section 2.4.3, TW4-30 does not
bound the plume immediately to the east this quarter due to the increase in concentration last
quarter that brought TW4-30 into the plume for the first time.
However, the plume is bounded to the north by TW4-25 (non-detect); to the west and southwest
by MW-28 (non-detect), MW-31 (non-detect), MW-32 (non-detect), TW4-6 (approximately 3.8
µg/L) and TW4-23 (non-detect); to the east by TW4-3 (non-detect), TW4-5 (nearly 13 µg/L),
TW4-8 (nearly 27 µg/L), TW4-9 (approximately 39 µg/L), TW4-13 (non-detect), TW4-14
(approxjmately 1.8 µg/L), TW4-18 (approximately 52 µg/L), TW4-27 (nearly 4.7 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 quarte1· of 2018. Because the econd
quarter of 2018 wa the second con ecutive quarter that chloroform in TW4-40 exceeded 70
µg/L the required Plan and Time Schedule was submitted and TW4-42 was in talled
34
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).
Except for TW4-30, located in the southeastern extremity of the plume, data collected to date
indicate there are sufficient chloroform monitoring and pumping wells to effectively define,
control, and monitor the plume. Subsequent data will determine whether or not TW4-30 remains
within the plume and can serve (as in the past) as a bounding well. Regardless of whether or not
TW 4-30 remains within the plume, site water level data indicate that perched groundwater flow
to the east of TW4-30, along the eastern site property boundary, is to the south-southwest;
therefore it is unlikely that any chloroform within this portion of the plume could ever migrate
across the eastern property boundary. In addition, chloroform in the vicinity of TW4-30 is
migrating relatively slowly; it took more than 30 quarters for chloroform exceeding 70 µg/L at
TW4-29 to migrate approximately 160 feet to TW4-30. Furthermore, hydraulic gradients from
TW4-29 to TW4-30 that are now nearly non-existent as a result of long-term decline is expected
to reduce chloroform migrations rates in this area.
The water level contour maps for the first quarter, 2021 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 TW 4-1, TW 4-2, and TW 4-11 during the first quarter of 2015. Capture in the
northwestern portion of the plume was enhanced by start-up of chloroform pumping wells TW4-
21 and TW4-37 during the second quarter of 2015; and of TW4-39 during the fourth quarter of
2016. Capture in the southernmost portion of the plume was enhanced by start-up of pumping at
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 chlor9form pumping well TW4-4 until the third quarter of 2018. Increased drawdowns
in this area since the second quarter of 2018, and development of a definable capture zone, is
attributable to pumping at adjacent well TW4-41.
The capture zone associated with TW4-4 was likely obscured prior to the second quarter of 2018
by the historically relatively low water level at adjacent well TW4-14 and the two orders of
magnitude decrease in permeability south of TW4-4. However, as noted in previous reports,
between the first quarter of 2010 and the second quarter of 2014, decreases in chloroform
concentrations and the rate of water level rise at TW4-6 (located downgradient of TW4-4) likely
resulted from TW 4-4 pumping.
Cones of depression associated with the nitrate pumping wells became evident as of the fourth
quarter of 2013, and capture associated with the nitrate pumping is expected to continue to
develop. Overall, the apparent capture area of the combined chloroform and nitrate pumping
systems is smaller than last quarter, with capture decreasing within the northern and southern
35
portions of the combined pumping system due primarily to decreased drawdowns at TW4-19,
TW4-21, TW4-39, TW4-40 and TWN-2.
'Background' flow through the chloroform plume was calculated as approximately 3.4 gpm (See
HGC, March 31, 2016: Corrective Action Comprehensive Monitoring Evaluation [CACME]
Report, White Mesa Uranium Mill, Near Blanding, Utah). Pumping from wells within and
immediately adjacent to the chloroform plume during the current quarter (from wells MW-4,
MW-26, TW4-1, TW4-2, TW4-4, TW4-ll, TW4-19, TW4-21, TW4-22, TW4-24, TW4-37,
TW4-39, TW4-40 and TW4-41) is approximately 5.2 gpm. The combined pumping rate of 5.2
gpm exceeds the calculated background flow by 1.8 gpm or 53%, and is considered adequate at
the present time.
Chloroform concentrations at many of the wells with detected chloroform were within 20% of
the values reported during the previous quarter, suggesting that variations are within the range
typical for sampling and analytical error. Wells MW-26, TW4-8, TW4-10, TW4-14, TW4-19,
TW4-21, TW4-22, TW4-24, TW4-27, TW4-39 and TW4-40 had changes in concentration
greater than 20%. Of these, MW-26, TW4-19, TW4-21, TW4-39, and TW4-40 are chloroform
pumping wells; and TW4-22 and TW4-24 are nitrate pumping wells. TW4-8 is located adjacent
to chloroform pumping well MW-4; TW4-10 is located adjacent to chloroform pumping wells
MW-26 and TW4-11; TW4-14 is located adjacent to chloroform pumping wells TW4-4 and
TW4-41; and TW4-27 is located just outside the plume boundary ..
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 TW4-14 and TW4-27 are expected based on their locations near
the plume margins. Furthermore, changes in concentrations at chloroform wells are expected to
result from continued operation of the nitrate pumping system, as the capture associated with
nitrate pumping expands and flow directions change locally.
Chloroform pumping wells MW-26 (3,060 µg/L); TW4-11 (2,750 µg/L); TW4-19 (6,660 µg/L);
TW4-37 (9,380 µg/L); and TW4-39 (2,970 µg/L); and nitrate pumping well TW4-22 (5,100
µg/L), had the highest detected chloroform concentrations. ,Although pumping well TW4-20,
formerly located between pumping wells TW4-19 and TW4-37, would typically be distinguished
as having one of the highest concentrations, TW4-20 collapsed during August, 2020 and was
abandoned in October, 2020.
Since last quarter, the chloroform concentrations in MW-26 increased from 866 to 3,060 µg/L;
TW4-11 increased from 2,670 to 2,750 µg/L; TW4-19 increased from 660 to 6,660 µg/L; TW4-
37 decreased from 10,300 µg/L to 9,380 µg/L; and TW4-39 increased from 648 to 2,970 µg/L. In
addition, the chloroform concentration in chloroform pumping well TW4-21 decreased from 948
to 400 µg/L; the concentration in nitrate pumping well TW4-22 increased from 3,640 to 5,100
µg/L; and the concentration in nitrate pumping well TW4-24 increased from 72.6 to 96.2 µg/L,
remaining just within the plume boundary this quarter. Nitrate pumping well TW4-25 remained
non-detect. TW4-25, located north of TW4-21, bounds the chloroform plume to the north.
36
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased from 51.3 µg/L to 26.9 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 1,150 µg/L. Although the plume boundary remained between MW-
4 and TW4-8 from the first quarter of 2005 through the fourth quarter of 2013, TW4-8 was re-
incorporated into the plume between the first quarter of 2014 and the fourth quarter of 2019.
Elevated chloroform at TW4-8 was 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 (which has remained below 10 µg/L). Although previously elevated, TW4-
8 has remained outside of and has bounded the plume since the end of 2019. Changes in the
plume boundary near TW4-8 are expected to result from changes in pumping and reduced
dilution resulting from cessation of water delivery to the northern wildlife ponds.
Detectable chloroform concentrations at TW4-14 (since the fourth quarter of 2014) and TW4-27
(since the third quarter of 2015) are consistent with continued, but slow, downgradient migration
of chloroform from the distal end of the plume (near TW4-29 and TW4-33) into the low
permeability materials penetrated by TW4-14 and TW4-27. Chloroform at TW4-14 decreased
from approximately 2.7 µg/L to 1.8 µg/L and chloroform at TW4-27 decreased from
approximately 7.8 µg/L to 4.7 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 decreased from 671 µg/L to 577 µg/L; and
chloroform at TW4-30, located immediately cross-to downgradient of TW4-29, decreased from
nearly 83 µg/L to nearly 75 µg/L, remaining within the plume. Slow downgradient migration is
consistent with the more than 30 quarters needed for chloroform exceeding 70 µg/L at TW4-29
to migrate approximately 160 feet downgradient to TW4-30.
Chloroform at TW4-29 is bounded to the north by TW4-27 (approximately 4.7µg/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 3.8 µg/L) and TW4-23 (non-detect). As a consequence of
the increase at TW4-30 last quarter, TW4-30 does not bound the plume immediately to the east.
In addition, general increases in concentrations at TW4-26 since the third quarter of 2016 are
consistent with continuing downgradient chloroform migration, which is likely enhanced by the
decay of the groundwater mound associated with the southern wildlife pond.
Chloroform at TW4-33 (located between TW4-4 and TW4-29) showed a decrease in
concentration, from less than 81 µg/L to less than 65 µg/L. Chloroform at TW4-33 is bounded
to the north by TW4-14 (approximately 1.8 µg/L), to the east by TW4-27 (approximately 4.7
µg/L), and to the west by TW4-6 (approximately 3.8 µg/L) and TW4-23 (non-detect).
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for slight
contractions near TW4-8, TW4-16 and TW4-21; and slight expansion near TW4-24. The
37
chloroform concentration increase at TW4-24, from approximately 72.6 µg/L to 96.2 µg/L
caused slight expansion of the plume boundary to the west of TW 4-24. The concentration
decreases at TW4-8 (from approximately 51 µg/L to 27 µg/L); at TW4-16 (from approximately
270 µg/L to 248 µg/L); and at TW4-21 (from approximately 948 µg/L to 400 µg/L); caused
slight contractions of the plume boundary. Similar to the last four quarters, due primarily to
decreases in concentrations at TW4-6 and TW4-33, the kriging algorithm has 'pinched off' the
southern extremity of the plume.
TW 4-9 remained outside the plume this quarter. Chloroform concentrations at TW 4-9 decreased
from approximately 47 µg/L to 39 µg/L causing little change to the plume boundary. TW4-9 was
incorporated into the plume from the first quarter of 2016 until the first quarter of 2019 due to
increased concentrations attributable to reduced recharge (and dilution) from the northern
wildlife ponds. However, except for the fourth quarter of 2014, TW4-9 was outside the plume
prior to the first quarter of 2016. TW4-38 was installed to the east-southeast of TW4-9 to serve
as a bounding well when concentrations at TW4-9 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 is again just within the plume this quarter.
TW4-24 likely remained primarily outside the plume since 2014 due to initiation of TW4-37
pumping in the second quarter of 2015 and reduced productivity at TW4-24 (since the third
quarter of 2014). Subsequent to the first quarter of 2014, generally increased concentrations at
TW4-6 and TW4-16 (both of which were within the chloroform plume in the past), caused the
plume boundary to migrate to the southwest and temporarily re-incorporate both wells. Increased
concentrations at these wells subsequent to the first quarter of 2014 are likely related to reduced
dilution from cessation of water delivery to the northern wildlife ponds and more westerly flow
induced by nitrate pumping. In addition, concentrations at TW 4-6 may be influenced by reduced
recharge at the southern wildlife pond and the decay of the associated groundwater mound.
Since 2014, TW4-16 has been both within and outside the plume; whereas a decreasing trend in
chloroform concentrations at TW4-6 (since the third quarter of 2015) has once again taken TW4-
6 outside the plume. This quarter, TW4-16 and TW4-6 remain within and outside the plume,
respectively. Although chloroform at TW4-16 has been above and below 70 µg/L since 2014,
and was detected at 248 µg/L this quarter, concentrations have generally increased since 2018,
likely in response to reduced dilution.
The decreasing trend in chloroform concentration at TW4-6 since the third quarter of 2015, and
generally increased concentrations at TW4-26 since the third quarter of 2016, suggest that TW4-
4 pumping has arrested chloroform migration between TW 4-4 and TW 4-6, and that the increased
chloroform at TW4-26 results from a remnant of the plume that continues to migrate south
toward TW4-26. Pumping at adjacent well TW4-41 since the second quarter of 2018 has likely
enhanced the decline in TW 4-6 concentrations to less than 70 µg/L.
Although the nitrate pumping system may redistribute chloroform within the plume and cause
changes in the chloroform plume boundaries, continued operation of the nitrate pumping system
is expected to enhance capture associated with the chloroform pumping system. Furthermore, the
38
addition of chloroform pumping wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-37, TW4-39,
TW4-40 and TW4-41 since the beginning of 2015 is expected to have a beneficial impact.
Generally reduced concentrations at TW4-6 (since the third quarter of 2015) and TW4-16 (since
the fourth quarter of 2014) after previous increases are likely the result of initiation of TW4-l,
TW4-2, and TW4-11 pumping.
Continued operation of the original chloroform pumping wells (MW-4, MW-26, and TW4-19) is
recommended. Pumping these wells, regardless of any short-term fluctuations in concentrations
detected at the wells, helps to reduce downgradient chloroform migration by removing
chloroform mass and reducing hydraulic gradient thereby allowing natural attenuation to be
more effective.
Continued operation of chloroform pumping well TW4-4, augmented by pumping at adjacent
well TW 4-41, is recommended to improve capture of chloroform to the extent practical in the
southern portion of the plume. The overall decrease in chloroform concentrations at TW 4-6 from
1,000 µg/L in the first quarter of 2010 to 10.3 µg/L in the second quarter of 2014 is likely related
to pumping at TW 4-4. The decrease in the long-term rate of water level rise at TW 4-6 once
TW 4-4 pumping began, which suggests that T\V 4-6 is within the hydraulic influence of TW 4-4,
is also consistent with the decrease in chloroform concentrations at TW 4-6 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 chloroform pumping wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-37,
TW4-39, TW4-40 and TW4-41 is also recommended because pumping these wells has increased
overall capture and improved chloroform mass removal. In particular, continued pumping of
TW4-37 (in conjunction with TW4-19) is expected to at least partially compensate for the loss of
TW4-20; and pumping at TW4-40 has expanded capture within the southern extremity of the
plume.
Furthermore, because of the influence of TW4-4 pumping (augmented by TW4-41 pumping
since the second quarter of 2018), and by analogy with the concentration decreases at TW4-6 and
TW 4-26 that occurred after initiation of TW 4-4 pumping, chloroform concentrations at TW 4-29
and TW4-33 are expected to eventually trend downward. Since installation in 2013, however,
concentrations at TW4-33 appear to be relatively stable to decreasing, while, since the third
quarter of 2014, concentrations at TW4-29 appear to be on an upward trend (although
concentrations appear to have generally stabilized and decreased since the second quarter of
2020). The relatively stable chloroform at TW4-33 and increasing to stable concentrations at
TW4-29 suggest that chloroform migration has been arrested at TW4-33 by TW4-4 pumping and
that increased chloroform at downgradient well TW4-29 resulted from a remnant of the plume
that continues to migrate downgradient (toward TW4-30, which until the previous quarter
bounded the plume to the east). The influence of TW4-4 pumping at the distal end of the plume
is consistent with decreasing water levels at both TW4-29 and TW4-33. Pumping at adjacent
well TW4-41 is likely to help maintain or enhance these decreasing trends in water levels and to
39
augment the expected eventual reductions in concentrations in the distal end of the plume.
Continued evaluation of trends at TW4-29 and TW4-33 will be provided in subsequent quarters.
EFRI and its consultants have raised the issues and potential effects associated with cessation of
water delivery to the northern wildlife ponds in March, 2012 during discussions with DWMRC
in March 2012 and May 2013. While past recharge from the ponds has helped limit many
constituent concentrations within the chloroform and nitrate plumes by dilution, the associated
groundwater mounding has increased hydraulic gradients and contributed to plume migration.
Since use of the northern wildlife ponds ceased in March 2012, the reduction in recharge and
decay of the associated groundwater mound has caused the expected decrease in hydraulic
gradients and the increases in constituent concentrations within the chloroform plume. Generally
increased chloroform concentrations at TW4-6 (between 2013 and 2020); 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 since the first quarter of 2015; and
concentrations at TW4-9 have been trending downward since the first quarter of 2018). As
discussed above, increased concentrations at TW4-26 since the third quarter of 2016 that are
consistent with continuing downgradient chloroform migration are also likely enhanced by the
decay of the groundwater mound associated with the southern wildlife pond.
The net impact of reduced wildlife pond recharge is expected to be beneficial even though it is
also expected to result in higher concentrations that will persist until continued mass reduction
via pumping and natural attenuation ultimately reduce concentrations. Temporary increases in
chloroform concentrations are judged less important than reduced chloroform migration rates.
The evolution of the impacts of reduced recharge on concentrations and plume migration rates
will be defined by continued monitoring.
9.0 ELECTRONIC DATA FILES AND FORMAT
EFRI has provided to the Director an electronic copy of the laboratory results for groundwater
quality monitoring conducted under the chloroform contaminant investigation during the quarter,
in Comma Separated Values format. A copy of the transmittal e-mail is included under Tab M.
40
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc.
Energy Fuels Resources (USA) Inc.
By:
Scott Bakken Digitally signed by Scott Bakken
'Date: 2021.05.07 09:08:32 -06'00'
Scott A. Bakken Date
Vice President, Regulatory Affairs
41
Certification:
I certify, under penalty of law, that this document and all attachments were prepared
under my direction or supervision in accordance with a system designed to assure that qualified
personnel properly gather and evaluate the information submitted. Based on my inquiry of the
person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate,
and complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations.
Digitally signed by Scott
Scott Bakken ~:~~~;02,.os.07 o9:os:s6
-06'00'
Scott A. Bakken
Vice President, Regulatory Affairs
Energy Fuels Resources (USA) Inc.
42
Tables
Table 1: Summary of Well Sampling for the Period
Well SnmpJeDate Date. of Lab Report
MW-04 2/23/2021 3/10/2021
TW4-0l 2/23/2021 3/10/2021
TW4-02 2/23/2021 3/10/2021
TW4-03 3/17/2021 3/31/2021
TW4-03R 3/16/2021 3/31/2021
TW4-04 2/23/2021 3/10/2021
TW4-05 3/18/2021 3/31/2021
TW4-06 3/18/202 I 3/31/2021
TW4-07 3/24/2021 3/31/2021
TW4-08 3/18/2021 3/31/2021
TW4-09 3/18/2021 3/31/2021
TW4-IO 3/24/2021 3/31/2021
TW4-ll 2/23/2021 3/10/2021
TW4-12 3/17/202 I 3/31/2021
TW4-13 3/17/2021 3/31/2021
TW4-14 3/18/2021 3/31/2021
MW-26 2/23/2021 3/10/2021
TW4-16 3/24/2021 3/31/2021
TW4-16R 3/23/2021 3/31/2021
MW-32 3/22/2021 3/31/202 I
TW4-18 3/18/2021 3/31/202]
TW4-19 2/23/2021 3/10/2021
TW4-21 2/23/2021 3/10/2021
TW4-22 2/23/2021 3/10/2021
TW4-23 3/17/2021 3/31/2021
TW4-24 2/23/2021 3/10/2021
TW4-25 2/23/2021 3/10/2021
TW4-26 3/24/2021 3/31/2021
TW4-27 3/18/2021 3/31/2021
TW4-28 3/17/2021 3/31/2021
TW4-29 3/24/2021 3/31/2021
TW4-30 3/18/2021 3/31/2021
TW4-31 3/17/2021 3/31/202 I
TW4-32 3/17/2021 3/31/2021
TW4-33 3/18/2021 3/31/2021
TW4-34 3/17/2021 3/31/2021
TW4-35 3/17/2021 3/31/2021
TW4-36 3/17/2021 3/31/2021
TW4-37 2/23/2021 3/10/2021
TW4-38 3/18/2021 3/31/2021
TW4-39 2/23/2021 3/10/2021
TW4-40 2/23/2021 3/10/2021
TW4-41 2/23/2021 3/10/2021
TW4-42 3/17/2021 3/31/2021
TW4-60 2/23/2021 3/10/2021
TW4-65 3/17/2021 3/31/2021
TW4-70 3/18/2021 3/31/2021
TW4-75 3/22/2021 3/31/2021
All sample locations were sampled for Chloroform, Carbon Tetrachloride, Chloromethane, Methylene
Chloride, Chloride and Nitrogen.
Date in parantheses is the date the analytical data package was resubmitted by the laboratory. The
package was resubmitted to correct an error.
"R" following a well number deisgnates a rinsate sample collected ptior to purging of the well of that
number.
TW4-60 is a DI Field Blank, TW4-65 is a duplicate ofTW4-03, and TW4-70 is a duplicate of TW4-09
and TW4-75 is a duplicate ofMW-32.
Highlighted wells are continuously pumped.
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
1-7 QNQC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform Isoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
Tab N Exceedance Notices for the Reporting Period
Tab A
Site Plan and Perched Well Locations White Mesa Site
MW-24A perched monitoring well installed • December 2019
TW-442 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 0 well
PIEZ-1 perched piezometer ~
RUIN SPRING
b seep or spring
HYDRO
GEO
CHEM, INC.
WHITE MESA SITE PLAN SHOWING LOCATIONS OF
PERCHED WELLS AND PIEZOMETERS
APPROVED DATE REFERENCE
H:/718000/nov20/Uwelloc1220.srf
FIGUA-1
TabB
Order of Sampling and Field Data Worksheets
. .
Order of Contamination for 1st Quarter 2021 Chloroform Purging Event
Chlorofonn
Well Sample time Levels Rlnsate date/time
TW4-03 ?>Ltzftt 0,n ND
TW4-42 :5/17/'Z.J ()J'-1'7 ND
TW4-28 3/1'7ht 0157 ND
TW4-32 '3/T1 /U 0 8,0"t ND
TW4-12 at,1/z.t Cf$H ND
TW4-I3 :\/17/t.t Q~~ ND
TW4-36 :!,/t1/z.l Q~U. ND
TW4-31 $/111?.J 083'1 ND
TW4-34 ?,/(1/z.·I Q i'fZ. ND
TW4-35_3/t7/t.t OjCJ> ND
TW4-23:,t,ztt.c O,QO ND
-MW-32 J lt.t.(!:l l 'l..'}O ND
TW4-38 3/J£1Z.I Q61Z. ND
TW4-iS Z./tJ/zJ octz. ND
TW4-14 Ml!{t,1 0$2.3 2.69
TW4-06 3/lK/21 {)~~ 4.61
TW4-27 3/liC/CJ 0154'f 7.8
TW4-05 3/13/e.1 Ots~ 15.6
TW4-09 3/l(ht Q$5S 47.1
TW4-08 3/JK/u O'll"Z. 51.3
TW4-18;!/ IS/zt {)'\Z3 58.6
TW4-24 't/1..'VZ.I 0,5'. 72.6
TW4-33 YISl/ti Q't~S 80.6
TW4-30 '?,(lr,11,1 O"j'i'i 82.8
TW4-40 -z./:a3h,l JZ'j'i 264
"'TW4-16 3/?.~/ZI tHas 270
TW4-39 2./t.~ti.1 too l 648
TW4-19 2./p/2.I Og,30 660
-TW4-29 }/1.'i/'t.l Q §z.!> 671
MW-26 ut.VZ.f toC>1 866
-TW4-10 :!/r.1/z.1 O'S'{O 903
TW4-0l ?../t.3/z.J JZ.I'-924
TW4-21 '2./2311,1 03(g 948
-TW4-07 '.3/V4 ht Q f..'13 967
TW4-04 i,/Z.'3/2,1 )t35 979
TW4-41 ?./z.3/-r.1 J'Z.?.f. 1020
MW-04 'l../t?,/2.I 12-oZ 1050
TW4-02 1../'Z.:)h,1 IOU. 1130
-TW4-26 3/2.'1/7-l Qg51 1160
TW4-ll t/t3h,1 )Qlb 2670
TW4-22 Z.(t3{:z1 o<,~'f 3640
TW4-37 2,,/?3/z, pq:53 10300
TW4~0 D.I. Blank 2.l z~1zo2 1
TW4~5 Duplicate ~L11{U>2.I
TW4-70 Duplicate ";,.t 1~£2.0't.\
~ TW4-75 Duplicate ~£:z~l'.211~1
Comments:
68'00
013'2...
Of!,S
l'Z.30
Water Well
level Depth
141 -rt,.)~-o'!.R_ o~\r..~ou 0~1.S
86
107
115.1
101.5
102.5
99
106
97.2
87.5
114
130.6 Bladder pump
ll2.75
134.8 Cont. Pumping
93
97.5
96
120
120
125
137.5
112.5 Cont. Pumping
87.9
92.S
86' Cont. Pumping
146.3 "TIP&.4-1&1~-03.2:S'ZO'l.l Otoo
120 Cont. Pumping
125 Cont. Pumping
93.5
122.S Cont. Pumping
111
llO Cont. Pumping
121 Cont. Pumping
120
112 Cont. Pumping
97.75 Cont. Pumping
124 Cont. Pumping
120 Cont. Pumping
86
100 Cont. Pumping
113.5 Cont. Pumping
112 Cont. Pumping
~ i · ,,..--• p--. • 'F-:. ~ .. ~,...~ ~~-~ _ .. .''.l.· __ ~· . ,-=:,-s
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 O
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance (micromhos)
Date/Time
2/23/202112:07.
[volume of water purged O
I Fina_l_Q_epth to Waterj_feet)
Gallons Purged
Name of Certified Analyt__i_cal Laboratory_
AWSL
Anal~ical Samples Information
Type of Sample/Analysis
VOCs-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
MW-04 Sampl~ng Program Chloroform Monitoring
MW-04 02232021 Sampli!'g Event 2021 Ql Chloroform
2/23/202112:07
2/23/202112:08 !sampler TH/DL
Pump Weather Conditions Sunny
Grundfos External Ambient Temperature (C) 9
2 Casings Previous Well Sampled TW4-02
13.92
7.0 Well Depth (ft} 123.60
4.0 Well Casing Diameter (in) 3
1000 Depth to Water Before Purging (ft) 85.65
Conductivity Dissolved
(umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
1887 7.08 14.89 435 0 49.0
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 4.0
Time to evacuate 2 Casing Volumes ()
88.23 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Sample Container Preservative
Collected? Matrix Number Type Sample Filtered? Type Added?
y WATER 3 40ml VOA u HCI (p H<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
[ Arrived on site at 1204. Samples collected at 1208. Water was clear. Left site at 1210.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-01 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-0l 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/202112:15
Sample Date & Time 2/23/202112:16 jsampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 10
Purging Method 2 Casings Previous Well Sampled MW-04
Casing Volume (gal) 10.06
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft) 111.30
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 95.89
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/202112:16 2983 7.41 13.80 431 0 62.0
Pumping Rate Calculations
!Volume of water purged () Flow Rate (Q = S/60) (gal/min) 12.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 109.17 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 1212. Samples collected at 1216. Water was clear. Left site at 1219.
Signature of Field Technician
-::3~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-02 Sameling Program Chloroform Monitoring
Field Sample ID TW4-02 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/202110:25
Sample Date & Time 2/23/202110:26 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 8
Purging Method 2 Casings Previous Well Sampled TW4-ll
Casing Volume (gal) 19.02
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) 91.77
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/202J 10:25 3771 7.07 14.00 417 0 96.0
[volume of _water_purged ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes O
[Fina_l Dep!~ to Water _{feet) 116.58 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-ml HOPE u H2504 (pH<2), 4 Deg C y
Comments: ! Arrived on site at 1023. Samples collected at 1026. Water was clear. Left site at 1029.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan er,E::~ _,,.----\ / ,, .,. /· . .,. ~---'•---_:r ~~
•. ~-~
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03 Same_lln_g_ Program Chloroform Monitoring
Field Sample ID TW4-03 03172021 Samplin_9_ Event 2021 Ql Chloroform
Purge Date & Time 3/16/2021 8:35
Sample Date & Time 3/17/2021 7:32 !sampler TH/DL
Purging Equipment Pump Weather Conditions Raining
Pump Type Grundfos External Ambient Temperature (C) 3
Purging Method 2 Casings Previous Well Sampled TW4-03R
Casing Volume (gal) 50.01
Calculated Casing Volumes Purge Duration (min) 9.09
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) 63.71
Conductivity Dissolved
Dateffime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/2021 8:41 68.75 1885 6.80 14.47 432 5.5 82.0
3/17/2021 7:31 1818 6.67 14.88 Before
3/17/2021 7:34 1824 6.69 14.93 After
[volume of water purged (g~ls)
Pumping Rate Calculations
68.75 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 6.25
[Final Depth to Water (feet} 137.78 Number of casing Volumes 1.37
Volume, if well evacuated to dryness (gals) 68.75
Name of Certified Analytical Labor_atory
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 0830. Purge began at 0835. Purged well for a total of 6 minutes and 15 seconds. Purged well dry. Water was clear. Purge ended at 0841 . Left site at 0845.
Arrived on site at 0728. Depth to water was 64.28. Samples bailed and collected at 0732. Left site at 0735.
Signature of Field Technician
-.:3=~-M~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-03R Sampling Program
Field Sample ID T\N4-03R 03162021 Samplin_g_ Event 2021 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/16/2021 8:15 !Sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
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 O Depth to Water Before Purging_(ft)
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/2021 8:14 133.00 2.7 7.80 12.60 409 0 42.0
Pumping Rate Calculations
!Yolume of 1r1a!er purged__{)_ Flow Rate (Q = S/60) O
Time to evacuate 2 Casing Volumes ()
[ Final Depth to Water (feet) Number of casing_ Volumes
Volume, if well evacuated to dryness ()
Name of Certified Analytical Lab_oratory
A\NSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y \NATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y \NATER 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
Groundwater Discharge Permit
-e· ~·
___.~ y , I :r
~·· ~--~
'. , f · ~-~~-=zs
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-04 Same'_i_ng ~l'_ogram Chloroform Monitoring
Field Sample ID TW4-04 02232021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time 2/23/202112:34
Sample Date & Time 2/23/2021 12:35 !Sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 10
Purging Method 2 Casings Previous Well Sampled TW4-41
Casing Volume (gal) 24.10
Calculated Casing Volumes Purge Duration O
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) 77.58
Conductivity Dissolved
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/202112:34 2460 7.17 15.02 432 0 104.0
Pumping_ Rate Calculations
!volume of water purged () Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
!Final Dept_h to Water (f__eet) 107.90 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Same_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
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: I Arrived on site at 1231 . Samples collected at 1235. Water was clear. Left site at 1237.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan -e-~l --.-· <"~-:r--' . . l -$ . _r,· -/ , -.. ~Yl'=LJ
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-05 Sampling Program Chloroform Monitoring
Field Sample ID TW4-05 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17/202111:52
Sample Date & Time 3/18/2021 8:53 [samf)_ler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 9
Purging Method 2 Casings Previous Well Sampled TW4-27
Casing Volume (gal) 32.77
Calculated Casing Volumes Purge Duration (min) 5.95
pH Buffer 7.0 7.0 Well Depth (ft) 121.85
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 71.66
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17/202111:57 55.00 1617 6.72 15.43 448 3.0 66.0
3/17/202111:58 66.00 1600 6.78 15.44 448 2.8 64.0
3/17 /202111:59 77.00 1586 6.83 15.44 447 2.7 63.0
3/17 /202.112:00 88.00 1570 6.87 15.44 447 2.7 62.0
Pumping Rate Calculations
@e>~ume ofwater p1.irged (gals) 88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
[ Final Depth_ to WateUfeet) 74.55 Number of casing Volumes 2.00
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:
Arrived on site at 1148. Purge began at 1152. Purged well for a total of 8 minutes. Purge ended at 1200. Water was clear. left site at 1203. Arrived on site at 0849. Depth to water was 71 .92.
Samples bailed and collected at 0853. left site at 0854.
Signature of Field Technician
~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-06 Sampling Program Chloroform Monitoring
Field Sample ID TW4-06 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17/202110:33
Sample Date & Time 3/18/2021 8:34 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-14
Casing Volume (gal) 13.61
Calculated Casing Volumes Purge Duration (min) 2.47
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) 78.75
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17 /202110:34 13.75 3987 6.64 14.48 459 26.0 6.7
3/18/2021 8:34 4068 6.51 14.08 Before
3/18/2021 8:35 4065 6.53 14.11 After
Pumping Rate Calculations
[volume of water purged{g_als) 13.75 Flow Rate (0 = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.25
[Final Dept_l!to Water (feet) 96.99 Number of casing Volumes 1.01
Volume, if well evacuated to dryness (gals} 13.75
Name of Certified Analytic~! Labo!atory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VO Cs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
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 1029. Purge began at 1033. Purged well for a total of 1 minute and 15 seconds. Purged well dry. Water was a little murky. Purge ended at 1034. Left site at 1037.
Arrived on site at 0829. Depth to water was 79. 18. Sameles bailed and collected at 0834. Left site at 0836.
Signature of Field Technician
~aAr.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan E!. ~!I' ~ .. ,,~ .,··1 • r , ~~~.._ ---:-' ,.. 7 ~1,
-. ---~ ~--._,
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-07 Sampling Program Chloroform Monitoring_
Field Sample ID TW4-07 03242021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/23/202110:10
Sample Date & Time 3/24/2021 8:48 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-10
Casing Volume (gal) 25.44
Calculated Casing Volumes Purge Duration (min) 4.62
pH Buffer 7.0 7.0 Well Depth (ft) 121.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 82.03
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/23/202110:15 55.00 1720 7.05 14.80 377 18.0 35.0
3/24/2021 8:48 1586 6.77 13.44 Before
3/24/2021 8:49 1588 6.81 13.48 After
!Volume of water purged (gals) 55.00
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 5.00
[Firial Deptl"l_to_ Waterjfeet) 117.92 Number of casing Volumes 2.00
Volume, if well evacuated to dryness (gals) 55.00
Name of Certified Analytica_!_Laboratory
AWSL
AnalytJc_al Sameles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1006. Purge began at 1010. Purged well for a total of 5 minutes. Purged well dry. Purge ended at 1015. Water was a little murky. Leh site at 1018.
Arrived on site at 0844. Depth to water was 84.04. Samples bailed_§._nd collected at 0848. _§nowin_g_ at time of collection. Left site at 0850.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-08 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-08 03182021 Sampl_i_n_g_ Event 2021 Ql Chloroform
Purge Date & Time 3/17/2021 12:57
Sample Date & Time 3/18/2021 9:12 jsameler TH/Dl
Purging Eguipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 11
Purging Method 2 Casings Previous Well Sampled TW4-09
Casing Volume (ga_l} 25.83
Calculated Casing Volumes Purge DtJ~Uon (min) 4.69
pH Buffer 7.0 7.0 Well Depth (ft) 126.20
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 86.64
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17 /202112:59 22.00 4977 6.55 14.94 452 4.0 2.5
3/17/202113:00 33.00 4975 6.59 14.93 451 3.9 2.4
3/17/202113:01 44.00 4976 6.61 14.94 450 3.8 2.3
3/17 /202113:02 55.00 4976 6.64 14.97 450 3.7 2.3
jVolume of water_purged {gals)
Pumping_ Rate Calculations
55.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 5.00
jFinal Depth to Water_(feet) 122.41 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1253. Purge began at 1257. Purged well for a total of 5 minutes. Purge ended at 1302. Water was clear. Left site at 1305.
Arrived on site at 0908. Depth to Weiter was 86.98. Samples bailed and collected at 0912. Left site at 0913.
Signature of Field Technician
~q..lUV~/,;
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_03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17 /202112:23
Sample Date & Time 3/18/2021 8:58 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 10
Purging Method 2 Casings Previous Well Sampled TW4-05
Casing Volume (gal) 32.94
Calculated Casing Volumes Purge Duration (min) 5.98
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) 69.65
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/202112:28 55.00 2585 6.53 15.01 459 21.0 2.7
3/17/202112:29 66.00 2578 6.56 15.01 457 22.0 2.5
3/17/202112:30 77.00 2575 6.62 15.03 455 23.0 2.4
3/17/202112:31 88.00 2572 6.66 15.02 454 23.1 2.3
Pumping Rate Calculations
[v_orum! of water pl.ll'ged (gals) 88.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
!Final Depth to IJl{ater (!eet) 85.10 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1219. Purge began at 1223. Purged well for a total of 8 minutes. Purge ended at 1231 . Water was a little murky. Left site at 1234.
Arrived on site at 0855. Depth to water was 69.82. Samples bailed and collected at 0858. Left site at 0902.
Signature of Field Technician
-:=)<,./~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-10 Samplin_g_ Program Chloroform Monitoring
Field Sample ID TW4-10 03242021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/23/2021 9:40
Sample Date & Time 3/24/2021 8:40 ~a_lll_E_ler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-29
Casing Volume (gal) 29.07
Calculated Casing Volumes Purge Duration (min) 5.28
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) 68.68
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen{%) Before/After
3/23/2021 9:43 40.33 2988 6.35 14.78 419 28.0 22.00
3/24/2021 8:40 2711 6.85 13.41 Before
3/24/2021 8:41 2714 6.81 13.26 After
Pumpi_l'lg Rate Calculations
[yolume of water JJUrged (gals) 40.33 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.67
[Final DE!pth t1> WaterJfeet) 110.76 Number of casing Volumes 1.38
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0936. Purge began at 0940. Purged well for a total of 3 minutes and 40 seconds. Purged well dry. Purge ended at 0943. Left site at 0946.
Arrived on site at 0836. DepJh to wat_er was _68.76. ~amples bailed and collected at 0840. Snowing at time of collection. Left site at 0842.
Signature of Field Technician
~{µ"~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan --~-· ...-----~ I r -
,---~ -=z: s ~r~~ White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-11 Sampling_ Program Chloroform Monitorin_g_
Field Sample ID TW4-11 02232021 Samel_ing Event 2021 Ql Chloroform
Purge Date & Time 2/23/202110:15
Sample Date & Time 2/23/202110:16 [sampler TH/DL
Purging Equipment Pum p Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled MW-26
Casing Volume (gal) 6.17
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) 92.95
Dissolved
Date/Time Gallons Purged Conductivity (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/202110:15 3773 6.93 13.36 368 0 90.0
[yoh.1me o_f water pur_g_ed ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 15.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 100.51 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 Sampl e/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-mLPoly 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 1012. Samples collected at 1016. Water was clear. Left site at 1020.
Signature of Field Technician
~u.,~-fA.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-12 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-12 03172021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/16/202111:00
Sample Date & Time 3/17/20218:11 [sampler TH/DL
Purging Equipment Pum p Weather Conditions Raining
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-32
Casing Volume (gal) 31.38
Calculated Casing Volumes Purge Duration (min) 5.70
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) 55.13
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units} Temp (deg C} Redox (mV} Turbidity (NTU} Oxygen(%} Before/After
3/16/202111:03 38.50 1613 6.82 14.58 457 3.5 48.0
3/17/2021 8:10 1436 7.56 12.78 Before
3/17/2021 8:12 1480 7.54 12.83 After
Pumping Rate Calculations
!Volume of water purged (gals) 38.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.50
!Final Depth to Water (feet} 100.56 Number of casing Volumes 1.22
Volume, if well evacuated to dryness (gals) 38.50
Name of Certified Anal~ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-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 1056. Purge began at 1100. Purged well for a total of 3 minutes and 30 seconds. Purged well dry. Purge ended at 1103. Water was clear. Left site at 1107.
Arrived on site at 0807. De_e_th to water was 55.50. Samples bailed and collected at 08 11 . Left site at 0813.
Signature of Field Technician
~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan ~ ---~. -s ~ -.--White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-13 Sampling Program Chloroform Monitoring
Field Sample ID TW4-13 03172021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/16/202112:00
Sample Date & Time 3/17/20218:19 !sampler TH/DL
Purging Equipment Pump Weather Conditions Raining
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-12
Casing Volume (gal) 32.40
Calculated Casing Volumes Purge Duration (min) 5.89
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) 56.08
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/202112:03 41.25 2134 6.79 14.92 451 5.2 72.0
3/17/2021 8:19 2111 7.22 12.75 Before
3/17/20218:20 2110 7.22 12.81 After
Pumping Rate Calculations
!volume of water purged (gals) 41.25 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.75
[Final Depth to Water (feet) 103.07 Number of casing Volumes 1.27
Volume, if well evacuated to dryness (gals) 41.25
Name of Certified Analytical Laboratory
AWSL
Analytical Sameles Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 {pH<2), 4 Deg C y
Comments:
Arrived on site at 1156. Purge began at 1200. Purged well for a total of 3 minutes-and 45 seconds: Water was clear. Purged well dry. Purge ended at 1204. Left site at 1207.
Arrived on site at 0815. Depth to water was 56.56. Sameles bailed and collected at 0819. Left site at 0821 .
Signature of Field Technician
..=:'.)=~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-14 Sampling Program Chloroform Monitoring
Field Sample ID TW4-14 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17/202110:06
Sample Date & Time 3/18/2021 8:23 !sam_e_ler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-38
Casing Volume (gal) 11.70
Calculated Casing Volumes Purge Duration (min) 2.12
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) 77.18
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17/202110:07 13.75 5345 6.30 14.99 474 63 .0 91.0
3/18/2021 8:23 5450 6.50 15.32 Before
3/18/2021 8:24 5454 6.49 15.24 After
!Volume of wat_er purged (gals) 13.75
Pume!ng Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.25
[Final Depth to Water (feet) 92.88 Number of casing Volumes 1.17
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 HDPE u H2504 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1002. Purge began at 1006. Purged well for a total of 1 minute and 15 seconds. Purged well dry. Water was murky. Purge ended at 1007. Left site at 1010.
Arrived on site at 0819. Depth to water was 77.40. Samples bailed and collected at 0823. Left site at 0825.
Signature of Field Technician
~CL,~ ~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID MW-26 Sampling Program Chloroform Monitoring
Field Sample ID MW-26 02232021 Sam_e_ling Event 2021 Ql Chloroform
Purge Date & Time 2/23/202110:06
Sample Date & Time 2/23/202110:07 jsami>_ler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-39
Casing Volume (gal) 27.20
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) 79.67
Conductivity Dissolved
DatefTime Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/202110:06 3404 6.88 14.71 353 0 35.3
Pumping Rate Calculations
jvolume of water purged() Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
jFinal Depth to Water (fe~!) 110.51 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-Ch loroform y WATER 3 40mlVOA u HCI (pH<2}, 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HDPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived on site at 1003. Samples collected at 1007. Water was clear. Left site at 1009.
Signature of Field Technician
~C<.11.r.
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 03242021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/23/2021 8:35
Sample Date & Time 3/24/2021 8:15 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled MW-32
Casing Volume (gal) 48.62
Calculated Casing Volumes Purge Duration (min) 8.84
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) 73.14
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/23/2021 8:42 77.00 3767 6.74 14.71 371 12.0 5.0
3/23/2021 8:43 88.00 3787 6.74 14.70 370 11.0 5.0
3/23/2021 8:44 99.00 3773 6.74 14.70 369 10.8 5.2
3/23/2021 8:45 110.00 3700 6.79 14.73 363 11.0 5.3
Pumping Rate Calculations
[volume of water purged_(gals) 110.00 Flow Rate (Q = S/60) {gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 10.00
!Final Depth to WatE!_r (feet) 110.23 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
AnalY!ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0831. Purge began at 0835. Purged well for a total of 10 minutes. Purge ended at 0845. Water was a little murky. Left site at 0848.
Arrived on site at 081 1. Depth to water was 73.24. Samples ba~ed and co~ected at 0815. Sno_wln_g at time of collection. Left site at 0817.
Signature of Field Technician
..=3~
Groundwater Discharge Permit
~ ~. s e . y~ ... ~ ~-· 1
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-16R Sampling_F>rogram
Field Sample ID TW4-16R 03232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/23/2021 8:00 !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 O
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing_Diam~ter O
Specific Conductance () Depth to Water Before Purging (ft)
Conductivity Dissolved
Date/Time Gallons Purged (gal} (umhos/cm} pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/23/2021 7:59 133.00 3.6 6.92 15.19 265 0 27.1
Pumping Rate Calculations
!Volume of water purge~ () Flow Rate (Q = S/60) Q
[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 Lab.oratory
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 H2504 {pH<2), 4 Deg C y
Comments:
Signature of Field Technician
~~-17~
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 03222021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time 3/22/2021 7:30
Sample Date & Time 3/22/202112:30 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny and windy
Pump Type QED External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled TW4-18
Casing Volume (gal) 32.11
Calculated Casing Volumes Purge Duration (min) 295.98
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) 81.42
Conductivity Dissolved
Datefrime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/22/202112:27 64.44 3775 6.50 14.19 328 67.0 6.5
3/22/202112:28 64.66 3773 6.50 14.20 315 66.0 6.5
3/22/202112:29 64.88 3771 6.51 14.18 308 64.0 6.4
3/22/202112:30 65.10 3775 6.52 14.20 298 63.0 6.3
Pumping Rate Calculations
!volume of _wate_r purged (gals) 65.10 Flow Rate (Q = S/60) (gal/min) .217
Time to evacuate 2 Casing Volumes (min) 300.00
[Final D!pth to Water (feet) 87.39 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analyttcal 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 07~6. Purge beg_an at 0730. Purged well for a tcltal of 300 minutes. P_LJ!S_e ended and samples collected at 1230. ~ater was_ murky. Left site at 1239.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-18 SameJjng P_l'_og_ram Chloroform Monitorin~
Field Sample ID TW4-18 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17/202113:26
Sample Date & Time 3/18/2021 9:23 jsampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-08
Casing Volume (gal) 41.87
Calculated Casing Volumes Purge Duration (min) 7.61
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) 72.78
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/202113:32 66.00 2000 6.55 15.52 443 20.0 13.0
3/17/202113:33 77.00 1990 6.60 15.54 443 20.2 13.3
3/17/202113:34 88.00 1950 6.63 15.53 443 20.0 13.5
3/17/202113:35 99.00 1920 6.65 15.54 443 19.5 13.3
jvo_lume __c:>f wl3!er purgedjgals!
Pumping Rate Calculations
99.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 9.00 I Final Depth to V'{ater _{feet) 73.10 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2}, 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1323. Purge began at 1326. Purged well for a total of 9 minutes. Purge ended at 1335. Water was a little murky. Left site at 1337.
Arrived on site at 0919. Depth to water was 73.03. Samples bailed and collected 0923. Left site at 0924.
Signature of Field Technician
-:3~-d~
Groundwater Discharge Permit e. w;: ,.---. \ ,, ';I • 1 . I
_. ' '/ c I ~YF'«,«=7 'S
-.• J '/
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-19 Samplin9.?r.9_!:1_ram Chloroform Monitoring
Field Sample ID TW4-19 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/2021 8:29
Sample Date & Time 2/23/2021 8:30 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 2
Purging Method 2 Casings Previous Well Sampled TW4-60
Casing Volume (gal) 32.98
Calculated Casing Volumes Purge Duration O
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) 76.34
Dissolved
Date/Time Gallons Purged Conductivity (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/2021 8:29 2585 6.50 16.07 526 0 28.7
[volume of water pur_g_ed ()
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
[Final Depth to Water (feet) 82.87 Number of casing Volumes
Volume, if well evacuated to dryness() 0
Name of Certified Analytical Laboratory
AWSL
AnalyticaJ Samples Information
Sample Container Preservative
Type of Sam ple/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 0826_._ SamJJ_les collected at 0830. Water was clear. Lett site at 0834.
Signature of Field Technician
~u./'.JV~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-21 Sampling P_l'_o_g_ram Chloroform Monitoring
Field Sample ID TW4-21 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/2021 9:17
Sample Date & Time 2/23/2021 9:18 jSampler TH/OL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-19
Casing Volume (gal) 28.63
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) 74.95
Conductivity Dissolved
Date/Time Gallons Purged {umhos/cm) pH (pH Units) Temp {deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/2021 9:17 2950 6.88 15.39 403 0 40.1
Pumein_g_ Rate Calculations -
Flow Rate (Q = S/60) (gal/min) 17.00 jvolume of water purged ()
Time to evacuate 2 Casing Volumes ()
!Final Depth to Water (feet) 84.76 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Sam_e_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 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 0914. Sa_1!1ples collected at 0918. Water was clear. Left site at 0921 .
Signature of Field Technician
~=~
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 O
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance (micromhos)
Date!Time
2/23/2021 9:43
~lume of water purged ()
[ Final D~pth to _Jiater (feet)
Gallons Purged
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Type of Sample/An alysis
voes-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-22 Sampling_Program Chloroform Monitoring
TW4-22 02232021 Sampling Event 2021 Ql Chloroform
2/23/2021 9:43
2/23/2021 9:44 jsampter TH/DL
Pump Weather Conditions Sunny
Grundfos External Ambient Temperature (C) 5
2 Casings Previous Well Sampled TW4-24
31.22
7.0 Well Depth (ft) 114.70
4.0 Well Casing Diameter (in) 4
1000 Depth to Water Before Purging (ft) 66.88
Conductivity Dissolved
(umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
5393 6.98 15.34 428 0 96.0
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
97.31 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Sample Container Preservative
Collected? Matrix Number Type Sample Filtered? Type Added?
y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
y WATER 1 500-ml Poly u None N
y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
[ Arrived on site at 0941 . Samples collected at 0944. Water was clear. Left site at 0946.
Signature of Field Technician
~u.-~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-23 Sampling Program Chloroform Monitoring
Field Sample ID TW4-23 03172021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/16/202114:32
Sample Date & Time 3/17/20219:00 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled TW4-35
Casing Volume (gal) 27.08
Calculated Casing Volumes Purge Duration (min) 4.92
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) 74.92
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/202114:37 55.00 3560 6.76 14.36 307 3.0 11.0
3/16/202114:38 66.00 3572 6.80 14.36 297 3.1 13.0
3/16/202114:39 77.00 3587 6.83 14.30 291 3.2 14.1
3/16/202114:40 88.00 3589 6.84 14.41 290 3.3 14.0
Pumping Rate Calculations -
[volume of water purge_d _(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) 95.83 Number of casing Volumes 2.00
Volume, if well evacuated to dryness() 0
Name of Certified Anal'i!ical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-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 1428. Purge began at 1432. Purged well for a total ot 8 minutes. Water had an orange coloration but was clearing as purge went on. Purge ended at 1440. Left site at 1442. Arrived
on site at 0857. Depth to water was 75.28. Samples bailed and collected at 0900. Left site at 0902.
Signature of Field Technician
~«.,'VV......__..,.
..
.,,,< ,
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 ()
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance (micromhos)
Date!Time
2/23/2021 9:36
[volume of water pur_g_ed O
l}=;_nal ~p!h to WaterJ!eet)
Gallons Purged
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Type of Sample/Analysis
voes-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-24 Sampling_ Program Chloroform Monitoring
TW4-24 02232021 Sampling Event 2021 Ql Chloroform
2/23/2021 9:35
2/23/2021 9:36 [sampler TH/DL
Pump Weather Conditions Sunny
Grundfos External Ambient Temperature (C) 4
2 Casings Previous Well Sampled TW4-25
27.62
7.0 Well Depth (ft) 114.80
4.0 Well Casing Diameter (in) 4
1000 Depth to Water Before Purging (ft) 72.49
Conductivity Dissolved
(umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
8723 6.90 15.09 433 3.0 37.7
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 16.00
Time to evacuate 2 Casing Volumes ()
76.55 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Sample Container Preservative
Collected? Matrix Number Type Sample Filtered? Type Added?
y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
y WATER 1 500-ml Poly u None N
y WATER 1 250-ml HOPE u H2504 (pH<2), 4 Deg C y
[Arriv~d_on site at 09~3. Samples collected at 0936. Water was clear. Left site at 0938.
Signature of Field Technician
-:3=~-JJ~
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 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/2021 9:25
Sample Date & Time 2/23/2021 9:26 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-21
Casing Volume (gal) 41.52
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) 73.11
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/2021 9:25 2626 6.95 15.09 413 0 38.1
Pumping Rate Calculations
@?lume of water purged_() Flow Rate (0 = S/60) (gal/min) 12.00
Time to evacuate 2 Casing Volumes ()
l~nal Depth_to Water (feet) 98.67 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments: I Arrived_Sln site at 0922. Same_les collected at 0926. Water was clear. Left site at 0928.
Signature of Field Technician
~«AJV~~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-26 Sampling Prog_ram Chloroform Monitoring
Field Sample ID TW4-26 03242021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/23/2021 10:44
Sample Date & Time 3/24/2021 8:57 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled TW4-07
Casing Volume (gal) 9.50
Calculated Casing Volumes Purge Duration (min) 1.72
pH Buffer 7.0 7.0 Well Depth (ft) 87.70
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance {micromhos} 1000 Depth to Water Before Purging (ft) 73.15
Conduct1v1ty Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/23/202110:45 11.00 4601 6.53 14.58 411 21.0 91.0
3/24/2021 8:57 4643 7.06 13.34 Before
3/24/2021 8:58 4646 7.06 13.36 After
Pumping Rate Calculations
[volume of water purged (gals) 11.00 Flow Rate (Q = S/60) {gal/min} 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
[Final Depth to Water (feet) 84.86 Number of casing Volumes 1.15
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical La_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 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 1040. Purge began at 1044. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1045. Water was a little murky. Left site at 1048. Arrived on site at 0853. Depth to
water was 73.51. Sarne_les bailed and collected at 0857. Snowing at time of collection. Left site at 0859.
Signature of Field Technician
~=~·
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-27 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-27 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17/202111:02
Sample Date & Time 3/18/2021 8:44 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 7
Purging Method 2 Casings Previous Well Sampled TW4-06
Casing Volume (gal) 11.06
Calculated Casing Volumes Purge Duration (min) 2.01
pH Buffer 7.0 7.0 Well Depth (ft) 95.75
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 78.81
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17 /202111 :03 11.00 5252 6.61 14.90 455 14.5 42.0
3/18/20218:44 5151 6.55 14.06 Before
3/18/2021 8:45 5160 6.55 14.08 After
!Volume ~f water pu_l'g_ed (gals) 11.00
........ .., ... ~ 1 IOL'G' "'an ... ulClLIVI ·~
Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
!Final Depth to Water (feet) 92.75 Number of casing Volumes 0.99
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical Laboratory
AWSL
Analytical samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1058. Purge began at 1102. Purged well for a total of 1 minute. Purged well dry. Purge ended at 1103. Water was mostly clear. Left site at 11006. Arrived on site at 0839. Depth to
water was 79.25. Samples bailed and collected at 0844. Left site at 0846.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e ·~ ~ -1-•• -..
. ~
..____::::.. --~ ~ ~Y~S
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-28 Samplin9Pr~ram Chloroform Monitoring
Field Sample ID TW4-28 03172021 Samef ing Event 2021 Ql Chloroform
Purge Date & Time 3/16/2021 9:46
Sample Date & Time 3/17/2021 7:57 !sampler TH/DL
Purging Equipment Pump Weather Conditions Raining
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-42
Casing Volume (gal) 39.19
Calculated Casing Volumes Purge Duration (min} 7.12
pH Buffer 7.0 7.0 Well Depth (ft) 108.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 48.46
Conductivity Dissolved
DatefTime Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/2021 9:50 49.50 1561 7.10 14.55 516 9.5 69.5
3/17/2021 7:56 1655 7.52 13.07 Before
3/17/2021 7:58 1660 7.55 13.14 After
Pum.eing Rate Calculations -
[volul!'e of !Jate.r-_purg_~d (gals) 49.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 4.50
[Final Depth t~ Wa~r (feet) 105.11 Number of casing Volumes 1.26
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 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 0942. Purge began at 0946. Purged well for a total of 4 minutes and 30 seconds. Purged well dry. Purge ended at 0950. Water was a little murky. Left site at 0953. Arrived on site at
0753. Deeth to water was_ 48.~t Sar11.ples bailed and collected at 0757. Left site at 0759.
Signature of Field Technician
~u/'~ ~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-29 Sampling Program Chloroform Monitoring
Field Sample ID TW4-29 03242021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/23/2021 9:12
Sample Date & Time 3/24/2021 8:25 [sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casi ngs Previous Well Sampled TW4-16
Casing Volume (gal) 10.87
Calculated Casing Volumes Purge Duration (min) 1.97
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) 77.83
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/23/2021 9:13 11.00 4156 6.59 14.58 412 4.7 93.0
3/24/2021 8:25 4052 6.47 14.46 Before
3/24/2021 8:26 4042 6.48 14.50 After
Pumping Rate Calculations
~llme of water purged (gals) 11.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.00
[Final C>epth to Water (feet) 92.13 Number of casing Volumes 1.01
Volume, if well evacuated to dryness (gals) 11.00
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
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 0908. Purge began at 0912. Purged well for a total of 1 minute. Purge ended at 0913. Purged well dry. Water was -clear. Left site at 0915. Arrived on site at 0821 . Depth to water
was 77.88. Samples bailed and collected at 0825. Left site at 0828. Snowing_ at time of collection.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-30 Sampling__!'rog_ram Chloroform Monitoring
Field Sample ID TW4-30 03182021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/17 /202114:29
Sample Date & Time 3/18/2021 9:44 [sampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature {C) 12
Purging Method 2 Casings Previous Well Sampled TW4-33
Casing Volume (gal) 12.10
Calculated Casing Volumes Purge Duration (min) 2.20
pH Buffer 7.0 7.0 Well Depth (ft) 93.48
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 74.94
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/17 /202114:30 14.66 4698 5.69 14.98 457 52.0 52.0
3/18/2021 9:44 4522 6.00 13.53 Before
3/18/2021 9:45 4539 5.99 13.57 After
lv_c:,lume ~f water purged (gals)
Pumping_ Rate Calculations
Flow Rate (Q = S/60) (gal/min) 11.00 14.66
Time to evacuate 2 Casing Volumes (min) 1.33
[!:inc!!_D_epth to Water _{feet) 91.10 Number of casing Volumes 1.21
Volume, if well evacuated to dryness (gals) 14.66
Name of Certified Analytical Laboratory
AWSL
Anal}'!ical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mL Poly u None N
Nitrate/nitrite as N y WATER 1 250-mL HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1425. Purge began at 1429. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 1430. Water was a little murky. Left site at 1433. Arrived on site at
0940. Depth to water was 75.13. Samples bailed and collected at 0944. Left site at 0946.
Signature of Field Technician
Groundwater Discharge Permit
4SF-: ..
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Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-31 Sampling Program Chloroform Monitorin1;
Field Sample ID TW4-31_03172021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time 3/16/202113:05
Sample Date & Time 3/17/2021 8:34 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-36
Casing Volume (gal) 20.65
Calculated Casing Volumes Purge Duration (min) 3.75
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) 75.85
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/202113:07 25.66 4010 6.67 15.00 424 68.4 24.2
3/17/2021 8:34 4038 7.01 13.45 Before
3/17/2021 8:35 4040 7.01 13.50 After
Pumelng Rate Calculations
~lume of water purged (gals) 25.66 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 2.33 I Final Depth to Wa_ter (feet} 104.88 Number of casing Volumes 1.24
Volume, if well evacuated to dryness (gals) 25.66
Name of Certified Analytical L~borato_l)'_
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 1301 . Purge began at 1305. Purged well for a total of 2 minutes and 20 seconds. Purged well dry. Purge ended at 1307. Water was a little murky. Left site at 1310. Arrived on site at
0830. Depth to water was 76.21 . Samples bailed and collected at 0834. Left site at 0836.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-32 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-32 03172021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time 3/16/202110:23
Sample Date & Time 3/17/20218:04 [sampler TH/DL
Purging Equipment Pump Weather Conditions Raini ng
Pump Type Grundfos External Ambient Temperature (C) 4
Purging Method 2 Casings Previous Well Sampled TW4-28
Casing Volume (gal) 38.65
Calculated Casing Volumes Purge Duration (min) 7.02
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) 55.45
Dissolved
Date/Time Gallons Purged (gal) >nductivity (umhos/c pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/202110:28 55.00 6590 3.85 14.70 512 4.3 2.2
3/16/202110:29 66.00 6615 3.87 14.71 512 4.0 2.1
3/16/202110:30 77.00 6615 3.88 14.74 512 3.9 2.1
3/16/202110:31 88.00 6612 3.89 14.73 511 3.8 2.2
Pumping Rate Calculations
§1ume of water p_urge~g_als) 88.00 Flow Rate (0 a= S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 8.00
jFinal Deptll_to W~er (feet) 87.98 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 1019. Purge began at 1023. Purged well for a total of 8 minutes. Purge ended at 1031 . Water was clear. Left site at 1033. Arrived on site at 0800. Depth to water was 55.83.
Samples bailed and collected at 0804. Left site at 0806.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
./ -~ .. ~-... -1· ./'---
' ,.. -s S ,r~YFL White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-33 Sampling Program Chloroform Monitoring
Field Sample ID TW4-33 03182021 Samplin.9_ Event 2021 Ql Chloroform
Purge Date & Time 3/17 /202114:01
Sample Date & Time 3/18/2021 9:35 jsampler TH/DL
Purging Equipment Pump Weather Conditions Partly cloudy
Pump Type Grundfos External Ambient Temperature (C) 12
Purging Method 2 Casings Previous Well Sampled TW4-18
Casing Volume (gal) 5.47
Calculated Casing Volumes Purge Duration (min) 0.99
pH Buffer 7.0 7.0 Well Depth (ft) 86.23
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 77.85
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17 /202114:01 5.50 5000 7.02 15.24 432 13.0 61.0
3/18/2021 9:35 4841 7.03 12.42
3/18/2021 9:36 4842 7.06 12.48
jvolume of water purged (gals) 5.50
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min)
Time to evacuate 2 Casing Volumes (min)
jFinal Depth to Water (feet) 84.01 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 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 1358. Purge began at 1401. Purged well for a total of 30 seconds. Purge ended at 1401 . Water was clear. Purged well dry. Left site at 1403,
Arrived on site at 0931 . Depth to water was 78.52. Samples bailed and collected at 0935. Left site at 0937.
Signature of Field Technician
Before
After
11.00
0.50
1.00
5.50
Added?
y
N
y
Groundwater Discharge Permit e--·-~-1·· ....--,.·
~. t'i . .·. ..-------=-I -·· T ~.~Y~S
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Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-34 Sam_e_ling Program Chloroform Monitoring
Field Sample ID TW4-34 03172021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 3/16/202113:35
Sample Date & Time 3/17/2021 8:42 !sampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled TW4-31
Casing Volume (gal) 12.85
Calculated Casing Volumes Purge Duration (min) 2.33
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) 76.05
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3/16/202113:36 16.50 3634 6.59 14.80 435 17.0 11.0
3/17/2021 8:42 3640 7.08 13.20 Before
3/17/20218:43 3642 7.08 13.25 After
Pumping Rate Calculations
[vol_UITle of water pu_rge_ci_ (gals) 16.50 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min') 1.50
[F=_ir,al D~th to Wa_te_r__(fee!)_ 92.49 Number of casing Volumes 1.28
Volume, if well evacuated to dryness (gals) 16.50
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
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 1305. Purged well for a total of 1 minute and 30 seconds. Purged well dry. Purge ended at 1306. Water was a little murky. Left site at 1309. Arrived on site at
0838. Depth to water was 76.41. Samples bailed and collected at 0842. Left site at 0844.
Signature of Field Technician
.-:3~~
Groundwater Discharge Permit e ·~-/ r----l --~ . , . , ~· .~ .
--t' ~·7,· -_u .r ~'YFJUEZ..S
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-35 Samplin_g_Prog_ram Chloroform Monitoring
Field Sample ID TW4-35_03172021 Sam_e_ling Event 2021 Ql Chloroform
Purge Date & Time 3/16/202114:04
Sample Date & Time 3/17/2021 8:50 jSampler TH/DL
Purging Equipment Pump Weather Conditions Cloudy
Pump Type Grundfos External Ambient Temperature (C) 6
Purging Method 2 Casings Previous Well Sampled TW4-34
Casing Volume (gal} 7.54
Calculated Casing Volumes Purge Duration (min) 1.37
pH Buffer 7.0 7.0 Well Depth (ft) 86.50
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos} 1000 Depth to Water Before Purging (ft) 74.95
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity {NTU) Oxygen(%) Before/After
3/16/202114:05 8.25 4516 6.40 14.54 393 12.7 42.0
3/17/2021 8:50 4478 6.75 13.10 Before
3/17/20218:51 4478 6.74 13.20 After
(vplume_of 11\/ater piJ__rged _(g_als)
Pumping_ Rate Calculations
8.25 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 0.75
Number of casing Volumes 1.09 (~inal Depthto Water {feet) 84.23
Volume, if well evacuated to dryness (gals} 8.25
Name of Certified Analytical Laboratory
AWSL
AnalY!_ical Sample.s Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sam ple 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 1400. Purge began at 1404. Purged well for a total of 45 seconds. Purged well dry. Water was a little murky. Purge ended at 1405. Left site at 1407. Arrived on site at 0846. Depth to
water was 75.1 8. Samples bailed and collected at 0850. Left site at 0852.
Signature of Field Technician
..:::=)...,vv,.
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
;~···---White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-36 Sampling Program Chloroform Monitoring
Field Sample ID TW4-36 03172021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time 3/16/202112:33
Sample Date & Time 3/17/20218:26 !sampler TH/DL
Purg_i_ng Equipment Pump Weather Conditions Cloudy
Pump Ty!)e Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-13
Casing_ Volume (g!I) 27.28
Calculated Casin_g_Volumes Purge Duration (min) 4.96
pH Buffer 7.0 7.0 Well Depth (ft) 99.41
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos) 1000 Depth to Water Before Purging (ft) 57.62
Conductivity Dissolved
Date!Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/16/202112:36 33.00 2470 6.75 15.00 276 45.9 3.5
3/17/20218:26 2481 7.05 13.45 Before
3/17/2021 8:27 2480 7.04 13.49 After
Pumping Rate Calculations
!volume of water purged (gals) 33.00 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 3.00 I Final De_e_th to Water (feet) 96.77 Number of casing Volumes 1.20
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 HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 1229. Purge began at 1233. Purged well for a total of 3 minutes. Purged well dry. Purge ended at 1236. Water was a little murky. Left site at 1240. Arrived on site at 0822. Depth to
water was 58.76. Samples bailed and collected at 0826. Left site at 0828.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan --e~ -I .~ _'/
~ ~--' ;' '. -7_-__.v~Y~S White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-37 Sampling Pr<>gram Chloroform Monitoring
Field Sample ID TW4-37 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/2021 9:52
Sample Date & Time 2/23/2021 9:53 !sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-22
Casing Volume ()
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) 67.92
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/2021 9:52 3570 7.03 15.47 417 0 96.0
!Volume of water purged()
Pume_ing Rate Calculations
Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes (}
l~i_11al D~eth to Water (feet) 95.14 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/Ana lysis 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:
[~rrivecj_cm site at 0949. Samples collected at 0953. Water was clear. Lett site at 0955.
Signature of Field Technician
.::3u..~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan e---~-r ,· ---. V: _.-. ) ' ~ . r , . . ~ ~-_,/ .. " __ / ~y~ s
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-38 Sampling_ Program Chloroform Monitoring
Field Sample ID TW4-38 03182021 Sam_eling Event 2021 Ql Chloroform
Purge Date & Time 3/17/20219:31
Sample Date & Time 3/18/2021 8:12 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 2
Purging Method 2 Casings Previous Well Sampled TW4-23
Casing Volume (gal) 35.46
Calculated Casing Volumes Purge Duration (min) 6.44
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) 59.61
Conductivity Dissolved
Date/Time Gallons Purged (gal) (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
3/17/20219:35 44.00 1957 6.65 14.59 475 12.0 70.0
3/17/2021 9:36 55.00 1912 6.71 13.63 474 14.0 66.0
3/17/20219:37 66.00 1901 6.73 14.64 469 15.0 65.0
3/17/20219:38 77.00 1934 6.78 14.66 463 15.0 63.0
[v_olume of water purged (gals)
Pumping Rate Calculations
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) 104.76 Number of casing Volumes 2.00
Volume, if well evacuated to dryness () 0
Name of Certified Analytical ~borat~I}'_
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Arrived on site at 0927. Purge began at 0931 . Purged well for a total of 7 minutes. Purge ended at 0938. Water was mostly clear. Left site at 0941. Arrived on site at 0808. Depth to water was 59.94.
Samples bailed and collected at 0812. Left site at 0814.
Signature of Field Technician
~~-J/t>~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-39 Sampling Program Chloroform Monitoring
Field Sample ID TW4-39 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/202110:00
Sample Date & Time 2/23/2021 10:01 [sampler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 5
Purging Method 2 Casings Previous Well Sampled TW4-37
Casing Volume (gal) 29.47
Calculated Casing Volumes Purge Duration O
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) 75.60
Conductivity Dissolved
Date!Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/After
2/23/202110:00 2209 7.10 15.05 438 1.5 42.5
[volume of water_purged_()
Pumping Rate Calculations
Flow Rate (Q = S/60) (gal/min} 18.00
Time to evacuate 2 Casing Volumes (}
[Final Depth to Watel'"_ (feet) 104.56 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nit rite as N y WATER 1 250-ml HDPE u H2S04 (pH<2), 4 Deg C y
Comments:
[ Arrived on site at 0957. Samples collected at 1001 . Water was clear. Left site at 1003.
Signature of Field Technician
..=3 .. ~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-40 Sampling_ Pr<>g_ram Chloroform Monitoring
Field Sample ID TW4-40 02232021 Samplil"lg Event 2021 Ql Chloroform
Purge Date & Time 2/23/202112:43
Sample Date & Time 2/23/2021 12:44 jsampler TH/DL
Purging Equipment Pump Weather Conditions Sun ny
Pump Type Grundfos External Ambient Temperature (C} 10
Purging Method 2 Casings Previous Well Sampled TW4-04
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft} 86.00
pH Buffer 4.0 4.0 Well Casing Diameter (in) 4
Specific Conductance (micromhos} 1000 Depth to Water Before Purging (ft) 71.70
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/202112:43 4079 6.84 14.81 441 2.8 110.0
Pumping Rate Calculations
!Volu111e of water p~rged () Flow Rate (Q = S/60) (gal/min) 18.00
Time to evacuate 2 Casing Volumes ()
~c!_I_Depth_to Wate_r-(feet) 81.03 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical Laboratory
AWSL
Anal}'tical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
voes-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-mLPoly 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 1244. Water was clear. Left site at 1247.
Signature of Field Technician
~<.v~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-41 Saml'_lin_g_Program Chloroform Monitoring
Field Sample ID TW4-41 02232021 Samplin9 Event 2021 Ql Chloroform
Purge Date & Time 2/23/202112:25
Sample Date & Time 2/23/202112:26 ~anieler TH/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 10
Purging Method 2 Casings Previous Well Sampled TW4-01
Casing Volume (gal) 7.22
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) 86.69
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/2021 12:26 2745 7.13 15.80 421 0 96.0
Pumping Rate Calculations
[yolume of w~~pur_g_ed O Flow Rate (Q = S/60) (gal/min) 5.0
Time to evacuate 2 Casing Volumes ()
IFi_'!_al Dtpth to Water (feet) 90.80 Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytica! Lall,oratory
AWSL
Analytical_§amp_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: ! Arrived on s~e at ! 223. Samples collected at 1226. Water was clear. Left site at 1229.
Signature of Field Technician
~=="~ ~
. :,---. , r e ··~··-.,,
--·t ,:··, .~~-· '_ ~/ ~Y~EZ S
Location ID
Field Sample ID
Purge Date & Time
Sample Date & Time
Purging Equipment
Pump Type
Purging Method
Casing Volume (gal)
Calculated Casing Volumes Purge Duration (min)
pH Buffer 7.0
pH Buffer 4.0
Specific Conductance (micromhos)
Date/Time Gallons Purged (gal)
3/16/2021 9:14
3/17/2021 7:46
3/17/2021 7:48
I Vol!Jme _c>f_ wat~_urged (gals)
§nal D_~th to W~ter (f~t)
14.66
Name of Certified Analytical Laboratory
AWSL
Analytical Samples Information
Type of Sample/Analysis
voes-Chloroform
Chloride
Nitrate/nitrite as N
Comments:
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
TW4-42 Sampling Prng_ram Chloroform Monitoring
TW4-42_03172021 Sampling Event 2021 Ql Chloroform
3/16/2021 9:13
3/17/2021 7:47 jsampler TH/DL
Pump Weather Conditions Raining
Grundfos External Ambient Temperature {C) 4
2 Casings Previous Well Sampled TW4-03
11.06
2.01
7.0 Well Depth (ft) 86.00
4.0 Well Casing Diameter (in) 4
1000 Depth to Water Before Purging (ft) 69.06
Conductivity Dissolved
(umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
3735 6.92 13.50 496 0.7 98.0
1086 7.03 13.76 Before
1130 7.04 13.81 After
Pumping_ Rate Calculations
14.66 Flow Rate (Q = S/60) (gal/min) 11.00
Time to evacuate 2 Casing Volumes (min) 1.33
83.49 Number of casing Volumes 1.32
Volume, if well evacuated to dryness (gals) 14.66
Sample Container Preservative
Collected? Matrix Number Type Sample Filtered? Type Added?
y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
y WATER 1 500-ml Poly u None N
y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Arrived on site at 0909. Purge began at 0913. Purged well for a total of 1 minute and 20 seconds. Purged well dry. Purge ended at 0914. Water was clear. Left site at 0918. Arrived on site aC0743.
Depth to_water was 69.35. Samples bailed and collected at 0747. Left site at 0750.
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-60 Sampling Program Chloroform Monitoring
Field Sample ID TW4-60 02232021 Sampling Event 2021 Ql Chloroform
Purge Date & Time 2/23/2021 7:59
Sample Date & Time 2/23/2021 8:00 [sampler Tl-f/DL
Purging Equipment Pump Weather Conditions Sunny
Pump Type Grundfos External Ambient Temperature (C) 0
Purging Method 2 Casings Previous Well Sampled N/A
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 7.0 Well Depth (ft)
pH Buffer 4.0 4.0 Well Casing_D_iam~er ()
Specific Conductance (micromhos) 1000 Depth to Water Before Purgingjft)
Conductivity Dissolved
Date/Time Gallons Purged (umhos/cm) pH (pH Units) Temp (deg C) Redox (mV) Turbidity (NTU) Oxygen(%) Before/ After
2/23/2021 7:59 2.1 7.36 16.48 544 5.0 16.5
Pumping Rate Calculations
!Volume of water p_urged () Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes () I Final _Depth_to Wa!er (feet) Number of casing Volumes
Volume, if well evacuated to dryness () 0
Name of Certified Analytical LabC)ratory
AWSL
Anal~ic_al Same_les Information
Sample Container Preservative
Type of Sample/Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40mlVOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments: I DI samples collected in the lab at 0800.
Signature of Field Technician
~c,./'~t,~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-65 Sampling_ Pr~_gram
Field Sample ID TW4-65 03172021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/17/2021 7:32 !sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature ()
Purging Method Previous Well Sampled
Casing Volume ()
Calculated Casing Volumes Purge Duration O
pH Buffer 7.0 Well Depth (ft)
pH Buffer 4.0 Well Casing Diameter Q
Specific Conductance () Depth to Water Before Purging (ft)
Date/Time Gallons Purged Conductivi!Y_ pH Temp Redox Turbidity Dissolved Oxygen I Before/After ]
Pumping Rate Calculations
[volume of water purged() Flow Rate {Q = S/60) ()
I Final Depth to Water (feet)
Time to evacuate 2 Casin_g_ Volumes {)
Number of casing Volumes
Volume, if well evacuated to drynes~ ()
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: ! Duplicate of TW4-03
Signature of Field Technician
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
,/ White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-70 SamplingProgram
Field Sample ID TW4-70 03182021 Sameting Event 2021 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/18/2021 8:58 !sampler TH/DL
Purging Equipment Weather Conditions
Pump Type External Ambient Temperature{)
Purging Method Previous Well Sampled
Casing Volume O
Calculated Casing Volumes Purge Duration ()
pH Buffer 7.0 Well Depth (ft}
pH Buffer 4.0 Well Casing_ Diameter O
Specific Conductance O Depth to Water Before Purging (~l
Date/Time Gallons Purged Conductivity pH Temp Redox Turbidity Dissolved Oxygen j Before/After j
Pumping Rate Calculations
lvolu_111e of water purged _Q Flow Rate (Q = S/60) ()
IFi!lal Deeth to Water (feet)
Time to evacuate 2 Casin_g_ Vol_umes ()
Number of casing_ Volumes
Volume, if well evacuated to d_ry_ne_ss ()
Name of Certified Analytical L3b_oratory
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 Due_licate of TW 4-09
Signature of Field Technician
..:3=~
Groundwater Discharge Permit
Groundwater Monitoring Quality Assurance Plan
White Mesa Mill
Field Data Worksheet For Groundwater
Location ID TW4-75 Sampling Program
Field Sample ID TW4-75 03222021 Sampling_ Event 2021 Ql Chloroform
Purge Date & Time
Sample Date & Time 3/22/202112:30 [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 O Depth to Water Before Purging (ft)
Date/Time Gallons Purged Conductivity pH Temp Redox Turbidity Dissolved Oxygen L Before/After_]
Pumping Rate Calculations
[volume of water purged () Flow Rate (Q = S/60) ()
Time to evacuate 2 Casing Volumes ()
[ Fina_l Depth to Water (feet) Number of casing_ Volumes
Volume, if well evacuated to dryness_JJ
Name of Certified Analytical Laboratory
AWSL
Anal}'tical Samples Information
Sample Container Preservative
Type of Sample/ Analysis Collected? Matrix Number Type Sample Filtered? Type Added?
VOCs-Chloroform y WATER 3 40ml VOA u HCI (pH<2), 4 Deg C y
Chloride y WATER 1 500-ml Poly u None N
Nitrate/nitrite as N y WATER 1 250-ml HOPE u H2S04 (pH<2), 4 Deg C y
Comments:
Duplicate of MW-32
Signature of Field Technician
~ .... ~ ~
TabC
Weekly and Monthly Depth to Water Data
Weekly Inspection Form
Date
Time WI D el eot h*
· sJ tem O eratlonar't, no note
C ts bl ommen 80)!'. ero ems/corrective actfonsi
ll Q"' -a MW-4 Q "I ,,,, Flow "" (J Va No
Meter ..!J 7 I!. 4 ,, er ~ .., ,_ '6e!lt No
MW-26 I(') I, 9,q Flow Y!D No .. -na~~ JI'.. n .
Meter c-u n <" 71. "' ¥a> No
TW4-19 Flow V. No -JfJl:fJ .., <r: c'Q I 1-11
Meter ..J ,: ~ 7 " , , . ~ --No
NA TW4-20 II.IA Flow 1\.1 4. Yes MD
Meter 1\1~ Yes ...
, n n ,:;-TW4-4 Q ,. Q ,:;-Flow J l, t./ .. _._ No
Meter 7 ~ Ii;\ -:r. /_ a c-\a No
loo,.,., TWN-2 /.Q. 1"" Flow I "7 c;t ..._ No
Meter 111 <i ,., a Q I'. ~No
n<1c'"a TW4-22 -re C:: I Flow I « f'I t'allL No
Meter 7/ • .,. ('\.," i;2 ~No
na~n TW4-24 ~ I f_/ Flow I I .. ,., _. No
Meter , c ~ 1-1 , "· .. , c.., -, ~ No
'n(l-::J.U TW4-25 7n .?,"1 Flow Ill () )far No
Meter r-q ~ /;, ~ -, -~, ~No
lt7Q t;"n TW4-1 11'10 'l. ,C"" Flow I :2 /. ._ No
Meter ?."lq g "i 11:1 ~ '\as, No
ll q"2.a TW4-2 on Q.(') Flow LI.. '2 v.. No
Meter "' ., n ,:-~ o ,.:, Va No
l)Q'2 n TW4-11 0() ,~ Flow /{L.,li Via No
Meter ~.,,,. ~ ':l ~ No
/JOI~ TW4"'."21 -, ,: IJ( t;"' Flow J/. n ¥es No
Meter !> "" ~ /.. ,n .!J c:, . 71 ._ No
n4ru. TW4-37 -,1-1. ,,._ n Flow .~ n \las) No
Meter 1«~-r"I"/ a .._ No
l")Q/~ TW4-39 0. n I "1,. Flow I t;I n V. No
Meter -, '4 q a 7 'l . "" ¥a No .... ............. ,n,.., TW4-40 -, ., "'&.,I./ Flow l SJ D '\a'No ...... ,
......._
Meter r,, , -; n "'\ 7 a 1-1 -No
n4,:;'~ TW4-41 O. ll "1'-Flow I' .... /J ~ No
Meter ~ '2 ., , /. <2 -: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.
Monthly Depth Check Form
Date 1-t..-a.o,u Name Deco V"' r'""' i.,,::,,." M.11,~--
Time Well Depth* Time Well Depth*
1a~1 MW-4 12.1!::f] 1 l~i TWN-1 (.fl,lQ
Ja.5 :z TW4-1 gc..1a 1lS2 TWN-2 ta I. It;"
, a.~!l. TW4-2 ~2..111 I Q;;t~ TWN-3 ~:l.'-1
12..!:I a TW4-3 '-3, 1, IOI~ TWN-4 fol, (o?J
13D3 TW4-4 zt..~a:z lDIO TWN-7 SQ,9"
,a ?io TW4-5 ll,!i!::I I QI S: TWN-18 Gi11:2i
l!I u TW4-6 1,s..~J JQQ~ MW-27 Ia.1, ii..,.
LiL!::IS. TW4-7 ii .~13 l!:I 2._3 MW-30 2f.. aa.
I .:l!::l S: TW4-8 S&.t.< 1!=1 as MW-31 t.~.a~
,2-~a. TW4-9 ,,..~Q
162.l .. TW4-10 ~t. 83
13'21 TW4-11 9 0,QS
l~QS: TW4-12 fS:. a,
l~Oa TW4-13 S::t.,3~ l!:IQi TW4-28 .. ,s.' ti,:
l :3 25'. TW4-14 '11. 3 I l3~0 TW4-29 '1.1,S '-2
J 13:Z TW4-15 -:r. •• ~~ ll33 TW4-30 :J~.s,
II !:i Q TW4-16 :Z 3, ~ D 1331 TW4-31 U.Z3
lj3!:f TW4-17 g l, 5:( I !l 11 TW4-32 $(-73
US:I TW4-18 :Z.-u:Z i 1,a:::i TW4-33 41,s:_,:
1D~Q TW4-19 ::z0.33 13li TW4-34 lCa, 11
l:!J A TW4-20 NA Jl?ar TW4-35 1s:..a~:
I l~Q TW4-21 :Z3.~ 1]5'.9 TW4-36 $1.18
113~ TW4-22 1.;z~:32. ·~~~-. TW4-37 1a.~
1312 TW4-23 :IS:. Q{1 l.23f.t TW4-38 5'.:!,3S
ll 30 TW4-24 t..g.s1. l~:U9 TW4-39 cz.J. NU :z!.l~
11'·1 ~ TW4-25 21.lcl. 1?.a.1 TW4-40 12 .a,a
1318 TW4-26 :Z3, l.l l]Q.Q. TW4-41 19,].a
134', TW4-27 16,115 132':t TW4-42 49.QCJ
Comments: (Please note the well number for any comments)
rltil~ -.1.a A ba..od11tu:d
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
Date 1 --1 1 -,i\ 1 '
Name
Tl me W II e D th* eo C ommen an~ ero ems corre ve actions}
J?.1.~ MW-4 ~::l. .9,~ Flow "1. (J ~No
Meter ~ ..., "1 rA 1.1 /',. :; t;" q _.._ No
Jt)~.2 MW-26 ,/,, ~I Flow J I~ fJ -No
Meter r; '"I ;i 7 -, ri ~ ~ No
J LI J A TW4-19 7;:J..t.7 Flow I~ .. ~ 49 No
Meter ~ r:' '-I q ~ n 15 5' -No
t-..lA TW4-20 NA Flow NA Yes Ml>,
Meter "' A. Yes ----"-•
I~ \'"11.:1 TW4-4 . ~\. \; Flow I l.. '1 ... -No . Meter 7 ~ q '-' q q . i;-~No
Oct&.'~ TWN-2 ~~ 1-0 Flow I /A IA -. No
I Meter ~ ~ '-' , a Q 7 .. No
I fl (i ,;-' TW4-22 7;;-() I:( Flow I~ n \fs9 No
Meter -, c;-"'f, 1 q . q Yea No
innD TW4-24 "~ • J 0 Flow / I'-/) --No
Meter 1 ,; '-i -:J., ..,'-I I t *" No
lnq14' TW4-25 7'-1,/9. Flow "" IA -No
Meter 7"' -i_ u ~ tz .., ~ '-No
I"\:'.)~ TW4-1 I fJ ,:::(", "1 "1 Flow 1.:l.'-/ ~ No
Meter 3 r; pg~ .:.t • \ ~No
ll0"4CI TW4-2 , nn 4 IA Flow I/,. '-I ~ No
Meter L.1 ~ , ,_ :i ~ ::> '$ No
I f1 '-l 11 TW4-11 ~~ q'l.. Flow It; t..J \a No
Meter ,:; 7 1 ~ r ... )(a,:, No
no~c:, TW4-21 7~, if Flow ,.., n ~No
' Meter ~ c-n'!«, "--~ 6. ~No
IOI~ TW4-37 .., ".J -:z,-, Flow IR n ¥i!li No
Meler , ~ n 1 1 , A rA . ~ \9.. No
1n'lll TW4-39 ,'3 '1~ Flow I~ 0 '6ea--No
Meter -, r: -2 "£:"<Q . -, ~No
,-,.~!) TW4-40 j".1_ .--a..n Flow I~() ~ No
Meter ~-, ~ "1 '-f C:: ~t; Va No ,~~7 TW4-41 siq "\ Flow z: 4 --No I Meter ~ ~ ~ 'l-=, "I t.f I ~ No
Operatlonal Problems (Please list well number): ~y-~
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Ti W fl D th*
Namey2 < _ G: '.f'o,.,~ k-taM;;_ & £l '?
Sv~em Operational ,lfno:ote
C ts bl I
Date J-I$ • .2..l
me e eo ommen an~ ero ams correctfve actions}
inq~ ~-MW-4 O.'l nt_ Flow 1.,4 0 ~ No
Meter ~ -, !ll =-'"' '] t~ 1..=1 ~ No
nqn" MW-26 Q~ Lf.l. Flow Jr.. t..f MIIP No
Meter i::"" '"' q , ,_ , lta No
J"'.'1.tn TW4-19 ,"'\ 1~ Flow JI,. JJ ~ No ,
Meter 'J r; c;.-q c;,; :i ~ .-.. No
1\.1 6. TW4-20 N 6.-Flow "1 &. Yes a.
Meter .... ~ Yes .ca
/')QUT TW4-4 Q.<". ~ n Flow I/,.. q ,,, ~ No
Meter 7£1 n r;-~ t , ¥81 No
"~ i.~ TWN-2 C-Q ,:, I> Flow 17, ~ ~ No I Meter ~ '-4 "'l J-~ ·~ ,A ~No
09. Lf t'.,. TW4-22 r..~. ~/J Flow I(,., "1 ._ No
Meter --r/ .. /,. ', z; I.-, ¥la No
t') Q. "'#") TW4-24 t..:. .q . 7. I Flow J (.. I) .. No
Meter ,,;~j \ 74 ;]~ -No
fl~~/. TW4-25 ~Q ...,< Flow 1n ~ ~ No
Meter -, ,,,, Q 7' 41 a ~ n l{Bt No
nc=t~~ TW4-1 ll>~ 9.a.f Flow I:, 'A ... No
Meter ~ Ii I .:> -~ :1 .., -No
l)Q'.]~ TW4-2 ,nn 7< Flow 11,J n ... No
Meter ~ :2 .:1 q ,; c ~ -No
0(111-TW4-11 Qt). ::u, Flow J ;"'. .,, ~-No
Meter /A n _.:, . '1 -r .W. No
nQ~f) TW4-21 -,11 ,..., Flow 17 /'1 ,_ No
Meter~ i::-t1 ~" "I ~ 'ta-No
-
/),:J <'::J TW4-37 /_ /,. /_/') Flow I 9. 0 -No Meter j 4 o tn 1' n 1 • fl ~ No
nc:,nn TW4-39 <J.a.,c:i Flow ,~ n .... No
Meter ...,~,,.. tJ ".l 1 ' 'as No
QQ~t.::: TW4-40 ""H . ~a:;-Flow 19., I) ~ No
Meter ,,., <2 kl ::l -:t. , ...--. No
/'14 '-I I TW4-41 ljlq. QI Flow (,.. () ~ No
Meter ~ l.. 4 ,::, q"' ,:i 'l ~ No
Operalional Problems (Please list well number): f!:'t':!,J,,1!:J)
Corrective Action(s) Taken (Please list well number): ----------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date
Time Well
Name p,,,, c~ 'J'm-, Ieoacc Hell, 7.
Deoth*
ystem Operatfo al (ff no note
Comments anv oroblems/corrective actions)
,,q~/. MW-4 C.'.l ~n
Meter ..:;t"T~n, ... 1.11-4 ,,.. ~ No
MW-26 .,. tJ ,_,., Flow 11-.n 'Git No
Meter ~'-171 "'1 ~. ,,,.. 'im No
Jt"(n TW4-19 -aq l' Flow 1 ,.. n "-No
Meter ..1.. rt' 7 /J .., u 2 , 'W1 No
NA TW4-20 NA Flow "' A Yes ,Mat
Meter l'>l A Yes. ble:>
TW4-4 Flow , iA ~ .. 'Ala No
Meter ., t.t I c...Q c:;-, ,;-"91 No
ti ca ,:-.i TWN-2 Flow 17. n V. No
Meter ", ... , ~ Af. &. LI "-8 No
1nc,1n TW4-22 Flow ,, •. 1.. V.. No
Meter ., ~ ~ .=u1 ~ . .!l ._ No
nqo2.. TW4-24 -rn qc Flow 11 •• 9. 'aes No
"MJI No
ns ... :or TW4-25 ~ 'I ~" Flow 11 o 't.e No
Meter 7 , 5" 1 1-( ~ -.r ,,.., '31 No
, nn ,;-TW4-1 1 n ::i , '21 Flow , :i ,-, ~ No
Meter .,. I;" , "'1,. t:". 1 • \il!IP No
1nq" S1 TW4-2 qo, ~t:. Flow , ,. '.::I "81 No
Meter ,., 1.."' """ , , , ':I ~ No
nq~q TW4-11 o.q. a" Flow , r:-1. )ia No
Meter 7 ef , q n V. No
1119"" TW4-21 -, .2. 1 « Flow , "-" V.-No
Yee ·No
()Q, t-TW4-37 t:. r. .. !U Flow , ". a ~ No
llCf 2 '\ TW4-39 -, "'· ., 'T Flow , • o .._ No
"-No
JtJ:J.. ~ TW4-40 7 fl • 1 q Flow 1-A • n )aa No
Meter r. q" n 11 '3. D 1 "88 No
Lnl::J. TW4-41 ~9 ~~ Flow /...O "-No
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
Date a,-t -&,I Name Pc, 0sG:::
T W II D th* C lme e eo ommen 8031'. ero ems corrective actlonsl
Jlln"f MW-4 4 ~. I\ Flow "4 • () ._. No
ts
Meter .:> .., ~ .., « .., n ~ ~ ~ No
-
l.-'>G" 0 MW-26 "1Q .,~ Flow I I. n Vat No
Meter ,;;,.., ~ ~ ~-, .:i Va -No .
II""~ TW4-19 (11, q .I:: Flow Y,?n ll ~No
Meter , < ~ n Q « .., , /J -.. No
I\JA TW4-20 ~u .. Flow f\.l 6.. Yes ...
