DRC-2016-013063 - 0901a06880dbde45

SERGYFUELS
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.energyfuels.com
May 19, 2016 Div of Waste Management
and Radiation Control
Sent VIA OVERNIGHT DELIVERY MAY 2 3 2016
Mr. Scott Anderson
Director 'Wimy-DDim
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84114-4820
Re: Transmittal of 1st Quarter 2016 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Mr. Anderson:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 1st Quarter of
2016 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs
each containing a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Energy Fuels Resources (USA) Inc.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Harold R. Roberts
David E. Turk
Logan Shumway
Scott Bakken
Yours very truly.
May 19, 2016
Sent VIA OVERNIGHT DELIVERY
Mr. Scott Anderson
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84114-4820
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www .energyfuels.com
Re: Transmittal of 1st Quarter 2016 Routine Chloroform Monitoring Report
UDEQ Docket No. UGW-20-01 White Mesa Uranium Mill
Dear Mr. Anderson:
Enclosed are two copies of the White Mesa Uranium Mill Chloroform Monitoring Report for the 1st Quarter of
2016 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs
each containing a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
1(aq k~
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Harold R. Roberts
David E. Turk
Logan Shumway
Scott Bakken
White Mesa Uranium Mill
Chloroform Monitoring Report
State of Utah
Stipulation and Consent Order Docket No. UGW-20-01
1st Quarter
(January through March)
2016
Prepared by:
~It: ~I:~ERGYFUELS
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
May 19,2016
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 ......................................................................... 10
4.0 INTERPRETATION OF DATA ....................................................................... 11
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions ........... 11
4.1.1 Current Site Groundwater Contour Map ................................................... 11
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater
Contour Maps for Previous Quarter ......................................................... 16
4.1.4 Depth to Groundwater Measured and Groundwater Elevation ................. 18
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture ............................ 18
4.2 Review of Analytical Results ............................................................................ 21
4.2.1 Current Chloroform Isoconcentration Map .............................................. 21
4.2.2 Chloroform Concentration Trend Data and Graphs .................................. 21
4.2.3 Interpretation of Analytical Data .............................................................. 21
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND
TW4-4 OPERATIONS REPORT ..................................................................... 24
5.1 Introduction ....................................................................................................... 24
5.2 Pump Test Data Collection ............................................................................... 25
i
5.3 Water Level Measurements .............................................................................. 25
5.4 Pumping Rates and Volumes ............................................................................ 26
5.4.1 TW4-24 ............................................................................................................ 26
5.4.2 TW4-19 and MW-26 ........................................................................................ 26
5.5 Mass Removed and Plume Residual Mass ....................................................... 26
5.6 Inspections ........................................................................................................ 27
5.7 Conditions That May Affect Water Levels in Piezometers .............................. 27
6.0 CORRECTIVE ACTION REPORT ................................................................. 27
6.1 Assessment of Previous Quarter's Corrective Actions ..................................... 27
7.0 CURRENT COMPLIANCE STATUS ............................................................. 27
7.1 Long Term Chloroform Plume Control ............................................................ 27
7.2 Well Construction, Maintenance and Operation ............................................... 27
7.3 Disposal of Extracted Groundwater. ................................................................. 28
7.4 Compliance Well Performance ......................................................................... 28
7.5 Chloroform Plume Monitoring for Wells within 500 Feet of the Property
Boundary .......................................................................................................... 28
8.0 CONCLUSIONS AND RECOMMENDATIONS ............................................ 28
9.0 ELECTRONIC DATA FILES AND FORMAT .............................................. 32
10.0 SIGNATURE AND CERTIFICATION ........................................................... 33
LIST OF TABLES
Table 1 Summary of Well Sampling for the Period
ii
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture
Zone Details Map, and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater
Elevations Over Time for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells
OverTime
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 Evaluation
1-7 QA/QC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
1-9 Rinsate Check
Tab J Kriged Current Quarter Chloroform Isoconcentration Map
Tab K Analyte Concentration Data and Chloroform Concentration Trend Graphs Over
Time
Tab L Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
Tab M CSV Transmittal Letter
iii
1.0 INTRODUCTION
The presence of chloroform was initially identified in groundwater at the White Mesa Mill (the
"Mill") as a result of split sampling performed in May 1999. The discovery resulted in the
issuance of State of Utah Notice of Violation ("NOV") and Groundwater Corrective Action
Order ("CAO") State of Utah Department of Environmental Quality ("UDEQ"), Division of
Waste Management and Radiation Control ("DWMRC") Docket No. UGW-20-01, which
required that Energy Fuels Resources (USA) Inc. ("EFRI") submit a Contamination Investigation
Plan and Report pursuant to the provisions of UAC R317-6-6.15(D). In response to the NOV,
EFRI submitted a series of documents outlining plans for investigation of the chloroform
contamination. This plan of action and preliminary schedule was set out in EFRI submittals
dated: September 20, 1999; June 30, 2000; April 14, 2005; and November 29, 2006. EFRI
submitted a draft Groundwater Corrective Action Plan ("GCAP") dated August 22, 2007. The
draft GCAP was reviewed by the Director, who advised EFRI in 2013 that modifications were
required. In an effort to expedite and formalize active and continued remediation of the
chloroform plume, both parties have agreed to the GCAP found in Attachment 1, of the final
Stipulation and Consent Order ("SCO") dated September 14, 2015.
This is the Quarterly Chloroform Monitoring Report for the first quarter of 2016 as required
under the SCO. This report also includes the Operations Report for MW-04, TW4-01, TW4-04,
TW4-02, TW4-11, TW4-19, TW4-20, TW4-21, MW-26, TW4-22, TW4-24, TW4-25, and TW4-
3 7 for the quarter.
2.0 CHLOROFORM MONITORING
2.1 Samples and Measurements Taken During the Quarter
A map showing the location of all groundwater monitoring wells, piezometers, existing wells,
temporary chloroform contaminant investigation wells and temporary nitrate investigation wells
is attached under Tab A. Chloroform samples and measurements taken during this reporting
period are discussed in the remainder of this section.
2.1.1 Chloroform Monitoring
Quarterly sampling for chloroform monitoring parameters is currently required in the following
wells:
MW-4 TW4-9 TW4-18 TW4-27 TW4-36
TW4-1 TW4-10 TW4-19 TW4-28 TW4-37
TW4-2 TW4-11 TW4-20 TW4-29
TW4-3 TW4-12 TW4-21 TW4-30
TW4-4 TW4-13 TW4-22 TW4-31
TW4-5 TW4-14 TW4-23 TW4-32
TW4-6 MW-26 (formerly TW4-15) TW4-24 TW4-33
TW4-7 TW4-16 TW4-25 TW4-34
TW4-8 MW-32 (formerly TW4-17) TW4-26 TW4-35
1
Chloroform monitoring was performed in all of the required chloroform monitoring wells.
Table 1 provides an overview of all wells sampled during the quarter, along with the date
samples were collected from each well, and the date(s) when analytical data were received from
the contract laboratory. Table 1 also identifies equipment rinsate samples collected, as well as
sample numbers associated with the deionized field blank ("DIFB") and any required duplicates.
2.1.2 Parameters Analyzed
Wells sampled during this reporting period were analyzed for the following constituents:
• Chloroform
• Chloromethane
• Carbon tetrachloride
• Methylene chloride
• Chloride
• Nitrate plus Nitrite as Nitrogen
Use of analytical methods is consistent with the requirements of the Chloroform Investigation
Monitoring Quality Assurance Program (the "Chloroform QAP") attached as Appendix A to the
White Mesa Uranium Mill Groundwater Monitoring QAP Revision 7.2, dated June 6, 2012.
2.1.3 Groundwater Head Monitoring
Depth to groundwater was measured in the following wells and/or piezometers, pursuant to Part
I.E.3 of the Groundwater Discharge Permit (the "GWDP"):
• The quarterly groundwater compliance monitoring wells
• Existing monitoring well MW -4 and all of the temporary chloroform investigation wells
• Piezometers P-1, P-2, P-3, P-4 and P-5
• MW-20 and MW-22
• Nitrate monitoring wells
• The DR piezometers that were installed during the Southwest Hydrologic Investigation
In addition to the above, depth to water measurements are routinely observed in conjunction with
sampling events for all wells sampled during quarterly and accelerated efforts, regardless of the
sampling purpose.
Weekly and monthly depth to groundwater measurements were taken in the chloroform
pumping wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21,
TW4-37, 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. The revised Groundwater QAP and Chloroform QAP, Revision
7.2 were approved by DWMRC on June 7, 2012.
The sampling methodology, equipment and decontamination procedures used in the chloroform
contaminant investigation, as summarized below, are consistent with the approved QAP
Revision 7.2 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;
d) the DI water solution is pumped through the pump and pump outlet lines into the drain line
connected to Cell 1;
3
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 is thus established. The list is included with the Field Data
Worksheets under Tab B. Mill personnel start purging with all of the non-detect wells and then
move to the wells with detectable chloroform concentrations staring with the lowest
concentration and proceeding to the wells with the highest concentration. One deviation to this
practice is made for the continuously pumping wells. These wells are sampled throughout the
sampling event and are not sampled in the order of contamination. This practice does not affect
the samples for this reason: the pumping wells have dedicated pumps and there will be no cross-
contamination resulting from the sampling order.
Samples are collected by means of disposable bailer(s) the day following the purging. The
disposable bailer is used only for the collection of a sample from an individual well and disposed
subsequent to the sampling. As noted in the approved QAP, Revision 7.2, 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 deionized ("DI")
water. Where portable (non-dedicated) sampling equipment is used, a rinsate sample is collected
at a frequency of one rinsate sample per 20 field samples. Well depth measurements are taken
and the one casing volume is calculated for those wells which do not have a dedicated pump as
described in Attachment 2-3 of the QAP. Purging is completed to remove stagnant water from
the casing and to assure that representative samples of formation water are collected for analysis.
There are three purging strategies that are used to remove stagnant water from the casing during
groundwater sampling at the Mill. The three strategies are as follows:
1. Purging three well casing volumes with a single measurement of field parameters
specific conductivity, turbidity, pH, redox potential, and water temperature
2. Purging two casing volumes with stable field parameters for specific conductivity,
turbidity, pH, redox potential, and water temperature (within 10% Relative Percent
Difference ["RPD"])
3. Purging a well to dryness and stability (within 10% RPD) of field parameters for pH,
specific conductivity, and water temperature only after recovery
If the well has a dedicated pump, it is pumped on a set schedule per the remediation plan and is
considered sufficiently evacuated to immediately collect a sample; however, if a pumping well
has been out of service for 48 hours or more, EFRI will follow the purging requirements outlined
in Attachment 2-3 of the QAP. The dedicated pump is used to collect parameters and to collect
the samples as described below. If the well does not have a dedicated pump, a Grundfos pump
4
(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 bailers.
Mill personnel use a disposable bailer to sample each well that does not have a dedicated pump.
The bailer is attached to a reel of approximately 150 feet of nylon rope and then lowered into the
well. After coming into contact with the water, the bailer is allowed to sink into the water in
order to fill. Once full, the bailer is reeled up out of the well and the sample bottles are filled as
follows:
• Volatile Organic Compound ("VOC") samples are collected first. This sample consists
of three 40 ml vials provided by the Analytical Laboratory. The VOC sample is not
filtered and is preserved with HCl;
• A sample for nitrate/nitrite is then collected. This sample consists of one 250 ml. bottle
that is provided by the Analytical Laboratory. The nitrate/nitrite sample is not filtered
and is preserved with H2S04;
• A sample for chloride is then collected. This sample consists of one 500 ml. bottle that is
provided by the Analytical Laboratory. The chloride sample is not filtered and is not
chemically preserved.
After the samples have been collected for a particular well, the bailer is disposed of and the
samples are placed into the cooler that contains ice. The well is then recapped and Mill personnel
proceed to the next well.
5
2.3 Field Data
Attached under Tab B are copies of the Field Data Worksheets that were completed during the
quarter for the chloroform contaminant investigation monitoring wells identified in paragraph
2.1.1 above, and Table 1.
2.4 Depth to Groundwater Data and Water Table Contour Map
Attached under Tab C are copies of the Depth to Water Sheets for the weekly monitoring of
MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22, TW4-
24, TW4-25, TW4-37, 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
1lists the dates when analytical results were reported to the QA Manager for each sample.
Results from the analyses of samples collected for this quarter's chloroform contaminant
investigation are provided under Tab H of this Report. Also included under Tab H are the results
of the analyses for duplicate samples, the DIFB, and rinsate samples for this sampling effort, as
identified in Table 1, as well as results for trip blank analyses required by the Chloroform QAP.
2.5.2 Regulatory Framework
As discussed in Section 1.0, above, the SCO triggered a series of actions on EFRI's part. In
addition to the monitoring program, EFRI has equipped one nitrate well and thirteen chloroform
wells with pumps to recover impacted groundwater, and has initiated recovery of chloroform
from the perched zone.
Sections 4 and 5, below, interpret the groundwater level and flow information, contaminant
analytical results, and pump test data to assess effectiveness of EFRI's chloroform capture
program.
3.0 QUALITY ASSURANCE AND DATA VALIDATION
The QA Manager performed a QA/Quality Control ("QC") review to confirm compliance of the
monitoring program with requirements of the QAP. As required in the QAP, data QA includes
preparation and analysis of QC samples in the field, review of field procedures, an analyte
completeness review, and QC review of laboratory methods and data. Identification of field QC
6
samples collected and analyzed is provided in Section 3.1. Discussion of adherence to Mill
sampling Standard Operating Procedures ("SOPs") is provided in Section 3.2. Analytical
completeness review results are provided in Section 3.3. The steps and tests applied to check
laboratory data QA/QC are discussed in Sections 3.4.4 through 3.4.9 below.
The analytical laboratory has provided summary reports of the analytical QA/QC measurements
necessary to maintain conformance with National Environmental Laboratory Accreditation
Conference ("NELAC") certification and reporting protocol. The Analytical Laboratory QA/QC
Summary Reports, including copies of the Mill's Chain of Custody and Analytical Request
Record forms for each set of Analytical Results, follow the analytical results under Tab H.
Results of the review of the laboratory QA/QC information are provided under Tab I and are
discussed in Section 3.4, below.
3.1 Field QC Samples
The following QC samples were generated by Mill personnel and submitted to the analytical
laboratory in order to assess the quality of data resulting from the field sampling program.
Field QC samples for the chloroform investigation program consist of one field duplicate sample
for each 20 samples, a trip blank for each shipped cooler that contains VOCs, one DIFB and
rinsate samples.
During this quarter, two duplicate samples were collected as indicated in Table 1. The duplicates
were sent blind to the analytical laboratory and analyzed for the same parameters as the
chloroform wells.
Two trip blanks were provided by AW ALand returned with the quarterly chloroform monitoring
samples.
Two rinsate blank samples were collected at a frequency of one rinsate per twenty samples per
QAP Section 4.3.2 and 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
QAIQC evaluation of sample duplicates, a QC Control Limit check for analyses and blanks
including the DIFB and a rinsate sample check. Each evaluation is discussed in the following
sections. Data check tables indicating the results of each test are provided under Tab I.
3.4.1 Field Data QA/QC Evaluation
The QA Manager performs a review of the field recorded parameters to assess their adherence
with QAP requirements. The assessment involved review of two sources of information: the
Field Data Sheets and the Quarterly Depth to Water summary sheet. Review of the Field Data
Sheets addresses well purging volumes and measurement of field parameters based on the
requirements discussed in section 2.2.1 above. The purging technique employed determines the
requirements for field parameter measurement and whether stability criteria are applied. Review
of the Depth to Water data confirms that all depth measurements used for development of the
groundwater contour maps were conducted within a five-day period as indicated by the
measurement dates in the summary sheet under Tab D. The results of this quarter's review of
field data are provided under Tab I.
Based upon the review of the field data sheets, the purging and field measurements were
completed in conformance with the QAP requirements. A summary of the purging techniques
employed and field measurements taken is described below:
Purging Two Casing Volumes with Stable Field Parameter (within 10% RPD)
Wells TW4-5, TW4-7, TW4-8, TW4-9, TW4-12, TW4-16, MW-32, TW4-18, TW4-23, TW4-28,
and TW4-32 were sampled after two casing volumes were removed. Field parameters (pH,
specific conductivity, turbidity, water temperature, and redox potential) were measured during
purging. All field parameters for this requirement were stable within 10% RPD.
Purging a Well to Dryne sand Stability of a Limited List of Field Parameters
Wells TW4-3, TW4-6, TW4-10, TW4-13, TW4-14, TW4-26, TW4-27, TW4-29, TW4-30, TW4-
31, TW4-33, TW4-34, TW4-35, and TW4-36 were pumped to dryness before two casing
volumes were evacuated. After well recovery, one set of measurements were taken. The samples
were then collected, and another set of measurements were taken. Stabilization of pH,
conductivity and temperature are required within 10% RPD under the QAP, Revision 7.2. The
QAP requirements for stabilization were met.
Continuously Pumped Wells
Wells MW-4, TW4-1, TW4-2, TW4-4, TW4-11, MW-26, TW4-19, TW4-20, TW4-21, TW4-22,
TW4-24, TW4-25, and TW4-37 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, Revision 7.2 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 TW4-7, TW4-9, TW4-11, TW4-12, TW4-16, MW-32, TW4-18, TW4-23, TW4-28, and
TW4-32 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
9
than the increased detection limit.
3.4.6 Receipt pH Evaluation
Appendix A of the QAP states that volatile samples are required to be preserved and arrive at the
laboratory with a pH less than 2. A review of the laboratory data revealed that the volatile
samples were received at the laboratory with a pH less than 2.
3.4. 7 Trip Blank Evaluation
Trip blank results were reviewed to identify any VOC contamination resulting from transport of
the samples. Trip blank checks are provided in Tab I. The trip blank results were less than the
reporting limit for all VOCs.
3.4.8 QA/QC Evaluation for Sample Duplicates
Section 9.1.4 a) of the QAP states that RPDs will be calculated for the comparison of duplicate
and original field samples. The QAP acceptance limits for RPDs between the duplicate and
original field sample is less than or equal to 20% unless the measured results are less than 5
times the required detection limit. This standard is based on the EPA Contract Laboratory
Program National Functional Guidelines for Inorganic Data Review, February 1994, 9240.1-05-
01 as cited in the QAP. The RPDs are calculated for the duplicate pairs for all analytes
regardless of whether or not the reported concentrations are greater than 5 times the required
detection limits; however, data are considered noncompliant only when the results are greater
than 5 times the reported detection limit and the RPD is greater than 20%. The additional
duplicate information is provided for information purposes.
Duplicate results were within a 20% RPD in the quarterly samples. Duplicate results are
provided under 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. The rinsate blank sample results were
nondetect for this quarter.
While not required by the Chloroform QAP, DIFB samples are collected to analyze the quality of
the DI water system at the Mill, which is also used to collect rinsate samples. A review of the
analytical results reported for the DIFB sample indicated the sample results were nondetect.
3.4.10 Other Laboratory QA/QC
Section 9.2 of the QAP requires that the laboratory's QA/QC Manager check the following items
in developing data reports: (1) sample preparation information is correct and complete, (2)
analysis information is correct and complete, (3) appropriate analytical laboratory procedures are
followed, (4) analytical results are correct and complete, (5) QC samples are within established
control limits, (6) blanks are within QC limits, (7) special sample preparation and analytical
10
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 for
the regulated compounds except as indicated in Tab I. The data recoveries which are outside the
laboratory established acceptance limits do not affect the quality or usability of the data because
the recoveries outside of the acceptance limits are indicative of matrix interference. 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.
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 QNQC Summary Reports indicates that the surrogate recoveries for the
quarterly 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 information from the Laboratory QNQC Summary Reports indicates that the Laboratory
Control Samples (the "LCS") recoveries were within acceptable laboratory limits for the LCS
compounds.
4.0 INTERPRETATION OF DATA
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.
4.1.1 Current Site Groundwater Contour Map
11
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 wildlife ponds
disrupts the generally southwesterly flow pattern, to the extent that locally northerly flow occurs
near 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 mound decays due to reduced recharge.
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, has resulted in changing
conditions that are expected to impact constituent concentrations and migration rates within the
plumes. Specifically, past recharge from the ponds has helped limit many constituent
concentrations within the plumes by dilution while the associated groundwater mounding has
increased hydraulic gradients and contributed to plume migration. Since use of the northern
wildlife ponds ceased in March 2012, the reduction in recharge and decay of the associated
groundwater mound are expected to increase many constituent concentrations within the plumes
while reducing hydraulic gradients and acting to reduce rates of plume migration. EFRI and its
consultants have raised the issues and potential effects associated with cessation of water
delivery to the northern wildlife ponds during discussions with DWMRC in March 2012 and
May 2013.
The impacts associated with cessation of water delivery to the northern ponds are expected to
propagate downgradient (south and southwest) over time. Wells close to the ponds are generally
expected to be impacted sooner than wells farther downgradient of the ponds. Therefore,
constituent concentrations are generally expected to increase in downgradient wells close to the
ponds before increases are detected in wells farther downgradient of the ponds. Although such
increases are anticipated to result from reduced dilution, the magnitude and timing of the
increases are 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. The potential exists for
some wells completed in higher permeability materials to be impacted sooner than some wells
completed in lower permeability materials even though the wells completed in lower
permeability materials may be closer to the ponds.
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 rmxmg of low constituent concentration pond recharge into
existing perched groundwater will be reduced over time.
12
2) Reduced saturated thicknesses -dewatering of higher permeability layers recetvmg
primarily low constituent concentration pond water will result in wells intercepting these
layers receiving a smaller proportion of the low constituent concentration water.
The combined impact of the above two mechanisms may be especially evident at chloroform
pumping wells MW-4, MW-26, TW4-4, TW4-19, and TW4-20; nitrate pumping wells TW4-22,
TW4-24, TW4-25, and TWN-2; and non-pumped wells adjacent to the pumped wells. Impacts
are also expected to occur over time at wells added to the chloroform pumping network during
the first quarter of2015 (TW4-1, TW4-2, TW4-ll), and to those added during the second quarter
of 2015 (TW4-21 and TW4-37). The overall impact is expected to be generally higher
constituent concentrations in these wells over time until mass reduction resulting from pumping
and natural attenuation eventually reduces concentrations. Short-term changes in concentrations
at pumping wells and wells adjacent to pumping wells are also expected to result from changes
in pumping conditions.
In addition to changes in the flow regime caused by wildlife pond recharge, perched flow
directions are locally influenced by operation of the chloroform and nitrate pumping wells. Well
defined cones of depression are evident in the vicinity of all chloroform pumping wells except
TW4-4, which began pumping in the first quarter of 2010, and TW4-37, which began pumping
during the second quarter of 2015. Although operation of chloroform pumping well TW4-4 has
depressed the water table in the vicinity of TW 4-4, a well-defined cone of depression is not
clearly evident. The lack of a well-defined cone of depression near TW4-4 likely results from 1)
variable permeability conditions in the vicinity of TW4-4, and 2) persistent relatively low water
levels at adjacent well TW4-14. The lack of a well-defined cone of depression near TW4-37
likely results from recent start-up and close proximity to other pumping wells.
Nitrate pumping wells TW4-22, TW4-24, TW4-25, and TWN-2 started pumping during the first
quarter of 2013. Water level patterns near these 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 persistently low water level elevation at TWN-7. By the fourth quarter of
2013, operation of the nitrate pumping system had produced well-defined impacts on water
levels. The long-term interaction between the nitrate and chloroform pumping systems IS
evolving, and changes will be reflected in data collected as part of routine monitoring.