Meter NA Yes ...
tn'l, TW4-4 <a. n ,ci. Flow , ., n .; :-No
Meter 7W ':J-, l) /,... •.., ._. No
~O~"'.l TWN-2 ;,:. LJ "2.1./ Flow II. "ii. ._ No
Meter -,. .., ci."' n ~ ~ Yea No -
l)Q"l1' TW4-22 QI D~ Flow 14 /J .... No
Meter ., ., .,, n c-,:-q VS> No
OG".l4. TW4-24 "T/1 9.Q Flow JI. n ¥ea No
Meter , e "· / c « ~ , , V:n No --
/}Qlf .. TW4-25 Qt le'" Flow J,, ,. ¥a No
Meter ., -i 1 , •.,. 'l !I -. No
Jl)l':I TW4-1 1n:i ~7t Flow I !l Q ,_ No
Meter "1.r ~"· ~-, c-V. No
Jfl n"" TW4-2 I I\ -C:: I Cl Flow 'I.. '.'.J "-No
Meter u~ .... ~r:..,,o cas> No
{)Q,:: /_ lW4-11 an 14. Flow I /,. /') v.. No
Meter q « <'. -, 9. ~No
Qq1 I TW4-21 ~"' C: l!J Flow ,.., ., "*-No
Meter !l c ., '-~ ,.,, , r.r-"8a.... No ,
lt")Q1oG. TW4-37 /. I. QJ) Flow 14 /'J .._ No
Meter 1 4 , t.. o , '\ . -, VD No -.
Oct&.11. TW4-39 .., .... -..,..., Flow I~ (1 .. No
Meter 7 ~., ,. ,: 1,. . n ._. No
,,, ':111 TW4-40 "'f I I.I~ Flow ,-a n V. No
Meter 1 .. q t:: 1,, i:; q n /J "fillJf> No
I n141. TW4-41 ~Q IA t:;" Flow /. fJ Yes, No
Meter 'l .... "-':l"' .:i. ~M Vea 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
Tl W II
Name:J2cce G:: l,rmr""'/• ~ ~
Svstem O eratiC!_al_~ote
Comments anv D bl i
Date a-,-N
me e eo ro ems corcectlve actlonsl
13.l I MW-4 'st 2 () /'_ Flow 4.n Vas No
D th*
Meter 2..ca n t; .::1 , :1 !J ~ ~ No
l~D~ MW-26 -tO, 1i:;'" Flow IL 11 ~ No
Meter z; < n !i'ZJ s. ~ ~ No
Ff rJ(J TW4-19 70 oc:i. Flow ( C. 0 "88 No -Meter :J ;:-q 'J... / 'i" t;": , ~ No
NA TW4-20 1\.1 A Flow NA Yes MD
Meter t-...1 A. Yes ..
'" 3 IM TW4-4 "itl l 'h Flow It...~ 'A .. -No
Mete, ., .... ~ -v_: -a ---..,, ~ 1' <Z. I "-I .., -.,. No
J :1. "ID TWN-2 K(:\ t. I~ Flow J t:. c.. .. No
Meter '). q 9,. n < 1 'l Yae:9-No
,1~1 TW4-22 l,.q. ,q Flow 1-a Q Wit No
Meter -, ., , :i , 11. t:5' .._ No
12.'1~ TW4-24 71 ~I) Flow J (,. '.l ._. No
Meter , 'f' ., ~ , o ~ t ... q V. No
,~"l~ TW4-25 71',, .21 Flow I {} J./' V. No
~
Meter -y -i • -i. ~ ~ 0 sr ¥iee-No
I~~ g' TW4-1 ,01 '1l Flow ,1.~ ~No
Meter -.., ~ J -, a ~ -a.c 'rt L./ t'. D t:;" ~No .,
I~\ Co TW4-2 qc. ,:~ Flow ,t, "" .. No
Meter "'.!> 11:''"T, " ~ ._. No
J~ \ \ TW4-11 cw t,.n Flow J(. 0 ._. No
Meter 102'1. -,() 'lCB" No
f!l!lQ TW4-21 7 . ..3.. .~ .. Flow I I'. ~ v.. No
Meter ~ c-.33 s; ~. t:.~ '8!IS> No
I !l ,;'~ TW4-37 /..I':. !l..".l Flow I 'ii. 0 ~ No
Meter , q "n"1 -t ;1 1 c:,' 11119 No
I'\ 00 TW4-39 ., .... Q"1 Flow 11i n .._. No
Meter 11',./,qt;c, ~ Ya No
l "1. &.f ":I TW4-40 "'11 ~"1 Flow 19. .0 ~ No
Meter -,n~".l~~ ~ *8 No
I '3~ \ TW4-41 'Act "7 !3 Flow t;.O <3!la-No
Meter ~ '.2-, i..4 ~fl !i ir' ~No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Monthly Depth Check Form
Date ,;1 1 V -z.p-z.l Name ---r'eoocc HR u:J.e.j , Pc:ea l~me,,,
Time Well Depth* Time Well Depth*
Q'l~j MW-4 81 -ts'..:2 Q~l:Z TWN-1 bS 17;t
o~~~ TW4-1 ~-, 9D Og6~ TWN-2 sa.~
Q9:!:.t TW4-2 ~l. lb Q9~Q TWN-3 ~2..5~
O~l':1 TW4-3 ~.9 '1 091'1 TWN-4 C,, I. bi; '
IDQI TW4-4 ~~-~ Q~ ~(.,. TWN-7 ~t> .~l._
Q81~ TW4-5 1 1 . .ss 09.2.5 TWN-18 ,2.ig
Q32.~ TW4-6 :18. 51 Q~:;3 MW-27 57.~I
0$1~ TW4-7 ~1 .)3 Q~l~ MW-30 ,S.08
Qg 'Z..I TW4-8 8'2 '2C Q~ID MW-31 ~~.9~
()g I~ TW4-9 kz~.'ifa
ogoe; TW4-10 b~.8~
Q~~A., TW4-11 ~{l.)~
Q~~ TW4-12 5S .'-i Z:
c)9L~O TW4-13 5~-~~ cis~ TW4-28 ~rs;1-.l--
QZ~b TW4-14 :J.J.~g Qfi~~ TW4-29 1!,00
Oj1j TW4-15 !1.51 '~~~ TW4-30 7~.Sl
Q90::? TW4-16 i:!>;~~ 0~6 TW4-31 1, l!
C~Q~ TW4-17 g1.~ Bfflo3.Sb TW4-32 SS,1 ~
Q~ 19 TW4-18 i:J. .C.b OK~~ TW4-33 ,1., gb
11 :IQ TW4-19 7:l..2.'i OS!4C} TW4-34 :1, 2 ll
I'll-A TW4-20 t':"."/A 08':12 TW4-35 1S,I/ '
Q~IC... TW4-21 75.72. Of$~~ TW4-36 57 ,7 2
ot:t2> TW4-22 '8 % O[Sl TW4-37 b7,5b
()~2~ TW4-23 :lS-~ QSllz TW4-38 59.!:H
0~35 TW4-24 12g I g5 Q2:~ TW4-39 ~6: ~~
O§Z.I TW4-25 LI .91 IOO~ TW4-40 7 1.gc.
Dg2.9 TW4-26 J ~ '!t i Q~:55 TW4-41 ~g .1 1
D~'\C.. TW4-27 18,7 S D~::l, TW4-42
"" 22
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
Ti W II D th•
Name O« o <I: /fnrr"t; -C,:,,; Ko(/,'), ·<
' stem O eration:?ilf no note
C ts bl 1
Date a-is:, At
.__me e 8D ommen anx Qro ems corrective actions)
t,Ql,f 11 MW-4 ... Cl!:l Flow '"' () V.S. No
Meter ~a,~ -::a. 1 !l C'/.. '$ No
nCf!2~ MW-26 "..,. ,; "1 Flow ,,.. / .. ¥81' No
Meter C'.c' ~ Q 11 ~ ~ ~ No
I I i..t I') TW4-19 "T!I '.:l~ Flow J /. n ~ No
Meter ..=._ l. () I /) ~ I. c::" ~ No
NA TW4-20 Nb.. Flow I\JA Yes ~
Meter 1'.IA Yes -1nru TW4-4 Q c:" c:-,: Flow l '1. '-4. ., ¥ta No
Meter .., .1.1 '-' q \ \.l • "" ~ No
1)4'1G TWN-2 CtA :l.l Flow u. -~ -No . -
Meter ~ , t,,,. ., n .., a \!Bis No
"~ ".1 TW4-22 /_fl 1 ~ Flow I '1. I "-' No
Meter -,..,,:zw ~ ""-~ ~No
I /JCI '2 I( TW4-24 /-Cl.ct~ Flow J/... ~ Y:a No
Meter I lr'<Qlla-, t /J7 ~ No
n« '!ll a TW4-25 ,.,_ .. qt Flow ' f) &.J *8 No
Meter ~ -a. '-I •I .:i "' . "1 '-I -No
/)Q&.IQ TW4-1 Q"'f Q ('\ Flow I ~ « \As> No
Meter ~,:1-10 ~ 1 .... ct ~ No
lt')Q'1t1 TW4-2 Q. \ \ ,_ Flow , .., t ... -¥19 No
Meter .., 'l 1. "'1 , '1 ~ ,._ No
oq~~ TW4-11 4n .~ Flow I l.f • <;l ·~No
Meter , , It' ..., .., ~ 11MR, No
O 'Z I C: TW4-21 -,r-, '2 Flow , , .. '"' ~ No
Meter !'1 c "' 1 'l I t q "'° ~No
'l)Cl.4i"'I TW4-37 t.1. i::t. Flow ,~.n ... No -Meter '°'., ~ ~-1_C\. a..t "8a No
l.tJg ,:,i TW4-39 .I .. Q "'I,./ Flow IQ I'} ... No
Meter -, ,. ~ fi1 ~ \ • ~ ... No
1on a TW4-40 .,, flt~ Flow J ill ll Yes No
Meter 7 /J T ~ "" ~ 1.t ..:i. Yes No
_nq,:,: TW4-41 1Ul.1 I Flow I •• t> ~ No
Meter -,. '.l q ~ , -,. t::' I.I ¥:as, 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
Tl W JI D th*
Nameq,0 rry«•-z; -,;:;1 ; 1/«t?~, s ;tem o eratlonalff no note
Comments anv orobl ~ ctl I l
Date a-aa -a,
me e ep emscorre ve act ons
OCJ':1 n -MW-4 'Kl f ~ Flow "{ .o V.. No
Meter ~o. ,t.\~ <c:t.Lf« "-No
OQtJ ,. MW-26 ~« ti Flow J (.. .!I. -No
Meter r: ~ ,: n 1 '1 i:-... No
-
Ill.If: TW4-19 qw 7-' Flow }~ « ¥.as, No
Meter !lL. J tJ q 7 -, .., --No -
tJA TW4-20 N6. Flow Nf.t.. Yes *' Meter Na. Yes ..
111n, TW4-4 -JQ .«q Flow Jl .. L../ .,. Vas No
Meter ""T..., ~ n ~-" Ll ~ No n•~.., TWN-2 e4 ,:, Flow I (,. ll Va No
Meter ~ -. ,., ~ , , ~ --No
-
I l'J '9l'·t .:i TW4-22 ~C". q_q Flow J /,. :J. ¥.a. No
Meter ..., .., ~ ..:1_-, ~ "'.] ¥af> No
D91&4 TW4-24 1,.q,n.:1 Flow I/.. "'{ "86. No
Meter 1C•.,~n1 ~~ dl1iN No
10 S1 .2..1 TW4-25 ~/) 11.f Flow I~ 0 ~ No .
Meter '7 'i/7"~, ~. Q 7 ~No
nq~~ TW4-1 JIJ~, !In Flow J .2. 0 Yle,s No
Meter '3 G 'I 7 ~ .. ,. l) WBB-No
l{)q~_\ TW4-2 q\ ltiL.. Flow Jln . -,_ Via No
Meter 'I :i_., ., ..._ ".l. • \ 'Mt No
l)Q\ t:' TW4-11 IIQ.~'"1 Flow I a;' a../ '*6. No
Meter 1 -a Cl( ..., • "" &../ .-,No
IOJI"/~ TW4-21 761/ • ..,.~ Flow J'1.I.. "81 No
Meter JJ.~~s 7 -r~. ;;-I ~ No
lbSl~O TW4-37 la1,'"19 Flow J 9 /') '9 No
Meter,a.., a Q ~, '-I .__ _No
AQ"n TW4-39 -,~ "4/ .. Flow UI.O .._ No
Meter , ., , ,. 12a • .:i V. No
Jn i~ TW4-40 .., \ ~~ Flow ,~ n V. No
Meter ~• .1, n~ ~q ..._,.No
,lf'Jq"' '!J TW4-41 q_o .111. Flow ~-iR .... No
Meter ~ .J q 4. o ,; ,r,. 1 ¥at, No
Operational Problems {Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date ,-,,a., Name Deen C.. l4rnon G:ec: c in f!. \mcc I I
Time Well Depth* Comments
llC\·~• MW-4 «1 •• ~ Flow "" n
Meter !J_• ~, R., L 1 ~
nct1n MW-26 "1 ]. I~ Flow ),. "
Meter ~~'7~ ~1.1
101G TW4-19 "'l".2 .,(.1 Flow J t: 9.
Meter .2.t. !I. n T '7 fl. a
NA TW4-20 Flow ""•A
Meter N.b.
4if. It. Flow ,~ o
Meter ~ ... ~, -:i_q.~
bC1 < TWN-2 Flow u .. 2
Meter .,,,:-.2..~C". ~•
r
lJ'IIIT TW4-22 Flow , , •• 11
Meter .., ., ., " -a :i .. 2.
n1ta, 1 TW4-24 Flow ·". 0 Meter I C" .. "114 ,r ti. 7 C"'
~ 't.
D11.fl TW4-25 Flow JIJ. ,,,, .. ,,
Meter ~ll1 !!we.~\ --
Flow 1,'.:l .~
Meter :iJ"4"..., .l .:i , 'i
1nQ~~ TW4-2 Flow ,.., . 0
Meter o11 .2.1 ., ., 1. ~
OC\lt.. TW4-11 Qll. ll .. Flow Jll.1'1
Meter , .,. .... ~ -~~
11«<, TW4-37 G~.~n Flow 11.rJ
Meter I G ~ ... .& c ct .• 2.
.Dlltn~ TW4-39 '1'1 .,.,, Flow IA.D
_ ~ _ _ Meter ,.,,. 'I ~o. «
OQ."1'1 TW4-40 ~.;.i:_,,-Flow , ~ o
Meter -,1 ~ ':I 1t.. o<
oqcq TW4-41 flai 1\0 Flow &.. n
Meter 4 ~ o &f '11. '!: "·
System Operational {If no note
anv oroblams/correctlve actions}
'ua No
'lfel No
V.. No
.._. No
Yea No
le!II No
._ No
"-No .... No
"'-No -No
._ No
-... No
. ... No ._. No
}{a, No
).., No
'ml No ... No .... No
Via No
..... No
~-No
'lta No
~No
"-No
.._. No
'a No
Va No
'*9 No
"81 No
Operational Problems (Please list well number):H /.-r.:*l,~~"-"':J"T"''"""· "'ln.iA~\t-----------1 .41 --.J ~-J J
Corrective Act1on(s) Taken (Please hst well number):_'-, ____ ,, ___________ _
* Depth is measured to the nearest 0.01 feet.
Weekly .Inspection Form
Date 3-S-a,, Name;;r:;..co & t"'<Ji, :z:;:111:< 1'i//,,,_, vstem Ope~atlonUff no note
C ts bf st 1· W II D th* ,me e en ommen ank'. ~ro em corrective actlonst
inn '7 MW-4 oan.'-~ Flow L( /) VD No
Meter ~~':ta.a~, .. 1.-1 ~ 'tD No
()Q a::: I MW-26 7!.l.."il:l Flow ,., .. n ~ No
Meter < ,;-q c; 11t -i V... No
1 ~ "=l" TW4-19 ~., ".l I Flow Ir. -r. ~ No
Meter :'.) , • .,,'1 Q 1 -, '] 'e No
r,..1.A TW4-20 ,.., A Flow fl.It. Yes ..Mt
Meter ,.., A Yes_•
11' •HI TW4-4 -,Q .Ad Flow JI •. ~ ., '>lei No
Meter 7"' 'I. :i. , , • _ Q -No
il)Q'\rt TWN-2 ,C' ~ "1 l Flow //-r, Ya No
Meter "'..,",. , o "· -No
n4~a TW4-22 .,,._,:', .. " Flow J~ "I Ya No
Meter 7 ~« 7-, 2 ,... -No
na-.,,: TW4-24 71. I\ Flow II'."' -No
Meter 1 c;-cHt Q er -, -, ~ V. No
no,,. TW4-25 ~ .. ".2« Flow ,n a )a No
Meter -, 1; :i 1A .'J ~. ~ s:, V.. No
1n1~ TW4-1 I/JC t',. e;' Flow ~ J'.I.« ~ No
Meter ~ t;" f ... l -a. , ~ V:ar No .
1/ln~ TW4-2 JI I ~ t Flow Ir..~ Vee No
Meter "' ~ c:t -, ., ~ ,,. Ya No
/JOI!!',. TW4-11 «.~ "1.1 Flow It. n Vea No
. Meter , 1.. <' ~ " ,, ._ No
nant. TW4-21 -, C'. 'ff "' Flow ,, •• ,rJ. '-No
Meter ~ c , .. , ,. a'"' ..,. n ~No -
IJOq.O TW4-37 ~, ... ct.n Flow 14 n "-No
Meter , " ~ Q 1 " a . , ... -. No
[IJ41/lf' TW4-39 -,4,f /J J Flow 11'.1> '*" No
Meter -, 7 71?"" r ~ "9 No
Ill':\ "!J TW4-40 ""1 l , .. u:::-Flow I ti.. /) '-. No
Meter "1 ::l. -1, -, ;_ .., .., ll ~No
f/'IIQ TW4-41 61"\ .,. Flow I,. () Yiatt. No
Meter '1 :t 1 ~ "l 4. na ilD No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date :,-,s:~a.,
Time Well
StemJ)r,eratloaHtf no note
Deoth* Comments anv problerns/correctfve actions)
Name:;o.,rz i<r4<'/. ~c< &:;;/~.,,
Q.a '-1'1 Flow "'-o "8s No
n .. qn MW-26 q.C-. --1" Flow , <a ,.., 'lea No
Meter ~ t:. 1 -, it &-1 ~ No
, 11-10 TW4-19 '7 !l i ~ Ffow , t. o .Ya No
.-.. No
JJA TW4-20 NA Flow NA Yes Nit
Meter tJ .Jt.-Yes le
rn,v .. TW4-4 7" ~ "::t Flow 1 t.. n ., ._ No
Meter ., '"I q-.,,, n , :l. Ve No
:o«~Q lWN-2 4'1'. ~~ Flow 1 'T o-._, No
Meter "'srQ "J._-, 1 a.t Vs No
,,,~,., 1W4-22 'An .1, Ffow , 1t n ~ No
Meter , ~ o i..1 7 t., .. ?i -.._ No
J,,.,..., TW4-24 71 «1 Flow 11 .. a .._. No
Meter , t. o ~ su ,;-7 a. 'Mil No
051 ,.. -cl TW4-25 1~q '1!1 Flow 1D ~ 'a No
Meter '71... otH1 ~ ar, V. No
nQ.ir;-~ TW4-1 10« 7n Flow , ~. :1 V:ea No
V.. No
1 n 41.f ,c-TW 4-2 11 .; 1 -a F•ow , 1.. '1 'Ml No
Meter 4~ll ~ g~ 4,c "91 No
Vies No
Meter , , qq '~"" V... No
01"4&4 TW4-21 Flow /&..,. -No ¥ll!S No
IL>Q 1411 TW4-37 Flow u1 o .._ No
Meter , 111 ., ~ T q .:a_. :a --._No
fJ'l2.&4 TW4-39 "'1'\. -rte Flow 1 11, 11·;· 'a No
' Meter 7« n "1 "4 , .::t "1l:m No
1010 TW4-40 -, .2. ':I.ct Flow ,~.n '*9 No
._ No
1 tUJI TW 4-41 Flow ra. o 'ifla' No
~ 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
Time Well
MW-4
nq-a~ MW-26
, ~ ~n TW4-19
J\I A.. TW4-20
J/Ull TW44
,, Q , <:t TWN-2
nQ'.l~ TW4-22
1ne11..,,, .TW4-24
nQn.., TW4-25
tJQr::'-t TW4-1
ntu,o TW4-11
nqn ~ TW4-21
na.,.u::~ TW4-37
n9.,: ~ TW4-39
IIJI t. 1W4-40
JIIIJU TW4-41
Deoth*
Weekly Inspection Form
Name17«n tryoo,. :z::=r: M.l(.z
System Op: ttonal (If no note
""l , , Flow 'I' o ._ No
Comments any problems/corrective actions)
'mil No
Meter ,: I'. 4.11 < 1 :i 'MIi No
...,, «t'. Flow ,t....n V. No
"-No
Flow ...i b:.
Meter NA Yes~
'7'\ ., ,:. Flow , ,. oS( ._, No
~ No
Flow u ... '1 "lfm No
Meter <'n 7 "11 , t;" -_ No
,,. <'. gl;"' Flow , ~. ,. V. No Meter .,. -i ".I \ c; ,~ 'a No
,;ta q -, Flow , /. "' V. No
.__ No
to« ..-1 Flow , ~ n "-No Meter 7£./. ~ !l_'-/. ~q-'699 No
1 " "' , '1 Flow , 2 , .. V.. No
Meter ~c;:7~ ~,. ct Vies No
Q~-"''l Flow JI'.·. !l ._ No
Meter " 1 /·<R 7 ~ 7 .._ No
QI\ 1./\ Flow , , .. n ._ No
Meter , • ., .., q r .._ No
~ . .!I .6-z Flow ,~ . .2. *8o No
~ No
~ «. 9. .,_ Flow , <r n 'w No 'Meter , Q a.(~~ n.:) i. ¥al No
7"'1. ~" Flow , o. () Ya No
Meter ··uu w,, ,_ -« ¥m No
.., ~ , ~ Flow 1 ~ () ¥ca No
Meter 7~u:~ 7'H. q-"' V. No
a ., "' -, Flow. t. . I) ¥.al No
YA ·No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number):
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date 3 .. ;t,-cJ
Time Well
Name Men ,;... 'fmaj :z;;;;,.«: .f&t,:7,t
System Ope onal lit no note
Deoth* Comments anv problems/corrective actions)
« :1 ., ,,_ Flow 4. n -_ No
lo.Q~t; MW-26 .., ..2. "11.1 Flow ·, 1. '] 'lfes No
Meter z: ,. ,. '1 '1 '.:> . "-1. V. No
I 't I~ TW4-19 "~q c,.\ Flow 1~ O ..._ No
Meter ~ /:. c. n"" .:i...!l. • I V.... No
rJA TW4-20 ,..., b. Flow N 6. Yes .W.:..
Meter N b.. Yes "-
J£ln1 TW4-4 ~, .. ,a; Flow '~-~ ... ~ No
Meter 7.tt:~/J 3-A.D -S No
rn«ir ~ TWN-2 c.a ~"' Flow , ,. 'l 'a No
Meter c !J '-'nu n ~ '8 No
1n<1 I/. TW4-22 V.. No
Meter TQ ~q ~ ,,. . /) ~No
Otl()t,,. TW4-24 'Tra ,_.._ Flow Lt._ t .. ¥ID No
Meter , ,. 1 , q J;" q 1-r *""'No
11'A&.1-r TW4-25 1..,q_ 1.1. Flow ,o.,,. V. No
Meter ., -, .tJ "-2 h • "q 'a No
1 '1 "'« TW4-1 • ,.~ '.1..!l. Flow , '!I. .. 'a No
Meter ~~111 "I I n ~ No
net"""' TW4-2 11L1"'\ Flow u. '.:l. "-No
Meter .&.f ~ "let 1&.1."1 .._ No
aqu ~ TW4-11 Qn n« Flow '"'· • 'tles No
Meter , a 1 ... 1. r. ,;-*it-No
IOtJ'in TW4-21 7~ ~it') Flow .Jt:..6'1 \a No
.._ No
100, 1 TW4-37 I';./,. e:z: Flow , ~ fl 'all No Meter , 1111 r: ~ ~ q ~ . ..., Y411J No
nq, n TW4-39 -,,,1. ull Flow 1 « n "-No
Meter -,~,; ~q.~ "-No
/6-'LJ" TW4-40 7.::t .1' -:l. Flow 1 q . n ¥ea No
Meter -,a./n ~., n.r:-n ¥111 No
, '\,C"~ TW4-41 ~«. /..ill Flow ~ _ n 't. No
Meter -·~14''1 ff.ct~ 4!Bs, No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------------
• Depth is measured to the nearest 0.01 feet.
TabD
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary
Name: Tanner Holliday, Deen Lyman
Date: 3/ I I /2021
Depth to Depth to
Date Time Well Water (ft.) Date Time Well Water (fl.)
3/11/2021 1429 MW-01 64.71 3/11/2021 906 MW-04 82.63
3/11/2021 1318 MW-02 109.41 3/J 1/2021 900 TW4-0I 105.11
3/11/2021 1300 MW-03A 83.47 3/11/202] 909 TW4-02 111.30
3/11/2021 1211 MW-05 108.08 3/11/2021 921 TW4-03 63.92
3/11/2021 739 MW-11 84.99 3/11/2021 853 TW4-04 79.51
3/11/2021 1215 MW-12 109.60 3/11/202 I 930 TW4-05 71.46
3/11/2021 1006 MW-14 101.60 3/11/2021 850 TW4-06 78.58
3/11/2021 1009 MW-15 !05.23 3/l 1/2021 903 TW4-07 82.04
3/11/202 I 1305 MW-17 71.74 3/1 l/2021 917 TW4-08 86.48
3/11/2021 1424 MW-18 73.40 3/11/2021 927 TW4-09 69.41
3/11/2021 1352 MW-19 65.50 3/11/2021 933 TW4-JO 68.78
3/11/2021 715 MW-20 85.01 3/11/2021 913 TW4-IJ 90.08
3/11/2021 656 MW-22 66.10 3/J 1/2021 837 TW4-J2 55.24
3/J 1/2021 1219 MW-23 113.86 3/11/202 I 834 TW4-13 56.28
3/11/2021 1204 MW-24A I 11.24 3/11/2021 828 TW4-J4 77.22
3/11/2021 1201 MW-24 110.18 3/J 1/2021 953 TW4-16 73.27
3/11/2021 742 MW-25 80.72 3/11/2021 1045 TW4-J8 72.55
3/11/2021 937 MW-26 74.08 3/J 1/2021 1058 TW4-19 73,15
3/11/2021 1052 MW-27 57.31 3/11/2021 1048 TW4-2J 70.71
3/11/2021 1151 MW-28 74.28 3/J 1/2021 947 TW4-22 68.81
3/11/2021 1156 MW-29 J07.03 3/11/2021 746 TW4-23 75.05
3/11/2021 826 MW-30 75.05 3/11/2021 950 TW4-24 69.94
3/11/2021 JOO] MW-31 68.87 3/11/2021 J039 TW4-25 70.01
3/11/2021 957 MW-32 81.60 3/11/2021 750 TW4-26 73.29
3/11/2021 1230 MW-33 DRY 3/l 1/2021 809 TW4-27 78.73
3/11/2021 J015 MW-34 107.36 3/11/2021 840 TW4-28 48.68
3/11/2021 1223 MW-35 J 12.11 3/11/2021 825 TW4-29 77.91
3/11/2021 1226 MW-36 I J0.33 3/11/2021 815 TW4-30 74.85
3/11/2021 JOJ2 MW-37 J05.98 3/11/2021 812 TW4-31 75.99
3/1 J/2021 701 MW-38 70.32 3/11/2021 843 TW4-32 55.65
3/11/202] 704 MW-39 64.66 3/11/2021 806 TW4-33 77.66
3/11/202] 804 MW-40 79.56 3/11/2021 822 TW4-34 76.24
3/11/2021 818 TW4-35 75.38
MW-26 = TW4-15 3/11/2021 831 TW4-36 57.75
MW-32=TW4-17 3/11/2021 943 TW4-37 69.19
Comments: 3/11/2021 924 TW4-38 59.45
3/11/2021 940 TW4-39 72.25
3/11/2021 753 TW4-40 71.41
3/11/2021 856 TW4-41 89.22
3/l 1/2021 803 TW4-42 69.18
Date Time
3/11/2021 1356
3/J 1/2021 ]347
3/11/2021 1340
3/11/2021 756
3/11/2021 800
3/ll/2021 1042
3/11/2021 1036
3/11/2021 1327
3/11/2021 1335
3/11/2021 1421
3/11/2021 1434
3/11/2021 1407
3/11/2021 1412
3/11/2021 1331
3/11/2021 813
3/1 J/2021 804
3/J 1/2021 801
3/11/2021 1235
3/J 1/2021 756
3/11/2021 753
3/11/2021 751
3/11/2021 1253
3/11/2021 1249
3/11/2021 1244
3/l 1/2021 746
3/11/2021 710
3/11/2021 743
3/11/2021 731
3/11/2021 728
3/11/2021 720
3/11/202] 735
3/11/2021 724
3/11/2021 738
Well
PIEZ-01
PIEZ-02
PIEZ-03A
PJEZ-04
PIEZ-05
TWN-01
TWN-02
TWN-03
TWN-04
TWN-06
TWN-07
TWN-14
TWN-16
TWN-18
TWN-19
UR-05
DR-06
DR-07
DR-08
DR-09
DR-JO
DR-11
DR-12
DR-13
DR-14
DR-15
DR-17
DR-19
DR-20
DR-21
DR-22
DR-23
DR-24
Depth to
Water (ft.)
66.84
45.40
56.57
66.57
65.35
68.58
58.12
42.88
61.58
80.21
81.08
59.39
47.46
62.09
53.61
83.05
94.08
91.73
51.25
86.43
78.33
97.92
91.88
69.50
76.04
92.78
64.49
63.23
55.32
100.44
DRY
70.25
44.28
@ estimated dry area
TW442 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:,'55
504 perched monitoring well showing
ele.vation In feet amsl
TW4-12 0 5569 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 h d . . . .A.5568 temporary perc e nitrate monitoring
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5589 elevation In feet amsl
RUIN SPRING b 5380 seep or spring showing
elevation in feet amsl
·.~~r~ .,·,· \.
C ~~--~ NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11 , TW4-19, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells; TW4-1, TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
KRIGED 1st QUARTER, 2021 WATER LEVELS
WHITE MESA SITE
CHEM, INC. APPROVED DATE REFERENCE FIGURE
H :/718000/may21 /WL/Uwl0321 srf D-1
--,, ,,
II
@
TW4-42
9 5526
MW-38
-Q-5463
estimated chloroform capture zone boundary
stream tubes resulting from pumping. (note:
combined capture shown for MW-4, TW4-1,
TW4-2, TW4-4, TW4-11, TW4-40 and
TW4-41; and for MW-26, TW4-19, TW4-21,
TW4-37 and TW4-39)
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
combined capture shown for TW4-22,
TW4-24 and TW4-25)
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
TW440 temporary perched monitoring well
+5526 installed February, 2018 showing
elevation in feet amsl
M:';5
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 d . . . A.5568 temporary perc e nitrate monitoring
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5589 elevation in feet amsl
RUIN SPRING o 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells; TW4-1, TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM, INC.
KRIGED 1st QUARTER, 2021 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/may21 /WUUwl0321 cz2.srf D-2
--,, ,,
II
• TW4-42
¢5526
TW4-40
+5526
MW-25
e 5532
TW4-7
0 5539
PIEZ-2
'-5583
estimated chloroform capture zone boundary
i;tream tubes resulting from pumping. (note:
combined caplure shown for MW-4. TW4-1,
TW4-2, TW4-4, TW4-11, T\:\14-40 and
TW4-41; and for MW-26, TW4-19, TW4-21,
TW4-37 and TW4-39)
estimated nitrate capture zone boundary
stream tube resulting from pumping (note:
combined capture shown for TW4-22,
TW4-24 and TW4-25)
temporary perched monitoring well
installed April, 2019 showing
elevation in feet amsl
temporary perched monitoring well
installed February, 2018 showing
elevation in feet amsl
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well
showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
..
..-:. ----
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells; TW4-1, TW4-2 and TW4-11 water levels are below the base of the Burro Canyon Formation
HYDRO
GEO
KRIGED 1st QUARTER, 2021 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
detail ma CHEM, INC. APPROVED DATE REFERENCE FIGURE
H :/718000/may21 /WUUwl0321 cz.srf D-3
TabE
Kriged Previous Quarter Groundwater Contour Map
@ estimated dry area
TW"42 temporary perched monitoring well
¢ 5526 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
+5523 installed February, 2018 showing
elevation in feet amsl
M:';5
504 perched monitoring well showing
elevation in feet amsl
TW4-12 . . 0 5569 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 ched . . . A temporary per nitrate monitoring v 5568 well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
-i 5588 elevation in feet amsl
RUIN SPRING
<!, 5380 seep or spring showing
elevation in feet amsl
HYDRO
GEO
CHEM, INC.
KRIGED 4th QUARTER, 2020 WATER LEVELS
WHITE MESA SITE
AF>PROIIEO DATE REFERENCE FIGURE
H:/718000/feb21 /WUUwl1220.srf E-1
TabF
Depths to Groundwater and Elevations and Hydrographs of Groundwater Elevations over Time for
Chloroform Monitoring Wells
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD Well
5,620.77 5,622.33 1.56 123.6
5,527.63 09/25/79 94.70 93.14
5,527.63 10/10/79 94.70 93.14
5,528.43 01/10/80 93.90 92.34
5,529.93 03/20/80 92.40 90.84
5,528.03 06/17/80 94.30 92.74
5,528.03 09/15/80 94.30 92.74
5,527.93 10/08/80 94.40 92.84
5,527.93 02/12/81 94.40 92.84
5,525.93 09/01/84 96.40 94.84
5,528.33 12/01/84 94.00 92.44
5,528.13 02/01/85 94.20 92.64
5,528.33 06/01/85 94.00 92.44
5,528.93 09/01/85 93.40 91.84
5,528.93 10/01/85 93.40 91.84
5,528.93 11/01/85 93.40 91.84
5,528.83 12/01/85 93.50 91.94
5,512.33 03/01/86 110.00 108.44
5,528.91 06/19/86 93.42 91.86
5,528.83 09/01/86 93.50 91.94
5,529.16 12/01/86 93.17 91.61
5,526.66 02/20/87 95.67 94.11
5,529.16 04/28/87 93.17 91.61
5,529.08 08/14/87 93.25 91.69
5,529.00 11/20/87 93.33 91.77
5,528.75 01/26/88 93.58 92.02
5,528.91 06/01/88 93.42 91.86
5,528.25 08/23/88 94.08 92.52
5,529.00 11/02/88 93.33 91.77
5,528.33 03/09/89 94.00 92.44
5,529.10 06/21/89 93.23 91.67
5,529.06 09/01/89 93.27 91.71
5,529.21 11/15/89 93.12 91.56
5,529.22 02/16/90 93.11 91.55
5,529.43 05/08/90 92.90 91.34
5,529.40 08/07/90 92.93 91.37
5,529.53 11/13/90 92.80 91.24
5,529.86 02/27/91 92.47 90.91
5,529.91 05/21/91 92.42 90.86
5,529.77 08/27/91 92.56 91.00
5,529.79 12/03/91 92.54 90.98
5,530.13 03/17/92 92.20 90.64
5,529.85 06/11/92 92.48 90.92
5,529.90 09/13/92 92.43 90.87
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) 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) L D) (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
5,536.94 09/21/20 85.39 83.83
5,535.31 12/28/20 87.02 85.46
5,539.70 03/11/21 82.63 81.07
...... N 0
......
0 0
Depth Below Measuring Point (ft.)
00 0 °' 0 ~ N 0 0
09/25/79
02/06/81
06/21/82
11/03/83
03/17/85
07/30/86
12/12/87
04/25/89
09/07/90
01/20/92 ~
06/03/93 ~
.a;.
10/16/94 ~ 02/28/96 -('O
07/12/97 "1
~
11/24/98 ('O
"'C
04/07/00 ~
0
08/20/01 ~ ('O
"1
01/02/03 ~ ....
05/16/04 e ('O
09/28/05 ,-.._
?
02/10/07 'a' -06/24/08 e
"'C '-'
11/06/09
03/21/11
08/02/12
12/15/13
04/29/15
09/10/16
01/23/18
06/07/19
10/19/20
03/03/22
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) Monitorin~ (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,537.23 11/08/99 81.35 80.33
5,537.38 11/09/99 81.20 80.18
5,537.48 01/02/00 81.10 80.08
5,537.48 01/10/00 81.10 80.08
5,537.23 01/17/00 81.35 80.33
5,537.28 01/24/00 81.30 80.28
5,537.28 02/01/00 81.30 80.28
5,537.18 02/07/00 81.40 80.38
5,537.48 02/14/00 81.10 80.08
5,537.48 02/23/00 81.10 80.08
5,537.58 03/01/00 81.00 79.98
5,537.68 03/08/00 80.90 79.88
5,537.98 03/15/00 80.60 79.58
5,537.68 03/20/00 80.90 79.88
5,537.68 03/29/00 80.90 79.88
5,537.43 04/04/00 81.15 80.13
5,537.18 04/13/00 81.40 80.38
5,537.48 04/21/00 81.10 80.08
5,537.68 04/28/00 80.90 79.88
5,537.58 05/01/00 81.00 79.98
5,537.88 05/11/00 80.70 79.68
5,537.58 05/15/00 81.00 79.98
5,537.88 05/25/00 80.70 79.68
5,537.88 06/09/00 80.70 79.68
5,537.90 06/16/00 80.68 79.66
5,537.88 06/26/00 80.70 79.68
5,538.10 07/06/00 80.48 79.46
5,538.04 07/13/00 80.54 79.52
5,538.16 07/18/00 80.42 79.40
5,538.42 07/27/00 80.16 79.14
5,538.56 08/02/00 80.02 79.00
5,538.68 08/09/00 79.90 78.88
5,538.66 08/15/00 79.92 78.90
5,538.33 08/31/00 80.25 79.23
5,539.18 09/01/00 79.40 78.38
5,539.12 09/08/00 79.46 78.44
5,539.34 09/13/00 79.24 78.22
5,539.50 09/20/00 79.08 78.06
5,539.69 10/05/00 78.89 77.87
5,540.33 11/09/00 78.25 77.23
5,540.74 12/06/00 77.84 76.82
5,542.39 01/14/01 76.19 75.17
5,543.69 02/02/01 74.89 73.87
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,544.96 03/29/01 73.62 72.60
5,545.45 04/30/01 73.13 72.11
5,545.89 05/31/01 72.69 71.67
5,546.19 06/21/01 72.39 71.37
5,546.50 07/10/01 72.08 71.06
5,547.18 08/20/01 71.40 70.38
5,547.59 09/19/01 70.99 69.97
5,547.84 10/02/01 70.74 69.72
5,548.12 11/08/01 70.46 69.44
5,548.65 12/03/01 69.93 68.91
5,548.87 01/03/02 69.71 68.69
5,549.37 02/06/02 69.21 68.19
5,550.00 03/26/02 68.58 67.56
5,550.22 04/09/02 68.36 67.34
5,550.81 05/23/02 67.77 66.75
5,550.79 06/05/02 67.79 66.77
5,551.08 07/08/02 67.50 66.48
5,551.54 08/23/02 67.04 66.02
5,551.79 09/11/02 66.79 65.77
5,552.19 10/23/02 66.39 65.37
5,552.27 11/22/02 66.31 65.29
5,552.48 12/03/02 66.10 65.08
5,552.74 01/09/03 65.84 64.82
5,552.92 02/12/03 65.66 64.64
5,553.40 03/26/03 65.18 64.16
5,553.48 04/02/03 65.10 64.08
5,552.32 05/01/03 66.26 65.24
5,550.53 06/09/03 68.05 67.03
5,550.09 07/07/03 68.49 67.47
5,549.64 08/04/03 68.94 67.92
5,549.31 09/11/03 69.27 68.25
5,549.58 10/02/03 69.00 67.98
5,549.50 11/07/03 69.08 68.06
5,550.07 12/03/03 68.51 67.49
5,551.86 01/15/04 66.72 65.70
5,552.57 02/10/04 66.01 64.99
5,553.63 03/28/04 64.95 63.93
5,554.04 04/12/04 64.54 63.52
5,554.60 05/13/04 63.98 62.96
5,556.28 06/18/04 62.30 61.28
5,556.61 07/28/04 61.97 60.95
5,554.21 08/30/04 64.37 63.35
5,553.49 09/16/04 65 .09 64.07
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,552.53 10/11/04 66.05 65.03
5,552.42 11/16/04 66.16 65.14
5,552.46 12/22/04 66.12 65.10
5,552.07 01/18/05 66.51 65.49
5,552.21 02/28/05 66.37 65.35
5,552.26 03/15/05 66.32 65.30
5,552.30 04/26/05 66.28 65.26
5,552.25 05/24/05 66.33 65.31
5,552.22 06/30/05 66.36 65.34
5,552.15 07/29/05 66.43 65.41
5,552.47 09/12/05 66.11 65.09
5,552.50 12/07/05 66.08 65.06
5,552.96 03/08/06 65.62 64.60
5,553.23 06/14/06 65.35 64.33
5,557.20 07/18/06 61.38 60.36
5,553.32 11/07/06 65.26 64.24
5,554.35 02/27/07 64.23 63.21
5,554.07 05/02/07 64.51 63.49
5,554.07 08/14/07 64.51 63.49
5,553.88 10/10/07 64.70 63.68
5,555.73 03/26/08 62.85 61.83
5,556.60 06/24/08 61.98 60.96
5,556.83 08/26/08 61.75 60.73
5,556.87 10/14/08 61.71 60.69
5,556.90 03/10/09 61.68 60.66
5,556.91 06/24/09 61.67 60.65
5,556.61 09/10/09 61.97 60.95
5,556.78 12/11/09 61.8 60.78
5,556.75 03/11/10 61.83 60.81
5,556.19 05/11/10 62.39 61.37
5,555.26 09/29/10 63.32 62.30
5,554.66 12/21/10 63.92 62.90
5,554.74 02/28/11 63.84 62.82
5,554.57 06/21/11 64.01 62.99
5,554.13 09/20/11 64.45 63.43
5,554.54 12/21/11 64.04 63.02
5,553.64 03/27/12 64.94 63.92
5,553.66 06/28/12 64.92 63.90
5,553.73 09/27/12 64.85 63.83
5,553.59 12/28/12 64.99 63.97
5,554.73 03/28/13 63.85 62.83
5,554.44 06/27/13 64.14 63.12
5,554.37 09/27/13 64.21 63.19
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.30
5,553.92 12/20/13 64.66 63.64
5,553.20 03/27/14 65.38 64.36
5,552.20 06/25/14 66.38 65.36
5,551.13 09/25/14 67.45 66.43
5,550.72 12/17/14 67.86 66.84
5,546.50 03/26/15 72.08 71.06
5,544.18 06/22/15 74.40 73.38
5,535.85 09/30/15 82.73 81.71
5,529.54 12/02/15 89.04 88.02
5,527.55 03/30/16 91.03 90.01
5,525.92 06/30/16 92.66 91.64
5,524.48 09/29/16 94.10 93.08
5,533.15 12/21/16 85.43 84.41
5,527.92 03/30/17 90.66 89.64
5,534.48 06/27/17 84.10 83.08
5,524.98 09/28/17 93.60 92.58
5,525.88 11/30/17 92.70 91.68
5,526.18 03/28/18 92.40 91.38
5,515.78 06/22/18 102.80 101.78
5,510.83 09/24/18 107.75 106.73
5,542.47 12/17/18 76.11 75.09
5,531.82 03/25/19 86.76 85.74
5,539.90 06/24/19 78.68 77.66
5,538.56 08/12/19 80.02 79.00
5,510.85 11/18/19 107.73 106.71
5,513.12 02/10/20 105.46 104.44
5,512.44 05/04/20 106.14 105.12
5,517.82 09/21/20 100.76 99.74
5,520.38 12/28/20 98.20 97.18
5,513.47 03/11/21 105.11 104.09
,....
N 0
,.... ,....
0
Depth Below Measuring Point (ft.)
......
8 \0 0 00 0 -..J 0 ~ U'I 0
11/08/99
04/06/00
09/03/00
01/31/01
06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04
03/11/05
08/08/05
01/05/06 ~
06/04/06 ~ 11/01/06 ,&;;i..
03/31/07 I ~
08/28/07 ~ 01/25/08
06/23/08 -~
11/20/08 lo'1
04/19/09 ~ ~ 09/16/09 "'C
02/13/10 -=r" 07/13/10 0 12/10/10 < 05/09/11 ~ lo'1 10/06/11 ~ 03/04/12 ....
08/01/12 = 12/29/12 ~ --05/28/13 ?
10/25/13 O"" 03/24/14 -= 08/21/14 "'C 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
01/11/22
06/10/22
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,548.57 11/08/99 76.15 74.53
5,548.57 11/09/99 76 .15 74.53
5,548.32 01/02/00 76.40 74.78
5,548.52 01/10/00 76.20 74.58
5,548.32 01/17/00 76.40 74.78
5,548.72 01/24/00 76.00 74.38
5,548.62 02/01/00 76.10 74.48
5,548.62 02/07/00 76.10 74.48
5,549.02 02/14/00 75.70 74.08
5,549.12 02/23/00 75.60 73.98
5,549.22 03/01/00 75.50 73.88
5,549.32 03/08/00 75.40 73.78
5,549.22 03/15/00 75.50 73.88
5,549.92 03/20/00 74.80 73.18
5,549.72 03/29/00 75.00 73.38
5,549.42 04/04/00 75.30 73.68
5,549.52 04/13/00 75 .20 73.58
5,549.72 04/21/00 75.00 73.38
5,549.82 04/28/00 74.90 73.28
5,549.82 05/01/00 74.90 73.28
5,550.12 05/11/00 74.60 72.98
5,549.82 05/15/00 74.90 73.28
5,550.12 05/25/00 74.60 72.98
5,550.12 06/09/00 74.60 72.98
5,550.22 06/16/00 74.50 72.88
5,550.07 06/26/00 74.65 73.03
5,550.17 07/06/00 74.55 72.93
5,550.17 07/13/00 74.55 72.93
5,550.18 07/18/00 74.54 72.92
5,550.33 07/27/00 74.39 72.77
5,550.38 08/02/00 74.34 72.72
5,550.40 08/09/00 74.32 72.70
5,550.42 08/15/00 74.30 72.68
5,550.54 08/31/00 74.18 72.56
5,550.87 09/08/00 73.85 72.23
5,550.97 09/13/00 73.75 72.13
5,551.04 09/20/00 73.68 72.06
5,545.83 10/05/00 78.89 77.27
5,546.47 11/09/00 78.25 76.63
5,546.88 12/06/00 77.84 76.22
5,552.18 01/26/01 72.54 70.92
5,552.20 02/02/01 72.52 70.90
5,551.10 03/29/01 73.62 72.00
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,551.59 04/30/01 73.13 71.51
5,552.03 05/31/01 72.69 71.07
5,552.33 06/21/01 72.39 70.77
5,552.64 07/10/01 72.08 70.46
5,553.32 08/20/01 71.40 69.78
5,553.73 09/19/01 70.99 69.37
5,553.98 10/02/01 70.74 69.12
5,554.14 11/08/01 70.58 68.96
5,554.79 12/03/01 69.93 68.31
5,554.74 01/03/02 69.98 68.36
5,554.91 02/06/02 69.81 68.19
5,555.15 03/26/02 69.57 67 .95
5,555.39 04/09/02 69.33 67.71
5,555.73 05/23/02 68.99 67.37
5,555.79 06/05/02 68.93 67.31
5,555.91 07/08/02 68.81 67.19
5,556.04 08/23/02 68.68 67.06
5,556.25 09/11/02 68.47 66.85
5,556.72 10/23/02 68.00 66.38
5,556.42 11/22/02 68.30 66.68
5,557.01 12/03/02 67.71 66.09
5,557.20 01/09/03 67.52 65.90
5,557.35 02/12/03 67.37 65.75
5,557.83 03/26/03 66.89 65.27
5,557.87 04/02/03 66.85 65.23
5,553.71 05/01/03 71.01 69.39
5,548.98 06/09/03 75.74 74.12
5,548.14 07/07/03 76.58 74.96
5,547.75 08/04/03 76.97 75.35
5,547.22 09/11/03 77.50 75.88
5,547.68 10/02/03 77.04 75.42
5,547.52 11/07/03 77.20 75.58
5,548.29 12/03/03 76.43 74.81
5,554.00 01/15/04 70.72 69.10
5,555.46 02/10/04 69.26 67.64
5,556.90 03/28/04 67.82 66.20
5,557.49 04/12/04 67.23 65.61
5,558.07 05/13/04 66.65 65.03
5,558.19 06/18/04 66.53 64.91
5,559.00 07/28/04 65.72 64.10
5,554.26 08/30/04 70.46 68.84
5,551.97 09/16/04 72.75 71.13
5,549.65 10/11/04 75.07 73.45
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,549.89 11/16/04 74.83 73.21
5,550.37 12/22/04 74.35 72.73
5,549.95 01/18/05 74.77 73.15
5,550.09 02/28/05 74.63 73.01
5,550.13 03/15/05 74.59 72.97
5,550.18 04/26/05 74.54 72.92
5,550.32 05/24/05 74.40 72.78
5,550.21 06/30/05 74.51 72.89
5,550.11 07/29/05 74.61 72.99
5,550.33 09/12/05 74.39 72.77
5,550.29 12/07/05 74.43 72.81
5,551.30 03/08/06 73.42 71.80
5,551.42 06/14/06 73.30 71.68
5,550.52 07/18/06 74.20 72.58
5550.52 11/07/06 74.20 72.58
5552.89 02/27/07 71.83 70.21
5,552.06 05/02/07 72.66 71.04
5,552.02 08/14/07 72.70 71.08
5,552.20 10/10/07 72.52 70.90
5,554.58 03/26/08 70.14 68.52
5,555.23 06/24/08 69.49 67.87
5,555.29 08/26/08 69.43 67.81
5,555.43 10/14/08 69.29 67.67
5,555.73 03/10/09 68.99 67.37
5,556.25 06/24/09 68.47 66.85
5,555.94 09/10/09 68.78 67.16
5,556.53 12/11/09 68.19 66.57
5,557.87 03/11/10 66.85 65.23
5,557.63 05/11/10 67.09 65.47
5,557.24 09/29/10 67.48 65.86
5,557.00 12/21/10 67.72 66.10
5,557.61 02/28/11 67.11 65.49
5,557.58 06/21/11 67.14 65.52
5,557.46 09/20/11 67.26 65.64
5,557.84 12/21/11 66.88 65.26
5,557.86 03/27/12 66.86 65.24
5,557.87 06/28/12 66.85 65.23
5,557.46 09/27/12 67.26 65.64
5,557.82 12/28/12 66.90 65.28
5,559.39 03/28/13 65.33 63.71
5,559.21 06/27/13 65.51 63.89
5,559.26 09/27/13 65.46 63.84
5,559.27 12/20/13 65.45 63.83
Water Levels and Data over Time
White Mesa Mill -Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 120.900
5,558.92 03/27/14 65.80 64.18
5,557.99 06/25/14 66.73 65.11
5,557.09 09/25/14 67.63 66.01
5,557.07 12/17/14 67.65 66.03
5,549.93 03/26/15 74.79 73.17
5,551.30 06/22/15 73.42 71.80
5,547.12 09/30/15 77.60 75.98
5,538.34 12/02/15 86.38 84.76
5,542.22 03/30/16 82.50 80.88
5,538.31 06/30/16 86.41 84.79
5,536.70 09/29/16 88.02 86.40
5,540.40 12/21/16 84.32 82.70
5,536.61 03/30/17 88.11 86.49
5,547.16 06/27/17 77.56 75.94
5,522.65 09/28/17 102.07 100.45
5,532.64 11/30/17 92.08 90.46
5,506.94 03/28/18 117.78 116.16
5,521.60 06/22/18 103.12 101.50
5,510.01 09/24/18 114.71 113.09
5,543.01 12/17/18 81.71 80.09
5,522.70 03/25/19 102.02 100.40
5,522.49 06/24/19 102.23 100.61
5,522.29 08/12/19 102.43 100.81
5,515.62 11/18/19 109.10 107.48
5,516.60 02/10/20 108.12 106.5
5,514.51 05/04/20 110.21 108.59
5,522.29 09/21/20 102.43 100.81
5,521.08 12/28/20 103.64 102.02
5,513.42 03/11/21 111.30 109.68
-w 0 -~ --0
Depth Below Measuring Point (ft.) -8 '° 0 00 0 --.l 0 0\ 0
V,
0
11/08/99
04/06/00
09/03/00
01/31/01
06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04
03/11/05
08/08/05
01/05/06 ~
06/04/06 ~ 11/01/06 ,a;..
03/31/07 I N
08/28/07 ~ 01/25/08
06/23/08 -~
11/20/08 l"1
04/19/09 ~ ~ 09/16/09 "Cl
02/13/10 -t:r" 07/13/10 0 12/10/10 < 05/09/11 ~ l"1 10/06/11 ~ 03/04/12 ...
08/01/12 9
12/29/12 ~ -05/28/13 ?
10/25/13 a" 03/24/14 -9 08/21/14 "Cl 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
01/11/22
06/10/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,565.78 11/29/99 66.45 65.43
5,566.93 01/02/00 65.30 64.28
5,567.03 01/10/00 65.20 64.18
5,566.83 01/17/00 65.40 64.38
5,567.13 01/24/00 65.10 64.08
5,567.33 02/01/00 64.90 63.88
5,567.13 02/07/00 65.10 64.08
5,567.43 02/14/00 64.80 63.78
5,567.63 02/23/00 64.60 63.58
5,567.73 03/01/00 64.50 63.48
5,567.83 03/08/00 64.40 63.38
5,567.70 03/15/00 64.53 63.51
5,568.03 03/20/00 64.20 63.18
5,567.93 03/29/00 64.30 63.28
5,567.63 04/04/00 64.60 63.58
5,567.83 04/13/00 64.40 63.38
5,568.03 04/21/00 64.20 63.18
5,568.23 04/28/00 64.00 62.98
5,568.13 05/01/00 64.10 63.08
5,568.53 05/11/00 63.70 62.68
5,568.23 05115/00 64.00 62.98
5,568.53 05/25/00 63.70 62.68
5,568.61 06/09/00 63.62 62.60
5,568.69 06/16/00 63.54 62.52
5,568.45 06/26/00 63.78 62.76
5,568.61 07/06/00 63.62 62.60
5,568.61 07/06/00 63.62 62.60
5,568.49 07/13/00 63.74 62.72
5,568.55 07/18/00 63.68 62.66
5,568.65 07/27/00 63.58 62.56
5,568.73 08/02/00 63.50 62.48
5,568.77 08/09/00 63.46 62.44
5,568.76 08/16/00 63.47 62.45
5,568.95 08/31/00 63.28 62.26
5,568.49 09/08/00 63.74 62.72
5,568.67 09/13/00 63.56 62.54
5,568.96 09/20/00 63.27 62.25
5,568.93 10/05/00 63.30 62.28
5,569.34 11/09/00 62.89 61.87
5,568.79 12/06/00 63.44 62.42
5,569.11 01/03/01 63.12 62.10
5,569.75 02/09/01 62.48 61.46
5,570.34 03/28/01 61.89 60.87
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,570.61 04/30/01 61.62 60.60
5,570.70 05/31/01 61.53 60.51
5,570.88 06/21/01 61.35 60.33
5,571.02 07/10/01 61.21 60.19
5,571.70 08/20/01 60.53 59.51
5,572.12 09/19/01 60.11 59.09
5,572.08 10/02/01 60.15 59.13
5,572.78 11/08/01 59.45 58.43
5,573.27 12/03/01 58.96 57.94
5,573.47 01/03/02 58.76 57.74
5,573.93 02/06/02 58.30 57.28
5,574.75 03/26/02 57.48 56.46
5,574.26 04/09/02 57.97 56.95
5,575.39 05/23/02 56.84 55.82
5,574.84 06/05/02 57.39 56.37
5,575.33 07/08/02 56.90 55.88
5,575.79 08/23/02 56.44 55.42
5,576.08 09/11/02 56.15 55.13
5,576.30 10/23/02 55.93 54.91
5,576.35 11/22/02 55.88 54.86
5,576.54 12/03/02 55.69 54.67
5,576.96 01/09/03 55.27 54.25
5,577.11 02/12/03 55.12 54.10
5,577.61 03/26/03 54.62 53.60
5,572.80 04/02/03 59.43 58.41
5,577.89 05/01/03 54.34 53.32
5,577.91 06/09/03 54.32 53.30
5,577.53 07/07/03 54.70 53.68
5,577.50 08/04/03 54.73 53.71
5,577.71 09/11/03 54.52 53.50
5,577.31 10/02/03 54.92 53.90
5,577.33 11/07/03 54.90 53.88
5,577.34 12/03/03 54.89 53.87
5,578.24 01/15/04 53.99 52.97
5,578.38 02/10/04 53.85 52.83
5,578.69 03/28/04 53.54 52.52
5,579.15 04/12/04 53.08 52.06
5,579.47 05/13/04 52.76 51.74
5,579.53 06/18/04 52.70 51.68
5,580.17 07/28/04 52.06 51.04
5,580.20 08/30/04 52.03 51.01
5,580.26 09/16/04 51.97 50.95
5,580.12 10/11/04 52.11 51.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (L D) (MP) Riser (L Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,579.93 11/16/04 52.30 51.28
5,580.07 12/22/04 52.16 51.14
5,579.80 01/18/05 52.43 51.41
5,580.35 02/28/05 51.88 50.86
5,580.57 03/15/05 51.66 50.64
5,580.86 04/26/05 51.37 50.35
5,581.20 05/24/05 51.03 50.01
5,581.51 06/30/05 50.72 49.70
5,581.55 07/29/05 50.68 49.66
5,581.68 09/12/05 50.55 49.53
5,581.83 12/07/05 50.40 49.38
5,564.92 03/08/06 67.31 66.29
5,582.73 06/13/06 49.50 48.48
5,582.33 07/18/06 49.90 48.88
5,582.75 11/07/06 49.48 48.46
5583.35 02/27/07 48.88 47.86
5,559.57 05/02/07 72.66 71.64
5,583.29 08/14/07 48.94 47.92
5,583.49 10/10/07 48.74 47.72
5,584.95 03/26/08 47.28 46.26
5,584.59 06/24/08 47.64 46.62
5,584.55 08/26/08 47.68 46.66
5,584.03 10/14/08 48.20 47.18
5,583.64 03/03/09 48.59 47.57
5,587.34 06/24/09 44.89 43.87
5,582.90 09/10/09 49.33 48.31
5,583.27 12/11/09 48.96 47.94
5,583.63 03/11/10 48.60 47.58
5,583.82 05/11/10 48.41 47.39
5,583.51 09/29/10 48.72 47.70
5,582.86 12/21/10 49.37 48.35
5,582.60 02/28/11 49.63 48.61
5,590.00 06/21/11 42.23 41.21
5,582.70 09/20/11 49.53 48.51
5,583.05 12/21/11 49.18 48.16
5,581.93 03/27/12 50.30 49.28
5,582.03 06/28/12 50.20 49.18
5,582.08 09/27/12 50.15 49.13
5,581.94 12/28/12 50.29 49.27
5,581.52 03/28/13 50.71 49.69
5,580.88 06/27/13 51.35 50.33
5,580.58 09/27/13 51.65 50.63
5,580.38 12/20/13 51.85 50.83
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 140.30
5,579.62 03/27/14 52.61 51.59
5,578.52 06/25/14 53.71 52.69
5,577.59 09/25/14 54.64 53.62
5,577.40 12/17/14 54.83 53.81
5,576.73 03/26/15 55.50 54.48
5,576.62 06/22/15 55.61 54.59
5,576.16 09/30/15 56.07 55 .05
5,575.57 12/02/15 56.66 55.64
5,575.62 03/30/16 56.61 55.59
5,574.89 06/30/16 57.34 56.32
5,574.37 09/29/16 57.86 56.84
5,574.23 12/21/16 58.00 56.98
5,574.23 03/30/17 58.00 56.98
5,573.72 06/27/17 58.51 57.49
5,573.28 09/28/17 58.95 57.93
5,572.66 11/30/17 59.57 58.55
5,572.19 03/28/18 60.04 59.02
5,571.83 06/22/18 60.40 59.38
5,571.34 09/25/18 60.89 59.87
5,570.99 12/17/18 61.24 60.22
5,570.21 03/25/19 62.02 61.00
5,570.28 06/24/19 61.95 60.93
5,570.04 08/12/19 62.19 61.17
5,569.68 11/18/19 62.55 61.53
5,569.35 02/10/20 62.88 61.86
5,568.92 05/04/20 63.31 62.29
5,568.38 09/22/20 63.85 62.83
5,568.28 12/30/20 63.95 62.93
5,568.31 03/11/21 63.92 62.90
-..J
V,
-..J 0
Depth Below Measuring Point (ft.)
°' V, ~ V,
V,
V,
0 ~ V, ~ 0
~---t---.~---t-----t------;----1----;-11/29/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04
11/02/04
04/01/05
08/29/05
01/26/06
06/25/06
11/22/06
04/21/07
09/18/07
02/15/08
07/14/08
12/11/08
05/10/09
10/07/09
03/06/10
08/03/10
12/31/10
05/30/11
10/27/11
03/25/12
08/22/12
01/19/13
06/18/13
11/15/13
04/14/14
09/11/14
02/08/15
07/08/15
12/05/15
05/03/16
09/30/16
02/27/17
07/27/17
12/24/17
05/23/18
10/20/18
03/19/19
08/16/19
01/13/20
06/11/20
11/08/20
04/07/21
09/04/21
02/01/22 ..__ __ _._ __ ___.__ __ __J.._ __ _,__ __ ___.__ __ __J.__ __ --L 07/01/22
~ ~ I ~
~ ""'" ~ ~
i:,
~ "'O ~
0 < ~ ~
~ .... a ~ -?
r::r -a "'O --
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.L D) 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 11/16/04 68.96 67.78
5,544.63 12/22/04 68.86 67.68
5,544.31 01/18/05 69.18 68.00
5,544.59 02/28/05 68.90 67.72
5,544.69 03/15/05 68.80 67.62
5,544.68 04/26/05 68.81 67.63
5,544.79 05/24/05 68.70 67.52
5,544.80 06/30/05 68.69 67.51
5,544.78 07/29/05 68.71 67.53
5,545.01 09/12/05 68.48 67.30
5,545.23 12/07/05 68.26 67.08
5,545.74 03/08/06 67.75 66.57
5,545.79 06/14/06 67.70 66.52
5,545.86 07/18/06 67.63 66.45
5,545.81 11/07/06 67.68 66.50
5,546.68 02/27/07 66.81 65.63
5,546.54 05/02/07 66.95 65.77
5,547.16 08/15/07 66.33 65.15
5,547.22 10/10/07 66.27 65.09
5,548.31 03/26/08 65.18 64.00
5,548.87 06/24/08 64.62 63.44
5,549.24 08/26/08 64.25 63.07
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,612.301 5,613.485 J.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
5,539.39 09/21/20 74.10 72.92
5,536.54 12/28/20 76.95 75.77
5,533.98 03/11/21 79.51 78.33
---0 0 0
Depth Below Measuring Point (ft.)
'° 0 00 0 -.J 0 O'I 0 UI 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 1-3 07/23/06 ~ 12/20/06 ,I;;;,,. 05/19/07 I ,I;;;,,. 10/16/07 ~ 03/14/08
08/11/08 -01/08/09 ~ "1
06/07/09 ~
11/04/09 ~ "'O 04/03/10 -08/31/10 =r"
01/28/11 0 < 06/27/11 ~
11/24/11 "1
04/22/12 1-3 ...
09/19/12 e
02/16/13 ~ --07/16/13 ? 12/13/13 O" 05/12/14 -10/09/14 e
03/08/15 "'O --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
10/02/21
03/01/22
07/29/22
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
5,579.30 01/02/00 61.40 59.45
5,579.60 01/10/00 61.lO 59.15
5,579.35 01/17/00 61.35 59.40
5,579.60 01/24/00 61.10 59.15
5,579.50 02/01/00 61.20 59.25
5,579.50 02/07/00 61.20 59.25
5,579.90 02/14/00 60.80 58.85
5,579.90 02/23/00 60.80 58.85
5,580.20 03/01/00 60.50 58.55
5,580.00 03/08/00 60.70 58.75
5,580.04 03/15/00 60.66 58.71
5,580.70 03/20/00 60.00 58.05
5,580.30 03/29/00 60.40 58.45
5,580.00 04/04/00 60.70 58.75
5,580.20 04/13/00 60.50 58.55
5,580.40 04/21/00 60.30 58.35
5,580.50 04/28/00 60.20 58.25
5,580.50 05/01/00 60.20 58.25
5,580.90 05/11/00 59.80 57.85
5,580.50 05/15/00 60.20 58.25
5,580.75 05/25/00 59.95 58.00
5,580.80 06/09/00 59.90 57.95
5,580.92 06/16/00 59.78 57.83
5,580.80 06/26/00 59.90 57.95
5,580.90 07/06/00 59.80 57.85
5,581.05 07/13/00 59.65 57.70
5,580.90 07/18/00 59.80 57.85
5,581.05 07/27/00 59.65 57.70
5,581.06 08/02/00 59.64 57.69
5,581.08 08/09/00 59.62 57.67
5,581.07 08/16/00 59.63 57.68
5,581.25 08/31/00 59.45 57.50
5,581.32 09/08/00 59.38 57.43
5,581.34 09/13/00 59.36 57.41
5,581.41 09/20/00 59.29 57.34
5,581.37 10/05/00 59.33 57.38
5,581.66 11/09/00 59.04 57.09
5,581.63 12/06/00 59.07 57.12
5,581.92 01/03/01 58.78 56.83
5,582.20 02/09/01 58.50 56.55
5,582.54 03/28/01 58.16 56.21
5,582.72 04/30/01 57.98 56.03
5,582.72 05/31/01 57.98 56.03
5,582.81 06/22/01 57.89 55.94
5,582.92 07/10/01 57.78 55 .83
5,583.17 08/20/01 57.53 55.58
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 12 1.85
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 (bhv.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 121.85
5,586.03 07/29/05 54.67 52.72
5,586.05 09/12/05 54.65 52.70
5,585.80 12/07/05 54.90 52.95
5,587.06 03/08/06 53.64 51.69
5,585.90 06/13/06 54.80 52.85
5,585.32 07/18/06 55.38 53.43
5,585.35 11/07/06 55.35 53.40
5585.81 02/27/07 54.89 52.94
5,585.20 05/02/07 55.50 53.55
5,586.66 08/14/07 54.04 52.09
5,586.80 10/10/07 53.90 51.95
5,588.48 03/26/08 52.22 50.27
5,586.51 06/24/08 54.19 52.24
5,586.45 08/26/08 54.25 52.30
5,585.40 10/14/08 55.30 53.35
5,584.80 03/03/09 55.90 53.95
5,584.73 06/24/09 55 .97 54.02
5,584.36 09/10/09 56.34 54.39
5,585.02 12/11/09 55.68 53.73
5,585.66 03/11/10 55.04 53.09
5,584.86 05/11/10 55.84 53.89
5,584.55 09/29/10 56.15 54.20
5,584.17 12/21/10 56.53 54.58
5,583.55 02/28/11 57.15 55.20
5,584.72 06/21/11 55.98 54.03
5,584.62 09/20/11 56.08 54.13
5,585.04 11/21/11 55.66 53.71
5,583.89 03/27/12 56.81 54.86
5,583.92 06/28/12 56.78 54.83
5,583.89 09/27/12 56.81 54.86
5,583.89 12/28/12 56.81 54.86
5,582.88 03/28/13 57.82 55.87
5,582.05 06/27/13 58.65 56.70
5,581.35 09/27/13 59.35 57.40
5,580.52 12/20/13 60.18 58.23
5,579.44 03/27/14 61.26 59.31
5,578.11 06/25/14 62.59 60.64
5,577.15 09/25/14 63.55 61.60
5,577.44 12/17/14 63.26 61.31
5,577.37 03/26/15 63.33 61.38
5,577.46 06/22/15 63.24 61.29
5,576.92 09/30/15 63.78 61.83
5,576.33 12/02/15 64.37 62.42
5,576.30 03/30/16 64.40 62.45
5,575.72 06/30/16 64.98 63.03
5,575.12 09/29/16 65.58 63.63
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 121. 5
5,574.77 12/21/16 65.93 63.98
5,575.03 03/30/17 65.67 63.72
5,574.55 06/27/17 66.15 64.20
5,574.09 09/28/17 66.61 64.66
5,573.48 11/30/17 67.22 65.27
5,573.05 03/28/18 67.65 65.70
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
5,569.36 09/22/20 71.34 69.39
5,569.17 12/30/20 71.53 69.58
5,569.24 03/11/21 71.46 69.51
-.J Vl -.J 0
Depth Below Measuring Point (ft.)
°' Vl ~ Vl Vl Vl 0
t-------t------;-------~r-------t------;-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
10/08/21
03/07/22
'----------'-------'------'----------'------'-08/04/22
~ ~ I {I)
~ ;-
"'1 e:,
~ "'Cl g.
0 < ~ "'1
~ .... a ~ ,,-...
?
"a' §"
"'Cl '-"
Water Levels and Data over Time
White Mesa Mill -Well TW 4-6
Total or
Measuring Measured Total Total
Water Land Point Depth to Depth to Depth Of
Elevation Surface Elevation Length Of Date Of Water Water Well
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,607.33 5,608.78 1.450 99.60
5,522.28 05/25/00 86.50 85.05
5,521.5] 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
5,530.36 09/22/20 78.42 76.97
5,530.29 12/30/20 78.49 77.04
5,530.20 03/11/21 78.58 77.13
\0 0 00 00 VI 0
Depth Below Measuring Point (ft.)
-.J -..J 0\ 0\ VI VI 0 VI 0 VI VI 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 ~
05/19/07 ,I;..
I
.. 10/16/07 0'-1
03/14/08 ~ 08/11/08 """ 01/08/09 ~ ""1 06/07/09 ~ .. 11/04/09 ~
04/03/10 ~ """ 08/31/10 =r"
01/28/11 0
06/27/11 < ~
11/24/11 ""1
04/22/12 ~ ...
09/19/12 9
02/16/13 ~
07/16/13 --~
12/13/13 .
05/12/14 O"" -10/09/14 9
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
10/02/21
03/01/22
07/29/22
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,552.37 11/29/99 68.70 67.50
5,553.57 01/02/00 67.50 66.30
5,553.87 01/10/00 67.20 66.00
5,553.72 01/17/00 67.35 66.15
5,553.97 01/24/00 67.10 65.90
5,553.87 02/01/00 67.20 66.00
5,553.87 02/07/00 67.20 66.00
5,554.17 02/14/00 66.90 65.70
5,554.27 02/23/00 66.80 65.60
5,554.37 03/01/00 66.70 65.50
5,554.37 03/08/00 66.70 65.50
5,554.27 03/15/00 66.80 65.60
5,554.77 03/20/00 66.30 65.10
5,554.57 03/29/00 66.50 65.30
5,554.27 04/04/00 66.80 65.60
5,554.57 04/13/00 66.50 65.30
5,554.77 04/21/00 66.30 65.10
5,554.87 04/28/00 66.20 65.00
5,554.87 05/01/00 66.20 65.00
5,555.27 05/11/00 65.80 64.60
5,554.97 05/15/00 66.10 64.90
5,555.27 05/25/00 65.80 64.60
5,555.33 06/09/00 65.74 64.54
5,555.45 06/16/00 65.62 64.42
5,555.22 06/26/00 65.85 64.65
5,555.45 07/06/00 65.62 64.42
5,555.40 07/13/00 65.67 64.47
5,555.45 07/18/00 65.62 64.42
5,555.59 07/27/00 65.48 64.28
5,555.65 08/02/00 65.42 64.22
5,555.70 08/09/00 65.37 64.17
5,555.74 08/16/00 65.33 64.13
5,555.96 08/31/00 65.11 63.91
5,555.87 09/08/00 65.20 64.00
5,555.95 09/13/00 65.12 63.92
5,556.05 09/20/00 65.02 63.82
5,556.06 10/05/00 65.01 63.81
5,556.17 10/12/00 64.90 63.70
5,556.20 10/19/00 64.87 63.67
5,556.22 10/23/00 64.85 63.65
5,556.36 11/09/00 64.71 63.51
5,556.42 11/14/00 64.65 63.45
5,556.45 11/30/00 64.62 63.42
5,556.15 12/06/00 64.92 63.72
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 121.0
5,556.89 01/14/01 64.18 62.98
5,557.07 02/09/01 64.00 62.80
5,557.62 03/29/01 63.45 62.25
5,557.51 04/30/01 63.56 62.36
5,557.77 05/31/01 63.30 62.10
5,557.84 06/21/01 63.23 62.03
5,557.98 07/10/01 63.09 61.89
5,558.33 08/20/01 62.74 61.54
5,558.57 09/19/01 62.50 61.30
5,558.53 10/02/01 62.54 61.34
5,558.62 11/08/01 62.45 61.25
5,559.03 12/03/01 62.04 60.84
5,559.08 01/03/02 61.99 60.79
5,559.32 02/06/02 61.75 60.55
5,559.63 03/26/02 61.44 60.24
5,559.55 04/09/02 61.52 60.32
5,560.06 05/23/02 61.01 59.81
5,559.91 06/05/02 61.16 59.96
5,560.09 07/08/02 60.98 59.78
5,560.01 08/23/02 61.06 59.86
5,560.23 09/11/02 60.84 59.64
5,560.43 10/23/02 60.64 59.44
5,560.39 11/22/02 60.68 59.48
5,560.61 12/03/02 60.46 59.26
5,560.89 01/09/03 60.18 58.98
5,560.94 02/12/03 60.13 58.93
5,561.28 03/26/03 59.79 58.59
5,561.35 04/02/03 59.72 58.52
5,546.20 05/01/03 74.87 73.67
5,539.47 06/09/03 81.60 80.40
5,541.87 07/07/03 79.20 78.00
5,542.12 08/04/03 78.95 77.75
5,541.91 09/11/03 79.16 77.96
5,544.62 10/02/03 76.45 75.25
5,542.67 11/07/03 78.40 77.20
5,549.96 12/03/03 71.11 69.91
5,557.17 01/15/04 63.90 62.70
5,558.65 02/10/04 62.42 61.22
5,559.90 03/28/04 61.17 59.97
5,560.36 04/12/04 60.71 59.51
5,560.87 05/13/04 60.20 59.00
5,560.95 06/18/04 60.12 58.92
5,561.64 07/28/04 59.43 58.23
5,543.00 08/30/04 78.07 76.87
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5 621.07 1.20 121 .0
5,541.91 09/16/04 79.16 77.96
5,540.08 10/11/04 80.99 79.79
5,546.92 11/16/04 74.15 72.95
5,546.97 12/22/04 74.10 72.90
5,546.51 01/18/05 74.56 73.36
5,546.66 02/28/05 74.41 73.21
5,546.81 03/15/05 74.26 73.06
5,548.19 04/26/05 72.88 71.68
5,547.11 05/24/05 73.96 72.76
5,546.98 06/30/05 74.09 72.89
5,546.92 07/29/05 74.15 72.95
5,547.26 09/12/05 73.81 72.61
5,547.26 12/07/05 73.81 72.61
5,548.86 03/08/06 72.21 71.01
5,548.62 06/13/06 72.45 71.25
5,550.04 07/18/06 71.03 69.83
5,548.32 11/07/06 72.75 71.55
5,550.44 02/27/07 70.63 69.43
5,549.69 05/02/07 71.38 70.18
5,549.97 08/14/07 71.10 69.90
5,550.30 10/10/07 70.77 69.57
5,551.92 03/26/08 69.15 67.95
5,552.94 06/24/08 68.13 66.93
5,552.34 08/26/08 68.73 67.53
5,552.61 10/14/08 68.46 67.26
5,552.81 03/10/09 68.26 67.06
5,553.11 06/24/09 67.96 66.76
5,552.55 09/10/09 68.52 67.32
5,553.06 12/11/09 68.01 66.81
5,554.64 03/11/10 66.43 65.23
5,554.20 05/11/10 66.87 65.67
5,553.45 09/29/10 67.62 66.42
5,553.40 12/21/10 67.67 66.47
5,553.93 02/28/11 67.14 65.94
5,553.67 06/21/11 67.4 66.20
5,553.46 09/20/11 67.61 66.41
5,553.78 12/21/11 67.29 66.09
5,553.17 03/27/12 67.90 66.70
5,553.21 06/28/12 67.86 66.66
5,552.90 09/27/12 68.17 66.97
5,553.15 12/28/12 67.92 66.72
5,556.23 03/28/13 64.84 63.64
5,556.04 06/27/13 65.03 63.83
5,556.09 09/27/13 64.98 63.78
Water Levels and Data over Time
White Mesa Mill -Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5 619.87 5 621.07 1.20 121.0
5,555.80 12/20/13 65.27 64.07
5,555.40 03/27/14 65.67 64.47
5,554.20 06/25/14 66.87 65.67
5,552.96 09/25/14 68.11 66.91
5,552.62 12/17/14 68.45 67.25
5,548.57 03/26/15 72.50 71.30
5,555.88 06/22/15 65.19 63.99
5,546.22 09/30/15 74.85 73.65
5,539.47 12/02/15 81.60 80.40
5,545.08 03/30/16 75.99 74.79
5,544.62 06/30/16 76.45 75.25
5,544.61 09/29/16 76.46 75.26
5,544.09 12/21/16 76.98 75.78
5,546.07 03/30/17 75.00 73.80
5,549.36 06/27/17 71.71 70.51
5,541.91 09/28/17 79.16 77.96
5,540.51 11/30/17 80.56 79.36
5,540.71 03/28/18 80.36 79.16
5,540.12 06/22/18 80.95 79.75
5,540.17 09/25/18 80.90 79.70
5,538.26 12/17/18 82.81 81.61
5,538.81 03/25/19 82.26 81.06
5,539.11 06/24/19 81.96 80.76
5,539.75 08/12/19 81.32 80.12
5,539.13 11/18/19 81.94 80.74
5,538.03 02/10/20 83.04 81.84
5,538.29 05/04/20 82.78 81.58
5,540.28 09/22/20 80.79 79.59
5,539.17 12/30/20 81.90 80.70
5,539.03 03/11/21 82.04 80.84
00 Ul 00 0
Depth Below Measuring Point (ft.)
-l Ul -l 0 0\ Ul 0\ 0
Ul
Ul
U\
0
11/29/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04
11/02/04
04/01/05
08/29/05
01/26/06 ~
06/25/06 ~ 11/22/06 ,&;...
04/21/07 I .....:a
09/18/07 ~ 02/15/08
07/14/08 """ ~
12/11/08 ""1
05/10/09 ~
10/07/09 ~ "O
03/06/10 """ =-08/03/10 0 12/31/10 < 05/30/11 ~ ""1 10/27/11 ~ 03/25/12 ....
08/22/12 e
01/19/13 ~ -06/18/13 ? 11/15/13 C"' 04/14/14 -09/11/14 e "O 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
02/01/22
07/01/22
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 l l/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
5,535.49 09/22/20 85.91 81.31
5,534.69 12/30/20 86.71 82.11
5,534.92 03/11/21 86.48 81.88
-8 \0 0 00 0
Depth Below Measuring Point (ft.)
-.J 0 °°' 0 Vl 0
.j:::..
0
t,.l
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 1-3
06/25/06 ! 11/22/06
04/21/07 I 00
09/18/07 ~ 02/15/08
07/14/08 -~
12/11/08 .,
05/10/09 ~
10/07/09 ~ "'C
03/06/10 -=-08/03/10 0 12/31/10 -< 05/30/11 ~ .,
10/27/11 1-3 03/25/12 -· 08/22/12 a ~ 01/19/13 -06/18/13 ?
11/15/13 O"' 04/14/14 -a 09/11/14 "'C 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
02/01/22
07/01/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.1
5,577.09 12/20/99 60.50 59.02
5,577.09 01/02/00 60.50 59.02
5,577.29 01/10/00 60.30 58.82
5,577.09 01/17/00 60.50 59.02
5,577.39 01/24/00 60.20 58.72
5,577.29 02/01/00 60.30 58.82
5,577.19 02/07/00 60.40 58.92
5,577.69 02/14/00 59.90 58.42
5,577.69 02/23/00 59.90 58.42
5,577.79 03/01/00 59.80 58.32
5,577.79 03/08/00 59.80 58.32
5,577.89 03/15/00 59.70 58.22
5,568.49 03/20/00 69.10 67.62
5,578.14 03/29/00 59.45 57.97
5,577.84 04/04/00 59.75 58.27
5,578.04 04/13/00 59.55 58.07
5,578.24 04/21/00 59.35 57.87
5,578.39 04/28/00 59.20 57.72
5,578.39 05/01/00 59.20 57.72
5,578.79 05/11/00 58.80 57.32
5,578.39 05/15/00 59.20 57.72
5,578.79 05/25/00 58.80 57.32
5,578.81 06/09/00 58.78 57.30
5,578.89 06/16/00 58.70 57.22
5,578.74 06/26/00 58.85 57.37
5,578.86 07/06/00 58.73 57.25
5,578.87 07/13/00 58.72 57.24
5,578.84 07/18/00 58.75 57.27
5,579.03 07/27/00 58.56 57.08
5,579.03 08/02/00 58.56 57.08
5,579.05 08/09/00 58.54 57.06
5,579.04 08/15/00 58.55 57.07
5,579.25 08/31/00 58.34 56.86
5,579.35 09/08/00 58.24 56.76
5,579.40 09/13/00 58.19 56.71
5,579.46 09/20/00 58.13 56.65
5,579.44 10/05/00 58.15 56.67
5,579.79 11/09/00 57.80 56.32
5,579.73 12/06/00 57.86 56.38
5,580.01 01/03/01 57.58 56.10
5,580.30 02/09/01 57.29 55.81
5,580.66 03/27/01 56.93 55.45
5,580.75 04/30/01 56.84 55.36
Water Levels and Data over Time
White Mesa Mill -Well TW 4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.l
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 TW4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 120.1
5,583.54 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
5,568.30 09/22/20 69.29 67.81
5,568.12 12/30/20 69.47 67.99
5,568.18 03/11/21 69.41 67.93
-.J 0 O'I 00 O'I O'I
Depth Below Measuring Point (ft.)
O'I .j:::.. O'I N O'I 0 Vl 00 Vl O'I Vl .j:::.. Vl N Vl 0
12/20/99
05/18/00
l 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 I '° 10/09/07 ~ 03/07/08
08/04/08 -~ 01/01/09 "1
05/31/09 ~
10/28/09 ~ ~ 03/27/10 -08/24/10 =-
01/21/11 0 -< 06/20/11 ~
11/17/11 "1
04/15/12 ~ -· 09/12/12 a
02/09/13 ~ ---07/09/13 ? 12/06/13 O" 05/05/14 -10/02/14 a
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
02/22/22
07/22/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5,631.99 5,634.24 2.25 113.2
5,576.75 01/03/02 57.49 55.24
5,576.92 02/06/02 57.32 55.07
5,577.43 03/26/02 56.81 54.56
5,577.22 04/09/02 57.02 54.77
5,577.80 05/23/02 56.44 54.19
5,577.47 06/05/02 56.77 54.52
5,577.55 07/08/02 56.69 54.44
5,578.10 08/23/02 56.14 53.89
5,578.24 09/11/02 56.00 53.75
5,578.49 10/23/02 55.75 53.50
5,578.43 11/22/02 55.81 53.56
5,578.43 12/03/02 55.81 53.56
5,578.66 01/09/03 55.58 53.33
5,578.66 02/12/03 55.58 53.33
5,578.78 03/26/03 55.46 53.21
5,578.90 04/02/03 55.34 53.09
5,578.83 05/01/03 55.41 53.16
5,578.05 06/09/03 56.19 53.94
5,577.38 07/07/03 56.86 54.61
5,577.15 08/04/03 57.09 54.84
5,576.76 09/11/03 57.48 55.23
5,576.36 10/02/03 57.88 55.63
5,576.05 11/07 /03 58.19 55.94
5,576.20 12/03/03 58.04 55.79
5,577.43 01/15/04 56.81 54.56
5,577.81 02/10/04 56.43 54.18
5,578.47 03/28/04 55.77 53.52
5,578.69 04/12/04 55.55 53.30
5,578.93 05/13/04 55.31 53.06
5,578.99 06/18/04 55.25 53.00
5,579.18 07/28/04 55.06 52.81
5,579.06 08/30/04 55.18 52.93
5,578.78 09/16/04 55.46 53.21
5,577.80 10/11/04 56.44 54.19
5,577.13 11/16/04 57.11 54.86
5,576.96 12/22/04 57.28 55.03
5,576.63 01/18/05 57.61 55.36
5,576.82 02/28/05 57.42 55.17
5,576.86 03/15/05 57.38 55.13
5,577.52 04/26/05 56.72 54.47
5,578.01 05/24/05 56.23 53.98
5,578.15 06/30/05 56.09 53.84
5,577.90 07/29/05 56.34 54.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5,631.99 5,634.24 2.25 113.2
5,578.02 09/12/05 56.22 53.97
5,577.56 12/07/05 56.68 54.43
5,579.69 03/08/06 54.55 52.30
5,578.34 06/13/06 55.90 53.65
5,577.94 07/18/06 56.30 54.05
5,578.01 11/07/06 56.23 53.98
5578.43 02/27/07 55.81 53.56
5,577.84 05/02/07 56.40 54.15
5,578.74 08/14/07 55.50 53.25
5,579.04 10/10/07 55.20 52.95
5,580.69 03/26/08 53.55 51.30
5,579.87 06/24/08 54.37 52.12
5,579.47 08/26/08 54.77 52.52
5,578.87 10/14/08 55.37 53.12
5,578.01 03/10/09 56.23 53.98
5,577.85 06/24/09 56.39 54.14
5,577.49 09/10/09 56.75 54.50
5,577.98 12/11/09 56.26 54.01
5,578.38 03/11/10 55.86 53.61
5,578.16 05/11/10 56.08 53.83
5,577.85 09/29/10 56.39 54.14
5,577.28 12/21/10 56.96 54.71
5,577.14 02/28/11 57.10 54.85
5,578.09 06/21/11 56.15 53.90
5,578.24 09/20/11 56.00 53.75
5,578.74 12/21/11 55.50 53.25
5,577.89 03/27/12 56.35 54.10
5,577.90 06/28/12 56.34 54.09
5,578.29 09/27/12 55.95 53.70
5,577.87 12/28/12 56.37 54.12
5,577.92 03/28/13 56.32 54.07
5,577.19 06/27/13 57.05 54.80
5,576.77 09/27/13 57.47 55.22
5,576.22 12/20/13 58.02 55.77
5,575.36 03/27/14 58.88 56.63
5,574.11 06/25/14 60.13 57.88
5,573.19 09/25/14 61.05 58.80
5,573.19 12/17/14 61.05 58.80
5,573.12 03/26/15 61.12 58.87
5,573.33 06/22/15 60.91 58.66
5,572.98 09/30/15 61.26 59.01
5,572.39 12/02/15 61.85 59.60
5,572.64 03/30/16 61.60 59.35
Water Levels and Data over Time
White Mesa Mill · Well TW 4-10
Total or
Measuring Measured Total
Water Land Point Length Depth to Depth to Total
Elevation Surface Elevation Of Riser Date Of Water Water Depth Of
(WL) (LSD) (MP) (L) Monitoring (blw.MP) (blw.LSD) Well
5,631.99 5,634.24 2.25 113.2
5,571.79 06/30/16 62.45 60.20
5,571.27 09/29/16 62.97 60.72
5,570.94 12/21/16 63.30 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
5,565.53 09/22/20 68.71 66.46
5,565.33 12/30/20 68.91 66.66
5,565.46 03/11/21 68.78 66.53
00 0 -..J 0 0\ 0
Depth Below Measuring Point (ft.)
V, 0 ~ 0
\;.)
0 N 0 -0 0
01/03/02
06/02/02
10/30/02
~ 03/29/03
08/26/03
01/23/04
06/21/04
11/18/04
04/17/05
09/14/05
02/11/06
07/11/06
12/08/06
05/07/07 ~ 10/04/07 ~ 03/02/08 ~
07/30/08 I
""'"" 12/27/08 0
05/26/09 ~ 10/23/09 -03/22/10 ~ "'1
08/19/10 0
01/16/11 ~ "'CS 06/15/11 ;.
11/12/11 0 04/10/12 <
09/07/12 ~ "'1
02/04/13 ~
07/04/13 .... a 12/01/13 ~
04/30/14 ,-...
? 09/27/14 -r::r 02/24/15 -07/24/15 a "'CS 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
09/20/21
02/17/22
07/17/22
Water Levels and Data over Time
White Mesa Mill-Well TW4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 102.4
5,548.32 01/03/02 75.30 73.60
5,548.73 02/06/02 74.89 73.19
5,549.03 03/26/02 74.59 72.89
5,548.84 04/09/02 74.78 73.08
5,549.30 05/23/02 74.32 72.62
5,549.01 06/05/02 74.61 72.91
5,549.22 07/08/02 74.40 72.70
5,549.44 08/23/02 74.18 72.48
5,549.57 09/11/02 74.05 72.35
5,549.64 10/23/02 73.98 72.28
5,549.58 11/22/02 74.04 72.34
5,549.62 12/03/02 74.00 72.30
5,549.85 01/09/03 73.77 72.07
5,549.91 02/12/03 73.71 72.01
5,550.15 03/26/03 73.47 71.77
5,550.01 04/02/03 73.61 71.91
5,550.31 05/01/03 73.31 71.61
5,550.44 06/09/03 73.18 71.48
5,550.33 07/07/03 73.29 71.59
5,550.35 08/04/03 73.27 71.57
5,550.44 09/11/03 73.18 71.48
5,550.47 10/02/03 73.15 71.45
5,550.60 11/07/03 73.02 71.32
5,550.60 12/03/03 73.02 71.32
5,550.94 01/15/04 72.68 70.98
5,551.00 02/10/04 72.62 70.92
5,550.34 03/28/04 73.28 71.58
5,551.54 04/12/04 72.08 70.38
5,551.89 05/13/04 71.73 70.03
5,551.94 06/18/04 71.68 69.98
5,552.49 07/28/04 71.13 69.43
5,552.74 08/30/04 70.88 69.18
5,553.01 09/16/04 70.61 68.91
5,553.11 10/11/04 70.51 68.81
5,553.19 11/16/04 70.43 68.73
5,553.53 12/22/04 70.09 68.39
5,553.31 01/18/05 70.31 68.61
5,553.84 02/28/05 69.78 68.08
5,554.04 03/15/05 69.58 67.88
5,554.23 04/26/05 69.39 67.69
5,553.87 05/24/05 69.75 68.05
5,554.46 06/30/05 69.16 67.46
5,554.57 07/29/05 69.05 67.35
Water Levels and Data over Time
White Mesa Mill -Well TW 4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 102.4
5,553.86 09/12/05 69.76 68 .06
5,555.30 12/07/05 68.32 66.62
5,556.20 03/08/06 67.42 65.72
5,556.48 06/14/06 67.14 65.44
5,556.37 07/18/06 67.25 65.55
5,556.94 11/07/06 66.68 64.98
5557.92 02/27/07 65.70 64.00
5,557.84 05/02/07 65.78 64.08
5,558.02 08/15/07 65.60 63.90
5,557.13 10/10/07 66.49 64.79
5,569.74 03/26/08 53.88 52.18
5,561.01 06/24/08 62.61 60.91
5,562.07 08/26/08 61.55 59.85
5,562.47 10/14/08 61.15 59.45
5,563.80 03/10/09 59.82 58.12
5,564.27 06/24/09 59.35 57.65
5,564.32 09/10/09 59.30 57.60
5,564.70 12/11/09 58.92 57.22
5,565.14 03/11/10 58.48 56.78
5,565.61 05/11/10 58.01 56.31
5,565.67 09/29/10 57.95 56.25
5,565.62 12/21/10 58.00 56.30
5,565.42 02/28/11 58.20 56.50
5,566.01 06/21/11 57.61 55.91
5,566.03 09/20/11 57.59 55.89
5,566.63 12/21/11 56.99 55.29
5,565.81 03/27/12 57.81 56.11
5,565.82 06/28/12 57.80 56.10
5,566.66 09/27/12 56.96 55.26
5,565.77 12/28/12 57.85 56.15
5,566.89 03/28/13 56.73 55.03
5,566.32 06/27/13 57.30 55.60
5,565.92 09/27/13 57.70 56.00
5,565.63 12/20/13 57.99 56.29
5,565.03 03/27/14 58.59 56.89
5,564.18 06/25/14 59.44 57.74
5,563.52 09/25/14 60.10 58.40
5,563.37 12/17/14 60.25 58.55
5,532.62 03/26/15 91.00 89.30
5,527.07 06/22/15 96.55 94.85
5,533.27 09/30/15 90.35 88.65
5,532.67 12/02/15 90.95 89.25
5,531.44 03/30/16 92.18 90.48
Water Levels and Data over Time
White Mesa Mill -Well 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
5,530.54 09/21/20 93.08 91.38
5,533.51 12/28/20 90.11 88.41
5,533.54 03/11/21 90.08 88.38
.....
8 \0 VI \0 0
Depth Below Measuring Point (ft.)
00 VI 00 0 -...J VI -...J 0 0\ VI 0\ 0 VI VI VI 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 .a;.
07/30/08 I
"""' 12/27/08 """'
05/26/09 ~ 10/23/09 -~ 03/22/10 "1
08/19/10 ~
01/16/11 ~ ~
06/15/11 -=--11/12/11 0 04/10/12 <
09/07/12 ~ "1
02/04/13 ~ ...
07/04/13 e
12/01/13 ~
04/30/14 ,-.,
? 09/27/14 O" 02/24/15 -07/24/15 e ~ 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
09/20/21
02/17/22
07/17/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 103.2
5,580.91 08/23/02 43.32 41.47
5,581.54 09/11/02 42.69 40.84
5,581.33 10/23/02 42.90 41.05
5,581.47 11/22/02 42.76 40.91
5,581.55 12/03/02 42.68 40.83
5,582.58 01/09/03 41.65 39.80
5,582.47 02/12/03 41.76 39.91
5,582.71 03/26/03 41.52 39.67
5,582.11 04/02/03 42.12 40.27
5,582.92 05/01/03 41.31 39.46
5,583.13 06/09/03 41.10 39.25
5,583.21 07/07/03 41.02 39.17
5,583.31 08/04/03 40.92 39.07
5,583.55 09/11/03 40.68 38.83
5,583.72 10/02/03 40.51 38.66
5,583.77 11/07/03 40.46 38.61
5,584.01 12/03/03 40.22 38.37
5,584.37 01/15/04 39.86 38.01
5,584.39 02/10/04 39.84 37.99
5,584.51 03/28/04 39.72 37.87
5,584.90 04/12/04 39.33 37.48
5,584.88 05/13/04 39.35 37.50
5,584.93 06/18/04 39.30 37.45
5,585.36 07/28/04 38.87 37.02
5,585.38 08/30/04 38.85 37.00
5,585.49 09/16/04 38.74 36.89
5,585.85 10/11/04 38.38 36.53
5,585.91 11/16/04 38.32 36.47
5,586.35 12/22/04 37.88 36.03
5,586.14 01/18/05 38.09 36.24
5,586.56 02/28/05 37.67 35.82
5,586.95 03/15/05 37.28 35.43
5,587.20 04/26/05 37.03 35.18
5,587.35 05/24/05 36.88 35.03
5,587.58 06/30/05 36.65 34.80
5,587.58 07/29/05 36.65 34.80
5,587.94 09/12/05 36.29 34.44
5,588.43 12/07/05 35.80 33.95
5,588.92 03/08/06 35.31 33.46
5,588.34 06/13/06 35.89 34.04
5,588.33 07/18/06 35.90 34.05
5,584.70 11/07/06 39.53 37.68
5588.85 02/27/07 35.38 33.53
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) 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) Monitoring (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 103.2
5,573.64 03/28/18 50.59 48.74
5,572.58 06/22/18 51.65 49.80
5,571.91 09/25/18 52.32 50.47
5,571.49 12/17/18 52.74 50.89
5,570.77 03/25/19 53.46 51.61
5,570.78 06/24/19 53.45 51.60
5,570.54 08/12/19 53.69 51.84
5,570.06 11/18/19 54.17 52.32
5,570.02 02/10/20 54.21 52.36
5,569.45 05/04/20 54.78 52.93
5,569.03 09/22/20 55.20 53.35
5,568.91 12/30/20 55.32 53.47
5,568.99 03/11/21 55.24 53.39
Vl \0 Vl +'"
Depth Below Measuring Point (ft.)
+'" \0 +'" +'" VJ \0 VJ +'"
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 ,&;;;..
I
03/19/09
,....
N
08/16/09 ~ 01/13/10 """ 06/12/10 ~ "'1
11/09/10 ~
04/08/11 ~ "'Cl 09/05/11 ~ 02/02/12 0 07/01/12 ~
11/28/12 ~ "'1
04/27/13 ~ ....
09/24/13 a
02/21/14 ~ -..
07/21/14 ?
12/18/14 -a-
05/17/15 -a 10/14/15 "'Cl '-' 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
12/11/21
05/10/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,529.66 08/23/02 90.28 88.43
5,530.66 09/11/02 89.28 87.43
5,529.10 10/23/02 90.84 88.99
5,530.58 11/22/02 89.36 87.51
5,530.61 12/03/02 89.33 87.48
5,529.74 01/09/03 90.20 88.35
5,531.03 02/12/03 88.91 87.06
5,531.82 03/26/03 88.12 86.27
5,524.63 04/02/03 95.31 93.46
5,531.54 05/01/03 88.40 86.55
5,538.46 06/09/03 81.48 79.63
5,539.38 07/07/03 80.56 78.71
5,540.72 08/04/03 79.22 77.37
5,541.25 09/11/03 78.69 76.84
5,541.34 10/02/03 78.60 76.75
5,541.69 11/07/03 78.25 76.40
5,541.91 12/03/03 78.03 76.18
5,542.44 01/15/04 77.50 75.65
5,542.47 02/10/04 77.47 75.62
5,542.84 03/28/04 77.10 75.25
5,543.08 04/12/04 76.86 75.01
5,543.34 05/13/04 76.60 74.75
5,543.40 06/18/04 76.54 74.69
5,544.06 07/28/04 75.88 74.03
5,544.61 08/30/04 75.33 73.48
5,545.23 09/16/04 74.71 72.86
5,546.20 10/11/04 73.74 71.89
5,547.43 11/16/04 72.51 70.66
5,548.96 12/22/04 70.98 69.13
5,549.02 01/18/05 70.92 69.07
5,550.66 02/28/05 69.28 67.43
5,551.26 03/15/05 68.68 66.83
5,552.23 04/26/05 67.71 65.86
5,552.87 05/24/05 67.07 65.22
5,553.42 06/30/05 66.52 64.67
5,554.00 07/29/05 65.94 64.09
5,555.21 09/12/05 64.73 62.88
5,558.13 12/07/05 61.81 59.96
5,562.93 03/08/06 57.01 55.16
5,564.39 06/13/06 55.55 53.70
5,562.09 07/18/06 57.85 56.00
5,565.49 11/07/06 54.45 52.60
5,571.08 02/27/07 48.86 47.01
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,570.63 05/02/07 49.31 47.46
5,565.24 08/14/07 54.70 52.85
5,565.83 10/10/07 54.11 52.26
5,569.29 03/26/08 50.65 48.80
5,570.00 06/24/08 49.94 48.09
5,570.41 08/26/08 49.53 47.68
5,570.64 10/14/08 49.30 47.45
5,570.43 03/03/09 49.51 47.66
5,570.56 06/24/09 49.38 47.53
5,570.42 09/10/09 49.52 47.67
5,571.15 12/11/09 48.79 46.94
5,572.01 03/11/10 47.93 46.08
5,572.88 05/11/10 47.06 45.21
5,573.17 09/29/10 46.77 44.92
5,573.14 12/21/10 46.80 44.95
5,573.10 02/28/11 46.84 44.99
5,573.75 06/21/11 46.19 44.34
5,573.63 09/20/11 46.31 44.46
5,573.94 12/21/11 46.00 44.15
5,572.79 03/27/12 47.15 45.30
5,572.77 06/28/12 47.17 45.32
5,573.04 09/27/12 46.90 45.05
5,572.79 12/28/12 47.15 45.30
5,573.03 03/28/13 46.91 45.06
5,572.44 06/27/13 47.50 45.65
5,573.46 09/27/13 46.48 44.63
5,573.46 12/20/13 46.48 44.63
5,572.90 03/27/14 47.04 45.19
5,571.79 06/25/14 48.15 46.30
5,571.04 09/25/14 48.90 47.05
5,571.08 12/17 /14 48.86 47.01
5,569.50 03/26/15 50.44 48.59
5,569.16 06/22/15 50.78 48.93
5,568.66 09/30/15 51.28 49.43
5,568.02 12/02/15 51.92 50.07
5,568.39 03/30/16 51.55 49.70
5,567.49 06/30/16 52.45 50.60
5,566.99 09/29/16 52.95 51.10
5,566.94 12/21/16 53.00 51.15
5,567.24 03/30/17 52.70 50.85
5,566.79 06/27/17 53.15 51.30
5,566.43 09/28/17 53.51 51.66
5,566.28 11/29/17 53.66 51.81
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 105.7
5,566.24 03/28/18 53.70 51.85
5,566.03 06/22/18 53.91 52.06
5,565.61 09/25/18 54.33 52.48
5,565.32 12/17/18 54.62 52.77
5,564.78 03/25/19 55.16 53.31
5,564.99 06/24/19 54.95 53.10
5,564.78 08/12/19 55.16 53.31
5,564.39 11/18/19 55.55 53.70
5,564.39 02/10/20 55.55 53.70
5,563.82 05/04/20 56.12 54.27
5,563.55 09/22/20 56.39 54.54
5,563.51 12/30/20 56.43 54.58
5,563.66 03/11/21 56.28 54.43
.....
8 I.O 0
Depth Below Measuring Point (ft.)
00 0 -...J 0 0\ 0
lJI 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 I
i,,,,-
03/19/09 ""' 08/16/09 ~ 01/13/10 -06/12/10 ~ "'l
11/09/10 ~
04/08/11 ~ ~
09/05/11 -=-02/02/12 0
07/01/12 < ~ 11/28/12 "'l
04/27/13 ~ ....
09/24/13 9
02/21/14 ~ ,-...
07/21/14 ?
12/18/14 'r::r' -05/17/15 9
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
12/11/21
05/10/22
Water Levels and Data over Time
White Mesa Mill -Well TW 4-14
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) Monitorini (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 TW 4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 95.1
5,522.47 05/02/07 90.30 88.45
5,520.74 08/14/07 92.03 90.18
5,518.13 10/10/07 94.64 92.79
5,522.85 03/26/08 89.92 88.07
5,522.91 06/24/08 89.86 88.01
5,523.01 08/26/08 89.76 87.91
5,522.96 10/14/08 89.81 87.96
5,523.20 03/03/09 89.57 87.72
5,523.33 06/24/09 89.44 87.59
5,523.47 09/10/09 89.30 87.45
5,523.54 12/11/09 89.23 87.38
5,522.98 03/11/10 89.79 87.94
5,524.01 05/11/10 88.76 86.91
5,524.37 09/29/10 88.40 86.55
5,524.62 12/21/10 88.15 86.30
5,524.78 02/28/11 87.99 86.14
5,525.23 06/21/11 87.54 85.69
5,525.45 09/20/11 87.32 85.47
5,525.72 12/21/11 87.05 85.20
5,525.88 03/27/12 86.89 85.04
5,525.97 06/28/12 86.80 84.95
5,526.32 09/27/12 86.45 84.60
5,525.88 12/28/12 86.89 85.04
5,526.91 03/28/13 85.86 84.01
5,526.99 06/27/13 85.78 83.93
5,527.68 09/27/13 85.09 83.24
5,528.19 12/20/13 84.58 82.73
5,528.75 03/27/14 84.02 82.17
5,529.21 06/25/14 83.56 81.71
5,529.78 09/25/14 82.99 81.14
5,530.41 12/17/14 82.36 80.51
5,530.86 03/26/15 81.91 80.06
5,531.40 06/22/15 81.37 79.52
5,532.15 09/30/15 80.62 78.77
5,532.12 12/02/15 80.65 78.80
5,533.12 03/30/16 79.65 77.80
5,533.13 06/30/16 79.64 77.79
5,533.24 09/29/16 79.53 77.68
5,533.42 12/21/16 79.35 77.50
5,533.97 03/30/17 78.80 76.95
5,534.05 06/27/17 78.72 76.87
5,534.07 09/28/17 78.70 76.85
5,534.29 11/29/17 78.48 76.63
Water Levels and Data over Time
White Mesa Mill -Well TW 4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 95.1
5,534.56 03/28/18 78.21 76.36
5,534.67 06/22/18 78.10 76.25
5,534.75 09/25/18 78.02 76.17
5,534.71 12/17/18 78.06 76.21
5,534.71 03/25/19 78.06 76.21
5,535.04 06/24/19 77.73 75.88
5,535.17 08/12/19 77.60 75.75
5,535.09 11/18/19 77.68 75.83
5,535.31 02/10/20 77.46 75.61
5,535.12 05/04/20 77.65 75.80
5,535.25 09/22/20 77.52 75.67
5,535.54 12/30/20 77.23 75.38
5,535.55 03/11/21 77.22 75.37
8
~ , \0 0
~
-<.
•
~
• •
• • ' ..
~
~
•
00 0
• •
• I<~
1,
• ~
0
0
l
• • •
• t
Depth Below Measuring Point (ft.)
....... 0 ~ u,
0 +s-o (.;.)
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 ! 10/20/08 I
03/19/09 ~ ...
08/16/09 ~ 01/13/10 -06/12/10 ~ "'S
11/09/10 ~
04/08/11 ~ ~ 09/05/11 -=-02/02/12 0 07/01/12 <
11/28/12 ~ "'S
04/27/13 ~ ....
09/24/13 9
02/21/14 ~ -07/21/14 ?
12/18/14 O"
05/17/15 -9 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
12/11/21
05/10/22
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) Monitorin; (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
5,545.34 09/21/20 80.11 78.81
5,551.33 12/28/20 74.12 72.82
5,551.37 03/11/21 74.08 72.78
-8 \0 0
Depth Below Measuring Point (ft.)
00 0 -.J 0 O'I 0 Ul 0
.j::..
0
----+----------;--------------;-08/23/02
01/20/03
06/19/03
11/16/03
04/14/04
09/11/04
02/08/05
07/08/05
12/05/05
05/04/06
10/01/06
02/28/07
07/28/07
-12/25/07
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
12/11/21 ._ __ ____. ___ ___,_ ___ __.._ ___ ~ ___ _,__ ___ __._ 05/10/22
~ N
O'I
~ ;-
"1
~ ~ ~ ~
0 ~ ~ "1
~ .... = ~ ,-..,
?
"a" a ~ '-'
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,562.91 08/23/02 61.11 57.74
5,563.45 09/11/02 60.57 57.20
5,563.75 10/23/02 60.27 56.90
5,563.68 11/22/02 60.34 56.97
5,563.68 12/03/02 60.34 56.97
5,564.16 01/09/03 59.86 56.49
5,564.25 02/12/03 59.77 56.40
5,564.53 03/26/03 59.49 56.12
5,564.46 04/02/03 59.56 56.19
5,564.79 05/01/03 59.23 55.86
5,564.31 06/09/03 59.71 56.34
5,563.29 07/07/03 60.73 57.36
5,562.76 08/04/03 61.26 57.89
5,561.73 09/11/03 62.29 58.92
5,561.04 10/02/03 62.98 59.61
5,560.39 11/07/03 63.63 60.26
5,559.79 12/03/03 64.23 60.86
5,561.02 01/15/04 63.00 59.63
5,561.75 02/10/04 62.27 58.90
5,562.98 03/28/04 61.04 57.67
5,563.29 04/12/04 60.73 57.36
5,564.03 05/13/04 59.99 56.62
5,564.09 06/18/04 59.93 56.56
5,565.08 07/28/04 58.94 55.57
5,564.56 08/30/04 59.46 56.09
5,563.55 09/16/04 60.47 57.10
5,561.79 10/11/04 62.23 58.86
5,560.38 11/16/04 63.64 60.27
5,559.71 12/22/04 64.31 60.94
5,559.14 01/18/05 64.88 61.51
5,558.65 02/28/05 65.37 62.00
5,558.54 03/15/05 65.48 62.11
5,558.22 04/26/05 65.80 62.43
5,558.54 05/24/05 65.48 62.11
5,559.24 06/30/05 64.78 61.41
5,559.38 07/29/05 64.64 61.27
5,559.23 09/12/05 64.79 61.42
5,557.67 12/07/05 66.35 62.98
5,557.92 03/08/06 66.10 62.73
5,558.47 06/13/06 65.55 62.18
5,558.42 07/18/06 65.60 62.23
5,558.09 11/07/06 65.93 62.56
5,557.34 02/27/07 66.68 63.31
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,625.28 5,628.65 3.37 147.6
5,547.11 05/02/07 76.91 73.54
5,558.52 08/14/07 65.50 62.13
5,559.02 10/10/07 65.00 61.63
5,561.04 03/26/08 62.98 59.61
5,560.06 06/24/08 63.96 60.59
5,559.32 08/26/08 64.70 61.33
5,558.89 10/14/08 65.13 61.76
5,558.40 03/03/09 65.62 62.25
5,558.32 06/24/09 65.70 62.33
5,558.03 09/10/09 65.99 62.62
5,558.81 12/11/09 65.21 61.84
5,559.80 03/11/10 64.22 60.85
5,559.85 05/11/10 64.17 60.80
5,560.54 09/29/10 63.48 60.11
5,558.65 12/21/10 65.37 62.00
5,559.26 02/28/11 64.76 61.39
5,560.48 06/21/11 63.54 60.17
5,561.52 09/20/11 62.50 59.13
5,562.95 12/21/11 61.07 57.70
5,563.76 03/27/12 60.26 56.89
5,563.90 06/28/12 60.12 56.75
5,564.65 09/27/12 59.37 56.00
5,563.77 12/28/12 60.25 56.88
5,564.74 03/28/13 59.28 55.91
5,563.66 06/27/13 60.36 56.99
5,562.27 09/27/13 61.75 58.38
5,562.17 12/20/13 61.85 58.48
5,561.17 03/27/14 62.85 59.48
5,559.53 06/25/14 64.49 61.12
5,558.36 09/25/14 65.66 62.29
5,558.00 12/17/14 66.02 62.65
5,559.02 03/26/15 65.00 61.63
5,560.62 06/22/15 63.40 60.03
5,560.62 09/30/15 63.40 60.03
5,560.85 12/02/15 63.17 59.80
5,560.92 03/30/16 63.10 59.73
5,559.95 06/30/16 64.07 60.70
5,559.72 09/29/16 64.30 60.93
5,559.71 12/21/16 64.31 60.94
5,559.53 03/30/17 64.49 61.12
5,569.02 06/27/17 59.63 56.26
5,558.97 09/28/17 69.68 66.31
5,558.51 11/30/17 70.14 66.77
Water Levels and Data over Time
White Mesa Mill -Well TW4-16
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.L D) 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
5,555.53 09/22/20 73.12 69.75
5,555.37 12/30/20 73.28 69.91
5,555.38 03/11/21 73.27 69.9
00 V, 00 0
Depth Below Measuring Point (ft.)
-..J V, -..J 0 0\ V, 0\ 0
V,
V,
V,
0
l-----+-----+---l-----+------4M<+----l-----t-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
12/11/21 ,___ __ _.__ __ __,_ ___ .____ __ ......__ __ __._ ___ ......._ __ ...._05/10/22
~ ! I
i,,-.
0-.,
~ ;-
"1
t:,
(D
"'O ;.
0 -< (D
"1
~ ... ~ --?
'Cj" a "'O --
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) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625 .24 1.83 130.6
5,546.56 05/02/07 78 .68 76.85
5,546.81 08/15/07 78.43 76.6
5,546.96 10/10/07 78.28 76.45
5,547.90 03/26/08 77.34 75.51
5,548.08 06/25/08 77.16 75.33
5,548.42 08/26/08 76.82 74.99
5,548.05 10/14/08 77.19 75.36
5,548.29 03/03/09 76.95 75.12
5,548.09 06/24/09 77.15 75.32
5,547.79 09/10/09 77.45 75.62
5,548.09 12/11/09 77.15 75.32
5,548.50 03/11/10 76.74 74.91
5,548.89 05/11/10 76.35 74.52
5,548.83 09/29/10 76.41 74.58
5,548.97 12/21/10 76.27 74.44
5,548.68 02/28/11 76.56 74.73
5,549.33 06/21/11 75.91 74.08
5,549.19 09/20/11 76.05 74.22
5,550.06 12/21/11 75.18 73.35
5,550.31 03/27/12 74.93 73.10
5,550.32 06/28/12 74.92 73.09
5,550.88 09/27/12 74.36 72.53
5,550.29 12/28/12 74.95 73.12
5,551.54 03/28/13 73.70 71.87
5,550.34 06/27/13 74.90 73.07
5,551.35 09/27/13 73.89 72.06
5,551.33 12/20/13 73.91 72.08
5,550.97 03/27/14 74.27 72.44
5,550.16 06/25/14 75.08 73.25
5,549.29 09/25/14 75.95 74.12
5,548.99 12/17/14 76.25 74.42
5,548.24 03/26/15 77.00 75.17
5,548.29 06/22/15 76.95 75.12
5,548.33 09/30/15 76.91 75.08
5,547.98 12/02/15 77.26 75.43
5,548.24 03/30/16 77.00 75.17
5,547.68 06/30/16 77.56 75.73
5,547.29 09/29/16 77.95 76.12
5,547.09 12/21/16 78.15 76.32
5,547.34 03/30/17 77.90 76.07
5,546.94 06/27/17 78.30 76.47
5,546.59 09/28/17 78.65 76.82
5,546.32 11/30/17 78.92 77.09
Water Levels and Data over Time
White Mesa Mill -Well MW-32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5,546.19 03/29/18 79.05 77.22
5,545.99 06/22/18 79.25 77.42
5,545.57 09/26/18 79.67 77.84
5,545.56 12/17/18 79.68 77.85
5,545.08 03/26/19 80.16 78.33
5,544.99 06/24/19 80.25 78.42
5,544.87 08/12/19 80.37 78.54
5,544.70 11/19/19 80.54 78.71
5,544.57 02/13/20 80.67 78.84
5,544.99 05/05/20 80.25 78.42
5,543.69 09/22/20 81.55 79.72
5,543.67 12/30/20 81.57 79.74
5,543.64 03/11/21 81.60 79.77
00 .i::,. 00 N
Depth Below Measuring Point (ft.)
00 0 -.l 00 -.l 0\ -.l .i::,. -.l N
i---_ _.,...----t-------+------------;---------+-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
12/11/21 .__ __ __. ___ __,_ ___ ___._ ___ _._ ___ ___,__ ___ _,_ 05/10/22
~ ~ ~
~ ;-
1"1
~ ~
Er
0 ~
~ ...
9 ~ -?
i 't:S ._,
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 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
5,571.45 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
5,568.90 09/22/20 72.38 70.23
5,568.70 12/30/20 72.58 70.43
5,568.73 03/11/21 72.55 70.40
00 0 -..J 0 0\ 0
Depth Below Measuring Point (ft.)
t.ll 0
,I:,..
0 w 0 N 0 -0 0
1------+----t--<11----+----+-----+------t-----t------t-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
12/11/21
'------'---.L----'-----'-----'----'---_,__ __ _._ 05/10/22
~ ~ ,I;;,,.
I i,-.
00
~ ~ "'1
0 ~ "'C ;.
0 < ~ "'1
~ -· a ~ -? a -a "'C '-"
Water Levels and Data over Time
White Mesa Mill -Well TW4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 126.86
5,581.88 08/23/02 49.51 47.65
5,582.14 09/11/02 49.25 47.39
5,582.06 10/23/02 49.33 47.47
5,582.07 11/22/02 49.32 47.46
5,582.16 12/03/02 49.23 47.37
5,582.28 01/09/03 49.11 47.25
5,582.29 02/21/03 49.10 47.24
5,582.74 03/26/03 48.65 46.79
5,582.82 04/02/03 48.57 46.71
5,548.47 05/01/03 82.92 81.06
5,564.76 06/09/03 66.63 64.77
5,562.53 07/07/03 68.86 67.00
5,564.10 08/04/03 67.29 65.43
5,566.01 08/30/04 65.38 63.52
5,555.16 09/16/04 76.23 74.37
5,549.80 10/11/04 81.59 79.73
5,546.04 11/16/04 85.35 83.49
5,547.34 12/22/04 84.05 82.19
5,548.77 01/18/05 82.62 80.76
5,551.18 02/28/05 80.21 78.35
5,556.81 03/15/05 74.58 72.72
5,562.63 04/26/05 68.76 66.90
5,573.42 05/24/05 57.97 56.11
5,552.94 07/29/05 78.45 76.59
5,554.00 09/12/05 77.39 75.53
5,555.98 12/07/05 75.41 73.55
5,552.00 03/08/06 79.39 77.53
5,545.74 06/13/06 85.65 83.79
5,544.06 07/18/06 87.33 85.47
5,548.81 11/07/06 82.58 80.72
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 TW4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 126.86
5,561.35 05/11/10 70.04 68.18
5,535.26 09/29/10 96.13 94.27
5,568.40 12/21/10 62.99 61.13
5,550.36 02/28/11 81.03 79.17
5,570.41 06/21/11 60.98 59.12
5,567.84 09/20/11 63.55 61.69
5,571.32 12/21/11 60.07 58.21
5,572.40 03/27/12 58.99 57.13
5,572.39 06/28/12 59.00 57.14
5,571.40 09/27/12 59.99 58.13
5,568.21 12/28/12 63.18 61.32
5,572.51 03/28/13 58.88 57.02
5,566.00 06/27/13 65.39 63.53
5,568.37 09/27/13 63.02 61.16
5,564.55 12/20/13 66.84 64.98
5,565.11 03/27/14 66.28 64.42
5,561.49 06/25/14 69.90 68.04
5,562.67 09/25/14 68.72 66.86
5,562.99 12/17/14 68.40 66.54
5,567.99 03/26/15 63.40 61.54
5,562.79 06/22/15 68.60 66.74
5,568.16 09/30/15 63.23 61.37
5,567.51 12/02/15 63.88 62.02
5,566.38 03/30/16 65.01 63.15
5,566.91 06/30/16 64.48 62.62
5,567.38 09/29/16 64.01 62.15
5,567.41 12/21/16 63.98 62.12
5,566.87 03/30/17 64.52 62.66
5,566.76 06/27/17 64.63 62.77
5,565.19 09/28/17 66.20 64.34
5,565.79 11/30/17 65.60 63.74
5,563.79 03/28/18 67.60 65.74
5,564.58 06/22/18 66.81 64.95
5,562.56 09/24/18 68.83 66.97
5,555.78 12/18/18 75.61 73.75
5,547.86 03/25/19 83.53 81.67
5,557.99 06/24/19 73.40 71.54
5,554.26 08/12/19 77.13 75.27
5,561.87 11/18/19 69.52 67.66
5,561.71 02/10/20 69.68 67.82
5,563.21 05/04/20 68.18 66.32
5,559.19 09/21/20 72.20 70.34
5,554.95 12/28/20 76.44 74.58
Water Land
Elevation Surface
(WL) (LSD)
5,629.53
5,558.24
Water Levels and Data over Time
White Mesa Mill -Well TW 4-19
Total or
Measuring Measured
Point Depth to
Elevation Length Of Date Of Water
(MP) Riser (L) Monitoring (blw.MP)
5,631.39 1.86
03/11/21 73.15
Total Depth
to Water
(blw.LSD)
71.29
Total Depth Of
Well
126.86
-0 0 \0 0
Depth Below Measuring Point (ft.)
00 0 -.J 0 O'I 0
Vl
0 t
1-----+----+----+-----t------;----i-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
03/09/07
08/06/07
01/03/08
06/01/08
10/29/08
03/28/09
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
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
02/23/21
07/23/21
12/20/21 L_ __ ___JL_ __ ---1 ___ -.L.. ___ -1... ___ __._ ___ _._ 05/19/22
~ ! I ~
\e
~ ;-
~
~ ~ "'CS ~
0 ;g
~
~ ... = ~ --?
C" -= "'CS ,,_,
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
5,566.29 09/21/20 73.06 71.91
5,562.48 12/28/20 76.87 75.72
5,568.64 03/11/21 70.71 69.56
\0 0 00 0 -..J 0
Depth Below Measuring Point (ft.)
O'I 0 Ul 0 ~ vJ 0 N 0 -0 0
07/29/05
12/26/05
05/25/06
10/22/06
03/21/07
08/18/07
01/15/08
06/13/08
11/10/08
04/09/09
09/06/09
02/03/10
07/03/10
11/30/10
04/29/11
09/26/11
02/23/12
07/22/12
12/19/12
05/18/13
10/15/13
03/14/14
08/11/14
01/08/15
06/07/15
11/04/15
04/02/16
08/30/16
01/27/17
06/26/17
11/23/17
04/22/18
09/19/18
02/16/19
07/16/19
12/13/19
05/11/20
10/08/20
03/07/21
08/04/21
01/01/22
~ ! I N ,.._
~ ;-..,
~ ~ "Cl g.
0 < ~ ..,
~ ... ~ -. ?
~ a "Cl '-'
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
5,559.12 09/21/20 69.88 68 .71
5,564.70 12/28/20 64.30 63.13
5,560.19 03/11/21 68.81 67.64
-8 I.O 0 00 0
Depth Below Measuring Point (ft.)
-.l 0 ~ V,
0
.j::,.
0
u.)
0 N 0 -0 0
07/29/05
12/26/05
05/25/06
10/22/06
03/21/07
08/18/07
01/15/08
06/13/08
11/10/08
04/09/09
09/06/09
02/03/10 ~ ~ 07/03/10 ,&;;:..
I
11/30/10 N N
04/29/11 ~ 09/26/11 """ 02/23/12 ('I)
""l
07/22/12 C,
('I)
12/19/12 ~
05/18/13
g.
0 10/15/13 ~ ('I)
03/14/14 ""l
08/11/14 ~ ...
01/08/15 a ('I)
06/07/15 ,-.,
?
11/04/15 a--04/02/16 a
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
08/04/21
01/01/22
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
5,532.33 09/22/20 75.04 73.44
5,532.30 12/30/20 75.07 73.47
5,532.32 03/11/21 75.05 73.45
Depth Below Measuring Point (ft.)
....J ....J ....J ....J O'I O'I ~ O'I O'I .I:,. N 0 00 O'I 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 ""'3
10/22/11 ~
03/20/12 ...
I N
08/17/12 w
~ 01/14/13
""'" 06/13/13 ~ "1
11/10/13 ~ ~
04/09/14 "C ~
09/06/14 0 < 02/03/15 ~ "1
07/03/15 ""'3 ...
11/30/15 9 ~
04/28/16 -?
09/25/16 'Cj"
02/22/17 a "C
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
08/30/21
01/27/22
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 l l/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
5,558.88 09/21/20 68.95 66.82
5,556.76 12/28/20 71.07 68.94
5,557.89 03/11/21 69.94 67.81
\0 0 0
00 0 0
-.J 0 0
Depth Below Measuring Point (ft.)
°' 0 0
Vt 0 0 c!5 0
(.;.l
0 0
N 0 0
.....
0 0 0 0
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10
05/25/11 ~
10/22/11 ~
03/20/12 .&;.
I N
08/17/12 .&;.
~ 01/14/13 -06/13/13 ~ ..,
11/10/13 0 ~ ~ 04/09/14 -=-09/06/14 0 < 02/03/15 ~ ..,
07/03/15 ~ -· 11/30/15 a ~
04/28/16 --?
09/25/16 O" -02/22/17 a ~
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
08/30/21
01/27/22
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) Monitoring (blw.MP) (blw.LSD) Well
5,642.82 5,644.91 2.09 136.7
5,584.79 03/27/14 60.12 58.03
5,582.44 06/25/14 62.47 60.38
5,583.95 09/25/14 60.96 58.87
5,581.13 12/17/14 63.78 61.69
5,587.40 03/26/15 57.51 55.42
5,581.91 06/22/15 63.00 60.91
5,581.40 09/30/15 63.51 61.42
5,578.42 12/02/15 66.49 64.40
5,579.42 03/30/16 65.49 63.40
5,579.25 06/30/16 65.66 63.57
5,579.68 09/29/16 65.23 63.14
5,577.73 12/21/16 67.18 65.09
5,584.44 03/30/17 60.47 58.38
5,580.19 06/27/17 64.72 62.63
5,573.63 09/28/17 71.28 69.19
5,577.88 11/30/17 67.03 64.94
5,543.71 03/28/18 101.20 99.11
5,575.26 06/22/18 69.65 67.56
5,578.78 09/24/18 66.13 64.04
5,567.86 12/17/18 77.05 74.96
5,572.46 03/25/19 72.45 70.36
5,571.58 06/24/19 73.33 71.24
5,572.15 08/12/19 72.76 70.67
5,572.66 11/18/19 72.25 70.16
5,572.77 02/10/20 72.14 70.05
5,572.46 05/04/20 72.45 70.36
5,575.17 09/21/20 69.74 67.65
5,574.42 12/28/20 70.49 68.40
5,574.90 03/11/21 70.01 67.92
...... ......
~ 8
Depth Below Measuring Point (ft.)
00 0 °' 0 ~ 0 N 0 0
09/13/07
02/10/08
07/09/08
12/06/08
05/05/09
10/02/09
03/01/10
07/29/10
12/26/10
05/25/11 ~
10/22/11 ~ • 03/20/12 I N
~ 08/17/12 th
~ 01/14/13 -06/13/13 ~ ..,
11/10/13 ~ ~ 'C 04/09/14 -=--09/06/14 0 ~ 02/03/15 ~ ..,
07/03/15 ~ -· 11/30/15 a ~
04/28/16 ..-?
09/25/16 C" -02/22/17 a 'C
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
08/30/21
01/27/22
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
5,528.48 09/22/20 73.20 71.50
5,528.42 12/30/20 73.26 71.56
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
5,528.39 03/11/21 73.29 71.59
~
8
-..J N
8
Depth Below Measuring Point (ft.)
-..J 0
8
0\ 00
0 0
0\ 0\
8
0\ .j:,.
0 0
0\ N
0 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 ~
05/06/13 ~ .&:;;.
I N
-10/03/13 °'
03/02/14 ~ -~
07/30/14 "1
~
12/27/14 ~ "O
05/26/15 ;.
0
10/23/15 -< ~ "1
03/21/16 ~ .....
· 08/18/16 9 ~ --01/15/17 ?
'r:::t'
06/14/17 -9
11/11/17 "O -
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
• 12/20/21
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 I 2/21/11 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
5,528.89 09/22/20 79.05 77.30
5,529.12 12/30/20 78.82 77.07
5,529.21 03/11/21 78.73 76.98
Depth Below Measuring Point (ft.)
I.O I.O 00 00 00 00 00 .....
N 0 00 en .IS, N 0 00 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
04/17/11
09/14/11
02/11/12
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~
12/27/14 ~ .&;.
I N
05/26/15 -...l
~ 10/23/15 -~ "1
03/21/16 ~ ~
08/18/16 "Cl -=-
01/15/17 0 < ~
06/14/17 "1
~ ...
11/11/17 a ~ --04/10/18 ?
'r:1" 09/07/18 -a
02/04/19 "Cl '-"
07/04/19
12/01/19
04/29/20
09/26/20
02/23/21
07/23/21
12/20/21
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
5,568.41 09/22/20 48.59 45.11
5,568.29 12/30/20 48.71 45.23
5,568.32 03/11/21 48.68 45.20
0\ 0
8
Depth Below Measuring Point (ft.)
Vl .i::,. v.l N 0 0 0 0 o o o o 0 0 0 0
·~
'
~
•
1
•
~
••
'
•
'
•
••
l
·~
•
0
I
'
0
0
-0 0 0
0
8
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14
05/26/15
10/23/15
03/21/16
08/18/16
01/15/17
06/14/17
11/11/17
04/10/18
09/07/18
02/04/19
07/04/19
12/01/19
04/29/20
09/26/20
02/23/21
07/23/21
12/20/21
~ ~ ,I;:,,. I N QO
~ """ ~ ""l
~ ~ "Cl """ =-0 < ~ ""l
~ ... e ~ ---?
C"' -e "Cl '"-'
Water Levels and Data over Time
White Mesa Mill -Well TW4-29
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,602.56 5,606.04 3.48 94.48
5,533.98 03/28/13 72.06 68.58
5,533.84 06/27/13 72.20 68.72
5,534.27 09/27/13 71.77 68.29
5,534.43 12/20/13 71.61 68.13
5,534.32 03/27/14 71.72 68.24
5,533.85 06/25/14 72.19 68.71
5,533.53 09/25/14 72.51 69.03
5,533.60 12/17/14 72.44 68.96
5,533.04 03/26/15 73.00 69.52
5,532.93 06/22/15 73.11 69.63
5,532.79 09/30/15 73.25 69.77
5,532.34 12/02/15 73.70 70.22
5,532.54 03/30/16 73.50 70.02
5,532.01 06/30/16 74.03 70.55
5,531.58 09/29/16 74.46 70.98
5,531.49 12/21/16 74.55 71.07
5,531.60 03/30/17 74.44 70.96
5,531.24 06/27/17 74.80 71.32
5,530.95 09/28/17 75.09 71.61
5,530.83 11/29/17 75.21 71.73
5,530.74 03/28/18 75.30 71.82
5,530.54 06/21/18 75.50 72.02
5,530.28 09/25/18 75.76 72.28
5,530.11 12/17/18 75.93 72.45
5,527.99 03/25/19 78.05 74.57
5,529.77 06/24/19 76.27 72.79
5,529.64 08/12/19 76.40 72.92
5,529.23 11/18/19 76.81 73.33
5,529.10 02/10/20 76.94 73.46
5,528.51 05/04/20 77.53 74.05
5,528.21 09/22/20 77.83 74.35
5,528.13 12/30/20 77.91 74.43
5,528.13 03/11/21 77.91 74.43
-.J \0
8
-.J 00
8
Depth Below Measuring Point (ft.) -1 -.J -.J -.J -.J -.J ~ ~ ~ ~ o o o o o 0 0 0 0 0
-.J N 0 0
-.J .....
8
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14 ~
05/26/15 ~ ,l;;i,,.
I N
10/23/15 \C
03/21/16 ~ -~
Jo"f
08/18/16 ~ ~ ~ 01/15/17 -=--
06/14/17 0 < ~
Jo"f
11/11/17 ~ ...
04/10/18 a ~ ,-..
09/07/18 ?
a--02/04/19 a ~ .._,
07/04/19
12/01/19
04/29/20
09/26/20
02/23/21
07/23/21
12/20/21
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
5,527.75 09/22/20 75.06 71.58
5,527.90 12/30/20 74.91 71.43
5,527.96 03/11/21 74.85 71.37
-...l
00 U'I 0
-...l
00 0 0
Depth Below Measuring Point (ft.)
-...l -...l
U'I 0
-...l -...l
8
-...l O'I U'I 0
-...l O'I
8
-...l V,
U'I 0
-...l V,
0 0
-...l ~
U'I 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14
12/27/14 ""'3 ~
05/26/15 ~ I ~ Q
10/23/15 ~
03/21/16 """" ~ "1
08/18/16 ~ ~ "'C
01/15/17 """" =-0
06/14/17 < ~ "1
11/11/17 ""'3 ...
9
04/10/18 ~ --.
09/07/18 ?
a"
02/04/19 a
"'C '-'
07/04/19
12/01/19
04/29/20
09/26/20
02/23/21
07/23/21
12/20/21
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
5,528.13 09/22/20 76.45 72.97
5,528.41 12/30/20 76.17 72.69
5,528.59 03/11/21 75.99 72.51
00 °' 8
00 .j:::..
0 0
Depth Below Measuring Point (ft.)
00 N
8
00 0 8
-.l 00
8
-.l -.l °' .j:::..
8 0 0
07/10/12
12/07/12
05/06/13
10/03/13
03/02/14
07/30/14 ~
12/27/14 ~ .i. I ~
05/26/15 ~
10/23/15 i -~
03/21/16 "1
t:,
~
08/18/16 "Cl -::r
01/15/17 0 < ~
06/14/17 "1
~ ....
11/11/17 a ~
04/10/18 -?
09/07/18 ~ -a
02/04/19 "Cl '-"
07/04/19
12/01/19
04/29/20
09/26/20
02/23/21
07/23/21
12/20/21
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
5,555.99 09/22/20 55.85 54.21
5,555.99 12/30/20 55.85 54.21
5,556.19 03/11/21 55.65 54.01
Vo -..J 0 0
Vo 0\ 0 0
Vo Vo
8
Depth Below Measuring Point (ft.)
Vo .j::,..
8
Vo vJ
0 0
Vo N
8
Vo -8
Vo .j::,..
0 '° 0 0 0 0
.j::,..
00
0 0
.j::,.. .j::,..
-..J 0\
8 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
02/23/21
07/23/21
12/20/21
~ ~ ,I:,,.
I ~ N
~ ;-
""I
0 ~ '"CS ~
0 < ~ ""I
~ ... a ~ -?
O"' 9
'"CS --
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
5,529.30 09/22/20 77.43 75.90
5,529.15 12/30/20 77.58 76.05
5,529.07 03/11/21 77.66 76.13
-..l '° 8
-..l 00
8
-..l -..l
8
Depth Below Measuring Point (ft.)
-..l 0\
8
-..l Vl
8
-..l .j::..
8
-..l w
8
-..l N
8
-..l -0 0
-..l 0
8
0\ \0 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
02/23/21
07/23/21
12/20/21
~ ~ .a. I ~ ~
~ ;-
""S
~ ('I) ~ ;.
0 < ('I)
""S
~ .... a ('I) --?
O" 9 ~ ,_,
Water Levels and Data over Time
White Mesa Mill -Well TW 4-34
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,601.60 5,603.34 1.74 95.74
5,534.04 09/27/13 69.30 67.56
5,534.14 12/20/13 69.20 67.46
5,533.89 03/27/14 69.45 67.71
5,533.32 06/25/14 70.02 68 .28
5,532.94 09/25/14 70.40 68.66
5,532.99 12/17/14 70.35 68.61
5,532.37 03/26/15 70.97 69.23
5,532.24 06/22/15 71.10 69 .36
5,532.08 09/30/15 71.26 69.52
5,531.79 12/02/15 71.55 69.81
5,531.80 03/30/16 71.54 69.80
5,531.28 06/30/16 72.06 70.32
5,530.87 09/29/16 72.47 70.73
5,530.74 12/21/16 72.60 70.86
5,530.79 03/30/17 72 .55 70.81
5,530.43 06/27/17 72.91 71.17
5,530.12 09/28/17 73.22 71.48
5,530.01 11/29/17 73.33 71.59
5,529.84 03/28/18 73.50 71.76
5,529.64 06/21/18 73.70 71.96
5,529.39 09/25/18 73.95 72.21
5,529.23 12/17/18 74.11 72.37
5,528.83 03/25/19 74.51 72.77
5,528.84 06/24/19 74.50 72.76
5,528.75 08/12/19 74.59 72.85
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
5,527.28 09/22/20 76.06 74.32
5,527.22 12/30/20 76.12 74.38
5,527.10 03/11/21 76.24 74.50
OZ/81/90
61/"'70/ZO --Q. s -,.Q
¢! ,_,
Q,j s LI/ZZ/60 .... E-t
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Q. Q,j 9I/Ol/~O Q
J.. Q,j ..... ~
""' ~ I
""' t'I/LZ/Zl ~ E-t
£1/"71/80
Zl/10/"70
0 0 0 0 0 0 0 0 0 0 0 0 0 C: 0 C: 0 C: 0 0 00 0\ 0 -C'i (") ~ V"l \0 r-..: I.O I.O r---r---r---r---r---r---r---r---
('l.J) lll!Od iuµnsugw MOPS: qidga
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
5,524.71 09/22/20 75.16 73.96
5,524.82 12/30/20 75.05 73.85
5,524.49 03/11/21 75.38 74.18
OZ/81/90
--Q. e -,.Q 61/'170/ZO ~ '-'
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In 91/01/~0 ""' I "" ~ E-4
'171/LZ/ZI
£1/'171/80
0 0 0 0 0 0 0 0 0 0 0 ~ 00 0 N 'tj" \0 00 ~ C"! '<:I: ~
(") (") ~ ~ ~ ~ ~ "' "' "' "' r-r-r-r-r-r-r-r-r-r-r-
(':JJ) lU!Od ~uµnsugw MOJgg q1dgQ
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
5,558.64 09/22/20 57.95 56.54
5,558.76 12/30/20 57.83 56.42
5,558.84 03/11/21 57.75 56.34
--Q. e -,J:;.
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OZ/8I/90
6I/r0/ZO
LI/ZZ/60
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tl/LZ/Zl
0 ~ r-
V'l
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
5,553.36 09/21/20 78.49 76.77
5,563.37 12/28/20 68.48 66.76
5,562.66 03/11/21 69.19 67.47
OZ/81/90
--~ e -,t:J.
;t! --QI 61/170/ZO e .... ~ ..
QI ~
0
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0 0 0 0 0 0 0 0 0 0 0 0 0 0
c::i c::i c::i c::i 0 c::i c::i N "Sf" \Ci 00 0 N
("lJ) lll!Od ~uµnsugw MOPS: qldgQ ...... ......
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
5,570.69 09/22/20 59.30 58.13
5,570.74 12/30/20 59.25 58.08
5,570.54 03/11/21 59.45 58.28
lZ/170/10
OZ/81/90
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91/81/80
0 0 0 0 0 8 0 ~ 0 0 C: 0 C: 0 C: 0 N c<"'l ~ tr) \0 r-..: 00 O'I ci tr) tr) tr) tr) tr) tr) tr) tr) '° ("lJ) lU!Od ~uµns1igw Mapa qidga
Water Levels and Data over Time
White Mesa Mill -Well TW4-39
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
5,552.04 09/21/20 77.52 76.78
5,553.71 12/28/20 75.85 75.11
5,557.31 03/11/21 72.25 71 .51
lZ/170/IO
OZ/81/90
--Q.c e 61/IO/Zl -,.Q
~ .._,
Qi e ·-~ 61/~l/~O
~ Qi ;..,.
0
,fl
Q.c 81/LZ/Ol Qi
Q
~ Qi .... t
O'I 81/01/170 ~ I "" ~ ~
ll/ZZ/60
lI/90/£0
91/81/80
0 0 0 0 0 0 0 0 0 0 0 0 0 0
ci ci ci 0 ci ci ci N s::t" \0 00 0 N
('lJ) lU!Od 8uµnsU.)W Mopg qld~Q --
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
5,525.51 09/21/20 72.07 70.15
5,523.08 12/28/20 74.50 72.58
5,526.17 03/11/21 71.41 69.49
-~ .§
~
ct:: '-'
ClJ s ·~ ~ -ClJ ;.,.
0
-= ~ ClJ ~ -ClJ ..... ~ = "" I "" ~ ~
IZ/tl/10
OZ/ll/80
Ol/Ol/EO
61/ZZ/Ol
61/~Z/~O
8 l/9Z/Zl
8I/6Z/LO
00 I.O 0 r--r-
Water Levels and Data over Time
White Mesa Mill -Well TW4-41
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,613.31 5,614.96 1.65 97.8
5,539.24 03/28/18 75.72 74.07
5,526.18 06/22/18 88.78 87.13
5,513.86 09/24/18 101.10 99.45
5,536.53 12/17/18 78.43 76.78
5,521.88 03/25/19 93.08 91.43
5,527.89 06/24/19 87.07 85.42
5,530.75 08/12/19 84.21 82.56
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
5,529.30 09/21/20 85.66 84.01
5,528.43 12/28/20 86.53 84.88
5,525.74 03/11/21 89.22 87.57
,-..,
Col e -,.Q
~ '-'
a.> e .... ~ -a.> ~ 0 ..= -Col a.> Q -a.> -t
,...,t
'-::I' I '-::I' ~ ~
IZ/tl/IO
OZ/l I/80
OZIOZ/£0
61/ZZ/OI
61/~Z/~O
8I/9Z/ZI
8I/6Z/LO
0 0 N 0 \0 0 00 8 0 N --
Water Levels and Data over Time
White Mesa Mill -Well TW 4-42
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,592.39 5,594.70 2.31 86.0
5,518.98 03/28/18 75.72 73.41
5,528.28 06/24/19 66.42 64.11
5,527.90 08/12/19 66.80 64.49
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
5,525.75 09/22/20 68.95 66.64
5,525.59 12/30/20 69.11 66.80
5,525.52 03/11/21 69.18 66.87
--Q. s -,l:J
rt: '-'
a.) s .... ~ ..
a.)
j;;,,,
0 ..= ....
Q. a.)
Q .. a.) .... ~
M "" I "" ~ ~
IZ/tl/10
OZ/ll/80
Ol/Ol/£0
61/ZZ/OI
61/~Z/~O
8I/9Z/ZI
8I/6Z/LO
8I/I0/£0 +--~~--+-~~~+--~~-+-~~~1----~~--1-~~---+~~-----1
;z 00 l,C) 0 I"-\0 I"-00 I"-
TabG
Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells over Time
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
·-. ·-MW-4 TW~LS (fQriiw'f;y MW-26) . --· -----
Total ~
Pumped Total Pumped Total Total Total Total Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) Pumped (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 1307110 3370 4947411.4 l.6673E+l0 16673 36.8 930510 1660 3521980.4 5846487381 5846 12.9
Q2 2007 81230 2000 307455.6 614911100 615 1.4 54400 300 205904.0 61771200 62 0.1
Q3 2007 100700 2600 381149.5 990988700 991 2.2 72080 1400 272822.8 381951920 382 0.8
Q4 2007 90830 2300 343791.6 790720565 791 1.7 61750 2000 233723.8 467447500 467 1.0
QI 2008 83950 2400 317750.8 762601800 763 1.7 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 1.7 52970 950 200491.5 190466878 190 0.4
Q2 2009 450040 1800 1703401.4 3066122520 3066 6.8 58050 410 219719.3 90084892.5 90 0.2
Q3 2009 90420 2000 342239.7 684479400 684 1.5 57610 850 218053.9 185345773 185 0.4
Q4 2009 322380 1800 1220208.3 2196374940 2196 4.8 61960 1100 234518.6 257970460 258 0.6
QI 2010 68125 1600 257853.1 412565000 413 0.9 61320 780 232096.2 181035036 181 0.4
Q2 2010 84005.33 2100 317960.2 667716366 668 1.5 60500 1900 228992.5 435085750 435 1.0
Q3 2010 79859.1 1900 302266.7 574306718 574 1.3 63850 2200 241672.3 531678950 532 1.2
Q4 2010 90042.2 1500 340809.7 511214591 511 1.1 60180 970 227781.3 220947861 221 0.5
QI 2011 76247.6 1700 288597.2 490615182 491 1.l 55130 450 208667.1 93900172.5 94 0.2
Q2 2011 85849.3 1700 324939.6 552397321 552 1.2 55800.6 1800 211205.3 380169488 380 0.8
Q3 2011 85327.7 1700 322965.3 549041086 549 1.2 65618 720 248364.1 178822174 179 0.4
Q4 2011 89735.0 1600 339647.0 543435160 543 1.2 50191.3 1800 189974.1 341953327 342 0.8
QI 2012 90376.4 1500 342074.7 513112011 513 1.1 31440.1 2400 119000.8 285601868 286 0.6
Q2 2012 90916.5 1400 344118.8 481766269 482 1.1 26701.2 3000 101064.1 303192353 303 0.7
Q3 2012 91607.0 1500 346732.5 520098743 520 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 23263.1 1400 88050.8 123271167 123 0.3
Q2 2014 71934.9 1390 272273.6 378460299 378 0.8 23757.5 1960 89922.1 176247390 176 0.4
Q3 2014 74788.2 1490 283073.3 421779272 422 0.9 24062.4 2120 91076.2 193081510 193 0.4
Q4 2014 63093.0 1440 238807.0 343882087 344 0.8 21875.8 2090 82799.9 173051797 173 0.4
QI 2015 76454.3 1400 289379.5 405131336 405 0.9 24004.9 1980 90858.5 179899922 180 0.4
Q2 2015 60714.7 1300 229805.1 298746681 299 0.7 27804.6 1980 105240.4 208376014 208 0.5
Q3 2015 89520.8 1290 338836.2 437098734 437 1.0 21042.0 2350 79644.0 187163330 187 0.4
Q4 2015 99633.4 1200 377112.4 452534903 453 1.0 19355.6 2680 73260.9 196339335 196 0.4
QI 2016 90882.1 1240 343988.7 426546048 427 0.9 19150.8 2650 72485.8 192087312 192 0.4
Q2 2016 96540.5 1580 365405.8 577341152 577 1.3 22105.7 2220 83670.1 185747565 186 0.4
Q3 2016 79786.4 1430 301991.5 431847879 432 1.0 17149.5 3190 64910.9 207065635 207 0.5
Q4 2016 85414.0 1470 323292.0 475239225 475 1.0 18541.6 2510 70180.0 176151690 176 0.4
QI 2017 76642.3 1450 290091.1 420632103 421 0.9 26107.0 1290 98815.0 127471344 127 0.3
Q2 2017 72299.8 1430 273654.7 391326282 391 0.9 25921.8 2450 98114.0 240379332 240 0.5
Q3 2017 95349.3 1400 360897.1 505255941 505 1.1 27489.9 1230 104049.3 127980604 128 0.3
Q4 2017 I 06679.8 1320 403783.0 532993617 533 1.2 26445.8 2570 100097.4 257250197 257 0.6
Table G-1
--· .. _,. -· ..... -.... ,-... "" .. ""' -···~· _. ............. _. ......... --.......... ""-·' . ~·-··~-............. ~_. ........................
-. MW-4 TW4-15 (foJmerly,MW-~ -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 1.1 26654.7 1870 100888.0 188660634 189 0.4
Q3 2018 95480.5 1300 361393.7 469811800 470 1.0 25536.l 1680 96654.1 162378953 162 0.4
Q4 2018 102884.8 1330 389418.9 517927177 518 1.1 23791.3 1480 90050.l 133274104 133 0.3
Ql 2019 111746.9 1190 422962.0 503324800 503 1.1 26798.5 1110 101432.3 112589878 113 0.2
Q2 2019 94540.7 1300 357836.5 465187514 465 1.0 24050.2 1280 91030.0 l 16518409 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 l.l 22384.8 1390 84726.5 117769791 118 0.3
QI 2020 102597.0 1230 388329.6 477645370 478 1.1 24107.0 1100 91245.0 100369495 100 0.2
Q2 2020 101850.7 1250 385504.9 481881077 482 1.1 25418.4 1610 96208.6 154895917 155 0.3
Q3 2020 84607.8 1240 320240.6 397098342 397 0.9 23663.7 1130 89567.1 101210828 101 0.2
Q4 2020 91258.6 1050 345413.8 362684491 363 0.8 28934.5 866 109517.1 94841793.4 95 0.2
QI 2021 93486.7 1150 353847.3 406924364 407 0.9 27898.0 3060 105593.9 323117426 323 0.7
Totals 6730777.43 107.9 2942169.9 38.2
TableG-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-19 -TW4-29
' 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
Ql 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
Ql 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 1268111 260 1268 2.8
Q3 2009 200650 6600 759460.3 5012437650 5012 I l. I 51030 13000 193148.6 2510931150 2511 5.5
Q4 2009 454205 4700 1719165.9 8080079848 8080 17.8 208790 15000 790270.2 l.1854E+IO I 1854 26.1
Ql 2010 348550 940 1319261.8 1240106045 1240 2.7 14490 3500 54844.7 191956275 192 0.4
Q2 2010 453340 1800 1715891.9 3088605420 3089 6.8 39014.86 18000 147671.2 2658082412 2658 5.9
Q3 2010 116899.2 2000 442463.5 884926944 885 2.0 39098.3 15000 147987.l 2219805983 2220 4.9
Q4 2010 767970.5 1200 2906768.3 3488122011 3488 7.7 36752.5 24000 139108.2 3338597100 3339 7.4
Ql 2011 454607.9 3400 1720690.9 5850349065 5850 12.9 37187.5 31000 140754.7 4363395313 4363 9.6
Q2 2011 159238.9 4000 602719.2 2410876946 2411 5.3 67907.7 8100 257030.6 2081948220 2082 4.6
Q3 2011 141542.6 970 535738.7 519666578.8 520 1.1 72311.2 6800 273697.9 1861145666 1861 4.1
Q42011 147647.2 2200 558844.7 1229458234 1229 2.7 72089.3 7900 272858.0 2155578204 2156 4.8
Ql 2012 148747 650 563007.4 365954806.8 366 0.8 76306 11000 288818.2 3177000310 3177 7.0
Q2 2012 172082.03 460 651330.5 299612022.4 300 0.7 22956.43 36000 86890.1 3128043152 3128 6.9
Q3 2012 171345 950 648540.8 616113783.8 616 1.4 22025 13000 83364.6 1083740125 1084 2.4
Q4 2012 156653 1500 592931.6 889397407.5 889 2.0 20114 19000 76131.5 1446498310 1446 3.2
Ql 2013 210908 4210 798286.8 3360787344 3361 7.4 18177 18500 68799.9 1272798983 1273 2.8
Q2 2013 226224 2070 856257.8 1772453729 1772 3.9 20252.4 26300 76655.3 2016035284 2016 4.4
Q3 2013 329460.1 8100 1247006.5 !0100752476 10101 22.3 19731 26800 74681.8 2001473178 2001 4.4
Q4 2013 403974 942 1529041.6 1440357178 1440 3.2 19280.2 15700 72975.6 1145716245 1146 2.5
Ql 2014 304851 586 1153861.0 676162566.5 676 1.5 18781.6 17800 71088.4 1265372737 1265 2.8
Q2 2014 297660.0 810 1126643.1 912580911 913 2.0 18462.4 22100 69880.2 1544352066 1544 3.4
Q3 2014 309742.0 1410 1172373.5 1653046593 1653 3.6 17237.9 12400 65245.5 809043599 809 1.8
Q4 2014 198331.0 4310 750682.8 3235443019 3235 7.1 16341.8 23300 61853.7 1441191513 1441 3.2
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.l 17600 70984.3 1249323126 1249 2.8
Q3 2015 116503.9 7860 440967.3 3466002675 3466 7.6 17657.3 17000 66832.9 1136158969 1136 2.5
Q4 2015 112762.7 7840 426806.8 3346165465 3346 7.4 15547.4 17000 58846.9 1000397453 1000 2.2
QI 2016 116597.0 7780 441319.6 3433466838 3433 7.6 14353.5 21600 54328.0 l 173484746 1173 2.6
Q2 2016 123768.0 12600 468461.9 5902619688 5903 13.0 15818.3 33700 59872.3 2017695347 2018 4.4
Q3 2016 103609.0 6040 392160.1 2368646793 2369 5.2 12186.6 23600 46126.3 1088580232 1089 2.4
Q4 2016 104919.4 6640 397119.9 2636876329 2637 5.8 12879.6 21300 48749.3 1038359792 1038 2.3
Ql 2017 110416.7 1240 417927.2 518229739.8 518 1.1 13552.8 23400 51297.3 1200357943 1200 2.6
Q2 2017 109943.0 510 416134.3 212228470.l 212 0.5 12475.3 18100 47219.0 854664090 855 1.9
Q3 2017 I l 2626.4 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 l 1600 54015.7 626582526 627 1.4
Table G-1
-·-·. ----~--... ,_.. .. ..,.. 00 """" .... ~ ~-0 0. 0 ... _, 0 ·-T ..... _ ,...,. • _.'""'' T _.,,...,,, __ '-'' ,, ... .,_, • ._.,,,.,.. .... .,,. -TW4-19 TW4-20 --
Total
Pumped Total Pumped Total Total Total Total Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) Pumped (gal) Cone (liters) Total (ug) (grams) (pounds)
01 2018 109856.3 2640 415806.1 1097728092 1098 2.4 14258.4 15400 53968.0 831107878 831 1.8
Q2 2018 111271.4 2980 421162.2 1255063502 1255 2.8 13367.6 12000 50596.4 607156392 607 1.3
Q3 201 8 105821.8 1910 400535.5 765022829.8 765 1.7 12443.6 10500 47099.0 494539773 495 I. I
Q4 2018 107197.4 5270 405742.2 2138261178 2138 4.7 12841.l 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
Q42019 98806.8 551 373983.7 206065039.6 206 0.5 8317.69 8790 31482.5 276730794 277 0.6
QI 2020 96857.9 8720 366607.2 3196814361 3197 7.0 9505.05 14300 35976.6 514465584 514 l.l
Q2 2020 136619.7 7600 517105.6 3930002290 3930 8.7 100713.8 5800 381201.6 2210969393 2211 4.9
Q3 2020 154514.4 1350 584837.0 789529955.4 790 1.7 12476.2 Well collapsed and not sampled
Q4 2020 144512.0 660 546977.9 361005427 .2 361 0.8 Well collapsed and not sampled
Ql 2021 133462.3 6660 505154.8 3364331005 3364 7.4 Well collapsed and not sampled
Totals 19694795.13 449.5 2582397.89 296.2
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
Qi 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q22008 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 84513.9 2000 319885.1 639770223 640 1.4 NA NA NA NA NA NA
Q3 2010 76916.8 2100 291130.1 611373184.8 611 1.3 NA NA NA NA NA NA
Q4 2010 86872.1 1700 328810.9 558978527.5 559 1.2 NA NA NA NA NA NA
Ql 2011 73360.0 1800 277667.6 499801680 500 l.l NA NA NA NA NA NA
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
Q42011 109043.5 1500 412729.6 619094471.3 619 1.4 NA NA NA NA NA NA
Ql 2012 101616.8 1200 384619.6 461543505.6 462 1.0 NA NA NA NA NA NA
Q2 2012 87759.1 1500 332168.2 498252290.3 498 I. I NA NA NA NA NA NA
Q3 2012 80006.0 1600 302822.7 484516336 485 l.1 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 16677.4 10600 63124.0 669113965.4 669.1 1.5
Q2 2013 65603.4 1330 248308.9 330250795.8 330 0.7 25523.2 12500 96605.3 1207566400.0 1207.6 2.7
Q3 2013 63515.4 1380 240405.8 331759988.8 332 0.7 25592.9 9640 96869.1 933818379.5 933.8 2.1
Q4 2013 60233.6 1360 227984.2 310058479.4 310 0.7 24952.2 13300 94444.1 1256106224.1 1256.1 2.8
Ql 2014 58992.9 1260 223288.1 281343039.4 281 0.6 24532.0 12100 92853.6 l 123528802.0 1123.5 2.5
Q2 2014 60235.3 1220 227990.6 278148544.8 278 0.6 24193.9 12400 91573.9 1135516502.6 1135.5 2.5
Q3 2014 69229.4 1320 262033.3 345883928.3 346 0.8 24610.9 12400 93152.3 1155087980.6 1155.1 2.5
Q4 2014 64422.6 1130 243839.5 275538681.3 276 0.6 23956.9 12400 90676.9 1124393144.6 I 124.4 2.5
Ql 2015 36941.3 1350 139822.8 188760807.7 189 0.4 22046.9 12700 83447.S 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. l 297 0.7 24619.9 7810 93186.3 727785170.9 727.8 1.6
Q4 2015 59235.1 1190 224204.9 266803775.7 267 0.6 23657.6 7530 89544.0 674266440.5 674.3 1.5
QI 2016 57274.0 1190 216782.1 257970687. I 258 0.6 24517.8 6070 92799.9 563295229.1 563.3 1.2
Q2 2016 61378.0 1780 232315.7 413521999.4 414 0.9 26506.3 8570 100326.3 859796780.9 859.8 1.9
Q3 2016 50104.2 1380 189644.4 261709267.9 262 0.6 22144.1 5840 83815.4 489482044.0 489.5 I. l
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 l 14873130 115 0.3 24066.2 5320 91090.6 484601816.4 484.6 I.I
Q2 2017 23244.9 1290 87981.9 11349671 l 113 0.3 23685.0 3670 89647.7 329007150.8 329.0 0.7
Q3 2017 23937.3 1290 90602.7 116877457.8 117 0.3 24583.2 5150 93047.4 479194171.8 479.2 1.1
Q4 2017 22900.6 1120 86678.8 97080223.52 97 0.2 23779.6 4770 90005.8 429327599.2 429.3 0.9
Table G-1
.......... ~-·· _ .................... "'""' ...... . ..................... ~ ........... ,.. ----··~ ...... ~ .... -· ............ ""' ,,, ........ -, ........ _,.'"" .....
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
Q2 2019 14311.9 1070 54170.5 57962479.41 58 0.1 23073.1 4690 8733 l.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 34776788 l .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
Q3 2020 14389.9 1110 54465.8 60457006.37 60 0.1 23050.6 3760 87246.5 328046919.0 328.0 0.7
Q4 2020 15061.5 979 57007.8 55810614.17 56 0.1 22866.1 3640 86548.2 315035406.l 315.0 0.7
QI 2021 13740.8 1130 52008.9 58770088.64 59 0.1 22605.6 5100 85562.2 436367199.6 436.4 1.0
Totals 2178088.9 26.0 785694.4 44.3
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)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q22011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
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.l 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.l 0.1 126576.5 0.0 479092.1 0.0 0.0 0.0
Ql 2014 229063.9 78.5 867006.9 68060038.6 68.l 0.2 129979.2 0.0 491971.3 0.0 0.0 0.0
Q2 2014 216984.1 62.7 821284.8 51494558.1 5 J.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.l 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 J 1.8 0.026 124137.1 0.0 469858.9 0.0 0.0 0.0
Q4 2015 107799.1 25.3 408019.6 10322895.7 10.3 0.023 116420.1 0.0 440650.1 0.0 0.0 0.0
QI 2016 100063.2 22.8 378739.2 8635254.0 8.6 0.019 115483.2 0.0 437103.9 0.0 0.0 0.0
Q2 2016 65233.6 69.6 246909.2 17184878.6 17.2 0.038 125606.0 0.0 475418.7 0.0 0.0 0.0
Q3 2016 51765.8 17.8 195933.6 3487617.2 3.5 0.008 104983.6 0.0 397362.9 0.0 0.0 0.0
Q4 2016 99522.5 20.8 376692.7 7835207.4 7.8 0.017 98681.2 0.0 373508.3 0.0 0.0 0.0
QI 2017 99117.4 18.3 375159.4 6865416.3 6.9 0.015 161.2 1.15 610.1 701.7 0.0 0.0
Q2 2017 52808.7 17.2 199880.9 3437952.0 3.4 0.008 101617.2 0.0 384621. I 0.0 0.0 0.0
Q3 2017 55574.6 17.8 210349.9 3744227.5 3.7 0.008 124138.4 0.0 469863.8 0.0 0.0 0.0
Q4 2017 106021.4 16.0 401291.0 6420656.0 6.4 0.014 116731.9 0.0 441830.2 0.0 0.0 0.0
Table G-1
--------~-. ---·--· --· -----·--. --··· ~-·--· -· ' ----...... --
TW4-24 TW4-25 -
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
01 2018 96900.2 24.9 366767.3 9132504.7 9.1 0.020 116991.7 0.0 442813.6 0.0 0.0 0.0
Q2 2018 53117.9 49.2 201051.3 9891721.6 9.9 0.022 117758.3 0.0 445715.2 0.0 0.0 0.0
Q3 2018 53142.5 35.0 201144.4 7040052.7 7.0 0.016 11 I 657.5 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 579893 I .3 5.8 0.013 88302.0 0.0 334223. l 0.0 0.0 0.0
Q3 2019 54445.7 31.1 206077.0 6408993.9 6.4 0.014 87609.5 0.0 331602.0 0.0 0.0 0.0
Q4 2019 102211.02 43.3 386868.7 16751415.2 16.8 0.037 85928.53 0.0 325239.5 0.0 0.0 0.0
Ql 2020 86344.38 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
Q3 2020 53316.1 63.8 201801.4 12874931.8 12.9 0.028 83956.3 0.0 317774.6 0.0 0.0 0.0
Q4 2020 103987.2 72.6 393591.6 28574746.7 28.6 0.063 86254.4 0.0 326472.7 0.0 0.0 0.0
Q I 2021 81891.2 96.2 309958.3 29817985.4 29.8 0.066 80272.2 0.0 303830.4 0.0 0.0 0.0
Totals 3653608.5 1.2 3432179.8 0.0
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
~ --TW4-0J -TW4:02
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
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
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
Ql 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2015 24569.2 1130 92994.4 l 05083696.9 105.1 0.23 24156.7 1840 91433.1 168236921.5 168.2 0.37
Q2 2015 23989.9 1260 90801.8 114410232.1 114.4 0.25 22029.9 1650 83383.2 137582233.0 137.6 0.30
Q3 2015 23652.0 1060 89522.8 94894189.2 94.9 0.21 21586.9 1310 81706.4 I 07035405.6 107.0 0.24
Q4 2015 20764.3 1040 78592.9 81736590.5 81.7 0.18 21769.8 2070 82398.7 l 70565294.5 170.6 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 1160 59097.1 68552633.1 68.6 0.15 17487.4 1780 66189.8 l 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 137434856.4 137.4 0.30
Q3 2017 17413.6 958 65910.5 63142236.0 63.1 0.14 19338.8 1310 73197.4 95888539.0 95.9 0.21
Q4 2017 14089.8 556 53329.9 29651420.5 29.7 0.07 17327.6 1610 65585.0 l 05591795.3 105.6 0.23
Table G-1
--· -·-·. ·-·--·----·· -· -.·---· ............. ··-··-~. ----··-. . . --·-··--..... -.. -··· -.... ---TW4-0l TW4-02 --·
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
01 2018 12505.7 70.4 47334.1 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.l 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
Q42019 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
Q3 2020 9487.3 1060 35909.4 38063996.3 38.06 0.08 14009.5 1260 53026.0 66812706.5 66.81 0.15
Q4 2020 9318.7 924 35271 .3 32590662.3 32.59 0.07 14582.9 l 130 55196.3 62371792.4 62.37 0.14
Ql 2021 9066.4 948 34316.3 32531875.2 32.53 0.07 13189.6 939 49922.6 46877355.2 46.88 0.10
Totals 358894.6 2.8 433758.8 5.2
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-11 TW4-21
. '' Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q22008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2009 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q22011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q42011 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
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
04 2015 4110.3 2730 15557.5 42471935.4 42.5 0.09 134774.9 339 510123.0 172931695.8 172.9 0.38
QI 2016 3676.2 2660 13914.4 37012349.2 37.0 0.08 125513.3 390 475067.8 185276457.8 185.3 0.41
Q2 2016 3760.4 3340 14233.1 47538600.8 47.5 0.10 132248.7 545 500561.3 272805924.6 272.8 0.60
Q3 2016 2953.8 3200 11180.1 35776425.6 35.8 0.08 110381.9 456 417795.5 190514744.1 190.5 0.42
Q4 2016 3050.2 3180 11545.0 36713122.3 36.7 0.08 130311.3 434 493228.3 214061069.4 214.1 0.47
QI 2017 2984.2 3310 11295.2 37387102.1 37.4 0.08 54333.5 598 205652.3 122980073.9 123.0 0.27
Q2 2017 2845.9 3370 10771.7 36300735.2 36.3 0.08 60969.7 224 230770.3 51692550.4 51.7 0.11
Q3 2017 2830.0 3290 10711.6 35240999.5 35.2 0.08 120116.2 537 454639.8 244141581.7 244.1 0.54
Q4 2017 2612.7 2880 9889.1 28480520.2 28.5 0.06 126492.5 466 478774.1 223108736.4 223.1 0.49
Table G·l
uuarter1v ca1cu1auon or cn1orororm Kemoveo a no Total VOiume or water t'umoea
. -TW4-I1 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)
01 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 25053331.4 25.1 0.06 110001.4 476 416355.3 198185122.3 198.2 0.44
Q4 2018 2379.5 2930 9006.4 26388774.0 26.4 0.06 121686.3 585 460582.8 269440914.0 269.4 0.59
QI 2019 2342.4 2820 8866.0 25002074.9 25.00 0.06 123264 323 466554.6 150697141.8 150.70 0.3
Q2 2019 2195.1 2970 8308.5 24676106.9 24.68 0.05 106893.6 734 404592.3 296970730.6 297.0 0.7
Q3 2019 2046.0 2790 7744.1 21606066.9 21.61 0.05 108132.9 596 409283.0 243932683.8 243.9 0.5
Q4 2019 1983.9 3250 7509.1 24404449.9 24.40 0.05 116167.55 794 439694.2 349117176.3 349.1 0.8
Ql 2020 1947.4 2990 7370.9 22039017.9 22.04 0.05 106622.01 844 403564.3 340608275.8 340.6 0.8
Q2 2020 2003.9 2810 7584.8 21313179.8 21.31 0.05 110999.13 767 420131.7 322241019.3 322.2 0.7
Q3 2020 1784.l 3070 6752.8 20731152.8 20.73 0.05 99515.11 920 376664.7 346531516.0 346.5 0.8
Q4 2020 1394.6 2670 5278.6 14093757.9 14.09 0.03 107061.16 948 405226.5 384154713.l 384.2 0.8
Ql 2021 2195.1 2750 8308.5 22848455.3 22.85 0.05 97211.49 400 367945.5 147178195.9 147.2 0.3
Totals 75076.8 1.8 2593238.9 11.7
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-37 TW4-39
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Ql 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2007 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2008 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2008 NA NA NA NA NA NA NA NA NA NA NA NA
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
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
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA
QI 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA
Ql 2015 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2015 29206.0 30200 110544.7 3338450242.0 3338.5 7.4 NA NA NA NA NA NA
Q3 2015 118063.9 19100 446871.9 8535252554.7 8535.3 18.8 NA NA NA NA NA NA
Q4 2015 111737.5 19500 422926.4 8247065531.3 8247.1 18.2 NA NA NA NA NA NA
Ql 2016 111591.0 17500 422371.9 7391508862.5 7391.5 16.3 NA NA NA NA NA NA
Q2 2016 119241.2 16200 451327.9 7311512660.4 7311.5 16.1 NA NA NA NA NA NA
Q3 2016 98377.6 15900 372359 5920511534.4 5920.5 13.1 NA NA NA NA NA NA
Q4 2016 101949.1 16400 385877 6328388433.4 6328.4 14.0 3598.3 2800 13620 38134783.4 38.1 0.1
QI 2017 97071.7 18000 367416 6613494921.0 6613.5 14.6 103117.8 6460 390301 2521343639.6 2521.3 5.56
Q2 2017 93191.3 15800 352729 5573119313.9 5573.1 12.3 41313.0 5560 156370 869415559 .8 869.4 1.92
Q3 2017 81749.3 15000 309421 4641316507.5 4641.3 10.2 34546.3 10000 130758 1307577455.0 1307.6 2.9
Q4 2017 87529.6 15500 331300 5135142808.0 5135.1 11.3 68180.2 552 258062 142450255.5 142.5 0.3
Table G-1
--· ·-· .. --· ---~--~ ~-• •,....-• ~ • ..,., • °'" • ._., ••~ • ........ .,., ,._. I ............ • ,..-, 'WI,, .... ._. .. I Y • _..__, 0 ... , I I ......... ~
-TW4-37 TW4-39
Total Total l C 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)
012018 84769.3 12900 320852 4138988226.5 4139.0 9.1 59262.2 2870 224307 643762315.5 643.8 1.4
Q2 2018 83653.1 14400 316627 4559428562.4 4559.4 10.1 34259.8 7160 129673 928461135.9 928.5 2.0
Q3 2018 77457.8 14100 293178 4133806599.3 4133.8 9.1 33473.4 8180 126697 1036379979 .4 1036.4 2.3
Q4 2018 76271.4 15200 288687 4388046184.8 4388.0 9.7 37003.6 6520 140059 913182241.5 913.2 2.0
QI 2019 77591 13300 293683.4 3905989871.7 3906.0 8.6 49117 885 185907.5 164528107.9 164.5 0.4
Q2 2019 64950.1 16200 245836.1 3982545281.7 3982.5 8.8 34285.7 8640 129771.4 1121224675.7 1121.2 2.5
Q3 2019 67572.0 11900 255760.0 3043544238.0 3043.5 6.7 36976.2 4240 139954.9 593408848.1 593.4 1.3
Q4 2019 66732.4 13100 252582.1 3308825955.4 3308.8 7.3 51808.6 1650 196095.6 323557659.2 323.6 0.7
Ql 2020 65554.2 12000 248122.6 2977471764.0 2977.5 6.6 43169.3 812 163395.8 132677390.0 132.7 0.3
Q2 2020 65163.8 11700 246645.0 2885746301.l 2885.7 6.4 37352.7 5870 141380.0 829900421.0 829.9 1.8
Q3 2020 56659.3 13800 214455.5 2959485216.9 2959.5 6.5 35628.2 5960 134852.7 803722312.5 803.7 1.8
Q4 2020 61323.9 10300 232111.0 2390742903.5 2390.7 5.3 46794.2 648 177116.0 114771198.5 114.8 0.3
Ql 2021 59907.4 9380 226749.5 2126910394.4 2126.9 4.7 38932.4 2970 147359.1 437656628.0 437.7 1.0
Totals 1957314.3 251.0 788818.8 28.5
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
Qµarter (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
Q42007 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.l
Q3 2010 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 376623.4
Q4 2010 NA NA NA NA NA NA NA NA NA NA NA NA 17.9 1041817.3
Ql 2011 NA NA NA NA NA NA NA NA NA NA NA NA 24.9 696533.0
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA 13. I 449131. l
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA 8.1 462334.5
Q4201 l NA NA NA NA NA NA NA NA NA NA NA NA 10.8 468706.3
Ql 2012 NA NA NA NA NA NA NA NA NA NA NA NA 10.6 448486.3
Q2 2012 NA NA NA NA NA NA NA NA NA NA NA NA 10.4 400415.2
Q3 2012 NA NA NA NA NA NA NA NA NA NA NA NA 6.6 390229.0
Q4 2012 NA NA NA NA NA NA NA NA NA NA NA NA 7.1 358000.0
QI 2013 NA NA NA NA NA NA NA NA NA NA NA NA 13.7 634286.1
Q2 2013 NA NA NA NA NA NA NA NA NA NA NA NA 13.5 768953.4
Q3 2013 NA NA NA NA NA NA NA NA NA NA NA NA 31. l 950505.6
Q4 2013 NA NA NA NA NA NA NA NA NA NA NA NA 10.3 990119.8
QI 2014 NA NA NA NA NA NA NA NA NA NA NA NA 8.6 859297.5
Q2 2014 NA NA NA NA NA NA NA NA NA NA NA NA 9.9 838057.9
Q3 2014 NA NA NA NA NA NA NA NA NA NA NA NA 10.2 852987.2
Q4 2014 NA NA NA NA NA NA NA NA NA NA NA NA 14.6 673905.9
Ql 2015 NA NA NA NA NA NA NA NA NA NA NA NA 9.9 458271.4
Q2 2015 NA NA NA NA NA NA NA NA NA NA NA NA 15.3 539592.9
Q3 2015 NA NA NA NA NA NA NA NA NA NA NA NA 33.4 816299.8
Q4 2015 NA NA NA NA NA NA NA NA NA NA NA NA 32.3 847567.8
Ql 2016 NA NA NA NA NA NA NA NA NA NA NA NA 30.6 819302.3
Q2 2016 NA NA NA NA NA NA NA NA NA NA NA NA 39.4 832418.9
03 2016 NA NA NA NA NA NA NA NA NA NA NA NA 24.7 686543.4
Q4 2016 NA NA NA NA NA NA NA NA NA NA NA NA 25.6 750667.4
QI 2017 NA NA NA NA NA NA NA NA NA NA NA NA 27.2 667899.1
Q2 2017 NA NA NA NA NA NA NA NA NA NA NA NA 19.6 657232.5
Q3 2017 NA NA NA NA NA NA NA NA NA NA NA NA 28.5 754250.l
Q4 2017 NA NA NA NA NA NA NA NA NA NA NA NA 16.9 841953.7
Table G-1
................. , •. ..-,oT _ ... ,_._,-.,_, ...... ,," • -·••'-''""' ..... '''' •"'""'"•••"W ...... OOWO. ...... 0 ........... ,.,...,...,., ,,._...__., ' ... ,,, -""
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)
012018 NA NA NA NA NA NA NA NA NA NA NA NA 18.0 810330.4
Q2 2018 NA NA NA NA NA NA 73711.2 1400 278997 390595648.8 390.6 0.9 20.1 803034.5
Q3 2018 NA NA NA NA NA NA 44981.6 1390 170255 236654734.4 236.7 0.5 17.6 733435.6
Q4 2018 NA NA NA NA NA NA 35431.6 1320 134108 177023110.1 177.0 0.4 20.8 800443.6
QI 2019 NA NA NA NA NA NA 31904 1220 120755.] 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 80190.5 I 13068638.8 l 13.I 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 0.31 17294.9 1220 65461.1 79862567.4 79.9 0.2 25.2 910974.8
Q3 2020 86264.50 333 326511.1 108728207.1 108.7 0.24 13411.4 1110 50762.3 563461 I 1.4 56.3 0.1 13.4 766734.5
Q4 2020 77535.9 264 293473.5 77477002.7 77.5 0.17 17765.7 1020 67243.3 68588115.2 68.6 0.2 9.6 82865 I .4
QI 2021 72543.4 436 274576.7 119715421.8 119.7 0.26 13407.5 1170 50747.3 59374310.5 59.4 0.1 16.8 759810.1
Totals 745581.2 2.1 335575.8 3.6 1270.2 48542390.0
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 TW4-01 TW4-02 TW4-11 TW4-21 TW4-37 TW4-39 TW4-40 TW4-41 Quarter
Ouarter* (lbs.) (lbs,) (lbs.) {lbs.)•• (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) Totals (lbs.)
QI 2007 36.8 12.9 150.2 87.0 NA NA NA NA NA NA NA NA NA NA NA NA 286.9 02 2007 1.4 0.1 0.0 2.5 NA NA NA NA NA NA NA NA NA NA NA NA 4.0
03 2007 2.2 0.8 2.9 3.1 NA NA NA NA NA NA NA NA NA NA NA NA 9.0
Q4 2007 1.7 1.0 3.1 4.8 NA NA NA NA NA NA NA NA NA NA NA NA 10.6
Qi 2008 1.7 0.4 4.6 7.2 NA NA NA NA NA NA NA NA NA NA NA NA 13.8
Q2 2008 1.3 0.5 3.2 9.9 NA NA NA NA NA NA NA NA NA NA NA NA 14.8
03 2008 1.2 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
QI 2009 1.7 0.4 4.3 3.6 NA NA NA NA NA NA NA NA NA NA NA NA 10.0
Q2 2009 6.8 0.2 3.7 2.8 NA NA NA NA NA NA NA NA NA NA NA NA 13.5
Q3 2009 1.5 0.4 I I.I 5.5 NA NA NA NA NA NA NA NA NA NA NA NA 18.5
04 2009 4.8 0.6 17.8 26.1 NA NA NA NA NA NA NA NA NA NA NA NA 49.4
0[ 2010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA NA NA NA 4.5
02 2010 1.5 1.0 6.8 5.9 1.4 NA NA NA NA NA NA NA NA NA NA NA 16.5
Q3 2010 1.3 l.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA NA NA NA 10.6
Q42010 I.I 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA NA NA NA 17.9
QI 2011 I.I 0.2 12.9 9.6 1.1 NA NA NA NA NA NA NA NA NA NA NA 24.9
Q22011 l.2 0.8 5.3 4.6 1.1 NA NA NA NA NA NA NA NA NA NA NA 13.I
Q3 2011 1.2 0.4 LI 4.1 l.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
012012 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
Q3 2012 I.I 0.7 1.4 2.4 I.I NA NA NA NA NA NA NA NA NA NA NA 6.6
04 2012 0.9 0.3 2.0 3.2 0.8 NA NA NA NA NA NA NA NA NA NA NA 7.2
01 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
03 2013 0.9 0.6 22.3 4.4 0.7 2.1 0.1 0.0 NA NA NA NA NA NA NA NA 31.1
04 2013 0.8 0.3 3.2 2.5 0.7 2.8 0.1 0.0 NA NA NA NA NA NA NA NA 10.3
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
Q22014 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
03 2014 0.9 0.4 3.6 1.8 0.8 2,5 0.1 0.0 NA NA NA NA NA NA NA NA 10.2
Q4 2014 0.8 0.4 7.1 3.2 0.6 2.5 0.04 0.0 NA NA NA NA NA NA NA NA 14.6
QI 2015 0.9 0.4 2.4 2.6 0.4 2.3 0.04 0.0 0.23 0.37 0.20 NA NA NA NA NA 9.9
02 2015 0.7 0.5 1.0 2.8 0.7 1.6 0.00 0.0 0.25 0.30 0.12 0.09 7.4 NA NA NA 15.3
Q3 2015 1.0 0.4 7.6 2.5 0.7 1.6 O.Q3 o.o 0.21 0.24 0.03 0.29 18.8 NA NA NA 33.4
Q420l5 l.O 0.4 7.4 2.2 0.6 1.5 0.02 0.0 0.18 0.38 0.09 0.38 18.2 NA NA NA 32.3
QI 2016 0.9 0.4 7.6 2.6 0.6 1.2 0.02 0.0 0.16 0.34 0.08 0.41 16.3 NA NA NA 30.6
Q2 2016 1.3 0.4 13.0 4.4 0.9 1.9 0.04 0.0 0.19 0.36 0.10 0.60 16.1 NA NA NA 39.4
03 2016 LO 0.5 5.2 2.4 0.6 I.I 0.01 0.0 0.15 0.26 0.08 0.42 13.1 NA NA NA 24.7
=2016 l.O 0.4 5.8 2.3 0.4 0.7 0,017 0.0 0.19 0.26 0.08 0.47 14.0 0.1 NA NA 25.6
QI 2017 0.9 0.3 1.1 2.6 0.3 I.I O.Q\5 0.0 O.D7 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
Q4 2017 1.2 0.6 0.1 1.4 0.2 0.9 0.014 0.0 O.D7 0.23 0.06 0.49 11.3 0.3 NA NA 16.9
Ql 2018 1.2 0.3 2.4 1.8 0.2 0.9 0.020 0.0 0.01 0.10 O.D7 0.41 9.1 1.4 NA NA 18.0
Q2 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.l
Q3 2018 1.0 0.4 1.7 l.l 0.1 0.6 0.016 0.0 0.08 0.12 0.06 0.44 9.J 2.3 NA 0.5 17.6
Q420l8 1.1 0.3 4.7 l.O O.l 0.5 0,018 0.0 0.06 0.11 0.06 0.59 9.7 2.0 NA 0.4 20.8
QI 2019 I.I 0.2 2.0 l.9 0.1 0.9 0.023 0.0 0.01 0.14 0.06 0.33 8.6 0.4 NA 0.3 16.2
Q2 2019 1.0 0.3 9.7 1.5 0.1 0.9 0.013 0.0 0.08 0.16 0.05 0.65 8.8 2.5 0.18 0.3 26.l
03 2019 0.9 0.3 5.6 1.2 0.1 0.7 0.014 0.0 0.07 0.09 0.05 0.5 6.7 1.3 0.37 0.2 18.3
04 2019 I.I 0.3 0.5 0.6 0.1 0.8 0.037 0.0 0.08 0.11 0.05 0.8 7.3 0.7 0.28 0.2 13.0
QI 2020 I.I 0.2 7.0 I.I 0.1 0.8 0.044 0.0 0.09 0.21 0.05 0.8 6.6 0.3 0.31 0.2 18.9
TableG-2
Chloroform Mass Removal Per Well Per Quarter
'TW4'1S
MW~ (MW-26) TW4-19 TW4-20 T\\'4-4 TW4-Z2 TW4-24 TW4-2S 'TW4-01 TW4-02 TW4-ll TW4-2l TW4-37 TW,4-39 TW440 TW4-4.l Quarter ouartlr• (lbs.) (lbs.) (I~.) ,(lbs.)" ,(lbs.) (lbs.) (Lbs.) {l.m.) (lbs.) (I~) (Jbs.)' (lbs.) (lbs.) (lbs.) (lbs.) (lb$.) Totals (lbs.)
Q22020 1.1 0.3 8.7 4.9 0.1 0.5 0.024 0.0 0.04 0.13 0.05 0.7 6.4 1.8 0.31 0.2 25.2
Q32020 0.9 0.2 1.7 0.0 0.1 0.7 0,028 0.0 0.08 0.15 0.05 o.s 6.5 1.8 024 0.1 13.4
Q.1 2020 0.8 0.2 0.8 o.o 0.1 0.7 0.063 0.0 0.07 0.14 0.03 0.8 5.3 0.3 0.17 0.2 9.b
QI 2021 0.9 0.7 7.4 0.0 0.1 1.0 0.066 0.0 om 0.10 0.05 0.3 4.7 1.0 0.26 0.1 16.8
Well Tolals 107.9 38.2 449.5 296.2 26.0 44.3 1.2 0.0 2.8 S.2 1.8 11.7 251.0 28.5 2.1 3.6 1270.2
* QI 2007 represents the cumulative total priQr to u.nd including Qi 2007.
** TW4-20 collapsed in August 2020 and was abandoned on October I, 2020
Table G-3 Well Pumping Rates and Volumes
Volume of Water Pumped
Pumping Well Name During the Quarter (gals) Average Pump Rate (Jl:Pm)
MW-4 93486.7 4.0
MW-26 27898.0 16.2
TW4-19 133462.3 16.0
TW4-4 13740.8 16.6
TWN-2 23310.5 16.7
TW4-22 22605.6 17.2
TW4-24 81891.2 16.3
TW4-25 80272.2 10.8
TW4-0l 9066.4 12.7
TW4-02 13189.6 16.4
TW4-ll 2195.1 15.5
TW4-21 97211.5 16.6
TW4-37 59907.4 18.0
TW4-39 38932.4 18.0
TW4-40 72543.4 18.0
TW4-41 13407.5 5.9
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Volume Pumped by Quarter (gal.)
12000000.0 ~------------------------------
10000000.0 -----------------------------------------------
8000000.0 +-.---------------------------------------------
6000000.0 -+-11---------------------------------------------
4000000.0 -----------------------------------------------
2000000.0 -----------------------------------------------
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20072007200820082009200920102010201120112012201220132013201420142015201520162016201720172018201820192019202020202021
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 N 0 00 I.D s:t N .-t .-t
...... ...... "' "' w u, 0 u, 0 u, 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0
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Q3 2015
Q4 2015
Ql 2016
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Q2 2020
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.... ....