As discussed above, variable permeability conditions likely contribute to the lack of a well-
defined cone of depression near chloroform pumping well TW4-4. Changes in water levels at
wells immediately south and southeast (downgradient) of TW4-4 resulting from TW4-4 pumping
are expected to be muted because TW4-4 is located at a transition from relatively high to
relatively low permeability conditions south and southeast of TW4-4. As will be discussed
below, the permeability of the perched zone at TW4-6 and TW4-26, and relatively recently
installed wells TW4-29, TW4-30, TW4-31, TW4-33, TW4-34, and TW4-35 is one to two orders
of magnitude lower than at TW4-4, and the permeability at TW4-27 is approximately three
orders of magnitude lower than at TW 4-4. Detecting water level drawdowns in wells
immediately south and southeast of TW4-4 resulting from TW4-4 pumping has also been
difficult because of the general, long-term increase in water levels in this area attributable to past
wildlife pond recharge.
13
Between the fourth quarter of 2007 and the fourth quarter of 2009 (just prior to the start of TW4-
4 pumping), water levels at TW4-4 and TW4-6 increased by nearly 2.7 and 2.9 feet at rates of
approximately 1.2 feet/year and 1.3 feet/year, respectively. However, the rate of increase in
water levels at TW4-6 after the start of pumping at TW4-4 (first quarter of 2010) was reduced to
less than 0.5 feet/year suggesting that TW 4-6 is within the hydraulic influence of TW 4-4.
Since the fourth quarter of 2013, water levels in all wells currently within the chloroform plume
south ofTW4-4 (TW4-6, TW4-29, and TW4-33) have been trending downward. This downward
trend is attributable to the cessation of water delivery to the northern wildlife ponds and
pumping. However, water level trends have been upward in many wells located at the margin of
the chloroform plume southeast of TW4-4 (TW4-14, TW4-27, TW4-30, and TW4-31). These
wells appear as yet to be responding to past wildlife pond recharge and expansion of the
groundwater mound.
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 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 ponds. Wells that are more
hydraulically isolated will also respond more slowly to changes in pumping.
The lack of a well-defined cone of depression at TW4-4 is also influenced by the persistent,
relatively low water level at non-pumping well TW4-14, located east of TW4-4 and TW4-6. For
the current quarter, the water level at TW4-14 (approximately 5533.2 feet above mean sea level
["ft amsl"]), is more than 3 feet lower than the water level at TW4-6 (approximately 5536.8 ft
amsl) and approximately 7 feet lower than the water level at TW4-4 (approximately 5540.4 ft
amsl), even though TW4-4 is pumping. However, water level differences among these wells are
diminishing.
The static water levels at wells TW 4-14 and downgradient well TW 4-27 (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. The current quarterly water level at TW4-27
(approximately 5528.6 ft amsl) is 4.6 feet lower than the water level at TW4-14 (5533.2 ft amsl).
Recent increases in the differences between water levels at TW4-14 and TW4-27 are due to more
rapid increases in water levels at TW 4-14 resulting from past delivery of water to the northern
wildlife ponds. The rate of water level increase at TW4-27 is smaller than at TW4-14 because
TW4-27 is farther downgradient of the ponds.
TW4-27 was positioned at a location considered likely to detect any chloroform present and/or to
bound the chloroform plume to the southeast and east (respectively) of TW4-4 and TW4-6. As
will be discussed below, groundwater data collected since installation indicates that TW4-27
does indeed bound the chloroform plume to the southeast and east of TW 4-4 and TW 4-6
(respectively); however chloroform exceeding 70 !J.g/L has been detected at relatively recently
installed temporary perched wells TW4-29 (located south of TW4-27) and TW4-33 (located
between TW4-4 and TW4-29).
14
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 low water level at TW4-14. The water level at TW4-26 (5535.2
feet amsl) is, however, lower than water levels at adjacent wells TW4-6 (5536.8 feet amsl), and
TW4-23 (5538.3 feet amsl).
Hydraulic tests indicate that the permeability at TW4-27 is an order of magnitude lower than at
TW4-6 and three orders of magnitude lower than at TW4-4 (see Hydro Geo Chern, 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 relatively recently installed wells TW4-29, TW4-30, TW4-31, TW4-33, TW4-34
and TW4-35, which indicate that the permeability of these wells is one to two orders of
magnitude higher than the permeability of TW4-27 (see: HGC, January 23, 2014, Contamination
Investigation Report, TW4-12 and TW4-27 Areas, White Mesa Uranium Mill Near Blanding,
Utah; and HGC, July 1, 2014, Installation and Hydraulic Testing of TW4-35 and TW4-36,
White Mesa Uranium Mill Near Blanding, Utah [As-Built Report]). Hydraulic tests also indicate
that the permeability at TW4-36 is slightly higher than but comparable to the low permeability at
TW4-27, suggesting that TW4-36, TW4-14 and TW4-27 are completed in a continuous low
permeability zone.
The low permeability at TW4-14 and TW4-27 is expected to retard the transport of chloroform
to these wells (compared to nearby wells). As will be discussed in Section 4.2.3, TW4-14 and
TW4-27 remain outside the plume with first quarter, 2016 chloroform concentrations of 4.5 f!g/L
and 2.1 f!g/L, respectively.
Chloroform exceeding 70 f!g/L detected at TW4-29 and TW4-33 since their relatively recent
installation in 2013 indicates that, in addition to migrating south from TW 4-4 to TW 4-6 and
TW4-26, chloroform also migrated along a 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 relatively recently, placed TW4-14 almost directly downgradient of TW4-
4. Such migration was historically possible because the water levels at TW 4-29 have been 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.
15
Chloroform during the current quarter was detected at only approximately 5.2 j..tg/L at relatively
recently installed well TW4-30 (located east and downgradient of TW4-29), and was not
detected at relatively recently installed wells TW4-31 (located east of TW4-27), TW4-34
(located south and cross-gradient of TW4-29), nor TW4-35 (located southeast and cross-to
downgradient of TW 4-29).
Data from existing and relatively recently installed wells indicate that:
1. Chloroform exceeding 70 ~-tg/L at TW4-29 is bounded by concentrations below 70 j..tg/L at
wells TW4-26, TW4-27, TW4-30, TW4-34, and TW4-35. TW4-30 is downgradient of
TW4-29; TW4-26 is cross-to upgradient ofTW4-29; and TW4-27, TW4-34 and TW4-35
are cross-to downgradient of TW4-29.
2. Chloroform concentrations at TW4-33 that are lower than concentrations at TW4-29, and
the likelihood that a pathway exists from TW4-4 to TW4-33 to TW4-29, suggest that
concentrations in the vicinity of TW4-33 were likely higher prior to initiation of TW4-4
pumping, and that lower concentrations currently detected at TW4-33 are due to its closer
proximity to TW 4-4.
Furthermore, TW4-4 pumping is likely to eventually 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 decreases in chloroform concentrations that occurred at TW4-6 and TW4-26
once TW4-4 pumping began. Since installation in 2013, however, concentrations at TW4-33
appear to be relatively stable; since the third quarter of 2014, concentrations at TW4-29 appear to
be generally increasing.
Relatively stable chloroform at TW4-33 and generally increasing concentrations at TW4-29
suggest that chloroform migration has been arrested at TW4-33 by TW4-4 pumping and that
increasing chloroform at downgradient well TW4-29 results from a remnant of the plume that
continues to migrate downgradient (toward TW4-30, which bounds to plume to the east). The
influence of TW 4-4 pumping at the distal end of the plume is consistent with generally
decreasing water levels at both TW4-29 and TW4-33.
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 (defined by TW4-29 and TW4-33) into the low
permeability materials penetrated by TW4-14 and TW4-27.
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 2015, as submitted with
the Chloroform Monitoring Report for the fourth quarter of 2015, is attached under Tab E.
A comparison of the water table contour maps for the current quarter (first quarter of 2016) to
the water table contour maps for the previous quarter (fourth quarter of 2015) indicates similar
16
patterns of drawdowns associated with pumping wells. A significant cone of depression
associated with relatively new chloroform pumping well TW4-37 is not yet evident. Drawdowns
at chloroform pumping wells MW-4, TW4-1, and nitrate pumping well TWN-2 increased by 2 or
more feet this quarter. Draw downs at chloroform pumping well TW 4-2 and nitrate pumping
wells TW4-22 and TW4-24 decreased by more than 2 feet this quarter.
Nitrate pumping wells TW4-22, TW4-24, TW4-25, and TWN-2 were brought into operation
during the first quarter of 2013 and their impact on water level patterns was evident as of the
fourth quarter of 2013. Water levels in nitrate pumping wells showed both increases (decreases
in drawdown) and decreases (increases in drawdown) this quarter.
As discussed in Section 4.1.1, pumping at chloroform well TW 4-4, which began in the first
quarter of 2010, has depressed the water table near TW4-4, but a well-defined cone of depression
is not clearly evident, likely due to variable permeability conditions near TW4-4 and the
persistently low water level at adjacent well TW4-14.
Small (<1 foot) changes in water levels were reported at the majority of site wells; water levels
and water level contours for the site have not changed significantly since the last quarter except
for a few locations. Reported decreases in water levels (increases in drawdown) of approximately
9.0, 2.0, and 3.6 feet occurred in chloroform pumping wells MW-4, TW4-1, and nitrate pumping
well TWN-2, respectively. Increases in water level (decreases in drawdown) of approximately
3.9, 2.1, and 2.8 feet were reported for chloroform pumping well TW4-2 and nitrate pumping
wells TW4-22 and TW4-24, respectively. The reported water level for TW4-11 is slightly below
the depth of the Brushy Basin contact this quarter. Changes in water levels at other pumping
wells (chloroform pumping wells MW-26, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, and
TW4-37, and nitrate pumping well TW4-25) were less than 2 feet. Water level fluctuations at
pumping wells typically occur in part because of fluctuations in pumping conditions just prior to
and at the time the measurements are taken.
Although increases in water levels (decreases in drawdown) occurred in some pumping wells
and decreases in water levels (increases in drawdown) occurred in others, the overall apparent
capture of the combined pumping system is approximately the same as last quarter
Reported water level decreases of up to 0.37 feet at Piezometers 1, 2, 4, and 5, TWN-1, and
TWN-4 may result from cessation of water delivery to the northern wildlife ponds as discussed
in Section 4.1.1 and the consequent continuing decay of the associated perched water mound.
Reported water level decreases of approximately 0.2 feet and 0.3 feet at Piezometers 4 and 5,
respectively, may also result from reduced recharge at the southern wildlife pond.
Reported water levels increased by approximately 3.9 feet, 3 feet, and 6 feet at MW-20, MW-23,
and MW-37, respectively, approximately compensating for the decreases reported last quarter.
Water level variability at these wells is likely the result of low permeability and variable
intervals between purging/sampling and water level measurement. Measurable water was again
reported at DR-22. Although DR-22 is typically dry, measurable water has been reported in the
bottom of its casing since the second quarter of 2015.
17
4.1.3 Hydrographs
Attached under Tab F are hydrographs showing groundwater elevation m each chloroform
contaminant investigation monitor well over time.
4.1.4 Depth to Groundwater Measured and Groundwater Elevation
Attached under Tab F are tables showing depth to groundwater measured and groundwater
elevation over time for each of the wells listed in Section 2.1.1 above.
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, TW4-4, TW4-19, and TW4-20, and, since the first
half of 2015, wells TW4-1, TW4-2, TW4-11, TW4-21, and TW4-37. The primary purpose of
the pumping is to reduce total chloroform mass in the perched zone as rapidly as is practical.
Pumping wells up gradient of TW 4-4 were chosen because 1) they are 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 pumping wells results in the wells having a relatively
high productivity. The combination of relatively high productivity and high chloroform
concentrations allows for a high rate of chloroform mass removal. TW 4-4 is located in a
downgradient area having relatively high chloroform concentrations but relatively small
saturated thickness, and at a transition from relatively high to relatively low permeability
conditions downgradient of TW4-4. As with the other chloroform pumping wells, pumping
TW 4-4 helps to reduce the rate of chloroform migration in downgradient portions of the plume.
The impact of chloroform pumping is indicated by the water level contour maps attached under
Tabs D and E. Cones of depression are evident in the vicinity of MW-4, MW-26, TW4-19, and
TW4-20 which continue to remove significant quantities of chloroform from the perched zone.