N .i:,. en 00 0 N 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
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Q3 2010
Q4 2010
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Ql 2021
I-' I-' N .IS, O'I 00 0 N 0 0 0 0 0 0 0 0 0 0 0 0
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Q2 2016 1 I 11 I I I I -I ~
Q3 2016 I I #{ I I I I .i::. I ....
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012011 I I t I I I I I ~ -C
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MW-26 Volume Pumped by Quarter (gal.)
1000000
I 900000
800000
700000
600000
500000
400000
300000
200000
100000 ~~ _....
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& &
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Ql 2007 represents the cumulative total prior to and including Ql 2007.
8000000 ~=======----==~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
TW4-19 Volume Pumped by Quarter (gal.)
7000000 +--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
6000000 .Ll~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
5000000 -+-t,--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
4000000 .L..JL--~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
3000000 l-l-~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~~
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20072007200820082009200920102010201120112012201220132013201420142015201520162016201720172018201820192019202020202021
Ql 2007 represents the cumulative total prior to and including QI 2007.
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I-' I-' N N w l/1 0 l/1 0 l/1 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
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Laboratory Analytical Reports
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: l st Quarter Chloroform 202 l
LabSampleID: 2102631-0llC
Client Sample ID: MW-04_02232021
Collection Date: 2/23/202 l 1208h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/25/202 l 1250h Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
,alt Lake City, UT 84119
Analyzed: 2/26/202 l 1452h
Units: µg/L
Compound
Chloroform
Phone: (80 I) 263-8686 Surrogate Units: µg/L
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
Surr: l,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 4,970 5,000 99.4
460-00-4 5,040 5,000 IOI
1868-53-7 ~,980 5,000 99.5
2037-26-5 5,140 5,000 103
SW8260D
Analytical
Result Qual
1,150
Limits Qual
80-136
85-121
78-132
81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1254h
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 Qua]
< 1.00
< 1.00
< 1.00
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 58.5 50.00 117 80-136
460-00-4 44.9 50.00 89.8 85-121
1868-53-7 59.0 50.00 118 78-132
2037-26-5 51.7 50.00 103 81-123
Report Date: 3/ I 0/2021 Page 32 of 46
All anal~ ses applicJblc lo the CW A. SDW A. and RCRA are perfom1ed in accordance lo NE LAC protocols Pertinenl sampling infonnru.ion is located on the allached COC Confidential Business lnfonnation: This rcpor1 is pro\'ided for the exclusi, e use or the
~ddressee Pri\ ile~es o_f sub...5eq~enl ~~e or the ~~1e or this .co~pany or an~ ~mber or ils staff, or repmductio~ ~rthis repo~ in .con~ection .. with the ~,•ertisernenl. P~?motio.n or ~aJe of!"~~~ ~1och~cl or p~ocess, ~r in ~onn~.tion w!lh th: r~·publicnlion or lhis report
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-011
Client Sample ID: MW-04_02232021
Collection Date: 2/23/2021 1208h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride
Nitrate/Nitrite (as N)
mg/L
mg/L
Date
Analyzed
3/6/2021 830h
3/l /2021 1256h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 46.5
E353.2 0.100 4.61 ---
Report Date: 3/ I 0/2021 Page 16 of 46
All analyses applicable lo the CWA. SOWA. Md RCRA are perfom1ed in accordance to NELAC protocols Pertinenl sampling informalion is localed on the aflached COC Confidential Business lnformalion: This repon is prO\•ided for 1he e.xclush e use of the
~ddressee. Pri\·ile~es of sub__seq~nt ~e of lhe ~~ne of this .con:ipany or nny 1~ml>er of its stnff, or reproducli~! ~f lhis repo~ in ~1~1ection ... ,,i1h the a~vertisemenl, p~omoli°:41 or sale of ~!Y ~rodl~CI or p~ocess, ~r in ~"~!ion ,,·!lh 1h7 r:p~blicalion or 1his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 210263 l-007C
Client Sample ID: TW4-0l~02232021
ANAL vr1 cA L L Ano RAT oR Its Collection Date: 2/23/2021 1216h
3440 South 700 West
,alt Lake City, UT 84119
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1333h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENI00
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 948
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
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
499
510
510
521
--The reporting limits were raised due to high analyle concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1 I 36h
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 99.9 80-136
500.0 102 85-121
500.0 102 78-132
500.0 104 81-123
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 57.2 50.00 114 80-136
Surr: 4-Bromofluorobenzene 460-00-4 48.4 50.00 96.9 85-121
Surr: Dibromofluoromethane 1868-53-7 57.3 50.00 115 78-132
Surr: Toluene-d8 2037-26-5 51.8 50.00 104 81-123
Report Date: 3/10/2021 Page 28 of 46
All an;ilyses applicable to 1ho tW A. SOWA. and RCRA nre performed in accordnnce lo NELAC protocols. Pertincol sampling inlonnotion is located Oil the oll:1ched COC Confidential Business Information: This report is pro,·ided for the e.,._;clusi, e use of the
~ddressee. Pri,·ite~es of S11~~Wfll ~~e of the ~~h! of this .cm~1prmy or ru,~· ~mber of ils stall, or reproductio~ ~f this repo~ in .con~ection~ with Lhe a~~ertisem~nl. p~molio.n or sale of :U!Y ~rod~cl or p~o~s, ~r in ~nn~c!ion \\'~th th~ r:-publicalion of !his report
American West ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2102631-007
Client Sample ID: TW4-01_02232021
Collection Date: 2/23/2021 1216h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite ( as N) mg/L
Date
Analyzed
3/3/2021 455h
3/1/2021 1249h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua!
E300.0 1.00 45.4
E353.2 0.100 2.72
Report Date: 3/ I 0/2021 Page 12 of 46
All ana.l)ses applicable lo 1he CWA. SOWA. and RCRA are performed in accordance to NELAC protocols, Pertinent sampling information is locoted on the attached COC Confidentiol Business Jnformalion: This report is pro\'ided f'or the e.'l'.clusi\'e use of the
~ddressee Pri, ile~es o.r sub ... seq~enl ~~e of 1he ~~e of this .co1~pany or any ~'!1ber of its slaIT, or reproduclio~ ~~ lhis repo~ in ~n~eclion ... \\ilh the u~,·ertisement, p~omoti~n ~r saJe of~~. ~rod~ct or p~ocess, ~r in ~nn:c!ion \\'!th th~ r:-p~blication of this report
ORGANIC ANALYTICAL REPORT
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 202 I
Lab Sample ID: 2102631-012C
Client Sample ID: TW4-02_02232021
Collection Date: 2/23/2021 I 026h
Received Date: 2/25/2021 1250h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/26/2021 1514h
Units: µg/L Dilution Factor: 100 Method: SW8260D
3440 South 700 West
;aJt Lake City, UT 84 I I 9 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-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 939
Result Amount Spiked %REC Limits Qual
4,960 5,000 99.2 80-136
5,070 5,000 101 85-121
5,080 5,000 102 78-132
5,180 5,000 104 81-123
--The reporling limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1313h
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:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Method:
CAS
Number
Reporting
56-23-5
74-87-3
75-09-2
Result Amount Spiked
59.2 50.00
49.1 50.00
58.9 50.00
52.3 50.00
Limit
1.00
1.00
1.00
%REC
118
98.1
118
105
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
80-136
85-121
78-132
81-123
Report Date: 3/10/2021 Page 33 of 46
All anal) ses applicable lo the CW A. SOWA. and RCRA are perfonned in accordance to NELAC protocols Pertinenl sampling informal.ion is locnled on the auached COC Conlidential Business lnfo1 mation: This report is provided for the exclusi, e use of the
~ddressee. Pri, ile~es of sub~seq~enl ~~e or1he ~~e orlhis .crn~pany or ml) ~':"ber ofils sin.IT, or reproducti~ ~flhis repo~ in ;oo?eclion_ \\ith Lhe ™!:ertisemenL P~?motio_n o_r sale of ?-'!Y ~1odl!cl or p•;?Cess, ~r in 7°nn1;c~ion w!lh 1h~ r:-publicaJ.ion of lhis report
American West
ANALYTICAL LAB0RATORIE6
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!·mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2102631-012
Client Sample ID: TW4-02_02232021
Collection Date: 2/23/2021 1026h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/6/2021 802h
3/1/2021 1257h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 43.3
E353.2 0.100 3.30 ----
Report Date: 3/10/2021 Page I 7 of 46
All anal) ses applicable lo the CWA. SDWA. and RCRA are performed in accordance lo NELAC protocols.. Pertinenl sampling information is located on lhe attached COC Confidential Business Jnfonnation: This report is provided for the e.'l:clusi,e use of the
~ddressee, P1i,·ile~es o,f sub .. seq~ent ~e of lhe ~~e of this .cm~pany or any n~mber of its s1aff, or reproductio~ ~f this repo~ in ~on~eclion .. with the a~vertisemenl, P~?moli~ or sale of ?J!Y ~rodt~I or p~ocess, ~r in ~nn~c~ion w~lh 1h~ r~-publicaJ.ion or lhis report
American West
ANALYTICAL LA80 RATORl£8
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-002C
Client Sample ID: TW4-03 _ 03172021
Collection Date: 3/17/2021 732h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1123h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: ~tg/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-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
48.6 50.00 97.2 80-136
47.4 50.00 94.7 85-121
47.9 50.00 95.7 78-132
47.4 50.00 94.9 81-123
Report Date: 3/31/2021 Page 32 of 65
All analyses applicable to lhe CWA, SDWA. and RCRA are performed in accordance to NELAC protocols Per1inenl sampling infonnalion is located on lhe attached COC Connctentiul Business lnformalion: This report is prm•ided for the exclusil"e use of the
~ddressee Pri,·ile~es o,r sub .. scq~ent ~~e of lhe ~~e of this .co1~pany or nny ~';'ber of ils stafT, or reproductio~ ~f this repo~ in .con~ection_. "ith the ~vet1isemenl. P~?moLio.n or sale of ~!Y ~rod~cl or p~ocess, ~r in ~nn~c!ion w!lh 1h7 r~-p~blicu.1ion of this report
American West
ANALVTICAL LAB0RAT0RIE8
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-002
Client Sample ID: TW4-03 _ 03 l 7202 l
Collection Date: 3/17/2021 732h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 1840h
3/20/2021 1228h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 28.4
E353.2 0.100 6.19
Report Date: 3/31/2021 Page 8 of 65
All Ma.lyses applicnble to lhe CWA. SOWA. Md RCRA are perf'omled in accordance 10 NELAC prolocols. Peninenl snmpling inrormation is located on the Rllnc:hed COC. Conrichmtinl Business lnformntion: This report is pro"ided for theexclushe use of the
~ddressee Pri, ile~es o:sub .. seq~tenl ~~e of the ~~e of lhis .co1~pn1\y or M~ 1~mbor of its stnrf, or reproductio~ ~~this repo~ in .con~ection,. ,,ith the n~~ ertise1!1ent. P~?motio1n ~r sale of ~!Y. fodl~Cl or P~?cess, ~r in ~nn~.tion '''!lh th~ r~·publication of lhis repon
American West ANALYTICAi LABORATORlfB
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: I st Quarter Chloroform 2021
Lab Sample ID: 2103541-00lC
Client Sample ID: TW4-03R_03162021
Collection Date: 3/16/2021 8 I 5h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1104h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 1.69
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
48.3 50.00 96.6 80-136
48.1 50.00 96.2 85-121
47.9 50.00 95.7 78-132
47.7 50.00 95.3 81-123
Report Date: 3/31/2021 Page 31 of 65
All annlyses applicnble to the CWA. SOWA. tu1J RCRA are performed in accordance 10 NELAC protocols, Pertinent sampling information is located on the nllached COC Confidenlial Business Information: TI1is report is provided for the exclusiYe use of the
~ddressee. Prfrile~es o! su~seq~ent ~~e of the !~?'.ne.o(lhis .co~pnny or an) ~mber of its staff, or reproductio~ ~~ this repo~ in ~on~ection .... \\·ith lhe a~,·ertisement, P~?mo1io.n or saJe of ~!Y ~rod~cl or P~?cess, ~r in ?>1m~c)ion \\'!th 1h~ r1;·publication of this repon
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: (80 l) 263-8687
!-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-001
Client Sample ID: TW4-03R_03162021
Collection Date: 3/16/2021 815h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 1812h
3/20/2021 1227h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 3/31/2021 Page 7 of65
All a.nnlyses applicnble 10 1he CWA. SDW ~ n.nd RCRA are perlonned in accordance 10 NELAC protOC"o, r~r1m~u somplin,S: inlbt1nAt.ion is locnted on the nttnched COC. Conndenlinl Business lnformotion: This repon is provided for 1he, e..'<<'l~ire use, of lhe
~ddressee. Pririle~es of ,1~q~ent ~;e of1hc ~~1oor lhis .cm~pany or any ,~~ber of Its slnlT, or rcproducti~ ~r1his ri:i~ in ,con~u:clion ... with the n~venise~ent. P~?motio.n ~r ~ale of ~!Y. ~rodl~ct or p1:~ess, ~r in ~onn~c!ion w!lh 1h~ ";·publica1lon ol' this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
LabSampleID: 2102631-009C
Client Sample ID: TW4-04_02232021
ANALvr1 cAL LAB0RAT0R1Es Collection Date: 2/23/2021 1235h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1412h Extracted:
Units: µg/L Dilution Factor:
3440 South 700 West
;;alt Lake City, UT 84119 Compound
Chloroform
---
Phone: [phone] Surrogate Units: µg/L CAS
Toll Free: [phone] Surr: 1,2-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
100
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qua!
67-66-3 100 1,130
Result Amount Spiked %REC Limits Qual
5,030 5,000 101 80-136
5,150 5,000 103 85-121
5,050 5,000 101 78-132
5,260 5,000 105 81-123
--The reporting limits were raised due to high ana/yte concentrations.
web: www.awal-labs.com Analyzed: 2/26/2021 1215h Extracted:
Units: µg/L Dilution Factor: Method: SW8260D
Kyle F. Gross CAS Reporting Analytical
Compound Number Limit Result Qual
Laboratory Director
Carbon tetrachloride 56-23-5 1.00 < 1.00
Jose Rocha Chloromethane 74-87-3 1.00 < 1.00
QA Officer 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 54.5 50.00 109 80-136
Surr: 4-Bromofluorobenzene 460-00-4 44.1 50.00 88.1 85-121
Surr: Dibromofluoromethane 1868-53-7 53.9 50.00 108 78-132
Surr: Toluene-d8 2037-26-5 48.5 50.00 97.0 81-123
Report Date: 3/10/2021 Page 30 of 46
All amil) ses applicable 10 lhe CWA. SOWA. and RCRA me performed in accordance 10 NELAC protocols, Pertinent sampling informolion is loc:ited ot1 the au ached COC Confiden1ial Business lnfonnation: This relX,Jrt is pro,·ided for the exclusi,·e use of the
~ddressee P1l, ile~es of sub~seq~tenl ~~e of the ~~e of this .co1~pany or :m~· ~mber of its slnff, or reproduclio~ ~f !his repo~ in ~n~eclioo~ with 1he a~vertisement, P~?moli°:° ~r sale of~~~ r1od~ct or P~?Cess, ~r in ~oon~~on \\'!Lh th~ r~-p~blicll.lion of lhis repon
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratmy Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-009
Client Sample ID: TW4-04_02232021
Collection Date: 2/23/2021 1235h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 550h
3/1/2021 1254h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 39.8
E353.2 0.100 6.75 ---
Report Date: 3/ I 0/2021 Page 14 of 46
All analyses applicable lo the CWA, SOW A. and RCRA are perfomted in accordance to NELAC protocols. Pertinenl sampling informarion is located on the auached COC Confidenlinl Business Information: This report is prO\•ided for 1he exclush e use of the
~dressee J>ri,·ile~es o! sub .. seq~enl ~~e of the ~~1.ne of this .co~pany or an) ~mber of its staff, or reproductio!~ ~f this repo~ in ~on~ection,. with the a~~·ertise1~1enL p~~motio.n ~r saJe of~!~. ~rod1~c1 or P•.ocess, ~r in ~nm;c!ion ,,·!th 1h~ r~·p~blication or !his report
American West ANALYTICAL LABOAATORlfl
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2103541-0I8C
Client Sample ID: TW4-05 _ 03 I 82021
Collection Date: 3/18/2021 853h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1154h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-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 12.9
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
48.6 50.00 97.1 80-136
47.2 50.00 94.5 85-121
48.4 50.00 96.7 78-132
47.6 50.00 95.3 81-123
Report Date: 3/31/2021 Page 48 of 65
All nnnlyses epµlicnble lo lhe CWA. SDWA. Md R RA ore perlbnncd in acc.."<'l'-0.nnt:e to NELAC protocols. renhu:nt semplmy; informntion is localed on the nttnched COC. C'Of\011\.'ntinl Business Information: This n.,pon is provided ror 1he exclusire use of the
~ddressee. Pririle~es of sub .. seq~ent ~1~e of lhe ~~~ or this .cOl~pol\11' or ru1y 1!!;'"bcr of its stnJT, or reproducllo~~ ~fthis rcpo~ in .con~1ection .. "~th the u~~'ertise~1ent. P~?motio.n ~r !Ble of ?J!>'._~rodl~cl or p1:?Cess, ~r in ~nn~c~io11 w!lh lh~ r~·Pl!blicn1io11 or this reporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-018
Client Sample ID: TW4-05 _ 03 l 8202 l
Collection Date: 3/18/2021 853h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/202 1 548h
3/20/2021 1257h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 46.0
E353.2 0.100 7.43
Report Date: 3/31/2021 Page 24 of 65
All analyses applicable lo lhe CWA, SOWA, and RCRA are perfom1ed in accordance to NELAC protocols. Pertinenl sampling information is located on the allached COC Confidential Business Information: This report is prO\·ided for the e.xclusi,e use of the
~ddressee Pri\·ile~es o~ sub~seq~nt ~~e of lhe ~~e of lhis .co1~pany or oor 1~'!1ber of its staff, or reproduclio~ ~f this repo~ in .con~eclion~ \\ilh the a~~·enisemenl, p~motio,n or sale of ~~y ~rod~cl or p~ocess, ~r in ~nn~!ion \\'!lh th~ r:_-p~blication of this repon
American West ANALYTICAL I A80~ATORIE8
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-016C
Client Sample ID: TW4-06 _ 03 l 8202 l
Collection Date: 3/18/2021 834h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 838h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 3.78
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-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
48.7
47.6
48.2
47.4
50.00 97.4 80-136
50.00 95.3 85-121
50,00 96.4 78-132
50.00 94.9 81-123
Report Date: 3/31/2021 Page 46 of 65
All anal) ses applicable lo the CWA. SOW A. and RCRA nre l)erfonned in Rccordance to NE LAC protocols. romnmt somp1iny informlltion is locnted on the nttoched COC. Confidenlinl Business lnrormotion: This report is provided for Iha exclmh·e Uk of the
~ddressee. P1ivile~es o_r su~se~~ent ~~e of lhe ~~e of I his .co1~po11~, or nny 1~mber of ils slnff, or reproducll~~ !?'this r~•! in fOll)leclion ... \\·ilh lhe n~~·ertise"!lent. P~?molio.n ~r sale of ~!Y ~rodl~CI or p1:ocess, ~r in ~nn~!io1l \\'!lh th~ r~·P\!blico.tion of this report
American West ANAI.VTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 841 I 9
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-016
Client Sample ID: TW4-06_03182021
Collection Date: 3/18/2021 834h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 30 I h
3/20/2021 1255h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 41.6
E353.2 0.100 0.205
Report Date: 3/31/2021 Page 22 of 65
All anal) ses applicable to the CWA. SOW A. and RCRA are performed in accordance 10 NELAC protocols, Per1inent sampling inforrnation is located on Lhe a.llached COC ConfidenLiol Business lnformulion: This repon is provided for the exclush e use of the
~ddressee Privile~es of' sub,_seq~enl ~~e of the ~?1,11e of this .con:ipnny or M) ~mber of its stafT, or reproductio~ ?,~ this repo~ in .co~eclion~ ,vith the o~vertise~ent, P~?moli~n or sa1e of ~;r ~rod~cl or p1:ocess, ~r in ~nn:c!ion \\'!lh th~ r~-publication of this report
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2103706-006C
Client Sample ID: TW4-07 _ 03242021
Collection Date: 3/24/2021 848h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/26/2021 2034h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 875
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
495
487
495
483
--The reporting /imils were raised due to high analyle concentralions.
Analyzed: 3/25/2021 1656h
Units: µg/L
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
500.0
500.0
500.0
500.0
99.0 80-136
97.4 85-121
99.0 78-132
96.6 81-123
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 56.3 50.00 113 80-136
Surr: 4-Bromofluorobenzene 460-00-4 43.5 50.00 87.0 85-121
Surr: Dibromofluoromethane 1868-53-7 48.8 50.00 97.6 78-132
Surr: Toluene-dB 2037-26-5 53.2 50.00 106 81-123
Report Date: 3/31/2021 Page 18 of29
All anolyses applicable Lo lhe CWA, SOWA. Md RCRA w·e performed in accordance to NELAC protocols. Pe11lnmt s11rn,~iriy infornmlion is located on the attached COC. Confid~ntinl Business Jnformalion: This reporl is provided fbrth" e.xclu.s:h·e use or the
~ctdressee. P1ivile~es of sub .. se,,~enl ~1~e or the ~~1e orlhis
1
co1~pany or nny i~mber of its storr, or reproduc11~ ~r1his repo~ in .con~1eclion" with the n~!·ertise~ent, P~?moti~n a/ sllle or~!): ~rodl~ct or p1:ocess, ~r in ~nn~!ion w!th lh~ t~·µ~blico1ion 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-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2103706-006
Client Sample ID: TW4-07 _03242021
Collection Date: 3/24/2021 848h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 450h
3/30/2021 I 006h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 46.2
E353.2 0.100 4.25
Report Date: 3/31/2021 Page IO of 29
All annlyses applicable to lhe CWA. SOWA, and RCRA Qle performed in BCcordance 10 NELAC protocols. Pertinenl sampling information is located on the oUnched COC. Conftd~nti"I Business lnformo.tion: This report is provided for the oxclusi\"e use of the
~ddressee Ptl\'ile~es o_f sub .. seq~tent ~1~e of lhe ~~1e of this .co".'pany or nnr ~'?1be1 of its slnrf, or reproductio~ ~! this repo~ in fDll~ection .. ,\-ilh lhe n~~'ertisement, P~?molio.n ~r sale of ~!Y ~rod~cl or p1.?Cess, ~r in ':°n™:C)ion \\'!llt th~ ri;-p~blicolion 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-020C
Client Sample ID: TW4-08_03182021
Collection Date: 3/18/2021 912h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1233h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua!
56-23-5 1.00 < 1.00
67-66-3 1.00 26.9
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
48.5
48.3
48.5
47.5
50.00 96.9 80-136
50.00 96.6 85-121
50.00 97.0 78-132
50.00 94.9 81-123
Report Date: 3/31/202 I Page 50 of 65
All Mnlyses applicahh: to 1hi: CWA. SDWA. and RCRA ore µerl'om,ect in accordance to NELAC protocols. Pertinent sampling information is located 01, the a\lached COC. Confidcntinl Business lnfonnulion: This repor1 is provided ror ,m, o,~chsi\o LKC of the
~ctdressec. P1frilt~"tl-Of "\1~q~1enl ~?e of the ~~1e of I his _co1~pn11y or cmy l~~ber or ils stnff, or reproductio~ ~~ this repory in ~011~1ection,, \\ilh the n~~•el1ise1~enl, P~?mo1i~n ~r ~nlc of ~!Y. ~rodl~Ct or p1:?cess, ?r in ~onn!c.tion with th~ ~-publ1C'Cli<M1 of 1his report
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-020
Client Sample ID: TW4-08_03182021
Collection Date: 3/18/202 I 912h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L ----
Date
Analyzed
3/25/202 1 644h
3/20/2021 1259h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 52.8
E353.2 0.100 1.00
Report Date: 3/31/2021 Page 26 of 65
All analyses applicable to the CW A. SOWA, and RCRA nre performed in accordance lo NELAC protocols Pertinent sampling information is located on the altache.d COC. Conftdenlial Business lnformnlion: This report is pro\'ided for lhe e.xclushe use of the
~ddressee Pri\ ile~es of sub~seq~ent ~~e or lhe ~~e of this _co1~po.ny or any "2:mbe1 of ils slaff, or reproductim~ ~f this repo~ in ~01~1eclion~ wilh the n~~enise~nt, P~?motio.n ~r saJe of :U~)" ~rod~t or P~?cess, '?r in -:onn~~io,1 w!lh lh~ r~-publication or this 1eport
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chlorofonn 2021
Lab Sample ID: 2103541-019C
Client Sample ID: TW4-09 _03182021
Collection Date: 3/18/2021 858h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1214h 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-Bromotluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 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 39.0
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
49.0 50.00 98.0 80-136
48.3 50.00 96.6 85-121
49.0 50.00 98.1 78-132
48.1 50.00 96.1 81-123
Report Date: 3/31/202 1 Page 49 of 65
All unnlyses oppl1cnble to the CWA. SOWA. M<I R<.~RA are p,·rformed in accordance to NELAC protocols. Pe11inent snm1,Un!I' informn1lou is located on the attached COC. C'onfidentinl Busirms Informntion: This rc,pon is provided (or lhc exclut:h'(I use or the
~ddressee. Pri\'ilt~tl o,rsuh..5eq~1en1 ~1~e ofllit !~~~" uflhis .cQ1~lPlll\\ or My 1~'!1ber of its stnJT, or reproduclio~ ~f lhis rq)O~ in f011~\CCUoo .. ,villi the a~ver1ise1~ent, P~?moti~n ~r ~nle of :U!)'. J,M'O<h~ct or p1:?cess, ~r in ~nn~c~ion w!th lh! r~·l)1,1blic~tion or1his report
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-019
Client Sample ID: TW4-09 _ 03182021
Collection Date: 3/18/2021 858h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 616h
3/20/2021 1258h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 40.7
E353.2 0.100 1.06
Report Date: 3/31/2021 Page 25 of65
All anlll)'ses applicable to lhe CWA. SOWA, and RCRA are performed in accordance to NELAC protocols, Pertinenl sampling information is located on the aflached COC Confidential Business (nforrnnlion: This report is pro"ided for lhe es.clusiYe use or the
~ddressee. Pri, ile~es o~ sub .. seq~nt ~~e of lhe ~~e of lhis .con;'p::my or any ~';lber of its slafT, or reproducti~ ~f lhis repo~ in ~ot~ection .. \\·ilh Lhe o~ven.isemenl, p~omotio_n or sale of ~!Y ~rodl~t or p~ocess, ~r in ~1m:<=!ion \\·!th lh~ r~-publicalion of this report
ORGANIC ANALYTICAL REPORT
American West ANALYTICAL I ADORATORlfS
3440 South 700 West
~alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-005C
Client Sample ID: TW4-10_03242021
Collection Date: 3/24/2021 840h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/26/2021 2015h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
CAS 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-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 718
Result Amount Spiked %REC Limits Qual
489 500.0 97.8 80-136
473 500.0 94.6 85-121
490 500.0 98.0 78-132
479 500.0 95.8 81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/25/2021 1637h
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: 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
CAS Result Amount Spiked %REC Limits Qual
17060-07-0 55.7 50.00 111 80-136
460-00-4 45.5 50.00 91.0 85-121
1868-53-7 52.1 50.00 104 78-132
2037-26-5 52.6 50.00 105 81-123
Report Date: 3/31/2021 Page 17 of29
All nnnlrses applicnble to the CWA. SOWA. Md RCRA ore l)erfom1ed in nccordance to NELAC 1>101acol1. Per1inent s11mpllns_ informntion is located 011 the aUoched COC. Confidentlnl Business lnformnlion: This report is provided for the c.1«l1td\"ei u c of the
~ddressee. Pii,·ile~es o_f sub,.5eq~1enl ~1~e or the ~~1e of this 501~pn11y or MY '~'?1ber of its slnff, or te1,roduclio~ ~r lhis ,~ in ~011~1ecLion .. with the n~~·ertise~ent, P~?rnotio.n ~r sale of ~!Y ~rod~ct or p~~ess, ~r in ~onn~c!ion "'!th 1h7 r~-p~blk1nion or Lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-005
Client Sample ID: TW4-10_03242021
Collection Date: 3/24/2021 840h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 422h
3/30/2021 I 005h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua!
E300.0 1.00 58.1
E353.2 0.100 7.20
Report Date: 3/31/2021 Page 9 of 29
All nnolyses applicnblc to 1he CWA. SOWA, Md RCR.A 01e perfom1ed in accordance to NELAC protocols. Peninent s1nipl111i inConnntion is locnted on the attnched COC. Conlidentiol Business lnformnlion: This repon is pro\'ided for lhe exclusi\·e use of the
~ddressee. Privile~es orsul~q~enl ~1~e or th ~~~~k3 o( I his .cot~pany or nny 1~mber or its stofr, or reproductio~ ~~this rcpo~ In .con~eclion,. ,vilh lhe ~~·erlisement, P~?motio,n ~r saJe of !ll!Y ~rod~ct or p~ocess, ~r in ~onn!c~ion w!th th~ r~-publicatio11 of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2I02631-0 l 3C
Client Sample ID: TW4-I 1_02232021
Collection Date: 2/23/202 I IO 16h
Contact: Tanner Holliday
Received Date: 2/25/2021 1250h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;alt Lake City, UT 84119
Analyzed: 2/26/2021 1533h
Units: µg/L
Compound
Chloroform
Phone: [phone] Surrogate Units: µg/L
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: 100 Method:
CAS Reporting
Number Limit
67-66-3 IOO
CAS Result Amount Spiked %REC
17060-07-0 5,040 5,000 101
460-00-4 5,150 5,000 103
1868-53-7 5,020 5,000 100
2037-26-5 5,270 5,000 105
--The reporting limits were raised due to high analyle concentrations.
web: www.awal-labs.com Extracted: Analyzed: 2/26/2021 1332h
Units: µg/L Dilution Factor: Method:
Kyle F. Gross
Laboratory Director
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
---
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
CAS
Number
56-23-5
74-87-3
75-09-2
Reporting
Limit
1.00
1.00
1.00
Result Amount Spiked %REC
55.6 50.00 111
45.6 50.00 91.1
55.4 50.00 111
49.0 50.00 98.1
SW8260D
Analytical
Result Qual
2,750
Limits Qual
80-136
85-121
78-132
81-123
SW8260D
Analytical
Result Qual
< 1.00
< 1.00
< 1.00
Limits Qual
80-136
85-121
78-132
81-123
Report Date: 3/10/2021 Page 34 of 46
All analyses applicable to lhe CW A SDWA. and RCRA rue performed in accordance lo NELAC prolocols Pertinent sampling inrornmt.ion is located on the all ached COC Confidential Business Informal ion: TI1is report is provided for the exclusi, e use or the
~ddressee Prfrile~es o_Fsub~seq~ent ~~e of the ~~1e of this .con:ip:my or an~.· 1~1:'1be1 of ils stnff, or reproduclio~ ~rlhis repo~ in ~on~ection~ \,i1h the a~:ertise~ent, P~?moli~n ~r ~ale of ~!).~rodL~cl or pr3cess, ~r in ~onn:_c~ion w!th th; r:_-p~blicalion of this report
American West
ANALYTICAL LABORATOR IFS
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-013
Client Sample ID: TW4-11_02232021
Collection Date: 2/23/2021 1016h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/6/2021 734h
3/1/2021 1258h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 49.5
E353.2 0.100 7.21
Report Date: 3/10/2021 Page 18 of46
All arml)ses applicable lo lhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Pertinenl sampling information is located on the auached COC Conlidential Business lnfonnalion: This repor1 is proYided for the exclusi,•e use of the
~ddressee Pri,·ile~es of sub .. seq~enl ~~e oflhe 1!~e of this .con:ipany or an) ~r:nbe• of its slruf, or reproduclio.~ ~fthis repo~ in ~o~e<:tion~ n·ilh the a<!~ertiser~ent, P~?motio.n ~ ~a1e of?'!~ ~rodl~Ct or P~?Cess, ~r in ~orm~c~on w!th 1h~ r~-publicn.1io11 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-006C
Client Sample JD: TW4-12_03 l 72021
Collection Date: 3/17/2021 81 lh
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1242h
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
47.8 50.00 95.7 80-136
47.9 50.00 95.8 85-121
47.6 50.00 95.1 78-132
47.3 50.00 94.6 81-123
Report Date: 3/31/2021 Page36of65
All analyses appliC"Clble to lheCWA. OWA. and RCRA are lM."ffom1ed in accordance lo NELAC J>l'OlocolJ. Pertinent stunpliny. infornLillon is located on the nuached COC. CQ11Ddc-ntinl Business lnfonm:ilion: This report is provided fdr 1he,e,'(dU:1irt w:.: or1he
~ddn,ssee. Prh-ilci~cs o:sub.,5eq~)C:nl ~cor the ~~1e of lhis .con.,pauy or ony 1~mber of its stnff, or ~pnxluctio~ ~f this rcpo1! in ~on!1~oon .. wilh lhe ~~·enise~enl, P~?motiu;n QI' .. ,,~ of ~!Y ~rodl!CI or p1:?cess, ~r in ~nn!c!ion w!lh lh~· ':~bllc1:11ion 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: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-006
Client Sample ID: TW4-12_03172021
Collection Date: 3/17/2021 811 h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 2031 h
3/20/2021 1236h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 52.0
E353.2 0.100 3.10 ----
Report Date: 3/31/2021 Page 12 of65
All o.nnlyses applicable lo lhe CWA. SDWA. and RCRA nre performed in accordance to NELAC protocols.. Per1inen1 sn.mph"lt-infonnntion is located 011 the allnched COC. Confidentinl Business lnformolion: This repon is provided ror 1hc exclusire use or the
~ctdressee. PriYile~es of sub .. seq~ent ~1~e or lhe ~~le or1his .co1~pony or nn): 1~':'1ber or its stnrr, or rcproduclio~ .~f 1his r~ in ~on~ection" wi011he n~,,enisement, P~?moti~n ~r sa1e of~!)'. ~rod~cl or P~?cess, ~r in ~onn~c!ioll w!lh th~~-publication or I his report
American West
ANALYTICAL LAB0RATOR1l8
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: I st Quarter Chloroform 2021
Lab Sample ID: 2103541-007C
Client Sample ID: TW4-13_03172021
Collection Date: 3/17/2021 819h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1302h
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
48.7 50.00
48.5 50.00
47.4 50.00
47.6 50.00
97.3 80-136
97.0 85-121
94.7 78-132
95.2 81-123
Report Date: 3/31/2021 Page 3 7 of 65
All annlyses applicable to the CWA. SDWA. and RCRA ore perrormed in accordance to NELAC protocols. Pertinent srunpling informntion is located on the allached COC. Conlidenliol Business lnfonnotion: This report is provided for the exdusi\"e use of the
~rldressee PriYile~es o,r sub .. seq~1ent ~~e or the ~~1e or this .co1~pn11y or nnr 1~'!1ber of its sloIT, or reproductio~ ~f this repo~ in ~on~ection ... ,,i1h lhe n~venisement, p~~motio.n ~r sale of ?J!Y rrod~ct or p1;~cess, ?r in 7°nn:_c~ion \\'!th th: r~-p~blicnlion of this report
American West
ANALVTICAl l A00RATORIEB
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-007
Client Sample ID: TW 4-13 _ 03172021
Collection Date: 3/17/2021 819h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 2059h
3/20/2021 1237h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 67.3
E353 .2 0.100 5.57
Report Date: 3/31/2021 Page 13 of 65
All analyses applicable lo the CWA. SDWA, Md RCRA are µerfom1ed in accordance to NELAC protocols Per1inenl sampling information is located on the allnched COC. Confidential Business lnformnlion: This repon is provided for the exclush e use of the
~ddressee, Pri, ile~es o.r sub,.5eq~1enl ~?e of the ~~e of lhis .crn~puny or nn) '~'!1ber of its sln{T, or reproductio~ ~~ lhis repo~ in ,con~eclion .. \\ilh 1he n~~enise1~ent. P~?motio.n ~r ~ale of~!)~ ~rodl~CI or P~?Cess, ?r in ~onn1;c~ion w!lh lh~ r;·p~blication of this report
American West
ANALYTICAL I.AB0RATORIE8
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: awal @awal-Jabs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-015C
Client Sample ID: TW4-14_03182021
Collection Date: 3/18/2021 823h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 740h
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 1.77
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-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
48.8
48.0
48.9
48.4
50.00 97.6 80-136
50.00 96.0 85-121
50.00 97.7 78-132
50.00 96.9 81-123
Report Date: 3/31/2021 Page 45 of65
All nnolyses applicnble to the CWA. SOWA. and RCRA ore performed in nccordance to NELAC protocols. Pet1inent sL'l.mpling infom1Alion is localed on the nuached COC. Confidential Business lnformotion: This report is pro,•ided for lhot.~C'h,l.\h'C' u,--.e of the
~ctdressee. P1i\'ile~es o,rsu~seq~enl ~1~e of lhe ~~1e of !his .co1~p,my or nny 1~Tber of its slnrT, or reproductio~ ~fthis re~ in .con~1cc1ion ... with the n~Yertise1~ent, p~~molio.n ~r sale of ?1!Y ~rod~cl or p~ocess, ~r in ~nn~c~ion w!lh th~ r~-pub11cndon or this report
3440 South 700 West
,alt Lake City, UT 84 I 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-015
Client Sample ID: TW4-14_03182021
Collection Date: 3/18/2021 823h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3ns12021 2331,
3/20/2021 1253h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 48.2
E353.2 0.100 5.56 --~
Report Date: 3/31/2021 Page 21 of65
All analyses applicable lo lhe CWA. SOWA. and RCRA are perfom,ed in accordance to NELAC protocols. Pertinent sampling information is located on the nttached COC. Confidential Business Information: This report is provided for lhe exclusi, e use orthe
~ddressee Pri, ile~es o_f sub .. seq~enl ~~e of the ~~e of this .con:1pany or 811) ·~~ber of its staff, or reproduclio~ ~f I his repo~ in ~on~eclion ... \\~th lhe n<!vertisement, P~?n,otio.n ~r sale of ~!Y ~rod~ct or p~ocess, ~r in ~nn:c~ion w!th th~ r~-publica1ion of this repon
ORGANIC ANALYTICAL REPORT
American West
ANALYTICAl 1.AOORATOA l (S
3440 South 700 West
,alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-006C
Client Sample ID: MW-26_02232021
Collection Date: 2/23/2021 1007h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1313h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Phone: (801 ) 263-8686 Surrogate Units: µg/L CAS
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
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 3,060
Result Amount Spiked %REC Limits Qua!
4,930 5,000 98.7 80-136
5,040 5,000 101 85-121
5,130 5,000 103 78-132
5,210 5,000 104 81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1116h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
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 l.00 3.46
Result Amount Spiked %REC Limits Qual
56.9 50.00 114 80-136
46.0 50.00 92.0 85-121
56.5 50.00 113 78-132
50.5 50.00 101 81-123
ReportDate: 3/10/2021 Page 27of 46
All anal~ ses applicable to lhe CWA. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinen1 s11m1>ling inl'ormntion is Jocoted on the nllnched COC Confidenlinl Business Information· This repon is pro\'ided for lhe e.xclusi\'e use of the
~ddressee Prl\"ile~es of subyeq~enl !-':'e of the ~~e of this .co1~pm,y or nn~ ~mbel' of ils stnff, or reproductio~ ~f this repo~ ill ~n~lection .. \\ilh lhe o~:ertise1'!1eru. P~?molio_n ~r ~A.le of ?J!}. ~lodl~cl or p1.ocess, ~r in 7onn~c~ion w/lh th? r;_-p~blica1ion of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-006
Client Sample ID: MW-26_02232021
Collection Date: 2/23/2021 1007h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 331 h
3/1/2021 1248h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 2.00 59.5
E353.2 0.100 0.349
Report Date: 3/10/2021 Page 11 of 46
All anal~ ses applicuble to lhe CWA. SOWA, and RCRA are performed in accordance to NELAC prolocols Pertinent sampling informal.ion is localed on lhe allached COC. Confiden1ial Business Jnfonnation: This repor1 is prm ided for1he e.-..:clusi,·e use of the
~ddressee Pri,·ile~es o_f sub .. seq~1ent ~·~e of lhe ~:11,'le of this .co~pany or M)" ~mber of its slnff, or reproductio~ ~fthis repo~ in ~~ection .. ,,.;1.h the a~vertisem~nl, p~~moti~ or sale of :U!~ ~rod~cl or p~~ess, ~r in '?°nn~.lion w!lh th~ r!·P~blicruion of this report
American West
ANALYTICAL IABO~ATORIF8
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: I st Quarter Chloroform 2021
Lab Sample ID: 2 l03706-003C
Client Sample ID: TW4-16_03242021
Collection Date: 3/24/2021 815h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/25/2021 1342h 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-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 1.00 248
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
55 .1 50.00 I JO 80-136
43.8 50.00 87.5 85-121
53.2 50.00 106 78-132
52.7 50.00 105 81-123
Report Date: 3/31/2021 Page 15 of29
All rutalyses 011plicable lo lh~ CWA. SOWA. Md RCRA are 1)Cfforn~ in ftccordMce to NELAC protocols. Pc11inenl srunplin11, inlormnlion is localed on lhe nttnched COC. Confidential Business lnlonnotion: This report is pro,•ided for the e.'Xclusi, e use or1he
~tldressee. P11\ih1~-r:, or su~seq~,enl ~~e or the ~~~,e of thi!-.co~paoy or on~: 1~i:nber of its stnlT, or reproducti~ ~~this rcpo~ In fOll)l~lion,, \\·ith the a~~1er1ise'"!1e111, P~?molio,n ~1·~ale of ~!Y .. ~1 odl~cl or p~ocess, ~r in ~nn~!ion w!th 1h~ n:_·p~blicotion or this repon
American West ANALYTICAL LAQORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-003
Client Sample ID: TW4-16_03242021
Collection Date: 3/24/2021 815h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 135h
3/30/2021 I 003h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 92.6
E353.2 0.100 5.82
Report Date: 3/31/2021 Page 7 of 29
All analyses applicable to ihe CW A. SOWA. and RCRA nre perfomled in accordance 10 NELAC protocols Pertinent sampling infonnntion is locnted on the ntlnched C'OC. ConOdentinl Business lnformnlion: This report is pro,•ided for the e.xclusi\ e use of the
~ddressee Pri, ile~es or sub,_5eq~1ent ~1~e of the ~~e of this .co1~po.ny or MY 1~iyiber of its slnrf, or reproductio~ ~f this repo~ in ~on~eclion,. \\-ith the°<!~ ertisement, P~?mo1io,n ~r ~ale of ~!Y ~rod~cl or P~?Cess, ~r in ~nn~iion w!th th~ r~-publicotion or this repor1
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-00SC
American West Client Sample ID: TW4-16R_03232021
ANALvr1cAL LADORAroR1Fs Collection Date: 3/23/2021 800h
3440 South 700 West
;alt Lake City, UT 84119
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/25/2021 1519h
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 11.6
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: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
54.9 50.00 110 80-136
46.8 50.00 93.6 85-12[
53.2 50.00 106 78-132
52.3 50.00 105 81-123
Report Date: 3/31/2021 Page 20 of 29
All anolyses applicable to the CWA. SOWA. and RCRA nre perfomled in ftccordance to NELAC protocols, Pertinent sampling inform.ntion is loc,:ued 01\ the attached COC. Confid1mti11I Business lnfonnation: This repon is provided for the e.xclusi, e use of the
~ddressee Pririle~es o_f sub__seq~1ent ~1~e of the ~~1e of this .co1~puny or lUl)' J~_!"~ber ofits stnff, or reproductio~ ~f 1his repo11 in fOni1ection,, \\ith the n~~ ertise~ent. P~?mo1io.n ~r sale of ~!Y. ~l'Odl~CI or p1:ocess, ?r in ~onn~c!ion w!lh th~ r!·p~blication of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263 -8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-008
Client Sample ID: TW4-16R_03232021
Collection Date: 3/23/2021 800h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 546h
3/30/2021 1009h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 3/31/2021 Page 12 of29
All nnolyses applicable lo lhe CWA. SOWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infonnation is localed on the nttnched COC Conl1dentinl Business lnformntion: This report is provided for the exclusi,e use of1he
~ddressee. Piivile~es o,r sub .. seq~ent ~~e or the ~~e of this .coi~pany or onr 1~~~ber of ]ls slnlT, or reproductio~ ~~this repo~ in ~011!1ection ... with the n~~·ertise1~ent. P~?moti~n ~r ~ale of~!~~ frod~cl or P~?cess, ~r in ~onn~c~ion w!th th! r~-p~blicutio11 of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84 I 19
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-00lC
Client Sample ID: MW-32_03222021
Collection Date: 3/22/2021 1230h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/25/2021 1244h
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: I ,2-Dichloroethane-d4 17060-07-0 56.5 50.00 113 80-136
Surr: 4-Bromofluorobenzene 460-00-4 46.4 50.00 92.8 85-121
Surr: Dibromofluoromethane 1868-53-7 51.0 50.00 102 78-132
Surr: Toluene-d8 2037-26-5 53.6 50.00 107 81-123
Report Date: 3/31/2021 Page 13 of29
All anolyses applicable 10 lhe CWA, SOWA. and RCRA ore perfonned in accordance to NELAC prolocols Pertinent sn.mpling informntion is locuted on the uttnched COC Conncltmtiol Business Information: This ri,pon is provided for the exclush•e use of the
~ddressee Pririle~es or sub,.seq~enl ~~e of the ~~e of this .co1~pon~~ or nny l~'!lber of ils sla!T, or reproduclio~ ~r this repo~ in .con~ection .. wilh the n~rertise1°!1e11t. P~?mollo.n ~r !ale of ?J!>'. ~IOdl~CI or p11ocess, ~r in ~onn:c!ion W!th lh~ r!·p~blicntion of this report
American West
ANALYTICAL 1.ABOAATORIEB
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2103706-001
Client Sample ID: MW-32_03222021
Collection Date: 3/22/2021 1230h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 039h
3/30/2021 955h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 36.8
E353.2 0.100 < 0.100
Report Date: 3/31/2021 Page 5 of29
All analyses applicable to lhe CWA. SDWA. Md RCRA nre perfonned in accordance to NELAC prolocols Pertinent sampling informntion is located 011 lhe aUached COC. Confidential Business Information: This report is provided for the exclush'e use of the
~ddressee Pri\ ile~es o,f sub_.seq~enl ~e of lhe ~~e of lhis .co~pany or ru,~ ~mbe1 of its slaff, or reproductio~ ~f this repo~ in ~on?eclion .. \\·ith the n~vertisement, p~~motio.n ~r sale of ~!Y. ~rod~l or P~?Cess, ~r in ~nn~~ion w!th th~ r!•publicntion of lhis report
American West
ANAi YTICAl lAbORATORIE9
3440 South 700 West
:>alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: awal @awal-Jabs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-021C
Client Sample ID: TW4-18_03182021
Collection Date: 3/18/2021 923h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1253h
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 52.0
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
48.4
48.3
48.6
47.8
50.00 96.8 80-136
50.00 96.6 85-121
50.00 97.1 78-132
50.00 95.6 81-123
Report Date: 3/31/2021 Page 51 of 65
All onolyses applicable LO lht:i CWA. SOWA. Md RCRA ore perl'om,ed in accordance to NELAC protocols. Pertinerll sampling information is located on the atloched COC, Confidentinl Business Information: This report is provided for the exclusi, e use of the
~ddressee. P1i, ile~es o,r sub .. seq~1enl ~1~e or the ~!'1:"e of this 1co1~pany or MY J~~ber of its stnff, or reproduclio~ ~~ this repo~ in ~on~ection .. with lhe a~~ertisement, P~?motio.n ~r sale of~!): ~rodl~CI or p1.?Cess, ~r in ~nn:c~ion w!th th? r~~publicntion of 1his report
American West ANALYTICAL LAB0RATOR1f8
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-021
Client Sample ID: TW4-18_03182021
Collection Date: 3/18/2021 923h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 2152h
3/20/2021 1307h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua!
E300.0 1.00 41.8
E353.2 0.100 3.61 ----
Report Date: 3/31/2021 Page 27 of65
All anal) ses applicable to the CWA SOWA. and RCRA are perfomled in accordance 10 NELAC protocols Per1ineot sampling information is located on lhe atlached COC Confidentiol Business lnfonnofion: This report is provided for the e.xclusiYe use of !he
~ddressee_ Pri\ ile~es o~ su1:5eq~en1 ~,~e or the ~~e or this .co1~pany or fill) ~mber of its staff, or reproducti~ ~~ Lhis repo~ in ~o~ection .. wiU1 the ~ver1isemen1, P~?mo1io_n ~r sale of~!). ~rod~t or P~?cess, ~r in ~nn~c)ion w!Lh th~ r~-publication of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2102631-005C
Client Sample ID: TW4-l 9 _ 02232021
ANALvr,cA1 LAooAAroR1Es Collection Date: 2/23/2021 830h
Received Date: 2/25/2021 1250h
Analytical Results
Extracted:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/26/2021 15 lOh
Units: µg/L Dilution Factor: 100 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:[phone]
~-mail: [e-mail]
Surr: l ,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
67-66-3 100 6,660
Result Amount Spiked %REC Limits Qual ------
5,950 5,000 119 80-136
4,640 5,000 92.8 85-121
5,900 5,000 118 78-132
5,190 5,000 104 81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awaJ-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1057h
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
I 7060-07-0
460-00-4
1868-53-7
203 7-26-5
Method:
CAS
Number
Reporting
56-23-5
74-87-3
75-09-2
Result Amount Spiked
56.8 50.00
49.2 50.00
57.1 50.00
5 l.8 50.00
Limit
1.00
1.00
1.00
%REC
114
98.4
114
104
SW8260D
Analytical
Result Qual
8.40
< 1.00
< 1.00
Limits Qual
80-136
85-121
78-132
81-123
Report Date: 3/10/2021 Page 26 of 46
All annl~ ses applic.:iblc lo lhe CWA. SOWA. and RCRA are perfonned in nccordnnce to NELAC protocols Pertinenl sumpling int'ormnlion is loco.led on lhe attnched COC. Conlidentiol Business Information: This report is pro,·ided for lhe exclusi, e use of the
~ddressee Prfrile~es o_f sub .. seq~ent ~;e of the ~~e or this .co1~pany or nn)· ~mbe1 of its stnJT, or reproductio.1! ~! lhis repo~ in ~on~ection .. \\ilh lhe n~~ ertisemenl. ~?moti~ ~r snJe of ~!Y ~1odl~l or p1.?Cess, ~r in 7onn1;c,lion w!th 1h~ r:-publicution 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: I st Quarter Chloroform 2021
LabSamplelD: 2102631-005
ClientSampleID: TW4-19_02232021
Collection Date: 2/23/2021 830h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 303h
3/1/2021 1246h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 5.00 167
E353 .2 0.100 6.61
Report Date: 3/10/2021 Page IO of 46
All analyses applicable to 1he CWA. SOWA, and RCRA are performed in accordance to NELAC protOCO,s Pertinent sampling information is localed on lhe allached COC Conr.ctentlal Business Jnformalion: This report js pro\'ided for the exclusi, e use of the
~ddressee. Pri,ile~es of su~eq~enl ~~e or lhe ~~e of this .con;ipany or any ~~her of ils slnff, or reproduclio~ ~f this repo~ in ~o~ection .. with the ~"ertisement, P~?motio.n ~r ~aJe of~!). ~rod~ct or p~~' ~r in ~nn~c!ion '''!lh th~ r:publicalion of this repon
ORGANIC ANALYTICAL REPORT
American West
ANALYTICAi LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 210263 l-008C
Client Sample ID: TW4-21_02232021
Collection Date: 2/23/2021 918h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1352h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor:
Phone: (80 I) 263-8686 Surrogate Units: µg/L CAS
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 400
Result Amount Spiked %REC Limits Qual
502 500.0 100 80-136
504 500.0 101 85-121
506 500.0 IOI 78-132
520 500.0 104 81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-Jabs.com
Kyle F. Gross
Laboratmy Director
Analyzed: 2/26/2021 1155h
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: SW8260D
CAS
Number
Reporting Analytical
CAS
17060-07-0
460-00-4
1868-53-7
203 7-26-5
56-23-5
74-87-3
75-09-2
Result Amount Spiked
58.2 50.00
48.0 50.00
57.6 50.00
51.2 50.00
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
%REC Limits Qual
116 80-136
96.0 85-121
115 78-132
102 81-123
Report Date: 3/10/2021 Page 29 of 46
All analyses applicable to lhe CWA. SDWA. and RCRA me perfonned in accordAnce lo NELAC prolocols, Pertinent sampling information is located on the attached COC, Confirlentlal Business ln[ormalion: This re11ort is pro,,ided for 1he exclusi, e use of the
~ddressee P1frile~es or sub,_seq~1ent ~1~e of the ~~e of this .con.1pany or any 1~~mber of ils slnJT, or reproduclio1~ ~f 1his repo~ in ~o~eclion ... with the a~vertisemenl, P~?motio.n or sale of ?1!) ~rod~cl or p~ocess, ~r in ~nn:c!ion w!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: I st Quarter Chloroform 2021
Lab Sample ID: 2102631-008
Client Sample ID: TW4-21_02232021
Collection Date: 2/23/2021 918h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 522h
3/1/2021 1252h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 454
E353.2 0.200 15.2
Report Date: 3/ I 0/2021 Page 13 of 46
All analyses applicable lo lhe CWA_ SDWA_ and RCRA are perfonned in accordance to NELAC prolocols Pertinent sampling informalion is localed on lhe attached COC Confidential Business Jnformalion: This report is provided for lhe exclusi,e use of the
~ddressee Pri, ile~es of sub ... seq~enl ~e of the ~~le of I his .001~pany or any ~i:nber of its slaJT, or reproductio~ ~f this repo~ in ~o~eclion ... with the a<!vertisemenl, P~?moti~n ~r ~ale of ?1!) ~rodl~cl or p~ocess, ~r in ~nn:_c)ion w!lh th~ rt;:·publicalion of lhis report
American West
ANAIYTICAL LAOORATORIES
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2I0263l-Ol4C
Client Sample ID: TW4-22_02232021
Collection Date: 2/23/2021 944h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1553h Extracted:
Units: µg/L Dilution Factor:
Compound
Chloroform
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
100
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DENI00
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 100 5,100
Result Amount Spiked %REC Limits Qual
5,050 5,000 101 80-136
5,140 5,000 103 85-121
5,070 5,000 101 78-132
5,250 5,000 105 81-123
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 2/26/2021 1352h Extracted:
Units: µg/L Dilution Factor: Method: SW8260D
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 < 1.00
Chloromethane 74-87-3 1.00 < 1.00
Methylene chloride 75-09-2 1.00 < 1.00
---
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qua]
Surr: l ,2-Dichloroethane-d4 17060-07-0 58.3 50.00 117 80-136
Surr: 4-Bromofluorobenzene 460-00-4 47.4 50.00 94.9 85-121
Surr: Dibromofluoromethane 1868-53-7 57.9 50.00 116 78-132
Surr: Toluene-d8 2037-26-5 51.5 50.00 103 81-123
Report Date: 3/10/2021 Page 35 of 46
All analyses applicable to the CWA. SDWA. and RCRA are performed in accordance lo NELAC protocols. Pertinenl sampling information is located on a1e attached coc_ Confidential Business [nfo1 mation: This report is provided for the exclLLSi\ e use of the
~dressee Prl\-ile~es o! sub~seq~enl ~~e of lhe ~~e or lhis .con:ipany or 1:1ny ~mber orils slaJT, or reproductio~ ~r lhis repo~ in ~0~1eclion ... ,vith the ~~vertisement, P~?molio.n ~r sale of ?1!Y ~rod~cl or p~ocess, ~r in :onn:_c~ion "!th 1h; r:_-p~blication of 1his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2102631-014
Client Sample ID: TW4-22_02232021
Collection Date: 2/23/2021 944h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/6/2021 858h
3/1/2021 1300h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 618
E353.2 1.00 69.6
Report Date: 3/10/2021 Page 19 of 46
All anal) ses applicable to the CW A. SDWA. and RCRA are perfomied in accordance to NELAC protocols Per1inenl sampling informalion is located on the allached COC Confidentiol Business Information: This report is proYided for 1he exclusive llSe of the
addressee. Pri, ileges of subsequent use oflhe name of lhis company or rut) member of its slaJT, or reproduction of this report in conneclion "ilh lhe odvertisemenl promotion or sa1e of 811) product or process, or in connection with the re-publicntion of this report
... • , ., t II +II I o -... ,,! p o I -.. , • •* o o ol O O .... I I .. •
American West ANIHYTICAL LAB0RATOR1E8
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-012C
Client Sample ID: TW4-23 _ 03 l 7202 l
Collection Date: 3/17/2021 900h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1440h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qua)
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
46.4
45.8
45.7
45.8
50.00 92.8 80-136
50.00 91.6 85-121
50.00 91.5 78-132
50.00 91.7 81-123
Report Date: 3/31/2021 Page 42 of 65
All analyses applicnble to lhe CWA. SDWA. and RCRA ore perl'omled in accordance to NELAC protocols Pertinent snmpling information is located on the attnched COC Conf1ctential Business lnformalion: This repon is prm•ided for the exclusi\e use of1he
~ddressee Pri, ile~es orsub .. seq~1enl ~1~e of the ~~ne of this .co1~pnny or nny 1~mber or ils stnff, or re1>roductio~ ~f this repo~ in .con~1ection ... ,,i1h the a~vertisement, P~?motio.n ~r sale of ~!Y ~rodt~cl or p1.?cess, ~r in ~nni;c~ion w!th th~ r~-p~blicntion of this 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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-012
Client Sample ID: TW4-23 _ 03 l 72021
Collection Date: 3/17/2021 900h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 ]!Oh
3/20/2021 1245h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 51.6
E353.2 0.100 < 0.100
Report Date: 3/31/2021 Page 18 of 65
All analyses applicable to the CWA. SOWA. and RCRA ore perrormed in accordance to NELAC protocols Pertinent sampling information is located on lhe allached COC, Confidenlial Business lnformalion: This report is provided for the exclush·e use or the
~ddressee Prh ile~es o;su~seq~ent ~1~e or the ~~1e or this .co1~pany or nny ~mber or its slnff, or reproduclio~ ~~ this repo~ in fon:1ecliori,. \vith the n~~ertisement, P~?motio.n ~r ~ale of :11!). ~rod~cl or P~?cess, ~r in ~nn~c!ion w!lh th~ r1;-p~blicalion of this report
American West
ANALYTICAL l AB0RATORIE6
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: 1st Quarter Chloroform 2021
Lab Sample ID: 210263 l-002C
Client Sample ID: TW4-24_02232021
Collection Date: 2/23/2021 936h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 822h
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 96.2
74-87-3 1.00 3.60
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
56.5
50.0
55.5
51.8
50.00 113 80-136
50.00 100 85-121
50.00 Ill 78-132
50.00 104 81-123
Report Date: 3/10/2021 Page 23 of 46
All anol) ses e.pplicoble lo the CWA. SDWA. ru1d RCRA are performed m accordnnce to NELAC protocols Pertinent sampling information is localed on the auached COC. Confidential Business Information: This report is proYided for the exclusi,e use of the
~ddressee. Pri, ile~es o,C sub__seq~ent ~~e or lhe ~?1:11e or 1his .co1~1pony or nn~ 1~~ber of its slnff, or reproduclio~ ~r this repo~ in .con~ection,. with the a~,•ertisemenL P~?motio.n ':r ~ale of ?1!~. ~rodl~ct or P~?Cess, ~r in ~nn~c.tion w!th th~ i:-p~blication 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-002
Client Sample ID: TW4-24_ 0223202 l
Collection Date: 2/23/2021 936h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L -------
Date
Analyzed
3/3/2021 044h
3/1/2021 1240h ------
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 10.0 1,170
E353.2 0.500 41.9
Report Date; 3/10/2021 Page 7 of 46
All analyses applicable lo the CWA. SDWA_ and RCRA are performed in accordance to NELAC nrolocols, Pertinent sampling information is located on the attached COC Conlidenlial Business [nformation: This report is provided for lhe exclush e use of the
~ldressee Prfrile~es of su~seq~enl ~~e of the ~~e of Lhis .co~pany or M) ~mber of ils stall', or reproduclio~ ~f this repo~ in ~o~ecrion~ with the n~~1ertise~enl, P~?moli~n '!r sale of~!). ~rodL~ct or p~~ess, ~r in ~nn!c~ion w~Lh 1h~ r~-publication of lhis repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2021
LabSampleID: 2102631-00lC
Client Sample ID: TW4-25_02232021
ANA1 vr1cAL LAB0RAr0R1ts Collection Date: 2/23/2021 926h
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 802h Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: flg/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
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
54.9 50.00 110 80-136
49.0 50.00 97.9 85-121
54.3 50.00 109 78-132
52.6 50.00 105 81-123
' -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 3/10/2021 Page 22 of 46
All nn:,l~ses applicable 10 1he CWA. SOWA. Md RCRA ore perfom1ed in ftCcordMce to NELAC protocols Peninent sampling information is locoted on the auached COC Conridenllol Business lnfonnotion: This repon is provided for 1he exclusi, e ~ of1he
~ddressee P1frile~es o_f sub .. seq~nl ~e or lhe ~~1e or this .co1~pany or nnr ,~mber or its stnfT, or reproduclio~ ~f this repo~ in ~on~1ection ... w:ilh the a~~·erlise,~enl. P~?motio.n ~r sale of~!~. ~rodL~t or p1.ocess, ~r in ?>""~~ion w(th lh~ r~-p~blication of this report
3440 South 700 West
,alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
LabSamplelD: 2102631-001
Client Sample ID: TW4-25_02232021
Collection Date: 2/23/2021 926h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 016h
3/l /202 l 1328h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 2.00 100
E353.2 0.100 3.43
Report Date: 3/10/2021 Page 6 of 46
All analyses applicable 10 lhe CWA. SDWA and RCRA are perfom1ed in accordance to NELAC protocols Per1inent sampling information is located on lhe aHached COC Confidential Business Jnformation: This report is provided for lhe exclusi\ e use or the
~ddressee Pri\'ile~es o_f sub .. seq~enl ~~e of the ~?'!1e or this 1co1~pany or nny ~mber of ils staff, or reproducli~ ~r lhis repo~ in ~on~eclion .. \\~lh the ~,·ertise~e111, P~?moti~ or sale of ~!Y ~rodl~ct or P•.?Cess, ~r in ~nn~~ion w!th th~ ri;-p~blicalion or1his report
ORGANIC ANALYTICAL REPORT
American West ANAlVTICAl I ADOAATO~lfB
3440 South 700 West
;alt Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-007C
Client Sample ID: TW4-26_03242021
Collection Date: 3/24/2021 857h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/26/2021 2054h
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 1,030
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
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
203 7-26-5
4,860
4,710
4,860
4,760
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Analyzed: 3/25/2021 1715h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
5,000 97.1 80-136
5,000 94.2 85-121
5,000 97.3 78-132
5,000 95.3 81-123
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
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
54.6 50.00
45.6 50.00
52.5 50.00
46.2 50.00
109 80-136
91.3 85-121
105 78-132
92.4 81-123
Report Date: 3/31/2021 Page 19 of29
All analyses applicable to 1he CWA. SDWA. Md RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is locnted on the attached CDC. Conlid~ntinl Business Information: This r~port is pro"ided for lhe esclusin, use or the
~ddressee. Prfrile~es of sub,_seq~enl ~1~e or the ~~e or this .co1~pnny or M) 1~mber of ils stn!T, or reproduclio~ ~f lhis repo~ in ~on~ection .. \\ith the n~ret1isemenl. P~?moti~n ~r sale of ?1!Y ~rod~ct or P1.?cess, ?r in 7°"n!c!ion w!th th~ r!·publicntion of this report
American West ANALYTICAL LADORATORIES
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-007
Client Sample ID: TW4-26_0324202l
Collection Date: 3/24/2021 857h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L ------
Date
Analyzed
3/26/2021 518h
3/30/2021 I 007h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.9
E353.2 0.100 11.3 ---
Report Date: 3/31/2021 Page 11 of 29
All analyses al)plicable to 1he CWA. SDWA. Md RCRA are perfomied in accordance 10 NELAC protocols. Pcrt1nl'!nt s&11mplh1u infornuuion is located on the allached COC. c:anOlli:ntial Business Information: This repon is provided for lhe ~...;:clu1,lrc use of the
~ddressee Pti, ile~es of sub .. seq~1ent ~~e of lhe ~?1,11e of this .co1~pony or MY 1~mber or its stnff, or reproducltD!! ~f lhis ft'PO'! in .co11~10'C1100. "ilh the n~:·ertise1_~ent, P~?moti~ or ~rJo or ~!Y. ~rod~cl or P~?cess, ~r in ~nn!c~ion with th~ rt;·P~bl c-&1tit\U or 1his repon
American West ANALYTICAL lAhO~ATORlte
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax : (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chlorofonn 2021
2103541-017C
Client Sample ID: TW 4-27 03182021
Collection Date:
Received Date:
Analytical Results
3/18/2021
3/19/2021
Analyzed: 3/22/2021 1134h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chlorornethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
844h
805h
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 4.66
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual
48.4 50.00 96.8 80-136
47.5 50.00 95.0 85-121
48.1 50.00 96.3 78-132
47.4 50.00 94.7 81-123
Report Date: 3/31/2021 Page 4 7 of 65
All analyses applicnble to 1he CWA, SDWA Md RCRA ore perronned in accord!lllce to NELAC protocols, Pertinent snmpling information is locnted on the nttn.ched COC. Conlidtmlinl Business Information: This reporl is pro,•ided for the exclusin, use of the
~ddressee P1idle~es of sub .. seq~ent ~1~e or lhe ~~1e or this .co11_1po.ny or nny ~mber or its slnlT, or reproductio~ ~fthis repo~ in ~oni1ection .. "ilh the ~,,ertise"!1en1. P~?moti~ ~r ~nle or ~!Y ~rod~ct or p1,?Cess, ~r in ~nn~c~iot1 '''!th th~ r~·publico1io11 of 1his 1epon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-017
Client Sample ID: TW4-27_03182021
Collection Date: 3/18/2021 844h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/202 l 425h
3/20/2021 1256h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
£300.0 1.00 27.5
E353.2 0.200 23.0
Report Date: 3/31/2021 Page 23 of65
All anal) ses applicable Jo lhe CWA. SOWA, and RCRA nre perfonned in accordance 10 NELAC protocols, Pertinent sampling infornuuion is located on the allached COC Conlidenlial Business lnformolion: This report is provided for the exclusi,·e use of lhe
~ddressee Pri,·ile~es o.rsu~seq~1ent ~~e or lhe ?,~e of this .co1~pany or nny ,~mber of ils s1nrr, or reproductio~ ~~ this repo~ in ~rn~1eclion .. \\ith the u~vertisemenl, P~?motio.n ~r saJe of~!). ~rodl~I or p~ocess, ~r in ~nn~c!ion "'!'h th~ r~-publicalion of this report
American West
ANALYTICAL LAB0RATORIE8
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2I0354l-004C
Client Sample ID: TW4-28 _ 03 l 7202 l
Collection Date: 3/17/2021 757h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1203h
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 < 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: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
48.3
47.7
47.5
47.2
50.00 96.5 80-136
50.00 95.4 85-121
50.00 95.0 78-132
50.00 94.4 81-123
Report Date: 3/31/2021 Page 34 of 65
All analyses applicable to the CWA, SOW A. and RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on the nllached COC Confidential Business Information: This repon is prm•ided for the exclusi, e use of the
~ddressee P1i, ile~es of su~seq~ent ~~e of the ~~e of this .con:ipony or M) ·~~ber of its slaIT, or reproduclio~ ~f this repo~ in f011~1eclion ... wilh the a~~ el1ise1'!1ent. P~?moli~n l:r ~ale of~!)'. ~rod~cl or P1,?Cess, ~r in ~nm:c~ion w(lh th~ r~-publicalion of this reporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-004
Client Sample ID: TW4-28_03172021
Collection Date: 3/17/2021 757h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/202 l l 936h
3/20/2021 l 231 h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 51.8
E353.2 0.100 8.68
Report Date: 3/31/2021 Page 10 of65
All analyses applicnble lo the CWA. SDWA. and RCRA nre l)erfoml'-'d in accordance to NELAC protocols. Pe1tinen1 sampling i1lfornm1ion is locnled on the nUached COC Con!identinl Business Jnformulion: This report is provided for lhe exclusire use of the
~ddressee Pl'\, ile~es o,r su~seq~1en1 ~~e of the ~~e of this .co1~pm1y or nny 1~mbe1 of ils stnIT, or reproducti~ ~f this repo~ in ~011~ection,. ,~ilh lhe o~~'ertisement, P~?motio.n ~r sale or ~!Y. ~rodt~cl or P~?Cess, ~r in ~nn~c~ion \\'!th th~ r;-publicolion or this repon
American West
ANALYTICAi I ABORATORIFB
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-004C
Client Sample ID: TW4-29_03242021
Collection Date: 3/24/2021 825h
Received Date: 3/25/202 I IO 15h
Analytical Results
Analyzed: 3/26/2021 1955h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 10
CAS
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 577
---
CAS Result Amount Spiked %REC Limits Qual
----Phone: (80 I) 263-8686 Surrogate Units: µg/L
Toll Free: [phone]
Fax:[phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laborato1y Director
Jose Rocha
QA Officer
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
494
481
497
481
--The repor/ing limits were raised due to high analyte concentrations.
Analyzed: 3/25/2021 1617h
Units: µg/L
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
CAS
Number
56-23-5
74-87-3
75-09-2
500.0
500.0
500.0
500.0
98.7 80-136
96.3 85-121
99.3 78-132
96.2 81-123
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
-----
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 56.1 50.00 112 80-136
Surr: 4-Bromofluorobenzene 460-00-4 46.5 50.00 93.0 85-121
Surr: Dibromofluoromethane 1868-53-7 48.0 50.00 95.9 78-132
Surr: Toluene-d8 2037-26-5 52.8 50.00 106 81-123
Report Date: 3/31/2021 Page 16 of 29
All onalyses npplicnble to the CWA. SOWA. and RCRA are perlOrmed in nccordance to NELAC protocols. Pertinent snmpling information is located on the aUnched COC Conridenlia\ Business Information: This report is provided for 1he exclush e use or the
~ddressee Pri\'ile~es of sub .. seq~1ent ~1~e or the ~~u:, or this .co1~pml)' or nny 1~mber or its s1nrr, or reproductio~ ~( lhis repo~ in .con~1ection,, with the a~vertise1~e111. P~?mo1io.n ~r !ale of~!)'. ~rod~cl or P~?Cess, ~r in ~onn~.c~ion w!th 1h7 r1;·p~blication of I his report
American West
ANALYTICAL LA80RATORl£S
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: l st Quarter Chloroform 2021
Lab Sample ID: 2103706-004
Client Sample ID: TW4-29 _ 03242021
Collection Date: 3/24/2021 825h
Received Date: 3/25/2021 1015h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/26/2021 354h
3/30/2021 1004h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 44.3
E353.2 0.100 3.09
Report Date: 3/31/2021 Page 8 of29
All analyses applicable lo the CWA. SDWA. and RCRA a.re perlom1ed in accordance to NELAC protocols Pertinenl srunpling infornu1tion is located on Ute nllnched COC. Confidential Business lnformolion: This report is pro,•ided for the exch1si, e use of the
~ddressee Prfrile~es orsu~seq~enl ~~e of lhe ~~e of this .co1~pnny or MY l~~ber of its stnfT, or reproductio~ ~f lhis repo~ in 0C011)1eclion .. ,vilh lhe n~, ertisement, P~?moti~ ~r ~ale of ~!Y ~ro<h~cl or p~ocess, ~r in ~nn~c~ion with 1h~ r~-publication of this report
American West
ANAi YTICAI t.AOORATORIFB
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-023C
Client Sample ID: TW4-30_03182021
Collection Date: 3/18/2021 944h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1332h
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 74.8
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: 1,2-Dichloroethane-d4 17060-07-0 47.5 50.00 94.9 80-136
Surr: 4-Bromofluorobenzene 460-00-4 47.5 50.00 94.9 85-121
Surr: Dibromofluoromethane 1868-53-7 47.6 50.00 95.2 78-132
Surr: Toluene-d8 2037-26-5 47.3 50.00 94.6 81-123
Report Date: 3/31/2021 Page 53 of 65
All analyses applicable 10 lhe CW A. SOWA, Md RCRA are perlonned in accordance to NELAC prolocols, Per1inent sampling infommtion is located on the nttnched COC, Confidential Business Information: This repon is prm•ided for the exc\ush e use or lhe
~ddressee. Pri, ile~es o!' sub,.5eq~enl ~1~e or the ~~e of this .co1~pa11y or nn)' 1~~mber of ils stnfT, or reproductio~ ~f this repo~ in ~on~ection ... "~th the n~vertise1~ent, P~?moti~n <!r saJe of~!) ~rod~cl or p~ocess, ~r in ~onn~~ion w!lh 1h7 r~-p~blication or this reporl
American West
ANAi VTICAL 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:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2021
2103541-023
Client Sample ID: TW4-30 03182021
Collection Date: 3/18/2021 944h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3n5/202 l 2344h
3/20/2021 1312h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 37.6
E353.2 0.100 3.54
Report Date: 3/31/2021 Page 29 of65
All anoJyses applicable to the CWA, SOWA. and RCRA nre performed in accordance to NELAC protocols. Peninenl sampliny infonna1ion is locnted on the attached COC. Confidential Business Inform.ii ion: This repon is pro,·ided for the e.-xclusi\ e use of 1he
~ddressee Pri,·ile~es o.f sub .. seq~nt ~,;e of the ~~e of this .co~pnny or nny ~,:nbe, of ils slnIT, or reproducli~ ~f !his repo~ in ~on~eclion .. with lhe ~~ertise~nt, P~?moli~ or saJe of~!} ~rod~cl or p~ocess, ~r in ~nn~c!ion w~th th~ r~-p~blication of this report
American West ANALYTICAL LAB0RAT0Rl19
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: l st Quarter Chloroform 2021
Lab Sample ID: 2103541-009C
Client Sample ID: TW4-3 l _ 0317202 l
Collection Date: 3/17/2021 834h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 134th
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
48.9 50.00 97.8 80-136
48.1 50.00 96.2 85-121
47.7 50.00 95.4 78-132
47.9 50.00 95.9 81-123
Report Date: 3/31/2021 Page 39 of 65
All analyses applicable lo the CW A. SDWA, and RCRA llf'e perfom1ed in RCcordance 10 NE LAC protocols. Pertinent sampling information is loco1ed 011 the aUnched COC, Confidential Business lnformalion: This report is provided for lhe exclush e use of1he
~ddressee P1i, ile~es or sub .. seti~enl ~~e or lhe ~~e of this .co1~pany or M~· 1~7mber of its slnff, or reproductio~ ~f this repo~ in .con~eclion .. with the o~vertise~ent, p~~motio.n ~r sale of ~!Y. ~rodt:ct or P~?cess, ?Tin ~onn~c~ion w!th th~ r!~publicolion of lhis report
American West
ANAI.VTICAl LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax:[phone]
:-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2021
2103 541-009
Client Sample ID: TW4-3 l 03172021
Collection Date: 3/17/2021 834h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 2251 h
3/20/202 l 1242h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 40.3
E353.2 0.100 0.501
Report Date: 3/31/2021 Page 15 of65
All analyses applicable to lhe CWA. SOWA. Md RCRA nre perfom1ed in accordance to NELAC protocols. Pertinenl snmpling informntion is located on the nttnched COC, Confidential Business lnformolion; This repon is provided for 1he exclusive use or the
~ddressee Pri,·ile~es o,rsub,,seq~1en1 ~1~e of lhe ~~1e or this .co1~pn11y or any ~Tber of its stnfi, or reproductio~ ~~this repo~ in .co11~1ec1ion .. \\ith the n~vertisement. P~?moti~n ~r saJe of?'!), ~rod~ct or P~?cess, ~r in ~nn~c~ion w!lh th~ r:-publicatio11 or 1his report
American West 4NALYTIC4L L4BOR4T0Rlf8
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
foll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2103541-005C
Client Sample ID: TW4-32_03 l 72021
Collection Date: 3/17/2021 804h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1222h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
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
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
49.3
48.1
48.2
48.3
50.00 98.7 80-136
50.00 96.2 85-121
50.00 96.4 78-132
50.00 96.7 81-123
Report Date: 3/31/2021 Page 35 of65
All anal) ses applicnble to the CWA, SOW A. and RCRA ure performed in accordance 10 NE LAC protocols. Per1inent sampling informntion is located on the nttnched COC Conl'idenlinl Business lnfonnahon: This reporl is pro\'ided ror ll'lt1 t!((IU'S'h·c we of the
~ddressee Prl\"ile~es of su~seq~1ent ~,~e of lhe ~~e of this .co1~pan) or M.\ 1~mber of ils slnfT, or reproducli°!! ~f this repo1; in .co11~1eclion ... \1,i1h the n~\'ertise~ent, P~?mo1ia;n ~r ~ale of ~!Y .. ~rodt~cl or p~~ess, ?r in :onn:c!ion \\'!th th~ l'~P';'blicotion of this report
American West
ANALYTICAL I A90AAT0Aif8
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2103541-005
Client Sample ID: TW4-32_03172021
Collection Date: 3/17/2021 804h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L ---
Date
Analyzed
3/24/2021 2003h
3/20/2021 1234h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 60.5
E353.2 0.100 1.80
Report Date: 3/31/2021 Page 11 of 65
All analyses applicable lo the CWA. SOWA. and RCRA ore performed in flccordance to NELAC protocols Pertinent swnpling information is localed on 1he nllnched COC. Conlidential Business lnformulion: This report is pro"ided for 1he exclush e use of the
~ddressee Pii, ile~es of su~seq~1cmt ~1~e of the ~~1e of this
1
co1~pony or M) 1~mber of its slnff. or reproductio~ ~~ lhis repo~ in ~on~ection,. with the a~,,er1isemen1, P~?ntotio.n or ~ale or ~!Y ~rod~ct or p~9cess, ~r in ~onm;,c~ion "'!th th~ r1;-public1uion or this report
American West ANALYTICAL I ADORATORIES
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-022C
Client Sample ID: TW4-33 _ 03 I 8202 l
Collection Date: 3/18/2021 935h
Received Date: 3/19/202 I 805h
Analytical Results
Analyzed: 3/22/2021 1312h
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 64.9
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 J 7060-07-0 48.6 50.00 97.3 80-136
Surr: 4-Bromofluorobenzene 460-00-4 47.2 50.00 94.5 85-121
Surr: Dibromofluoromethane 1868-53-7 48.7 50.00 97.3 78-132
Surr: Toluene-d8 2037-26-5 47.8 50.00 95.6 81-123
Report Date: 3/31/2021 Page 52 of65
All nnolyses applicable to the CWA. SDW A. Md RCRA ore performed in accordance to NELAC protocols Pertinent samplin,g infonrmlion is locuted on tlle auached COC, Conlidenliol Business Jnfonootion: This report is pro\·ided for the o.,r;cluih'e Uit of tho
~ddressee Prhile~es o_f su~seq~ient ~~e or the ~~e oflhis .co1~puny or M)' 1~'!1ber of"its s1nrr, or reproductio~ ~f this repo~ in .con~eclion_. "i01 the "~':er1isef!1etll, P~?mo1io.n ~r ~ale of~!Y ~rod~ct or P~?Ces·i, ~r in ~nn~c~ion w!th th~ r!·publicatlo11 or this reporl
American West
ANALVTICAl LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2021
2103 541-022
Client Sample ID: TW4-33 03182021
Collection Date: 3/18/2021 935h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 2316h
3/20/2021 1311h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 55.6
E353.2 0.100 4.62
Report Date: 3/31/2021 Page 28 of 65
All analyses applicable Lo the CW A, SDWA. and RCRA are performed in accord8Jlce to NELAC protocols Pertinent sampling information is locmed on the allached COC. Confidenlial Business lnformalion: This report is pro,•ided for the exclusfre use of the
!ddressee Pri, ile~es o:sub,,seq~enl ~·~e orlhe ~?1,"e of this .co~pany or an)' ~mber ofils staff, or reproduclio~ ~f lhis repo~ in ~on~eclion,, ,vith the D~\•ertiseme111, P~?motio.n <!r sale of ~!Y. ~rod~cl or p~~cess, ~r in :°nn:c~ion w!th th~ r~-p~blication or this repon
American West ANALYTICAL LAQOAATO~lfB
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: I st Quarter Chloroform 2021
Lab Sample ID: 2103541-0IOC
Client Sample ID: TW4-34_ 03 l 7202 l
Collection Date: 3/17/2021 842h
Received Date: 3/ 19/202 I 805h
Analytical Results
Analyzed: 3/19/2021 1400h Extracted:'
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
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
I
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
48.2 50.00 96.4 80-136
47.3 50.00 94.6 85-121
47.4 50.00 94.7 78-132
47.2 50.00 94.5 81-123
Report Date: 3/3 1/2021 Page 40 of 65
All analyses applicable lo the CWA. SOWA. Md RCRA nre perfom1ed in accordance lo NELAC protocols Pertinenl sampling informo.1ion is locmed on the nllnched COC Conftdtmtial Business Jnfonnalion: This 1eport is provided for lhe exclusi\ e use of the
~cldressee Pri, ile~es o_f sub,_seq~enl ~1~e of lhe ~~e of lhis .cot~pnny or M~' 1~mber of its slnIT, or reproducli~ ~f'this repo~ in ~on~ection ... \\ith the (l~renisemenl, P~?mo1io.n ~r sale of~~>:~rod~ct or P~?Cess, ~r in ~nn!c~ion wfth lh~ r!-publicotion of lhis reporl
American West
ANAI.VTICAL lAB0RAT0RIE8
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-010
Client Sample ID: TW4-34_03172021
Collection Date: 3/17/2021 842h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 231 Sh
3/20/202 l 1243h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 19.3
E353.2 0.100 1.09
Report Date: 3/31/2021 Page 16 of 65
All analyses applicable to the CWA. SOWA and RCRA are perfom1ed in accordnnce to NELAC protocols. Pertinent sampling information is located on the allnched COC, Confidential Business lnfonna1ion: This report is pro"ided for lhe exclusi, e use of the
~ddressee. PriYile~es o,rsub .. seq~ent ~1~e of the ~~e or lhis .cot~pnny or nny ·~rriber of its stnIT, or reproductio~ ~fthis repo~ in fOn~ection,, '"ith the a~venisement, P~?motio.n ~r ~ale of ~!Y. ~rod~ct or p~ocess, ~r in ~nn:_c~ion w!lh th~ r~-publiclllion of lhis report
American West
ANALYTICAi l ABOAATORIEB
3440 South 700 West
;alt Lake City, UT 841 19
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-01 lC
Client Sample ID: TW4-35_03172021
Collection Date: 3/17/2021 850h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1420h
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: I ,2-Dichloroethane-d4 17060-07-0 48.8 50.00 97.5 80-136
Surr: 4-Bromofluorobenzene 460-00-4 47.9 50.00 95.8 85-121
Surr: Dibromofluoromethane 1868-53-7 47.4 50.00 94.8 78-132
Surr: Toluene-d8 2037-26-5 47.5 50.00 95.1 81-123
Report Date: 3/31/2021 Page 41 of 65
All W1alyses applicable lo the CWA. SOWA. and RCRA u.re performed in 11ccordance to NELAC protocols Pertinent sampling informntion is located on the attached COC. ConOdential Business Information: This r~port is provided for the c.xfh.lflfC\rJC' oflhe
~ddressee P1i, ile~es o,r su~seq~1ent ~1~e of the ~~,e or lhis 501~pon~R or nnr '~'!'her of ils stnrT, or reproductio~ ~r this repo~ in ~on~teclion ... wilh the n~,•ertise"?ent, P~?motio.n ~r ~ale of ~!Y. ~1od1~ct or P':?coss, ~r in :°nn~c~ion w!th 1h~ r~·~1>1it.itiDr1 o( 1his 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-011
Client Sample ID: TW4-35 _ 03 l 7202 l
Collection Date: 3/17/2021 850h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 042h
3/20/2021 1244h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 35.6
E353.2 0.100 0.991
Report Date: 3/31/2021 Page 17 of 65
All nnnlyses applico.ble lo the CWA. SOWA. Md RCRA o.re performed in accordance to NELAC protocols. Pertinent sompling infornmlion is located on ~1e attnched COC Confidentinl Business Information: This report is prol'ided for the e:-..clusi\"e use of the
~ddressee Pri, ile~es o,r sub,.5eq~enl ~1~e of the ~~e of lhis 1co1~pany or nn) 1~'!1be1 of its slnff, or reproductio~ ~f this repo~ in ~on~ection ... with 1he o~vertise~enl, P~?motio.n or sale of~!)'. rrod~ct or p1.?cess, ~r in ~nn~c!ion w!th 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2103541-008C
Client Sample ID: TW4-36 _ 03 I 7202 I
Collection Date: 3/17/2021 826h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 132 lh
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
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: l ,2-Dichloroethane-d4 17060-07-0 48.2 50.00 96.3 80-136
Surr: 4-Bromofluorobenzene 460-00-4 48.1 50.00 96.2 85-121
Surr: Dibromofluoromethane 1868-53-7 47.3 50.00 94.7 78-132
Surr: Toluene-d8 2037-26-5 47.3 50.00 94.7 81-123
Report Date: 3/31/2021 Page 38 of65
All nnalyses epplicnble lo lhe CW A SDWA. Md RCRA me performed in accordance to NELAC protocols. Pertinent swnplinb: information is located on Lhe attached COC, Confidential Business lnforrnnlion: This repon is pr°'•ided for 1he exclusi,·e use of the
~ddressee Pii,·ile~es o_f sub .. seq~enl ~~e of the ~~e of this .co1~pon~· or MY 1~1;1ber of i1s slnff, or reproductio~ ~'.this repo~ in ~on~eclion .. wilh 1he n~~·ertise~enl, P~?motio.n ~r sale of ?1!), ~rod~cl or p~ocess, ~r in ~nn~c~ion w!lh th~ r:_-publicntio1l of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-008
Client Sample ID: TW4-36_03172021
Collection Date: 3/17/2021 826h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 2127h
3/20/2021 1238h ------
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 72.5
E353.2 0.100 < 0.100 -------
Report Date: 3/31/2021 Page 14 of65
All nnal~ses applicable to lhe CWA. SDWA. and RCRA nre perfonned in accordance lo NELAC prolocols. Pertinent sampling information is located on the attnched COC. Conlidentinl Business Information: This report is pro,•ided ror·1heexclu1hc U!le of1he
~ddressee PriYile~es o_f su~seq~1ent ~~e of the ~~e of lhts .co,~pnny or nny ~!mber of its stnff, or reproducti~ ~~ lhis repo~ in .con~u~ction .. \\·ith the 0~~1ertise~e1\I, P~?motio.n ~r ~ale of ~~)'..f1od~c1 or p1:~ess, ~r in ~nn~c~ion \\'!lh 1~ t'~··J)ublicalion or this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax:[phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2102631-0I5C
Client Sample ID: TW4-37_02232021
Collection Date: 2/23/2021 953h
Contact: Tanner Holliday
Received Date:
Analytical Results
2/25/2021 1250h Test Code: 8260D-W-DEN 100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/26/2021 1613h
Units: µg/L
Compound
Chlorofonn
Extracted:
Dilution Factor: I 00
CAS
Number
67-66-3
Method:
Reporting
Limit
100
SW8260D
Analytical
Result
9,380
Qual
-----------------------
Surrogate Units: µg/L CAS Result Amount Spiked
---------
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
5,020
4,900
5,140
5,190
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 2/26/2021 1411h
Units: µg/L
Extracted:
Dilution Factor:
5,000
5,000
5,000
5,000
%REC
100
97.9
103
104
Method:
CAS
Number
Reporting
Compound Limit
Limits
80-136
85-121
78-132
81-123
SW8260D
Analytical
Result
Qual
Qual
Carbon tetrachloride
Jose Rocha Chloromethane
56-23-5
74-87-3
75-09-2
1.00 < 1.00
1.00 < 1.00
QA Officer Methylene chloride 1.00 < 1.00
----
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 58.2 50.00 116 80-136
Surr: 4-Bromofluorobenzene 460-00-4 46.0 50.00 92.0 85-121
Surr: Dibromofluoromethane 1868-53-7 58.2 50.00 116 78-132
Surr: Toluene-d8 2037-26-5 51.3 50.00 103 81-123
Report Date: 3/10/2021 Page 36 of 46
All analyses applicable to lhe CWA. SOWA, ru,d RCRA are performed in accordance to NELAC protocols Pertinent sampling inrormation is located on tJ1e aLtached COC Conlidenlial Business Information: This repon is provided for the exclusi\·e use of1he
~ddressee Pri\ ile~es o.r su~seq~enl ~e of the ~~e of this .co1~pany or nn~ ~mber of its slaN:. or reproduclio!! ~f I his repo~ in .co~eclion ... \\ilh the n~~ertisemenl, P~?moli°:" ~r saJe of :11!\ ~rod~cl or p~ocess, ~r in ~nn~!ion ''!th 1~ r~-publicalion or lhis repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-015
Client Sample ID: TW4-37 _ 02232021
ANA,vr1c .. , ,,.ooRAroR1Es Collection Date: 2/23/2021 953h
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 2/25/2021 1250h
Analytical Results
Compound
Chloride
Nitrate/Nitrite (as N)
Units
mg/L
mg/L
Date
Prepared
~-~ -
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/6/202 1 1021h E300.0 5.00 242
3/Jn021 1301h E353.2 0.500 26.9 ----
Report Date: 3/10/2021 Page 20 of 46
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance lo NELAC protocols Pertinent sampling informal.ion is locmed on the auached COC Confidenliol Business lnformolion: This report is provided for the e.xclusi, e use of the
~ctdressee Pri,ile~es ofsub .. seq~enl ~~e of the ~~e of1his _con_1pany or nn~ ~7~ber of its slnfT, or reproductio~ ~f this repo~ in .con~ection .. \\ilh the .n~Yenisement, p~~motio.n or ~ale of ?-1!Y ~rodl~cl or p1.?cess, ~r in ~nn~c!ion w!lh th? r~-publicaiion or this report
American West ANALYTICAL LA80AAT0R1£B
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: awal @awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-014C
Client Sample ID: TW4-38_03182021
Collection Date: 3/18/202 I 812h
Received Date: 3/19/202 I 805h
Analytical Results
Analyzed: 3/22/2021 720h
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
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
48.5
47.2
48.5
47.9
----
50.00 97.1 80-136
50.00 94.4 85-121
50.00 97.0 78-132
50.00 95.8 81-123
Report Date: 3/31/2021 Page 44 of 65
All annlyses applicnble to lhe CW A. SDW A. Md RCRA ore performed in accordance to NE LAC protocols. Pertinent sampling inrormalion is locuted on the al1nched COC. Confldentinl Business lnformnlion: This report is prO\'ided for the c-x-clusl\'C· use or the
~ddressee. Pririle~es o_f su~seq~tml ~;e or the ~!":"e or1his
1
C01~pony or MY l~'!lber or its starf, or reproduclio~ ~r lhis repo~ in f011~1ection .. \\.ith !he o~~:ertise1~ent, P~?moli~ ~r ~ale of ~!Y. prodl~CI or P~?cess, ~r in ~IUl~c.tion with th~ r~-p~hllcnt ()J\ of lhis report
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-014
Client Sample ID: TW4-38_03182021
Collection Date: 3/18/2021 812h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 206h
3/20/2021 1252h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 37.2
E353.2 0.100 8.24
Report Date: 3/31/2021 Page 20 of 65
All analyses applicable 10 the CW A. SOW A. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is locnted on the au ached COC. Conlidentinl Business lnfo1 molion: This report is provided for the exclusi, e use of the
~ddressee Pri, ile~es or sub .. seq~enl ~~e of lhe ~~e of this .cm~pony or any. ~'!1ber of its staff, or reproduclio~ ~~ lhis repo~ in ~on~eclion .. wi1.h the a~vertisement, P~?moli~n <!r ~ale of~;): ~rod~cl or P~?cess, ~r in ~nn!c.tion w!th th~ r~-publicalion or this report
American West
ANALYTICAL LADORATORIES
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. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-004C
Client Sample ID: TW4-39 _02232021
Collection Date: 2/23/2021 1 OOlh
Received Date: 2/25/2021 1250h
Analytical Results
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Analyzed: 2/26/2021 1450h
Units: µg/L
Compound
Chloroform
Extracted:
Dilution Factor: 100
CAS
Number
67-66-3
Method:
Reporting
Limit
100
SW8260D
Analytical
Result
2,970
Qual
--------
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 5,950
460-00-4 4,790
1868-53-7 5,840
2037-26-5 5,250
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 2/26/2021 1037h
Units: µg/L
Compound
Extracted:
Dilution Factor:
CAS
Number
-------------------
5,000
5,000
5,000
5,000
119
95.8
117
105
Method:
Reporting
Limit
80-136
85-121
78-132
81-123
SW8260D
Analytical
Result Qual
Carbon tetrachloride
Jose Rocha Chloromethane
56-23-5
74-87-3
75-09-2
1.00 < 1.00
1.00 < 1.00
QA Officer Methylene chloride 1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual ----
Surr: l ,2-Dichloroethane-d4 17060-07-0 56.6 50.00 113 80-136
Surr: 4-Bromofluorobenzene 460-00-4 48.2 50.00 96.3 85-121
Surr: Dibromofluoromethane 1868-53-7 56.6 50.00 113 78-132
Surr: Toluene-d8 2037-26-5 51.3 50.00 103 81-123
Report Date: 3/1 0/2021 Page 25 of 46
All anal, ses applicable 10 lhe CWA. SOWA. ru1d RCRA are perfom1ed in accordance to NELAC protocols Pertinenl sampJiny informal.ion is Jocoted on the auoched COC. Confiden1iol Business lnfonnation: This repon is pro\'ided for the c.,c-ltisin: use of the
~ddressee Pri\"ile~es of' sub .. seq~ent ~1~e of the ~~H: or this .co1~pany or rm) ~1!'ber of its stafT, or reproducti~ ~~ this repo~ in ~on?ection" \\ith the o~~·ertise~ent. P~?molio.n ~r ~aJe of ?'!Y .. ~rodl)Cl or P\?'ess, ~r in ~n~c~ion w!th th~ r~·publltmioo or this report
American West
ANAIVTICAL LABORATORIES
3440 South 700 West
)alt Lake City, UT 841 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 ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2021
Lab Sample ID: 2102631-004
Client Sample ID: TW4-39 _ 02232021
Collection Date: 2/23/2021 100 I h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 235h
3/l /2021 1245h -------
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 2.00 53.0
E353.2 0.100 2.12 ----------
Report Date: 3/10/2021 Page 9 of 46
All an.ifyses applicable lo the CWA SDW A,. and RCRA are performed in nccordance lo NELAC protocols. Pertinenl sampling information is located on the altached COC Confidential Business Information: This report is pro,,idel1 ror 1he c:-xctushc ldC or the
~ddressee P1i,·ile~es of sub ... seq~enl ~~e of 1he ~~e of lhis .con;ipany or an) 1~mber of its staIT, or reproducti~ ~~I his repo~ in .co~ection ... ,,~Lh the a~;ertise~enl, P~?motio.n ~r sale of :U!Y. _prod~cl or P~?c~s, ~r in ~nn~~ion w!lh 1~ r:pubhco1ion of 1his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
LabSamplelD: 2102631-003C
Client Sample ID: TW4-40_02232021
Collection Date: 2/23/2021 1244h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1431h
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 10.0 436
CAS Result Amount Spiked %REC Limits Qual Phone: (80 I) 263-8686 Surrogate ----------Units: µg/L
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: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
590
476
581
525
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 2/26/2021 84 lh Extracted:
Units: µg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
CAS
Number
56-23-5
74-87-3
75-09-2
500.0 118 80-136
500.0 95.2 85-121
500.0 116 78-132
500.0 105 81-123
Method: SW8260D
Reporting Analytical
Limit Result Qual
1.00 < l.00
1.00 3.51
1.00 < 1.00
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: l ,2-Dichloroethane-d4 17060-07-0 55.0 50.00 110 80-136
Surr: 4-Bromofluorobenzene 460-00-4 45.2 50.00 90.4 85-121
Surr: Dibromofluoromethane 1868-53-7 54.8 50.00 110 78-132
Surr: Toluene-d8 2037-26-5 50.3 50.00 101 81-123
Report Date: 3/ l 0/2021 Page 24 of 46
All on.ii) ses applicoble to the CWA. SOWA. Md RCRA are performed in accordance to NE LAC protocols Pertinent sampling information is located on lhe aunched COC Confidential Business lnfonnation: This repon is pro, ided for the exc\usi, e use of the
~ddressee P1i, ile~es or sub,.seq~ent ~1~e of lhe ~~1e of this .co1~pnny or rm~· l~~f;lber of ils stoff, or reproduclio~ ~: this repo~ in ~on~eclion,. with the ll~~ertisemenl, P~?motio.n or sale of ~!Y r1odl~CI or p1:?Cess, ~r in ~nn~~ion \\'!lh th~ !;:JlUblicotion of this r~por1
American West
ANALYTICAL LAll0RATORIF6
3440 South 700 West
,alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-003
Client Sample ID: TW4-40_02232021
Collection Date: 2/23/2021 1244h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 207h
3/1/2021 1244h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 36.0
E353.2 0.100 2.43 ----~-----
Report Date: 3/10/2021 Page 8 of 46
All amilyses :.PP.hcDble to lhe CWA. SDW ,\, rmd RCRA are perfomled in accordance lo NELAC pf()tocoti .. Pcnmrnt samphnu 111(onnnuou is located on the attached COC. Confidential Buriness Cnfor m311on: This report is pro"ided for the !.\~cl~\'~ use of the ~d~ Prin1c~i:s o_f su~seq~nl ~~e of 1hc ~:".'\C or1his .co~pnny or any 1~mber or ils staff, or reproducti~ ~r1l1is re110,! in !Ol'!'ec:1100 .. ,vilh lhe a~~·er1ise~ent, P~?motio.n ~r ~ale of:"!": J_>md,!cl or p~~ess, ~r in ~nn:c~ion w!lh th~ r~-pul)liQtJliun of !his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-0lOC
American West Client Sample ID: TW4-41_02232021
ANALvr1cAL LAB0RAr0R1[s Collection Date: 2/23/2021 1226h
Contact: Tanner Holliday
Received Date: 2/25/2021 1250h
Analytical Results
Test Code: 8260D-W-DENI00
VOAs by GC/MS Method 8260D/5030C
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
:-mail: [e-mail]
Analyzed: 2/26/2021 1432h
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: JOO Method:
CAS Reporting
Number Limit
67-66-3 100
CAS Result Amount Spiked %REC
17060-07-0 4,920 5,000 98.4
460-00-4 5,020 5,000 100
1868-53-7 5,020 5,000 100
2037-26-5 5,240 5,000 105
SW8260D
Analytical
Result Qual
1,170
Limits Qua)
80-136
85-121
78-132
81-123
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Analyzed: 2/26/2021 1234h
Units: µg/L
Compound
Carbon tetrachloride
Jose Rocha Chloromethane
QA Officer Methylene chloride
Surrogate Units: µg/L
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor: Method: SW8260D
CAS
Number
Reporting Analytical
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
56-23-5
74-87-3
75-09-2
Result Amount Spiked
57.7 50.00
45.8 50.00
58.2 50.00
50.6 50.00
Limit Result Qual
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
%REC Limits Qua!
115 80-136
91.6 85-121
116 78-132
IOI 81-123
Report Date: 3/10/2021 Page 31 of 46
All am:11) ses applicable lo the CWA. SOWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the allached COC. Confidential Business rnfo1 malion: This report is pro, ided for the exclusi\ e use or 1he
~rldressee Prh ile~es o,r sub~seq~enl ~?e or lhe ~~e or I his .con:ip:my or :m) ~mber of ils s1nff, or reproductio~ ~f this repo~ in ~on~eclion~ with the n~vertisement. P~?motio.n or saJe of~!). prod~ct or P~?Cess, ~r in ~nn~.tion w!th 1h~ 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-010
Client Sample ID: TW4-41_02232021
Collection Date: 2/23/2021 1226h
Received Date: 2/25/2021 1250h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/3/2021 618h
3/1/2021 1255h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qua)
E300.0 1.00 40.6
E353.2 0.100 6.41
Report Date: 3/10/2021 Page 15 of 46
All analyses applicable lo the CWA. SOWA, Md RCRA rue performed in accordance to NELAC protocols Pertinenl sampling information is locnted on the attached CDC Confidential Business lnformalion: This report is pro,·ided for the O:\dlID\'C U'l'e of the
~ddressee. Pri,ile~es of su~~ent ~~e of lhe ~~e or this .co~pony or :my ,~mber of ils slaJT, or repmducli°'! ~f this repo~ in ~~ection~ \\·ith the ~"ertisemenl, p~~molio.n ~r sale of ~2) piod~cl or p~ocess, ?r in ~nn:_c,tion ,v~th th~ r:-publkn1j041 af I his repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: l st Quarter Chloroform 2021
Lab Sample ID: 2103541-003C
American West Client Sample ID: TW4-42 _ 03 l 7202 l
• NAL vr1 cA t LAB oR Aro RI Ea Collection Date: 3/17/2021 747h
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1143h
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 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
---
Result Amount Spiked %REC Limits Qual -----
48.5 50.00 97.0 80-136
47.6 50.00 95.1 85-121
47.9 50.00 95.8 78-132
47.5 50.00 94.9 81-123
Report Date: 3/31/2021 Page 33 of 65
All analyses applicable lo lhe CWA. SOWA. and kCRA are perfomted in accordance 10 NELAC 11ro1ocols. i>cn ncnt sampling infonnntion is located on Jhe attached COC. C'ooridtnliol Business lnrormahon: This report is pro,•ided for the Ci.'<chuh'c we of lhe
addressee. Pri,·ileges of subsequenl use of lht n::unt <,r 1his company or nny member of its sloIT, or ,epnxtuctton or this report in connection ,,.,ilh the advertisement, promolion or s."\le of nny product orp,oc:ess, or in connection wilh the re-puhticalion oflhis report ~ ' ' f" ' '• ~" • • ' -• • j, ko •" ' ' " ,... •' " I o ',.. •' ' ._. ' ' .-, ' • ' f"
American West ANALYTICAL LABORATORIEI
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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-003
Client Sample ID: TW4-42_03172021
CollectionDate: 3/17/2021 747h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2021 1908h
3/20/2021 1230h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 24.2
E353.2 0.100 3.15
Report Date: 3/31/2021 Page 9 of 65
All Malyses applicable to lhe CWA. SOWA. and RCRA ore perfom1ed in acoord:uic:e to NELAC protocols. Pe11inent snmpling information is located on the nllnched COC. Conlidential Business lnformnlion: This report is provided for the exclusi, e use of the
~ddressee. Pri, ile~es or sub"seq~1ent ~~e of lhe ~~1e of this
1
co1~pany or MY 1~t~1ber of its staff, or reJ)roductio~ ~(this repo~ in ~on~1eclion .. with 1he n<!ver1isement, P~?moli~n or ~a.le of~!>". ~rodi~ct or P~?cess, ~r in ~nn:c~ion w!lh th7 r~-publication or this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-016C
Client Sample ID: TW4-60_02232021
ANALYTICA L LAB0RAT0R1es Collection Date: 2/23/2021 800h
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
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 959h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Extracted:
Dilution Factor:
----------
Surrogate Units: µg/L
Surr: J ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
1
Contact: Tanner Holliday
Test Code: 82600-W-DENIOO
VOAs by GC/MS Method 8260D/5030C
Method: SW8260P
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Result Amount Spiked %REC Limits Qual -------
52.9 50.00 106 80-136
45.9 50.00 91.9 85-121
51.6 50.00 103 78-132
48.6 50.00 97.3 81-123
Report Date: 3/10/2021 Page 3 7 of 46
All analyses applicable to the CW A. SDW A. tmd RCRA nre performed in accordance to NELAC protocols. rcr11nt111 scnnplinc lMorm:uion is locnted on the auached COC. Co1nlidcn1iul Business lnforrn1uion: This report is provided for the exclusi,·e use of the
~ddressee. Pri,·ile~es <1!so~q~enl ~:e or the~~~~ Qr1his .cot~pany or any 1~mber or its staff, or reproductio~ ~r this r~po~ ill ~n~1ec11on~ \\·ilh the a~~·ertise~enl, P~?moli~n O(nh: or ~Y. -~rodl~t or p~oocss. ~r in ~nn!c!ion ,,·!th 1h~ r:publication or lhis repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2102631-016
Client Sample ID: TW4-60 _ 0223202 l
ANALY TI CAL LAaoRAToR ,~s Collection Date: 2/23/2021 800h
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
Received Date: 2/25/2021
Analytical Results
Compound Units
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
1250h
Date
Prepared
-------
Contact: Tanner Holliday
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/8/202 l 2102h E300.0 1.00 < 1.00
3/1/202! I302h E353.2 0.100 <0.100
Report Date: 3/ I 0/2021 Page 21 of 46
All analyses applicable 10 the CWA. SDWA. nnd RCRA a.re perl'onned in accordance to NELAC 11mt0Cols. f'crtin~I sramphny, information is located on the Rll:\ched COC. ('oc1fldc:111ial 8usm~ss Jnformalion: This repor1 is provided for 1he ~Ch6n'o u,:e of lhe
~ddressee Prfrile~es of sub .. seq~enl ~~e or lhe ~~e of this .ccu~pany or ony ~inl>er of its stnlT, orrcproducli°'!! e'.lhis RP°'! i11 ~on~1i=cdo'!. with the ~~·ertise~enL P~?nlotio_r• or!,,'\!(! of~!~' ~!Odl)Cl or P\?cess, ~r in ~onn~c~ion "'!'h 1h~ r~-p~blkadou or this report
American West ANALYTICAL I ABORATORIEB
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: 1st Quarter Chlorofonn 2021
Lab Sample ID: 2103541-013C
Client Sample ID: TW4-65 _ 03172021
Collection Date: 3/17/2021 732h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/19/2021 1459h
Units: µg/L
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
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
47.4
46.9
46.7
46.6
50.00
50.00
50.00
50.00
--
94.7 80-136
93.8 85-121
93.4 78-132
93.J 81-123
Report Date: 3/31/2021 Page43 of65
All nnnlyses epplicnllle to lhe CWA. SOW A. and RCRA are perfom\Cd in accordance to NE LAC protocolJ rcrtinm1 snmphn.51 informntion is locQted on the au ached COC. Conflden1ial Business Jnformalion: This report is pro\'ided for the exclush·e use of the
~rldressee. Pri,·ile~es o;su~seq~1ent ~1~e or lhe ~~1e or this .co1~pnny or (lny 1~~'!1ber of its st(lff, or rcproducitl~ ~!'lhis teil>Ol! In ~oni1ection .. with lhe a~~·ertise~tenl, P~?moli<>!' ~r SAie of ~!Y .. ~rod~ct or p1:?Cess, ~r in ~nn!c~ion w!th th~ r~·p~blication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-013
Client Sample ID: TW4-65 _ 03 l 7202 l
Collection Date: 3/17/2021 732h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2021 138h
3/20/2021 1251h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 27.6
E353.2 0.100 6.64
Report Date: 3/31/2021 Page 19 of 65
All enolyses applicnble lo lhe CW A. SDWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is locnted on the auached COC. Conrirlentinl Business Information: This repon is provided for the exclush e use or the
~ddressee. Pri, ile~es of sub,._seq~enl ~~e or lhe ~?',11e or lhis .con_iponr or nn~ 1~mber or its staff, or reproductio~ ~~ this repo~ in ~on~ection ... with lhe n~, ertisernenl. P~?motio.n or saJe of ?1!). ~rod~cl or p~ocess, ~r in '?°nn~c~ion w!lh th? r~-publicntion or this repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
:-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-024C
Client Sample ID: TW4-70 _ 03182021
Collection Date: 3/18/2021 858h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1351h
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 38.2
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
---------
Result Amount Spiked %REC Limits Qual
48.2 50.00 96.5 80-136
47.7 50.00 95.4 85-121
48.8 50.00 97.6 78-132
47.6 50.00 95.1 81-123
Report Date: 3/31/2021 Page 54 of 65
All annlyses applicnbl;: to the CW A. SDW A. and RCRA ore j>C"rfonued in accordance 10 NE LAC protocols. Pertinent sumpling informnlion is \ocnted on the ntto.ched COC. Conlideminl Business lnformotion: This report is pl'Ovided ror tho exclusire use of the
~ddressee. Pri,·ile~es o,rsu~cq~lenl ~~e of1he ~~e of(his.co~p:in)' or nny ~~berofils slnli, or reproducli°!! ~~this repo~ in ~on~ection .. \\.ilh lhe n~~er1ise~dl11, P~?mo1ie;n ~r ~nJe of ~!~~-~rod~I or p1.~ess, ~r in ~nn~c.tion w!th 1h~ r~·JH!l>licntion 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103541-024
Client Sample ID: TW4-70 _ 03182021
Collection Date: 3/18/2021 858h
Received Date: 3/19/2021 805h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L -----
Date
Analyzed
3/26/2021 011 h
3/20/2021 1313h
Contact: Tanner Holliday
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 38.7
E353.2 0.100 1.07
Report Date: 3/31/2021 Page 30 of 65
All analyses applicable to lhe CWA SOWA. and RCRA ore perfonncd in accordance to NELAC protocols. Pertinent sampling inrormation is located on the altached COC, Confidential Business Information: This report is provided for the exclusi\·e use of the
~ddressee Pri, ile~es o_f sub .. seq~ent ~~e or the ~~e of this .cm~pany or nny ~mbe1 of its slnff, or reproduclio~ ~f this repo~ in .con~eclion~ wilh the ~vertisement, P~?moti~n or sale of~!): ~rod~cl or p1.ocess, ~r in ~nn~c!ion w!th th~ r~-publication of lhis repon
American West ANALYTICAL LABO~ATOAIES
3440 South 700 West
ialt 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: 1st Quarter Chloroform 2021
Lab Sample ID: 2103706-002C
Client Sample ID: TW4-75_03222021
Collection Date: 3/22/2021 1230h
Received Date: 3/25/2021 l O 15h
Analytical Results
Analyzed: 3/25/2021 1303h
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
CAS
Number
56-23-5
67-66-3
74-87-3
75-09-2
Method:
Reporting
Limit
1.00
1.00
1.00
1.00
SW8260D
Analytical
Result
< 1.00
< 1.00
< 1.00
< 1.00
Qual
---------------
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual ----
Surr: I ,2-Dichloroethane-d4 17060-07-0
Surr: 4-Bromofluorobenzene 460-00-4
Surr: Dibromofluoromethane 1868-53-7
Surr: Toluene-d8 2037-26-5
54.2 50.00
46.0 50.00
52.4 50.00
52.1 50.00
108
92.0
105
104
80-136
85-121
78-132
81-123
Report Date: 3/31/2021 Page 14 of29
All nnnlyses epplicnble to lhe CWA. SOWA. and RCRA ore perrom1~ in RCcordance to NE LAC protocol rcnhicnt sampling ii~formntion is locnted on the ollnched COC. ConHdentinl Business lnfomuitlon: This repon is provided rct 1hc exclusive use of the
~ddressee Pri, ile~es o_f s1.1b .. seq~1ent ~1:e or lhe ~~e or this .co~pnny or ruiy t~~mber or its slnrf, or tcptoduch~ ~(1his repo~ in .coni1eclion,, "ith tho n~~'ertise~enl, p~~mo1io,n ~r ~aJo of ?'!Y. ~rodt'.cl t'lr pr~ess, ~r in ~nn~ciion w!lh 1h~ r~·J>~bJkntion of I his repofl
American West
ANALYTICAL LAB0RAT0RIE8
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: I st Quarter Chloroform 2021
Lab Sample ID: 2103706-002
Client Sample ID: TW4-75 _ 03222021
Collection Date: 3/22/2021 1230h
Received Date: 3/25/2021 IO 15h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L ---
Contact: Tanner Holliday
Date Method Reporting
Analyzed Used Limit
3/26/2021 107h E300.0 1.00
3/30/2021 IO 17h E353.2 0.100 --------
Analytical
Result Qual
37.4
< 0.100 --
Report Date: 3/31/2021 Page 6 of29
All anal) ses applicable lo lhe CWA. SOW A, and RCRA ore performed in accordance 10 NELAC protocol.s. Pc,1i11ent sampling informalion is located on the nllached COC. onOdc.ntial Business lnfonmtlion: This report is pro,•ided for the t\'<thnh•o use of the
~ddressee Pri, ile~es or sub .. seq~ent ~~e of lhe ~~t of this .con,1pnny or any 1~J!lber of its slalT, or 1~producti~! ~f 1his repo~ in ,coll!1cction .. with 1he u~~·ertise~ent, P~?moti~ ~~f\lt of ~!Y .. ~rod~ct or p1:?ces.s, ~r in ~onn!c!ion w!th th~ r1;-pubHC'tl1ion or lhis 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
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
I st Quarter Chloroform 2021
210263 l-Ol 7A
Client Sample ID: Trip Blank
Collection Date: 2/23/2021 800h
Received Date: 2/25/2021 1250h
Analytical Results
Analyzed: 2/26/2021 1018h
Units: µg/L
Extracted:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Dilution Factor:
----
1
Contact: Tanner Holliday
Test Code: 8260D-W-DEN100
VOAs by GC/MS Method 8260D/5030C
Method: SW8260D
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
--
Surrogate Units: µg/L CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
----
56.7
47.4
55.4
51.1
50.00 113 80-136
50.00 94.7 85-121
50.00 I II 78-132
50.00 102 81-123
ReportDate: 3/10/2021 Page38of46
All anal) ses applicable lo the CW A_ SDW A. and RCRA me perfom1ed in accordance to NE LAC pro1ocolt. f'c11mer1l sampling lnforrnr11im1 is located on lhe attnched COC. Confiden1ial Bu!iincs:s Information: This report is pro,'lded for the e.'i:clusiYe use of the
~ddressee Pri,·ile~es o! sub~seq~enl .u~e or the~~~ or this .co":p:my or nny ~mber or its staff, or rcptoduch~! ~t1his repo~ in f°"?r!<:llon_ \\ilh lhe ™!~'ertisemenl. P~?molio.n ~r ~ale of ~~r ~1odi~cl Qr p~CM. ~r in ~nn:c~on w!Lh th~ r~-p~blical.ion or lhis report
American West IINALVTICAL LABORATORIEI
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: 1st Quarter Chloroform 2021
Lab Sample JD: 2103541-025A
Client Sample ID: TRJP BLANK
Collection Date: 3/16/2021 815h
Received Date: 3/19/2021 805h
Analytical Results
Analyzed: 3/22/2021 1411 h
Units: µg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate Units: µg/L
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Extracted:
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Tanner Holliday
Test Code: 8260D-W-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
47.1 50.00 94.2 80-136
46.4 50.00 92.7 85-121
46.9 50.00 93.8 78-132
46.6 50.00 93.1 81-123
Report Date: 3/31/2021 Page 55 of65
All analyses npplicnble lo the CWA. SOWA. and RCRA are 1M!1rum1ed in accordance to NE LAC pro10®l,J. Porlineint s11mplln~ infommtion is localed on lhe nttnched COC. Conficlential Business lnrornuulon: This repon is provided for the Q~chti, rt USC' or the
~cldressee. PriYile~es o,rsub,,seq~1ent ~~e or lhe ~~1e of I his ,c°";lp&\\' or nnr 1~~ber or its stnfT, or rc1uoduc1i~~ ~f ihis roi:iOf_! in fOll~ection .. "ith the n~~·er1ise1~ent, P!?motio
1
n ~r ~ale of?'!>'. .~rod~ct ('f f)~ess, ~r in ~onn~c!ion w!th th~ r!-p~blktuiu11 or 1his report
American West
ANALYTICAL LAB0RATOR1E8
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-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2021
2103706-009A
Client Sample ID: Trip Blank
Collection Date: 3/22/2021 1230h
Received Date: 3/25/2021 1015h
Analytical Results
Analyzed: 3/25/2021 1538h
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
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
56.5 50.00
47.3 50.00
50.9 50.00
54.0 50.00
------
113 80-136
94.6 85-121
102 78-132
108 81-123
Report Date: 3/31/2021 Page 21 of29
All anolrses applicable to the CWA. SOW • ft.lul RCRA ore perfomn:d in accordance to NELAC ptotOC'ols. l'erffnent somplin11 infom1n1ion is located on the allnched COC. Conlidential Business Jnrormolion: This report is provided (or 1ho a"<ch.1:1h·o me or1he
~ddressee. PriYile~es or sub .. seq~1en1 ~~e of the ~?1.uc cf this .co1~ptmy or nny 1~mber of its staff, or rllprOOuc11or, ~r1his repo1~ in ~oniu~ction ... with the n~~'e11ise1~en1. P~?motio.n ~r ~ale of ?J!Y. ~roch~cl or P~?cess, ~r in ~nn~c!ion w!th lh~ r~·J>l;lbliccnion or 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
Tanner Holliday
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2021
Dear Tanner Holliday: Lab SetID: 2102631
American West Analytical Laboratories received sample(s) on 2/25/2021 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: 2021 .03.10
13:38:28 -07'00'
Laboratory Director or designee
Report Date: 3/10/2021 Page I of 46
All anal) ses applicable lo lhe CWA. SOW A. and RCRA are performed in accordance to NE LAC prolocols, Pertinenl sampling informalion is located on the altached COC Conridentinl Business [nformation; This report is provided for the exclusi,·e use of the
~dressee Pri,il~ or sub~seq~ent ~~e of the ~?1:"e of this .co~pany or an)' ~'!lber of its sin.ff, or reproduclio~ ~f I his repo~ in ~o~ection~ wilh I.he n~vertisement, P~?molio.n ~r sale of~!~ ~rodL~cl or p~ocess, ?r in ~onn~c~ion w~lh th~ r1;-publicalion or lhis repon
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2021
Lab Set ID: 2102631
Date Received: 2/25/2021 1250h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
2102631-00lA TW4-25 02232021 2/23/2021 926h Aqueous Anions, E300.0
Mt Lake City, UT 84119 2102631-00IB TW4-25 02232021 2/23/2021 926h Aqueous Nitrite/Nitrate (as N), E353.2
2102631-00 l C TW4-25 02232021 2/23/2021 926h Aqueous VOA by GC/MS Method
8260D/5030C
Phone:[phone] 210263 l -002A TW4-24_0223202l 2/23/2021 936h Aqueous Anions, E300.0
210263 l -002B TW4-24 0223202 l 2/23/2021 936h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 210263 l -002C TW4-24_02232021 2/23/2021 936h Aqueous VOA by GC/MS Method
Fax: (80 l) 263-8687 8260D/5030C
~-mail: [e-mail] 2102631-003A TW4-40_02232021 2/23/2021 1244h Aqueous Anions, E300.0
210263 l-003B TW4-40 02232021 2/23/2021 1244h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2 I 0263 I -003C TW4-40 02232021 2/23/2021 1244h Aqueous VOA by GC/MS Method
8260D/5030C
210263 l-004A TW4-39_0223202l 2/23/2021 1001h Aqueous Anions, E300.0
Kyle F. Gross 210263 l-004B TW4-39 0223202 I 2/23/2021 1001h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l -004C TW4-39 02232021 2/23/2021 1001h Aqueous VOA by GC/MS Method Laboratory Director 8260D/5030C
2102631-00SA TW4-19 02232021 2/23/2021 830h Aqueous Anions, E300.0
Jose Rocha 2102631-00SB TW4-19 02232021 2/23/2021 830h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2102631-00SC TW4-19_0223202l 2/23/2021 830h Aqueous VOA by GC/MS Method
8260D/5030C
2102631-006A MW-26_02232021 2/23/2021 1007h Aqueous Anions, E300.0
2102631-006B MW-26 02232021 2/23/2021 1007h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l -006C MW-26 02232021 2/23/2021 1007h Aqueous VOA by GC/MS Method
8260D/5030C
2102631-00?A TW4-01 02232021 2/23/2021 1216h Aqueous Anions, E300.0
210263 I -007B TW4-0l 02232021 2/23/2021 1216h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l-007C TW4-0l 02232021 2/23/2021 1216h Aqueous VOA by GC/MS Method
8260D/5030C
210263 l -008A TW4-21_02232021 2/23/2021 918h Aqueous Anions, E300.0
210263 l -008B TW4-21 02232021 2/23/2021 918h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l-008C TW4-21_02232021 2/23/2021 918h Aqueous VOA by GC/MS Method
8260D/5030C
2 I 0263 l-009A TW4-04_02232021 2/23/2021 1235h Aqueous Anions, E300.0
210263 l -009B TW4-04 02232021 2/23/2021 1235h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l -009C TW4-04 02232021 2/23/2021 1235h Aqueous VOA by GC/MS Method
8260D/5030C
2102631-0lOA TW4-41 02232021 2/23/2021 1226h Aqueous Anions, E300.0
Report Date: 3/10/2021 Page 2 of 46
All analyses applicable to the CWA, SOWA. and RCRA are performed m accordance to NELAC protocols_ Pertinent sampling information is located on the all ached COC Confidential Business lnformalion: This report is pro,•ided ror 1he exclusi,·e use of lhe
~ddressee Pri,·ile~es o.r sub,.seq~enl ~;e or lhe ~~e or this .co1~pany or any ~mber or its slaff, or reproductio~ ~r this repm; in ~o~ec11on" "ilh the ~,·ertise~ent, P~?motio.n ~r sale of ?1!Y. ~rodl~cl or P~?cess, ~r in 7onn~c.1io11 w!lh d~ ~·11~blica1ion or I his report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: l st Quarter Chloroform 2021
Lab Set ID: 2102631
Date Received: 2/25/2021 1250h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2102631-0108 TW4-4 l 0223202 l 2/23/2021 1226h Aqueous Nitrite/Nitrate (as N), E353 .2
3440 South 700 West 2102631-0lOC TW4-41 02232021 2/23/2021 1226h Aqueous VOA by GC/MS Method
8260D/5030C
~alt Lake City, UT 84119 2102631-01 lA MW-04_02232021 2/23/2021 1208h Aqueous Anions, E300.0
2102631-01 lB MW-04_ 02232021 2/23/2021 1208h Aqueous Nitrite/Nitrate (as N), E353.2
2102631-011 C MW-04 02232021 2/23/2021 1208h Aqueous VOA by GC/MS Method
Phone: [phone]D/5030C
2102631-012A TW4-02_02232021 2/23/2021 1026h Aqueous Anions, E300.0
Toll Free: [phone] 2102631-0128 TW4-02 02232021 2/23/2021 1026h Aqueous Nitrite/Nitrate (as N), E353.2
Fax: [phone] 210263 l-012C TW4-02 02232021 2/23/2021 1026h Aqueous VOA by GC/MS Method
!-mail: [e-mail] 8260D/5030C
210263 l-013A TW4-ll 02232021 2/23/2021 1016h Aqueous Anions, E300.0
web: www.awal-labs.com 2102631-0138 TW4-ll 02232021 2/23/2021 1016h Aqueous Nitrite/Nitrate (as N), E353.2
2102631-0l3C TW4-ll 02232021 2/23/2021 1016h Aqueous VOA by GC/MS Method
8260D/5030C
2102631-014A TW4-22 02232021 2/23/2021 944h Aqueous Anions, E300.0 Kyle F. Gross 2102631-0148 TW4-22_02232021 2/23/2021 944h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2102631-014C TW4-22 02232021 2/23/2021 944h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 2102631-015A TW4-37 02232021 2/23/2021 953h Aqueous Anions, E300.0
QA Officer 2102631-0158 TW4-37 02232021 2/23/2021 953h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l-015C TW4-37 02232021 2/23/2021 953h Aqueous VOA by GC/MS Method
8260D/5030C
210263 l-016A TW4-60 02232021 2/23/2021 800h Aqueous Anions, E300.0
2102631-016B TW4-60 02232021 2/23/2021 800h Aqueous Nitrite/Nitrate (as N), E353.2
210263 l-016C TW4-60 02232021 2/23/2021 800h Aqueous VOA by GC/MS Method
8260D/5030C
210263 l-017A Trip Blank 2/23/2021 800h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/10/2021 Page 3 of 46
All analyses applicable lo Jhe CWA. SOWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling i11formation is loca1ed on the au ached COC. Conlidential Business Inroniullon· This report is provided for 1he exclusi, e use of1he
~ddressee Pri, ile~es o,r sub .. seq~enl ~~e of the ~?':'le of this .cot~pany or nn) ~mber of its stnfT, or reproduclio~ ~f this repo~ in ~on~1eclion .. "ilh the n~Yertisement, P~?moliO,O ~r sale of ?';r ~roch~t or ~OS, ~r in ';°nn~.tion w~th lh~ r~-publication of lhis repon
3440 South 700 West
Mt 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 Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
1st Quarter Chloroform 2021
2102631
2/25/2021
2/23/2021
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.
Duplicate (DUP): The parameters that required a duplicate analysis had RPDs
within the control limits.
Corrective Action: None required.
Report Date: 3/ I 0/2021 Page 4 of 46
All analyses applicable to the CWA. SDW t MJ RCRA are perfo,med in accordance lo NELAC J)J'OIOCal'S, Penjncnl snm11linl::I, information is localed on the attached COC. onlidcntial Bu,incs1 Information: This report is prO\·ided for the oxdosh r use of 1he
~ddressee. Pri,·ile~es o,rsu~seq~nl ~1?e of tht~~H: ofd1is.crn~pany or nny ~mber ofilS Slaff, or rtproducu~!!rthis ,c:pot! n _con~\ection .. "ilh the a~~·ertise~enl. P~?moti~• '-'!I' ,Ale off!~~ rodJ~ct or P~?cess. ~r in ~nn:_c~ion w!lh lh~ r~-public.a1l11>11 or lhis repon
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
1st Quarter Chloroform 2021
2102631
2/25/2021
2/23/2021
Intact
None
SW-846 8260D/5030C
Volatile Organic Compounds
General Set Comments: One or more target analytes were observed above reporting
limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met, with CCV exceptions noted on the reprots. 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 2102631-001 C 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: 3/10/2021 Page 5 of 46
All analyses applicable lo the CWA. SOWA, and RCRA are per(om1ed in accordance to NELAC protocols Pertinenl sampling information is located on lhe au ached COC Confidential Business lnformalion: This repoI1 is pro,•lded nir 1ho rxdt15.l\'e use of the
~ddressee Pri, ile~es o_f sub,_seq~enl ~~e of 1he ~~e of lhis .con:ipnny or an) ,~~I!1ber of ils staff, or reproducli~ ~r 1his repo~ in ~0~1eclion .. \\·ilh lhe a<!~'ertisement, P~?"101io.n o.r saJe of ~Y ~rod~ct or p~ocess, ~r in ~nn~~ion w~lh 1h~ ~fk!blh:ailan of I his repon
American West
ANALYTICAL LAB0~AT0R1E9
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2102631
Project: 1st Quarter Chloroform 2021
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
QC SUMMARY REPORT
Contact:
Dept:
Tanner Holliday
WC
Method MDL
Reporting
Limit
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS-R149373 Date Analyzed: 03/02/2021 2348h
Test Code: 300.0-W
Chloride 5.07 mg/L E300.0 0.0198 0.100 5.000 0 IOI
Lab Sample ID: LCS-R149453 Date Analyzed: 03/06/2021 706h
Test Code: 300.0-W
Chloride 5.39 mg/L E300.0 0.0198 0.100 5.000 0 108
Lab Sample ID: LCS-R149514 Date Analyzed: 03/08/2021 2035h
Test Code: 300.0-W
Chloride 4.99 mg/L E300.0 0.0198 0.100 5.000 0 99.8
Lab Sample ID: LCS-R149229 Date Analyzed: 03/01/2021 1231h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.02 mg/L E353.2 0.00541 0.0100 1.000 0 102
Limits
90 -110
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 3/10/2021 Page 39 of 46
analyses applicable to the CWA, SDWA, and RCRA are pcrfonncd in accordoncc 10 NELAC protocols. Pertinent sampling infonnation is located on the attached COC Confidential Business lnfom,ation: This report is provided for the exclusive use of d10 addressee. Privileges of subsequent use of tr
ne of this company or any member of its staff, or reproductinn of tlus 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 otherthan for the .idd.r~~e will be granted only on contact. Thls
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2102631
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: MB-R149373 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R149453 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
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
03/02/2021 2320h
mg/L E300.0 0.0198 0.100
03/06/2021 638h
mg/L E300.0 0.0198 0.100
Tanner Holliday
WC
MBLK
Spike Ref.
Amount %REC
-Lab Sample ID: MB-R149514 Date Analyzed: 03/08/2021 2007h
Test Code: 300.0-W
Chloride <0.100 mg/L E300.0 0.0198 0.100
Lab Sample ID: MB-R149229 Date Analyzed: 03/0l/2021 1230h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100 mg/L E353.2 0.00541 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 3/10/2021 Page 40 of 46
analyses applicable to the CWA. SOWA, and RCRA are pl!ffonncd in accorda..ncc 1.0 NE.LAC prolocols Pertinent sampling information is located on the attached COC. Confidential Business lnfonnation: 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 oflhis report m conncclion \\1ith 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: 2102631
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
__ill: SUMMARY REPORT
Contact: Tanner Holliday
Dept: WC
Project: 1st Quarter Chloroform 2021 QCType: MS
Analyte Result Units Method
Lab Sample ID: 2102631-002AMS Date Analyzed: 03/03/2021 112h
Test Code: 300.0-W
Chloride 2,150 mg/L E300.0
Lab Sample ID: 2102631-014AMS Date Analyzed: 03/06/2021 925h
Test Code: 300.0-W
Chloride 1,710 mg/L E300.0
Lab Sample ID: 2102631-016AMS Date Analyzed: 03/08/2021 2130h
Test Code: 300.0-W
Chloride 9.93 mg/L E300.0
Lab Sample ID: 2102631-016BMS Date Analyzed: 03/01/2021 1303h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) l.07 mg/L E353.2
Lab Sample ID: 2102631-002BMS Date Analyzed: 03/01/2021 1242h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 92.9 mg/L E353.2
MDL
3.96
3.96
0.0396
0.00541
0.270
Reporting
Limit
20.0
20.0
0.200
0.0100
0.500
Amount Spiked Spike Ref.
Amount %REC
1,000 1170 98.2
l,000 618 109
10.00 0 99.3
l.000 0 107
50.00 41.9 102
Limits
90 -110
90 -110
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPD Qual
Report Date: 3/10/2021 Page 41 of 46
analyses applicable to the CWA. SOY/A, -nl.'ld RCRA are perfonncd in accordance to NE LAC proto.:ols. Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction oflhis report in connection with the advertisement promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
ANALYTICAL LABORATORIES QC SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 2102631 Dept: WC
Project: I st Quarter Chlorofonn 2021 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: 2102631-002AMSD Date Analyzed: 03/03/2021 140h
Test Code: 300.0-W
Chloride 2,160 mg/L E300.0 3.96 20.0 1,000 1170 98.6 90-110 2150 0.202 20
Lab Sample ID: 2102631-014AMSD Date Analyzed: 03/06/2021 953h
Test Code: 300.0-W
Chloride 1,700 mg/L E300.0 3.96 20.0 1,000 618 109 90 -110 1710 0.525 20
Lab Sample ID: 2102631-016AMSD Date Analyzed: 03/08/2021 215 8h
Test Code: 300.0-W
Chloride 9.98 mg/L E300.0 0.0396 0.200 10.00 0 99.8 90 -110 9.93 0.541 20
Lab Sample ID: 2102631-016BMSD Date Analyzed: 03/01/2021 1307h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.06 mg/L E353.2 0.00541 0.0100 1.000 0 106 90 -110 1.07 0.752 IO
Lab Sample ID: 2102631-002BMSD Date Analyzed: 03/01/2021 1243h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite {as N) 93.4 mg/L E353,2 0.270 0.500 50.00 41.9 103 90 -110 92.9 0.558 IO
Report Date: 3/10/2021 Page 42 of 46
analyses applicable to the CWA. SOWA, and RCRA are perfom1c(i!. in accof'dunce to NEW\C pro1ocols Pertinent sampling infonnation is located on the att~ched COC Confidential Business Inform:ttion: T111s report is provided for the exclusive use of the addressee. Privileges of sub~ent use of tt
ne of this company or any member of its staff, or reproduction of 1h1s report In connccnon wi1h lne 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 contac, This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2102631
Project: 1st Quarter Chloroform 2021
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84 I 19
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_Q C SUMMARY REPORT
Contact: Tanner Holliday
Method MDL
Reporting
Limit
Dept: MS VOA
QC Type: LCS
Amount Spiked Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-1 022621A Date Analyzed: 02/26/2021 723h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-2 022621A
Test Code: 8260D-W-DEN I 00
Chloroform
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
18.6 µg/L SW8260D
20.3 µg/L SW8260D
14.8 µg/L SW8260D
19.7 µg/L SW8260D
52.3 µg/L SW8260D
48.7 µg/L SW8260D
53.1 µg/L SW8260D
51.2 µg/L SW8260D -Date Analyzed: 02/26/2021 659h
19.4 µg/L SW8260D
50.6 µg/L SW8260D
49.5 µg/L SW8260D
52.8 µg/L SW8260D
51.8 µg/L SW8260D
0.785 1.00 20.00 0 93.2
0.360 l.00 20.00 0 102
0.682 1.00 20.00 0 73.8
0.451 1.00 20.00 0 98.7
50.00 105
50.00 97.4
50.00 106
50.00 102
0.360 1.00 20.00 0 97.0
50.00 101
50.00 99.0
50.00 106
50.00 104
Limits
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
74 -120
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPD Qual
Report Date: 3/10/2021 Page 43 of 46
. analyses applicable to the CWA, SOW A, and RCRA are perfonned in accoldone<' to NEL,\C protocols Pertinent sampling infonnation is located on the attached COC Confidential Business lnform11tion: Th is 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 reproduct10110(1h1s 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 ndd~sce will be granted only on contact. This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2102631
Project: 1st Quarter Chlorofonn 2021
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-1022621A Date Analyzed: 02/26/2021 743h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Lab Sample JD: MB VOC-2 022621A
Test Code: 8260D-W-DEN100
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
< 1.00
< 1.00
< 1.00
< 1.00
54.7
49.8
54.4
52.6
Date Analyzed:
< 1.00
50.0
50.4
50.6
51.7
µg/L SW8260D 0.785 1.00
µg/L SW8260D 0.360 1.00
µg/L SW8260D 0.682 1.00
µg/L SW8260D 0.451 1.00
µg/L SW8260D 50.00 109
µg/L SW8260D 50.00 99.7
µg/L SW8260D 50.00 109
µg/L SW8260D 50.00 105
02/26/2021 718h
µg/L SW8260D 0.360 1.00
µg/L SW8260D 50.00 100
µg/L SW8260D 50.00 101
µg/L SW8260D 50.00 101
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
RPD Ref. RPD
Limit Amt %RPO Qual
Report Date: 3/10/2021 Page 44 of 46
analyses appl,cnble 10 the CWA. SDWA, and RCRA are performed in accordance 10 NE LAC protocols. Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee. Privileges of sub~quent use of tr
ne of this corn pan) or nny 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 Olhar than fort.he addressee will be granted only on cootacl. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2102631
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2102631-001 CMS Date Analyzed:
Test Code: 8260D-W-DEN!OO
Carbon tetrachloride 23.9
Chloroform 24.2
Chloromethane 16.8
Methylene chloride 22.8
Surr: l,2-Dichloroethane-d4 52.8
Surr: 4-Bromofluorobenzene 44.9
Surr: Dibromofluoromethane 52.5
Surr: Toluene-d8 50.1
Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
MS
Spike Ref.
Amount %REC
02/26/2021 920h
µg/L SW8260D 0.785 1.00 20.00 0 120
µg/L SW8260D 0.360 1.00 20.00 0 121
µg/L SW8260D 0.682 1.00 20.00 0 83.8
µg/L SW8260D 0.451 1.00 20.00 0 114
µg/L SW8260D 50.00 106
µg/L SW8260D 50.00 89.9
µg/L SW8260D 50.00 105
µg/L SW8260D 50.00 100
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
66 -143
74 -120
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: 3/10/2021 Page 45 of 46
analyses app11~blc tu 1he CWA, SDWA, and RCRA are pcrfonncd in accord:mce to NE:LAC prolocols. Pertinent sampling infonnntton 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 comp:\n)' or nn)' member of its staff, or reproduction of U,1s report in conncc.tion wnh 1h.c advertisement, promotion or g;i]c 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: 2102631
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2102631-00lCMSD Date Analyzed:
Test Code: 8260D-W-DENIOO
Carbon tetrachloride 24.8
Chloroform 24.6
Chloromethane 17.8
Methylene chloride 23.3
Surr: l ,2-Dichloroethane-d4 55.4
Surr: 4-Bromofluorobenzene 48.4
Surr: Dibromofluoromethane 54.7
Surr: Toluene-d8 51.5
Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Method MDL Limit
Tanner Holliday
MSVOA
MSD
Spike Ref.
Amount %REC
02/26/2021 939h
µg/L SW8260D 0.785 1.00 20.00 0 124
µg/L SW8260D 0.360 1.00 20.00 0 123
µg/L SW8260D 0.682 1.00 20.00 0 89.2
µg/L SW8260D 0.451 1.00 20.00 0 117
µg/L SW8260D 50.00 Ill
µg/L SW8260D 50.00 96.8
µg/L SW8260D 50.00 109
µg/L SW8260D 50.00 103
' -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
66 -143
74 -120
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
23.9 3.33 35
24.2 1.68 35
16.8 6.30 35
22.8 2.30 35
Qual
Report Date: 3/10/2021 Page 46 of 46
analyses applicable to the CWA. SDWA, and RCRA nre pcrfonncd m accordarn:c 10 NELAC pro1ocols Pertinent sampling information is located on the attached COC. Confidential Business lnfom1ation: This report is provided for tl1e exclusive use of the addressee Privileges of subsequent use oftt
ne of this company or any member of its staff, OUt:product1on of this report in eonncc.ucm wi1h the advertisement. promotion or sale of any product or process. or in connection with the re·publication of this report for any purpo.st Other than for the addressee will be granted only on contact. This
'
American West Analytical Laboratories Rpt Emailed: UL
Denison
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
Client ID: ENE300
Project: 1st Quarter Chloroform 2021
Comments: QC 3 (no chromatograms). EDD-Denison.
Sample ID Client Sample ID
2102631-00IA T\\14-25~02232021
2102631-00IB
2102631-00lC
2102631-002A T\\14-24_02232021
2102631-0028
2102631-002C
2102631-003A T\\14-40_02232021
2102631-0038
210263 l-003C
2102631-004A T\\14-39 _02232021
2102631-0048
2102631-004C
2102631-00SA T\\14-19_02232021
------·
2102631-00SB
2102631-00SC
Contact: Tanner Holliday
QC Level: III
WorkOrder: 2102631
Due Date: 3/11/2021
WO Type: Project
Page 1 of3
CC [e-mail]; (USE PROJECT for special DLs). Do not use "*R_" samples as MS/MSD.;
Collected Date Received Date Test Code Matrix Sel Storage
2/23/2021 0926h 2/25/2021 1250h 300.0-W Aqueous
1 SEL Analytes: CL
N02/N03-W-353.2
I SEL Analytes: N03N02N
8260D-W-DENIOO
Test Group: 8260D-W-DENI00; # of Analytes: 4 /#of Surr: 4
2/23/2021 0936h 2/25/2021 1250h 300.0-W Aqueous
I SEL Analytes: CL
N02/N03-W-353.2
l SEL Analytes: N03N02N
8260D-W-DEN100
Test GrouJJ_: 8260D-W-DENJOO; # of Analytes: 4 I# ofSurr: 4
2/23/2021 1244h 2/25/2021 1250h 300.0-W Aqueous
I SEL Analytes: CL
N02/N03-W-353.2
I SEL Analytes: N03N02N
8260D-W-DEN100
Test Group: 8260D-W:DENIOO; # of Analytes: 4 /# of Surr: 4
2/23/2021 lOOlh 2/25/20211250h 300.0-W Aqueous
I SEL Analytes: CL
N02/N03-W-353.2
1 SEL AnalJ,tes: N03N02N
8260D-W-DEN100
Test Group: 8260D-W-DENIOO; # of Analytes: 4 I# of Surr: 4
2/23/2021 0830h 2/25/2021 1250h 300.0-W
---------------l SEL Analytes: ~L
N02/N03-W-353.2
. ·-_ _ I SEL Analytes: N03N02N
8260D-W-DEN100
Aqueous
Test Group:_§260D-W-DENIOO; # of Analytes: 4 I# of Surr: 4
df-wc
df-no2/no3
VOCFridge
df-wc
df-no2/no3
VOCFridge
df-wc
df-no2/no3
VOCFridge
df-wc
df-no2/no3
voe.Fridge
df-wc
df-no2/no3
VOCFridge
3
3
3
3
3
Printed: 02/25/2 I 16:0 I LABORATORY CHECK: %M -, RT --:, CN '. -, TAT CJ QC [_::, LUO~-: HOK__ HOK __ _ HOK___ COC Emailed 'lv./J..
WORK ORDER Summary WorkOrder: 2102631 Pa.ge 2 of3
Client: Energy Fuels Resources, Inc. Due Date: 3/11/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2102631-006A MW-26_02232021 2/23/2021 I 007h 2/25/2021 1250h 300.0-W Aqueous df -\VC
I SELAnalytes: CL -"·-------2102631-0068 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
210263 l-006C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
2102631-007A TW4-01_02232021 2/23/20211216h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2102631-0078 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
210263 l-007C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
2102631-00SA 1W4-21_02232021 2/23/2021 0918h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2102631-0088 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2102631-00SC 8260D-W-DEN100 VOCFridge 3
Test Group"· 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
2102631-009A TW4-04_02232021 2/23/2021 1235h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes"· CL -···-2102631-0098 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
210263 l-009C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJ 00; # of Analytes"· 4 I # of Surr: 4
2102631-0IOA TW4-41_02232021 2/23/2021 1226h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2102631-0108 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2102631-01 oc 8260D-W-DEN100 YOCFridge 3
Test Group: 8260D-W-DENI00; # of Analytes: 4/# ofSurr: 4
2102631-0llA MW-04_02232021 2/23/2021 1208h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SELAnalytes: CL
2102631-0llB N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
2102631-0IIC 8260D-W-DEN100 YOCFridge 3
-•··--·--Test Group: 8260D-W-DENIOO; # of Analytes: 4 / # ofSurr: 4
Printed: 02/25/21 16:0 I LABORATORY CHECK: o/oM --RT [j CN =:J TAT= QC "-" Luo::= HOK ___ HOK ___ HOK ___ COC Emailed
WORK ORDER Summary Work Order: 2102631 Page3 of3
Client: Energy Fuels Resources, Inc. Due Date: 3/11/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2102631-012A T\\'4-02_02232021 2/23/202 J l 026h 2/25/2021 1250h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2102631-0128 N02/N03-W-353.2 df-no2/no3
1 SEL Ana/ytes: N03N02N
2102631-012C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Ana/ytes: 4 I # of Surr: 4
2102631-013A TW4-11_02232021 2/23/2021 1016h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2102631-013B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2102631-0BC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 4 /#ifS;,:,._. 4 ·
2102631-014A T\\'4-22_02232021 2/23/2021 0944h 2/25/2021 1250h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2102631-014B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2102631-014C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Ana/ytes: 4 I# ofSurr: 4
2102631-0lSA TW4-37_02232021 2/23/2021 0953h 2/25/2021 1250h 300.0-W Aqueous elf-WC
I SEL Analytes: CL
2102631-0158 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2102631-0lSC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
2102631-016A TW4-60_02232021 2/23/2021 0800h 2/25/2021 1250h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
210263)-0168 N02/N03-W-353.2 df-no2/no3
1 SEL Ana/ytes: N03N02N
2102631-016C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I # ofSurr: 4
210263J-Ol7A Trip Blank 2/23/2021 0800h 2/25/2021 1250h 8260D-W-DENIOO Aqueous VOCFridge 3
Test Group_: 8260D-W-DENI00; # of Al1(1_lytes: 4 /# ofSurr: 4
Printed: 02/25/21 16:0J LABORATORY CHECK: %M -: RT !J CN ~ TAT C"""! QC l--~ LUO" HOK~~ HOK __ _ HOK___ COC Emailed~----
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# (801 ) 263-8686 Toll Free# [phone]
CHAIN OF CUSTODY
All analysis will be conducted ueing NELAP accredned methods end all data will be reported using AWAL's standaJd analyte lists and reporting
Umlts (POL.) unless speciflcally requested otherwise on this Chain of Custody and/or attached documentation.
2./ d 2..(c 3L
AWAL Lab Sample Set#
Page 1 of 2
6 ---~ Fax#[phone] Email awal@awal~abs.com I QC Level: II TumAroundTlme: I Unlessotherarrangementshavebeenmade, IDueDate: I
signed raports v.,11 be emailed by 5:00 pm on
www.awal-labs.com 3 Standard the day they are due.
Client: Energy Fuels Resources, Inc. X Include EDD: Laboratory Use Only
Address· 6425 S. Hwy. 191 ~CCUSELUPLOAD ,,1....-. -Samples Wen,:I...A r _,,
Blanding UT 84511 Field Filtered For. -...
, ,e-handdollvorod
contact· Tanner Holliday ~ • 2 Arobionl~
[phone] ForComplianceWith: / q Phone#: Cell#: 0 NELAP 3 Tompom!Un> I { •c
Email· thoWda:,@energyfaeJs.c,om; [e-mail] D RCRA ---. D CWA • Rocelved 8rolton/l."""'9
1 t Quart Cbl f, 2021 0 SOWA (Improperly sealed) Projecl Name: 5 er oro orm. 0 ELAP / A2LA y /;;i,
o' 0 NLLAP V
Project#: <'j' 0 0 Non-Compriance s c[: Pms.<vod.
f;'.l Cl "' 0 Other. y N
PO#: I!! >< (2. ';:: g edatbo'1dl
T B llida :g :S C'l o IO Y N Sampler Name: anner O Y ·;;; "' O Cl C'I .---...;. _____ ================::;:p=====.::====I c: :. 11; ~ ~ Known Hazards a Received Wlthtn
O CD ......_ ~ CO ~Id. Ti Date Time u a. N ...__ U & 'Ing ,mes 'oEo-o vi N Sample ID: Sampled Sampled .. ,,i 11; U :> Sample Comments
TW4-25_02232021 2/23/2021 926 5 W X X X
TW4-24_02232021 2/23/2021 936 s W X X X
t-------------------------+-----+-----,t--t--,t--1--1---f--+--+-+-+-+-+-+-+---f~------------UCOCTopeWas:
' TW4-40_02232021 2/23/2021 1244 5 W X X X 1 ~onOuterPackage ~ N NA
TW4-39_02232021 2/23/2021 1001 5 W X X X 2 ),ljken on Outer Pad(age
TW4-19_02232021 2/23/2001 830 5 W X X X C N NA
6 MW•26_02232021 2/23/2001 1007 S W X X X 3 PresenlonSampte !":~
y N ~
TW4-01_02232021 2/23/2021 1216 s W X X X 4 Unbroken on Sample r \
TW4-21_02232021 2/23/2021 918 5 W X X X y N ~)
TW4-04_02232021 2/23/2021 1235 S W X X X DiscrepanciesBetweenSample
I TW4-41 02232021 2/23/2021 1226 5 W X X X Labels and COC Record/,;\
-y LI
I HW-04_02Z32021 2/23/2021 1208 S W X X X
! TW4-02_02232021 2/23/2021 1026 5 W X X X
1 TW4-11_02232021 2/23/2021 1016 5 W X X X
R~"'od t,y: -1 / fl hi /, ,..... Doto: Received by: Oate: S . I I tr t· """'"'u,• \,. .. ~oA' , • ,1 2/U/202t s ianaturo pec1a ns uc ions:
V ~ = Prf11I Name: Tan PO!'""""'-it 00 Prtnt Name: 1
R.Unqu!lhed t,y: Date, R""'"•od ~/' {' 1 /I / l . ,I o.te: , /. _ -/ / See the Analytical Scope of Work for Reporting Limits and VOC
ISlonatui, Sl•naturo 7 '. ..i' ' '· -· .1 ""' l ;l, '.'.> 'Z..... analyte list
Pl1ntNamo: ITTmtr. Prial Namo: ;f_/ /A'1 ?... -,:r;,. ""'0 ~-7 / ~ime: / '2-•;r (;,
Rollnqtd-by: 0$<1: Received by: I Oale:
L"1anotura Isla nature
(T1mo: IT'me:
Prlnt Name: Pr1nl Name:
RolOlqulshod by. Doto: Received by: Date:
l~111naturo Sia nature
I"'"'" Time: Pdnl NAmo: lPrint Name:
-
Address:
Contact:
Phone#'.
Emal:
Project Name:
Project#'.
PO#'.
Sampler Name:
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Toll Free# [phone]
6425 S. Hwy. 191
Blanclfng, UT 84511
Tanner Holliday
[phone] Cell#'.
tholHday@maergyfnel.s.c,c,m; [e-mail]
1st Quarter Chloroform 2021
Tanner Holliday
Dale
Samele ID: Samoled
,
1 TW4-22_02232021 2/23/2021
; TW4-37_02232021 2/23/2021
I TW4-60_02232021 2/23/2021
'TRIP BLANK 2/23/2021
I
1
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l""',oqui&lied by: 1saannru,.
Dato:
T"tmo:
IPrlntN.omo:
I
Time
Samoled
944
953
800
800
Received by:
~ .. -
CHAIN OF CUSTODY
All analysis will be conducted using NEVJ' 3Celedi!od m1101ods and all data win be _.toil uolng AW~'o standard anafyte llsls and reporting
limits (Pal) unless ll)OdrK:O!ly mquested ·-on !his Clulin or Cuotody ondlot ·-documenlalion.
QC Level:
II
Tum Around Time: I Unless other amingements have ~ made,
3 Standard ~-~~-•o•m•••• tha day they era due.
X Include EDD:
LOCUS UPLOAD
EXCEL
F',eld Filtered For:
For Compliance With:
D NELAP
D RCRA
D CWA
D SDWA
0 ELAP/A2LA
C) 0 NLLAP
~ c:i D N~ompfiance ~ Q D' D Other. l") I!! ~ .... Q " >< 0 IC c:: ·c:: l'l '1ii .. 0 Q C"I
'E :; z Q ~ Known Hazards 0 " l/) ..... ~ .. 0 C. N 0 & 0 E 0 0 g "' z Sample Comments "" CJ)
5 w X X X
5 w X X X
5 w X X X
3 w X
Oate: Special Instructions:
Tlmo:
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AWAL Lab Sample Set#
Page 2 of 2
l°"•Da<oa I
Laboratory Use Only
Samples Were:\...( /?.5
1 e Of tiond d:rivo .. ,:I
2-Gi
a Tamp()nl!ute / • i •c
4 Received Brokenlleaking
(lmpropMy Seal~
y N
5 ctrrfy Preserved N
Checked at bench
y N
6 Received Within
~) Holding Times
y
COC Tape Was: , 0_ on 01.(erPad<age
y I N NA
C'kon on Outer Package
YJ N NA
3 Present on Sample G,.i y N
4 Unbroken on Sample
y N E1
Ofscnlpancies Betwoen Sample
Labels e.nd COC Record?
y <9
PrlntN""*
R-.od by: ~ /1/1 . f l . / IOatoii._ /~tf'(i.. / See the Analytical Scope of Work for Reporting Limits and VOC
L<a<anat1.<e analyte list.
2-I vvi &,,. 1../,.._ J IA.--d ITlmo: I z &"°1.) Prim Nomo:
Received by: I \ Date:
Sfanature
nme:
Print Name:
IReceiVed by: Oale:
l~fnnature
Time:
Print Name:
Analysis
Ammonia
COD
<:vanide
Metals
NOifN03
O&G
Phenols
Sulfide
TKN
TP04
Cr VI+
Procedure:
Frequency:
Preservation Check Sheet
s le Set Ext
Preservative 1 7-. 3 '-I .,-
oH<2 H2S04
oH<2H2S04
nH>lONaOH
oH<2HN03
oH <2H2S04 \/,,<, Ve~ ~' ~I ,/,,r
oH<2HCL , r /'
0H<2H2S04
nH >9 NaOH. ZnAC
oH <2 ffiS04
nH<2H2S04
oH>9 (NH4h,S04
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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If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
A
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference .
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rev 10-28-2020
American West AIO.IVTICAL LAOOqATORl!9
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 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2021
Dear Tanner Holliday: Lab Set ID: 2103541
American West Analytical Laboratories received sample(s) on 3/19/2021 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 0$8 . by Jose G.
Rocha Rocha Date: 2021.03.31
16:34:54 -06'00'
Laboratory Director or designee
Report Date: 3/31/2021 Page I of 65
All onnlyses np1)llcible lo lhe CWA. SDWA, And RCRA are l)~fomled in &ecordance 10 NELAC protocols. Pertinenl sampling i1\lbrmntion is locn1ed on the nunched CDC. ConI1chm\ln\ Business Jnrormution: This report is pro,•ided for 1ho exclush·e use of the
~ddressee. Prhile~ o; sub .. seq~1ent ~1~e of the ~~1c or this .con.1pan~· or nny 1~~ber of its stalT, Of rcproduclio~ ~~this repo~ in .coni1ection .. \\ith lhe n<!"ertise1~1ent, P~?molio.n ~r ~ale of ~!Y. ~rodl)C:I or P~?Cess, ~r in ~nn!c~ion w(th 1h~ '!·pul.ilication of lhis report
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANAlVTICAl LllBO~ATOAIF8 Project: 1st Quarter Chloroform 2021
Lab Set ID: 2103541
Date Received: 3/19/2021 805h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West 2103541-00lA TW4-03R 03162021 3/16/2021 815h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2103541-00lB TW4-03R 03162021 3/16/2021 815h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-00lC TW4-03R 03162021 3/16/2021 815h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 210354 l-002A TW4-03 03172021 3/17/2021 732h Aqueous Anions, E300.0
210354 l-002B TW4-03 03172021 3/17/2021 732h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 210354 l-002C TW4-03 03172021 3/17/2021 732h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260D/5030C
!-m11il: [e-mail] 2103541-003A TW4-42 03172021 3/17/2021 747h Aqueous Anions, E300.0
2103541-003B TW4-42 03172021 3/17/2021 747h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2103541-003C TW4-42 03172021 3/17/2021 747h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-004A TW4-28 03172021 3/17/2021 757h Aqueous Anions, E300.0
Kyle F. Gross 2103541-004B TW4-28 03172021 3/17/2021 757h Aqueous Nitrite/Nitrate (as N), E353.2
210354 l-004C TW4-28_03 l 7202 l 3/17/2021 757h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2103541-005A TW4-32 03172021 3/17/2021 804h Aqueous Anions, E300.0
Jose Rocha 210354 l-005B TW4-32 03172021 3/17/2021 804h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 210354 l -005C TW4-32 03172021 3/17/2021 804h Aqueous VOA by GC/MS Method
8260D/5030C
210354 l-006A TW4-12 03172021 3/17/2021 81 lh Aqueous Anions, E300.0
210354 l-006B TW4-12 03172021 3/17/2021 81 lh Aqueous Nitrite/Nitrate (as N), E353.2
210354 l-006C TW4-12 03172021 3/17/2021 81 lh Aqueous VOA by GC/MS Method
8260D/5030C
2103541-007 A TW4-13 03172021 3/17/2021 819h Aqueous Anions, E300.0
2103541-007B TW4-13 03172021 3/17/2021 819h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-007C TW4-13 03172021 3/17/2021 819h Aqueous VOA by GC/MS Method
8260D/5030C
2 I 03541-00SA TW4-36 03172021 3/17/2021 826h Aqueous Anions, E300.0
2103541-00SB TW4-36 03172021 3/17/2021 826h Aqueous Nitrite/Nitrate (as N), E353.2
210354 l-008C TW4-36 03172021 3/17/2021 826h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-009A TW4-3 l 03172021 3/17/2021 834h Aqueous Anions, E300.0
210354 l-009B TW4-31 03172021 3/17/2021 834h Aqueous Nitrite/Nitrate (as N), E353.2
2 I 0354 l-009C TW4-31 03172021 3/17/2021 834h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-0IOA TW4-34 03172021 3/17/2021 842h Aqueous Anions, E300.0
Report Date: 3/31/2021 Page 2 of 65
All nnnlyscs applicnble to !he CWA. SOWA, Md RCRA are perfomu:d in nccordnnce 10 NELAC protocols. Pertinent snmpling h1formntion is located on the nttnched COC. C'onflrlentinl Business lnfom\lltlon: This repon is prm•ided for the exclusi, e use of the
~ddressee Pri\'ile~es o,rsul!seq~1ent ~1;e of the ~~1e of this .co1~pnny or nny 1~~~ber of its stnlT, or reptoduclio~ ~~this repo~ in ~on~ection .. \\ith the n~~'erlise~ent. P~?motio.n ~r ~ale of !'1!Y. ~rod1~ct or p,,ocess, ~r in ~onn~iion w!lh lh~ r~-p~blicnlion of this rtporl
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: 1st Quarter Chloroform 2021
American West Lab Set ID: 2103541
ANAi YTICAL I AB0R"-TOR1t9 Date Received: 3/19/2021 805h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2103541-0lOB TW4-34 03172021 3/17/2021 842h Aqueous Nitrite/Nitrate (as N), E353.2
3440 South 700 West 2103541-0lOC TW4-34 03172021 3/17/2021 842h Aqueous VOA by GC/MS Method
8260D/5030C
;alt Lake City, UT 84119 2103541-01 lA TW4-35_03 I 72021 3/17/2021 850h Aqueous Anions, E300.0
2103541-0l lB TW4-35 03172021 3/17/2021 850h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-0l lC TW4-35 03172021 3/17/2021 850h Aqueous VOA by GC/MS Method
Phone:[phone]D/5030C
210354l-012A TW4-23 03172021 3/17/2021 900h Aqueous Anions, E300.0
Toll Free: [phone] 2103541-0 l 2B TW4-23_03172021 3/17/2021 900h Aqueous Nitrite/Nitrate (as N), E353.2
Fax:[phone] 2103541-012C TW4-23 03172021 3/17/2021 900h Aqueous VOA by GC/MS Method
!-mai I: [e-mail] 8260D/5030C
2103541-013A TW4-65 03172021 3/17/2021 732h Aqueous Anions, E300.0
web: www.awal-Jabs.com 210354 l-OJ 3B TW 4-65 _ 031 72021 3/17/2021 732h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-013C TW4-65 03172021 3/17/2021 732h Aqueous VOA by GC/MS Method
8260D/5030C
210354 l-Ol4A TW4-38 03182021 3/18/2021 812h Aqueous Anions, E300.0 Kyle F. Gross 2103541-0 l 4B TW4-38 03182021 3/18/2021 812h Aqueous Nitrite/Nitrate (as N), E353.2
Laboratory Director 2 l03541-014C TW4-38 03182021 3/18/2021 812h Aqueous VOA by GC/MS Method
8260D/5030C
Jose Rocha 210354l-015A TW4-l4 03182021 3/18/2021 823h Aqueous Anions, E300.0
QA Officer 2l0354l-Ol5B TW4-14 03182021 3/18/2021 823h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-015C TW4-14 03182021 3/18/2021 823h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-016A TW4-06 03182021 3/18/2021 834h Aqueous Anions, E300.0
2103541-0 l 6B TW 4-06 03182021 3/18/2021 834h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-016C TW 4-06 03 I 82021 3/18/2021 834h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-0l 7A TW4-27 03182021 3/18/2021 844h Aqueous Anions, E300.0
2103541-0l 7B TW4-27 03182021 3/18/2021 844h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-017C TW4-27_03182021 3/18/2021 844h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-0l 8A TW4-05 03182021 3/18/2021 853h Aqueous Anions, E300.0
2103541-018B TW4-05 03182021 3/18/2021 853h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-018C TW4-05 03182021 3/18/2021 853h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-019A TW4-09 03182021 3/18/2021 858h Aqueous Anions, E300.0
2103541-0 l 9B TW4-09_0318202l 3/18/2021 858h Aqueous Nitrite/Nitrate (as N), E353.2
2 l0354l-Ol9C TW4-09 03182021 3/18/2021 858h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2021 Page 3 of 65
All e.nnl)'ses applicnbluo 1hc CWA. SOWA. Md RCRA nre perrormed in accordance to NELAC prolocols. Penintnt s(lrTlpling infomm1ion is localed on the atlnched COC. onOdtntiol Butmoss Jn1"omu11lon: This report is prO\·ided for 1he o,\clus:h~ ut:e or the
~ddress1:e. PriYile~es 6f Jul~q~1en1 ~,~e or lhe ~~1e or this .ccll~pm1y or ony 1~mber or ils s1nff, or reproducti~ ~f 11lis repo~ in 7011~1ection ... wilh lhe n~~'ertise~enl, P~?moti~ ~ u le of ~!Y r od~ct 01 p1~ess, ~r in ~nn~c~ion w!th th~ r~-p~btiCQlion of this report
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Project: I st Quarter Chloroform 2021
Lab Set ID: 2103541
Date Received: 3/19/2021 805h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
2103541-020A TW4-08 03182021 3/18/2021 912h Aqueous Anions, E300.0
3440 South 700 West 2103541-020B TW4-08 03182021 3/18/2021 912h Aqueous Nitrite/Nitrate (as N), E353.2
~alt Lake City, UT 84119 210354 l-020C TW4-08 03182021 3/18/2021 912h Aqueous VOA by GC/MS Method
8260D/5030C
2103541-021A TW4-18_03182021 3/18/2021 923h Aqueous Anions, E300.0
2103541-02IB TW4-18 03182021 3/18/2021 923h Aqueous Nitrite/Nitrate (as N), E353.2
Phone: [phone] 2103541-021C TW4-18 03182021 3/18/2021 923h Aqueous VOA by GC/MS Method
8260D/5030C
Toll Free: [phone] 2103541-022A TW4-33 03182021 3/18/2021 935h Aqueous Anions, E300.0
Fax:[phone] 210354 l-022B TW4-33_03182021 3/18/2021 935h Aqueous Nitrite/Nitrate (as N), E353.2
:-mail: [e-mail] 210354 l-022C TW4-33 03182021 3/18/2021 935h Aqueous VOA by GC/MS Method
8260D/5030C
web: www.awal-labs.com 2103541-023A TW4-30 03182021 3/18/2021 944h Aqueous Anions, E300.0
210354 l-023B TW4-30_03182021 3/18/2021 944h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-023C TW4-30 03182021 3/18/2021 944h Aqueous VOA by GC/MS Method
Kyle F. Gross 8260D/5030C
2103541-024A TW4-70 03182021 3/18/2021 858h Aqueous Anions, E300.0
Laboratory Director 210354 l-024B TW4-70 03182021 3/18/2021 858h Aqueous Nitrite/Nitrate (as N), E353.2
2103541-024C TW4-70 03182021 3/18/2021 858h Aqueous VOA by GC/MS Method
Jose Rocha 8260D/5030C
QA Officer 210354 l-025A TRIP BLANK 3/16/2021 815h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2021 Page 4 of 65
All analyses applicable 10 tht CWA. SOWA. Md RCRA are perf'omted in accordance lo NELAC pro1oco\s. Prnfn,nt saniphny infonnalion is locpted on the nllnched COC. Conlidl•nlial Business lnfonnntion: This report is prm•ided for the r:~:clnsh·t l.Gc oilhe
~ddressee. Pri\'ilc~es a:sub,.seq~ent ~1~e of the ~~i;ne of this 1co1~pany or MY 1~~~ber of its staff, or rcproductl~ ~f1his RPO'! in 7on?eclion ... "'ilh the n<!~'erCise1"?en1, P~?moti~l or~o.Jcof?'l>: rro<h'.cl or P~?cess, ~r in ~nn~.tion \\'!lh th~ r~-puhlictuion of1his reporl
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 Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
1st Quarter Chloroform 2021
2103541
3/19/2021
3/16-3/18/2021
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.
Duplicate (DUP): The parameters that required a duplicate analysis had RPDs
within the control limits.
Corrective Action: None required.
Report Date: 3/31/2021 Page 5 of 65
All analyses applicable to lhe CWA. SDW >\, nnd rt llA are perrom,ed in accordance to NELAC pmaocols. Pcn.mrnt samplinij infornuuioo is located on the atlnched COC. ('onOdMlinl Ou3'irwss lnformnlion: This report is pro"ided ror IDa os.clutiYe use of the
~ddressee. Privile~es o,r sub,.seq~enl ~1~e or the ~:'1.nc or this .co1~pnny or nny 1~~ber of its stnff, or 11.-pl'oducU~ ~r1his rc::PGI'! in fOn~cc1lon_. "·ith the «'!~·er1ise1~en1. P~?mo1io:,1 ~r lfl)~ of~~-f'Odl~ct or P~?CC5S, ~rill ~1m~!ion \\'!th 1h~ 1~1>uhlini.dot\ 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
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Tanner Holliday
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
1st Quarter Chloroform 2021
2103541
3/19/2021
3/16-3/18/2021
Intact
None
SW-846 8260D/5030C
Analysis: Volatile Organic Compounds
General Set Comments: One or more 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 BJanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike / Matrix Spike Duplicate (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, indicating no
apparent matrix interferences.
Surrogates: All surrogate recoveries were within established limits.
Corrective Action: None required.
Report Date: 3/31/2021 Page 6 of 65
All Mlllyses Rpplicablc 101hc CWA. SDWA, and RCRA are performed in accordance to NELAC p,o.1ucols. Pcnmrot s~m1t1in~ informotion is locoled on the ullached COC. Co11fld1:111th,l Business Information: This reµon is pro,•ided ro, \hc-c-.clush1,1 uie or the
~ddressee. PriYile~es of iub_!cici~ent ~1fe or \he ~~\e or1his .coi~puny or ru,y '~!'!'her or its staff, or IC?IUoducti ~ ~rthis ropd'! in ~on~eclion ... "ith the n~~·er1ise1.~wm1, p~11101i°!1 or ~nlo of?'!): l,'lad~cl or p~s, ~r in ~nn~~ion w/th lh~ r~~pllhlkall~n or this report
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: LCS-R150094 Date Analyzed:
Test Code: 300.0-W
Chloride 5.23
Lab Sample ID: LCS-R150142 Date Analyzed:
Test Code: 300.0-W
Chloride 5.23
Lab Sample ID: LCS-R149934 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.03
Lab Sample ID: LCS-RI49935 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.08
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 l) 263-8686, Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Tanner Holliday
Dept: WC
QC Type: LCS
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/24/2021 1744h
mg/L E300.0 0.0198 0.100 5.000 0 105
03/25/2021 1646h
---
mg/L E300.0 0.0198 0.100 5.000 0 105
03/20/2021 1226h
mg/L E353.2 0.00541 0.0100 1.000 0 103
03/20/2021 1306h
----
mg/L E353.2 0.00541 0.0100 1.000 0 108
Limits
90 -110
90 -110
90 -110
--
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
---
Report Date: 3/31/2021 Page 56 of 65
analyses applicable to the CWA. SDWA, and RCRA Ill< pcrfam1cd ,n a~c to NELAC pn>tocols. Pertinent sampling information is located on the attached COC. Conr1ck ntial Business Information: This rcpon is pro,•1dcd f« ti"' C'<Clusi,-c 0$< ohbc add«:sstt Pm,1c,g,:.sofsubscqucni use oflt
ne of this company or any member of its S(aJT. or r"Jlfodudion of this R:p()<I in oOM<Ction with th,; odvertisemenL promotion or sale of any product or process. oc in connection with the re-publication of this n,pon for any po,posc othc:,-thon for me addrtss«: "111 be :;r:,ni«I Mly on~ This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: MB-R150094 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R150142 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R149934 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-Rl49935 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
03/24/2021 1716h
mg/L E300.0 0.0198 0.100 -03/25/2021 1618h
mg/L E300 0 0.0198 0.100
03/20/2021 1225h
mg/L E353.2 0.00541 0.0100
03/20/2021 1305h
mg/L E353.2 0.00541 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: 3/31/2021 Page 57 of 65
nnn.1)'$1'$ applicable 10 1heCWA. SOWA. and RCR.A arc p<rfom,cd in ncconlnncc 10 NELAC protocols. Pcnment sampling informatioo l$ locrued on lhc atmcl>cd COC. Confidential Susin= Jnfonnmwn: Thrs rcpon i:s po)\'id<d for thc c<dus,,•c use oftlr addrcsscc. Pm'11ese>of subsequ<m use oCtt
ne of thas cocnp:my c,r 3ny member or iis smlT. or repn:,dualoo of lhis report in connoc1Jon w,th lhc ad~c:n,sc,n,.,,,l pR)mO(ion or $Ille of m,y ..-,,duct or process. or in cc,n11<-.1ion wtth the re-publication of this n,pon for ""JI purpose Olh<r th.in for the addn:sstt wtll be l1"3"1od anly on contact. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: I st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103541-0IOAMS Date Analyzed:
Test Code: 300.0-W
Chloride 124
Lab Sample ID: 2103541-017AMS Date Analyzed:
Test Code: 300.0-W
Chloride 131
Lab Sample ID: 2103541-021AMS Date Analyzed:
Test Code: 300.0-W -
Chloride 145
Lab Sample ID: 2103706-00JAMS Date Analyzed:
Test Code: 300.0-W
Chloride 193
Lab Sample ID: 2103541-00SBMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite ( as N) 1.14
Lab Sample ID: 2103541-012BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.06
Lab Sample ID: 2103541-021BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 8.80
3440 South 700 West
Salt Lake City, UT 84 I I 9
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
Tanner Holliday
WC
MS
Spike Ref.
Units Method MDL Limit Amount %REC Limits
03/24/2021 2346h
mg/L E300.0 0.396 2.00 100.0 19.3 105 90 -110
03/25/2021 453h
mg/L E300.0 0.396 2.00 100.0 27.5 104 90 -110
03/25/2021 2220h
mg/L E300.0 0.396 2.00 100.0 41.8 103 90 -110
03/26/2021 203h
mg/L E300.0 0.396 2.00 100.0 92.6 100 90 -110
03/20/2021 1239h
---
mg/L E353.2 0.00541 0.0100 1.000 0.0638 108 90 -110
03/20/2021 1249h
mg/L E353.2 0.00541 0.0100 1.000 0.00543 106 90 -110
03/20/2021 1308h
mg/L E353 2 0.0270 0.0500 5.000 3.61 104 90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2021 Page 58 of65
nnalyses applicable to the CW I\, SOWA. and RCRA arc pcrfomicd in accordn11<c to NEL>.C pmtor:ols Pertinent sampling information is located on the attached COC. Confidential Business lnformntion, Th,s rcpon is provided for 1'11, c.,clusr.·c use of lhe 3ddr= Privilcg,e, of sui,,;,,q..,,.. us,,of 1t
ne of th.is company or "'1)' member of itS sl4ff, or reproduction of 1his rc,pon in co,u,ccuon "'th the advc:t11sen<-0L pron101fon or sale of ony product or p<or:css. or in conncctlOll wilh lhe rc-publit:31lon of this report for any purpose odlO" th.m for the addrc:ss« wm be gf3l1ICd only on conCICI. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103541-0IOAMSD Date Analyzed:
Test Code: 300.0-W
Chloride 123
Lab Sample ID: 2103541-017AMSD Date Analyzed:
Test Code: 300.0-W
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
03/25/2021 014h
---
mg.IL E300.0 0.396 2.00 100.0
03/25/2021 521 h
Tanner Holliday
WC
MSD
Spike Ref.
Amount %REC
-
19.3 104
Limits
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit
124 0.908 20
Qual
-------
Chloride 131 mg.IL E300.0 0.396 2.00 100.0 27.5 103 90 -110 131 0.406 20
Lab Sample ID: 2103541-021AMSD Date Analyzed: 03/25/2021 2248h
Test Code: 300.0-W ------------------------
Chloride 146 mg.IL E300,0 0.396 2.00 100.0 41.8 104 90 -110 145 0.333 20
Lab Sample ID: 2103706-00JAMSD Date Analyzed: 03/26/2021 326h
Test Code: 300.0-W ---------------
Chloride 191 mg.IL E300,0 0.396 2.00 100.0 92.6 98.6 90 -110 193 0.874 20
Lab Sample ID: 2103541-008BMSD Date Analyzed: 03/20/2021 1240h
Test Code: N02/N03-W-353.2 -------
Nitrate/Nitrite (as N) 1.15 mg.IL E353.2 0.00541 0.0100 1.000 0.0638 109 90 -110 1.14 1.05 10
Lab Sample ID: 2103541-012BMSD Date Analyzed: 03/20/2021 1250h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.06 mg.IL E353.2 0.00541 0.0100 1.000 0.00543 106 90 -110 1.06 0.188 10
Lab Sample ID: 2103541-02IBMSD Date Analyzed: 03/20/2021 131 Oh
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 8.09 mg/L E353,2 0.0270 0.0500 5.000 3.61 89.5 90 -110 8.8 8.48 10 §
§ -QC limits are set with an accuracy of two significant figures, therefore the recovery rounds to an acceptable value within the control limits.
Report Date: 3/31/2021 Page 59 of 65
analyses applicable 10 111<: CWA. SDW A, and RCRA are performed In ao,Ol'oonc• 10 NELAC prot0<0M P,:,uncnt smnplins infMn:lllOO is loc:llcd on lhc unad,cd ("OC. Coof,dc,,tial Busnicss lnfonna1ion· Th,s.n:pon is p<O\',ded for tlic cxclusiv~ use of the addn,sstt. Prh-il~-csof subsequcnz ,.,., of,t
ne of this company or ony member of its staff, or reproduction of Ibis report in connection wilh lhe advertisement, promotion or sale of any product or prnc=. or in connection wilh lhe re-publication of Ibis report for any pwpose other than for the addressee -.;n be gr.,nu,d only on contacL 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
_QC SUMMARY REPORt_
Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
Lab Set ID: 2103541 Dept: MSVOA
Project: 1st Quarter Chlorofonn 2021 QC Type: LCS ----
Reporting Amount Spiked Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Amount %REC Limits Amt %RPO Limit Qual
Lab Sample ID: LCS VOC-2 031921A Date Analyzed: 03/19/2021 701h
Test Code: 8260D-W-DENIOO -
Carbon tetrachloride 18.8 µg/L SW8260D 0.785 1.00 20.00 0 94.1 66 -143
Chloroform 18.2 µg/L SW82600 0.360 1.00 20.00 0 90.8 74 -120
Chloromethane 12.8 µg/L SW8260D 0.682 1.00 20.00 0 64.0 30 -149
Methylene chloride 19.4 µg/L SW82600 0.451 1.00 20.00 0 97.0 65 -154
Surr: l ,2-Dichloroethane-d4 47.3 µg/L SW82600 50.00 94.5 80 -136
Surr: 4-Bromofluorobenzene 46.4 µg/L SW8260D 50.00 92.7 85 -121
Surr: Dibromofluoromethane 47.8 µg/L SW8260D 50.00 95.7 78 -132
Surr: Toluene-d8 47.0 µg/L SW82600 50.00 93.9 81 -123
Lab Sample ID: LCS VOC-2 032221A Date Analyzed: 03/22/2021 641 h
Test Code: 8260D-W-DEN100 ----
Carbon tetrachloride 2 1.1 µg/L SW82600 0.785 1.00 20.00 0 105 66 -143
Chloroform 19.2 µg/L SW82600 0.360 I.OD 20.00 0 96.2 74 -120
Chloromethane 8.70 µg/L SW82600 0.682 1.00 20.00 0 43.5 30 -149
Methylene chloride 20.8 µg/L SW8260D 0.451 1.00 20.00 0 104 65 -154
Surr: 1,2-Dichloroethane-d4 48.8 µg/L SW82600 50.00 97.5 80 -136
Surr: 4-Bromofluorobenzene 47.1 µg/L SW82600 50.00 94.1 85 -121
Surr: Dibromofluoromethane 49.0 µg/L SW82600 50.00 97.9 78 -132
Surr: Toluene-d8 48.0 µg/L SW8260D 50.00 95.9 81 -123
Lab Sample ID: LCS VOC-2 032321A Date Analyzed: 03/23/2021 639h
Test Code: 8260D-W-DEN100
Carbon tetrachloride 19.4 µg/L SW82600 0.785 1.00 20.00 0 97.1 66 -143
Chloroform 17.8 µg/L SW8260D 0.360 1.00 20.00 0 89.0 74 -120
Chloromethane 14.0 µg/L SW8260D 0.682 1.00 20.00 0 70.0 30 -149
Methylene chloride 20.5 µg/L SW8260D 0.451 1.00 20.00 0 103 65 -154
Surr: I ,2-Dichloroethane-d4 47.5 µg/L SW82600 50.00 95.0 80 -136
Surr: 4-Bromofluorobenzene 45.9 µg/L SW82600 50.00 91.8 85 -121
Report Date: 3/31 /2021 Page 60 of 65
analyses applk :,blo 10 the CWA. SDWA, and RCRA 3tc pcrfonncd m accordanc~ to NELAC' pro4ocols. Pertinent sampling infom1ation is located on the attached COC. Confidential Business lnfomu~ion: This report is provided ror the exclusive use ortbc nddn,sstt Pri,,jjq,,csor subs<,q,JCfll U$C ofrt
ne of this comp,,ny or 3ny member of its staff. or rcpoduction or 1his report in a>nncction with lhc advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose Olher 1han for !he addtcsscc will be ~rd only on COlll3CI.. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chlorofonn 2021
Analyte Result
Lab Sample ID: LCS VOC-2 032321A Date Analyzed:
Test Code: 8260D-W-DEN100
Surr: Dibromofluoromethane 48.3
Surr: Toluene-d8 47.0
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
LCS
Spike Ref.
Amount %REC
03/23/2021 639h
µg/L SW8260D 50.00 96.7
µg/L SW8260D 50.00 94.I
Limits
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2021 Page 61 of 65
analyses applicable to the CW A, SOW A, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. Contidential Business Information: This report is provided for the exclusive use of the ad<nssee. Privtleges of subsequent use of 11-
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, oc in connection with the re-publication of this report for any purpose other than for the addressee will be granted only oo c:ootacL This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: ( 888) 263-8686, Fax: ( 80 I) 263-8687
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-2 031921A Date Analyzed: 03/19/2021 72th
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: MB VOC-2 032221A
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-2 032321A
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
< 1.00
< 1.00
< 1.00
< 1.00
48.1
47.4
47.4
47.4
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
48.2
46.9
48.4
48.0
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
48.2
47.5
µg/L SW8260D 0.785
µg/L SW8260D 0.360
µg/L SW8260D 0.682
µg/L SW8260D 0.451
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
03/22/2021 701h
µg/L SW8260D 0.785
µg/L SW8260D 0.360
µg/L SW8260D 0.682
µg/L SW8260D 0.451
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
03/23/2021 659h
µg/L SW8260D 0.785
µg/L SW8260D 0.360
µg/L SW8260D 0.682
µg/L SW8260D 0.451
µg/L SW8260D
µg/L SW8260D
1.00
1.00
1.00
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
96.3
94.7
94.9
94.8
96.4
93.8
96.7
95.9
96.3
95.0
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limit Amt %RPD Qual
Report Date: 3/31/2021 Page 62 of65
analyses applicable lo the CWA, SDWA, and RCRA are perfonned in accordance to NE LAC prolocols. Pertinent sampling infonnation is located on the anached COC. Confidential Business lnfonnation: This report is provided for the exclusive use of the addressee. Privileges of subsequent use of ti-
ne of this company or any membe< of its staff, or reproduction of this report in connection wilh the advertisement. promotion or sale of any product or process. or in connection with the re-publication of !his report for any J)UJJ>OSC other than for the addressee will be granted only on conlact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: I st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: MB VOC-2 032321A Date Analyzed:
Test Code: 8260D-W-DEN100
Surr: Dibromofluoromethane
Surr: Toluene-d8
48.5
46.2
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: Tanner Holliday
Dept: MS VOA
QC Type: MBLK
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/23/2021 659h
µg/L SW8260D 50.00 97.1
µg/L SW8260D 50.00 92.4
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Limits Amt %RPD Limit
---
78 -132
81 -123
Qual
Report Date: 3/31/2021 Page 63 of 65
analyses applic,ibJc lo th< CWA. SOWA. and RCRA are pcrf'om1od m ~cc;otdancc to NEL~C protocols. Pertinent sampling information is located on the attachod COC. Confidential Business Information: Tius report ls prcvidc,d for the excloswe use of the addressee. Privileges of subsequent use oflt
ne of this comp,ny 0< any member of its.Sia/I~ or reproduction of this r<pQlt In connection with the ad\•ertisement promotion or sale of any product or process. or in connection with the rc,-publication of this n,pon for m,y purpose other than fo,-the oddress«-will be granted only on contact This
American West
Al'IALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 841 I 9
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Tanner Holliday
Dept: MSVOA
QC Type: MS
Reporting Amount Spiked Spike Ref.