Relatively large cones of depression have developed in the vicinities of wells TW4-1, TW4-2,
and TW4-11 which began pumping during the first quarter of 2015, and at TW4-21 which began
pumping during the second quarter of 2015. A cone of depression in the vicinity of chloroform
pumping well TW4-37, which began pumping during the second quarter of 2015, is not yet
evident. The water level contour maps indicate effective capture of water containing high
chloroform concentrations in the vicinities of these pumping wells. As discussed in Section
4.1.1, although chloroform pumping well TW 4-4 became operational in 2010, the draw down
associated with TW4-4 is likely less apparent due to variable permeability conditions near TW4-
4 and the persistently low water level at adjacent well TW4-14.
Compared to last quarter, both increases and decreases in water levels occurred at nitrate and
chloroform pumping wells. The water levels in chloroform pumping wells MW-4, TW4-1, TW4-
4, TW4-11, and TW4-19 decreased by approximately 9.0, 2.0, 1.3, 1.2, and 1.1 feet respectively,
while the water levels in chloroform pumping wells MW-26, TW4-2, TW4-20, TW4-21 and
TW4-37 increased by approximately 0.8, 3.9, 0.4, 1.9, and 1.6 feet, respectively. The water level
in nitrate pumping well TWN-2 decreased by approximately 3.6 feet while the water levels in
18
nitrate pumping wells TW4-22, TW4-24, and TW4-25 increased by approximately 2.1, 2.8, and
1.0 feet, respectively. Overall, the apparent capture of the combined pumping systems is about
the same as last quarter.
The capture associated with nitrate pumping wells is expected to increase over time as water
levels continue to decline due to cessation of water delivery to the northern wildlife ponds and
continued pumping. Slow development of hydraulic capture is consistent with and expected
based on the relatively low permeability of the perched zone at the site.
The hydraulic capture effectiveness of both chloroform and nitrate pumping systems depends to
some extent on the continued productivity of chloroform and nitrate pumping wells. Decreases in
productivity have been noted since the third quarter of 2014 in chloroform pumping well TW4-
19 and nitrate pumping well TW4-24. The impact of reduced productivity of these wells on
chloroform capture was discussed in Attachment N (Tab N) of the third quarter, 2015 report. The
report also included a discussion of the effectiveness of chloroform pumping on chloroform
capture. 'Background' flow through the chloroform plume was calculated in Attachment N as
approximately 3.3 gpm. A more refined 'background' flow calculation of 3.4 gpm was provided
in the CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah).
Pumping from the chloroform plume during the current quarter (from wells MW-4, MW-26,
TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, and TW4-37)
is approximately 4.6 gpm, which exceeds the calculated background flow by 1.2 gpm or 35%.
Therefore chloroform pumping is considered adequate at the present time even with the reduced
productivities ofTW4-19 and TW4-24. 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 TW4-20
toward these wells. The increase in concentration at TW4-8 from non-detect to 100 !J.giL in the
first quarter of 2014 (and to 634 !J.g/L this quarter) is likely related to reduced dilution. Although
the chloroform concentration in TW4-6 decreased slightly from 843 !J.giL to 834 !J.giL this
quarter, concentrations at TW4-6 have increased from approximately 10 !J.giL since the second
quarter of 2014. These changes are likely related to both reduced dilution and more westward
flow induced by nitrate pumping.
TW4-6 is located immediately south and cross-to downgradient of chloroform pumping well
TW4-4. Chloroform concentrations at TW4-6 exceeded 70 !J.giL between the first quarter of
2009 and the third quarter of 2010, and remained below 70 !J.giL between the fourth quarter of
2010 and the second quarter of 2014. Relatively low permeability and relatively small saturated
thickness in the vicinity of TW4-6 limit the rate at which chloroform mass can be removed by
pumping. However, pumping at more productive upgradient locations such as TW4-4 enhances
19
mass removal and lowers hydraulic gradients, thereby reducing the rate of downgradient
chloroform migration and allowing natural attenuation to be more effective. Pumping at TW 4-4
was implemented during the first quarter of 2010 to improve capture downgradient of TW 4-4 to
the extent allowable by the lower productivity conditions present in this area. The beneficial
effect of pumping TW 4-4 is demonstrated by the net decreases in TW 4-6 chloroform
concentrations from 1,000 ~-tg!L to 10.3 ~-tg!L, and in TW4-26 from 13 ~-tg!L to 4.2 ~-tg/L, between
the initiation of TW4-4 pumping and the second quarter of 2014. Concentrations at these wells
decreased substantially even though they do 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 is
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 TW 4-1, TW 4-2, and TW 4-11.
Regardless of whether TW 4-6 can be demonstrated to be within the hydraulic capture of TW 4-4,
pumping TW4-4 helps to reduce chloroform migration to TW4-6, TW4-26, and other
downgradient locations by the mechanisms discussed above.
Likewise, pumping at other productive upgradient locations has a beneficial impact on
downgradient chloroform even if the downgradient chloroform is not completely within the
hydraulic capture of the productive upgradient well(s). For example, pumping at MW-26 likely
reduced chloroform concentrations at TW4-16 from a maximum of 530 ~-tg!L in the second
quarter of 2004 to less than 70 ~-tg!L by the fourth quarter of 2005, and maintained concentrations
below 70 ~-tg!L until the second quarter of 2014, even though TW4-16 appears to be just 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 TW 4-1, TW 4-2, and TW 4-11
during the first quarter of 2015, and wells TW4-21 and TW4-37 during the second quarter of
2015. Operation of these additional wells may have reversed the increase in concentration at
TW4-16 which dropped from 387 ~-tg/L in the fourth quarter of 2014 to less than 70 ~-tg!L in the
second quarter of 2015. Chloroform at TW4-16 was detected at 46 ~-tg!L this quarter.
Chloroform exceeding 70 ~-tg!L was detected at relatively recently installed well TW4-29, located
south of TW4-27 and east of TW4-26, and generally cross-gradient of TW4-4 and TW4-6 with
respect to the groundwater flow directions implied by groundwater elevations in the area. As
discussed in Section 4.1.1, this may represent chloroform migrating around the low permeability
area defined by TW4-27, TW4-14 and TW4-36. The apparent migration pathway from TW4-4 to
TW4-29 is consistent with chloroform exceeding 70 ~-tg/L detected at relatively recently installed
well TW4-33, located between TW4-4 and TW4-29. Chloroform concentrations at TW4-33 that
are lower than concentrations at TW4-29, and the likelihood that a pathway exists from TW4-4
to TW4-33 to TW4-29, suggest that concentrations in the vicinity of TW4-33 were likely higher
prior to initiation of TW4-4 pumping. TW4-4 pumping is likely to eventually reduce chloroform
at both TW4-33 and TW4-29 by cutting off the source. The impact at TW4-33 is expected to be
greater than at TW4-29 because TW4-33 is in closer proximity to TW4-4 pumping. Such
behavior is expected by analogy with the decreases in chloroform concentrations at TW 4-6 and
TW4-26 that occurred once TW4-4 pumping began. However, concentrations at both TW4-29
and TW4-33 were relatively stable (rather than decreasing) for several quarters after installation.
Concentrations at TW4-29 appear to be on an upward trend since the third quarter of 2014. As
20
discussed in Section 4.1.1, although decreasing concentration trends at both wells are eventually
expected to occur, relatively stable chloroform at TW4-33 and recent increases in concentration
at TW4-29 suggest that chloroform migration has been arrested at TW4-33 by TW4-4 pumping
and that increasing chloroform at downgradient well TW4-29 results from a remnant of the
plume that continues to migrate downgradient (toward TW4-30, which bounds to plume to the
east). The influence of 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.
In addition, 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 into the low permeability
materials penetrated by these wells.
Chloroform analytical results from relatively recently installed wells TW4-35 and TW4-36 (as
discussed in Section 4.2.3) demonstrate that chloroform is bounded to the southeast of TW4-29
and to the east of TW4-8.
4.2 Review of Analytical Results
4.2.1 Current Chloroform Isoconcentration Map
Included under Tab J of this Report is a current chloroform isoconcentration map for the Mill
site. Details of the gridding procedure used to generate the chloroform isoconcentration map
(consistent with Part III.B.2.a through Part III.B.2.c of the GCAP) are provided in Tab L.
4.2.2 Chloroform Concentration Trend Data and Graphs
Attached under Tab K are tables summarizing values for all required parameters, chloride,
nitrate/nitrite, carbon tetrachloride, chloroform, chloromethane, and methylene chloride, for each
well over time.
Attached under Tab K are graphs showing chloroform concentration trends in each monitor well
over time.
4.2.3 Interpretation of Analytical Data
Comparing the chloroform analytical results to those of the previous quarter, as summarized in
the tables included under Tab K, the following observations can be made:
a) Chloroform concentrations have increased by more than 20% in the following wells
compared to last quarter: MW-26, TW4-14, TW4-20, TW4-27, and TW4-30;
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: TW4-16, TW4-26 and TW4-29;
21
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, TW4-8, TW4-
9, TW4-10, TW4-11, TW4-18, TW4-19, TW4-21, TW4-22, TW4-24, TW4-33, and
TW4-37;
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, and TW4-36.
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, TW4-14,
TW4-16, TW4-20, TW4-26, TW4-27, TW4-29 and TW4-30 had changes in concentration
greater than 20%. Of these, MW-26 and TW4-20 are chloroform pumping wells and TW4-16 is
located adjacent to chloroform pumping wells TW4-11 and MW-26. Fluctuations in
concentrations at both chloroform and nitrate pumping wells and wells adjacent to pumping
wells likely result in part from changes in pumping.
TW4-26 is located immediately southwest of the plume boundary. TW4-14 and TW4-27 are
located immediately east of the plume boundary. Currently, TW4-14 is located cross-to
downgradient of TW4-4, and TW4-27 is generally downgradient of TW4-33. TW4-29 is located
within the extreme southeast portion of the plume and TW4-30 is located just outside the plume
boundary immediately east (and downgradient) of TW4-29. Fluctuations in concentrations at
these wells are expected based on their locations at the plume margins.
Chloroform pumping wells TW4-20 and TW4-37, and nitrate pumping well TW4-22, had the
highest detected chloroform concentrations of 21,600, 17,500, and 6,070 ~-tg!L, respectively.
Since the last quarter, the chloroform concentration in TW4-20 increased from 17,000 ~-tg!L to
21,600 ~-tg!L, the concentration in adjacent pumping well TW4-19 decreased slightly from 7,840
to 7,780 ~-tg!L, and the concentration in nearby pumping well TW4-21 increased from 339 to 390
~-tg!L. The chloroform concentration in nitrate pumping well TW4-22 decreased from 7,530 ~-tg/L
to 6,070 ~-tg!L. The chloroform concentration in nitrate pumping well TW4-24 decreased from
25.3 to 22.8 ~-tg!L, and remains outside the chloroform plume. Nitrate pumping well TW4-25
remained non-detect for chloroform. 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 770 ~-tg!L to 634 ~-tg!L. TW4-8 is located immediately east of
chloroform pumping well MW -4, where chloroform was detected at a concentration of 1,240
~-tg!L. From the first quarter of 2005 through the fourth quarter of 2013, the plume boundary
remained between MW-4 and TW4-8. The occurrence of elevated chloroform at TW4-8 is likely
related to its location along the eastern plume boundary immediately east of pumping well MW-
4. Changes in the plume boundary near TW4-8 are expected to result from changes in pumping
and reduced dilution resulting from cessation of water delivery to the northern wildlife ponds.
Chloroform at TW4-8 is bounded to the north by TW4-3 (non-detect), to the northeast by TW4-
22
13 (non-detect), to the east by TW4-36 (non-detect), and to the southeast by TW4-14 (4.5 ~giL).
The increase in chloroform at TW4-14 from approximately 1.5 ~giL to 4.5 ~giL, and at TW4-27
from approximately 1.6 ~giL to approximately 2.1 ~g/L, is consistent with ongoing, but slow,
downgradient migration.
Chloroform at relatively recently installed well TW4-29 (located at the southern tip of the plume,
to the east of TW 4-26 and to the south of TW 4-27) decreased substantially from 631 ~giL to 335
~giL. Chloroform at TW4-30, located immediately downgradient of TW4-29, increased from
approximately 3.5 11-g/L to approximately 5.2 ~giL. As with TW4-27, the change at TW4-30 is
consistent with ongoing, but slow, downgradient migration. Chloroform at TW4-29 is bounded
to the north by TW4-27 (2.1 ~giL), to the east by TW4-30 (5.2 ~giL), to the southeast by TW4-
35 (non-detect), to the south by TW4-34 (non-detect), and to the west by TW4-26 (1.8 ~giL).
Chloroform at relatively recently installed well TW4-33 (located between TW4-4 and TW4-29)
showed a slight decrease in concentration, from 129 ~giL to 122 ~giL. Chloroform at TW4-33
is bounded to the north by TW4-14 (4.5 ~g/), to the east by TW4-27 (2.1 ~g/L), to the west by
TW4-23 (non-detect), and to the south and west by TW4-26 (1.8 ~giL). This chloroform
distribution indicates that the plume southeast of TW 4-4 is very narrow compared to more
upgradient locations.
As discussed above, the chloroform concentration in TW 4-6 decreased to 834 ~g/L, and remains
within the chloroform plume boundary. Concentrations at TW 4-6 exceeded 70 ~giL from the
first quarter of 2009 through the third quarter of 2010, then remained below 70 ~giL until the
third quarter of 2014. 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 ~giL to
10.3 ~giL. TW4-6, installed in the second quarter of 2000, was the most downgradient
temporary perched well prior to installation of temporary well TW4-23 in 2007 and temporary
well TW4-26 in the second quarter of 2010. TW4-6 remained outside the chloroform plume
between the second quarter of 2000 and the fourth quarter of 2008. TW4-6 likely remained
outside the chloroform plume during this time due to a combination of 1) slow rates of
downgradient chloroform migration in this area due to low permeability conditions and the
effects of up gradient chloroform removal by pumping, and 2) natural attenuation.
The relatively slow rate of chloroform migration in the vicinity of TW4-6 in the past is
demonstrated by comparing the rate of increase in chloroform at this well to the rate of increase
in the nearest upgradient well TW4-4. Concentrations at TW4-4 increased from non-detect to
more than 2,200 ~giL within only 2 quarters whereas 16 quarters were required for
concentrations in TW4-6 to increase from non-detect to only 81 ~giL. 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 order of magnitude decrease in permeability south (downgradient) of
TW4-4. Chloroform migration rates in the vicinity of well TW4-26 and relatively recently
installed wells TW4-29 and TW4-33 are also 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 TW4-29 and TW4-33 are expected to eventually trend downward.
23
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for a slight
expansion near TW4-9 (which is just inside the plume this quarter), and a contraction near TW4-
16 (which is again outside the plume). The chloroform concentration at TW4-9 increased from
approximately 68 f,!g/L to 74 f,!g/L, bringing TW4-9 back inside the plume for the first time since
the fourth quarter of 2014. The plume boundary is now located between TW4-9 and TW4-12
(which is non-detect for chloroform and cross-gradient of TW 4-9). The increase is attributable to
reduced recharge (and dilution) from the northern wildlife ponds.
Nitrate pumping generally caused the boundary of the northern portion of the chloroform plume
to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-24 has been both
inside and outside the plume and remains outside the plume this quarter, likely due to initiation
of TW4-37 pumping in the second quarter of 2015 and reduced productivity at TW4-24 (since
the third quarter of 2014). Generally increased concentrations at TW4-6 and TW4-16 (both of
which were within the chloroform plume in the past) since the second quarter of 2014 indicate
that the plume boundary migrated to the southwest and re-incorporated both wells. TW4-6
remains within the plume this quarter and TW4-16 (with a concentration of approximately 46
f,!g/L) is again outside the plume. Increases at these wells beginning in the second 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. However, continued
operation of the nitrate pumping system is expected to enhance the capture zone associated with
the chloroform pumping system even though nitrate pumping may redistribute chloroform within
the plume and cause changes in the plume boundaries. Furthermore, the addition of chloroform
wells TW4-1, TW4-2, and TW4-11 to the chloroform pumping network in the first quarter of
2015, and TW4-21 and TW4-37 in the second quarter of 2015, is expected to have a beneficial
impact. Generally reduced concentrations at TW 4-6 and TW 4-16 after previous increases are
likely the result of initiation ofTW4-1, TW4-2, and TW4-11 pumping.
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND TW4-4
OPERATIONS REPORT
5.1 Introduction
As a part of the investigation of chloroform contamination at the Mill site, EFRI has been
conducting a Long Term Pump Test on MW-4, TW4-19, MW-26, and TW4-20, and, since
January 31, 2010, TW4-4. The purpose of the test is to serve as an interim action that will
remove a significant amount of chloroform-contaminated water while gathering additional data
on hydraulic properties in the area of investigation.
Beginning in January 2013, EFRI began long term pumping of TW4-22, TW4-24, TW4-25, and
TWN-02 as required by the Nitrate CAP, dated May 7, 2012 and the Stipulated Consent Order
(the "SCO") dated December 12, 2012. Because wells TW4-22, TW4-24, and TW4-25 are
chloroform program wells, they are included in this report and any chloroform removal realized
as part of this pumping is calculated and included in the chloroform quarterly reports.
Beginning on January 14, 2015, EFRI began long term pumping ofTW4-1, TW4-2, and TW4-11
and began long term pumping of TW 4-21 and TW 4-3 7 on June 9, 2015.
24
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 Chern, Inc. were on site to conduct the first phase
of the pump test and collect the initial two days of monitoring data for MW-4. EFRI personnel
have gathered subsequent water level and pumping data.
Analyses of hydraulic parameters and discussions of perched zone hydrogeology near MW -4 has
been provided by Hydro Geo Chern 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, TW4-19, MW-26, TW4-20, and TW4-4,
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
• Measurement of water levels weekly at TW4-22, TW4-24, TW4-25, and TWN-02
commencing January 28, 2013, and on a monthly basis for selected temporary
wells and permanent monitoring wells.
5.3 Water Level Measurements
Beginning August 16, 2003, the frequency of water level measurements from MW-4, MW-26,
and TW4-19 was reduced to weekly. From commencement of pumping TW4-20, and regularly
after March 1, 2010 for TW4-4, water levels in these wells have been measured weekly. From
commencement of pumping, water levels in wells TW4-1, TW4-2, TW4-11, TW4-21, TW4-22,
TW4-24, TW4-25, TW4-37, and TWN-2 have been measured weekly. Depth to groundwater in
all other chloroform contaminant investigation wells is monitored monthly. Copies of the
weekly Depth to Water monitoring sheets for MW-4, MW-26, TW4-1, TW4-2, TW4-11, TW4-
19, TW4-20, TW4-21, TW4-4, TW4-22, TW4-24, TW4-25, TW4-37, 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.
25
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 in Section 5.4.1.
Unless specifically noted below, no additional operational problems were observed with the well
or pumping equipment during the quarter.
5.4.1 TW4-24
On January 5, 2016, Mill Field Personnel noted during the routine weekly inspection that the
flow meter on TW4-24 was malfunctioning. The well continued to pump. The flow meter was
replaced. No official notifications to DWMRC were required as the issue was rectified within
24-hours and there was no loss of pumping.
5.4.2 TW4-19 and MW-26
On January 11, 2016, Mill Field Personnel replaced the heat lamps in the TW4-19 and MW-26
enclosures.
The heat lamp replacements noted above did not result in any adverse Issues. Pumping
continued uninterrupted.
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 30.6 lb, which is within about 5% of the approximately 32.3 lb
removed last quarter.
The residual mass of chloroform within the plume is estimated as 1,946 lb using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 77 lb more than last quarter's estimate of 1,869 lb and is
attributable to slightly higher average chloroform concentrations within the plume this quarter.
As per Part ill.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.
26
The residual mass is plotted in Figure L.l. Based on the current and last two quarter's estimates,
the trend is upward. Subsequent residual plume mass estimates will be calculated quarterly,
added to the graph, and the trendline updated as per Part III.B.3 of the GCAP.
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
There are no corrective actions required during the current monitoring period.
6.1 Assessment of Previous Quarter's Corrective Actions
There are no corrective actions required during the previous 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
!!giL (Tab J). The plume is bounded to the north by TW4-25 (non-detect); to the west and
southwest by MW-31 (non-detect), MW-32 (non-detect), TW4-16 (approximately 46 !!giL),
TW4-23 (non-detect), TW4-24 (approximately 23 !!giL), and TW4-26 (approximately 2 !!giL);
to the east by TW4-3 (non-detect), TW4-5 (approximately 11 !!giL), TW4-12 (non-detect),
TW4-13 (non-detect), TW4-14 (approximately 4.5 !!giL), TW4-18 (approximately 57 !!giL),
TW4-27 (approximately 2 !!giL), TW4-30 (approximately 5 !!giL), and TW4-36 (non-detect); to
the south by TW4-34 (non-detect); and to the southeast by TW4-35 (non-detect).
Data collected to date indicate there are sufficient chloroform monitoring and pumping wells to
effectively define, control, and monitor the plume.
7.2 Well Construction, Maintenance and Operation
Part II of the GCAP specifies that EFRI must construct, maintain and operate the chloroform
wells in accordance with the specifications delineated therein. No new wells were installed
during the quarter and all previously installed wells were installed in accordance with the GCAP
requirements. The existing 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.
27
7.3 Disposal of Extracted Groundwater
Part II of the GCAP requires that all extracted groundwater be disposed of in the tailings
management system or fed in the Mill process. All extracted groundwater was handled as
required by the GCAP.
7.4 Compliance Well Performance
Part II.G of the GCAP states that an exceedance of the compliance well performance standard is
defined as the presence of chloroform in any compliance monitoring well in excess of 70 ug!L
for two or more quarters.
The compliance well chloroform concentrations were below the 70 ug/L except for TW4-9. 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 TW4-9 was less than 70 ug/L (68.4 ug/L). Because an exceedance
of chloroform in TW4-9 has not been reported two or more consecutive quarters, an Exceedance
Notice and Plan and Time Schedule are not required.
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 1,946 lb using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 77 lb more than last quarter's estimate of 1,869 lb and is
attributable to slightly higher average chloroform concentrations within the plume this quarter.
The mass of chloroform removed from the plume this quarter is approximately 30.6 lb, which is
within about 5% of the approximately 32.3 lb removed last quarter.
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
~-tg/L. The plume is bounded to the north by TW4-25; to the west and southwest by MW-31,
MW-32, TW4-16, TW4-23, TW4-24, and TW4-26; to the east by TW4-3, TW4-5, TW4-12,
TW4-13, TW4-14, TW4-18, TW4-27, TW4-30, and TW4-36; to the south by TW4-34; and to
the southeast by TW4-35. Data collected to date indicate there are sufficient chloroform
monitoring and pumping wells to effectively define, control, and monitor the plume.
The water level contour maps for the first quarter, 2016 indicate effective capture of water
containing high chloroform concentrations in the vicinity of chloroform pumping wells MW -4,
MW-26, TW4-19, and TW4-20. Capture in the vicinity of MW-4 has been enhanced by start-up
of chloroform pumping wells TW4-1, TW4-2, and TW4-11 during the first quarter of 2015.
Well-defined capture zones are not clearly evident at chloroform pumping well TW4-37 which
began pumping during the second quarter of 2015, nor at TW4-4. The capture zone associated
with TW4-4 is likely obscured by the low water level at adjacent well TW4-14 and the two
28
orders of magnitude decrease in permeability south of TW4-4. However, 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 TW4-4
pumping. Cones of depression associated with the nitrate pumping wells became evident as of
the fourth quarter, 2013, and capture associated with the nitrate pumping is expected to continue
to develop. The start-up of chloroform pumping wells TW4-21 and TW4-37 during the second
quarter of 2015 is also expected to increase capture and chloroform removal rates. Overall
capture this quarter is about the same as last quarter.