Method MDL Limit Amount %REC
Lab Sample ID: 2103541-014CMS Date Analyzed: 03/22/2021 937h
Test Code: 8260D-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 2103541-002CMS
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
22.6
20.4
21.5
21.7
48.0
46.8
48.8
47.2
Date Analyzed:
22.7
20.5
16.7
21.8
48.0
45.4
48.8
46.8
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
03/23/2021 749h
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
µg/L SW8260D
0.785 1.00 20.00 0 113
0.360 1.00 20.00 0 102
0.682 1.00 20.00 0 107
0.451 1.00 20.00 0 108
50.00 96.1
50.00 93.6
50.00 97.6
50.00 94.5
0.785 1.00 20.00 0 113
0.360 1.00 20.00 0 102
0.682 1.00 20.00 0 83.5
0.451 1.00 20.00 0 109
50.00 96.0
50.00 90.7
50.00 97.7
50.00 93.6
Limits
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/31/2021 Page 64 of 65
annlyscs apphc:,ble 10 the CW A, 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 f0< the exclusive use of the addressee. Priv,leges of <uhs<quent 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 pwpose othe,-than for the addressee will be i;r.,n1ed only on contact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103541
Project: 1st Quarter Chloroform 2021
Aoalyte Result
Lab Sample ID: 2l03541-0l4CMSD Date Analyzed:
Test Code: 8260D-W-DENI 00
Carbon tetrachloride 22.0
Chloroform 19.6
Chloromethane 17.2
Methylene chloride 20.8
Surr: I ,2-Dichloroethane-d4 48.1
Surr: 4-Bromofluorobenzene 46.3
Surr: Dibromofluoromethane 48.9
Surr: Toluene-d8 47.4
Lab Sample ID: 2l03541-002CMSD Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 26.4
Chloroform 23 .3
Chloromethane 14.9
Methylene chloride 24.6
Surr: l ,2-Dichloroethane-d4 47.8
Surr: 4-Bromofluorobenzene 46.4
Surr: Dibromofluoromethane 48.6
Surr: Toluene-d8 47.l
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
03/22/2021 956h
µg/1 SW82600 0.785 1.00 20.00
µg/1 SW8260D 0.360 1.00 20.00
µg/1 SW8260D 0.682 1.00 20.00
µg/1 SW82600 0.451 1.00 20.00
µg/1 SW8260D 50.00
µg/1 SW82600 50.00
µg/1 SW82600 50.00
µg/1 SW8260D 50.00
03/23/2021 808h
µg/L SW8260D 0.785 1.00 20.00
µg/1 SW8260D 0.360 1.00 20.00
µg/1 SW8260D 0.682 1.00 20.00
µg/1 SW82600 0.451 1.00 20.00
µg/1 SW82600 50.00
µg/1 SW8260D 50.00
µg/1 SW82600 50.00
µg/1 SW8260D 50.00
Tanner Holliday
MSVOA
MSD
Spike Ref.
Amount %REC
0 110
0 97.8
0 85.8
0 104
96.2
92.6
97.8
94.7
0 132
0 117
0 74.6
0 123
95.7
92.8
97.2
94.l
Limits
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
--
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
22.6 2.91 35
20.4 4.20 35
21.5 22.5 35
21.7 3.90 35
----·
22.7 14.9 35
20.5 13.l 35
16.7 11.3 35
21.8 12.0 35
Report Date: 3/31 /2021 Page 65 of 65
analyses applicable to the CW A, SOWA. und RCRA are performed i,, accord:!n<t-10 NB.AC f)C'Oloxols Pertinent sampling infonnation is located on the attached COC Confidential Business lnfonnation: This report is provided for the exclusive use of lhe addressee. PriVIleges of subseqUOJ:11 use of 11-
ne of this compan)' or any member of its Staff. or reprodi,ctton of this n:pon in c:onncctlon with the odvertisement. promotion or sale of any product or process. oc in connection with lhe re-publication of !his report for any pU1J>OSC other than for the admessee will be £fllllled only on contact. This
American West Analytical Laboratories Rpt Emailed: UL
Denison
WORK ORDER Summary Work Order: 2103541 Pagel ofS
Client:
Client ID:
Project:
Comments:
Sample ID
2103541-00lA
2103541-0018
2103541-00IC
2103541-002A
2103541-002B
2103541-002C
2103541-003A
2103541-003B
210354 l-003C
2103541-004A
2103541-004B
210354!-004C
2103541-00SA
2103541-00SB
2103541-00SC
Printed: 03/19/21 09:59
Energy Fuels Resources, Inc. Due Date: 4/2/2021
ENE300 Contact: Tanner Holliday
1st Quarter Chloroform 2021 QC Level: III WO Type: Project
QC 3 (no chromatograms). EDD-Denison. CC [e-mail]. Do not use "*R_" samples as MS/MSD.; ne,
Client Sample ID
1W.µ)3R_03162021
1W4-03_03172021
1W4-42_03172021
1W4-28_03172021
----
TW4-32_03172021
Collected Date Received Date Test Code Matrix Sel Storage
3/16/2021 0815h 3/19/2021 0805h 300.0-W Aqueous
I SEL Anai}'_tes: CL
N02/N03-W-353.2
1 SEL Analytes: N03N02N
8260D-W-DEN100
Test Graue_: 8260D-W-DENIOO; # of Analytes: 41 # of Surr: 4
3/l 7 /2021 0732h 3/19/2021 0805h 300.0-W Aqueous
1 SEL Analytes: CL
N02/N03-W-353.2
I SEL Analytes: N03N02N
8260D-W-DEN100
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 1 # of Surr: 4
3/17/2021 0747h 3/19/2021 0805h 300.0-W Aqueous
I SEL Analytes: CL
N02/N03-W-353.2
I SEL Anaf)l_les: N03N02N
8260D-W-DEN100
Test Group: 8260D-W-DEN]2_0; # of Analytes: 41 # of Surr: 4
3/17/2021 0757h 3/19/2021 0805h 300.0-W
I SEL Analytes: CL
N02/N03-W-353.2
---------------------·_] SELAnalytes: N03N02N
8260D-W-DEN100
Aqueous
Test Group: 8260D-W-DENJOO; # o[Analytes: 41# ofSurr: 4
3/l 7 /2021 0804h 3/19/2021 0805h 300.0-W Aqueous
df-wc
df-no2/no3
VOCFridge
df-wc
df-no2/no3
VOCFridge
df-wc
df-no2/no3
VOCFridgc
df-wc
df-no2/no3
VOCFridge
df-wc
3
3
3
3
I SEL Analytes: ~L------------------------
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge 3
Test Group: 8260D~W-DENI 00; # of Analytes: 41__/1 of Surr: 4
LABORATORY CHECK: %M [_} RT [J CN C TAT O QC O LUO 0 HOK ___ HOK __ _ HOK coc Emailed _ 1--, , ---.
WORK ORDER Summary WorkOrder: 2103541 Page 2 ofS
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2103541-006A TW4-12_03172021 3/l 7 /2021 081 lh 3/19/2021 0805h 300.0-W Aqueous elf-we
I SEL Analytes: CL
2103541-006B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2103541-006C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Su": 4
2103541-007A TW4-13_03172021 3/17/2021 0819h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103541-007B N02/N03-W-353.2 elf-no2/no3
I SEL Analytes: N03N02N
2103541-007C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 41 # ofSurr: 4
2103541-00SA TW4-36_03172021 3/17/2021 0826h 3/19/2021 0805h 300.0-W Aqueous elf-we
1 SELAnalytes: CL ------2103541-00SB N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N ------
210354I-008C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENIOO; # of Analytes: 41 # of Surr: 4
2103541-009A TW4-31_03172021 3/17/2021 0834h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
210354I-009B N02/N03-W-353.2 elf-no2/no3
I SEL Analytes: N03N02N
2I0354l-009C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI 00; # of Analytes: 41 # of Surr: 4
2103541-0IOA TW4-34_03172021 3/17/2021 0842h 3/19/2021 0805h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2103541-0IOB N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N -----
2103541-0lOC 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENI 00; # of Analytes: 4 1 # of Surr: 4
2103541-01 lA TW4-35_03172021 3/17/2021 0850h 3/19/2021 0805h 300.0-W Aqueous elf-we
I SEL Analytes: CL
2103541-0IJB N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N ·---·-
2103541-0I IC 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENIOO; # of. Analy_tes: 41 # of Surr: 4
Printed: 03/19/21 09:59 LABORATORY CHECK: %M [J RT::::-~ CN 1-=:1 TAT C ace LUO C! HOK ___ HOK ___ HO~--COG Emailed
WORK ORDER Summary WorkOrder: 2103541 Page 3 of 5
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2103541-012A T\'14-23_03172021 3/17/2021 0900h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2l03541-012B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2103541-012C 8260D-W-DENIOO VOCFridgc 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
2I03541-0l3A TW4-65_03172021 3/17/2021 0732h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103541-0l3B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2103541-0l3C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# ofSurr: 4
2103541-014A T\'14-38_03182021 3/18/2021 0812h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2I0354l-Ol4B N02/N03-W-3S3.2 df-no2/no3
1 SEL Analytes: N03N02N
2103541-014C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-Dl}_l!__l 00; # of Analytes: 4 I# of Surr: 4
2103541-0lSA TW4-14_03182021 3/18/2021 0823h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103541-0lSB N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
2103541-0lSC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 /# ofSurr: 4
2103541-016A TW4-06_03182021 3/18/2021 0834h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2I03541-0l6B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2103541-016C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENI 00; # of Analytes: 4 I# of Surr: 4
2103541-017A T\'14-27_03182021 3/18/2021 0844h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL -· 2103541-0l?B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
Printed: 03/J9/21 09:59 LABORATORY CHECK: %M ;::J RT C CN O TAT CJ ace LUO [J HO~--HOK __ HOK ___ COCEmailed
WORK ORDER Summary WorkOrder: 2103541 Page 4 of5
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2103541-0l?C TW4-27_03182021 3/18/2021 0844h 3/19/2021 0805h 8260D-W-DEN100 Aqueous VOCFridgc 3
Test Group: 8260D-W-DENJ 00; # of Analytes: 4 I# of Surr: 4
2103541-0l&A T\\'4-05_03182021 3/18/2021 0853h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103541-0l&B N02/NOJ-W-J53.2 df-no2/no3
I SEL Analytes: N03N02N
2103541-0l8C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Surr: 4
2I0354l-Ol9A T\\'4-09_03182021 3/18/2021 0858h 3/19/2021 0805h 300.0-W Aqueous df-wc
I SELAnalytes: CL
2103541-019B N02/NOJ-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2103541-019C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 /# ofSurr: 4
2103541-020A T\\'4-08_03182021 3/18/2021 0912h 3/19/2021 0805h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2103541-020B N02/NOJ-W-353.2 df-no2/oo3
I SEL Analytes: N03N02N
2103541-020C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 4 I# of Surr: 4
2I03541-021A T\\'4-18_03182021 3/18/2021 0923h 3/19/2021 0805h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2103541-021B N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
2103541-021C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # oj'Analytes: 4/# ofSurr: 4
2103541-022A T\\'4-33_03182021 3/18/2021 0935h 3/19/2021 0805h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
2103541-022B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
210354 l-022C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
2103541-023A TW4-30_03182021 3/18/2021 0944h 3/19/2021 0805h 300.0-W Aqueous df-wc
I SEL Analytes: CL
Printed: 03/19/21 09:59 LABORATORY CHECK: %M C RT CJ CN [J TAT 0 QCO LUOO HOK ___ HOK ___ HOK ___ COCEmailed
WORK ORDER Summary WorkOrder: 2103541 Page 5 of5
Client: Energy Fuels Resources, Inc. Due Date: 4/2/2021
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
210354l-023B 1W4-30_03182021 3/18/2021 0944h 3/19/2021 0805h N02/N03-W-353.2 Aqueous df-no2/no3
1 SEL Analytes: N03N02N
2l0354I-023C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DEN 100; # of Analytes: 4 I# of Surr: 4
210354I-024A TW4-70_03182021 3/18/2021 0858h 3/19/2021 0805h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103541-024B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
2103541-024C 8260D-W-DENIOO VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
2103541-025A TRIP BLANK 3/16/2021 0815h 3/19/2021 0805h 8260D-W-DENIOO Aqueous VOCFridge 3
Test Group_: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
Printed: 03/J 9/2 J 09:59 LABORATORY CHECK: %M C] RT [J CN O TAT O QC [J LUO 0 HOK~~-HOK~--HOK___ Coe Emailed ____ _
American West
Analytical Laboratories
4e3 W. 360G s. Soll la~• Cily, UT e,1115
Phone # (001) 263~666 roffree # (~.i :16::.-8666
L~~ Fa, I' (801) 263-e687 Email av,,"[e-mail]
wvm.awal-lebs.com
Cliert. Eueqy Fuels Reaoarees, Inc.
Address: 6425 8. Hwy. 191
Blaadmg, UT 84511
Contact Tanaer Bolllday
Phone#: [phone] CeR#:
Email: tJsollld~ela-cam; KWemel@eDa&::Vfi,ela.com
1st Quarter ChlMof'orm 2021 Project Naroo, -
Project#:
PO#:
Sampler~: Tanner Holliday
Date
Saml)lelD:-Sampled
TW4-03R_03162021 3/16/2021 --. . -2 t TW<H>3_03172021 3/17/~02~
3 I TW<l-4~_0317202~ 3/17/2021
1 TW4-28_03172021 3/17/2021
-
1 TW4-3a._03172021 3/17/2021
a I TW4-12_03172021 3/17/2021
' TW4-13_03172021 3/17/2021
I TW4-36_03172021 3/17/2021
1 TW4-31_03172021 3/17/2021
a TW4-34_03172021 3/17/2021
I TW4-3S_03172021 3/17/2021
I TW4-23_03172021 3/17/2021
I TW4-66_03172021 d 3/17/2021
~by: _ --\,., AU/1,,. }:Jh_/~pry/ OCID: -311in021 -~ ' -,
nmr. l'l. K D -i;. Prrnttl-'ITT!r. TanncMtt:::irda,
-~l,y. Ow: -,.,,._
'"""' PrlnlNwn.O'!
Rcd~t,y: °"'"' , __
nmo:
Prlnt-
""lncjwl,N oy. OG isa,,_
Timt:
PIWN-.
Time
Sampled
816
732
747
757
804
811
819
826
834
842
860
900
732
-~y:
"'"""""°
Prl~NA'M~
-.. 1:y: ,...,...,_
Prin:INam-.:
RooelvOdby:
Sionaturo
PrirtNamo; ReoeiYed by:
Si1nalu1W
PrlO:Nomr.
I
,
CHAIN OF CUSTODY
All •nalyois Will be oonductod uelng NEI.AP BCCfeortod methods ono all dot,, win bo r-rt<od """9 AWIU. '° al .... nl OCSJ!• nots am 1eportlng
llmlls(POI..) unr .... pec1r.,.11y ""!ueslod-onu,;,, Chain cfeu.lody--.od <11><....-n.
QC Level:
II
Tum Around Time: I Unr ... other amu,~ nave boeo made,
3 Standard
signed repollo ,.,,, bo .,...led by S:00 prn. on
the dBy tltey an, duo.
X Include EDD:
LOCUS UPLOAD
EXCEL
Aekl rnerad For.
For Compliance With:
D NELAP
D RCRA
D CWA
D SDWA
0 ElAPIA2lA
c' D NUAP ~ cl [) Non-Compliance ~ 0 ll D Other:
~ "> ~ ·l! .. 0
~ t'l 0 IO 1ii ~ 0 ~
:! 0 ~ Known Hazards C: II) 0 " .... ::t. II 0 a. C, u & 'I; E i a g .. Sample Comments .. "'
5 w X X ~
s w X X X
5 w X X X
5 w X X X
·x x .. 5 w 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 ~
, 0 AA ·, .A O:\J'-1> 1 1 J ~e; ·3 LC, I -Z....) Spt!Cial Instructions:
·~ ..1,"\{~ ~_.Al.,Ll/\ r.mo: '><.OS
2it):?v54: I
AWAL Lab Sample Set#
Page 1 of 2
Due Date: 2-\ 2-} 4
Laborato!y Use Only
~IOIWore:
1~
2 ·otcti!od
a Temperetura 2 ,.3, •c
4 Ro<&ivod 8"'"""'1.eakfng
y .' N (lmpn,pertySoal~
tn:-ed y N
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y N a -· Times y N
:
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11!J'OftoutarP~ ,y N NII
~nono.(•P-• N NA
~-~ V H NA.
4 -.., on Semple~ Y N 1111
Discn,ponc:les Belween samplo
V N
l.abels and COC ROOOfO~
°""" Sec the Analytical Scope of Work for Reporting Limits end VOC
r.,.: analytc list.
O.lo:
rune:
Data:
iune.:
American West
Analytical Laboratories CHAIN OF CUSTODY
46'.i W. ;!.;06 s. Salt Lake C~y. UT 84115
?bone# (801l 26H686 Toi! Free I! (888) 263-8SB6
All anelysis 'WIii be c:ondlld:ad u.i.lng NELAP accr&dlted .mel:hoda C1d all dale wiU b& reported uglng AWA L's 81:arx:laJd onelyle lists and reportin;
lmi!s (PQ4 ur1 ... spadf,cal!y roque,tod olherwls&on thi&Chaln of c..toclyond/or r.tadlodcloaJ!nO<Ullon ,,._., F;;;c # (801} ~>ll6S7 Email awai@awa\-4abs.com
w.w1.awal--labs.com
cnent: Energy Fllels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact TaDDer HoWday
Phone#: [phone] Cell#:
Emal: tholllda~ei..c-; [e-mail],n
Project Name: 1st Quarter Chloroform 2021
QC Level:
3
~~#: ~
ro#: ~
c' ci
U' e ~
Sampler Name: Tanner Holliday j j 3
"' ::. II!;
~ a
0 ~ :t.
0 IO ('q l!!.
Date
Samole ID: Sampled
1' TW4-38_03182021 3/18/2021
15 TW4-l4_03182021 3/18/2021
1e TW4-06_031a20:u 3/18/2021
nme
Sampled
812
823
834
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. ,tgnad ,.ports wlll be emailed try s:oo pm on
the day they .... duo.
X Include EDD:
LOCO& UPLOAD
EXCEL
Field Fillen>d For.
For Compllance With:
D NELAP
:J RCRA
0 CWA
D SOWA
D ELAP/A2lA
D NUAP
D Non-Compliance
D Other:
Known Hazards
&
Sample Comments
210~~
AWAL lab Sample Set#
Page 2 of 2
Due Date: 41 ~I~\
Laboratory U.se Only
2
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11 TW4-27_03182021 3/18/2021 844
1alTW4-0S_03182021 3/18/2021 853 ~
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1g TW-4-09_03182021 3/18/2021 858
20 TW4-08_03182021 3{18/2021 912
21 TW4-18_031S2021 3/18/2021 923
s IW I XI XI X
SIWIXIXIX
5 IW I XI XIX
3 Pn>antonSemple ffi V N NA
4 Url>ll>krmonSamplo
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~ TW4-33_03182021 3/18/2021 935
23 TW4--30_0318::w21 3/18/2021 944
2ol TW,.:_70_03182021 3/lB/2021 858 I I r.EEl:1:1111111111 IF;.~
211 TRIP BLAIIK 3/16/2021 815 3 IW X
28 J
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:.01µ0: -1:::l>jlc
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Aint:Name:
R"°"r,edt,y: Date: s--
' Time:
Print Name:
Reoelved by.-pate:
""'"'""" T1mo: --...
Preservation Check Sheet
s amp le Set E dpH
Analysis Preservative rCQ r&Y -~ ~f~ '""ct.b ~ea:, -001 -E)Ojf --Od\ -OtO L-OJl
Ammonia pH<2H2S04
COD 0H<2H2S04
Cvanide pH>12NaOH
Metals pH<2HN03
N02/N03 oH<2H2S04 I\IP.b l'\lPS l~iPh ·'1t'h 1\VS \Jl<;i '\lf'S N&, "\.]{"'~ r..J..~ A \J?TJ
O&G oH<2HCL I I ' I I I I ' I I I
Phenols oB<2H2S04
Sulfide pH>9NaOH,
Zn Acetate
TKN oH<2 H2S04
TP04 pH<2H2S04
CrVI+ pH>9
(NH4)2S04
.;·olC\ ,OU) -f-17.J ~f)?_2__ -02.~ f'Dll --02!:J
tJO .... /J.."1 ~ n" LJ_ LI so.1 ,f~~S \l ()~ \(Pc_ 1,, p .(..._ l\f e'_c., \IP<.. ,PS
7 ..., I /, I I I • r I , 1 I
Procedure:
Frequency:
1)
2)
3)
4)
5)
6)
7)
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 Hd
If sample is not preserved, properly list its extcnsjon and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
A
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference .
-0\2..
l'\.VJt;
I
Lab Set ID:
pH Lot#:
f-el3 -014
l'\JLA 1\/P~
I I
-ou;
l"\{f' &
I
2\\J3S4\
~'"2-
l-tOI~ -n11 OtB
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I I I
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 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2021
Dear Tanner Holliday: Lab Set ID: 2103706
American West Analytical Laboratories received sample(s) on 3/25/2021 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 QS9 . by Jose G.
Rocha Rocha Date: 2021.03.31
16:29:26 -06'00'
Laboratory Director or designee
Report Date: 3/31/2021 Page I of 29
All annlyses applicoblC! 10 tho CWA, SOWA, Md ltCRA nre perfom1ed in accordance to NELAC prolocols. Penlniimt samptin; informntion is located on the attached COC. (:onfidentinl Business rnromwtlon: This report is provided ror lhe-exclusire use of the
~ddressee. Pririle~es o:su~cq~enl ~~eof1ht ?,~.ne or1his.co~pany or M)' 1~mber olils stoff, or reproducliO!? ~~this repo'! in ~oni1eclion .. "ilh the o~~·ertise~ent, P~?moti~•, s:ilt of ~!Y .. rrod~ct or p1~e~s, ~r in :onn~c~ion w!th 1h~ r~-publicalion of 1his report
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Tanner Holliday
ANALYTICAL LABORATORIES Project: 1st Quarter Chloroform 2021
Lab Set ID: 2103706
Date Received: 3/25/2021 1015h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West 2103706-00lA MW-32_03222021 3/22/2021 1230h Aqueous Anions, E300.0
;alt Lake City, UT 84119 2103706-00JB MW-32 03222021 3/22/2021 1230h Aqueous Nitrite/Nitrate (as N), E353.2
2103706-00lC MW-32 03222021 3/22/2021 1230h Aqueous VOA by GC/MS Method
8260D/5030C
Phone: [phone] 706-002A TW4-75 03222021 3/22/2021 1230h Aqueous Anions, E300.0
2103 706-002B TW4-75 03222021 3/22/2021 1230h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 2103 706-002C TW4-75 03222021 3/22/2021 1230h Aqueous VOA by GC/MS Method
Fax: [phone]D/5030C
!-mail: [e-mail] 2103706-003A TW4-16 03242021 3/24/2021 815h Aqueous Anions, E300.0
2103706-003B TW4-16 03242021 3/24/2021 815h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 2103706-003C TW4-16 03242021 3/24/2021 815h Aqueous VOA by GC/MS Method
8260D/5030C
2103706-004A TW4-29 03242021 3/24/2021 825h Aqueous Anions, E300.0
Kyle F. Gross 2 l03706-004B TW4-29 03242021 3/24/2021 825h Aqueous Nitrite/Nitrate (as N), E353.2
2103 706-004C TW4-29 03242021 3/24/2021 825h Aqueous VOA by GC/MS Method
Laboratory Director 8260D/5030C
2103 706-00SA TW4-10 03242021 3/24/2021 840h Aqueous Anions, E300.0
Jose Rocha 2103706-00SB TW4-10 03242021 3/24/2021 840h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 2103706-00SC TW4-10 03242021 3/24/2021 840h Aqueous VOA by GC/MS Method
8260D/5030C
2103706-006A TW4-07 03242021 3/24/2021 848h Aqueous Anions, E300.0
2103 706-006B TW4-07 03242021 3/24/2021 848h Aqueous Nitrite/Nitrate (as N), E353.2
2103706-006C TW4-07 03242021 3/24/2021 848h Aqueous VOA by GC/MS Method
8260D/5030C
2103706-007A TW4-26 03242021 3/24/2021 857h Aqueous Anions, E300.0
2103 706-007B TW4-26_03242021 3/24/2021 857h Aqueous Nitrite/Nitrate (as N), E353.2
2103 706-007C TW4-26 03242021 3/24/2021 857h Aqueous VOA by GC/MS Method
8260D/5030C
2103 706-008A TW4-16R 03232021 3/23/2021 800h Aqueous Anions, E300.0
2103706-008B TW4-16R 03232021 3/23/2021 800h Aqueous Nitrite/Nitrate (as N), E353.2
2103 706-008C TW4-16R 03232021 3/23/2021 800h Aqueous VOA by GC/MS Method
8260D/5030C
2103706-009A Trip Blank 3/22/2021 1230h Aqueous VOA by GC/MS Method
8260D/5030C
Report Date: 3/31/2021 Page 2 of29
All onnlyses applicnble to lhe CWA. SOWA. and RCRA are µerfom1ed in a1:cordance 10 NELAC protocols Pertinent sompliny infornmtion is located on 1he nltnched COC. Conlidentiol Business lnfonnalion: This repon is pro,•ided for the exch.JSi,·e use of the
~ddressee PriYile~es o,rsub .. seq~1enl ~1~e of the ~~1e of lhis .con;,pnny or nny 1~mber of its stnIT, or reproduclio~ ~f this repo~ in fOn~1ec1ion .. ,\-ilh lhe a~vertise~enl, p~~moii~ ~r ~ale of ~!Y. ~rod~t or p~~s. ~r in ~nn~c!ion w(lh 1h~ r~-publication of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
foll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awaf-Jabs.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 of Collection:
Sample Condition:
C-0-C Discrepancies:
1st Quarter Chloroform 2021
2103706
3/25/2021
3/22-3/24/2021
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.
Duplicate (DUP): The parameters that required a duplicate analysis had RPDs
within the control limits.
Corrective Action: None required.
Report Date: 3/31/2021 Page 3 of29
All nnolysos applicable lo the CWA, SOWA. Md RCRA 01e performed in accordance to NELAC protocols Per1inenl sampling information is located on the allachect COC Confidential Business Jnformntion: This report is prm•ided for1hc exclusi\·e use of1he
~ddressee. PriYile~es o,rsub .. se~~ienl ~1;e of the ~!":'1e of this .co1~pm1~· or MY ~'!lber of its s1nIT, or repri;,ducli~ ~f !his repo~ in fOO~eclion .. '"ilh the ~"ertise~ent, P~?moti~n ~r sale or?'!>: -~rod~cl or P~?Cess, ~r in ~nn~c~ion w!lh lh~ ~-p~blic111io1) of lhis report
Volatile Case Narrative
American West Client: ANALYTICAL LABORATORIES Energy Fuels Resources, Inc.
Tanner Holliday
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
Contact:
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
I st Quarter Chloroform 2021
2103706
3/25/2021
3/22-3/24/202 l
Intact
None
SW-846 8260D/5030C
Volatile Organic Compounds
General Set Comments: One or more 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: 3/31/2021 Page 4 of 29
All analyses applicnbli:! 10 lhc C'WA, SOW A. and RCRA are performed in accordance to NE LAC pra1oools. Pertinent swnpHng inforn~uon is locnled on lhe altacbcd CO . ConOdet1tlol Business lnromiallon: This repon is provided for tho c.(CIU$h't..• use of the
~ddressee. Pii\'ile~es er ~U':Soq~enl ~~e of lhe ~~le of lhis .co1~pany or nny l~mber or its staff, or rcµroducll~ ~rd1is ~K)'! in ~on~1cction ... with 1he n~~·ertise~enl, P!~ntOli~ ~r s:ila of !1'!-' rod~ct Of p1:~ess, ~r in 7°TITI~~ion w!lh th~ n;-publiaulon or this report
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103 706
Project: 1st Quarter Chlorofonn 2021
Analyte Result
Lab Sample ID: LCS-RI50142 Date Analyzed:
Test Code: 300.0-W
Chloride 5.23
Lab Sample ID: LCS-RI50258 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.07
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone]. Toll Free: [phone], Fax: [phone]
e-mail: awal@),awal-labs.com, web: www.awal-labs.com
C SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount Spiked
Units Method MDL Limit
03/25/2021 1646h
mg/L E300.0 0.0198 0.100 5.000 -03/30/2021 941h
mg/L E353.2 0.00541 0.0100 1.000
Tanner Holliday
WC
LCS
Spike Ref.
Amount %REC
0 105
0 107
Limits
90 -110
90 -110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPO Ref. RPO
Amt %RPO Limit Qual
Report Date: 3/31/2021 Page 22 of 29
Qn:,Jysc,s applicable 10 the CWA. SOWA, and RCRA arc pcr(omicd in """°tdancc 10 NELAC prc)!OCOls Pcruncnt samplini: 1nform:,11on is locau:d oo the ou<>dicd COC. Confodcntllll 8 ~ lnformmioo: Tins Rport is p<o~idcd Tnr ti.. ca:lusn·c = oflhc :ddrcssct-. Pri•,il,:,gcs of subs,c,quc,ra""" of it
neof 1hi• comp;uty or any member of ilS S1l11T. or rcproduct100 of1hi• n-pcxt ln conncaic,n with 1hc oo,·<rtiscntmt. prnmo<ion or we of any p<oduct or proc:css. or in CX>flDl:<:tion wi1h the ,....publ,c:mon of this n:p<1<1 for any purpose Olhcril1:1n for tb::add:esscc .. ;n b<,grantcd only oo c-Thi<
American West ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: MB-Rl50142 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-Rl50258 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
_QC SUMMARY REPORT
Contact: Tanner Holliday
Dept: WC
QC Type: MBLK
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/25/202 l 1618h
mg/L E300.0 0.0198 0.100
03/30/2021 940h
mg/L E353.2 0.00541 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2021 Page 23 of29
nn31yscs :,pplic:ibf e 10 the CW A. SOW A. Md RCRA nn, pafooncd in aa:O<dance 10 NELAC pro1oc:ols. Pertinent sampling information is located on the attached COC. Confidential Business lnfonnlllion This rqx,rt is Jl"O';dcd for the c:xclusi,c use or lhe 3ddrc:sscc. Pnvilcges or suhscqucnt use of 1~
nc or this ccmpony or any member or il5 stofT. or rcprodut1iun of this rq,on in COMCdion wlth me :ich·cnlsemcnt. pn,mooon or sale of"">" pcodud « pcoccss. or in conn«:UOn wilJ, lhe 11:epublicatlon of1his n,pc,rt for z y purpose od,...1han f« 1hc addrc:s,cc wall be sr.,mcd only on ron1aet. Tlus
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103541-021AMS Date Analyzed:
Test Code: 300.0-W
Chloride 145
Lab Sample ID: 2103706-00JAMS Date Analyzed:
Test Code: 300.0-W
Chloride 193
Lab Sample ID: 2103706-00IBMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.01
3440 South 700 West
Salt Lake City, UT 84 I J 9
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact:
Dept:
Tanner Holliday
WC
QC Type: MS
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/25/2021 2220h
mg/L E300.0 0.396 2.00 100.0 41.8 103
03/26/2021 203h
---
mg/L E300.0 0.396 2.00 100.0 92.6 100
03/30/2021 959h
mg/L E353.2 0.00541 0.0100 1.000 0 IOI
Limits
90 -110
90 -110
90 -110
Kyle F. Gross
Laboratory D irector
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPO Limit Qual
Report Date: 3/31/2021 Page 24 of 29
analyses :,pplicnblt lo 1he CWA. SOWA. ond RCRA ore pcrfomtcd in =ordantt io NELAC pro1ocols Pertmcnl wnpli"!I mform:IIJOO is locn1cd on lhc 111iachcd COC. u,n11d,:nual Business lnfonn:1.1ion: Th1s rcpon is pn,,1dtd fonhc o:clusive use of the~ Pm-ilcgesot's11bsequml use of li-
ne of 1his company or :my mcmbc,-of its smlT, or rqroductioa of this rcp,,n in C>Onn<edion wilh the :,ch-cntS<mmt. pron,01100 or sale of any product « p.-octSS. or in c.onn«:rion with 1he ro--public:11:ion <>f 1his repon for 311)' purpose other thtln fa< the addressee \\111 be granted only on coomct. Th,s
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103541-02IAMSD Date Analyzed:
Test Code: 300.0-W
Chloride 146
Lab Sample ID: 2103706-00JAMSD Date Analyzed:
Test Code: 300.0-W
Chloride 191
Lab Sample ID: 2103706-00IBMSD Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.988
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
CK_SUMMARY REPORT
Contact:
Dept:
Tanner Holliday
WC
QC Type: MSD
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/25/2021 2248h
-
mg/L E300.0 0.396 2.00 100.0 41.8 104 -03/26/2021 326h
---
mg/L E300.0 0.396 2.00 100.0 92.6 98.6
03/30/2021 1000h
mg/L E353,2 0.00541 0.0100 1.000 0 98.8
Limits
---
90 -1 JO
-
90 -110
90 -I JO
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPO Limit Qual
-----
145 0.333 20
193 0.874 20
1.01 2.03 10
Report Date: 3/31/2021 Page 25 of29
amlyscs applicable lo d>c CWA. SOWA. and. RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business lnforma11on Thi$ n:pon i$ prO\~<lcd for 1bc C'<cl,...;,.., use ofll>e nddrcs.<tt. PmilC£",< of subsoqUOJII use, o( 1~
nc ofU,i!. comp:,ny or any member of nssmlT, or rq,roduct,on of1his n,pan m =ion wi~1 1hc :id,-ertisem<nt. ,.-omooion or sale ofnny produa or prnc<:S$. or m <onn«tkm wilh the rc,.public:ition of this rq,or, for nny purpo<c odlcr lhrut for the :iddrcss<,<, will be granted only on contOCL llus
American West ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 202 I
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: awal(@..awal-labs.com, 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 032521A DateAnalyzed: 03/25/2021 716h
Test Code: 8260D-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-2 0326218
Test Code: 8260D-W-DENIOO
Chloroform
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.0 µg/L SW8260D
19.3 µg/L SW8260D
15.9 µg/L SW8260D
19.2 µg/L SW8260D
54.0 µg/L SW8260D
43.8 µg/L SW8260D
51.6 µg/L SW8260D
48.7 µg/L SW8260D
Date Analyzed: 03/26/2021 1639h
19.0 µg/L SW8260D
48.1 µg/L SW8260D
46.6 µg/L SW8260D
49.0 µg/L SW8260D
47.7 µg/L SW8260D
0.785 1.00 20.00 0 95.2
0.360 1.00 20.00 0 96.5
0.682 1.00 20.00 0 79.7
0.451 1.00 20.00 0 96.0
50.00 108
50.00 87.7
50.00 103
50.00 97.4
0.360 1.00 20.00 0 95.2
50.00 96.2
50.00 93.3
50.00 97.9
50.00 95 .3
Limits
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
74 -120
80 -136
85 -121
78 -132
81 • 123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Limit Amt %RPO Qual
Report Date: 3/31/2021 Page 26 of 29
analyses applicable 10 !he CW A, SOW A, and RCRA arc performed in accordance, 10 NELAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business lnfonnation: This repon is provided for the e.~clusive use of the addressee. Pri,·ileges of ~uent use of tt
ne of this comp.my or any member of its staff, or reprodi1<1ion of this report in connection with the :,dvenisement promotion or sale of any product or process. or in conne<1ion with the re-pub I ication of this report for any purpose olher than for the addressee will be granted only on contact_ This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: I st Quarter Chloroform 202 l
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Method MDL
Contact:
Dept:
QC Type:
Tanner Holliday
MSVOA
MBLK
Reporting Amount Spiked Spike Ref.
Limit Amount %REC
Lab Sample ID: MB VOC-1 032521A Date Analyzed: 03/25/2021 736h
Test Code: 82600-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-2 032621B
Test Code: 8260D-W-DEN100
Chloroform
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
54.8
47.1
51.3
47.9
Date Analyzed:
< 1.00
47.0
46.8
47.3
46.4
µg/L SW8260D 0.785 1.00
µg/L SW8260D 0.360 1.00
µg/L SW8260D 0.682 1.00
µg/L SW8260D 0.451 1.00
µg/L SW8260D 50.00 110
µg/L SW8260D 50.00 94.2
µg/L SW8260D 50.00 103
µg/L SW8260D 50.00 95.8
03/26/2021 1659h
µg/L SW8260D 0.360 1.00
µg/L SW8260D 50.00 94.1
µg/L SW8260D 50.00 93.5
µg/L SW8260D 50.00 94.5
µg/L SW8260D 50.00 92.8
Limits
80 -136
85 -121
78 -132
81 -123
80 -136
85 -121
78 -132
81 • 123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/31/2021 Page 2 7 of 29
analyses applicable to lhe CWA, SOWA, and RCRA are pc,fonned in ru:cordance to NELAC protocols Pertinent sampling information is located on the altached COC. Confidential Business lnformarion: This ,eport is pro,;ded foc the e.,clusive use of the addressee_ Privileges of.5Ubsa<quent use oftt
ne of lhis company O< any member of its staff. oc reproduction of this repoct in connection with the advertisement. prom orion or sale of any product or process. oc in connection with the re-publication of this report for any pulJ)OSe other than fo, the addressee will be gr:mu:d only on COOl8CI. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103706-00ICMS Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 24.0
Chloroform 22.4
Chloromethane 20.4
Methylene chloride 22.0
Surr: I ,2-Dichloroethane-d4 55.1
Surr: 4-Bromofluorobenzene 43.2
Surr: Dibromofluoromethane 52.3
Surr: Toluene-d8 47.2
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
03/25/2021 1440h
µg/L SW8260D 0.785 1.00 20.00 0 120
µg/L SW8260D 0.360 1.00 20.00 0 112
µg/L SW8260D 0.682 1.00 20.00 0 102
µg/L SW8260D 0.451 1.00 20.00 0 110
µg/L SW8260D 50.00 110
µg/L SW8260D 50.00 86.4
µg/L SW8260D 50.00 105
µg/L SW8260D 50.00 94.3
Limits
66 -143
74 -120
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 Qual
Report Date: 3/31/2021 Page 28 of 29
aJUlyscs applicable to the CWA. SOW A, and RCRA are p,:tformed in ~=tdon<c to NELAC protoools. Pertinent sampling infonnation is located on the attached COC. Confidential Business lnfonn:ition: This ,epon is pro-.•1dt-d for 11>< e.~clRSn'e ll>Cof tbt addrcssc,,. Pm"ltb-es of 5Ubscq""'11 use of ti-
ne of this company or any member of its staff, or reproducdon of a his 1':po,1 in connection "'ith the advertisemen~ promotion or sale of any product or process. or in connection with the re-publication of this ,epon for any purpose Olh<:r ahan fonhendclrcsstt ... ,11 be sr:,nt«l 1,1nl; on conlllct. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 2103706
Project: 1st Quarter Chloroform 2021
Analyte Result
Lab Sample ID: 2103706-00lCMSD Date Analyzed:
Test Code: 8260D-W-DEN100
Carbon tetrachloride 19.7
Chloroform 18.9
Chloromethane 15.3
Methylene chloride 20.2
Surr: l ,2-Dichloroethane-d4 52.0
Surr: 4-Bromofluorobenzene 43.4
Surr: Dibromofluoromethane 45.1
Surr: Toluene-d8 48.2
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: Tanner Holliday
Dept: MS VOA
QC Type: MSD
Reporting Amount Spiked Spike Ref.
Units Method MDL Limit Amount %REC
03/25/2021 1500h
--
µg/L SW8260D 0.785 1.00 20.00 0 98.4
µg/L SW8260D 0.360 1.00 20.00 0 94.5
µg/L SW8260D 0.682 1.00 20.00 0 76.7
µg/L SW8260D 0.451 1.00 20.00 0 101
µg/L SW8260D 50.00 104
µg/L SW8260D 50.00 86.7
µg/L SW8260D 50.00 90.2
µg/L SW8260D 50.00 96.5
Limits
66 -143
74 -120
30 -149
65 -154
80 -136
85 -121
78 -132
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit
24 19.9 35
22.4 16.8 35
20.4 28.4 35
22 8.29 35
Qual
Report Date: 3/31/2021 Page 29 of 29
analyses applicable to the CW A. SDW A. and RCRA are pcrfonncd in :u:cO«lan« to NEL.\C prouxols Pertinent sampling information is located oo the attached COC. Confidential Business lnfonnation· This rcpan is pro,·1ded for tl1< c.~ch!Sl,'C us,, of the addre,...,e. Pri~,leges of suhscqulont use of it
ne of this company or any member of its staff, or rcprodu<tion of this rcpon in connccllon with the odvertisemcnt., promotion or sale of any p.-oduct or process. or in connection with the re-publication of thtS rcpon for any purpos,, othei-than for the addn:ss<c will be i;n,nlod only on contact. This
American West Analytical Laboratories Rpt Emailed: UL
Denison
WORK ORDER Summary WorkOrder: 2103706
Due Date: 4/8/2021
Page 1 of2
Client:
Client ID:
Project:
Comments:
Sample ID
2!<>3706-00lA
2103706-00lB
2103706-00lC
2103706-002A
2103 706-002B
2103 706-002C
2103 706-003A
2103706-003B
2103706-003C
2103 706-004A
2103706-004B
2103 706-004C
2103 706-005A
2103706-005B
2103 706-005C
Printed: 03/25/21 13:58
Energy Fuels Resources, Inc.
ENE300
1st Quarter Chloroform 2021
Contact: Tanner Holliday
QC Level: III WO Type: Project
QC 3 (no chromatograms). EDD-Denison. CC [e-mail]; (USE PROJECT for special DLs). Do not use "*R_" samples as MS/MSD.; -~ ~
Client Sample ID Collected Date Received Date Test Code Matrix·· Sel Storage
MW-32 _ 03222021 ·. ''·' :. >}~?!J9~J 12~0~ 3/25/2021 1015h 300.0aW . · , .• -11:cr~~9~s: • ·, . ~·· , .. I
df-wc
1 SEL Ana/JJ_tes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
·:· ! ' Test Group: 8260D-W-DENI 00; # of Analytes: 41 # of Surr: 4
T\\14-75_03222021 3/22/20211230h 3i2S/20211015h 300.0-W Aqueous df-wc
1 SEL Ana/ytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Anal)i_tes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENJOO; #of Analytes: 4 /#ofSurr: 4
T\\14-16_03242021 3/24/2021 0815h 3/25/2021 1015h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-DENI00; # of Analytes: 4_/ # of Surr: 4
T\\14-29_03242021 3/24/2021 0825h 3/25/20211015h 300.0-W Aqueous df-wc
1 SEL Alzalytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana/ytes: N03N02N
8260D-W-DEN100 VOCFridge
Test Group: 8260D-W-_DENJ 00; #yj Analytes: 41 # of Surr: 4
T\\14-10_03242021 3/24/2021 0840h 3/25/20211015h 300.0-W Aqueous df-wc
1 SEL Anal;i_res: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Ana/ytes: N03N02N
8260D-W-DEN100 VOCFridge
Test GrouE_: 8260D-'/!':_DEN I 00; #_of Ana/yles: 41 # of Surr: 4
LABORATORY CHECK: %M O RT O CN O TAT O QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed'"-----
3
3
3
3
3
WORK ORDER Summary WorkOrder: 2103706 Page2 of2
Client: Energy Fuels Resources, Inc. Due Date: 4/8/2021 ·
Sample ID Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
2103706-006A TW4-07 _03242021 3/24/2021 0848h 3/25/2021 1015h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103 706-006B N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
2103706-006C 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DEN100; # of Analytes: 41 # of Surr: 4
2103706-007A 1W4-26_03242021 3/24/2021 0857h 3/25/2021 1015h 300.0-W Aqueous df-wc
I SEL Analytes: CL
2103706-0078 N02/N03-W-353.2 df • no2/no3
1 SEL Analytes: N03N02N
2103706-007C 8260D-W-DEN100 VOCFridge 3
• , •• '. ,; ,•i Test Group: 8260D-W-DENIOO; # of Analytes: 41 # of Surr: 4
2103706-00SA 1W4-16R_03232021 3/23/2021 0800h 3/25/2021 1015h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
2103706-00SB N02/NOJ-W-JSJ.2 df-no2/no3
1 SEL Analytes: N03N02N
2103706-00SC 8260D-W-DEN100 VOCFridge 3
Test Group: 8260D-W-DENJOO; #of Analytes: 4/# ofSurr: 4
2103706-009A Trip Blank 3/22/2021 1230h 3/25/2021 1015h 8260D-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260D-W-DENJOO; # of Analytes: 41 # of Surr: 4
Printed: 03/25/21 I 0:51 LABORATORY CHECK: %M O RT O CN O TAT [J QC O LUO 0 HOK ___ HOK __ _ HOK___ COC Emailed ____ _
~
Client:
Address:
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Toll Free# [phone]
Fax# [phone] Email [e-mail]
www.awal-labs.com
Energy Fuels Resources, Inc.
6425 S. Hwy. 191
Blanding, UT 84511
Contact: .GaHin Pldffli!~ -(._t\QL(" H2 ll; ~~~
Phone#: [phone] Cell#:
Email: thollida:,@ellergyfa.els.com; [e-mail]
Project Name: 1st Quarter Chloroform 2021
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Samoled
IMW-32_03222021 3/22/2021
Time
Samoled
1230
CHAIN OF CUSTODY 2./0!J?o (1
All analysis wiU bo conduc:led using NBA!' -m<!llodG and all data will be reported uolng AWA!.'s slandaro analyte lists and reporting
llmlto (PQL) unless spocilk:ally NICIIJ05!«1 olhotwloe on lhls Chain of Custody ond/Of ollllchod documenlation.
AWAL Lab Sample Set#
Page 1 of 1
~ )( ~ ·c: 1ii ~ ~
0 ., C.J ci
'l5 E co .. ell
5 w
QC Level:
3
c:;-a'
c5 f;j c:,
0) ~ ..
ti) 0 c:, g c:,
lt) ..... ~ C'1 g 0
X X
G' c:,
IO "' ~ .. t) g
X
Turn Around Time:
Standard
Unless ether arrangemenls have been made, 11Due Date:
signed reports will be emailed by 5:00 pm on
the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
FM Compliance With:
0 NELAP
0 RCRA
D CWA
0 SOWA
0 El.AP/ A2LA
0 NLLAP a No~mpliance
D Other:
Known Hazards
&
Sample Comments
Laboratory Use Only
Samples Were: (/( P J
•ebanddo(]vered
2 Amt:1111111 .. e
3 T~moro /, 7"' •e
4 ReailYod e"'~on/1.ealdng
(lmpmpody Soalodt'. 1 y lY
S ~Y Preserved N
~elbench
y N
6 Received Within
Holdlng Times
CJ N
2 fMW-'1&_03222o:H-_ T w~ -rr_ d )'2.,"2,J.(h, 3/22/2021 1230 5 w X X X
3 TW4-16_03242021 3/24/2021 815 5 w X X X
COC Tepe Was: -,... -.. L_____. :..:..:=:..:.....:_:_,1.. ____ --11-+-'l--+--+-+---+--t:_-t--t---t--t--t--;r,--------------,1 1 Present on Outer Package
c) N NA
:r-
4 TW4-29_03242021 3/24/2021 825 5 w X X X
s TW4-10_03242021 3/24/2021 840 5 w X X X
2 ~kenonOderPackage
f!.._) N NA
6 TW4-07_03242021 3/24/2021 848 5 w X X X
7 TW4-26_03242021 3/24/2021 857 5 w X X X
s TW4-16R_03232021 3/23/2021 800 5 w X X X
3 Present on Sample ~
y N ~
4 Unbroken on Sample t:::7\
y N ~
9 TRIPBLANK 3/22/2021 1230 3 w X
0
Oisaepondos Batwoon Sample ------------t.-=~::..:==+-=..:....:.-+-1-1---~-~-il---l---f--t--t--t--+-+-+-t------------;1~andCOCRecoro/N,
y u
2
RolinQ\Ji!lled by: -'\ J,/. f , ~. J
~lgnaluro ~4'lf\/ft__7/~
T~Hoffiday V
Data:
,Tlmo;
,Rl>cGl•ed by:
312.4/202 I 1S1cnaM11
11oolPdnt Nomo: /
[Oalr. Special Instructions:
'11ma:
iPrHNam!"_ ,~-~ r= ,:=~¥~31£~: 1,/ 11a::~~ytical Scope of Work for Reporting Lumm and VOC
P~Namo: ~ .
RallnQUillled by:
IS1ana1uto IO•t•: R-ved by: T \ -10..t.:
[s;gnnturo % d~ U'ALl l!-i2±W tnme: Time: ' I. V \ ..... ~~, , I ,~-~ d 'Pr1ntNmno: Print Name:
Rlll~by:
SlgMlurl
Dalo: Received by:
ISil!aa!ure
Date: .vl__
Tlmo: IJime:
Print Nnmot P.!!!J!j,lame:
Analysis
Ammonia
COD
Cvanide
Metals
N02/N03
O&G
Phenols
Sulfide
TKN
TPO~
CrVI+
Procedure:
Frequency:
Preservation Check Sheet
s le Set E amo:
Preservative I ,2_ b c.-/ 5 ('o
pH<2H2S04
oH<2H2S04
oH>12 NaOH
oH<2HN03
nH<2B2S04 \/, 5 v_ t; Y,f t5" ~/ V/s
nH<2HCL , , .,, .r I' ,
oH <2 H2S04 I
pH>9NaOH,
Zn Acetate
oH<2H2S04
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
:::J
ii.,.;-
dpH
8"
~f
l)
2)
3)
4)
5)
6)
7)
lf 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:
pH Lot#:
2103 ?6' G,
(x_(j(,L
Tab I
Quality Assurance and Data Validation Tables
1-1: Field QA/QC Evaluation
1x Casing
Volume
NA
48.62
32.11
41.87
NA
NA
NI\
27.08
65.10
99.00
Continuous I Pum ed well
Oontinuousl . Pumped well
Continuous! Pumped well
88.00
2x Casing
Volume
97.24
64.22
83.74
54.16
Volume Check
oka
Conductivit H
1887
2983
3773 3700 1.95 6.74 6.79 0.74
3771 3775 0.11 6.51 6.52 0.15
1950 1920 6.63 6.65 0.30
2585 6.50 NC
2950 6.88 NC
5393 6.98 NC
3587 3589 6.83 6.84
8723 6.90
Tern erature
14.89
13.80
14.70 14.73 369 363 1.64 10:a 11 .0 1.83 5.2 5.3 1.90
14.18 14.20 0.14 308 298 3.30 &4:0 63.0 1.57 6.4 6.3 1.57
15.53 15.54 0.06 443 443 0.00 20.0 19.5 2.53 13.5 13.3 1.49
16.07 NC 526 NC 0 NC 28-.7 NC
15.39 NC 403 NC 0 NC 40.1 NC
15.34 NC 428 NC 0 NC 96.0 NC
14.30 14.41 291 290 3.2 3.3 14.1 14.0 0.71
15.09 433 37.7 NC
The OAP does not require that turbidity measurements be less than 5 NTU prior to
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
Trip Blank Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
Trip Blank Chloroform 2/23/2021 2/26/2021 3 14 OK
Trip Blank Chloromethane 2/23/2021 2/26/2021 3 14 OK
Trip Blank Methylene chloride 2/23/2021 2/26/2021 3 14 OK
Trip Blank Carbon tetrachloride 3/16/2021 3/22/2021 6 14 OK
Trip Blank Chloroform 3/16/2021 3/22/2021 6 14 OK
Trip Blank Chloromethane 3/16/2021 3/22/2021 6 14 OK
Trip Blank Methylene chloride 3/16/2021 3/22/2021 6 14 OK
Trip Blank Carbon tetrachloride 3/22/2021 3/25/2021 3 14 OK
Trip Blank Chloroform 3/22/2021 3/25/2021 3 14 OK
Trip Blank Chloromethane 3/22/2021 3/25/2021 3 14 OK
Trip Blank Methylene chloride 3/22/2021 3/25/2021 3 14 OK
MW-04 Chloride 2/23/2021 3/6/2021 11 28 OK
MW-04 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
MW-04 Chloroform 2/23/2021 2/26/2021 3 14 OK
MW-04 Chloromethane 2/23/2021 2/26/2021 3 14 OK
MW-04 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
MW-04 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-01 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-01 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-01 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-0l Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-01 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-0l Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-02 Chloride 2/23/2021 3/6/2021 11 28 OK
TW4-02 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-02 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-02 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-02 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-02 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-03 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-03 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-03 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-03 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-03 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-03 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-03R Chloride 3/16/2021 3/24/2021 8 28 OK
TW4-03R Carbon tetrachloride 3/16/2021 3/19/2021 3 14 OK
TW4-03R Chloroform 3/16/2021 3/19/2021 3 14 OK
TW4-03R Chloromethane 3/16/2021 3/19/2021 3 14 OK
TW4-03R Methylene chloride 3/16/2021 3/19/2021 3 14 OK
TW4-03R Nitrate/Nitrite (as N) 3/16/2021 3/20/2021 4 28 OK
TW4-04 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-04 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-04 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-04 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-04 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-04 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-05 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-05 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-05 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-05 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-05 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
I-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Anal¥sis Date (Days) Time (Days) Check
TW4-05 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-06 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-06 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-06 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-06 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-06 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-06 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-07 Chloride 3/24/2021 3/26/2021 2 28 OK
TW4-07 Carbon tetrachloride 3/24/2021 3/25/2021 1 14 OK
TW4-07 Chloroform 3/24/2021 3/26/2021 2 14 OK
TW4-07 Chloromethane 3/24/2021 3/25/2021 I 14 OK
TW4-07 Methylene chloride 3/24/2021 3/25/2021 1 14 OK
TW4-07 Nitrate/Nitrite (as N) 3/24/2021 3/30/2021 6 28 OK
TW4-08 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-08 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-08 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-08 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-08 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-08 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-09 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-09 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-09 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-09 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-09 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-09 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-10 Chloride 3/24/2021 3/26/2021 2 28 OK
TW4-10 Carbon tetrachloride 3/24/2021 3/25/2021 1 14 OK
TW4-10 Chloroform 3/24/2021 3/26/2021 2 14 OK
TW4-10 Chloromethane 3/24/2021 3/25/2021 1 14 OK
TW4-10 Methylene chloride 3/24/2021 3/25/2021 1 14 OK
TW4-10 Nitrate/Nitrite (as N) 3/24/2021 3/30/2021 6 28 OK
TW4-ll Chloride 2/23/2021 3/6/2021 11 28 OK
TW4-11 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-11 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-11 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-11 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-l l Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-12 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-12 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-12 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-12 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-12 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-12 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-13 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-I3 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-I3 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-I3 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-13 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-13 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-14 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-14 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-14 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-14 Chloromethane 3/18/2021 3/22/2021 4 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
TW4-14 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-14 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
MW-26 Chloride 2/23/2021 3/3/2021 8 28 OK
MW-26 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
MW-26 Chloroform 2/23/2021 2/26/2021 3 14 OK
MW-26 Chloromethane 2/23/2021 2/26/2021 3 14 OK
MW-26 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
MW-26 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-16 Chloride 3/24/2021 3/26/2021 2 28 OK
TW4-16 Carbon tetrachloride 3/24/2021 3/25/2021 1 14 OK
TW4-16 Chloroform 3/24/2021 3/25/2021 1 14 OK
TW4-16 Chloromethane 3/24/2021 3/25/2021 1 14 OK
TW4-16 Methylene chloride 3/24/2021 3/25/2021 1 14 OK
TW4-16 Nitrate/Nitrite (as N) 3/24/2021 3/30/2021 6 28 OK
TW4-16R Chloride 3/23/2021 3/26/2021 3 28 OK
TW4-16R Carbon tetrachloride 3/23/2021 3/25/2021 2 14 OK
TW4-16R Chloroform 3/23/2021 3/25/2021 2 14 OK
TW4-16R Chloromethane 3/23/2021 3/25/2021 2 14 OK
TW4-16R Methylene chloride 3/23/2021 3/25/2021 2 14 OK
TW4-16R Nitrate/Nitrite (as N) 3/23/2021 3/30/2021 7 28 OK
MW-32 Chloride 3/22/2021 3/26/2021 4 28 OK
MW-32 Carbon tetrachloride 3/22/2021 3/25/2021 3 14 OK
MW-32 Chloroform 3/22/2021 3/25/2021 3 14 OK
MW-32 Chloromethane 3/22/2021 3/25/2021 3 14 OK
MW-32 Methylene chloride 3/22/2021 3/25/2021 3 14 OK
MW-32 Nitrate/Nitrite (as N) 3/22/2021 3/30/2021 8 28 OK
TW4-18 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-18 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-18 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-18 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-18 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-18 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-19 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-19 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-19 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-19 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-19 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-19 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-21 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-21 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-21 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-21 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-21 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-21 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-22 Chloride 2/23/2021 3/6/2021 11 28 OK
TW4-22 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-22 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-22 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-22 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-22 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-23 Chloride 3/17/2021 3/25/2021 8 28 OK
TW4-23 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-23 Chloroform 3/17/2021 3/19/2021 2 14 OK
1-2: Holding Time Evaluation
I'
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-23 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-23 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-23 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-24 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-24 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-24 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-24 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-24 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-24 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-25 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-25 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-25 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-25 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-25 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-25 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-26 Chloride 3/24/2021 3/26/2021 2 28 OK
TW4-26 Carbon tetrachloride 3/24/2021 3/25/2021 1 14 OK
TW4-26 Chloroform 3/24/2021 3/26/2021 2 14 OK
TW4-26 Chloromethane 3/24/2021 3/25/2021 1 14 OK
TW4-26 Methylene chloride 3/24/2021 3/25/2021 1 14 OK
TW4-26 Nitrate/Nitrite (as N) 3/24/2021 3/30/2021 6 28 OK
TW4-27 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-27 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-27 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-27 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-27 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-27 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-28 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-28 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-28 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-28 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-28 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-28 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-29 Chloride 3/24/2021 3/26/2021 2 28 OK
TW4-29 Carbon tetrachloride 3/24/2021 3/25/2021 1 14 OK
TW4-29 Chloroform 3/24/2021 3/26/2021 2 14 OK
TW4-29 Chloromethane 3/24/2021 3/25/2021 1 14 OK
TW4-29 Methylene chloride 3/24/2021 3/25/2021 1 14 OK
TW4-29 Nitrate/Nitrite (as N) 3/24/2021 3/30/2021 6 28 OK
TW4-30 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-30 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-30 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-30 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-30 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-30 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-31 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-31 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-31 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-31 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-31 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-31 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-32 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-32 Carbon tetrachloride 3/17/2021 3/19/2021 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
TW4-32 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-32 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-32 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-32 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-33 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-33 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-33 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-33 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-33 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-33 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-34 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-34 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-34 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-34 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-34 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-34 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-35 Chloride 3/17/2021 3/25/2021 8 28 OK
TW4-35 Carbon tetrachloride 3/17 /202 I 3/19/2021 2 14 OK
TW4-35 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-35 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-35 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-35 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-36 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-36 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-36 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-36 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-36 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-36 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-37 Chloride 2/23/2021 3/6/2021 11 28 OK
TW4-37 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-37 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-37 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-37 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-37 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-38 Chloride 3/18/2021 3/25/2021 7 28 OK
TW4-38 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-38 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-38 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-38 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-38 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-39 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-39 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-39 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-39 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-39 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-39 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-40 Chloride 2/23/2021 3/3/2021 8 28 OK
TW4-40 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-40 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-40 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-40 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-40 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-41 Chloride 2/23/2021 3/3/2021 8 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
TW4-41 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-41 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-41 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-41 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-41 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-42 Chloride 3/17/2021 3/24/2021 7 28 OK
TW4-42 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-42 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-42 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-42 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-42 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-60 Chloride 2/23/2021 3/8/2021 13 28 OK
TW4-60 Carbon tetrachloride 2/23/2021 2/26/2021 3 14 OK
TW4-60 Chloroform 2/23/2021 2/26/2021 3 14 OK
TW4-60 Chloromethane 2/23/2021 2/26/2021 3 14 OK
TW4-60 Methylene chloride 2/23/2021 2/26/2021 3 14 OK
TW4-60 Nitrate/Nitrite (as N) 2/23/2021 3/1/2021 6 28 OK
TW4-65 Chloride 3/17/2021 3/25/2021 8 28 OK
TW4-65 Carbon tetrachloride 3/17/2021 3/19/2021 2 14 OK
TW4-65 Chloroform 3/17/2021 3/19/2021 2 14 OK
TW4-65 Chloromethane 3/17/2021 3/19/2021 2 14 OK
TW4-65 Methylene chloride 3/17/2021 3/19/2021 2 14 OK
TW4-65 Nitrate/Nitrite (as N) 3/17/2021 3/20/2021 3 28 OK
TW4-70 Chloride 3/18/2021 3/26/2021 8 28 OK
TW4-70 Carbon tetrachloride 3/18/2021 3/22/2021 4 14 OK
TW4-70 Chloroform 3/18/2021 3/22/2021 4 14 OK
TW4-70 Chloromethane 3/18/2021 3/22/2021 4 14 OK
TW4-70 Methylene chloride 3/18/2021 3/22/2021 4 14 OK
TW4-70 Nitrate/Nitrite (as N) 3/18/2021 3/20/2021 2 28 OK
TW4-75 Chloride 3/22/2021 3/26/2021 4 28 OK
TW4-75 Carbon tetrachloride 3/22/2021 3/25/2021 3 14 OK
TW4-75 Chloroform 3/22/2021 3/25/2021 3 14 OK
TW4-75 Chloromethane 3/22/2021 3/25/2021 3 14 OK
TW4-75 Methylene chloride 3/22/2021 3/25/2021 3 14 OK
TW4-75 Nitrate/Nitrite (as N) 3/22/2021 3/30/2021 8 28 OK
Table I-3 Recipt Temperature Check
Sample Batch Wells in Batch Temperature
MW-04, TW4-0l, TW4-02, TW4-04, TW4-ll, MW-26, TW4-19, TW4-21,
2102631 TW4-22, TW4-24, TW4-25, TW4-37, TW4-39, TW4-40, TW4-41, TW4-60, l.4°C
Trip Blank
TW4-03, TW4-03R, TW4-05, TW4-06, TW4-08, TW4-09, TW4-12, TW4-13,
2103541 TW4-14, TW4-18, TW4-23, TW4-27, TW4-28, TW4-30, TW4-31, TW4-32, 2.3°C TW4-33, TW4-34, TW4-35, TW4-36, TW4-38, TW4-42, TW4-65, TW4-70,
Trip Blank
2103706 TW4-07, TW4-10, TW4-16, TW4-16R, MW-32, TW4-26, TW4-29, TW4-75, l.4°C 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 -eporlmg 1m1t ec L .. Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
Trip Blank Carbon tetrachloride 1 ug/L u 1 l OK
Trip Blank Chloroform 1 ug/L u 1 l OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
Trip Blank Carbon tetrachloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u 1 I OK
Trip Blank Methylene chloride 1 ug/L u I l OK
Trip Blank Carbon tetrachloride 1 ug/L u l 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 10 1 OK
MW-04 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-04 Chloroform 100 ug/L 100 1 OK
MW-04 Chloromethane 1 ug/L u 1 1 OK
MW-04 Methylene chloride 1 ug/L u 1 I OK
MW-04 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-01 Chloride 1 mg/L 10 1 OK
TW4-01 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-01 Chloroform 10 ug/L 10 1 OK
TW4-01 Chloromethane 1 ug/L u 1 l OK
TW4-0l Methylene chloride 1 ug/L u l 1 OK
TW4-0l Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-02 Chloride 1 mg/L 10 1 OK
TW4-02 Carbon tetrachloride l ug/L u 1 1 OK
TW4-02 Chloroform 100 ug/L 100 l 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 10 1 OK
TW4-03 Carbon tetrachloride l ug/L u 1 l OK
TW4-03 Chloroform 1 ug/L u l 1 OK
TW4-03 Chloromethane 1 ug/L u 1 1 OK
TW4-03 Methylene chloride l ug/L u 1 1 OK
TW4-03 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-03R Chloride 1 mg/L u 1 1 OK
TW4-03R Carbon tetrachloride 1 ug/L u l 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 l mg/L 10 1 OK
TW4-04 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-04 Chloroform 100 ug/L 100 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 5 0.1 OK
TW4-05 Chloride 1 mg/L 10 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
TW4-05 Methylene chloride 1 ug/L u 1 1 OK
TW4-05 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
I 5 R -eportJni:t 1m1t ec L .. Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-06 Chloride I m,g/L JO I OK
TW4-06 Carbon tetrachloride I ug/L u I I OK
TW4-06 Chloroform I ug/L I 1 OK
TW4-06 Chloromethane I ug/L u I 1 OK
TW4-06 Methylene chloride I ug/L u I I OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-07 Chloride I mg/L 10 I OK
TW4-07 Carbon tetrachloride I ug/L u 1 1 OK
TW4-07 Chloroform 10 ug/L 10 I OK
TW4-07 Chloromethane I ug/L u I I OK
TW4-07 Methylene chloride I ug/L u 1 I OK
TW4-07 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-08 Chloride I mg/L 10 I OK
TW4-08 Carbon tetrachloride I u,g/L u I I OK
TW4-08 Chloroform I ug/L I 1 OK
TW4-08 Chloromethane I ug/L u I I OK
TW4-08 Methylene chloride I ug/L u I I OK
TW4-08 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-09 Chloride 1 mg/L 10 1 OK
TW4-09 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-09 Chloroform 1 ug/L I l OK
TW4-09 Chloromethane 1 ug/L u I I OK
TW4-09 Methylene chloride I ug/L u 1 I OK
TW4-09 Nitrate/Nitrite (as N) 0.1 mg/L I 0.1 OK
TW4-IO Chloride I mg/L 10 I OK
TW4-10 Carbon tetrachloride I ug/L u I I OK
TW4-10 Chloroform 10 ug/L 10 1 OK
TW4-10 Chloromethane 1 ug/L u 1 1 OK
TW4-10 Methylene chloride I ug/L u 1 1 OK
TW4-10 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-l l Chloride 1 mg/L 10 I OK
TW4-ll Carbon tetrachloride 1 ug/L u 1 I OK
TW4-l l Chloroform 100 ug/L 100 1 OK
TW4-11 Chloromethane 1 ug/L u 1 I OK
TW4-11 Methylene chloride 1 ug/L u I 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 I 1 OK
TW4-12 Chloroform 1 ug/L u 1 1 OK
TW4-12 Chloromethane 1 ug/L u I 1 OK
TW4-12 Methylene chloride 1 ug/L u 1 1 OK
TW4-12 Nitrate/Nitrite (as N) 0.1 mg/L 5 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 I I OK
TW4-13 Methylene chloride 1 ug/L u I I OK
TW4-13 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-14 Chloride 1 mg/L 10 1 OK
TW4-14 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-14 Chloroform 1 ug/L 1 1 OK
TW4-14 Chloromethane 1 ug/L u 1 1 OK
TW4-14 Methylene chloride I ug/L u 1 1 OK
TW4-14 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
I 5 R -eporting 1m1t ec L .. Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
MW-26 Chloride 2 mg/L 20 1 OK
MW-26 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-26 Chloroform 100 ug/L 100 1 OK
MW-26 Chloromethane I ug/L u 1 1 OK
MW-26 Methylene chloride I ug/L 1 1 OK
MW-26 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-16 Chloride J mg/L JO 1 OK
TW4-16 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-16 Chloroform 1 ug/L 1 1 OK
TW4-16 Chloromethane 1 ug/L u 1 1 OK
TW4-16 Methylene chloride I ug/L u 1 1 OK
TW4-16 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-16R Chloride 1 mg/L u 10 1 OK
TW4-16R Carbon tetrachloride I ug/L u 1 1 OK
TW4-16R Chloroform J ug/L l 1 OK
TW4-16R Chloromethane 1 ug/L u 1 1 OK
TW4-I6R Methylene chloride I ug/L u I 1 OK
TW4-16R Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
MW-32 Chloride 1 mg/L JO 1 OK
MW-32 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-32 Chloroform 1 ug/L u 1 1 OK
MW-32 Chloromethane 1 ug/L u 1 1 OK
MW-32 Methylene chloride 1 ug/L u 1 1 OK
MW-32 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-18 Chloride 1 mg/L 10 1 OK
TW4-18 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-18 Chloroform I ug/L l 1 OK
TW4-18 Chloromethane I 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 I ug/L 1 1 OK
TW4-19 Chloroform 100 ug/L JOO 1 OK
TW4-19 Chloromethane 1 ug/L u 1 1 OK
TW4-19 Methylene chloride 1 ug/L u 1 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-21 Chloride 10 mg/L 100 1 OK
TW4-21 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-21 Chloroform 10 ug/L 10 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 10 mg/L 100 1 OK
TW4-22 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-22 Chloroform 100 ug/L 100 1 OK
TW4-22 Chloromethane 1 ug/L u 1 1 OK
TW4-22 Methylene chloride 1 ug/L u 1 1 OK
TW4-22 Nitrate/Nitrite (as N) 1 mg/L 100 0.1 OK
TW4-23 Chloride 1 mg/L 10 1 OK
TW4-23 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-23 Chloroform 1 ug/L u 1 1 OK
TW4-23 Chloromethane 1 ug/L u 1 1 OK
TW4-23 Methylene chloride 1 ug/L u 1 1 OK
TW4-23 Nitrate/Nitrite (as N) 0.1 mg/L u l 0.1 OK
I 5 R -eponm_g 1m1t ec L .. Ch k
Lab
I Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-24 Chloride 10 mg/L 100 1 OK
TW4-24 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-24 Chloroform 1 ug/L 1 1 OK
TW4-24 Chloromethane 1 ug/L 1 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 I 1 OK
TW4-25 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-26 Chloride 1 mg/L 10 1 OK
TW4-26 Carbon tetrachloride 1 ug/L u I 1 OK
TW4-26 Chloroform 100 ug/L 100 1 OK
TW4-26 Chloromethane 1 ug/L u 1 1 OK
TW4-26 Methylene chloride I ug/L u 1 I OK
TW4-26 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-27 Chloride 1 mg/L 10 1 OK
TW4-27 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-27 Chloroform I ug/L 1 1 OK
TW4-27 Chloromethane 1 ug/L u 1 1 OK
TW4-27 Methylene chloride 1 ug/L u I I OK
TW4-27 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-28 Chloride L mg/L 10 1 OK
TW4-28 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-28 Chloroform 1 ug/L u 1 l OK
TW4-28 Chloromethane 1 ug/L u l 1 OK
TW4-28 Methylene chloride l 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 10 1 OK
TW4-29 Carbon tetrachloride 1 ug/L u l 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 l 1 OK
TW4-29 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-30 Chloride I mg/L 10 1 OK
TW4-30 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-30 Chloroform 1 ug/L 1 1 OK
TW4-30 Chloromethane 1 u,g/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
TW4-3I Chloride 1 mg/L 10 l OK
TW4-31 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-31 Chloroform 1 u,g/L u I 1 OK
TW4-31 Chloromethane 1 ug/L u 1 1 OK
TW4-31 Methylene chloride I ug/L u 1 1 OK
TW4-3I Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-32 Chloride 1 mg/L 10 1 OK
TW4-32 Carbon tetrachloride 1 ug/L u l l OK
TW4-32 Chloroform 1 ug/L u 1 1 OK
TW4-32 Chloromethane 1 ug/L u 1 1 OK
TW4-32 Methylene chloride 1 ug/L u 1 1 OK
TW4-32 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
I 5 R -eportmg Ifill ec L' . Ch k
Lab
Reporting Dilution Required
Location Analvte Limit Units Qualifier Factor Reportinp; Limit RLCheck
TW4-33 Chloride 1 mp;/L 10 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 5 0.1 OK
TW4-34 Chloride 1 mg/L 10 1 OK
TW4-34 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-34 Chloroform 1 ug/L u 1 1 OK
TW4-34 Chloromethane I ug/L u 1 1 OK
TW4-34 Methylene chloride 1 ug/L u 1 1 OK
TW4-34 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-35 Chloride 1 mg/L 10 1 OK
TW4-35 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-35 Chloroform 1 ug/L u 1 1 OK
TW4-35 Chloromethane I ug/L u 1 1 OK
TW4-35 Methylene chloride 1 ug/L u 1 1 OK
TW4-35 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-36 Chloride 1 mg/L 10 1 OK
TW4-36 Carbon tetrachloride 1 ug/L u I 1 OK
TW4-36 Chloroform 1 ug/L u I 1 OK
TW4-36 Chloromethane 1 ug/L u I 1 OK
TW4-36 Methylene chloride 1 ug/L u 1 I OK
TW4-36 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
TW4-37 Chloride 5 mg/L 50 1 OK
TW4-37 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-37 Chloroform 100 ug/L 100 1 OK
TW4-37 Chloromethane 1 ug/L u I 1 OK
TW4-37 Methylene chloride I ug/L u 1 1 OK
TW4-37 Nitrate/Nitrite (as N) 0.5 mg/L 50 0.1 OK
TW4-38 Chloride 1 mg/L 10 I OK
TW4-38 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-38 Chloroform 1 ug/L u 1 1 OK
TW4-38 Chloromethane 1 ug/L u 1 1 OK
TW4-38 Methylene chloride I ug/L u I 1 OK
TW4-38 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-39 Chloride 2 mg/L 20 1 OK
TW4-39 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-39 Chloroform 100 ug/L 100 1 OK
TW4-39 Chloromethane 1 ug/L u 1 1 OK
TW4-39 Methylene chloride 1 ug/L u 1 1 OK
TW4-39 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-40 Chloride 1 mg/L 10 1 OK
TW4-40 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-40 Chloroform 10 ug/L 10 1 OK
TW4-40 Chloromethane 1 ug/L 1 I OK
TW4-40 Methylene chloride 1 ug/L u I I OK
TW4-40 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-41 Chloride I m.11:/L 10 1 OK
TW4-41 Carbon tetrachloride I ug/L u 1 I OK
TW4-41 Chloroform 100 ug/L 100 1 OK
TW4-41 Chloromethane 1 ug/L u I 1 OK
TW4-41 Methylene chloride 1 ug/L u I 1 OK
TW4-41 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
I 5 R -cporung 1mtt ec L .. Ch k
Lab
Reporting Dilution Required
Location Analyte Limit Units Qualifier Factor Reporting Limit RLCheck
TW4-42 Chloride 1 mg/L 10 I OK
TW4-42 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-42 Chloroform 1 ug/L u 1 I OK
TW4-42 Chloromethane 1 ug/L u I I OK
TW4-42 Methylene chloride I ug/L u I 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 I OK
TW4-60 Chloroform I ug/L u I 1 OK
TW4-60 Chloromethane 1 ug/L u I I OK
TW4-60 Methylene chloride 1 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 1 1 OK
TW4-65 Chloroform 1 ug/L u I 1 OK
TW4-65 Chloromethane 1 ug/L u 1 I OK
TW4-65 Methylene chloride I ug/L u I I OK
TW4-65 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-70 Chloride 1 mg/L 10 1 OK
TW4-70 Carbon tetrachloride I ug/L u 1 l OK
TW4-70 Chloroform I ug/L I 1 OK
TW4-70 Ch loromethane I ug/L u I I OK
TW4-70 Methylene chloride 1 ug/L u 1 1 OK
TW4-70 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-75 Chloride 1 mg/L 10 1 OK
TW4-75 Carbon tetrachloride I ug/L u I 1 OK
TW4-75 Chloroform I ug/L u I 1 OK
TW4-75 Chloromethane 1 ug/L u 1 1 OK
TW4-75 Methylene chloride 1 ug/L u 1 1 OK
TW4-75 Nitrate/Nitrite (as N) 0.1 mg/L u 1 0.1 OK
1-6 Trip Blank Evaluation
Lab Report Constituent Result
Carbon tetrachloride ND ug/L
2102631 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
2103541 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
Carbon tetrachloride ND ug/L
2103706 Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
I-7 QNQC Evaluation for Sample Duplicates
Constituent
Chloride (mi!IL)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chlorome1hane
Dichloromethane (Methylene Chloride)
Constituent
Chloride (mp/L)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Ch loromethane
Dichloromethane (Methylene Chloride)
Constituent
Chloride (mg/L)
Nitrate + Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chlorome1hane
Dichloromethane (Meth ylene Chloride)
RPD = Relative Percent Difference
ND = The analyte was not detected
TW4-03
28.4
6.19
ND
ND
ND
ND
TW4-09
40.7
1.06
ND
39.0
ND
ND
MW-32
36.8
ND
ND
ND
ND
ND
TW4-65 %RPO
27 .6 2.9
6.64 7.0
ND NC
ND NC
ND NC
ND NC
TW4-70 %RPO
38.7 5.0
1.07 0.9
ND NC
38.2 2.1
ND NC
ND NC
TW4-75 %RPO
37.4 1.6
ND NC
ND NC
ND NC
ND NC
ND NC
I-8 QC Control Limits for Analysis and Blanks
Method Blank Detections
All Method Blanks (MB) for the quarter were nondetect.
Matrix Spike % Recoveries
MS l\'fSD %REC RPD
Lab Report Lab Sample ID Well Analyte %REC %REC Range RPD Rang~
2102631 2102631-001 TW4-25 Chloroform 121 123 74 -120 1.68 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.
I-9 Rinsate Evaluation
~il~e
Iti1lil al~ R~<im1it
$'.afllilp;le,_ •F11ilu:ad ~· (ut tL) iP11,evis t~~ ~1elll 1 t11;g1t ~
TW4-03R Chloroform 1.69 NA
TW4-16R Chloroform 11.6 TW4-30
NA= This rinsate sample was collected prior to the first use of the pump.
TabJ
Kriged Current Quarter Chloroform Isoconcentration Map
EXPLANATION
NS = not sampled; ND= not detected;
ND 40 = not detected in 4th quarter
MW-24A installed during December, 2019
......_ 70 kriged chloroform isocon and label
TW4-42
¢ND
TW4-40
.436
MW-38
-¢"ND
MW-32
e ND
TW4-7
0 875
TWN-1
Q NS
PIEZ-1
~NS
temporary perched monitoring well
installed April, 2019 showing
concentration in µg/L
temporary perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well
installed February, 2018 showing
concentration in µg/L
perched monitoring well showing
concentration in µg/L
temporary perched monitoring well
showing concentration in µg/L
temporary perched nitrate monitoring
well (not sampled)
perched piezometer (not sampled)
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are
chloroform pumping wells; TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells
HYDRO
GEO
KRIGED 1st QUARTER, 2021 CHLOROFORM (1,19/L)
WHITE MESA SITE
CHEM, INC. APPROVED DATE REFERENCE FIGURE
H:/718000/may21 /chloroform/Uchl0321.srf J-1
NS= not sampled; ND= not detected;
ND 4Q = not detected in 4th quarter
...._ 70 kriged chloroform isocon and label
TW442
¢ND
TW4-40
... 436
MW-32
.ND
TW4-7
0 875
PIEZ-2
Q NS
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, TW4-21, TW4-37, TW4-39, TW4-40 and TW4-41 are
chloroform pumping wells; TW4-22, TW4-24, TW4-25 and TWN-2 are nitrate pumping wells
HYDRO
GEO
KRIGED 1st QUARTER, 2021 CHLOROFORM (µg/L)
WHITE MESA SITE
CHEM, INC. APPROVED DATE
(detail map)
REFERENCE H:/718000/may21/
chloroform/Uchl0321 det.srf
FIGURE
J-2
~-
'S
NS = not sampled; ND= not detected;
ND 4Q = not detected in 4th quarter
....._ 70
TW4-42
¢ND
TW4-40
... 436
MW-32
e ND
TW4-7
0 875
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, TW4-21, 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, 2021 CHLOROFORM
GREATER THAN OR EQUAL TO 70 µg/L GRID
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/may21 /
chloroform/Uchl0321 ge 70.srf
FIGURE
J-3
TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs over Time
' Cdon Obloroform Clffitrom ane 1: ,)II Nitrate Chloride ' MWl.4 T ... ~·
(ug/J) (q/1) c~_ :.:_ ('ilf#l (mg/I) (mgl} (uatll I
28-Sep-99 6200
28-Sep-99 5820
28°Sep-99 6020
15-Mar-OO 5520
15-Mar-00 5430
2-Sep-00 5420 9.63
30-Nov-OO 6470 9.37
29-Mar-01 4360 8.77
22-Jun-01 6300 9.02
20-Sep-Ol 5300 9.45
8-Nov-Ol 5200 8
26-Mar-02 4700 8.19
22-May-02 4300 8.21
12-Sep-02 6000 8.45
24-Nov-02 2500 8.1
28-Mar-03 2000 8.3
30-Apr-03 3300 NA
30-May-03 3400 8.2
23-Jun-03 4300 8.2
30-Jul-03 3600 8.1
29-Aug-03 4100 8.4
12-Sep-03 3500 8.5
15-0ct-03 3800 8.1
8-Nov-03 3800 8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 3300 6.71
17-Nov-04 4300 7.5
16-Mar-05 2900 6.3
25-May-05 3170 NA NA NA 7.1 NA
31-Aug-05 3500 <10 <10 <10 7.0 NA
1-Dec-05 3000 <50 <50 <50 7.0 NA
9-Mar-06 3100 <50 <50 50 6 49
14-Jun-06 3000 <50 <50 50 6 49
20-Jul-06 2820 <50 <50 <50 1.2 48
9-Nov-06 2830 2.1 1.4 <1 6.4 50
28-Feb-07 2300 1.6 <1 <1 6.3 47
27-Jun-07 2000 1.8 <1 <1 7 45
15-Aug-07 2600 1.9 <1 <1 6.2 47
10-0ct-07 2300 1.7 <1 <1 6.2 45
26-Mar-08 2400 1.7 <1 <1 5.8 42
25-Jun-08 2500 1.6 <1 <1 6.09 42
10-Sep-08 1800 1.8 <1 <l 6.36 35
15-0ct-08 2100 1.7 <1 <l 5.86 45
4-Mar-09 2200 1.5 <1 <1 5.7 37
23-Jun-09 1800 1.3 <1 <1 5.2 34
14-Sep-09 2000 1.4 <1 <1 5.3 43
C Cli &memane Me" -Nit11ate Chlo.ride MW-4 OJ'O Gl!'M Tetra"'' .. -.
(up() (ua/J), ( ~ Chtoride{ ~ (m~ (mgll)
14-Dec-09 1800 1.6 ND ND 5.8 44
17-Feb-10 1600 1.2 ND ND 4 45
14-Jun-10 2100 1.2 ND ND 5.1 41
16-Aug-10 1900 1.5 ND ND 4.8 38
11-0ct-10 1500 1.4 ND ND 4.9 41
23-Feb-l 1 1700 1.5 ND ND 4.6 40
1-Jun-11 1700 1.4 ND ND 4.9 35
17-Aug-11 1700 1.1 ND ND 4.9 41
16-Nov-1 l 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 I ND ND 4.8 42
ll-Feb-13 1670 1.49 ND ND 4.78 37.8
5-Jun-13 1490 1.31 ND ND 4.22 44
3-Sep-13 1520 1.13 ND ND 4.89 41.4
29-0ct-13 1410 5.58 ND ND 5.25 40.1
27-Jan-14 1390 4.15 ND ND 4.7 38.5
19-May-14 1390 5.21 ND ND 4.08 39.9
24-Aug-14 1490 ND 7.6 ND 3.7 41
21-0ct-14 1440 ND ND ND 5.07 41.5
9-Mar-15 1400 1.26 ND ND 5.75 40.7
8-Jun-15 1300 ND ND ND 2.53 43.1
31-Aug-15 1290 ND ND ND 4.79 44.3
19-0ct-15 1200 ND ND ND 4.43 40.8
9-Mar-16 1240 ND ND ND 5.15 42.2
23-May-16 1580 1.44 ND ND 4.54 43.7
25-Jul-16 1430 ND ND ND 4.95 42.5
12-0ct-16 1470 1.24 ND ND 4.88 44.8
8-Mar-17 1450 1.22 ND ND 4.99 43.3
13-Jun-17 1430 1.15 ND ND 4.88 44.0
26-Jul-17 1400 1.15 ND ND 4.59 43.8
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
1 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
4-Sep-20 1240 ND ND ND 4.93 43.8
28-0ct-20 1050 ND ND ND 4.62 41.4
23-Feb-21 1150 ND ND ND 4.61 46.5
0
......
0 0 0
I\) 0 0 0
(ug/L)
w 0 0 0
~ 0 0 0
(.11 0 0 0
a,
0 0 0
--.J 0 0 0
Sep-99 +-----+----+-----+----+---.---+---_.,,.....,...__--1
Mar-00
Sep-00
Mar-01
Sep-01
Mar-02
Sep-02
g~~!~ I f J .t i:
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
Sep-20
s:: ~ ~ I ()
::J"'
0 a -0 -,
3
~
C: ([) en
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 Tetrachloride Chloride
11 (ug/1) (ug/1) (ug/1) (ug/1) (mg/I) (mg/I)
11
28-Jun-99 1700 7.2
10-Nov-99 5.8
15-Mar-OO 1100
10-Apr-OO 1490
6-Jun-00 1530
2-Sep-00 2320 5.58
30-Nov-OO 3440 7.79
29-Mar-Ol 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.l
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. l
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 <l <1 9.4 47
28-Feb-07 1900 1.2 <l <l 8.9 47
27-Jun-07 1900 1.4 <1 <l 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 <1 <1 7.6 39
25-Jun-08 1900 1.1 <1 <l 8.68 39
10-Sep-08 1700 1.3 <I <l 8.15 35
15-0ct-08 1700 1.3 <1 <1 9.3 41
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-l (ug/1) Tetrachloride (ug/1) Chloride (mg/)) (mg/I) (ug/1) I (ug/1)
11-Mar-09 1700 1.1 <l <l 7.5 37
24-Jun-09 1500 1 <l <l 6.9 37
15-Sep-09 1700 <1 <1 <l 7.3 36
29-Dec-09 1400 <l <1 <l 6.8 41
3-Mar-10 1300 <l <l <1 7.1 35
15-Jun-JO 1600 1.2 <l <l 6.8 40
24-Aug-10 1500 <l <1 <l 6.8 35
14-0ct-10 1500 <l <1 <l 6.6 40
24-Feb-l 1 1300 ND ND ND 6.6 41
l-Jun-11 1200 ND ND ND 7 35
18-Aug-11 1300 ND ND ND 6.8 36
29-Nov-l 1 1300 ND ND ND 6.6 37
19-Jan-12 1300 ND ND ND 6.8 38
14-Jun-12 1000 ND ND ND 7.1 42
13-Sep-12 1000 ND ND ND 5 39
4-0ct-12 1100 ND ND ND 6.5 40
13-Feb-13 1320 3.66 ND ND 6.99 37.6
19-Jun-13 1100 ND ND ND 6.87 39.1
12-Sep-13 1150 ND ND ND 7.12 37.6
14-Nov-13 1280 ND ND ND 7.08 36.5
5-Feb-14 1090 5.47 ND ND 7.74 38.9
23-May-14 1020 4.77 ND ND 6.93 37.4
27-Aug-14 845 ND 1.4 ND 4.8 38
29-0ct-14 1140 ND ND ND 6.31 38.7
9-Mar-15 1130 ND ND ND 7.06 38.3
8-Jun-15 1260 ND ND ND 6.07 40.3
31-Aug-15 1060 ND ND ND 6.28 45.9
19-0ct-15 1040 ND ND ND 1.55 38.5
9-Mar-16 974 ND ND ND 0.148 41.7
23-May-16 1140 ND ND ND 0.138 44.4
25-Jul-16 1160 ND ND ND 5.49 44.7
13-0ct-16 1330 ND ND ND 0.746 44.2
8-Mar-17 519 ND ND ND 4.44 41.5
13-Jun-17 977 ND ND ND 5.74 41.8
26-Jul-l 7 958 ND ND ND 5.04 42.8
ll-Oct-17 556 ND ND ND 5.78 38.5
12-Mar-18 70.4 ND ND ND 4.84 45.8
8-Jun-18 942 ND ND ND 4.38 42.0
22-Aug-18 1010 ND ND ND 4.30 47.3
Chlorofonn Carbon Cbloromeihane Methylene Nitrate Ohloride TW4-1 (ug/1) Tetrathloride tug(I) Chloride (Jng/1) ~mg/l) ~ug/1) ~ug/1) II
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
4-Sep-20 1060 ND ND ND 2.22 43.7
28-0ct-20 924 ND ND ND 4.30 41.9
23-Feb-21 948 ND ND ND 27.20 45.4
0
......
0 0 0
I\)
0 0 0
(ug/L)
c,.:,
0 0 0
.j:>.
0 0 0
CJ1 0 0 0
O')
0 0 0
-..J 0 0 0
28-Jun-99 L I • I ~ I I I I
28-Dec-99
28-Jun-OO
28-Dec-OO
28-Jun-01
28-Dec-01
28-Jun-02
28-Dec-02
28-Jun-03
28-Dec-03
28-Jun-04
28-Dec-04
28-Jun-05
28-Dec-05
28-Jun-06
28-Dec-06
28-Jun-07
28-Dec-07
28-Jun-08
28-Dec-08
28-Jun-09
28-Dec-09
28-Jun-10
28-Dec-10
28-Jun-11
28-Dec-11
28-Jun-12
28-Dec-12
28-Jun-13
28-Dec-13
28-Jun-14
28-Dec-14
28-Jun-15
28-Dec-15
28-Jun-16
28-Dec-16
28-Jun-17
28-Dec-17
28-Jun-18
28-Dec-18
28-J un-1 9 l-----.i.._J,,,
28-Dec-19
28-Jun-20
28-Dec-20 .____._ ____ __. ___ ......_ __ __._ ___ ..__ __ __._ __ ___,
-4 :E .,:a. I ....
0 :T o ... ~ ...
3
< !.
C
C1> (/1
CM l'Gfcmn C rlJen CM. -l\tetlqlene Nttr.ate Chfulde TW4-2 Tetra hmride aoe Cbl.ui~ (ug/1) (ot!'AH ( w*) (ffi!fl) (anwi) (mgAI)
II
10-Nov-99 2510
2-Sep-00 5220
28-Nov-00 4220 10.7
29-Mar-Ol 3890 10.2
22-Jun-Ol 5500 9.67
20-Sep-Ol 4900 11.4
8-Nov-01 5300 10.1
26-Mar-02 5100 9.98
23-May-02 4700 9.78
12-Sep-02 6000 9.44
24-Nov-02 5400 10.4
28-Mar-03 4700 9.5
23-Jun-03 5100 9.6
12-Sep-03 3200 8.6
8-Nov-03 4700 9.7
29-Mar-04 4200 9.14
22-Jun-04 4300 8.22
17-Sep-04 4100 8.4
17-Nov-04 4500 8.6
16-Mar-05 3700 7.7
25-May-05 3750 8.6
31-Aug-05 3900 <10 <10 <10 8 NA
l-Dec-05 3500 <50 <50 <50 7.8 NA
9-Mar-06 3800 <50 <50 <50 7.5 56
14-Jun-06 3200 <50 <50 <50 7.1 56
20-Jul-06 4120 <50 <50 <50 7.4 54
8-Nov-06 3420 2.3 <1 <l 7.6 55
28-Feb-07 2900 1.8 <l <l 7.3 54
27-Jun-07 3000 2.5 <1 <l 7.8 50
15-Aug-07 340 2.2 <1 <l 7.3 49
10-0ct-07 3200 2.1 <1 <l 6.9 51
26-Mar-08 3300 2.3 <l <I 6.9 48
25-Jun-08 3100 2.2 <l <l 7.44 46
10-Sep-08 2800 2.4 <l <l 7.1 42
15-0ct-08 3200 2.4 <2 <2 7.99 47
ll-Mar-09 3100 2.2 <l <l 6.5 46
24-Jun-09 2800 2 <l <l 6.4 44
15-Sep-09 3000 2 <l <l 6.6 43
29-Dec-09 1600 2 <l <1 6.4 46
Chloroform Cub"Gn Ckloro th M:e~ene Nitrate Chloride TW4·2 T a~ Ide :e Cbi'Oride (bg/1) {lt!!ff> {lig/iJ lttal:li) (mg/I) ~pigll)
' 3-Mar-10 2600 2 <1 <l 6.8 42
15-Jun-10 3300 2.6 <1 <l 6.7 43
16-Aug-10 3300 2.5 <l <1 6.6 43
14-0ct-10 3000 2.1 <1 <1 6.5 41
24-Feb-l l 3100 2.4 ND ND 7 46
2-Jun-11 3000 2.2 ND ND 6.8 42
17-Aug-11 2400 1.6 ND ND 6 48
29-Nov-l 1 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
11-0ct-17 1610 ND ND ND 3.28 43.5
12-Mar-18 764 ND ND ND 2.94 44.4
8-Jun-18 949 ND ND ND 3.50 41.3
22-Aug-18 980 ND ND ND 4.83 44.3
28-Nov-18 822 ND ND ND 3.52 41.7
8-Mar-19 1040 ND ND ND 3.92 40.4
5-Jun-19 1360 ND ND ND 4.38 39.8
4-Sep-19 797 ND ND ND 4.79 40.8
Chloroform CarbQJl €h1oromethane Methylene Nitrate Chloride TW4.2 (ugll) TetrachloJ'itle (ug/1) Chloride (mg/I) (mg/I) (ul!/1) (ul!/1)
10-Dec-19 934 ND ND ND 3.40 41.5
19-Feb-20 1880 ND ND ND 6.07 42.l
27-May-20 1070 ND ND ND 3.62 40.6
4-Sep-20 1260 ND ND ND 3.35 41.3
28-0ct-20 1130 ND ND ND 2.34 38.7
23-Feb-21 939 ND ND ND 3.30 43.3
10-Nov-99
10-May-OO
10-Nov-OO
10-May-01
10-Nov-01
10-May-02
10-Nov-02
10-May-03
10-Nov-03
10-May-04
10-Nov-04
10-May-05
10-Nov-05
10-May-06
10-Nov-06
10-May-07
10-Nov-07
10-May-08
10-Nov-08
10-May-09
10-Nov-09
10-May-10
10-Nov-10
10-May-11
10-Nov-11
1 O-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
10-May-20
10-Nov-20
0
0 0 0
9:iir~oO cO-co _Ill
g-Q.z~iii
::J~C:0"0 iir Q ~ i» Q. o'<coo;! o ~ cii-< cii """'0£e."""'"'O g, ... ~:rmro ...... ::J Ill C: C/l
9g_m~~ (") C.. -g C.-1~ ~-~ ~ (") C. 0 5lloD3=i s· -m
(Cl ~ "O
st cii" g CD C. en
I\)
0 0 0
(ug/L)
c.v 0 0 0
.j::,.