'Background' flow through the chloroform plume was calculated as approximately 3.4 gpm as
presented in CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah). Pumping from
the chloroform plume during the current quarter (from wells MW-4, MW-26, TW4-1, TW4-2,
TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, and TW4-37) is
approximately 4.6 gpm, which exceeds the calculated background flow by 1.2 gpm or 35%.
Therefore chloroform pumping 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. Changes in concentration greater than 20% occurred in
wells MW-26, TW4-14, TW4-16, TW4-20, TW4-26, TW4-27, TW4-29 and TW4-30. Of these,
MW-26 and TW4-20 are chloroform pumping wells and TW4-16 is located adjacent to
chloroform pumping wells TW4-11 and MW-26. 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, changes in concentrations at chloroform wells are
expected to result from continued operation of nitrate pumping wells as the capture associated
with nitrate pumping expands and flow directions change locally.
TW4-26 is located immediately southwest of the plume boundary. TW4-14 and TW4-27 are
located immediately east of the plume boundary. Currently, TW4-14 is located cross-to
downgradient of TW4-4, and TW4-27 is generally downgradient of TW4-33. TW4-29 is located
within the extreme southeast portion of the plume and TW4-30 is located just outside the plume
boundary immediately east (and downgradient) of TW4-29. Fluctuations in concentrations at
these wells are expected based on their locations at the plume margins.
Chloroform at TW4-8 (which was non-detect from the first quarter of 2008 through the fourth
quarter of 2013) decreased from 770 !!giL to 634 !!giL. TW4-8 is located immediately east of
chloroform pumping well MW-4, where chloroform was detected at a concentration of 1,240
!!giL. From the first quarter of 2005 through the fourth quarter of 2013, the plume boundary
remained between MW-4 and TW4-8. The occurrence of elevated chloroform at TW4-8 is likely
related to its location along the eastern plume boundary immediately east of pumping well MW-
4. Changes in the plume boundary near TW 4-8 are expected to result from changes in pumping
and reduced dilution resulting from cessation of water delivery to the northern wildlife ponds.
Chloroform at TW4-8 is bounded to the north by TW4-3 (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 (4.5 !!giL).
The increase in chloroform at TW4-14 from approximately 1.5 !!giL to 4.5 !!giL, and at TW4-27
29
from approximately 1.6 ~-tg!L to approximately 2.1 ~-tg!L, is consistent with ongoing, but slow,
downgradient chloroform migration.
Chloroform pumping wells TW4-20 and TW4-37, and nitrate pumping well TW4-22, had the
highest detected chloroform concentrations of 21,600, 17,500, and 6,070 ~-tg/L, respectively.
Since the last quarter, the chloroform concentration in TW4-20 increased from 17,000 ~-tg/L to
21,600 ~-tg!L, the concentration in adjacent pumping well TW4-19 decreased slightly from 7,840
to 7,780 ~-tg!L, and the concentration in nearby pumping well TW4-21 increased from 339 to 390
~-tg!L. The chloroform concentration in nitrate pumping well TW4-22 decreased from 7,530 ~-tg/L
to 6,070 ~-tg!L. The chloroform concentration in nitrate pumping well TW4-24 decreased from
25.3 ~-tg!L to 22.8 ~-tg!L, remaining outside the chloroform plume. Nitrate pumping well TW4-25
remained non-detect for chloroform. TW4-25, located north of TW4-21, bounds the chloroform
plume to the north.
Chloroform at relatively recently installed well TW4-29 (located at the southern tip of the plume,
to the east ofTW4-26 and to the south ofTW4-27) decreased substantially from 631 ~-tg/L to 335
~-tg!L. Chloroform at TW4-30, located immediately downgradient of TW4-29, increased from
approximately 3.5 ~-tg!L to approximately 5.2 ~-tg/L. As with TW4-27, the change at TW4-30 is
consistent with ongoing, but slow, downgradient migration. Chloroform at TW4-29 is bounded
to the north by TW4-27 (2.1 ~-tg!L), to the east by TW4-30 (5.2 ~-tg/L), to the southeast by TW4-
35 (non-detect), to the south by TW4-34 (non-detect), and to the west by TW4-26 (1.8 ~-tg!L).
Chloroform at relatively recently installed well TW4-33 (located between TW4-4 and TW4-29)
showed a slight decrease in concentration, from 129 ~-tg!L to 122 ~-tg!L. Chloroform at TW4-33
is bounded to the north by TW4-14 (4.5 ~-tg/), to the east by TW4-27 (2.1 ~-tg!L), to the west by
TW4-23 (non-detect), and to the south and west by TW4-26 (1.8 ~-tg!L). This chloroform
distribution indicates that the plume southeast of TW 4-4 is very narrow compared to more
upgradient locations.
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for a slight
expansion near TW4-9 (which is just inside the plume this quarter), and a contraction near TW4-
16 (which is again outside the plume). The chloroform concentration at TW4-9 increased from
approximately 68 ~-tg!L to 74 ~-tg/L, bringing TW4-9 back inside the plume for the first time since
the fourth quarter of 2014. The plume boundary is now located between TW4-9 and TW4-12
(which is non-detect for chloroform and cross-gradient of TW4-9). The increase is attributable to
reduced recharge (and reduced dilution) from the northern wildlife ponds.
Nitrate pumping generally caused the boundary of the northern portion of the chloroform plume
to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-24 has been both
inside and outside the plume and remains outside the plume this quarter, likely due to initiation
of TW4-37 pumping in the second quarter of 2015 and reduced productivity at TW4-24 (since
the third quarter of 2014). Generally increased concentrations at TW4-6 and TW4-16 (both of
which were within the chloroform plume in the past) since the second quarter of 2014 indicate
that the plume boundary migrated to the southwest and re-incorporated both wells. TW4-6
remains within the plume this quarter and TW4-16 (with a concentration of approximately 46
30
f!giL) is again outside the plume. Increases at these wells beginning in the second 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. However, continued
operation of the nitrate pumping system is expected to enhance the capture zone associated with
the chloroform pumping system even though nitrate pumping may redistribute chloroform within
the plume and cause changes in the plume boundaries. Furthermore, the addition of chloroform
wells TW4-1, TW4-2, and TW4-11 to the chloroform pumping network in the first quarter of
2015, and TW4-21 and TW4-37 in the second quarter of 2015, is expected to have a beneficial
impact. Generally reduced concentrations at TW 4-6 and TW 4-16 after previous increases are
likely the result of initiation of TW 4-1, TW 4-2, and TW 4-11 pumping.
Continued operation of chloroform pumping wells MW-4, MW-26, TW4-19, and TW4-20 is
recommended. Pumping these wells, regardless of any short term fluctuations in concentrations
detected at the wells helps to reduce downgradient chloroform migration by removing
chloroform mass and reducing hydraulic gradients, thereby allowing natural attenuation to be
more effective. Continued operation of chloroform pumping well TW4-4 is recommended to
improve capture of chloroform to the extent practical in the southern pmtion of the plume. The
overall decrease in chloroform concentrations at TW4-6 from 1,000 f!g/L in the first quarter of
2010 to 10.3 f!g/L in the second quarter of 2014 is likely related to pumping at TW4-4. The
decrease in the long-term rate of water level rise at TW4-6 once TW4-4 pumping began, which
suggests that TW 4-6 is within the hydraulic influence of TW 4-4, is also consistent with the
decrease in chloroform concentrations at TW4-6 between the first quarter of 2010 and the second
quarter of 2014. Continued operation of TW4-1, TW4-2, TW4-11, TW4-21, and TW4-37 is also
recommended. Pumping these wells has increased overall capture and improved chloroform
mass removal rates.
Furthermore, because of the influence of TW 4-4 pumping, and by analogy with the
concentration decreases at TW4-6 and TW4-26 that occurred after initiation of TW4-4 pumping,
chloroform concentrations at TW4-29 and TW4-33 are expected to eventually trend downward.
Since installation in 2013, however, concentrations at TW4-33 appear to be relatively stable,
while, since the third quarter of 2014, concentrations at TW4-29 appear to be on an upward
trend. The relatively stable chloroform at TW4-33 and recent increases in concentration at TW4-
29 suggest that chloroform migration has been arrested at TW4-33 by TW4-4 pumping and that
increasing chloroform at downgradient well TW 4-29 results from a remnant of the plume that
continues to migrate downgradient (toward TW4-30, which bounds to plume to the east). The
influence of TW 4-4 pumping at the distal end of the plume is consistent with decreasing water
levels at both TW4-29 and TW4-33. Continued evaluation of trends at TW4-29 and TW4-33 will
be provided in subsequent quarters.
EFRI and its consultants have raised the issues and potential effects associated with cessation of
water delivery to the northern wildlife ponds in March, 2012 during discussions with DWMRC
in March 2012 and May 2013. While past recharge from the ponds has helped limit many
constituent concentrations within the chloroform and nitrate plumes by dilution, the associated
groundwater mounding has increased hydraulic gradients and contributed to plume migration.
Since use of the northern wildlife ponds ceased in March 2012, the reduction in recharge and
decay of the associated groundwater mound are expected to increase constituent concentrations
31
within the plumes while reducing hydraulic gradients and rates of plume migration. Recent
increases in chloroform concentrations at TW4-6, TW4-8, TW4-9, and TW4-16 are likely related
in part to reduced dilution.
The net impact of reduced wildlife pond recharge is expected to be beneficial even though it is
also expected to result in higher concentrations that will persist until continued mass reduction
via pumping and natural attenuation ultimately reduce concentrations. Temporary increases in
chloroform concentrations are judged less important than reduced chloroform migration rates.
The actual impacts of reduced recharge on concentrations and migration rates will be defined by
continued monitoring.
9.0 ELECTRONIC DATA FILES AND FORMAT
EFRI has provided to the Executive Secretary 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.
32
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc. on May 19,2016
Energy Fuels Resources (USA) Inc.
By:
Scott A. Bakken
Senior Director Regulatory Affairs
33
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 ubmitted. Ba ed on my inquiry of the
person or persons who manage the y tem, or those per on directly respon ible for gathering the
information, the information ubmitted i , to the best of my knowledge and belief true, accmate
and complete. I am aware that there are significant penalties for ubrnitting fal e information
including the possibility of fine and imprisonment for knowing violations.
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
34
Tables
Table 1: Summary of Well Sampling for the Period
Well SampJeDate Date of Lab Report
MW-04 3/9/2016 3/28/2016
TW4-01 3/9/2016 3/28/2016
TW4-02 3/9/2016 3/28/2016
TW4-03 3/15/2016 4/11/2016
TW4-03R 3/14/2016 4/11/2016
TW4-04 3/9/2016 3/28/2016
TW4-05 3/17/2016 4/1112016
TW4-06 3/22/2016 3/30/2016
TW4-06R 3/2112016 3/30/2016
TW4-07 3/22/2016 3/30/2016
TW4-08 3117/2016 411112016
TW4-09 3/17/2016 411112016
TW4-10 3/22/2016 3/30/2016
TW4-11 3/9/2016 3/28/2016
TW4-12 3/15/2016 4/1112016
TW4-13 3/16/2016 4/11/2016
TW4-14 3/16/2016 4/1112016
MW-26 3/9/2016 3/28/2016
TW4-16 3117/2016 4111/2016
MW-32 3/22/2016 3/30/2016
TW4-18 3117/2016 411112016
TW4-19 3/9/2016 3/28/2016
TW4-20 3/9/2016 3/28/2016
TW4-21 3/9/2016 3/28/2016
TW4-22 3/9/2016 3/2812016
TW4-23 3/16/2016 411112016
TW4-24 3/9/2016 3/28/2016
TW4-25 3/9/2016 3/28/2016
TW4-26 3/16/2016 4/11/2016
TW4-27 3116/2016 4/1112016
TW4-28 3115/2016 4/1112016
TW4-29 3/17/2016 411112016
TW4-30 3/17/2016 411112016
TW4-31 3/16/2016 4111/2016
TW4-32 3/15/2016 4/11/2016
TW4-33 3117/2016 4/11/2016
TW4-34 3116/2016 4/11/2016
TW4-35 3116/2016 411112016
TW4-36 3/16/2016 4/11/2016
TW4-37 3/9/2016 3/28/2016
TW4-60 3/22/2016 3/30/2016
TW4-65 3/15/2016 4/ll/2016
TW4-70 3/22/2016 3/30/2016
All sample locations were sampled for Chloroform, Carbon Tetrachloride, Chloromethane, Methylene Chloride, Chloride
and Nitrogen
"R" following a well number deisgnates a rinsate sample collected prior to purging of the well of that number.
TW4-60 is a DI Field Blank, TW4-65 is a duplicate of TW4-28, and TW4-70 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
I-1 Field Data QNQC Evaluation
I-2 Holding Time Evaluation
I-3 Receipt Temperature Check
I-4 Analytical Method Check
I-5 Reporting Limit Evaluation
I-6 Trip Blank Evaluation
I-7 QNQC Evaluation for Sample Duplicates
I-8 QC Control Limits for Analyses and Blanks
I-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 A
Site Plan and Perched Well Locations White Mesa Site
TW4-19
EB
MW-5 •
TW4-12
0
TWN-7 ~
PIEZ-1
fOj
perched chloroform or
nitrate pumping well
perched monitoring well
temporary perched monitoring well
temporary perched nitrate monitoring
well
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 FIGURE
H:/718000/may16/Uwelloc0316.srf I A-1
TabB
Order of Sampling and Field Data Worksheets
(
Order of Contamination for 1st Quarter 2016 Chloroform Purging Event
Chloroform
Well Sample time Levels Rlnsate date/time
TW4-03 3' 11:,1 lk Cb3'1 ND
TW4-12 ·J!,~..;/11.;, ObS·.:. ND
TW4-28 :>ILS'.U. OL,S(. ND
TW4-32 ·>hS/j(. o/CS ND
TW4-13 )/1!../IC11 Qb42 ND
TW4-36 3/lb/IC. Ob'"i'( NO
TW4-31 ')/lb/)b C£S1 NO
TW4-34 '!>llbllb Ole...~ ND
TW4-35 '3/l~l.b C7 L> ND
TW4-23 :;,/1.(./\!Q o]tl NO
-MW-32 J/1.2./jL, 1'~-:l,D NO
TW4-25 :>1'1/14 oqpL. ND
TW4-14 ~/ll:,lll.;. O]'Z.t.j 1.46
TW4-27 '3/lblt(..ci,'Si, 1.6
TW4-26 'V ib/1!. CJ"'8 3.45
TW4-30 ~/1]/j.l,. QJSD 3.48
TW4-05 31 l?flb 000'1 11
TW4-24 3 19/ll. \Oct! 25.3
TW4-18 rVFiht:, c~r?:> 52.9
TW4-09 Y IJifk oKZ.Z 68.4
TW4-16 )fiJI!(. Oli.Z.~ 112
TW4-33 3/11flk o!3~ 129
TW4-21 314/!(,. 0'1 '17 339
TW4-29 ;YIJ/11> ogy.s 631
TW4-08 :JIJI!k o&Sll 770
-TW4-06 3/z:ZI!t. o~.Sl 843
._ TW4-07 J/2Zh QiS.:Sg 847
TW4-01 :;1"/rl. 1'2..11 1040
TW4-04 st"/11.. 12.6 1190
MW -04 :, 1q 'lk. 11...10 1200
-TW4-10 '3 .-z:z.-u. o'lO(. 1350
TW4-02 '?:,/'1/ !!, ! l.OI 2070
MW-26 Y911l> ·1olili 2680
TW4-11 :,ft;\t!{:t d5.? 2730
TW4-22 :»/'l/\Cz tO!A 7530
TW4-19 3/0./lb 1~'3>!> 7840
TW4-20 -:':>14 /lt. i03 r 17000
TW4-37 :3/"!!J h !oZ.? 19500
--TW4-60 D.l. Blank 3hVl(. 1~:00
2..'!. TW4-65 Duplicate ·>n)/1!, Q(.5(.
f'\;-.:-TW4-70 Duplicate -:'1/e?)ltq rZ.3D
~z. Comments:
Name:
Water
level
Date:
Well
Depth
141 -,~L.}-03R-O::jJLi20ib J'J29
101.5
107
115.1
102.5
99
106
97.2
87.5
114
132.5 Bladder pump
134.8 Cont. Pumping
93
96
86
92.5
120
112.5 Cont. Pumping
137.5
120
142
87.9
121 (..C.,,+ p"',.,f'':j
93.5
125
-97.5 'Twi·06R_u~2.1-'Z.Oi{, IC:/::.lj
120
110 G.:-,.,+. Pv.mJ>•n:\
112 Cont. Pumping
124 Cont. Pumping
111
120 c. ... ....\ g,_~'~'~r :-.~
122.5 Cont. Pumping
100 ev . .J p,,M?·"..~
113.5 Cont. Pumping
125 Cont. Pumping
I 06 Cont. Pumping
112 Cont. Pumping
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ S.i' Qt:~:Pirohr C.h 1 orOf'orfl'l ZO I Co
;' See instruction
Location (well name): ._I __ M._W_~O_Y,_ ________ __.
Sampler Name
and initials: l~nna-J:}oJI,'d~hfJ
Field Sample ID MW-o4-03oq-zol!:.
Date and Time for Purging ~.-1 -~..!..~-~.:..;.(_'l.b_l-=~-----....1
Well Purging Equip Used: (![]pump or [QJ bailer
and Sampling (if different)!~,_ /\/.__;_~.;...14 ________ _J
Well Pump (if other than Bennet) I C:OfJJI11AOvt.S
Purging Method Used: [QJ2 casings [QJ3 casings
Sampling Event I Q\J\o..r}~d.!1 C..l'\lorOfOnYJ Prev. Well Sampled in Sampling Eventl ,_ _1\_W_~_-_o_z _____ __,
pH Buffer 7.0 1....__7-'-,'-() ___ ___.
Specific Conductance!~,_ _l;...D..;..O;...b ___ --.JI !!MHOS/ em
Depth to Water Before Purging I 7~ 1 & 0
Weather Cond.
Time 1 l7.1b I Gal. Purged I 1)
Conductance I l~S$.( I pH I 7,37
Temp. °C I lq.i~ I
Redox Potential Eh (mV) I zs~ I
Turbidity (NTU) I 6 I
Time I I Gal. Purged I
Conductance I I pH I
Temp. °C I I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater
I
I
I
I
pH Buffer 4.0 Lj,O
Well Depth(O.Olft): ~.-1 ..;_;lz_:q~.o_o __ _~
Casing Volume (V) 4" We ll:~(.653h)
3" Well: · 4)-(.367h)
,7..
Ext'l Amb. Temp. ·c (prior sampling event),_! 4_,_0 __ ___.
Time I I Gal. Purged I I
Conductance I I pHI I
Temp. oc I I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
Time I I Gal. Purged I I
Conductance I I pHI I
Temp. oc I I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = ._I _4_,_3 __ _..
Time to evacuate two casing volumes (2V)
T = 2V/Q = I7.S'-I I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated 0
N arne of Certified Analytical Laboratory if Other Than Energy Labs A\JA-L
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs ~ D 3x40 ml D "!] HCL f) D
Nutrients ll D 100 ml D tl H2S04 tJ D
Heavy Metals D D 250m! D D HN03 D D
All Other Non Radiologies D D 250ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) !] D Sample volume D [I D ~
C..).,\oriJ~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I ....::.Z_L_5_7 __ __. Sample Time ._I _l'Z_-1 D ___ ___..
Comment
: ~ See instruction
An·; \JJ. Of\ $-i+e ~ I'Z.O/
~Mp\e~ c.o )Jec.ted ,._t
~1\flef" AA~ G-,.._r,;(\. pre.s.ent ··h c.olleL-t" ~f }e~.
l '2.10 , W(,(h:r l,t0a. ~ G /f!a..r
L~ ~;to& V\+ \-z.rz
MW-04 03-09-2016 I Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I J~T' Gv.b.rfu Chl oro torm "ZD I.b
Location (well name): ._l_-r~W~L\.._-.....;.0_1 _________ __.
Field Sample ID I Tw y-oL o~o~z.o 1 "
Sampler Name
and initials:
See instruction
Date and Time for Purging I 3/ '1 / "Z.O lb and Sampling (if different) 1\1/lt. ~--~----------------~
Well Purging Equip Used: [![]pump or [QJ bailer Well Pump (if other than Bennet) I Gonfn'l \AOV..~
Purging Method Used: [1[]2 casings [QJ3 casings
Sampling Event I QU\:o..Ff~~~ C~\ orO+orm Prev. Well Sampled in Sampling Eventl._ _M_UJ_-_0_lJ ______ _,
pH Buffer 7.0 I .D pH Buffer 4.0 4.0
Specific Conductance!~... _l;.:;O~O.::;.O ______ ___JI !!MHOS/ em Well Depth(O.Olft): .... 1 _11_0_,0_0 __ ____,
Depth to Water Before Purging I ~9. 9l Casing Volume (V) 4" Well :l l b,~S 1(.653h)
3" Well: () (.367h) '-------1
Weather Con d. Ext'l Amb. Temp. ·c (prior sampling eventl .... l -'lo_• __ _,
Time I ~"2.-\/ I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I 2.3~5 I pH I 7,?.5 I Conductance I I pHI I
Temp. °C I 1s.-z.c: I Temp. oc I I
Redox Potential Eh (mV) I -z.Z:~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I L'1. I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (mV) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 == I \5 .o
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two casing volumes (2V)
T == 2V/Q = I 7., 18 I
0
6
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I ...:..A.:...;W__,_.ft_L _____ __,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs IE D 3x40 ml D [!:) HCL ~ D
Nutrients ~ D 100 ml D ~ H2S04 1!1 D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D 0 250m! D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume D ~ D 'f!l
Chlorick If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 'II. G.C Sample Time 1'2.17
Comment
rJ, See instruction
Aa:>Jed. 01"\ .sl+c. o..+ lZI'i ~nner "f\~ G-o..rrlr'\ preserrt fb c.olle.cf s.a.mpleS.
S~Yrlp)es c.o))ectea ~+ rz.n 1..0J'er v.:>~.s. G'eo.r
Le# s.li--c tA-t 121~
TW4-0l 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I JS-r Q"~rte.r Gh lor~rn-:t 'ZO 1(,
Location (well name): ._l11--'-"v.>.:....4_,__-....::0....::Z:.:-:::......... _______ ____J
Sampler Name
and initials: I :::=r;11n e(" Ho Jl 1 'J,.~ htJ
Field Sample ID
Date and Time for Purging I :)j~/Z6l"-.__~~~~----~ and Sampling (if different) .__M--'-V.'-/t _______ ___,
Well Purging Equip Used: [Q]pump or IT!] bailer Well Pump (if other than Bennet) I Co a }J ntJ.~ vt..>
Purging Method Used: (ID2 casings [!!]3 casings
Sampling Event I G"'"'""fec\j Gh lorofbrm Prev. Well Sampled in Sampling Event ._I_'"T_-_"J_Y_-_1 ) _____ ~
pH Buffer 7.0 ._I _7._,,_0 ___ ___, pH Buffer 4.0 y,o
Specific Conductance L-1 _lOo_i> ___ _.I!!MHOS/ em Well Depth(O.Olft): l'Z.O,oo .__ ____ ___.
Depth to Water Before Purging IJo,, S9 Casing Volume (V) 4" Well:l 2b.3<6 1(.653h)
3" Well:L-. _o ___ __,_(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! Cf_5 --~
Time I }"Z.O l I Gal. Purged I I) I Time I I Gal. Purged I I
Conductance 1 3\.jO~ I pH 17,23 I Conductance I I pHI I
Temp. °C I lS.l9 I Temp. oc I I
Redox Potential Eh (mV) I 2-57 I Redox Potential Eh (m V) I I
Turbidity (NTU) I l.o I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate Calcu'lation
Flow Rate (Q), in gpm.