0 0 0
(]l
0 0 0
0)
0 0 0
-...J 0 0 0
-t ! a{,
0 :::r 0 ... ~ ... 3
~ 2" Cl> rn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride II TW4-3 Tetrachloride Chloride (ug/1) (uwl) (ug/1) (uwl) (mg/I) (mg/I)
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-OI 390 2.61
20-Sep-Ol 300 3.06
7-Nov-01 170 3.6
26-Mar-02 11 3.87
21-May-02 204 4.34
12-Sep-02 203 4.32
24-Nov-02 102 4.9
28-Mar-03 0 4.6
23-Jun-03 0 4.8
12-Sep-03 0 4.3
8-Nov-03 0 4.8
29-Mar-04 0 4.48
22-Jun-04 0 3.68
17-Sep-04 0 3.88
17-Nov-04 0 4.1
16-Mar-05 0 3.5
25-May-05 <l NA NA NA 3.7 NA
31-Aug-05 <l <1 6.4 <1 3.5 NA
1-Dec-05 <l <l 2.3 <1 3.3 NA
9-Mar-06 <l <l 2.2 <1 3.3 26
14-Jun-06 <1 <1 <1 <l 3.2 26
20-Jul-06 <1 <l 1.6 <l 2.9 26
8-Nov-06 <l <l <1 <l 1.5 23
28-Feb-07 <1 <l <l <1 3.1 22
27-Jun-07 <1 <1 <1 <1 3.3 23
15-Aug-07 <1 <1 <1 <1 3.1 24
10-0ct-07 <l <1 <1 <l 2.8 27
26-Mar-08 <1 <1 <l <l 2.8 21
25-Jun-08 <l <l <l <1 2.85 19
10-Sep-08 <1 <l <1 <l 2.66 19
15-0ct-08 <l <l <1 <1 2.63 22
4-Mar-09 <l <l <1 <1 2.5 21
24-Jun-09 <1 <1 <1 <1 2.9 20
15-Sep-09 <1 <l <1 <l 2.8 21
16-Dec-09 <l <1 <1 <l 2.5 22
23-Feb-10 <l <1 <1 <1 2.8 23
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-3 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
' (ue/1) (ue/1)
8-Jun-10 <l <] <l <l 3 24
IO-Aug-IO <l <l <l <l 3.1 22
5-0ct-10 <l <l <1 <1 3.3 26
15-Feb-11 ND ND ND ND 3.5 23
25-May-l I ND ND ND ND 3.7 23
16-Aug-11 ND ND ND ND 4 23
15-Nov-1 l ND ND ND ND 4.4 23
17-Jan-12 ND ND ND ND 4.3 21
31-May-12 ND ND ND ND 4.4 24
29-Aug-12 ND ND ND ND 4.9 25
3-0ct-12 ND ND ND ND 4.8 25
7-Feb-13 ND ND ND ND 5.05 23.7
29-May-13 ND ND ND ND 5.83 23.8
29-Aug-13 ND ND ND ND 6.26 24.0
6-Nov-13 ND ND ND ND 5.89 24.1
22-Jan-14 ND ND ND ND 6.66 24.9
19-May-14 ND ND ND ND 6.01 24.4
13-Aug-14 ND ND ND ND 5.3 26
23-0ct-14 ND ND ND ND 6.07 26.7
l 1-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-l 6 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
ll-Sep-19 ND ND ND ND 5.12 26.0
12-Dec-19 ND ND ND ND 5.91 28.0
17-Mar-20 ND ND ND ND 6.15 27.7
10-Jun-20 ND ND ND ND 6.53 26.2
Chloroform t!arbnn C.ltlorornethane Methylene Nitrate Chloride II 1'W4-3 Tetrachloride Chlodde 11 I ~ug/1) (uJ?/1) (ug/1) (u2/'[) (mg/I) ~mg/I)
17-Sep-20 ND ND ND ND 6.36 25.9
4-Nov-20 ND ND ND ND 6.02 24.9
17-Mar-21 ND ND ND ND 6.19 28.4
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
Dec-20
0 0
...... u, 0 0 0 0 0 0 0
(ug/L)
...... I\) I\) u, 0 u,
0 0 0 0 0 0 0 0 0
w 0 0 0 0
3~ -· ~ r1' I
U'I w -· :s :::r n DJ tD U'I
S: er DJ tD ... tD n :s
:::r -N tD co ~ ... ,...
N :::r 0 DJ 0 :s w ,...
:::r
tD
a. tD ,...
tD n ,... -· 0 :::,
w .I). u, 0 0 0 0 0 0 0
-4 ! w
0 :::r
0
0 0 ""I 3
~
2" CD Cl)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-4 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2')) (u2'))
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 <1 <l 10.1 49
28-Feb-07 2200 1.5 <1 <l 9 49
27-Jun-07 2400 1.7 <1 <1 9.4 47
15-Aug-07 2700 1.5 <1 <1 9.5 45
10-0ct-07 2500 1.5 <l <1 9.5 47
26-Mar-08 2800 1.6 <1 <l 9.2 43
25-Jun-08 2500 1.5 <1 <l 10.8 42
10-Sep-08 2200 1.4 <1 <1 8.83 39
15-0ct-08 2500 2 <2 <2 10.1 44
4-Mar-09 2200 1.2 <l <1 10.2 37
24-Jun-09 1800 1.2 <1 <1 8.2 34
15-Sep-09 2000 1.1 <1 <1 8.4 39
29-Dec-09 950 1.1 <1 <1 7.6 41
Chloroform Carbon Chloromethane Methylene , Nitrate Chloride TW4-4 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u,z/1) (uwl)
17-Feb-10 1700 1 <l <l 6.6 48
10-Jun-10 2000 1.2 <l <l 7.6 35
16-Aug-10 2100 1.3 <l <l 7.3 36
l l-Oct-10 1700 1.3 <l <l 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-11 1500 I 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
ll-Aug-14 1320 ND 7 ND 5.30 40.0
21-0ct-14 1130 ND ND ND 7.02 40.0
9-Mar-15 1350 1 ND ND 7.70 37.6
8-Jun-15 1280 ND ND ND 6.33 41.3
31-Aug-15 1220 ND ND ND 6.45 45.8
19-0ct-15 1190 ND ND ND 6.27 38.5
9-Mar-16 1190 ND ND ND 6.71 39.7
23-May-16 1780 1 ND ND 6.56 41.9
26-Jul-16 1380 ND ND ND 7.22 40.2
13-0ct-16 1430 ND ND ND 6.77 42.3
8-Mar-17 1290 ND ND ND 6.87 41.7
13-Jun-17 1290 ND ND ND 7.06 40.7
26-Jul-17 1290 ND ND ND 6.47 40.5
l l-Oct-17 1290 ND ND ND 6.90 40.7
12-Mar-18 1160 ND ND ND 6.12 42.2
8-Jun-18 1050 ND ND ND 6.34 39.0
22-Aug-18 1030 ND ND ND 6.34 39.0
28-Nov-18 1140 ND ND ND 6.02 41.4
8-Mar-19 1050 ND ND ND 7.26 38.3
5-Jun-19 1070 ND ND ND 10.40 38.5
4-Sep-19 989 ND ND ND 6.32 39.8
Chloroform Carbon Chloromethane M th~lene Nitrate CJ1foride TW4-..4 (ng/1) Tetrachloride (ug/1~ Chloride ('mg/I) (mg/I) Cue/I) (ue/1)
10-Dec-19 1140 ND ND ND 6.52 40.4
19-Feb-20 1100 ND ND ND 4.58 43.4 1,
27-May-20 1140 ND ND ND 7.26 46.1
4-Sep-20 1110 ND ND ND 7.04 40.0
28-0ct-20 979 ND ND ND 6.77 38.6
23-Feb-21 1130 ND ND ND 6.75 39.8
U)
Cl)
:::::s ca >
E ...
0 -0 ...
.2 .t:. 0
oi::t' I oi::t' 3: I-
0 0 LO v
0 0 0 V
0 0 LO C')
0 0 0 C')
0 0 LO C\J
0 0 0 C\J
(1J6n)
0 0 LO .....
0 0 0 .....
0 0 LO
oz-unr-B~
L~-das-zz
v~-oaa-a
Z~-Jd\M
60-1nr-9
90-PO-O~
vo-uer-v~
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-5 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ullln (ul!II)
20-Dec-99 29.5
15-Mar-OO 49.0
2-Sep-00 124
29-Nov-00 255
28-Mar-Ol 236
20-Jun-Ol 240
20-Sep-OI 240
7-Nov-01 260
26-Mar-02 260
22-May-02 300
12-Sep-02 330
24-Nov-02 260
28-Mar-03 240
23-Jun-03 290
12-Sep-03 200
8-Nov-03 240
29-Mar-04 210
22-Jun-04 200
17-Sep-04 150
17-Nov-04 180
16-Mar-05 120
25-May-05 113 NA NA NA 3.7 NA
31-Aug-05 82.0 <2.5 5.8 <2.5 6 NA
1-Dec-05 63.0 <2.5 2.5 <2.5 6 NA
9-Mar-06 66.0 <2.5 3.1 <2.5 6 52
14-Jun-06 51.0 <1 <2.5 <2.5 5.9 51
20-Jul-06 53.7 <1 <1 <1 6.7 54
8-Nov-06 47.1 <1 <1 <1 2.9 55
28-Feb-07 33.0 <l <l <1 7.8 57
27-Jun-07 26 .0 <1 <1 <1 7 45
15-Aug-07 9.2 <1 <1 <1 7.7 38
10-0ct-07 9.4 <1 <1 <l 8.2 39
26-Mar-08 11.0 <l <1 <l 7.4 36
25-Jun-08 9.3 <1 <1 <1 8.7 37
IO-Sep-08 11.0 <1 <1 <1 7.91 34
15-0ct-08 10.0 <1 <l <1 9.3 37
4-Mar-09 12.0 <1 <1 <1 7.9 34
-
24-Jun-09 13.0 <1 <1 <1 7.5 37
-
15-Sep-09 12.0 <1 <1 <1 8.3 48
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-5 (og/1) Tetrachloride (og/1) Chloride (mg/I) (mg/I) (02'1) (02'1) '·
22-Dec-09 8.5 <l <l <1 7.5 41
25-Feb-10 13 .0 <1 <l <1 6.8 43
9-Jun-10 12.0 <l <1 <l 7.1 28
l 1-Aug-10 12.0 <1 <1 <1 7 38
13-0ct-10 11.0 <I <l <l 7.2 41
22-Feb-l 1 10.0 ND ND ND 7 34
26-May-l l 9.0 ND ND ND 7.2 35
17-Aug-l l 10.0 ND ND ND 7.5 37
7-Dec-11 7.9 ND ND ND 6 30
18-Jan-12 7.6 ND ND ND 5.8 22
6-Jun-12 8.4 ND ND ND 8 39
ll-Sep-12 12.0 ND ND ND 8.1 37
3-0ct-12 8.0 ND ND ND 7.7 38
13-Feb-13 10.8 ND ND ND 8.24 34.3
13-Jun-13 11.2 ND ND ND 10.7 36.5
5-Sep-13 11.6 ND ND ND 7.79 39. l
13-Nov-13 14.4 ND ND ND 7.75 41.1
30-Jan-14 12.5 ND ND ND 9.16 40.5
22-May-14 13.4 ND ND ND 7.78 51.4
14-Aug-14 12.0 ND ND ND 7.2 44
28-0ct-14 14.6 ND ND ND 8.31 45.l
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
l 2-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
Chloroform Carbe.n Chlormmethane Methy,leue Njtrate Chlo.rid TW4-5 (ugA) Tet.rachtoride (Ug/1) Cbteride (mgtl) (mg/I) .,
I (11ml} (:11fr1t)
ll-Sep-19 14.6 ND ND ND 7.02 46.l
14-Dec-19 15.7 ND ND ND 6.97 53.1
17-Mar-20 14.8 ND ND ND 7.1 48.3
11-Jun-20 15.4 ND ND ND 7.83 49.5
18-Sep-20 14.8 ND ND ND 6.37 47.0
4-Nov-20 15.6 ND ND ND 6.19 50.2
18-Mar-21 12.9 ND ND ND 7.43 46.0
,n
G.I :::,
ca >
E ... 0 -0 ...
.2 .s:::. 0
LI)
I o::t' ~
0 II)
C')
0 0 C')
0 II)
C\I
0 0 C\I
0 II) .....
(1J6n)
0 0 ..... 0 II)
oi-unr-B~
L~-das-cc
G ~ -Jd\f-~O
60-1nr-90
90-PO-O~
~Q-Jd\f-6 ~
0
II Cat<ho M'ethyfene CbJnrid.e1 II Ohlo-rororrn Chlo:tro~.tihan:e Nitrate TW4•6 'fdlraebtori e CM-ride {ug/.1) (ill~~ ~ gA} €11~1} (mg/I) (,mg/J)
J
6-Jun-00 0
2-Sep-00 0
28-Nov-00 0 ND
26-Mar-Ol 0 0.13
20-Jun-Ol 0 ND
20-Sep-01 4 ND
7-Nov-01 1 ND
26-Mar-02 0 ND
21-May-02 0 ND
12-Sep-02 0 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 0 ND
12-Sep-03 0 ND
8-Nov-03 0 ND
29-Mar-04 0 ND
22-Jun-04 0 ND
17-Sep-04 0 ND
17-Nov-04 0 ND
16-Mar-05 0 0.2
25-May-05 2.5 NA NA NA 0.4 NA
31-Aug-05 10.0 <1 2.8 <1 0.8 NA
l-Dec-05 17.0 <l 1.3 <1 0.9 NA
9-Mar-06 31.0 <1 <1 <1 1.2 31
14-Jun-06 19.0 <l <l <l 1 30
20-Jul-06 11.0 <l <l <1 0.6 37
8-Nov-06 42.8 <1 <l <1 1.4 65
28-Feb-07 46.0 <1 <1 <l 1.5 32
27-Jun-07 11.0 <1 <l <1 0.6 38
15-Aug-07 18.0 <l <1 <1 0.7 36
10-0ct-07 18.0 <1 <l <l 0.8 38
26-Mar-08 52.0 <l <l <l 1.1 33
25-Jun-08 24.0 <1 <1 <1 0.9 35
10-Sep-08 39.0 <1 <l <l 1.14 35
15-0ct-08 37.0 <l <1 <l 1.01 33
ll-Mar-09 81.0 <1 <l <l 2.2 35
24-Jun-09 120 <l <l <l 2.7 37
15-Sep-09 280 <1 <l <1 5.0 37
22-Dec-09 250 <l <1 <l 6.1 41
25-Feb-10 1000 <1 <l <l 1.6 45
10-Jun-10 590 <l <l <l 2.5 33
12-Aug-10 630 <l <l <l 3.9 31
13-0ct-10 420 <l <l <1 4.3 41
Lj-Feb-1 l 47 ND ND ND 0.7 40
Clilol'oform Ca11beu Obh>romethane MtibJI~ N 'tll'aie Oh ide I• TW4-6 'J~ide Oltlo.,ide (ugtlli 6mta1'> (ugtf} hwlll) (mg/I}, (mgll)
:Lo-May-I I 10 ND ND ND 0.3 42
17-Aug-11 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
l 3-Jun-13 4.9 ND ND ND 0.155 37.9
5-Sep-13 5.9 ND ND ND 0.157 40.6
13-Nov-13 5.5 ND ND ND 1.52 40.2
29-Jan-14 5.7 ND ND ND 0.184 40.6
22-May-14 10.3 ND ND ND 0.312 37
14-Aug-14 202 ND ND ND 4.2 40
24-Sep-14 260 ND ND ND NIA NIA
29-0ct-14 723 ND ND ND 6.92 41.1
18-Mar-15 1180 ND ND ND 5.25 41.2
ll-Jun-15 1040 ND ND ND 5.87 41.6
10-Sep-15 1040 ND ND ND 6.75 47.0
29-0ct-15 843 ND ND ND 5.61 40.2
22-Mar-16 834 ND ND ND 6.79 42.0
8-Jun-16 486 ND ND ND 3.19 44.1
4-Aug-16 433 ND ND ND 3.85 42.2
26-0ct-16 301 ND ND ND 3.74 46.1
16-Mar-17 288 ND ND ND 3.15 42.1
21-Jun-17 239 ND ND ND 2.42 42.6
3-Aug-17 129 ND ND ND 1.71 42.9
11-0ct-17 121 ND ND ND 1.71 37.6
20-Mar-18 159 ND ND ND 1.96 43.1
14-Jun-18 74.9 ND ND ND 1.48 40.2
5-Sep-18 53.2 ND ND ND 1.18 44.0
12-Dec-18 37.0 ND ND ND 0.900 20.0
19-Mar-19 23.2 ND ND ND 0.755 41.0
13-Jun-19 15.8 ND ND ND 0.484 38.1
ll-Sep-19 15.8 ND ND ND 0.412 39.7
14-Dec-19 7.40 ND ND ND 0.244 45.7
17-Mar-20 6.93 ND ND ND 0.222 43.2
l 1-Jun-20 4.86 ND ND ND 0.205 42.4
18-Sep-20 3.63 ND ND ND 0.144 40.5
4-Nov-20 4.61 ND ND ND 0.197 42.9
18-Mar-21 3.78 ND ND ND 0.205 41.6
24-Jul-98
19-Apr-01
14-Jan-04
10-0ct-06
6-Jul-09
1-Apr-12
~7-Dec-14
~2-Sep-17
18-Jun-20
15-Mar-23
0
I\) 0 0
~ 0 0
0) 0 0
(ug/L)
00 0 0
_..
0 0 0
_..
I\)
0 0
_..
~ 0 0
-I ! I a,
0 :::r
0 ~ a 0 ~ 3
~
C CD tn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-7 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1) (ue/1)
29-Nov-99 256
15-Mar-OO 616
2-Sep-00 698
29-Nov-OO 684 1.99
28-Mar-01 747 2.46
20-Jun-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
l-Dec-05 2500 <50 <50 <50 5.3 NA
9-Mar-06 1900 <50 <50 <50 1 48
14-Jun-06 2200 <50 <50 <50 4.5 47
20-Jul-06 2140 <50 <50 <50 4.7 51
8-Nov-06 2160 1.5 <l <l 4.6 49
28-Feb-07 1800 1.1 <1 <1 5 47
27-Jun-07 2600 1.5 <1 <l 5.1 45
14-Aug-07 2300 1.4 <l <1 4.7 44
10-0ct-07 1900 1.2 <1 <l 4.7 45
26-Mar-08 2200 1.3 <1 <1 4.2 43
25-Jun-08 1800 1.3 <1 <1 4.8 43
10-Sep-08 1600 1.4 <1 <) 4.16 35
15-0ct-08 1900 <2 <2 <2 4.01 40
11-Mar-09 1800 1.2 <1 <1 3.7 35
24-Jun-09 1400 <l <l <1 3.8 37
15-Sep-09 1500 1.0 <l <l 4.1 37
I Carbon Methylene
TW4-7 Chloroform Tetrachloride Chloromethane Chloride Nitrate Chloride
(ug/1)
I (02'1) (ug/1) (u2'1) (mg/I) (mg/I)
29-Dec-09 1300 <l <l <l 4.2 37
3-Mar-10 1200 <l <1 <l 3.8 36
IO-Jun-IO 1100 <1 <l <l 3.9 31
18-Aug-10 1500 1.1 <1 <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-11 1200 ND ND ND 4.10 37
29-Nov-11 1000 ND ND ND 3.80 37
19-Jan-l 2 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 44.1
4-Aug-16 1000 ND ND ND 4.21 42.3
27-0ct-16 886 ND ND ND 4.33 45.8
21-Mar-17 986 ND ND ND 3.87 40.5
21-Jun-17 968 ND ND ND 4.15 43 .3
4-Aug-17 1070 ND ND ND 4.20 44.7
l 1-0ct-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
I! Chloroform Ca¥1>cm Chlorom~t.hatJe MetlzyJene Nitrate Chloride TW4i-7 (ug/1) Tetr•eltlotid (ugtl) :b.lodde (mg/I) ~mg/I)
~ (u,w1): {owl)
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
19-Sep-20 971 ND ND ND 3.87 41.5
ll-Nov-20 967 ND ND ND 4.40 42.8
24-Mar-21 875 ND ND ND 4.25 46.2
0 Cl) :::s
ca >
E ...
0 -0 ...
0 ::c 0
" I "l:t' 3: t-
0 0 0 co
0 0 0 lO
0 0 0 '<:I"
0 0 0 ('I)
(1,Sn)
0 0 0 C\I
0 0 0 ,-
0
oi-unr-B~
L~-das-i,
v~-oao-Lc
c~-JdV-~
60-1nr-9
90-PO-O~
vo-uer-v~
~O-JdV-6~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-8 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul!II) (ut!/1)
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-OI 180 ND
20-Sep-01 180 0.35
7-Nov-01 180 ND
26-Mar-02 190 0.62
22-May-02 210 0.77
12-Sep-02 300 ND
24-Nov-02 450 ND
28-Mar-03 320 0.8
23-Jun-03 420 ND
12-Sep-03 66.0 ND
8-Nov-03 21.0 0.1
29-Mar-04 24.0 0.65
22-Jun-04 110 0.52
17-Sep-04 120 ND
17-Nov-04 120 ND
16-Mar-05 10.0 ND
25-May-05 <1 NA NA NA 0.2 NA
31-Aug-05 1.1 <1 1.7 <1 <0.1 NA
30-Nov-05 <l <1 <1 <1 <0.1 NA
9-Mar-06 1.3 <1 2.1 <1 0.3 39
14-Jun-06 1.0 <1 1.8 <l <0.1 37
20-Jul-06 <1 <1 <1 <1 0.1 39
8-Nov-06 <1 <1 <1 <1 <0.1 40
28-Feb-07 2.5 <1 <1 <1 0.7 39
27-Jun-07 2.5 <1 <1 <1 0.2 42
15-Aug-07 1.5 <1 <1 <1 <0.1 42
10-0ct-07 3.5 <1 <1 <1 0.5 43
26-Mar-08 <1 <1 <1 <1 0.1 46
25-Jun-08 <1 <1 <l <1 <0.05 45
10-Sep-08 <l <l <1 <l <0.05 39
15-0ct-08 <1 <1 <1 <l <0.05 44
4-Mar-09 <1 <l <1 <l <0.1 42
24-Jun-09 <1 <1 <1 <1 <0.1 44
15-Sep-09 <1 <1 <1 <1 <1 44
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-8 Tetrachloride Chloride (ug/1) (ug/1) 1, (mg/I) (mg/I) (ue/1) -(ue/1)
17-Dec-09 <1 <1 <1 <1 <0.1 51
24-Feb-10 <l <l <l <l <0.1 57
9-Jun-10 <l <l <l <l <0.1 42
1 l-Aug-10 <1 <l <l <l <0.1 45
5-0ct-10 <l <1 <l <1 <0.1 46
16-Feb-l l ND ND ND ND ND 52
25-May-l 1 ND ND ND ND 0.1 45
16-Aug-11 ND ND ND ND 0.1 46
7-Dec-11 ND ND ND ND 0.2 45
I8-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
1 l-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
ll-Oct-17 214 ND ND ND 1.97 52.2
21-Mar-18 220 ND ND ND 1.36 60.8
14-Jun-18 155 ND ND ND 1.31 53.8
5-Sep-18 137 ND ND ND 1.40 63.2
13-Dec-18 93.8 ND ND ND 0.123 65.8
19-Mar-19 103 ND ND ND 1.23 54.3
Chloroform Carbon Cbloromethane Methylene NUrate ChloJJide TW\1.8 (ug/1) Tetrachloride (ug/1) Chloride (nig(I) fmg/1) (ue/1') (ue/1)
19-Jun-19 96.0 ND ND ND 1.10 56.5
12-Sep-19 75.4 ND ND ND 0.999 52.0
18-Dec-19 84.4 ND ND ND 1.21 60.1
18-Mar-20 55.0 ND ND ND 1.04 53.8
12-Jun-20 53.8 ND ND ND 1.06 56.9
18-Sep-20 39.5 ND ND ND 0.894 52.6
11-Nov-20 51.3 ND ND ND 1.27 54.7
18-Mar-21 26.9 ND ND ND 1.00 52.8
0
I\) 0 0
.i,.. 0 0
(ug/L)
a, 0 0
co 0 0
......
0 0 0
......
I\) 0 0
24-Jul-98 +----+-----+-----+-----+-----+-----1
19-Apr-01
14-Jan-04
10-0ct-06 • I I I I I I I
6-Jul-09 t I I I I I I I
1-Apr-12 l I I I I I I I
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 -L-----'------'------'----------......_ ___ ___,
-I
== .1:1,,
I a,
0
::T 0 ...
0 -0 ... 3
< e!. C: (D en
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-9 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (owl) (URII) -
20-Dec-99 4.2
15-Mar-OO 1.9
2-Sep-00 14.2
29-Nov-00 39.4 ND
27-Mar-Ol 43.6 ND
20-Jun-Ol 59.0 0.15
20-Sep-01 19.0 0.4
7-Nov-01 49.0 0.1
26-Mar-02 41.0 0.5
22-May-02 38.0 0.65
12-Sep-02 49.0 0.2
24-Nov-02 51.0 0.6
28-Mar-03 34.0 0.6
23-Jun-03 33.0 0.8
12-Sep-03 32.0 1.1
8-Nov-03 46.0 1.1
29-Mar-04 48.0 0.82
22-Jun-04 48.0 0.75
17-Sep-04 39.0 0.81
17-Nov-04 26.0 1.2
16-Mar-05 3.8 1.3
25-May-05 1.2 NA NA NA 1.3 NA
31-Aug-05 <l <l 2.9 <l 1.3 NA
1-Dec-05 <l <1 <1 <l 1.3 NA
9-Mar-06 <1 <1 2.6 <1 1.5 38
14-Jun-06 <l <1 2.7 <1 1.5 39
20-Jul-06 <l <l <1 <1 0.9 41
8-Nov-06 <l <l <1 <1 0.7 44
28-Feb-07 <1 <] <1 <l 0.6 44
27-Jun-07 21 <1 <l <l 1.3 42
15-Aug-07 9.5 <1 <l <1 1.8 38
10-0ct-07 8.7 <l <l <1 2 40
26-Mar-08 1.3 <l <l <l 2.1 35
25-Jun-08 1.0 <l <1 <l 2.3 35
10-Sep-08 <l <l <1 <l 2.79 28
15-0ct-08 <l <1 <1 <l 1.99 58
4-Mar-09 <] <1 <l <1 2.5 30
24-Jun-09 <1 <l <l <1 2.3 30
15-Sep-09 <1 <l <1 <l 2.5 30
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-9 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
II (ul!I)) (ul!II)
17-Dec-09 <l <1 <1 <l 1.7 37
23-Feb-10 <1 <l <1 <1 1.7 47
9-Jun-10 <1 <l <1 <l 1.5 33
1 l-Aug-10 <l <l <1 <1 1.2 40
6-0ct-10 <l <l <1 <1 1.8 34
17-Feb-ll ND ND ND ND 1.3 41
25-May-1 l ND ND ND ND 3.4 38
16-Aug-l 1 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
l l-Jun-15 35.1 ND ND ND 1.83 35.3
3-Sep-15 48.2 ND ND ND 1.44 39.5
28-0ct-15 68.4 ND ND ND 2.89 29.2
17-Mar-16 74.3 ND ND ND 2.51 33.6
8-Jun-16 76.2 ND ND ND 2.16 35.1
3-Aug-16 76.8 ND ND ND 2.11 33.6
26-0ct-16 76 ND ND ND 2.24 37.4
16-Mar-17 113 ND ND ND 2.18 34.5
21-Jun-17 113 ND ND ND 1.92 35.9
3-Aug-17 118 ND ND ND 1.90 37.0
11-0ct-l 7 132 ND ND ND 2.18 32.3
21-Mar-18 159 ND ND ND 1.85 38.3
14-Jun-18 134 ND ND ND 1.85 35.7
5-Sep-18 94.2 ND ND ND 1.04 43.4
13-Dec-18 109 ND ND ND 1.23 36.3
19-Mar-19 86.4 ND ND ND 1.09 36.9
19-Jun-19 68.1 ND ND ND 0.785 38.3
II Chloroform CaFbon Chloromethane Methylene Nitrate Chloride TW4-9 (ugtl) Tetrachloride (ug/l) Chloride (mg/I) (mg/I) II (·&d) {ttwl)
ll-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
18-Sep-20 45.0 ND ND ND 0.867 36.7
11-Nov-20 47.1 ND ND ND 1.11 37.2
18-Mar-21 39.0 ND ND ND 1.06 40.7
UJ
CL> :,
'i >
E ... 0 -0 ... ..Q
.t:. 0
0,
I ~ 3: t-
0 CX) ,-
0 (0 ,-
0 s:t ,-
0 C\J ,-
0 0 ,-
(1J6n)
0 CX) 0 (0 0 C\J 0
oi-unr-8~
Li-das-ic
l ~ -Jd'v'-~
60-1nr-9
90-ioo-o~
vo-uer-vi
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-10 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I~ J (ue/1) (ue/1)
21-Jan-02 14
26-Mar-02 16 0.14
21-May-02 I7 0.11
12-Sep-02 6 ND
24-Nov-02 14 ND
28-Mar-03 29 0.2
23-Jun-03 110 0.4
12-Sep-03 74 0.4
8-Nov-03 75 0.3
29-Mar-04 22 0.1
22-Jun-04 32 ND
17-Sep-04 63 0.46
17-Nov-04 120 0.4
16-Mar-05 140 1.6
25-May-05 62.4 NA NA NA 0.8 NA
31-Aug-05 110 <2.5 6.2 <2.5 1.1 NA
l-Dec-05 300 <2.5 <2.5 <2.5 3.3 NA
9-Mar-06 190 <5 <50 <50 2.4 50
14-Jun-06 300 <5 <50 <50 3.5 54
20-Jul-06 504 <5 <50 <50 6.8 61
8-Nov-06 452 <1 1.6 1 5.7 58
28-Feb-07 500 <1 <l 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 <l <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
ll-Mar-09 1100 <1 <l 1 11.6 64
24-Jun-09 1200 <1 <1 I 9.8 62
15-Sep-09 910 <1 <l 1 8.1 51
22-Dec-09 300 <1 <l <1 3.5 51
3-Mar-IO 460 <1 <1 <1 5 49
10-Jun-IO 220 <1 <1 <1 1.6 42
12-Aug-10 100 <1 <l <l 0.8 38
13-0ct-10 1100 <l <1 <1 11 52
23-Feb-11 620 ND ND ND 9 62
1-Jun-11 280 ND ND ND 3.3 42
II Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-10 (ug/1) Tetrachloride (ug/1) Chloride 1 (mg/I) (mg/I) (uwl) (uwl)
17-Aug-1 I 180 ND ND ND 1.9 41
16-Nov-l I 110 ND ND ND I.I 45
19-Jan-12 76 ND ND ND 0.9 40
13-Jun-l 2 79 ND ND ND 0.8 46
12-Sep-12 130 ND ND ND 1.0 44
3-0ct-12 140 ND ND ND 1.6 45
13-Feb-13 154 ND ND ND 1.2 49.1
l 3-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
11-Jun-15 1240 ND ND ND 11.4 75
10-Sep-15 1280 ND ND ND 14.0 89.5
29-0ct-l 5 1350 ND ND ND 13.5 79.9
22-Mar-16 1430 ND ND ND 17.3 84.1
8-Jun-16 1510 ND ND ND 14.9 89.5
4-Aug-16 1500 ND ND ND 14.9 85.3
27-0ct-16 1290 ND ND ND 14.8 84.4
21-Mar-l 7 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-l 8 914 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
19-Sep-20 854 ND ND ND 7.34 53.9
l 1-Nov-20 903 ND ND ND 8.69 58.6
24-Mar-21 718 ND ND ND 7.20 58.1
(ug/L)
_. _. _. _.
I\) ~ C) (X) 0 I\) ~ C) 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 1 I ' I « I I I I I I -t =e .1::1,,
I .....
0
0 :::r
6-Jul-09 -l I I \ I I I "=-t I I 0 • ""I 0 -0 ""I
3
< e!.
1-Apr-12 i I I I I \ I I I I I C CD
tn
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 _.__ __ _,_ __ --L ___ L..__ __ ..1-. __ .....1-__ --1 ___ 1._ _ _J
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-11 Tetrachloride (ug/1) (owl) (ug/1) Chloride (ug/1) (mg/I) (mg/I) I
21-Jan-02 4700
26-Mar-02 4900 9.6
22-May-02 5200 9.07
12-Sep-02 6200 8.84
24-Nov-02 5800 9.7
28-Mar-03 5100 9.7
23-Jun-03 5700 9.4
12-Sep-03 4600 9.9
8-Nov-03 5200 9.3
29-Mar-04 5300 9.07
22-Jun-04 5700 8.74
17-Sep-04 4800 8.75
17-Nov-04 5800 9.7
16-Mar-05 4400 8.7
25-May-05 3590 NA NA NA 10.3 NA
31-Aug-05 4400 <10 <10 <10 9.4 NA
1-Dec-05 4400 <100 <100 <100 9.4 NA
9-Mar-06 4400 <50 <50 <50 9.2 56
14-Jun-06 4300 <50 <50 <50 IO 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 <l 1.1 10.2 53
10-0ct-07 4400 1.6 <l 1.2 9.8 53
26-Mar-08 340 <1 <l <] 7.7 63
25-Jun-08 640 <1 <l <l 7.28 46
10-Sep-08 900 <1 <l <l 7.93 42
15-0ct-08 1000 <2 <2 <2 9.46 47
l 1-Mar-09 1100 <] <l <1 7.3 49
24-Jun-09 980 <l <1 <1 6.8 44
15-Sep-09 1000 <l <l <1 7 49
29-Dec-09 860 <l <1 <l 6.6 46
3-Mar-10 820 <l <1 <l 6.8 42
10-Jun-10 820 <l <l <l 6.9 40
12-Aug-10 800 <l <1 <1 6.7 43
13-0ct-10 720 <l <1 <1 6.4 49
23-Feb-l 1 1000 ND ND ND 6.5 46
1-Jun-11 930 ND ND ND 7.3 49
Chloroform Carbon Chloromethane Methylene Nitrate Chloride I TW4-11 Tetrachloride (ug/1) (u2'1) (ug/1) Chloride (ug/1) (mg/I) (mg/I)
17-Aug-ll 820 ND ND ND 7.1 48
16-Nov-l 1 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 7.8I 56.4
25-Jul-J 6 3200 ND ND ND 8.83 55.3
12-0ct-16 3180 1.58 ND ND 8.92 57.2
8-Mar-17 3310 1.71 ND ND 8.12 49.8
13-Jun-l 7 3370 1.83 ND ND 7.92 51.4
26-Jul-17 3290 1.81 ND ND 7.78 51.0
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
4-Sep-20 3070 1.37 ND ND 7.59 46.3
28-0ct-20 2670 ND 3.86 ND 7.19 43.3
23-Feb-21 2750 ND 3.86 ND 7.21 49.5
(ug/L)
...... I\) w ~ CJ1 O> --.I 0 0 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 1 I I I ,-I I I I -t
== ~ I ...... ......
0 ;r
6-Jul-09 -l 1: I I I I I I 0 ... 0 -0 ... 3
< !.
1-Apr-12 i 1. I I I I I I I I C CD "'
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 ___.__ __ ____.._ ___ _.___ __ ___,, ___ _._ ___ .__ __ __._ __ ___,
Chloroform Carbon Chloromethane Methylene Nitrate Chloride
I TW4-12 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
' (ue/1) (ue/1)
12-Sep-02 2 2.54
24-Nov-02 0 2.2
28-Mar-03 0 1.9
23-Jun-03 0 1.8
12-Sep-03 0 1.8
9-Nov-03 0 1.6
29-Mar-04 0 1.58
22-Jun-04 0 1.4
17-Sep-04 0 1.24
17-Nov-04 0 1.5
16-Mar-05 0 1.4
25-May-05 <l NA NA NA 1.6 NA
31-Aug-05 <l <l 5.8 <1 1.5 NA
l-Dec-05 <1 <l 1.9 <2 1.4 NA
9-Mar-06 <1 <l 2.6 <1 1.3 19
14-Jun-06 <1 <1 1.4 <1 1.4 16
20-Jul-06 <1 <1 <1 <l 1.4 16
8-Nov-06 <l <1 <1 <1 1.4 16
28-Feb-07 <1 <1 <1 <1 1.5 16
27-Jun-07 <1 <1 <1 <1 1,5 18
15-Aug-07 <1 <l <1 <1 1.4 29
10-0ct-07 <1 <1 <I <1 1.4 16
26-Mar-08 <1 <1 <l <1 1.6 16
25-Jun-08 <l <1 <l <1 2.69 19
10-Sep-08 <1 <l <1 <1 2.65 18
15-0ct-08 <1 <l <1 <1 2.47 22
4-Mar-09 <1 <1 <1 <1 2.4 23
24-Jun-09 <1 <1 <1 <1 3.8 22
15-Sep-09 <l <l <1 <1 5.1 22
16-Dec-09 <1 <l <1 <l 3.6 23
23-Feb-10 <l <1 <1 <l 4 22
8-Jun-10 <1 <1 <1 <1 11 29
10-Aug-10 <1 <1 <1 <1 9 35
5-0ct-10 <l <l <1 <l 8 31
15-Feb-1 l ND ND ND ND 6.5 31
25-May-ll ND ND ND ND 7 32
16-Aug-1 l ND ND ND ND 6.8 31
15-Nov-11 ND ND ND ND 8 30
17-Jan-12 ND ND ND ND 7.7 28
Chloroform Carbon Chloromethane Methylene Nitrate
1
Chloride l,J TW4-12 Tetrachloride Chloride (ug/1) (uwl) (ug/1) (m?/1) (mg/I) (mg/I)
3 l-May-12 ND ND ND ND 10 34
29-Aug-12 ND ND ND ND 13 39
3-0ct-12 ND ND ND ND 13 39
7-Feb-13 ND ND ND ND 12.6 36.7
29-May-13 ND ND ND ND 14.2 38.6
29-Aug-13 ND ND ND ND 17.4 41.7
6-Nov-13 ND ND ND ND 16.4 41.4
22-Jan-14 ND ND ND ND 18.4 41.6
21-May-14 ND ND ND ND 17 40.2
27-Aug-14 ND ND ND ND 13 47
23-0ct-14 ND ND ND ND 16.1 50.2
ll-Mar-15 ND ND ND ND 19.2 50.6
10-Jun-15 ND ND ND ND 18.8 56
2-Sep-15 ND ND ND ND 16.4 60.2
21-0ct-15 ND ND ND ND 18 51.0
15-Mar-16 ND ND ND ND 34.8 56.2
25-May-16 ND ND ND ND 30.7 66.4
27-Jul-16 ND ND ND ND 37.7 67.5
19-0ct-16 ND ND ND ND 25.8 72.6
14-Mar-17 ND ND ND ND 25.9 62.6
14-Jun-17 1.25 ND ND ND 29.9 67.2
2-Aug-17 1.20 ND ND ND 25.1 65.3
l O-Oct-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
l J-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
17-Sep-20 ND ND ND ND 2.34 50.3
4-Nov-20 ND ND ND ND 5.91 48.0
17-Mar-21 ND ND ND ND 3.10 52.0
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
' ' :
' ' ' ,i
•• 0 i• ••
•
I
••
•• • • : •• 0
•• ••
•• :
0
•
0 • • 0 •• • • 0
0
0
H
0
9
01
(ug/L)
...... ......
0 01
--
I\)
0
i I .....
"' 0 ::r
0 ... a 0 ...
3
< m 2" CD rn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-13 Tetrachloride Chloride 11 (ug/1) (ug/1) (mg/I) (mg/I)
1, (ue/1) (ue/1)
12-Sep-02 ND ND
24-Nov-02 ND ND
28-Mar-03 ND 0.20
23-Jun-03 ND 0.20
12-Sep-03 ND ND
9-Nov-03 ND 0.90
29-Mar-04 ND 0.12
22-Jun-04 ND 0.17
17-Sep-04 ND 4.43
17-Nov-04 ND 4.70
16-Mar-05 ND 4.20
25-May-05 <I NA NA NA 4.30 NA
31-Aug-05 <l <l 3.1 <l 4.60 NA
l-Dec-05 <I <l <I <] 4.30 NA
9-Mar-06 <l <l 1.7 <I 4.20 67.0
14-Jun-06 <l <1 1.4 <] 4.90 66.0
20-Jul-06 <1 <1 <I <I 4.30 65.0
8-Nov-06 <1 <l <1 <1 0.80 33.0
28-Feb-07 <1 <l <I <1 4.00 59.0
27-Jun-07 <1 <l <1 <l 4.60 59.0
15-Aug-07 <1 <l <1 <l 4.40 58.0
IO-Oct-07 <1 <1 <I <1 4.10 58.0
26-Mar-08 <1 <l <1 <I 3.80 54.0
25-Jun-08 <1 <l <1 <1 4.24 58.0
10-Sep-08 <1 <l <l <l 4.26 50.0
15-0ct-08 <1 <1 <1 <I 4.63 58.0
4-Mar-09 <I <l <l <l 3.70 58.0
24-Jun-09 <l <1 <1 <l 1.20 57.0
15-Sep-09 <1 <l <l <l 4.70 63.0
16-Dec-09 <I <1 <1 <1 4.10 60.0
24-Feb-10 <1 <] <1 <1 4.30 53.0
8-Jun-10 <l <l <l <I 5.20 52.0
10-Aug-lO <l <l <l <I 5.60 55.0
5-0ct-10 <l <l <1 <l 5.80 55.0
15-Feb-I l ND ND ND ND 5.50 60.0
25-May-l l ND ND ND ND 5.40 56.0
16-Aug-11 ND ND ND ND 5.20 60.0
15-Nov-11 ND ND ND ND 5.90 54.0
17-Jan-12 ND ND ND ND 5.50 55.0
31-May-12 ND ND ND ND 6.00 59.0
29-Aug-12 ND ND ND ND 6.20 60.0
3-0ct-12 ND ND ND ND 5.90 60.0
I Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-13 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) I (owl) (mdl)
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.l
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-l 5 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
l 3-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
l l-Jun-20 ND ND ND ND 5.96 62.7
17-Sep-20 ND ND ND ND 5.25 60.2
4-Nov-20 ND ND ND ND 4.92 60.6
17-Mar-21 ND ND ND ND 5.57 67.3
Sep-02
Dec-02
Mar-03 Jun-03 Sep-03
Dec-03 Mar-04 Jun-04
Sep-04 Dec-04 Mar-05 Jun-05
Sep-05
Dec-05 Mar-06
Jun-06
Sep-06 Dec-06 Mar-07
Jun-07
Sep-07 Dec-07 Mar-08
Jun-08
Sep-08 Dec-08 Mar-09 Jun-09
Sep-09 Dec-09 Mar-10
Jun-10
Sep-10 Dec-10 Mar-11 Jun-11
Sep-11 Dec-11 Mar-12
Jun-12
Sep-12 Dec-12 Mar-13 Jun-13
Sep-13 Dec-13 Mar-14 Jun-14
Sep-14 Dec-14 Mar-15 Jun-15
Sep-15
Dec-15 Mar-16 Jun-16
Sep-16 Dec-16 Mar-17 Jun-17
Sep-17 Dec-17 Mar-18 Jun-18
Sep-18 Dec-18 Mar-19 Jun-19
Sep-19
Dec-19 Mar-20 Jun-20 Sep-20
Dec-20
Mar-21
0
J
0
~
' . ' .
~
0
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0
0
0
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0
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-14 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
II (ul!/1} (ul!ll)
8-Nov-06 <1 <1 <1 <1 2.40 37.0
28-Feb-07 <1 <1 <] <1 2.30 38.0
27-Jun-07 <l <1 <l <1 1.40 38.0
15-Aug-07 <l <1 <l <l 1.10 36.0
10-0ct-07 <1 <1 <1 <l 0.80 36.0
26-Mar-08 <1 <1 <1 <] 0.04 57.0
25-Jun-08 <1 <1 <1 <1 1.56 35.0
10-Sep-08 <l <l <1 <1 1.34 34.0
15-0ct-08 <l <l <1 <1 0.76 40.0
4-Mar-09 <1 <l <1 <1 1.60 35.0
24-Jun-09 <1 <l <l <l 1.40 36.0
15-Sep-09 <l <l <1 <] 1.50 38.0
16-Dec-09 <l <1 <1 <1 1.40 34.0
3-Mar-10 <1 <1 <1 <1 2.50 33.0
8-Jun-10 <1 <l <l <1 2.90 49.0
10-Aug-10 <l <l <l <l 2.80 35.0
6-0ct-10 <] <l <l <I 2.90 29.0
15-Feb-ll ND ND ND ND 1.80 25.0
16-Aug-1 l ND ND ND ND 2.60 33 .0
15-Nov-l l ND ND ND ND 1.70 15.0
17-Jan-12 ND ND ND ND 1.90 20.0
31-May-12 ND ND ND ND 3.30 35.0
29-Aug-12 ND ND ND ND 3.90 37.0
3-0ct-12 ND ND ND ND 4.20 37.0
7-Feb-13 ND ND ND ND 4.63 35.2
30-May-13 ND ND ND ND 4.37 38.6
29-Aug-13 ND ND ND ND 4.51 37.6
6-Nov-13 ND ND ND ND 4.81 36.5
22-Jan-14 ND ND ND ND 5.92 35.5
21-May-14 ND ND ND ND 4.87 32.5
13-Aug-14 ND ND ND ND 4.10 38.0
23-0ct-14 1.68 ND ND ND 5.22 38.9
12-Mar-15 1.71 ND ND ND 5.22 40.1
IO-Jun-15 1.82 ND ND ND 3.55 41.8
3-Sep-15 ND ND ND ND 2.77 42.4
21-0ct-15 1.46 ND ND ND 2.45 40.6
16-Mar-16 4.49 ND ND 2.18 2.94 42.4
26-May-16 6.15 ND ND 3.18 2.45 43.6
28-Jul-16 5.00 ND ND 1.80 2.88 42.4
Carbon Meffiylene ~
Chlorofol.!m Chloromethane Nitrate Chloride IIW4-t4 (ug/1) Tetrachloride (ug/1) Chlollide (mg/I) (mg/I)
I CuWI) (ustJI)
20-0ct-16 7.02 ND ND 1.59 2.86 45.6
15-Mar-17 6.45 ND ND ND 4.36 45.4
15-Jun-17 6.85 ND ND ND 5.12 46.9
2-Aug-17 6.14 ND ND ND 4.84 46.4
10-0ct-17 6.13 ND ND ND 4.73 42.5
15-Mar-18 5.80 ND ND ND 5.67 51.5
13-Jun-18 5.12 ND ND ND 6.36 46.9
30-Aug-18 4.76 ND ND ND 5.34 54.1
12-Dec-18 4.41 ND ND ND 5.85 48.7
16-Mar-19 4.08 ND ND ND 6.16 48.7
13-Jun-19 4.18 ND ND ND 5.86 48.3
ll-Sep-19 6.08 ND ND ND 4.77 45.4
14-Dec-19 3.83 ND ND ND 4.76 49.4
17-Mar-20 2.98 ND ND ND 6.17 48.4
l 1-Jun-20 2.87 ND ND ND 6.57 47.6
18-Sep-20 2.41 ND ND ND 5.57 45.1
4-Nov-20 2.69 ND ND ND 5.81 49.7
18-Mar-21 1.77 ND ND ND 5.56 48.2
0 0
a:i
0 0 r-..:
0 0 <.ci
0 0
ui
0 0 ..j,
0 0
C')
(1J6n)
0 ~ C\J
0 0 0 0
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L~-da -zz
17~-::>a -a
.-1
0 0
c\j
I
Chlo~ Oa!l'ii Ch ~ettlit · e ~ene t:mte Chlomh! MW-2' e.rm Teuaeltl9ride ChJo;Tide (ugA~ ~0211~, ~~ I ~) (mgil~ (n)@A(~
12-Sep-02 3 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 7800 14.5
15-Aug-03 7400 16.8
12-Sep-03 2500 2.7
25-Sep-03 2600 2.5
29-0ct-03 3100 3.1
8-Nov-03 3000 2.8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 1400 0.53
17-Nov-04 300 0.2
16-Mar-05 310 0.3
30-Mar-05 230 0.2
25-May-05 442 NA NA NA 0.2 NA
31-Aug-05 960 <5 5.4 <5 0.2 NA
l-Dec-05 1000 <50 <50 <50 0.3 NA
9-Mar-06 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 <1 5.5 0.5 56
27-Jun-07 300 <1 <1 13 0.4 49
15-Aug-07 1400 <1 <l 36 1 57
10-0ct-07 2000 <1 <1 14 0.6 57
26-Mar-08 930 <1 <1 40 0.1 49
25-Jun-08 1300 <1 <1 53 0.56 57
10-Sep-08 630 <1 <1 24 0.24 44
15-0ct-08 1700 <1 <1 100 0.65 64
4-Mar-09 950 <1 <l 51 0.4 49
24-Jun-09 410 <1 <1 12 0.2 48
15-Sep-09 850 <1 <1 30 0.1 46
14-Dec-09 1100 <l <1 40 2.3 60
17-Feb-10 780 <1 <1 19 0.2 57
9-Jun-10 1900 <1 <1 28 1.1 58
16-Aug-10 2200 <l <1 21 0.6 49
11-0ct-10 970 <1 <1 6.5 0.7 65
23-Feb-11 450 ND ND 3.6 0.5 57
Chloroform Catfi1»l1 Cble-rcmre1llt etltJfene Nitrate CldoJ,jde MW~26 :fe rachlurlde e adde ·(ugtJ) CmrJ;t) ('11~ (udl) ('mg()) (mgA)
·--
31-May-l 1 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
1 l-Aug-14 2120 ND 8.7 26 0.7 59
21-0ct-14 2090 ND ND 23.2 0.934 60.1
9-Mar-15 1980 -ND ND 27.4 0.732 56.5
8-Jun-15 1980 ND ND 11.2 0.419 62
31-Aug-15 2350 ND 4.05 11.6 0.684 69.6
19-0ct-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
ll-Oct-17 2570 ND ND 7.83 1.18 62.2
12-Mar-18 1210 ND ND 2.14 1.57 60.3
8-Jun-18 1870 ND ND 9.19 0.901 58.7
22-Aug-18 1680 ND ND ND 2.80 91.4
28-Nov-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
4-Sep-20 1130 ND ND 2.57 0.42 70.0
28-0ct-20 866 ND ND ND 3.62 67.4
Chloroform Carbon Chl9rometl1ane Methylene Nitrate Chlorides
MW-26 'f etrachloritle Chloride
II (ug/1) (02'1~ ~ug/1) iuml) (mgll) {mg/I)
23-Feb-21 3060 ND ND 3.46 0.349 59.5
oc:-unr-s~
u,
Cl) :::::, ca > C: kJdV-~ E ...
0 -0 ...
.2 .c
0
co 60-1nr-9 C\I I 3: :E
90-PO-O~
vo-uer-v ~
W-JdV-6 ~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 Lt) 0 Lt) 0 Lt) 0 LO 0 IO "<T "<T (") (") C\J C\J ,.... ,....
(1,Sn)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (usul) I (uwl)
12-Sep-02 140 ND
24-Nov-02 200 ND
28-Mar-03 260 ND
23-Jun-03 370 ND
12-Sep-03 350 ND
8-Nov-03 400 ND
29-Mar-04 430 ND
22-Jun-04 530 ND
17-Sep-04 400 ND
17-Nov-04 350 ND
16-Mar-05 240 ND
25-May-05 212 NA NA NA <0.1 NA
31-Aug-05 85 <l 3.2 43 <0.1 NA
l-Dec-05 14 <2.5 2.6 5.9 1.4 NA
9-Mar-06 39 <1 1.1 21 3 60
14-Jun-06 13 <1 2.4 8.9 1.9 55
20-Jul-06 5.2 <l <1 2.7 2.7 60
8-Nov-06 13.6 <1 <1 9.2 5.6 62
28-Feb-07 8.7 <l <1 6.5 12.3 79
27-Jun-07 2.6 <1 <l 1.8 9.9 75
15-Aug-07 7.1 <l <1 5.1 5.4 66
10-0ct-07 1.4 <l <1 <l 4.4 69
26-Mar-08 11 <l <l 26 ND 52
25-Jun-08 <1 <1 <1 <1 1.46 58
10-Sep-08 10 <l <1 14 10.5 71
l 5-0ct-08 3.9 <l <1 6.6 9.82 89
4-Mar-09 <1 <l <l <l 9.6 78
24-Jun-09 <l <1 <1 <l 8.9 76
15-Sep-09 <1 <1 <1 <1 8.8 79
17-Dec-09 <1 <1 <l <] 5.2 76
24-Feb-10 <l <1 <1 <1 4.2 77
9-Jun-10 2.1 <1 <1 <l 4.7 64
24-Aug-10 4.3 <1 <l <l 4.6 72
6-0ct-10 3 <1 <l <l 3.3 72
22-Feb-11 15 ND ND ND 7 86
26-May-11 16 ND ND ND 5 81
17-Aug-11 9.2 ND ND ND 1.7 63
16-Nov-l l ND ND ND 1.4 0.4 38
18-Jan-12 ND ND ND 1.7 0.1 48
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1)
I (u2'I) (ul!/1)
31-May-12 ND ND ND ND ND 53
30-Aug-12 ND ND ND ND ND 59
3-0ct-12 ND ND ND 3 ND 53
7-Feb-13 ND ND ND 3 ND 58.1
30-May-13 ND ND ND 4.21 ND 49.8
5-Sep-13 ND ND ND ND ND 54.4
7-Nov-13 13.4 ND ND ND I.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.l
12-Mar-l 5 153 ND ND ND 4.30 65.3
l l-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
11-0ct-l 7 97.8 ND ND ND 2.12 54.2
20-Mar-18 170 ND ND ND 4.55 85.l
14-Jun-18 54.5 ND ND ND 2.83 62.5
30-Aug-18 54.5 ND ND ND 2.53 73.0
12-Dec-18 52.0 ND ND ND 2.88 68.8
19-Mar-19 60.6 ND ND ND 3.36 66.3
19-Jun-19 76.2 ND ND ND 2.43 71.5
12-Sep-19 99.8 ND ND ND 3.55 72.9
18-Dec-19 94.3 ND ND ND 3.37 88.6
18-Mar-20 113 ND ND ND 3.91 76.2
12-Jun-20 141 ND ND ND 4.44 79.7
19-Sep-20 220 ND ND ND 4.74 77.4
4-Nov-20 270 ND ND ND 5.73 85.9
24-Mar-21 248 ND ND ND 5.82 92.6
0
......
0 0
I\)
0 0
(ug/L)
(,J
0 0
.j::,,.
0 0
01 0 0
O> 0 0
19-Apr-01 -i-----+-----+-----1-----1-----1------1
14-Jan-04
10-0ct-06
6-Jul-09 t I I I I I I I
1-Apr-12 1 ' I I I I I
,. II I • I ....... , I I 27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 .,__ ___ _._ ____ 1-___ ...J..._ ___ --1. ____ ..l..._ ___ -1
-I
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0 :::r
0 "'I 0 -0 "'I 3
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tn
Chloroform Carbon Chloromethane Methylene Nitrate Chloride MW-32 {ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2/I) (u211)
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
l 7-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 <l 3.2 <1 <0.1 NA
l-Dec-05 <1 <l <1 <1 <0.1 NA
9-Mar-06 <1 <l <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 <l <l 1.5 <1 <0.1 31
28-Feb-07 <1 <l <1 <1 <0.1 32
27-Jun-07 <1 <1 <1 <1 <0.1 32
15-Aug-07 <1 <1 <1 <1 <0.1 31
10-0ct-07 <1 <1 <1 <1 <0.1 32
26-Mar-08 <1 <1 <1 <1 <0.1 31
25-Jun-08 <l <l <1 <l <0.05 29
10-Sep-08 <1 <1 <1 <1 <0.05 30
15-0ct-08 <1 <1 <1 <1 <0.05 26
4-Mar-09 <1 <1 <1 <1 <0.1 30
24-Jun-09 <1 <l <1 <1 <0.1 31
15-Sep-09 <1 <1 <1 <1 <0.1 33
16-Dec-09 <1 <1 <1 <1 <0.1 34
17-Feb-10 <1 <1 <1 <1 <0.1 38
14-Jun-10 <1 <1 <1 <1 <0.1 32
16-Aug-10 <1 <1 <l <l <0.1 28
6-0ct-10 <1 <1 <1 <1 <0.1 24
23-Feb-l 1 ND ND ND ND ND 40
25-May-1 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
Chloroform Carbon Chloromethane Methylene Nitrate Chloride MW-32 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (owl) (utz/1)
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
1 O-Oct-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-Se_p-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
l 7-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
3 l-Oct-16 ND ND ND ND ND 36.9
21-Mar-17 ND ND ND ND ND 33.7
21-Jun-l 7 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-l 8 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
18-Sep-20 ND ND ND ND ND 34.7
4-Nov-20 ND ND ND ND ND 31.3
22-Mar-21 ND ND ND ND ND 36.8
V,
CD :::,
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0 0 ...
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(1/6n)
co
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Chloroform Carbon Cbloromethane Methylene Nitrate Chloride
I TW4-18 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
I (u2'I) -(ue/1) I
12-Sep-02 440 1.49
24-Nov-02 240 13.3
28-Mar-03 160 13. I
23-Jun-03 110 19
12-Sep-03 68.0 19.9
9-Nov-03 84.0 20.7
29-Mar-04 90.0 14
22-Jun-04 82.0 12.2
17-Sep-04 38.0 14.5
17-Nov-04 51.0 17.3
16-Mar-05 38.0 14. l
25-May-05 29.8 NA NA NA 12.9 NA
31-Aug-05 39 <1 2.8 <1 13.3 NA
l-Dec-05 14 <1 1.1 <I 7.3 NA
9-Mar-06 12.0 <1 1.1 <1 5.9 5.9
14-Jun-06 12.0 <l 1.6 <l 4.7 35
20-Jul-06 10.8 <l 2.7 <l 6.1 35
8-Nov-06 139 <1 <l <1 8.7 34
28-Feb-07 9.2 <1 <l <l 5.1 30
27-Jun-07 8.0 <l <l <1 4.9 28
15-Aug-07 8.9 <l <1 <1 5 32
10-0ct-07 7.4 <1 <1 <l 4.4 27
26-Mar-08 6.4 <l <l <] 0.7 23
25-Jun-08 5.7 <1 <l <l 4.55 23
10-Sep-08 8.0 <1 <1 <l 4.68 26
15-0ct-08 9.4 <l <l <1 5,15 30
4-Mar-09 11.0 <1 <l <1 5.2 29
24-Jun-09 16.0 <l <1 <1 6.2 30
15-Sep-09 13.0 <l <1 <l 5.9 26
22-Dec-09 8.2 <l <l <l 5.4 30
24-Feb-10 69.0 <l <1 <l 5.1 41
9-Jun-10 29.0 <l <l <1 9 35
12-Aug-10 29.0 <l <1 <l 9 37
13-0ct-10 30.0 <l <1 <1 10 50
22-Feb-l 1 39.0 ND ND ND 10 52
26-May-l l 26.0 ND ND ND 9 36
17-Aug-11 29.0 ND ND ND 4.6 23
7-Dec-11 28.0 ND ND ND 6.3 23
19-Jan-12 25.0 ND ND ND 4.4 18
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-18 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (owl) (ul?/1)
13-Jun-12 24.0 ND ND ND 6.6 30
11-Sep-12 38.0 ND ND ND 6.6 26
3-0ct-12 30.0 ND ND ND 6 27
13-Feb-13 34.9 ND ND ND 5.58 23.1
13-Jun-13 37.9 ND ND ND 8.86 22.9
5-Sep-13 41.0 ND ND ND 12.1 36.2
13-Nov-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
l l-Jun-15 30.5 ND ND ND 9.69 43.5
3-Sep-15 28.7 ND ND ND 15.7 47.6
28-0ct-15 52.9 ND ND ND 6.24 39.4
17-Mar-16 56.6 ND ND ND 5.96 40.7
8-Jun-16 60.0 ND ND ND 5.43 43.8
3-Aug-16 56.3 ND ND ND 5.79 40.7
26-0ct-16 60.1 ND ND ND 5.24 43.9
16-Mar-17 62.0 ND ND ND 4.47 39.4
20-Jun-17 63.8 ND ND ND 4.5 41.6
3-Aug-17 62.8 ND ND ND 4.24 40.4
10-0ct-l 7 62.9 ND ND ND 4.43 37.1
15-Mar-18 62.3 ND ND ND 4.32 44.3
13-Jun-18 59.9 ND ND ND 4.09 39.5
30-Aug-18 56.2 ND ND ND 3.51 45.6
13-Dec-18 57.6 ND ND ND 3.60 38.2
19-Mar-19 52.8 ND ND ND 3.85 37.6
19-Jun-19 54.2 ND ND ND 4.01 39.5
ll-Sep-19 56.2 ND ND ND 3.25 36.8
18-Dec-l 9 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
18-Sep-20 60.0 ND ND ND 3.36 38.7
11-Nov-20 58.6 ND ND ND 3.67 39.6
18-Mar-21 52.0 ND ND ND 3.61 41.8
u,
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I Cjd011Dform Ca:rlMn Methrlene
I TW14-19 Tettr bloride Cbl0r81Beth He CM8rfde Nifrat'e Udqr·
(~ (µ,d) (~ (~ (mg/I) (mg,'l)
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
l-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 <l <1 4 132
26-Mar-08 1800 2.9 <l <1 2.2 131
25-Jun-08 1000 1 <l <1 2.81 128
10-Sep-08 3600 8.6 <l <1 36.2 113
15-0ct-08 4200 12 <I <1 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <1 2.4 132
15-Sep-09 6600 15 <l <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 <l <1 5.9 142
Ctdotr Cub CMor,~ • hY,tene Nikate Chloridt,: II TW41.19 nu Tsa kwiide Chbmid tpgft) (~ gn) (10,mlo (nagn} ingtil)
11-0ct-10 1200 1.3 <1 <l 2.7 146
17-Feb-ll 3400 17 ND ND 17 135
7-Jun-11 4000 8.3 ND ND 12 148
17-Aug-11 970 2.1 ND ND 3 148
5-Dec-11 2200 5.4 ND ND 5 148
23-Jan-12 650 1.5 ND ND 0.6 138
6-Jun-12 460 1.1 ND ND 2.4 149
5-Sep-12 950 3.5 ND ND 2.5 149
3-0ct-12 1500 4 ND ND 4.1 150
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-17 510 1.35 ND ND 0.243 135
26-Jul-17 8840 13.0 ND ND 1.12 218
ll-Oct-17 129 ND ND ND 0.377 139
12-Mar-18 2640 1.36 ND ND 8.61 193
8-Jun-18 2980 3.45 ND ND 0.494 138
22-Aug-18 1910 2.03 ND ND 2.55 166
28-Nov-18 5270 6.18 ND ND 0.233 140
8-Mar-19 2050 2.43 ND ND 6.58 197
5-Jun-19 11500 15.90 ND ND 8.96 160
4-Sep-19 6670 10.10 ND ND 0.332 153
10-Dec-19 551 ND ND ND 0.535 147
19-Feb-20 8720 13.7 5.41 ND IO.I 205
Cblo11oform Carbo-u Chloro.methane Methylene Nitrate Chloride TW4 .. 19 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I)
II (ue;/1) {u(!/1)
27-May-20 7600 10.4 ND ND 1.14 147
4-Sep-20 1350 1.98 ND ND 11.6 188
28-0ct-20 660 1.10 ND ND 1.10 104
23-Feb-21 6660 8.40 ND ND 6.61 167
8c-JBl,IIJ-g~
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v~-oaa-a
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0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 s::t" C\I 0 CX) (0 s::t" C\I .-.-.-
(1/6n)
Chi l'Ofoma Carlma Chloromethane Mdliylene 1 Nitrate Cffloride TW4 .. 21 'fl ~adt! . Cbloitid.e CugJI) (ud) (Ug/1) (imlk.), (mg/I) ~mg/,l)
25-May-05 192 NA NA NA 14.6 NA
31-Aug-05 78 <5 <5 <5 10.1 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 <l <1 8.7 306
27-Jun-07 300 5.8 <1 <1 8.6 327
15-Aug-07 140 <1 <l <1 8.6 300
10-0ct-07 120 <l <l <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 <l 7.57 244
15-0ct-08 170 2 <1 <2 8.00 284
l l-Mar-09 180 <1 <l <1 8.3 279
24-Jun-09 200 <1 <1 <1 8.1 291
15-Sep-09 140 <1 <l <1 9.2 281
22-Dec-09 160 <1 <l <1 8.4 256
25-Feb-10 170 <l <1 <1 8.4 228
10-Jun-10 210 1.2 <1 <1 12 266
12-Aug-10 390 9.2 <1 <1 14 278
13-0ct-10 200 1.2 <1 <1 7 210
22-Feb-ll 230 1.2 ND ND 9 303
28-Jun-ll 290 4.8 ND ND 12 290
17-Aug-ll 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 Cara.. C1!4orometbane etl ylen Nitrate Chlo ·de
I TW4-21 (og/1) Tetmchlo e tugll) Chi i {.mgll) {m~) II fud) (ne(J.}
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
ll-Oct-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 15.4 353
4-Sep-20 920 ND ND ND 12.6 382
28-0ct-20 948 ND ND ND 16.3 411
23-Feb-21 400 ND ND ND 15.2 454
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-22 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (u2'1) (u2'1)
25-May-05 340 NA NA NA 18.2 NA
31-Aug-05 290 <5 <5 <5 15.7 NA
I-Dec-05 320 <5 <5 <5 15. l NA
9-Mar-06 390 <10 <10 <10 15.3 236
14-Jun-06 280 <10 <10 <10 14.3 221
20-Jul-06 864 <10 <10 <10 14.5 221
8-Nov-06 350 <1 1.6 <l 15.9 236
28-Feb-07 440 <l <l <1 20.9 347
27-Jun-07 740 <1 <1 <1 19.3 273
15-Aug-07 530 <1 <1 <l 19.3 259
10-0ct-07 440 <l <1 <l 18.8 238
26-Mar-08 1400 <1 <1 <l 39.l 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
1 l-Mar-09 390 <l <1 <1 20.7 177
24-Jun-09 730 <I <l <l 20.6 177
15-Sep-09 2300 <l <l <l 40.3 391
29-Dec-09 380 <1 <l <1 17.8 175
3-Mar-10 2200 <l <l <l 36.6 427
15-Jun-10 540 <1 <1 <1 19 134
24-Aug-10 340 <1 <1 <1 I5 130
13-0ct-10 340 <l <1 <l I6 134
23-Feb-l l 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
1 I-Feb-13 10600 3.24 ND ND 58 635
5-Jun-13 12500 3.35 ND ND 50.2 586
3-Sep-13 9640 3.25 ND ND 29.7 487
29-0ct-13 13300 8.09 ND ND 45.2 501
27-Jan-14 12100 6.06 ND 2.83 54.6 598
19-May-14 12400 6.65 ND ND 47.2 614
11-Aug-14 12400 1.9 40 ND 41.5 540
21-0ct-14 12400 3.32 1.61 ND 54.9 596
I Chloroform Carbon Chloromethane Methylene Nitrate Chloride !I TW4-22 Tetrachloride Chloride
!1 (ug/1) (u2'1) (ug/1) (ug/1) (mg/I) (mg/I)
9-Mar-15 12700 3.77 4.31 ND 69.2 675
8-Jun-15 8050 2.42 3.42 ND 47.l 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-l 7 5150 ND ND ND 66.1 391
11-0ct-l 7 4770 ND ND ND 80.l 600
12-Mar-18 4530 ND ND ND 62.3 607
8-Jun-18 30]0 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-I9 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
4-Sep-20 3760 ND ND ND 64.8 514
28-0ct-20 3640 ND 6.8 3 ND 64.9 523
23-Feb-21 5100 ND ND ND 69.6 618
oi-unr-B ~
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(1,Sn)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-23 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) I (ue/1) (ue/1) I
27-Jun-07 <1 <1 <1 <] <0.1 47
15-Aug-07 <l <1 <l <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 <l <l <l <l <0.05 41
10-Sep-08 <1 <1 <l <l <0.05 35
15-0ct-08 <2 <2 <2 <2 <0.05 51
4-Mar-09 <1 <1 <l <1 <0.1 41
24-Jun-09 <1 <1 <l <l <0.1 43
15-Sep-09 <1 <1 <1 <l <0.1 43
16-Dec-09 <l <l <l <1 <0.1 37
24-Feb-10 <1 <1 <1 <l <0.1 45
8-Jun-10 <l <l <1 <1 <0.1 40
10-Aug-10 <l <l <l <1 <0.1 40
5-0ct-10 <1 <l <1 <] <0.1 34
16-Feb-11 ND ND ND ND ND 44
25-May-l l ND ND ND ND ND 44
16-Aug-ll ND ND ND ND ND 41
15-Nov-l l 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
Chloroform C irltwt Cl'lloromethane Methylene Niwate Chloride TW4,.23 (ug(I~ Tetracfw:lrMe (ug/1) Otloride (mgtl) ('mg/t) (W?lrl} ·tu.e¥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-17 ND ND ND ND ND 44.7
14-Mar-18 ND ND ND ND ND 53.8
13-Jun-18 ND ND ND ND ND 47.6
30-Aug-18 ND ND ND ND ND 56.0
12-Dec-18 ND ND ND ND ND 54.9
16-Mar-19 ND ND ND ND ND 48.9
13-Jun-19 ND ND ND ND ND 50.2
11-Sep-19 ND ND ND ND ND 47.9
14-Dec-19 ND ND ND ND ND 54.4
17-Mar-20 ND ND ND ND ND 50.0
11-Jun-20 ND ND ND ND ND 49.0
17-Sep-20 ND ND ND ND ND 48.8
4-Nov-20 ND ND ND ND ND 49.3
17-Mar-21 ND ND ND ND ND 51.6
Jun-0
Sep-0
Dec-0
Mar-0
Jun-0
Sep-0
Dec-0
Mar-0
Jun-0
Sep-0
Dec-0
Mar-1
Jun-1
Sep-1
Dec-1
Mar-1
Jun-1
Sep-1
Dec-1
Mar-1
Jun-1
Sep-1
Dec-1
Mar-1
Jun-1
Sep-1
Dec-1
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
Sep-20
Dec-20
Mar-21
0
j~ •• ·~ 0
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11 Chloroform Carbon Chloromethane Methylene Nitrate Chloride II TW4-24 Tetrachloride Chloride (ug/1) ! (u2/I) (ug/1) (uwl) (mg/I) (mg/I) .
27-Jun-07 2.6 <1 <1 <l 26.1 770
15-Aug-07 2.2 <l <l <l 29 791
10-0ct-07 1.5 <l <1 <l 24.7 692
26-Mar-08 1.5 <l <l <l 24.4 740
25-Jun-08 1.4 <l <1 <1 45.3 834
10-Sep-08 2.9 <l <l <l 38.4 1180
15-0ct-08 <2 <2 <2 <2 44.6 1130
4-Mar-09 1.4 <l <l <l 30.5 1010
24-Jun-09 1.5 <l <l <l 30.4 759
15-Sep-09 1.4 <l <l <l 30.7 618
17-Dec-09 1.2 <l <l <l 28.3 1080
25-Feb-IO 1.3 <l <l <l 33.1 896
9-Jun-10 1.7 <l <l <l 30 639
24-Aug-10 1.8 <l <l <1 31 587
6-0ct-10 1.4 <l <l <l 31 522
17-Feb-ll 1.8 ND ND ND 31 1100
26-May-l l 1.1 ND ND ND 35 1110
17-Aug-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
19-0ct-15 25.3 ND ND ND 29.6 909
9-Mar-16 22.8 ND ND ND 29.1 989
23-May-16 69.6 ND ND ND 24.2 771
25-Jul-16 17.8 ND ND ND 34.4 1180
12-0ct-l 6 20.8 ND ND ND 31.9 1010
Chloroform Carll u Chtero . thane Me hyle Nitrate Chloride TW4-24 Tctr ~id Cldorlde
II (ug/l) (ud) (ugll~ fat.a4) (mg/I) (mg}l)
II
8-Mar-17 18.3 ND ND ND 41.3 1090
13-Jun-17 17.2 ND ND ND 39.9 1080
26-Ju]-17 17.8 ND ND ND 40.0 1230
l l-Oct-17 16.0 ND ND ND 31.7 895
12-Mar-18 24.9 ND ND ND 44.9 1320
14-Jun-18 49.2 ND ND ND 33.6 792
22-Aug-18 35.0 ND ND ND 33.8 996
28-Nov-18 21.0 ND ND ND 38.4 1100
8-Mar-19 28.1 ND ND ND 39.3 1040
5-Jun-19 28.8 ND ND ND 33.2 1020
4-Sep-19 31.1 ND ND ND 36.4 1130
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
4-Sep-20 63.8 ND ND ND 39.1 1100
28-0ct-20 72.6 ND ND ND 35.9 1050
23-Feb-21 96.2 ND 3.6 ND 41.9 1170
(ug/L)
~ ~ N .I>, en 00 0 N 0 0 0 0 0 0 0 0 0 0 0 0 0 0
10-0ct-06
6-Jul-09
1-Apr-12
27-Dec-14
22-Sep-17
18-Jun-20
15-Mar-23 ...._ ____ ...__ ____ ...__ ____ .1__ ____ 1-____ L_ ___ _J
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-25 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ul!/1) (u,VI)
27-Jun-07 <1 <1 <l <1 17 .1 395
15-Aug-07 <1 <1 <l <l 16.7 382
10-0ct-07 <1 <1 <l <1 17 356
26-Mar-08 <l <1 <1 <1 18.7 374
25-Jun-08 <l <l <l <l 22.1 344
10-Sep-08 <1 <l <I <1 18.8 333
15-0ct-08 <2 <2 <2 <2 21.3 366
4-Mar-09 <l <l <I <l 15.3 332
24-Jun-09 <1 <l <1 <l 15.3 328
15-Sep-09 <l <l <1 <l 3.3 328
16-Dec-09 <1 <l <l <l 14.2 371
23-Feb-10 <l <I <l <1 14.4 296
8-Jun-10 <1 <I <l <1 16 306
10-Aug-10 <l <I <1 <l 14 250
5-0ct-10 <l <1 <1 <l 15 312
16-Feb-l l ND ND ND ND 15 315
25-May-l l ND ND ND ND 16 321
16-Aug-l l ND ND ND ND 16 276
15-Nov-l l ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 ND ND ND ND 16 287
l 1-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
ChloFoform Carbon Cbloronletban~ Methylen Nitrate Chk>dlle. TW4-25 Tetr~for,ide Chloride (ug,11) " (W?/1~ (ug/l~ (u2'1) fmg/1) (~}
8-Mar-17 1 ND ND ND 17 285
13-Jun-17 ND ND ND ND 0.976 69.8
26-Jul-17 ND ND ND ND 1.23 70.1
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
4-Sep-20 ND ND ND ND 0.994 67.3
28-0ct-20 ND ND ND ND 1.64 61.3
23-Feb-21 ND ND ND ND 3.43 100
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
Sep-20
Dec-20
0
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0
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Chloroform Carbon Chloromethane Methylene Nitrate ' Chloride TW4-26 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) (ue/1.) (ue/1)
15-Jun-10 13 <I <1 <I 7.9 33
I I-Aug-IO 5 <l <I <l 9 17
6-0ct-10 5.4 <I <I <1 9.6 22
22-Feb-l l 2.0 ND ND ND 10 30
26-May-l l 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 IO 26
18-Jan-12 7.0 ND ND ND 11 17
6-Jun-12 4.1 ND ND ND 12 19
l l-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-l 3 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
l 1-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
19-Sep-20 1120 ND ND ND 10.5 34.8
Obloroform Cavbo.n Ohloromethane M1etby,lene Nitrate Obloride TW4~26 ~ugll) Tetrachloride (ugt)) Chloride (mg/I) '(mg/I) 1, ~uf!/L) (usdl)
l l-Nov-20 1160 ND ND ND 11.9 36.3
24-Mar-21 1030 ND ND ND I 1.3 38 .9
0
Jun-10
Oct-10
Feb-11
Jun-11
Oct-11
Feb-12
Jun-12
Oct-12
Feb-13
Jun-13
Oct-13
Feb-14
Jun-14
Oct-14
Feb-15
Jun-15
Oct-15
Feb-16
Jun-16
Oct-16
Feb-17
Jun-17
Oct-17
Feb-18
Jun-18
Oct-18
Feb-19
Jun-19
Oct-19
Feb-20
Jun-20
Oct-20
Feb-21
N 0 0
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en 0 0
(ug/1)
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-27 Tetrachloride (ug/1) (u211) (ug/1) Chloride ( ug/1) (mg/I) (mg/I)
-
24-Jan-12 9 ND ND ND 24 11
13-Jun-12 ND ND ND ND 41 17
30-Aug-12 ND ND ND ND 37 21
3-0ct-12 ND ND ND ND 36 18
7-Feb-13 ND ND ND ND 31.2 18.8
30-May-13 ND ND ND ND 29.4 20.3
29-Aug-13 ND ND ND ND 27.2 19
6-Nov-13 ND ND ND ND 29.8 21.8
23-Jan-14 ND ND ND ND 31.3 21.8
21-May-14 ND ND ND ND 31.1 20.6
13-Aug-14 ND ND ND ND 27.0 23
23-0ct-14 ND ND ND ND 28.2 24.4
l l-Mar-15 ND ND ND ND 26.5 26.2
10-Jun-l 5 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
I O-Oct-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
l l-Jun-20 7.92 ND ND ND 21.5 28.0
I 8-Sep-20 5.62 ND ND ND 25.2 26.2
4-Nov-20 7.80 ND ND ND 16.7 26.8
18-Mar-21 4.66 ND ND ND 23.0 27.5
(ug/1)
0 I-' N w .i::. V, C"I -..J 00 <.D I-' 0
~:~~H [ I I I I I I I I i I
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
Jul-20
Sep-20
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Ohloroform Carbon Chloromethane Methylene Nit,rate CMoml1e T 4-28 (~g/1) Tetrachloi:ide (ug/1) Chloride (mg/I) fmghl) ( .. we {ue/1)
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
10-Jun-15 ND ND ND ND 19 56.4
2-Sep-15 ND ND ND ND 17.8 61.4
21-0ct-15 ND ND ND ND 18.7 52.7
15-Mar-16 ND ND ND ND 34.0 61.6
25-May-16 ND ND ND ND 29.0 67.1
27-Jul-16 ND ND ND ND 31.3 70.1
19-0ct-16 ND ND ND ND 25.5 70.9
14-Mar-17 ND ND ND ND 24.4 64.2
14-Jun-17 ND ND ND ND 26.0 68.6
27-Jul-17 ND ND ND ND 24.8 67.1
10-0ct-l 7 ND ND ND ND 24.8 57.4
14-Mar-18 ND ND ND ND 17 .2 65.0
12-Jun-18 ND ND ND ND 19.0 55.7
29-Aug-18 ND ND ND ND 16.0 63.8
30-Nov-18 ND ND ND ND 17 .7 52.4
16-Mar-19 ND ND ND ND 17.2 51.7
13-Jun-19 ND ND ND ND 15 .0 51.8
ll-Sep-19 ND ND ND ND 10.2 49.0
12-Dec-19 ND ND ND ND 9.48 50.0
17-Mar-20 ND ND ND ND 9.87 52.1
10-Jun-20 ND ND ND ND 9.55 49.8
17-Sep-20 ND ND ND ND 8.36 47.4
4-Nov-20 ND ND ND ND 7.76 49.0
17-Mar-21 ND ND ND ND 8.68 51.8
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
Sep-20
Dec-20
Mar-21
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(ugt)) {ngtl) (mg/.1) ~) '(u2']) ~<IW'I}
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
ll-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
ll-Oct-17 466 ND ND ND 2.45 37.7
21-Mar-18 533 ND ND ND 2.44 43.1
14-Jun-18 474 ND ND ND 2.67 40.1
5-Sep-18 454 ND ND ND 2.52 45.9
13-Dec-18 521 ND ND ND 2.50 40.9
20-Mar-19 507 ND ND ND 2.67 39.9
19-Jun-19 537 ND ND ND 2.56 39.4
12-Sep-19 549 ND ND ND 2.55 38.0
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
19-Sep-20 621 ND ND ND 2.9 39.9
1 l-Nov-20 671 ND ND ND 3.27 40.8
24-Mar-21 577 ND ND ND 3.09 44.3
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I .~uaJ,f) -{uw'l)
19-Jun-13 ND ND ND ND 0.948 36
29-Aug-13 ND ND ND ND 0.952 36.3
7-Nov-13 ND ND ND ND 1.24 35.9
23-Jan-14 ND ND ND ND 1.36 36
21-May-14 ND ND ND ND 1.44 31.99
13-Aug-14 ND ND ND ND 1.5 38
23-0ct-14 ND ND ND ND 1.84 37.1
11-Mar-15 1.65 ND ND ND 2.15 38.3
10-Jun-15 2.25 ND ND ND 1.75 40.3
3-Sep-15 3.27 ND ND ND 1.75 44.2
28-0ct-15 3.48 ND ND ND 1.86 37.8
17-Mar-16 5.16 ND ND ND 2.74 39.6
26-May-16 7.38 ND ND ND 2.04 40.2
3-Aug-16 6.79 ND ND ND 2.32 38.6
20-0ct-16 8.69 ND ND ND 2.51 41.3
15-Mar-17 13 .6 ND ND ND 2.7 37.7
15-Jun-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-17 13.4 ND ND ND 2.58 34.9
15-Mar-18 16.4 ND ND ND 3.63 41.0
13-Jun-18 16.9 ND ND ND 3.93 37.4
30-Aug-18 19.8 ND ND ND 3.79 44.1
12-Dec-18 23.9 ND ND ND 3.70 35.5
16-Mar-19 25.3 ND ND ND 4.08 35.9
13-Jun-19 31.5 ND ND ND 4.13 27.2
ll-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
18-Sep-20 67.7 ND ND ND 3.49 35.0
1 l-Nov-20 82.8 ND ND ND 3.64 37.1
18-Mar-21 74.8 ND ND ND 3.54 37.6
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
Sep-20
Dec-20
Mar-21
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19-Jun-13 ND ND ND ND 1.26 28.4
5-Sep-13 ND ND ND ND 1.1 29.4
7-Nov-13 ND ND ND ND 1.33 28
23-Jan-14 ND ND ND ND 1.32 28.5
21-May-14 ND ND ND ND 1.22 26.3
13-Aug-14 ND ND ND ND 1.1 30
28-0ct-14 ND ND ND ND 1.23 30
11-Mar-15 ND ND ND ND 1.33 30.6
10-Jun-15 ND ND ND ND 1.19 31.1
2-Sep-15 ND ND ND ND 0.916 30.4
21-0ct-15 ND ND ND ND 0.953 29.1
16-Mar-16 ND ND ND ND 1.84 31.5
25-May-16 ND ND ND ND 1.36 32.5
28-Jul-16 ND ND ND ND 1.41 30.6
20-0ct-16 ND ND ND ND 1.14 34.0
15-Mar-17 ND ND ND ND 1.19 31.3
15-Jun-17 ND ND ND ND 1.21 33.4
2-Aug-17 ND ND ND ND 1.11 33.0
10-0ct-17 ND ND ND ND 1.04 30.9
14-Mar-18 ND ND ND ND 0.916 38.8
12-Jun-18 ND ND ND ND 0.948 34.4
29-Aug-18 ND ND ND ND 0.710 40.3
12-Dec-18 ND ND ND ND 0.766 35.2
16-Mar-19 ND ND ND ND 0.754 35.0
13-Jun-19 ND ND ND ND 0.713 36.9
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
l 1-Jun-20 ND ND ND ND 0.569 36.7
l 7-Sep-20 ND ND ND ND 0.507 36.5
4-Nov-20 ND ND ND ND 0.501 36.4
17-Mar-21 ND ND ND ND 0.501 40.3
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
Sep-20
Dec-20
Mar-21
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-32 Tetrachloride (ug/1) (uwl) (ug/1) Chloride (ug/1) (mg/I) (mg/I) -
14-Nov-13 ND ND ND ND 4 .26 52.1
22-Jan-14 ND ND ND ND 5.11 54.5
21-May-14 ND ND ND ND 5.63 54.9
13-Aug-14 ND ND ND ND 4.2 64
23-0ct-14 ND ND ND ND 2.14 62.6
l 1-Mar-15 ND ND ND ND 2.46 64.2
10-Jun-15 ND ND ND ND 1.21 62.7
2-Sep-15 ND ND ND ND 5.09 59.6
21-0ct-15 ND ND ND ND 1.19 55.1
15-Mar-16 ND ND ND ND 4.48 64.2
25-May-16 ND ND ND ND 3.16 71.8
28-Jul-16 ND ND ND ND 3.44 64.4
19-0ct-16 ND ND ND ND 2.87 66.0
14-Mar-17 ND ND ND ND 2.82 62.8
15-Jun-17 ND ND ND ND 2.37 53 .5
2-Aug-17 ND ND ND ND 2.47 65.8
10-0ct-17 ND ND ND ND 2.54 58.3
14-Mar-18 ND ND ND ND 2.94 65.4
12-Jun-18 ND ND ND ND 2.51 59.2
29-Aug-18 ND ND ND ND 2.56 68.1
30-Nov-18 ND ND ND ND 2.50 57.5
16-Mar-19 ND ND ND ND 2.15 57.5
l 3-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
17-Sep-20 ND ND ND ND 1.58 50.8
4-Nov-20 ND ND ND ND 1.74 53.7
17-Mar-21 ND ND ND ND 1.80 60.5
Nov-13
Feb-14
May-14
Aug-14
Nov-14
Feb-15
May-15
Aug-15
Nov-15
Feb-16
May-16
Aug-16
Nov-16
Feb-17
May-17
Aug-17
Nov-17
Feb-18
May-18
Aug-18
Nov-18
Feb-19
May-19
Aug-19
Nov-19
Feb-20
May-20
Aug-20
Nov-20
Feb-21
0
0
••
••
• ,,
•
•
'
•
•• •
•
~ ~.
i•
•
0
h
h
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0
0
0
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0
0
0
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(ug/L)
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C (I)
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' Carbon
TW4-33 Chloroform Tetrachloride Chloromethane Methylene Nitrate Chloride
(ug/1) (uwl) (ug/1) Chloride (ug/1) (mg/I) (mg/I)
14-Nov-13 J26 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-1 8 141 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
l 8-Dec-19 117 ND ND ND 1.86 48.8
I8-Mar-20 94 ND ND ND 2.44 45.3
12-Jun-20 90 ND ND ND 3.26 48.9
18-Sep-20 85 ND ND ND 3.58 51.0
11-Nov-20 80.6 ND ND ND 3.71 51.5
18-Mar-21 64.9 ND ND ND 4.62 55.6
0
Nov-13
Feb-14
May-14
Aug-14
Nov-14
Feb-15
May-15
Aug-15
Nov-15
Feb-16
May-16
Aug-16
Nov-16
Feb-17
May-17
Aug-17
Nov-17
Feb-18
May-18
Aug-18
Nov-18
Feb-19
May-19
Aug-19
Nov-19
Feb-20
May-20
Aug-20
Nov-20
Feb-21
I\J .i:,.
0 0
C)
0
(ug/L)
(X)
0
......
0 0
......
I\J 0
......
.i:,.
0
......
C)
0
i I w w
0 ~
0 ""I a 0
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< e!.
C C'D 0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-34 (ug/1) Tetrachloride (ug/1) Chloride (mg/I) (mg/I) r
(uwl) (u2'1) ..
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-l 7 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-l 7 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.l
l l-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 l-Jun-20 ND ND ND ND 1.24 20.9
17-Sep-20 ND ND ND ND 0.978 19.0
4-Nov-20 ND ND ND ND 1.04 18.7
17-Mar-21 ND ND ND ND 10.9 19.3
Nov-13
Feb-14
May-14
Aug-14
Nov-14
Feb-15
May-15
Aug-15
Nov-15
Feb-16
May-16
Aug-16
Nov-16
Feb-17
May-17
Aug-17
Nov-17
Feb-18
May-18
Aug-18
Nov-18
Feb-19
May-19
Aug-19
Nov-19
Feb-20
May-20
Aug-20
Nov-20
Feb-21
0
0
~
~
•
~
0
0
-
I
•I
0
0
0
0
0
0
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0
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0
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0
0
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Oht ofentil Carb Chlt'troIIW.flt ne Metliy!Me Nitra Ch me TW4-l5 {agtl) Tetiraehloride 11gtl) Cllmml1 (mg,lt) (mg/I~ (W!fi'}; (tl1?tl}
27-Aug-14 ND ND ND ND 0.2 34
28-0ct-14 ND ND ND ND 0.351 34.1
l 1-Mar-15 ND ND ND ND 0.436 34.9
10-Jun-15 ND ND ND ND 0.452 35.2
3-Sep-15 ND ND ND ND 0.304 35.9
28-0ct-15 ND ND ND ND 0.419 33.4
16-Mar-16 ND ND ND ND 0.521 35.4
26-May-16 ND ND ND ND 0.631 35.4
3-Aug-16 ND ND ND ND 0.723 34.8
20-0ct-16 ND ND ND ND 0.626 37.1
15-Mar-17 ND ND ND ND 0.673 33.7
15-Jun-17 ND ND ND ND 0.699 34.8
2-Aug-17 ND ND ND ND 0.670 36.3
10-0ct-17 ND ND ND ND 0.651 31.7
14-Mar-18 ND ND ND ND 0.740 37.4
13-Jun-18 ND ND ND ND 0.662 33.7
30-Aug-18 ND ND ND ND 0.527 39.3
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
1 l-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
l 1-Jun-20 ND ND ND ND 0.699 34.0
17-Sep-20 ND ND ND ND 0.760 32.2
4-Nov-20 ND ND ND ND 0.756 30.4
17-Mar-21 ND ND ND ND 0.991 35.6
Au
Oc
De
Fel
Ap
Jun
Aug
Oc
Dec
Feb
Apr
Jun
Aug
Oct
Dec-
Feb-
Apr-
Jun-
Aug-
Oct-
Dec-
Feb-
Apr-1
Jun-1
Aug-1
Oct-1
Dec-1
Feb-1
Apr-1
Jun-1
Aug-1
Oct-19
Dec-19
Feb-20
Apr-20
Jun-20
Aug-20
Oct-20
Dec-20
Feb-21
0 0 0 0 . ~
0
0
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0
0
0
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0
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C&torolenn Calf'lte'D CJ:1bummdta e Metlljlene Ma!rate I Clmmde TW4-l6 {ug/.1~ 'fetiradt;bmlde (u,gpl} QMarid.e
(lllgffl ' (agl,l) ~uilt) t,nd)
27-Aug-14 ND ND ND ND ND 65
23-0ct-14 ND ND ND ND ND 67.3
11-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
ll-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
11-Jun-20 ND ND ND ND ND 67.0
17-Sep-20 ND ND ND ND ND 66.0
4-Nov-20 ND ND ND ND ND 64.0
17-Mar-21 ND ND ND ND ND 72.5
Aug-
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-1
Apr-1
Jun-1
Aug-1
Oct-1
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
Aug-20
Oct-20
Dec-20
Feb-21
0
••
••
••
••
•• ••
••
••
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Cht fi an: Carb011 o 01t1 tihane Methyhme Nitr tie Chloride TW4-37 ( git~ Tetracfdoride (ugll) Chlo kle (mg/I~ (mg/I) hu?/0 Cul!ll)
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.l 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
4-Sep-20 13800 9.6 ND ND 29.5 273
28-0ct-20 10300 6.5 29.40 ND 28.7 254
23-Feb-21 9380 ND ND ND 26.9 242
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
Jun-20
Aug-20
Oct-20
Dec-20
Feb-21
0
U1 0 0 0
......
0 0 0 0
~ (ug/L)
g
I\)
0 0 0 0
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(..)
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Chloroform CaTbon Chl romethane Methylene Nitrate Chloride TW4-38 Tetllaehloride Chloride (ug/1) (uJ!/1) (rug/I) CueJ.l) (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
11-Jun-20 ND ND ND ND 9.00 34.9
18-Sep-20 ND ND ND ND 7.35 34.7
4-Nov-20 ND ND ND ND 7.72 35.1
18-Mar-21 ND ND ND ND 8.24 37.2
(ug/L)
0 0 0 0 0 ...... ...... ...... ...... _., ......
Nov-16
Feb-17
•
May-17
Aug-17 !
Nov-17
Feb-18 -
May-18 l I I I I I I I I I I -4 =E .1:1,
I
Aug-18 i I I I I I I I I I I w co
0 :::r
Nov-18 1 I I I I I I I I I I 0 ""I 0 -0 ""I
Feb-19 1 I I I I I I
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May-19 1 I I I I I I I I
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Aug-19
•
Nov-19
Feb-20 I
May-20 "
t Aug-20
Nov-20 !
Feb-21 -1
Chloroform Cali, Cltlorcmwffume M.tihyil ne Nitrate Ckfori TW4-39 TetrachlQride CMamte (ug/1~ Gwr/1,) fag;ti) €ttd0° ~mg/I) ~mg/rl:)
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
ll-Oct-17 552 ND ND ND 2.65 73.5
12-Mar-18 2870 3.10 ND ND 3.33 118
8-Jun-18 7160 7.94 ND ND 4.84 107
22-Aug-18 8180 12.50 2.33 ND 6.05 110
28-Nov-18 6520 6.08 ND ND 6.39 123
8-Mar-19 885 1.20 ND ND 2.08 49.0
5-Jun-19 8640 11.60 ND ND 8.45 114.0
4-Sep-19 4240 5.71 ND ND 1.75 48.2
10-Dec-19 1650 1.14 ND ND 0.948 74.7
19-Feb-20 812 ND ND ND 0.792 76.5
27-May-20 5870 7.56 ND ND 5.01 88.5
4-Sep-20 5960 8.18 ND ND 2.69 63.2
28-0ct-20 648 ND 1.19 ND 7.03 83.2
23-Feb-21 2970 ND ND ND 2.12 53.0
ti)
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0 0 0 0 ,....
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oi-onv
Oc-A'BV\I
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6 ~-onv
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' Car.ho Cbloromethan Methylene Chloroform Nitrat'e Chloride TWit-40 (ug/1) I Tetra-chloride (uglt) C&lomle ~mg/.l, (mg/I)
ii' <m~A) lnotr\
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
4-Sep-20 333 ND ND ND 2.88 34.2
28-0ct-20 264 ND ND ND 2.58 34.6
23-Feb-21 436 ND 4 ND 2.43 36.0
u,
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0 -0 ...
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0
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0 0 '<:t
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0 0 C')
0 LO C\J
{1J6n)
0 0 C\J
0 LO ,....
0 0 ,....
0 LO 0
~i-uer-v
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Cat'bon Methylene Chloride '
TW4-;!11 Ohloroform Tetr.ichlol" de Chlorom~lihane Chlol!jde NUHte (mg/I~ ,ug/1) (uwl) ~ug/1~ (ufYI)', ~mg())
'
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
4-Sep-20 1110 ND ND ND 6.69 40.2
28-0ct-20 1020 ND ND ND 6.25 39.7
23-Feb-21 1170 ND ND ND 6.41 40.6
u, a, :::,
ca >
E II.,
0 -0 II.,
.2 .c 0
T"" -.::I' I -.::I' 3= I-
0 0 <O ....
0 0 s::t" ....
0 0 C\I ....
0 0 0 ....
0 0 CX)
(1J6n)
0 0 <O
0 0 s::t"
0 0 C\I
oc-unr-a~
6 ~-oaa-~
6 ~ -Al3V\l-9 ~
a~-ioo-a
0
Carbon I Methylene Ohlorrdfol'ID dhlorometbane Nitrate €,htoride TW4-42 (ug/1) Tetrachloride {Ug/t) Chloriile (mgtl) (mg/I:)
L (mill) j (u211~
19-Jun-19 ND ND ND ND 2.57 23.3
ll-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
10-Jun-20 ND ND ND ND 3.23 23.1
l 7-Sep-20 ND ND ND ND 3.65 23.5
4-Nov-20 ND ND ND ND 2.77 22.4
17-Mar-21 ND ND ND ND 3.15 24.2
(ug/L)
0 0 0 0 0 ....
15-May-19 -.----+---+-----+---+---f-------+-----+----1-----1
•
23-Aug-19
•
1-Dec-19 •
-4 =e .,:a
10-Mar-20 ! I I I I I I I I I I I .,:a N
0 :::T
0 ..,
0 -0
18-Jun-20 f I I I I I I I I I
..,
3
< D>
C (D
tn
26-Sep-20 l I I I I I I I I I I
i
4-Jan-21
•
14-Apr-21
23-Jul-21 _.__ _ __._ __ _.__ _ __,_ __ ......_ _ __,_ __ ._ _ __._ ___ '-_ _._ _ ____,
TabL
Contour Map Based Chloroform Plume Mass Calculations and Data over Time
CHLOROFORM RESIDUAL MASS ESTIMATE DETAILS:
Chloroform Data File: CHL_Surferlnput_Q1_21.xls
Gridding details:
1) kriging parameters: SURFER™ default parameters (point kriging, linear
variogram, slope= 1, no anisotropy [anisotropy= l], no search constraints [all data
used])
2) minx, max x (UTME[m]): 631900, 633043
3) min y, may y (UTMN[m]): 4154240, 4155550.64
4) grid spacing in x, y (m): 15.24, 15.24
5) artificial or pseudo-data: none
6) Q4, 2020 (previous quarter) data used at wells: MW-1, MW-2, MW-3A, MW-5,
MW-12, MW-15, MW-17 through MW-20, MW-22, MW-23, MW-27 through
MW-29, MW-35, MW-37 (all non-detect).
Chloroform residual mass estimate kriged grid files (ascii format):
Ucm1Q21wl.grd: first quarter, 2021 Water Level Grid (ft amsl)
Ucm1Q2lbb.grd: first quarter, 2021 Aquifer Base Grid (ft amsl)
Ucm1Q21sat.grd: first quarter, 2021 Saturated Thickness Grid (ft)
Ucm1Q211ogchl.grd: first quarter, 2021 log of chloroform grid (log of ug/L)
Ucm1Q21chl.grd: first quarter, 2021 Chloroform Concentration Grid (ug/L)
Ucm1Q21ge70.grd: first quarter, 2021 Chloroform Concentration GE 70 Grid (ug/L)
Ucm1Q21volm3.grd: first quarter, 2021 Groundwater Volume Grid (m3)
Ucm1Q21masslb.grd: first quarter, 2021 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format}:
Ucm1Q21wl.dat: first quarter, 2021 Water Level Grid XYZ file (ft amsl)
Ucm1Q2lbb.dat: first quarter, 2021 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm1Q21sat.dat: first quarter, 2021 Saturated Thickness Grid XYZ file (ft)
Ucm1Q21logchl.dat: first quarter, 2021 log of chloroform grid XYZ file (log of ug/L)
Ucm1Q21chl.dat: first quarter, 2021 Chloroform Concentration Grid XYZ file (ug/L)
Ucm1Q21ge70.dat: first quarter, 2021 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm1Q21volm3.dat: first quarter, 2021 Groundwater Volume Grid XYZ file (m3)
Ucm1Q21masslb.dat: first quarter, 2021 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate file: Ucm1Q21result.xls
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2400
2200
2000
1800
1600
1400
1200
1000
800
600
400
200
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~~~~~~~~~~~~~~~~~~~~~~~ ~~~~~~~~~~~~~~~~~~~~~~~
~ mass estimate
-.. Linear (mass estimate)
HYDRO
GEO
CHEM, INC.
TIME SERIES OF RESIDUAL CHLOROFORM MASS
ESTIMATES
Approved I Date
SJS
Author I Date
SJS
File Name !Figure
....... IT ........... m l.1
H:\718000\may21\chloroform\masscalc\FL.1_resid_chl_mass_1Q21.xls: FL.1 Resid CHL Mass
TABLE L.1
Chloroform Plume Residual Mass
Since Third Quarter 2015
Residual
Plume Mass
Quarter (lbs)
0315 1712
0415 1869
01 16 1946
0216 2261
0316 1718
0416 1711
01 17 1271
0217 1372
0317 1948
0417 884
0118 1271
0218 1271
0318 1208
0418 1107
01 19 833
0219 1408
0319 1050
0419 770
01 20 1106
0220 1056
03 20 909
0420 715
01 21 1273
Notes:
lbs= pounds
H :\718000\may21 \chloroform \masscalc\FL. l_resid_ chi_ mass_1Q21.xls: Table L.1
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Monday, May 10, 2021 8:02 AM
Phillip Goble
'Dean Henderson'; David Frydenlund; Terry Slade; Scott Bakken; Logan Shumway; Garrin
Palmer
Transmittal of CSV Files White Mesa Mill 2021 Q1 Chloroform Monitoring
2102631-report-EDD.csv; 2103541-report-EDD.csv; 2103706-report-EDD.csv; Q1 2021
Chloroform Field Data.csv; Q1 2021 DTWs EIM -All Programs.csv
Attached to this e-mail is an electronic copy of laboratory results for chloroform monitoring conducted at the White
Mesa Mill during the first quarter of 2021, 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
May 10, 2021
VIA PDF AND OVERNIGHT DELIVERY
Jalynn Knudsen,
Interim Director of Waste Management and Radiation Control
State of 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: State of Utah Stipulation and Consent Order ("SCO") Docket Number UGW-20-01
White Mesa Uranium Mill -Energy Fuels Resources (USA) Inc. ("EFRI") Notice Pursuant
to Part 11.H.1 of the Groundwater Corrective Action Plan ("GCAP") included as
Attachment 1 to the SCO
Dear Ms. Knudsen:
EFRI performed first quarter 2021 chloroform monitoring during the period from January 1, to March 31,
2021 under the September 14, 2015 GCAP, included as Attachment 1 to the duly executed SCO.
Part ILG of the GCAP states that "An exceedance shall be defined as the presence of chloroform in any
Compliance Monitoring Well in excess of the Table 2 Groundwater Corrective Action Limit ("GCAL")
(70 ug/1) for two or more consecutive quarters." Further, Part II.H. l) states that "At any time EFR[I]
submits a quarterly report that demonstrates an exceedance (second quarter of chloroform exceedance),
EFR[I] will provide a written exceedance notice to the Director ("Exceedance Notice") for all wells that
have demonstrated such an exceedance." Pursuant to Part II.H.1 of the GCAP, please note that the
concentrations of chloroform in TW4-30 exceeded the respective GCAL of 70 ug/L for two or more
consecutive quarters as noted on Table 1 attached.
This letter serves as the Exceedance Notice required pursuant to Part II.H.1) of the GCAP.
Part II.H.2) of the GCAP requires that within 60 days after the time of submittal of a quarterly report that
demonstrates an exceedance, EFRI will provide a plan and schedule for remedial actions to address
excursion for Director approval. A Plan and Time Schedule as required by II.H.2) will be submitted
under separate cover within the timeframe specified.
If you should have any questions regarding this submittal, please contact me at [phone].
Yourst't t~y ~SOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David Frydenlund, Terry Slade, Logan Shumway, Scott Bakken
Table 1
TW4-30Data
Chlorofo Carbo Chlo o ethane e ylene ttate W4-30 (ug/1) et chlorid (ug/1) Chlo "de ( g/1) (ug/1) (ug/l)
11/11/2020 82.8 ND ND ND 3.64 37.1
3/18/2021 74.8 ND ND ND 3.54 37.6
ID UTM NAD83 E UTM NAD83 N Q1 chl log chl
MW-01 632048.762 4156277.343 0.5 -0.69315
MW-02 631111.458 4155147.645 0.5 -0.69315
MW-3A 631188 4153701 0.5 -0.69315
MW-04 632528.239 4154843.595 1150 7.047517
MW-05 631487.143 4154685.998 0.5 -0.69315
MW-11 631884.320 4154613.567 0.5 -0.69315
MW-12 631227.666 4154732.958 0.5 -0.69315
MW-14 631683.028 4154278.148 0.5 -0.69315
MW-15 631500.674 4154305.536 0.5 -0.69315
MW-17 631911.605 4154068.619 0.5 -0.69315
MW-18 632293.435 4156108.350 0.5 -0.69315
MW-19 632687.427 4155914.140 0.5 -0.69315
MW-20 631080.558 4153163.859 0.5 -0.69315
MW-22 632550.351 4152699.061 0.5 -0.69315
MW-23 631055.742 4154775.143 0.5 -0.69315
MW-24 631278.659 4155179.519 0.5 -0.69315
MW-25 632162.900 4154565.810 0.5 -0.69315
MW-27 632058.974 4155531.958 0.5 -0.69315
MW-28 631668.123 4155173.235 0.5 -0.69315
MW-29 631508.577 4154977.313 0.5 -0.69315
MW-30 631814.639 4154904.086 0.5 -0.69315
MW-31 632096.041 4154832.451 0.5 -0.69315
MW-33 631066.637 4154384.754
MW-34 631289.321 4154343.279
MW-35 631066.446 4154577.601 0.5 -0.69315
MW-36 631052.558 4154496.563 0.5 -0.69315
MW-37 631395.246 4154320.793 0.5 -0.69315
MW-38 631855.323 4153140.006 0.5 -0.69315
MW-39 632220.670 4153395.504 0.5 -0.69315
MW-40 632565.648 4153638.305 0.5 -0.69315
TW4-01 632520.433 4154799.077 948 6.854355
TW4-02 632528.370 4154876.070 939 6.844815
TW4-03 632529.958 4155043.522 0.5 -0.69315
TW4-04 632536.308 4154716.526 1130 7.029973
TW4-05 632510.114 4155144.358 12.9 2.557227
TW4-06 632522.020 4154641.120 3.78 1.329724
TW4-07 632514.876 4154837.177 875 6.774224
TW4-08 632563.295 4154833.208 26.9 3.292126
TW4-09 632514.876 4155095.960 39 3.663562
TW4-10 632447.407 4155045.933 718 6.57647
TW4-11 632452.964 4154913.377 2750 7.919356
TW4-12 632677.595 4155051.490 0.5 -0.69315
TW4-13 632653.783 4154905.439 0.5 -0.69315
TW4-14 632658.545 4154695.889 1.77 0.57098
MW-26 632333.661 4155062.031 3060 8.02617
TW4-16 632313.263 4154921.314 248 5.513429
MW-32 632310.150 4154786.287 0.5 -0.69315
TW4-18 632486.301 4155193.571 52 3.951244
TW4-19 632348.982 4155189.602 6660 8.803875
TW4-20 632306.120 4155155.471
TW4-21 632354.538 4155286.440 400 5.991465
TW4-22 632198.963 4155172.934 5100 8.536996
TW4-23 632383.895 4154586.902 0.5 -0.69315
TW4-24 632116.844 4155166.850 96.2 4.566429
TW4-25 632359.142 4155402.627 0.5 -0.69315
TW4-26 632518.845 4154554.601 1030 6.937314
TW4-27 632674.000 4154604.000 4.66 1.539015
TW4-28 632742.000 4155021.000 0.5 -0.69315
TW4-29 632668.000 4154547.000 577 6.357842
TW4-30 632715.000 4154561.000 74.8 4.314818
TW4-31 632734.000 4154601.000 0.5 -0.69315
TW4-32 632808.000 4154983.000 0.5 -0.69315
TW4-33 632609.000 4154617.000 64.9 4.172848
TW4-34 632667.000 4154471.000 0.5 -0.69315
TW4-35 632714.000 4154505.000 0.5 -0.69315
TW4-36 632674.000 4154828.000 0.5 -0.69315
TW4-37 632256.000 4155157.000 9380 9.146335
TW4-38 632584.643 4155087.571 0.5 -0.69315
TW4-39 632397.658 4155145.602 2970 7.996317
TW4-40 632513.410 4154480.872 436 6.077642
TW4-41 632553.968 4154729.708 1170 7.064759
TW4-42 632524.19 4154418.44 0.5 -0.69315
CHLOROFORM RESIDUAL MASS ESTIMATE DETAILS:
Chloroform Data File: CHL_SurferInput_Q1_21.xls Gridding details:
1) kriging parameters: SURFERTM default parameters (point kriging, linear
variogram, slope = 1, no anisotropy [anisotropy = 1], no search constraints [all data used]) 2) min x, max x (UTME[m]): 631900, 633043 3) min y, may y (UTMN[m]): 4154240, 4155550.64
4) grid spacing in x, y (m): 15.24, 15.24 5) artificial or pseudo-data: none 6) Q4, 2020 (previous quarter) data used at wells: MW-1, MW-2, MW-3A, MW-5, MW-12, MW-15, MW-17 through MW-20, MW-22, MW-23, MW-27 through MW-29, MW-35, MW-37 (all non-detect).
Chloroform residual mass estimate kriged grid files (ascii format): Ucm1Q21wl.grd: first quarter, 2021 Water Level Grid (ft amsl)
Ucm1Q21bb.grd: first quarter, 2021 Aquifer Base Grid (ft amsl) Ucm1Q21sat.grd: first quarter, 2021 Saturated Thickness Grid (ft)
Ucm1Q21logchl.grd: first quarter, 2021 log of chloroform grid (log of ug/L) Ucm1Q21chl.grd: first quarter, 2021 Chloroform Concentration Grid (ug/L) Ucm1Q21ge70.grd: first quarter, 2021 Chloroform Concentration GE 70 Grid (ug/L)
Ucm1Q21volm3.grd: first quarter, 2021 Groundwater Volume Grid (m3) Ucm1Q21masslb.grd: first quarter, 2021 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format): Ucm1Q21wl.dat: first quarter, 2021 Water Level Grid XYZ file (ft amsl)
Ucm1Q21bb.dat: first quarter, 2021 top of Aquifer Base Grid XYZ file (ft amsl) Ucm1Q21sat.dat: first quarter, 2021 Saturated Thickness Grid XYZ file (ft)
Ucm1Q21logchl.dat: first quarter, 2021 log of chloroform grid XYZ file (log of ug/L)
Ucm1Q21chl.dat: first quarter, 2021 Chloroform Concentration Grid XYZ file (ug/L) Ucm1Q21ge70.dat: first quarter, 2021 Chloroform Concentration GE 70 Grid (ug/L) XYZ file
Ucm1Q21volm3.dat: first quarter, 2021 Groundwater Volume Grid XYZ file (m3) Ucm1Q21masslb.dat: first quarter, 2021 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate file: Ucm1Q21result.xls
ClientSampSampID CollectionDPrepDate AnalDate Matrix Analyte CAS DF Rslt
LCS VOC‐1 032521A ########    Surr: 1,2‐17060‐07‐0 1 108
LCS VOC‐1 032521A ########    Surr: 4‐B 460‐00‐4 1 87.7
LCS VOC‐1 032521A ########    Surr: Dib1868‐53‐7 1 103
LCS VOC‐1 032521A ########    Surr: Tolu2037‐26‐5 1 97.4
LCS VOC‐1 032521A ######## Carbon tetr56‐23‐5119
LCS VOC‐1 032521A ######## Chloroform67‐66‐3 1 19.3
LCS VOC‐1 032521A ######## Chlorometh74‐87‐3 1 15.9
LCS VOC‐1 032521A ######## Methylene 75‐09‐2 1 19.2
LCS VOC‐2 032621B ########    Surr: 1,2‐17060‐07‐0 1 96.2
LCS VOC‐2 032621B ########    Surr: 4‐B 460‐00‐4 1 93.3
LCS VOC‐2 032621B ########    Surr: Dib1868‐53‐7 1 97.9
LCS VOC‐2 032621B ########    Surr: Tolu2037‐26‐5 1 95.3
LCS VOC‐2 032621B ######## Chloroform67‐66‐3119
LCS‐R150142 ######## Chloride 16887‐00‐6 1 5.23
LCS‐R150258 ######## Nitrate/Nit 7727‐37‐9 1 1.07
MB VOC‐1 032521A ########    Surr: 1,2‐17060‐07‐0 1 110
MB VOC‐1 032521A ########    Surr: 4‐B 460‐00‐4 1 94.2
MB VOC‐1 032521A ########    Surr: Dib1868‐53‐7 1 103
MB VOC‐1 032521A ########    Surr: Tolu2037‐26‐5 1 95.8
MB VOC‐1 032521A ######## Carbon tetr56‐23‐510
MB VOC‐1 032521A ######## Chloroform67‐66‐310
MB VOC‐1 032521A ######## Chlorometh74‐87‐310
MB VOC‐1 032521A ######## Methylene 75‐09‐210
MB VOC‐2 032621B ########    Surr: 1,2‐17060‐07‐0 1 94.1
MB VOC‐2 032621B ########    Surr: 4‐B 460‐00‐4 1 93.5
MB VOC‐2 032621B ########    Surr: Dib1868‐53‐7 1 94.5
MB VOC‐2 032621B ########    Surr: Tolu2037‐26‐5 1 92.8
MB VOC‐2 032621B ######## Chloroform67‐66‐310
MB‐R150142 ######## Chloride 16887‐00‐6 10
MB‐R150258 ######## Nitrate/Nit 7727‐37‐910
MW‐32_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 36.8
MW‐32_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐910
MW‐32_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
MW‐32_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 92.8
MW‐32_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 102
MW‐32_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 107
MW‐32_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
MW‐32_032103706‐00######## ######## Aqueous Chloroform67‐66‐310
MW‐32_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
MW‐32_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
Trip Blank 2103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
Trip Blank 2103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 94.6
Trip Blank 2103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 102
Trip Blank 2103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 108
Trip Blank 2103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
Trip Blank 2103706‐00######## ######## Aqueous Chloroform67‐66‐310
Trip Blank 2103706‐00######## ######## Aqueous Chlorometh74‐87‐310
Trip Blank 2103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐07_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 46.2
TW4‐07_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐9 5 4.25
TW4‐07_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
TW4‐07_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4187
TW4‐07_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 97.6
TW4‐07_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 106
TW4‐07_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐07_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐07_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐07_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 99
TW4‐07_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 97.4
TW4‐07_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐71099
TW4‐07_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 96.6
TW4‐07_032103706‐00######## ######## Aqueous Chloroform67‐66‐3 10 875
TW4‐10_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 58.1
TW4‐10_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐9 10 7.2
TW4‐10_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 111
TW4‐10_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4191
TW4‐10_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 104
TW4‐10_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 105
TW4‐10_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐10_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐10_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐10_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 97.8
TW4‐10_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 94.6
TW4‐10_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐71098
TW4‐10_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 95.8
TW4‐10_032103706‐00######## ######## Aqueous Chloroform67‐66‐3 10 718
TW4‐16_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 92.6
TW4‐16_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐9 5 5.82
TW4‐16_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 110
TW4‐16_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 87.5
TW4‐16_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 106
TW4‐16_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 105
TW4‐16_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐16_032103706‐00######## ######## Aqueous Chloroform67‐66‐3 1 248
TW4‐16_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐16_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐16R_02103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 0
TW4‐16R_02103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐910
TW4‐16R_02103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 110
TW4‐16R_02103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 93.6
TW4‐16R_02103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 106
TW4‐16R_02103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 105
TW4‐16R_02103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐16R_02103706‐00######## ######## Aqueous Chloroform67‐66‐3 1 11.6
TW4‐16R_02103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐16R_02103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐26_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 38.9
TW4‐26_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐9 10 11.3
TW4‐26_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 109
TW4‐26_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 91.3
TW4‐26_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 105
TW4‐26_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 92.4
TW4‐26_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐26_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐26_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐26_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 97.1
TW4‐26_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 94.2
TW4‐26_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 100 97.3
TW4‐26_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 95.3
TW4‐26_032103706‐00######## ######## Aqueous Chloroform67‐66‐3 100 1,030
TW4‐29_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 44.3
TW4‐29_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐9 5 3.09
TW4‐29_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 112
TW4‐29_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4193
TW4‐29_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 95.9
TW4‐29_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 106
TW4‐29_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐29_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐29_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐29_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 98.7
TW4‐29_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 96.3
TW4‐29_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 10 99.3
TW4‐29_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 96.2
TW4‐29_032103706‐00######## ######## Aqueous Chloroform67‐66‐3 10 577
TW4‐75_032103706‐00######## ######## Aqueous Chloride 16887‐00‐6 10 37.4
TW4‐75_032103706‐00######## ######## Aqueous Nitrate/Nit 7727‐37‐910
TW4‐75_032103706‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 108
TW4‐75_032103706‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4192
TW4‐75_032103706‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 105
TW4‐75_032103706‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 104
TW4‐75_032103706‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐75_032103706‐00######## ######## Aqueous Chloroform67‐66‐310
TW4‐75_032103706‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐75_032103706‐00######## ######## Aqueous Methylene 75‐09‐210
PQL Units Qual TestCode TextRslt ReceivedDaSampleTemp
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
0.1 mg/L 300.0‐W
0.01 mg/L NO2/NO3‐W‐353.2
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
0.1 mg/L 300.0‐W
0.01 mg/L NO2/NO3‐W‐353.2
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
Location IDField ParamMeasurem Measurem Field Meas Measurem Field Sample ID
MW‐04 Conductivit ######## 12:07 1887 umhos/cm MW‐04_02232021
MW‐04 Dissolved O ######## 12:07 49 % MW‐04_02232021
MW‐04 pH ######## 12:07 7.08 pH Units MW‐04_02232021
MW‐04 Redox ######## 12:07 435 mV MW‐04_02232021
MW‐04 Temperatu ######## 12:07 14.89 deg CMW‐04_02232021
MW‐04 Turbidity ######## 12:07 0 NTU MW‐04_02232021
MW‐26 Conductivit ######## 10:06 3404 umhos/cm MW‐26_02232021
MW‐26 Dissolved O ######## 10:06 35.3 % MW‐26_02232021
MW‐26 pH ######## 10:06 6.88 pH Units MW‐26_02232021
MW‐26 Redox ######## 10:06 353 mV MW‐26_02232021
MW‐26 Temperatu ######## 10:06 14.71 deg CMW‐26_02232021
MW‐26 Turbidity ######## 10:06 0 NTU MW‐26_02232021
MW‐32 Conductivit ######## 12:27 3775 umhos/cm MW‐32_03222021
MW‐32 Conductivit ######## 12:28 3773 umhos/cm MW‐32_03222021
MW‐32 Conductivit ######## 12:29 3771 umhos/cm MW‐32_03222021
MW‐32 Conductivit ######## 12:30 3775 umhos/cm MW‐32_03222021
MW‐32 Dissolved O ######## 12:27 6.5 % MW‐32_03222021
MW‐32 Dissolved O ######## 12:28 6.5 % MW‐32_03222021
MW‐32 Dissolved O ######## 12:29 6.4 % MW‐32_03222021
MW‐32 Dissolved O ######## 12:30 6.3 % MW‐32_03222021
MW‐32 pH ######## 12:27 6.5 pH Units MW‐32_03222021
MW‐32 pH ######## 12:28 6.5 pH Units MW‐32_03222021
MW‐32 pH ######## 12:29 6.51 pH Units MW‐32_03222021
MW‐32 pH ######## 12:30 6.52 pH Units MW‐32_03222021
MW‐32 Redox ######## 12:27 328 mV MW‐32_03222021
MW‐32 Redox ######## 12:28 315 mV MW‐32_03222021
MW‐32 Redox ######## 12:29 308 mV MW‐32_03222021
MW‐32 Redox ######## 12:30 298 mV MW‐32_03222021
MW‐32 Temperatu ######## 12:27 14.19 deg CMW‐32_03222021
MW‐32 Temperatu ######## 12:28 14.2 deg CMW‐32_03222021
MW‐32 Temperatu ######## 12:29 14.18 deg CMW‐32_03222021
MW‐32 Temperatu ######## 12:30 14.2 deg CMW‐32_03222021
MW‐32 Turbidity ######## 12:27 67 NTU MW‐32_03222021
MW‐32 Turbidity ######## 12:28 66 NTU MW‐32_03222021
MW‐32 Turbidity ######## 12:29 64 NTU MW‐32_03222021
MW‐32 Turbidity ######## 12:30 63 NTU MW‐32_03222021
TW4‐01 Conductivit ######## 12:16 2983 umhos/cm TW4‐01_02232021
TW4‐01 Dissolved O ######## 12:16 62 % TW4‐01_02232021
TW4‐01 pH ######## 12:16 7.41 pH Units TW4‐01_02232021
TW4‐01 Redox ######## 12:16 431 mV TW4‐01_02232021
TW4‐01 Temperatu ######## 12:16 13.8 deg C TW4‐01_02232021
TW4‐01 Turbidity ######## 12:16 0 NTU TW4‐01_02232021
TW4‐02 Conductivit ######## 10:25 3771 umhos/cm TW4‐02_02232021
TW4‐02 Dissolved O ######## 10:25 96 % TW4‐02_02232021
TW4‐02 pH ######## 10:25 7.07 pH Units TW4‐02_02232021
TW4‐02 Redox ######## 10:25 417 mV TW4‐02_02232021
TW4‐02 Temperatu ######## 10:25 14 deg C TW4‐02_02232021
TW4‐02 Turbidity ######## 10:25 0 NTU TW4‐02_02232021
TW4‐03 Conductivit ######## 8:14 2.7 umhos/cm TW4‐03R_03162021
TW4‐03 Conductivit ######## 8:41 1885 umhos/cm TW4‐03_03172021
TW4‐03 Dissolved O ######## 8:14 42 % TW4‐03R_03162021
TW4‐03 Dissolved O ######## 8:41 82 % TW4‐03_03172021
TW4‐03 pH ######## 8:14 7.8 pH Units TW4‐03R_03162021
TW4‐03 pH ######## 8:41 6.8 pH Units TW4‐03_03172021
TW4‐03 Redox ######## 8:14 409 mV TW4‐03R_03162021
TW4‐03 Redox ######## 8:41 432 mV TW4‐03_03172021
TW4‐03 Temperatu ######## 8:14 12.6 deg C TW4‐03R_03162021
TW4‐03 Temperatu ######## 8:41 14.47 deg C TW4‐03_03172021
TW4‐03 Turbidity ######## 8:14 0 NTU TW4‐03R_03162021
TW4‐03 Turbidity ######## 8:41 5.5 NTU TW4‐03_03172021
TW4‐03 Conductivit ######## 7:31 1818 umhos/cm TW4‐03_03172021
TW4‐03 Conductivit ######## 7:34 1824 umhos/cm TW4‐03_03172021
TW4‐03 pH ######## 7:31 6.67 pH Units TW4‐03_03172021
TW4‐03 pH ######## 7:34 6.69 pH Units TW4‐03_03172021
TW4‐03 Temperatu ######## 7:31 14.88 deg C TW4‐03_03172021
TW4‐03 Temperatu ######## 7:34 14.93 deg C TW4‐03_03172021
TW4‐04 Conductivit ######## 12:34 2460 umhos/cm TW4‐04_02232021
TW4‐04 Dissolved O ######## 12:34 104 % TW4‐04_02232021
TW4‐04 pH ######## 12:34 7.17 pH Units TW4‐04_02232021
TW4‐04 Redox ######## 12:34 432 mV TW4‐04_02232021
TW4‐04 Temperatu ######## 12:34 15.02 deg C TW4‐04_02232021
TW4‐04 Turbidity ######## 12:34 0 NTU TW4‐04_02232021
TW4‐05 Conductivit ######## 11:57 1617 umhos/cm TW4‐05_03182021
TW4‐05 Conductivit ######## 11:58 1600 umhos/cm TW4‐05_03182021
TW4‐05 Conductivit ######## 11:59 1586 umhos/cm TW4‐05_03182021
TW4‐05 Conductivit ######## 12:00 1570 umhos/cm TW4‐05_03182021
TW4‐05 Dissolved O ######## 11:57 66 % TW4‐05_03182021
TW4‐05 Dissolved O ######## 11:58 64 % TW4‐05_03182021
TW4‐05 Dissolved O ######## 11:59 63 % TW4‐05_03182021
TW4‐05 Dissolved O ######## 12:00 62 % TW4‐05_03182021
TW4‐05 pH ######## 11:57 6.72 pH Units TW4‐05_03182021
TW4‐05 pH ######## 11:58 6.78 pH Units TW4‐05_03182021
TW4‐05 pH ######## 11:59 6.83 pH Units TW4‐05_03182021
TW4‐05 pH ######## 12:00 6.87 pH Units TW4‐05_03182021
TW4‐05 Redox ######## 11:57 448 mV TW4‐05_03182021
TW4‐05 Redox ######## 11:58 448 mV TW4‐05_03182021
TW4‐05 Redox ######## 11:59 447 mV TW4‐05_03182021
TW4‐05 Redox ######## 12:00 447 mV TW4‐05_03182021
TW4‐05 Temperatu ######## 11:57 15.43 deg C TW4‐05_03182021
TW4‐05 Temperatu ######## 11:58 15.44 deg C TW4‐05_03182021
TW4‐05 Temperatu ######## 11:59 15.44 deg C TW4‐05_03182021
TW4‐05 Temperatu ######## 12:00 15.44 deg C TW4‐05_03182021
TW4‐05 Turbidity ######## 11:57 3 NTU TW4‐05_03182021
TW4‐05 Turbidity ######## 11:58 2.8 NTU TW4‐05_03182021
TW4‐05 Turbidity ######## 11:59 2.7 NTU TW4‐05_03182021
TW4‐05 Turbidity ######## 12:00 2.7 NTU TW4‐05_03182021
TW4‐06 Conductivit ######## 10:34 3987 umhos/cm TW4‐06_03182021
TW4‐06 Dissolved O ######## 10:34 6.7 % TW4‐06_03182021
TW4‐06 pH ######## 10:34 6.64 pH Units TW4‐06_03182021
TW4‐06 Redox ######## 10:34 459 mV TW4‐06_03182021
TW4‐06 Temperatu ######## 10:34 14.48 deg C TW4‐06_03182021
TW4‐06 Turbidity ######## 10:34 26 NTU TW4‐06_03182021
TW4‐06 Conductivit ######## 8:34 4068 umhos/cm TW4‐06_03182021
TW4‐06 Conductivit ######## 8:35 4065 umhos/cm TW4‐06_03182021
TW4‐06 pH ######## 8:34 6.51 pH Units TW4‐06_03182021
TW4‐06 pH ######## 8:35 6.53 pH Units TW4‐06_03182021
TW4‐06 Temperatu ######## 8:34 14.08 deg C TW4‐06_03182021
TW4‐06 Temperatu ######## 8:35 14.11 deg C TW4‐06_03182021
TW4‐07 Conductivit ######## 10:15 1720 umhos/cm TW4‐07_03242021
TW4‐07 Dissolved O ######## 10:15 35 % TW4‐07_03242021
TW4‐07 pH ######## 10:15 7.05 pH Units TW4‐07_03242021
TW4‐07 Redox ######## 10:15 377 mV TW4‐07_03242021
TW4‐07 Temperatu ######## 10:15 14.8 deg C TW4‐07_03242021
TW4‐07 Turbidity ######## 10:15 18 NTU TW4‐07_03242021
TW4‐07 Conductivit ######## 8:48 1586 umhos/cm TW4‐07_03242021
TW4‐07 Conductivit ######## 8:49 1588 umhos/cm TW4‐07_03242021
TW4‐07 pH ######## 8:48 6.77 pH Units TW4‐07_03242021
TW4‐07 pH ######## 8:49 6.81 pH Units TW4‐07_03242021
TW4‐07 Temperatu ######## 8:48 13.44 deg C TW4‐07_03242021
TW4‐07 Temperatu ######## 8:49 13.48 deg C TW4‐07_03242021
TW4‐08 Conductivit ######## 12:59 4977 umhos/cm TW4‐08_03182021
TW4‐08 Conductivit ######## 13:00 4975 umhos/cm TW4‐08_03182021
TW4‐08 Conductivit ######## 13:01 4976 umhos/cm TW4‐08_03182021
TW4‐08 Conductivit ######## 13:02 4976 umhos/cm TW4‐08_03182021
TW4‐08 Dissolved O ######## 12:59 2.5 % TW4‐08_03182021
TW4‐08 Dissolved O ######## 13:00 2.4 % TW4‐08_03182021
TW4‐08 Dissolved O ######## 13:01 2.3 % TW4‐08_03182021
TW4‐08 Dissolved O ######## 13:02 2.3 % TW4‐08_03182021
TW4‐08 pH ######## 12:59 6.55 pH Units TW4‐08_03182021
TW4‐08 pH ######## 13:00 6.59 pH Units TW4‐08_03182021
TW4‐08 pH ######## 13:01 6.61 pH Units TW4‐08_03182021
TW4‐08 pH ######## 13:02 6.64 pH Units TW4‐08_03182021
TW4‐08 Redox ######## 12:59 452 mV TW4‐08_03182021
TW4‐08 Redox ######## 13:00 451 mV TW4‐08_03182021
TW4‐08 Redox ######## 13:01 450 mV TW4‐08_03182021
TW4‐08 Redox ######## 13:02 450 mV TW4‐08_03182021
TW4‐08 Temperatu ######## 12:59 14.94 deg C TW4‐08_03182021
TW4‐08 Temperatu ######## 13:00 14.93 deg C TW4‐08_03182021
TW4‐08 Temperatu ######## 13:01 14.94 deg C TW4‐08_03182021
TW4‐08 Temperatu ######## 13:02 14.97 deg C TW4‐08_03182021
TW4‐08 Turbidity ######## 12:59 4 NTU TW4‐08_03182021
TW4‐08 Turbidity ######## 13:00 3.9 NTU TW4‐08_03182021
TW4‐08 Turbidity ######## 13:01 3.8 NTU TW4‐08_03182021
TW4‐08 Turbidity ######## 13:02 3.7 NTU TW4‐08_03182021
TW4‐09 Conductivit ######## 12:28 2585 umhos/cm TW4‐09_03182021
TW4‐09 Conductivit ######## 12:29 2578 umhos/cm TW4‐09_03182021
TW4‐09 Conductivit ######## 12:30 2575 umhos/cm TW4‐09_03182021
TW4‐09 Conductivit ######## 12:31 2572 umhos/cm TW4‐09_03182021
TW4‐09 Dissolved O ######## 12:28 2.7 % TW4‐09_03182021
TW4‐09 Dissolved O ######## 12:29 2.5 % TW4‐09_03182021
TW4‐09 Dissolved O ######## 12:30 2.4 % TW4‐09_03182021
TW4‐09 Dissolved O ######## 12:31 2.3 % TW4‐09_03182021
TW4‐09 pH ######## 12:28 6.53 pH Units TW4‐09_03182021
TW4‐09 pH ######## 12:29 6.56 pH Units TW4‐09_03182021
TW4‐09 pH ######## 12:30 6.62 pH Units TW4‐09_03182021
TW4‐09 pH ######## 12:31 6.66 pH Units TW4‐09_03182021
TW4‐09 Redox ######## 12:28 459 mV TW4‐09_03182021
TW4‐09 Redox ######## 12:29 457 mV TW4‐09_03182021
TW4‐09 Redox ######## 12:30 455 mV TW4‐09_03182021
TW4‐09 Redox ######## 12:31 454 mV TW4‐09_03182021
TW4‐09 Temperatu ######## 12:28 15.01 deg C TW4‐09_03182021
TW4‐09 Temperatu ######## 12:29 15.01 deg C TW4‐09_03182021
TW4‐09 Temperatu ######## 12:30 15.03 deg C TW4‐09_03182021
TW4‐09 Temperatu ######## 12:31 15.02 deg C TW4‐09_03182021
TW4‐09 Turbidity ######## 12:28 21 NTU TW4‐09_03182021
TW4‐09 Turbidity ######## 12:29 22 NTU TW4‐09_03182021
TW4‐09 Turbidity ######## 12:30 23 NTU TW4‐09_03182021
TW4‐09 Turbidity ######## 12:31 23.1 NTU TW4‐09_03182021
TW4‐10 Conductivit ######## 9:43 2988 umhos/cm TW4‐10_03242021
TW4‐10 Dissolved O ######## 9:43 22 % TW4‐10_03242021
TW4‐10 pH ######## 9:43 6.35 pH Units TW4‐10_03242021
TW4‐10 Redox ######## 9:43 419 mV TW4‐10_03242021
TW4‐10 Temperatu ######## 9:43 14.78 deg C TW4‐10_03242021
TW4‐10 Turbidity ######## 9:43 28 NTU TW4‐10_03242021
TW4‐10 Conductivit ######## 8:40 2711 umhos/cm TW4‐10_03242021
TW4‐10 Conductivit ######## 8:41 2714 umhos/cm TW4‐10_03242021
TW4‐10 pH ######## 8:40 6.85 pH Units TW4‐10_03242021
TW4‐10 pH ######## 8:41 6.81 pH Units TW4‐10_03242021
TW4‐10 Temperatu ######## 8:40 13.41 deg C TW4‐10_03242021
TW4‐10 Temperatu ######## 8:41 13.26 deg C TW4‐10_03242021
TW4‐11 Conductivit ######## 10:15 3773 umhos/cm TW4‐11_02232021
TW4‐11 Dissolved O ######## 10:15 90 % TW4‐11_02232021
TW4‐11 pH ######## 10:15 6.93 pH Units TW4‐11_02232021
TW4‐11 Redox ######## 10:15 368 mV TW4‐11_02232021
TW4‐11 Temperatu ######## 10:15 13.36 deg C TW4‐11_02232021
TW4‐11 Turbidity ######## 10:15 0 NTU TW4‐11_02232021
TW4‐12 Conductivit ######## 11:03 1613 umhos/cm TW4‐12_03172021
TW4‐12 Dissolved O ######## 11:03 48 % TW4‐12_03172021
TW4‐12 pH ######## 11:03 6.82 pH Units TW4‐12_03172021
TW4‐12 Redox ######## 11:03 457 mV TW4‐12_03172021
TW4‐12 Temperatu ######## 11:03 14.58 deg C TW4‐12_03172021
TW4‐12 Turbidity ######## 11:03 3.5 NTU TW4‐12_03172021
TW4‐12 Conductivit ######## 8:10 1436 umhos/cm TW4‐12_03172021
TW4‐12 Conductivit ######## 8:12 1480 umhos/cm TW4‐12_03172021
TW4‐12 pH ######## 8:10 7.56 pH Units TW4‐12_03172021
TW4‐12 pH ######## 8:12 7.54 pH Units TW4‐12_03172021
TW4‐12 Temperatu ######## 8:10 12.78 deg C TW4‐12_03172021
TW4‐12 Temperatu ######## 8:12 12.83 deg C TW4‐12_03172021
TW4‐13 Conductivit ######## 12:03 2134 umhos/cm TW4‐13_03172021
TW4‐13 Dissolved O ######## 12:03 72 % TW4‐13_03172021
TW4‐13 pH ######## 12:03 6.79 pH Units TW4‐13_03172021
TW4‐13 Redox ######## 12:03 451 mV TW4‐13_03172021
TW4‐13 Temperatu ######## 12:03 14.92 deg C TW4‐13_03172021
TW4‐13 Turbidity ######## 12:03 5.2 NTU TW4‐13_03172021
TW4‐13 Conductivit ######## 8:19 2111 umhos/cm TW4‐13_03172021
TW4‐13 Conductivit ######## 8:20 2110 umhos/cm TW4‐13_03172021
TW4‐13 pH ######## 8:19 7.22 pH Units TW4‐13_03172021
TW4‐13 pH ######## 8:20 7.22 pH Units TW4‐13_03172021
TW4‐13 Temperatu ######## 8:19 12.75 deg C TW4‐13_03172021
TW4‐13 Temperatu ######## 8:20 12.81 deg C TW4‐13_03172021
TW4‐14 Conductivit ######## 10:07 5345 umhos/cm TW4‐14_03182021
TW4‐14 Dissolved O ######## 10:07 91 % TW4‐14_03182021
TW4‐14 pH ######## 10:07 6.3 pH Units TW4‐14_03182021
TW4‐14 Redox ######## 10:07 474 mV TW4‐14_03182021
TW4‐14 Temperatu ######## 10:07 14.99 deg C TW4‐14_03182021
TW4‐14 Turbidity ######## 10:07 63 NTU TW4‐14_03182021
TW4‐14 Conductivit ######## 8:23 5450 umhos/cm TW4‐14_03182021
TW4‐14 Conductivit ######## 8:24 5454 umhos/cm TW4‐14_03182021
TW4‐14 pH ######## 8:23 6.5 pH Units TW4‐14_03182021
TW4‐14 pH ######## 8:24 6.49 pH Units TW4‐14_03182021
TW4‐14 Temperatu ######## 8:23 15.32 deg C TW4‐14_03182021
TW4‐14 Temperatu ######## 8:24 15.24 deg C TW4‐14_03182021
TW4‐16 Conductivit ######## 8:42 3767 umhos/cm TW4‐16_03242021
TW4‐16 Conductivit ######## 8:43 3787 umhos/cm TW4‐16_03242021
TW4‐16 Conductivit ######## 8:44 3773 umhos/cm TW4‐16_03242021
TW4‐16 Conductivit ######## 8:45 3700 umhos/cm TW4‐16_03242021
TW4‐16 Conductivit ######## 7:59 3.6 umhos/cm TW4‐16R_03232021
TW4‐16 Dissolved O ######## 8:42 5 % TW4‐16_03242021
TW4‐16 Dissolved O ######## 8:43 5 % TW4‐16_03242021
TW4‐16 Dissolved O ######## 8:44 5.2 % TW4‐16_03242021
TW4‐16 Dissolved O ######## 8:45 5.3 % TW4‐16_03242021
TW4‐16 Dissolved O ######## 7:59 27.1 % TW4‐16R_03232021
TW4‐16 pH ######## 8:42 6.74 pH Units TW4‐16_03242021
TW4‐16 pH ######## 8:43 6.74 pH Units TW4‐16_03242021
TW4‐16 pH ######## 8:44 6.74 pH Units TW4‐16_03242021
TW4‐16 pH ######## 8:45 6.79 pH Units TW4‐16_03242021
TW4‐16 pH ######## 7:59 6.92 pH Units TW4‐16R_03232021
TW4‐16 Redox ######## 8:42 371 mV TW4‐16_03242021
TW4‐16 Redox ######## 8:43 370 mV TW4‐16_03242021
TW4‐16 Redox ######## 8:44 369 mV TW4‐16_03242021
TW4‐16 Redox ######## 8:45 363 mV TW4‐16_03242021
TW4‐16 Redox ######## 7:59 265 mV TW4‐16R_03232021
TW4‐16 Temperatu ######## 8:42 14.71 deg C TW4‐16_03242021
TW4‐16 Temperatu ######## 8:43 14.7 deg C TW4‐16_03242021
TW4‐16 Temperatu ######## 8:44 14.7 deg C TW4‐16_03242021
TW4‐16 Temperatu ######## 8:45 14.73 deg C TW4‐16_03242021
TW4‐16 Temperatu ######## 7:59 15.19 deg C TW4‐16R_03232021
TW4‐16 Turbidity ######## 8:42 12 NTU TW4‐16_03242021
TW4‐16 Turbidity ######## 8:43 11 NTU TW4‐16_03242021
TW4‐16 Turbidity ######## 8:44 10.8 NTU TW4‐16_03242021
TW4‐16 Turbidity ######## 8:45 11 NTU TW4‐16_03242021
TW4‐16 Turbidity ######## 7:59 0 NTU TW4‐16R_03232021
TW4‐18 Conductivit ######## 13:32 2000 umhos/cm TW4‐18_03182021
TW4‐18 Conductivit ######## 13:33 1990 umhos/cm TW4‐18_03182021
TW4‐18 Conductivit ######## 13:34 1950 umhos/cm TW4‐18_03182021
TW4‐18 Conductivit ######## 13:35 1920 umhos/cm TW4‐18_03182021
TW4‐18 Dissolved O ######## 13:32 13 % TW4‐18_03182021
TW4‐18 Dissolved O ######## 13:33 13.3 % TW4‐18_03182021
TW4‐18 Dissolved O ######## 13:34 13.5 % TW4‐18_03182021
TW4‐18 Dissolved O ######## 13:35 13.3 % TW4‐18_03182021
TW4‐18 pH ######## 13:32 6.55 pH Units TW4‐18_03182021
TW4‐18 pH ######## 13:33 6.6 pH Units TW4‐18_03182021
TW4‐18 pH ######## 13:34 6.63 pH Units TW4‐18_03182021
TW4‐18 pH ######## 13:35 6.65 pH Units TW4‐18_03182021
TW4‐18 Redox ######## 13:32 443 mV TW4‐18_03182021
TW4‐18 Redox ######## 13:33 443 mV TW4‐18_03182021
TW4‐18 Redox ######## 13:34 443 mV TW4‐18_03182021
TW4‐18 Redox ######## 13:35 443 mV TW4‐18_03182021
TW4‐18 Temperatu ######## 13:32 15.52 deg C TW4‐18_03182021
TW4‐18 Temperatu ######## 13:33 15.54 deg C TW4‐18_03182021
TW4‐18 Temperatu ######## 13:34 15.53 deg C TW4‐18_03182021
TW4‐18 Temperatu ######## 13:35 15.54 deg C TW4‐18_03182021
TW4‐18 Turbidity ######## 13:32 20 NTU TW4‐18_03182021
TW4‐18 Turbidity ######## 13:33 20.2 NTU TW4‐18_03182021
TW4‐18 Turbidity ######## 13:34 20 NTU TW4‐18_03182021
TW4‐18 Turbidity ######## 13:35 19.5 NTU TW4‐18_03182021
TW4‐19 Conductivit ######## 8:29 2585 umhos/cm TW4‐19_02232021
TW4‐19 Dissolved O ######## 8:29 28.7 % TW4‐19_02232021
TW4‐19 pH ######## 8:29 6.5 pH Units TW4‐19_02232021
TW4‐19 Redox ######## 8:29 526 mV TW4‐19_02232021
TW4‐19 Temperatu ######## 8:29 16.07 deg C TW4‐19_02232021
TW4‐19 Turbidity ######## 8:29 0 NTU TW4‐19_02232021
TW4‐21 Conductivit ######## 9:17 2950 umhos/cm TW4‐21_02232021
TW4‐21 Dissolved O ######## 9:17 40.1 % TW4‐21_02232021
TW4‐21 pH ######## 9:17 6.88 pH Units TW4‐21_02232021
TW4‐21 Redox ######## 9:17 403 mV TW4‐21_02232021
TW4‐21 Temperatu ######## 9:17 15.39 deg C TW4‐21_02232021
TW4‐21 Turbidity ######## 9:17 0 NTU TW4‐21_02232021
TW4‐22 Conductivit ######## 9:43 5393 umhos/cm TW4‐22_02232021
TW4‐22 Dissolved O ######## 9:43 96 % TW4‐22_02232021
TW4‐22 pH ######## 9:43 6.98 pH Units TW4‐22_02232021
TW4‐22 Redox ######## 9:43 428 mV TW4‐22_02232021
TW4‐22 Temperatu ######## 9:43 15.34 deg C TW4‐22_02232021
TW4‐22 Turbidity ######## 9:43 0 NTU TW4‐22_02232021
TW4‐23 Conductivit ######## 14:37 3560 umhos/cm TW4‐23_03172021
TW4‐23 Conductivit ######## 14:38 3572 umhos/cm TW4‐23_03172021
TW4‐23 Conductivit ######## 14:39 3587 umhos/cm TW4‐23_03172021
TW4‐23 Conductivit ######## 14:40 3589 umhos/cm TW4‐23_03172021
TW4‐23 Dissolved O ######## 14:37 11 % TW4‐23_03172021
TW4‐23 Dissolved O ######## 14:38 13 % TW4‐23_03172021
TW4‐23 Dissolved O ######## 14:39 14.1 % TW4‐23_03172021
TW4‐23 Dissolved O ######## 14:40 14 % TW4‐23_03172021
TW4‐23 pH ######## 14:37 6.76 pH Units TW4‐23_03172021
TW4‐23 pH ######## 14:38 6.8 pH Units TW4‐23_03172021
TW4‐23 pH ######## 14:39 6.83 pH Units TW4‐23_03172021
TW4‐23 pH ######## 14:40 6.84 pH Units TW4‐23_03172021
TW4‐23 Redox ######## 14:37 307 mV TW4‐23_03172021
TW4‐23 Redox ######## 14:38 297 mV TW4‐23_03172021
TW4‐23 Redox ######## 14:39 291 mV TW4‐23_03172021
TW4‐23 Redox ######## 14:40 290 mV TW4‐23_03172021
TW4‐23 Temperatu ######## 14:37 14.36 deg C TW4‐23_03172021
TW4‐23 Temperatu ######## 14:38 14.36 deg C TW4‐23_03172021
TW4‐23 Temperatu ######## 14:39 14.3 deg C TW4‐23_03172021
TW4‐23 Temperatu ######## 14:40 14.41 deg C TW4‐23_03172021
TW4‐23 Turbidity ######## 14:37 3 NTU TW4‐23_03172021
TW4‐23 Turbidity ######## 14:38 3.1 NTU TW4‐23_03172021
TW4‐23 Turbidity ######## 14:39 3.2 NTU TW4‐23_03172021
TW4‐23 Turbidity ######## 14:40 3.3 NTU TW4‐23_03172021
TW4‐24 Conductivit ######## 9:36 8723 umhos/cm TW4‐24_02232021
TW4‐24 Dissolved O ######## 9:36 37.7 % TW4‐24_02232021
TW4‐24 pH ######## 9:36 6.9 pH Units TW4‐24_02232021
TW4‐24 Redox ######## 9:36 433 mV TW4‐24_02232021
TW4‐24 Temperatu ######## 9:36 15.09 deg C TW4‐24_02232021
TW4‐24 Turbidity ######## 9:36 3 NTU TW4‐24_02232021
TW4‐25 Conductivit ######## 9:25 2626 umhos/cm TW4‐25_02232021
TW4‐25 Dissolved O ######## 9:25 38.1 % TW4‐25_02232021
TW4‐25 pH ######## 9:25 6.95 pH Units TW4‐25_02232021
TW4‐25 Redox ######## 9:25 413 mV TW4‐25_02232021
Loc ID Measurem Measurem GW MeasuDry
MW‐01 ######## 1429 64.71 N
MW‐02 ######## 1318 109.41 N
MW‐03A ######## 1300 83.47 N
MW‐05 ######## 1211 108.08 N
MW‐11 ######## 739 84.99 N
MW‐12 ######## 1215 109.6 N
MW‐14 ######## 1006 101.6 N
MW‐15 ######## 1009 105.23 N
MW‐17 ######## 1305 71.74 N
MW‐18 ######## 1424 73.4 N
MW‐19 ######## 1352 65.5 N
MW‐20 ######## 715 85.01 N
MW‐22 ######## 656 66.1 N
MW‐23 ######## 1219 113.86 N
MW‐24 ######## 1204 111.24 N
MW‐24A ######## 1201 110.18 N
MW‐25 ######## 742 80.72 N
MW‐26 ######## 937 74.08 N
MW‐27 ######## 1052 57.31 N
MW‐28 ######## 1151 74.28 N
MW‐29 ######## 1156 107.03 N
MW‐30 ######## 826 75.05 N
MW‐31 ######## 1001 68.87 N
MW‐32 ######## 957 81.6 N
MW‐33 ######## 1230 Y
MW‐34 ######## 1015 107.36 N
MW‐35 ######## 1223 112.11 N
MW‐36 ######## 1226 110.33 N
MW‐37 ######## 1012 105.98 N
MW‐38 ######## 701 70.32 N
MW‐39 ######## 704 64.66 N
MW‐40 ######## 804 79.56 N
MW‐04 ######## 906 82.63 N
TW4‐01 ######## 900 105.11 N
TW4‐02 ######## 909 111.3 N
TW4‐03 ######## 921 63.92 N
TW4‐04 ######## 853 79.51 N
TW4‐05 ######## 930 71.46 N
TW4‐06 ######## 850 78.58 N
TW4‐07 ######## 903 82.04 N
TW4‐08 ######## 917 86.48 N
TW4‐09 ######## 927 69.41 N
TW4‐10 ######## 933 68.78 N
TW4‐11 ######## 913 90.08 N
TW4‐12 ######## 837 55.24 N
TW4‐13 ######## 834 56.28 N
TW4‐14 ######## 828 77.22 N
TW4‐16 ######## 953 73.27 N
TW4‐18 ######## 1045 72.55 N
TW4‐19 ######## 1058 73.15 N
TW4‐21 ######## 1048 70.71 N
TW4‐22 ######## 947 68.81 N
TW4‐23 ######## 746 75.05 N
TW4‐24 ######## 950 69.94 N
TW4‐25 ######## 1039 70.01 N
TW4‐26 ######## 750 73.29 N
TW4‐27 ######## 809 78.73 N
TW4‐28 ######## 840 48.68 N
TW4‐29 ######## 825 77.91 N
TW4‐30 ######## 815 74.85 N
TW4‐31 ######## 812 75.99 N
TW4‐32 ######## 843 55.65 N
TW4‐33 ######## 806 77.66 N
TW4‐34 ######## 822 76.24 N
TW4‐35 ######## 818 75.38 N
TW4‐36 ######## 831 57.75 N
TW4‐37 ######## 943 69.19 N
TW4‐38 ######## 924 59.45 N
TW4‐39 ######## 940 72.25 N
TW4‐40 ######## 753 71.41 N
TW4‐41 ######## 856 89.22 N
TW4‐42 ######## 803 69.18 N
PIEZ‐01 ######## 1356 66.84 N
PIEZ‐02 ######## 1347 45.4 N
PIEZ‐03A ######## 1340 56.57 N
PIEZ‐04 ######## 756 66.57 N
PIEZ‐05 ######## 800 65.35 N
TWN‐01 ######## 1042 68.58 N
TWN‐02 ######## 1036 58.12 N
TWN‐03 ######## 1327 42.88 N
TWN‐04 ######## 1335 61.58 N
TWN‐06 ######## 1421 80.21 N
TWN‐07 ######## 1434 81.08 N
TWN‐14 ######## 1407 59.39 N
TWN‐16 ######## 1412 47.46 N
TWN‐18 ######## 1331 62.09 N
TWN‐19 ######## 813 53.61 N
DR‐05 ######## 804 83.05 N
DR‐06 ######## 801 94.08 N
DR‐07 ######## 1235 91.73 N
DR‐08 ######## 756 51.25 N
DR‐09 ######## 753 86.43 N
DR‐10 ######## 751 78.33 N
DR‐11 ######## 1253 97.92 N
DR‐12 ######## 1249 91.88 N
DR‐13 ######## 1244 69.5 N
DR‐14 ######## 746 76.04 N
DR‐15 ######## 710 92.78 N
DR‐17 ######## 743 64.49 N
DR‐19 ######## 731 63.23 N
DR‐20 ######## 728 55.32 N
DR‐21 ######## 720 100.44 N
DR‐22 ######## 735 Y
DR‐23 ######## 724 70.25 N
DR‐24 ######## 738 44.28 N
TW4‐25 Temperatu ######## 9:25 15.09 deg C TW4‐25_02232021
TW4‐25 Turbidity ######## 9:25 0 NTU TW4‐25_02232021
TW4‐26 Conductivit ######## 10:45 4601 umhos/cm TW4‐26_03242021
TW4‐26 Dissolved O ######## 10:45 91 % TW4‐26_03242021
TW4‐26 pH ######## 10:45 6.53 pH Units TW4‐26_03242021
TW4‐26 Redox ######## 10:45 411 mV TW4‐26_03242021
TW4‐26 Temperatu ######## 10:45 14.58 deg C TW4‐26_03242021
TW4‐26 Turbidity ######## 10:45 21 NTU TW4‐26_03242021
TW4‐26 Conductivit ######## 8:57 4643 umhos/cm TW4‐26_03242021
TW4‐26 Conductivit ######## 8:58 4646 umhos/cm TW4‐26_03242021
TW4‐26 pH ######## 8:57 7.06 pH Units TW4‐26_03242021
TW4‐26 pH ######## 8:58 7.06 pH Units TW4‐26_03242021
TW4‐26 Temperatu ######## 8:57 13.34 deg C TW4‐26_03242021
TW4‐26 Temperatu ######## 8:58 13.36 deg C TW4‐26_03242021
TW4‐27 Conductivit ######## 11:03 5252 umhos/cm TW4‐27_03182021
TW4‐27 Dissolved O ######## 11:03 42 % TW4‐27_03182021
TW4‐27 pH ######## 11:03 6.61 pH Units TW4‐27_03182021
TW4‐27 Redox ######## 11:03 455 mV TW4‐27_03182021
TW4‐27 Temperatu ######## 11:03 14.9 deg C TW4‐27_03182021
TW4‐27 Turbidity ######## 11:03 14.5 NTU TW4‐27_03182021
TW4‐27 Conductivit ######## 8:44 5151 umhos/cm TW4‐27_03182021
TW4‐27 Conductivit ######## 8:45 5160 umhos/cm TW4‐27_03182021
TW4‐27 pH ######## 8:44 6.55 pH Units TW4‐27_03182021
TW4‐27 pH ######## 8:45 6.55 pH Units TW4‐27_03182021
TW4‐27 Temperatu ######## 8:44 14.06 deg C TW4‐27_03182021
TW4‐27 Temperatu ######## 8:45 14.08 deg C TW4‐27_03182021
TW4‐28 Conductivit ######## 9:50 1561 umhos/cm TW4‐28_03172021
TW4‐28 Dissolved O ######## 9:50 69.5 % TW4‐28_03172021
TW4‐28 pH ######## 9:50 7.1 pH Units TW4‐28_03172021
TW4‐28 Redox ######## 9:50 516 mV TW4‐28_03172021
TW4‐28 Temperatu ######## 9:50 14.55 deg C TW4‐28_03172021
TW4‐28 Turbidity ######## 9:50 9.5 NTU TW4‐28_03172021
TW4‐28 Conductivit ######## 7:56 1655 umhos/cm TW4‐28_03172021
TW4‐28 Conductivit ######## 7:58 1660 umhos/cm TW4‐28_03172021
TW4‐28 pH ######## 7:56 7.52 pH Units TW4‐28_03172021
TW4‐28 pH ######## 7:58 7.55 pH Units TW4‐28_03172021
TW4‐28 Temperatu ######## 7:56 13.07 deg C TW4‐28_03172021
TW4‐28 Temperatu ######## 7:58 13.14 deg C TW4‐28_03172021
TW4‐29 Conductivit ######## 9:13 4156 umhos/cm TW4‐29_03242021
TW4‐29 Dissolved O ######## 9:13 93 % TW4‐29_03242021
TW4‐29 pH ######## 9:13 6.59 pH Units TW4‐29_03242021
TW4‐29 Redox ######## 9:13 412 mV TW4‐29_03242021
TW4‐29 Temperatu ######## 9:13 14.58 deg C TW4‐29_03242021
TW4‐29 Turbidity ######## 9:13 4.7 NTU TW4‐29_03242021
TW4‐29 Conductivit ######## 8:25 4052 umhos/cm TW4‐29_03242021
TW4‐29 Conductivit ######## 8:26 4042 umhos/cm TW4‐29_03242021
TW4‐29 pH ######## 8:25 6.47 pH Units TW4‐29_03242021
TW4‐29 pH ######## 8:26 6.48 pH Units TW4‐29_03242021
TW4‐29 Temperatu ######## 8:25 14.46 deg C TW4‐29_03242021
TW4‐29 Temperatu ######## 8:26 14.5 deg C TW4‐29_03242021
TW4‐30 Conductivit ######## 14:30 4698 umhos/cm TW4‐30_03182021
TW4‐30 Dissolved O ######## 14:30 52 % TW4‐30_03182021
TW4‐30 pH ######## 14:30 5.69 pH Units TW4‐30_03182021
TW4‐30 Redox ######## 14:30 457 mV TW4‐30_03182021
TW4‐30 Temperatu ######## 14:30 14.98 deg C TW4‐30_03182021
TW4‐30 Turbidity ######## 14:30 52 NTU TW4‐30_03182021
TW4‐30 Conductivit ######## 9:44 4522 umhos/cm TW4‐30_03182021
TW4‐30 Conductivit ######## 9:45 4539 umhos/cm TW4‐30_03182021
TW4‐30 pH ######## 9:44 6 pH Units TW4‐30_03182021
TW4‐30 pH ######## 9:45 5.99 pH Units TW4‐30_03182021
TW4‐30 Temperatu ######## 9:44 13.53 deg C TW4‐30_03182021
TW4‐30 Temperatu ######## 9:45 13.57 deg C TW4‐30_03182021
TW4‐31 Conductivit ######## 13:07 4010 umhos/cm TW4‐31_03172021
TW4‐31 Dissolved O ######## 13:07 24.2 % TW4‐31_03172021
TW4‐31 pH ######## 13:07 6.67 pH Units TW4‐31_03172021
TW4‐31 Redox ######## 13:07 424 mV TW4‐31_03172021
TW4‐31 Temperatu ######## 13:07 15 deg C TW4‐31_03172021
TW4‐31 Turbidity ######## 13:07 68.4 NTU TW4‐31_03172021
TW4‐31 Conductivit ######## 8:34 4038 umhos/cm TW4‐31_03172021
TW4‐31 Conductivit ######## 8:35 4040 umhos/cm TW4‐31_03172021
TW4‐31 pH ######## 8:34 7.01 pH Units TW4‐31_03172021
TW4‐31 pH ######## 8:35 7.01 pH Units TW4‐31_03172021
TW4‐31 Temperatu ######## 8:34 13.45 deg C TW4‐31_03172021
TW4‐31 Temperatu ######## 8:35 13.5 deg C TW4‐31_03172021
TW4‐32 Conductivit ######## 10:28 6590 umhos/cm TW4‐32_03172021
TW4‐32 Conductivit ######## 10:29 6615 umhos/cm TW4‐32_03172021
TW4‐32 Conductivit ######## 10:30 6615 umhos/cm TW4‐32_03172021
TW4‐32 Conductivit ######## 10:31 6612 umhos/cm TW4‐32_03172021
TW4‐32 Dissolved O ######## 10:28 2.2 % TW4‐32_03172021
TW4‐32 Dissolved O ######## 10:29 2.1 % TW4‐32_03172021
TW4‐32 Dissolved O ######## 10:30 2.1 % TW4‐32_03172021
TW4‐32 Dissolved O ######## 10:31 2.2 % TW4‐32_03172021
TW4‐32 pH ######## 10:28 3.85 pH Units TW4‐32_03172021
TW4‐32 pH ######## 10:29 3.87 pH Units TW4‐32_03172021
TW4‐32 pH ######## 10:30 3.88 pH Units TW4‐32_03172021
TW4‐32 pH ######## 10:31 3.89 pH Units TW4‐32_03172021
TW4‐32 Redox ######## 10:28 512 mV TW4‐32_03172021
TW4‐32 Redox ######## 10:29 512 mV TW4‐32_03172021
TW4‐32 Redox ######## 10:30 512 mV TW4‐32_03172021
TW4‐32 Redox ######## 10:31 511 mV TW4‐32_03172021
TW4‐32 Temperatu ######## 10:28 14.7 deg C TW4‐32_03172021
TW4‐32 Temperatu ######## 10:29 14.71 deg C TW4‐32_03172021
TW4‐32 Temperatu ######## 10:30 14.74 deg C TW4‐32_03172021
TW4‐32 Temperatu ######## 10:31 14.73 deg C TW4‐32_03172021
TW4‐32 Turbidity ######## 10:28 4.3 NTU TW4‐32_03172021
TW4‐32 Turbidity ######## 10:29 4 NTU TW4‐32_03172021
TW4‐32 Turbidity ######## 10:30 3.9 NTU TW4‐32_03172021
TW4‐32 Turbidity ######## 10:31 3.8 NTU TW4‐32_03172021
TW4‐33 Conductivit ######## 14:01 5000 umhos/cm TW4‐33_03182021
TW4‐33 Dissolved O ######## 14:01 61 % TW4‐33_03182021
TW4‐33 pH ######## 14:01 7.02 pH Units TW4‐33_03182021
TW4‐33 Redox ######## 14:01 432 mV TW4‐33_03182021
TW4‐33 Temperatu ######## 14:01 15.24 deg C TW4‐33_03182021
TW4‐33 Turbidity ######## 14:01 13 NTU TW4‐33_03182021
TW4‐33 Conductivit ######## 9:35 4841 umhos/cm TW4‐33_03182021
TW4‐33 Conductivit ######## 9:36 4842 umhos/cm TW4‐33_03182021
TW4‐33 pH ######## 9:35 7.03 pH Units TW4‐33_03182021
TW4‐33 pH ######## 9:36 7.06 pH Units TW4‐33_03182021
TW4‐33 Temperatu ######## 9:35 12.42 deg C TW4‐33_03182021
TW4‐33 Temperatu ######## 9:36 12.48 deg C TW4‐33_03182021
TW4‐34 Conductivit ######## 13:36 3634 umhos/cm TW4‐34_03172021
TW4‐34 Dissolved O ######## 13:36 11 % TW4‐34_03172021
TW4‐34 pH ######## 13:36 6.59 pH Units TW4‐34_03172021
TW4‐34 Redox ######## 13:36 435 mV TW4‐34_03172021
TW4‐34 Temperatu ######## 13:36 14.8 deg C TW4‐34_03172021
TW4‐34 Turbidity ######## 13:36 17 NTU TW4‐34_03172021
TW4‐34 Conductivit ######## 8:42 3640 umhos/cm TW4‐34_03172021
TW4‐34 Conductivit ######## 8:43 3642 umhos/cm TW4‐34_03172021
TW4‐34 pH ######## 8:42 7.08 pH Units TW4‐34_03172021
TW4‐34 pH ######## 8:43 7.08 pH Units TW4‐34_03172021
TW4‐34 Temperatu ######## 8:42 13.2 deg C TW4‐34_03172021
TW4‐34 Temperatu ######## 8:43 13.25 deg C TW4‐34_03172021
TW4‐35 Conductivit ######## 14:05 4516 umhos/cm TW4‐35_03172021
TW4‐35 Dissolved O ######## 14:05 42 % TW4‐35_03172021
TW4‐35 pH ######## 14:05 6.4 pH Units TW4‐35_03172021
TW4‐35 Redox ######## 14:05 393 mV TW4‐35_03172021
TW4‐35 Temperatu ######## 14:05 14.54 deg C TW4‐35_03172021
TW4‐35 Turbidity ######## 14:05 12.7 NTU TW4‐35_03172021
TW4‐35 Conductivit ######## 8:50 4478 umhos/cm TW4‐35_03172021
TW4‐35 Conductivit ######## 8:51 4478 umhos/cm TW4‐35_03172021
TW4‐35 pH ######## 8:50 6.75 pH Units TW4‐35_03172021
TW4‐35 pH ######## 8:51 6.74 pH Units TW4‐35_03172021
TW4‐35 Temperatu ######## 8:50 13.1 deg C TW4‐35_03172021
TW4‐35 Temperatu ######## 8:51 13.2 deg C TW4‐35_03172021
TW4‐36 Conductivit ######## 12:36 2470 umhos/cm TW4‐36_03172021
TW4‐36 Dissolved O ######## 12:36 3.5 % TW4‐36_03172021
TW4‐36 pH ######## 12:36 6.75 pH Units TW4‐36_03172021
TW4‐36 Redox ######## 12:36 276 mV TW4‐36_03172021
TW4‐36 Temperatu ######## 12:36 15 deg C TW4‐36_03172021
TW4‐36 Turbidity ######## 12:36 45.9 NTU TW4‐36_03172021
TW4‐36 Conductivit ######## 8:26 2481 umhos/cm TW4‐36_03172021
TW4‐36 Conductivit ######## 8:27 2480 umhos/cm TW4‐36_03172021
TW4‐36 pH ######## 8:26 7.05 pH Units TW4‐36_03172021
TW4‐36 pH ######## 8:27 7.04 pH Units TW4‐36_03172021
TW4‐36 Temperatu ######## 8:26 13.45 deg C TW4‐36_03172021
TW4‐36 Temperatu ######## 8:27 13.49 deg C TW4‐36_03172021
TW4‐37 Conductivit ######## 9:52 3570 umhos/cm TW4‐37_02232021
TW4‐37 Dissolved O ######## 9:52 96 % TW4‐37_02232021
TW4‐37 pH ######## 9:52 7.03 pH Units TW4‐37_02232021
TW4‐37 Redox ######## 9:52 417 mV TW4‐37_02232021
TW4‐37 Temperatu ######## 9:52 15.47 deg C TW4‐37_02232021
TW4‐37 Turbidity ######## 9:52 0 NTU TW4‐37_02232021
TW4‐38 Conductivit ######## 9:35 1957 umhos/cm TW4‐38_03182021
TW4‐38 Conductivit ######## 9:36 1912 umhos/cm TW4‐38_03182021
TW4‐38 Conductivit ######## 9:37 1901 umhos/cm TW4‐38_03182021
TW4‐38 Conductivit ######## 9:38 1934 umhos/cm TW4‐38_03182021
TW4‐38 Dissolved O ######## 9:35 70 % TW4‐38_03182021
TW4‐38 Dissolved O ######## 9:36 66 % TW4‐38_03182021
TW4‐38 Dissolved O ######## 9:37 65 % TW4‐38_03182021
TW4‐38 Dissolved O ######## 9:38 63 % TW4‐38_03182021
TW4‐38 pH ######## 9:35 6.65 pH Units TW4‐38_03182021
TW4‐38 pH ######## 9:36 6.71 pH Units TW4‐38_03182021
TW4‐38 pH ######## 9:37 6.73 pH Units TW4‐38_03182021
TW4‐38 pH ######## 9:38 6.78 pH Units TW4‐38_03182021
TW4‐38 Redox ######## 9:35 475 mV TW4‐38_03182021
TW4‐38 Redox ######## 9:36 474 mV TW4‐38_03182021
TW4‐38 Redox ######## 9:37 469 mV TW4‐38_03182021
TW4‐38 Redox ######## 9:38 463 mV TW4‐38_03182021
TW4‐38 Temperatu ######## 9:35 14.59 deg C TW4‐38_03182021
TW4‐38 Temperatu ######## 9:36 13.63 deg C TW4‐38_03182021
TW4‐38 Temperatu ######## 9:37 14.64 deg C TW4‐38_03182021
TW4‐38 Temperatu ######## 9:38 14.66 deg C TW4‐38_03182021
TW4‐38 Turbidity ######## 9:35 12 NTU TW4‐38_03182021
TW4‐38 Turbidity ######## 9:36 14 NTU TW4‐38_03182021
TW4‐38 Turbidity ######## 9:37 15 NTU TW4‐38_03182021
TW4‐38 Turbidity ######## 9:38 15 NTU TW4‐38_03182021
TW4‐39 Conductivit ######## 10:00 2209 umhos/cm TW4‐39_02232021
TW4‐39 Dissolved O ######## 10:00 42.5 % TW4‐39_02232021
TW4‐39 pH ######## 10:00 7.1 pH Units TW4‐39_02232021
TW4‐39 Redox ######## 10:00 438 mV TW4‐39_02232021
TW4‐39 Temperatu ######## 10:00 15.05 deg C TW4‐39_02232021
TW4‐39 Turbidity ######## 10:00 1.5 NTU TW4‐39_02232021
TW4‐40 Conductivit ######## 12:43 4079 umhos/cm TW4‐40_02232021
TW4‐40 Dissolved O ######## 12:43 110 % TW4‐40_02232021
TW4‐40 pH ######## 12:43 6.84 pH Units TW4‐40_02232021
TW4‐40 Redox ######## 12:43 441 mV TW4‐40_02232021
TW4‐40 Temperatu ######## 12:43 14.81 deg C TW4‐40_02232021
TW4‐40 Turbidity ######## 12:43 2.8 NTU TW4‐40_02232021
TW4‐41 Conductivit ######## 12:26 2745 umhos/cm TW4‐41_02232021
TW4‐41 Dissolved O ######## 12:26 96 % TW4‐41_02232021
TW4‐41 pH ######## 12:26 7.13 pH Units TW4‐41_02232021
TW4‐41 Redox ######## 12:26 421 mV TW4‐41_02232021
TW4‐41 Temperatu ######## 12:26 15.8 deg C TW4‐41_02232021
TW4‐41 Turbidity ######## 12:26 0 NTU TW4‐41_02232021
TW4‐42 Conductivit ######## 9:14 3735 umhos/cm TW4‐42_03172021
TW4‐42 Dissolved O ######## 9:14 98 % TW4‐42_03172021
TW4‐42 pH ######## 9:14 6.92 pH Units TW4‐42_03172021
TW4‐42 Redox ######## 9:14 496 mV TW4‐42_03172021
TW4‐42 Temperatu ######## 9:14 13.5 deg C TW4‐42_03172021
TW4‐42 Turbidity ######## 9:14 0.7 NTU TW4‐42_03172021
TW4‐42 Conductivit ######## 7:46 1086 umhos/cm TW4‐42_03172021
TW4‐42 Conductivit ######## 7:48 1130 umhos/cm TW4‐42_03172021
TW4‐42 pH ######## 7:46 7.03 pH Units TW4‐42_03172021
TW4‐42 pH ######## 7:48 7.04 pH Units TW4‐42_03172021
TW4‐42 Temperatu ######## 7:46 13.76 deg C TW4‐42_03172021
TW4‐42 Temperatu ######## 7:48 13.81 deg C TW4‐42_03172021
TW4‐60 Conductivit ######## 7:59 2.1 umhos/cm TW4‐60_02232021
TW4‐60 Dissolved O ######## 7:59 16.5 % TW4‐60_02232021
TW4‐60 pH ######## 7:59 7.36 pH Units TW4‐60_02232021
TW4‐60 Redox ######## 7:59 544 mV TW4‐60_02232021
TW4‐60 Temperatu ######## 7:59 16.48 deg C TW4‐60_02232021
TW4‐60 Turbidity ######## 7:59 5 NTU TW4‐60_02232021
ClientSampSampID CollectionDPrepDate AnalDate Matrix Analyte CAS DF Rslt
LCS VOC‐1 022621A ########    Surr: 1,2‐17060‐07‐0 1 105
LCS VOC‐1 022621A ########    Surr: 4‐B 460‐00‐4 1 97.4
LCS VOC‐1 022621A ########    Surr: Dib1868‐53‐7 1 106
LCS VOC‐1 022621A ########    Surr: Tolu2037‐26‐5 1 102
LCS VOC‐1 022621A ######## Carbon tetr56‐23‐5 1 18.6
LCS VOC‐1 022621A ######## Chloroform67‐66‐3 1 20.3
LCS VOC‐1 022621A ######## Chlorometh74‐87‐3 1 14.8
LCS VOC‐1 022621A ######## Methylene 75‐09‐2 1 19.7
LCS VOC‐2 022621A ########    Surr: 1,2‐17060‐07‐0 1 101
LCS VOC‐2 022621A ########    Surr: 4‐B 460‐00‐4199
LCS VOC‐2 022621A ########    Surr: Dib1868‐53‐7 1 106
LCS VOC‐2 022621A ########    Surr: Tolu2037‐26‐5 1 104
LCS VOC‐2 022621A ######## Chloroform67‐66‐3 1 19.4
LCS‐R149229 3/1/2021 Nitrate/Nit 7727‐37‐9 1 1.02
LCS‐R149373 3/2/2021 Chloride 16887‐00‐6 1 5.07
LCS‐R149453 3/6/2021 Chloride 16887‐00‐6 1 5.39
LCS‐R149514 3/8/2021 Chloride 16887‐00‐6 1 4.99
MB VOC‐1 022621A ########    Surr: 1,2‐17060‐07‐0 1 109
MB VOC‐1 022621A ########    Surr: 4‐B 460‐00‐4 1 99.7
MB VOC‐1 022621A ########    Surr: Dib1868‐53‐7 1 109
MB VOC‐1 022621A ########    Surr: Tolu2037‐26‐5 1 105
MB VOC‐1 022621A ######## Carbon tetr56‐23‐510
MB VOC‐1 022621A ######## Chloroform67‐66‐310
MB VOC‐1 022621A ######## Chlorometh74‐87‐310
MB VOC‐1 022621A ######## Methylene 75‐09‐210
MB VOC‐2 022621A ########    Surr: 1,2‐17060‐07‐0 1 100
MB VOC‐2 022621A ########    Surr: 4‐B 460‐00‐4 1 101
MB VOC‐2 022621A ########    Surr: Dib1868‐53‐7 1 101
MB VOC‐2 022621A ########    Surr: Tolu2037‐26‐5 1 103
MB VOC‐2 022621A ######## Chloroform67‐66‐310
MB‐R149229 3/1/2021 Nitrate/Nit 7727‐37‐910
MB‐R149373 3/2/2021 Chloride 16887‐00‐6 10
MB‐R149453 3/6/2021 Chloride 16887‐00‐6 10
MB‐R149514 3/8/2021 Chloride 16887‐00‐6 10
MW‐04_022102631‐0 ######## 3/6/2021 Aqueous Chloride 16887‐00‐6 10 46.5
MW‐04_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 4.61
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 117
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 89.8
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 118
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 103
MW‐04_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
MW‐04_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
MW‐04_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 99.4
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 101
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 99.5
MW‐04_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 103
MW‐04_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 1,150
MW‐26_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 20 59.5
MW‐26_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 0.349
MW‐26_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 114
MW‐26_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4192
MW‐26_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 113
MW‐26_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 101
MW‐26_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
MW‐26_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
MW‐26_022102631‐00######## ######## Aqueous Methylene 75‐09‐2 1 3.46
MW‐26_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 98.7
MW‐26_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 101
MW‐26_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 100 103
MW‐26_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 104
MW‐26_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 100 3,060
Trip Blank 2102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
Trip Blank 2102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 94.7
Trip Blank 2102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 111
Trip Blank 2102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 102
Trip Blank 2102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
Trip Blank 2102631‐0 ######## ######## Aqueous Chloroform67‐66‐310
Trip Blank 2102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
Trip Blank 2102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐01_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 10 45.4
TW4‐01_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 2.72
TW4‐01_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 114
TW4‐01_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 96.9
TW4‐01_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 115
TW4‐01_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 104
TW4‐01_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐01_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐01_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐01_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 99.9
TW4‐01_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 102
TW4‐01_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 10 102
TW4‐01_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 104
TW4‐01_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 10 948
TW4‐02_022102631‐0 ######## 3/6/2021 Aqueous Chloride 16887‐00‐6 10 43.3
TW4‐02_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 3.3
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 118
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 98.1
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 118
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 105
TW4‐02_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐02_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐02_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 99.2
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 101
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 102
TW4‐02_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 104
TW4‐02_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 939
TW4‐04_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 10 39.8
TW4‐04_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 6.75
TW4‐04_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 109
TW4‐04_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 88.1
TW4‐04_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 108
TW4‐04_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5197
TW4‐04_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐04_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐04_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐04_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 101
TW4‐04_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 103
TW4‐04_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 100 101
TW4‐04_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 105
TW4‐04_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 100 1,130
TW4‐11_022102631‐0 ######## 3/6/2021 Aqueous Chloride 16887‐00‐6 10 49.5
TW4‐11_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 7.21
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 111
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 91.1
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 111
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 98.1
TW4‐11_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐11_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐11_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 101
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 103
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 100
TW4‐11_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 105
TW4‐11_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 2,750
TW4‐19_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 50 167
TW4‐19_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 10 6.61
TW4‐19_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 114
TW4‐19_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 98.4
TW4‐19_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 114
TW4‐19_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 104
TW4‐19_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐5 1 8.4
TW4‐19_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐19_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐19_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 119
TW4‐19_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 92.8
TW4‐19_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 100 118
TW4‐19_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 104
TW4‐19_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 100 6,660
TW4‐21_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 100 454
TW4‐21_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 20 15.2
TW4‐21_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 116
TW4‐21_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4196
TW4‐21_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 115
TW4‐21_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 102
TW4‐21_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐21_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐21_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐21_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 100
TW4‐21_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 101
TW4‐21_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 10 101
TW4‐21_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 104
TW4‐21_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 10 400
TW4‐22_022102631‐0 ######## 3/6/2021 Aqueous Chloride 16887‐00‐6 100 618
TW4‐22_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 100 69.6
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 117
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 94.9
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 116
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 103
TW4‐22_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐22_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐22_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 101
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 103
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 101
TW4‐22_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 105
TW4‐22_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 5,100
TW4‐24_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 100 1,170
TW4‐24_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 50 41.9
TW4‐24_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
TW4‐24_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 100
TW4‐24_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 111
TW4‐24_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 104
TW4‐24_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐24_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 1 96.2
TW4‐24_022102631‐00######## ######## Aqueous Chlorometh74‐87‐3 1 3.6
TW4‐24_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐25_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 20 100
TW4‐25_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 3.43
TW4‐25_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 110
TW4‐25_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 97.9
TW4‐25_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 109
TW4‐25_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 105
TW4‐25_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐25_022102631‐00######## ######## Aqueous Chloroform67‐66‐310
TW4‐25_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐25_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐37_022102631‐0 ######## 3/6/2021 Aqueous Chloride 16887‐00‐6 50 242
TW4‐37_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 50 26.9
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 116
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4192
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 116
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 103
TW4‐37_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐37_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐37_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 100
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 97.9
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 103
TW4‐37_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 104
TW4‐37_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 9,380
TW4‐39_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 20 53
TW4‐39_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 2.12
TW4‐39_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 113
TW4‐39_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 96.3
TW4‐39_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 113
TW4‐39_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 103
TW4‐39_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐39_022102631‐00######## ######## Aqueous Chlorometh74‐87‐310
TW4‐39_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐39_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 119
TW4‐39_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 95.8
TW4‐39_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 100 117
TW4‐39_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 105
TW4‐39_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 100 2,970
TW4‐40_022102631‐00######## 3/3/2021 Aqueous Chloride 16887‐00‐6 10 36
TW4‐40_022102631‐00######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 2.43
TW4‐40_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 110
TW4‐40_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 90.4
TW4‐40_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 1 110
TW4‐40_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 101
TW4‐40_022102631‐00######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐40_022102631‐00######## ######## Aqueous Chlorometh74‐87‐3 1 3.51
TW4‐40_022102631‐00######## ######## Aqueous Methylene 75‐09‐210
TW4‐40_022102631‐00######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 10 118
TW4‐40_022102631‐00######## ######## Aqueous     Surr: 4‐B 460‐00‐4 10 95.2
TW4‐40_022102631‐00######## ######## Aqueous     Surr: Dib1868‐53‐7 10 116
TW4‐40_022102631‐00######## ######## Aqueous     Surr: Tolu2037‐26‐5 10 105
TW4‐40_022102631‐00######## ######## Aqueous Chloroform67‐66‐3 10 436
TW4‐41_022102631‐0 ######## 3/3/2021 Aqueous Chloride 16887‐00‐6 10 40.6
TW4‐41_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐9 5 6.41
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 115
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 91.6
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 116
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 101
TW4‐41_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐41_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐41_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 100 98.4
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 100 100
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 100 100
TW4‐41_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 100 105
TW4‐41_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐3 100 1,170
TW4‐60_022102631‐0 ######## 3/8/2021 Aqueous Chloride 16887‐00‐6 10
TW4‐60_022102631‐0 ######## 3/1/2021 Aqueous Nitrate/Nit 7727‐37‐910
TW4‐60_022102631‐0 ######## ######## Aqueous     Surr: 1,2‐17060‐07‐0 1 106
TW4‐60_022102631‐0 ######## ######## Aqueous     Surr: 4‐B 460‐00‐4 1 91.9
TW4‐60_022102631‐0 ######## ######## Aqueous     Surr: Dib1868‐53‐7 1 103
TW4‐60_022102631‐0 ######## ######## Aqueous     Surr: Tolu2037‐26‐5 1 97.3
TW4‐60_022102631‐0 ######## ######## Aqueous Carbon tetr56‐23‐510
TW4‐60_022102631‐0 ######## ######## Aqueous Chloroform67‐66‐310
TW4‐60_022102631‐0 ######## ######## Aqueous Chlorometh74‐87‐310
TW4‐60_022102631‐0 ######## ######## Aqueous Methylene 75‐09‐210
PQL Units Qual TestCode TextRslt ReceivedDaSampleTemp
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
0.01 mg/L NO2/NO3‐W‐353.2
0.1 mg/L 300.0‐W
0.1 mg/L 300.0‐W
0.1 mg/L 300.0‐W
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
%Rec 8260D‐W‐DEN100
1 µg/L 8260D‐W‐DEN100
0.01 mg/L NO2/NO3‐W‐353.2
0.1 mg/L 300.0‐W
0.1 mg/L 300.0‐W
0.1 mg/L 300.0‐W
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
2 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
5 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
10 mg/L 300.0‐W ######## 1.4°C
0.2 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
10 mg/L 300.0‐W ######## 1.4°C
1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
10 mg/L 300.0‐W ######## 1.4°C
0.5 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
2 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
5 mg/L 300.0‐W ######## 1.4°C
0.5 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
2 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
10 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
100 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 mg/L 300.0‐W ######## 1.4°C
0.1 mg/L NO2/NO3‐W‐353.2 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
%Rec 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C
1 µg/L 8260D‐W‐DEN100 ######## 1.4°C