S/60 = I 1 g . ()
Time to evacuate two ca. ing volumes (2V)
T=2V/Q= I 2.'13 I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated I o
Name of Certified Analytical Laboratory if Other Than Energy Labs
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs ll D 3x40 ml D IE HCL 1!1 D
Nutrients rn D 100 ml D I1J H2S04 -1!1 D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 0 D
Other (specify) ~ D Sample volume D Ill D ~
G'h I or Ide If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I -=?>=S_,_, Y-1..,;,...1 __ __, Sample Time }'Z.DI
Comment
l ~ See instruction
A rr; \) ea on .sJ+-e. l'J II s ~ lAfln-t.r MJ G-o..rr•'11 pr-~soUJ:J-fo
.S"-Mfl~ c.o llecJeJ ~r l'Zo\ IN<A-+.e.r lA)~ C..\ecJ
l~fr !:,It~ "'-+ )'(.(.)~
TW4-02 03-09-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \~1 Q\1\o,r+et'& Gv...o..r-1-er C\-!lorOf'orTYJ 'Z.DI6
r See instruction
Location (well name): ~.-1 "T\)....;..__4..:..-....;0:::..:C3=---------____..J
Sampler Name
and initials: I ::r;_l"lr>e:r HoJJ·'Cl~/1ii
Field Sample ID
Date and Time for Purging L..l3---'-/_llf"-'-/_'Z_lJ_l_b ____ _, and Sampling (if different) I '3/15/zo 1(. ~~~------~
Well Purging Equip Used: ~pump or @]bailer Well Pump (if other than Bennet) IGrunJ"R,s
Purging Method Used: ~2 casings @]3 casings
Sampling Event I Qv.o..rh:.l~ Ghlo(of6or1 Prev. Well Sampled in Sampling Event 1-rwy -03 R
pH Buffer 7.0 IL-7.---'-, o ___ ____J pH Buffer 4.0 I Y.o
Specific Conductance ~.-l_)o_o_o ___ ........ h.tMHOS/ em Well Depth(O.Olft): I 1'11. 00
Depth to Water Before Purging I 5'-./ 0 Casing Volume (V) 4" Well:I 55.6Ll 1(.653h)
3" Well: 0 (.367h) ,__ ___ ........
Weather Cond. Ext'l Amb. Temp. "C (prior sampling eventll<--.:...;11_6 __ ........
Time I 1909 I Gal. Purged I no I Time I I Gal. Purged I I
Conductance I \71.(.. I pH 1 b.3g I Conductance I I pHI I
Temp. oc I 19.19 I Temp. °C I I
Redox Potential Eh (m V) I 93~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I H5.9 I Turbidity (NTU) I I
Time I 063K I Gal. Purged I 0 I Time 1Db4l I Gal. Purged l o I
Conductance I pog I pH I s.Gf1 I Conductance ll71Y I pH lb.C>I I
Temp. oc 119.ZJ I Temp. °C 114. tZ I
Redox Potential Eh (mV) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged liD gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca i ng volumes (2V)
S/60 = I 10.0 T = 2V /Q = I \ I. DO I
Number of casing volumes evacuated (if other than two) I l. '~~
If well evacuated to dryness, number of gallons evacuated no
Name of Certified Analytical Laboratory if Other Than Energy Labs L..l _,_AL.:.W_,A-'-=L _____ _,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs m 0 3x40 ml D rE HCL m
Nutrients [] 0 lOOml 0 ~ H2S04 og
Heavy Metals D 0 250 ml 0 0 HN03 0
All Other Non Radiologies D 0 250ml D 0 No Preserv. D
Gross Alpha 0 0 1,000 m1 D 0 HN03 D
Other (specify) Cl;j D Sample volume 0 Ill D
C h lDf' jJ-e_ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I )3~.7~ Sample Time 1._0_6_3_1-'-------'
See instruction
Comment
Arr\\Je~ 01\ sl+~ ~-t 131..\~ -r'Mn~r o."J,. c-o-rr•'n preS<!tl-r +or pu..r~<: • Pv.r~c: b~.jtllt'l o..-r
1353 ?u..,~ed. \Nell ~r o.. fot.,.,J of' 11 mlnv...+~~. Pu..r'Ccl (,.)dJ Jrt]. wo:t~r I.A.)4S, c.Jear
fIN"~ 'C. efldd. ~A.-t 1404. Left-S. i+~ ~+-)YO(;.
An·i\Jed. 01"\ si+e. o..+ Ob~b JoJHl~(' a.()d. Go.r6n
WtA.~ 57.25 S"f"\PI~ bc:>.:JeJ o..t Ob3tl
pre.serd-+a c,ollec.t" .St~f\'1 pl.es,
Le.f'f $ ;+~ tA.t OGY'2
TW4-03 03-14-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
0
0
D
D
~
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I l 5"1" Q\API.(fer GhlorOf'orrYI 'Z.DI(,
See instruction
Location (well name): l.___-r_w_~_-_0_3_R _______ ___.
Sampler Name
and initials: I -r;f'l nel'"' t'Jd ll •d4ii.::j/"1"'H
Field Sample ID
Date and Time for Purging I '3/lLI/20ik. and Sampling (if different) /'1/A
Well Purging Equip Used: IJ[jpump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [QJ2 casings [QJ3 casings
Sampling Event I GhJ.Ar't~<"b Gh\orOfon'll Prev. Well Sampled in Sampling Event LI_"T_W_Y_-_I_Cj ______ _J
pH Buffer 7.0 7.0 pH Buffer 4.0 q.o
Specific Conductance Ll _\_O_o_o ___ __JI ~-tMHOS/ em Well Depth(O.Olft): '-I _o ___ _..
Depth to Water Before Purging l..___o ___ ....~ Casing Volume (V) 4" Well:~_o ___ --tl(.653h)
3" Well:_ C> . (.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)l._1_0_0 __ _.
Time I l'Z>:Z~ I Gal. Purged I 13.0 I Time I I Gal. Purged I I
Conductance I o.ZJ I pH I7.2.S I Conductance I I pHI I
Temp. °C I II.ZJc; I Temp. °C I I
Redox Potential Eh (m V) I q-z.l'6 I Redox Potential Eh (m V) I I
Turbidity (NTU) I l ,'~ I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. °C I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged ISO gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I \0,0 T = 2V /Q = I 50 I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated 0
Name of Certified Analytical Laboratory if Other Than Energy Labs L-1 ..:...A:....:.W....!A~L=--------J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs 129
Nutrients Ill
Heavy Metals 0
All Other Non Radiologies 0
Gross Alpha 0
Other (specify) ~
c. 'h \o{'; Je.
Final Depth L-1 _o ____ _J
Comment
Arriveci 01'\ ~ite
R;f\s.(A. te. b~~Q.,
o ~ n I w".:rer:
Le.Q-~ ;+e ~}
o...+ 1~17.
o..i--l~\.S
SAMf>)e.S
J~3Z
N specified below) y N y
0 3x40 ml D m HCL 13
D 100 ml D Ill H2S04 El
D 250 ml 0 D HN03 0
0 250 ml D D No Preserv. 0
0 1,000 ml D 0 HN03 0
0 Sample volume 0 czg 0
If preservative is used, specify
Type and Quantity of Preservative:
Sample Time Ll ).:.....3_7._9...;...._ _ __;
, ,..~ See instruction
-r;fll'lef" o.I'\J.. G().rr;fl p r'e#i)-cflt +~ C.t!!l/i!c.+ .S(;..Mpl~s .
Pv..l'\'JpeJ. ~o {;..t~,./lo~ ~ o~F L0o.+er o.I'H~ /DO G(/\.1/ons
collec+ed o..+ 1'329
TW4-03R 03-14-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
0
D
0
12
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \~1 Qu.o.f'kr G\11 or of~ rM "Z.D 14
Location (well name): ._I _i";_w_~....;..-_0__,_~------------'
Field Sample ID 1-n..J'-{-0 1L 03D~ZO/(.
Sampler Name
and initials:
See instruction
Date and Time for Purging Ll3_f_~:_/_'t..._O_l'-;;__ _____ _, and Sampling (if different) ._I /\/._:;-:_~ ________ _..
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) I Gon:h~lAO\AS
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Qv.tAf'+ec~ G)1 lorbfa rtl'l Prev. Well Sampled in Sampling Event .... 1_-r_w_~_-_D_J _____ __..
pH Buffer 7.0 1.6 pH Buffer 4.0 q,o
Specific Conductance Ll_l_Do_6 ___ __.I!!MHOS/ em Well Depth(O.Olft): I Jl'2.00 .___,_:...._ ___ ___.
Depth to Water Before Purging I 7Z.,3C. Casing Volume (V) 4" Well:l '2.5, <68 1(.653h)
3" Well:.__ o ___ ___._ (.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)._ll_l_6 __ _,
Time I \:Z:~ I Gal. Purged I () I Time I I Gal. Purged I I
Conductance I -z.~ol I pH I 7.11 I Conductance I I pHI I
Temp. oc I lG .. oz I Temp. oc I I
Redox Potential Eh (m V) I "2}~2 I Redox Potential Eh (m V) I I
Turbidity (NTU) I \ 1 # 0 I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
-Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate CalculaLion
Flow Rate (Q), in gprn.
s16o = I \ l.o
Time to evacuate two casing volumes (2V)
T=2V/Q= I q.70 I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs L..:l tf~W"'-A-..:..L ______ __.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs [I
Nutrients '[]
Heavy Metals D
All Other Non Radiologies D
Gross Alpha D
Other (specify) '(]
G'h\ or;de.
Final Depth!._ 7_~_,'f.;._q __ __,
Comment
Arrl\J-e.!J. on ~;+-e. a-+ I7.'Z:Z.
SQ.mfle~ c.()\leckJ CA.+
l e. .Q. ~ tre. ~ + rz:z. E
N specified below)
D 3x40 rnl
D 100 rnl
D 250 ml
D 250ml
D 1,000 m1
D Sample volume
Sample Time IZZ5
TW4-04 03-09-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
y N y
D '!I HCL ~
D !] H2S04 e::J
D D HN03 D
D D No Preserv. D
D D HN03 D
D lJ D
If preservative is used, specify
Type and Quantity of Preservative:
See instruction
pr~~~,t +D c.ollec.t
mos-r\c::j uie.t>r
N
D
D
D
D
D
~
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 1 !:.T Q v.o..rfel" CJl locO"ft)(M "ZO J..b
/". See instruction
Location (well name): ._l!i_W_Y_-_0-=~=------------'
Sampler Name
and initials: l~nner' RoJiiJ~/'7'13
Field Sample ID
Date and Time for Purging ~_I_'3__;/_J..::.6.:..../2f>_:....:l.4=--------' and Sampling (if different) L..:l31=.!.....!1....:..7..:.../-=2..:...0.:....;lb=---------..J
Well Purging Equip Used: (IDpump or [QJ bailer Well Pump (if other than Bennet) L.:IG::....:....:ru...:....n__;(}.:...~.:........:~=------__J
Purging Method Used: [![12 casings [QJ3 casings
Sampling Event I QWJ.. .. r+erb Ch lor;Rlrm Prev. Well Sampled in Sampling Event ~_l-ri_VJ_4_-_3_0 _____ ____,
pH Buffer 7.0 7.0 pH Buffer 4.0 4.0
Specific Conductance Ll ...:..I o_o...:c.:...._ ___ _..JI r.tMHOS/ em Well Depth(O.Olft): I \20,00
Depth to Water Before Purging I "'4. SS Casing Volume (V) 4" Well :,.3b.7..0 ,(.653h)
3" Well :_ 0 (.367h) ......_ ___ ___,
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._l _(?_0
__ .....J
Time I IOY1 I Gal. Purged I 70 I Time I loY& I Gal. Purged I go I
Conductance I )'-\'\7 I pH I C) I '2.S I Conductance l14q"Z I pH I 6.27 I
Temp. oc l \5.'29 I Temp. oc I p;,-z.3 I
Redox Potential Eh (mV) I 9-z.~ I Redox Potential Eh (m V) I Y 21 I
Turbidity (NTU) I ~.~ I Turbidity (NTU) L 3ol J
Time l ~~u ' I Gal. Purged I qD
1644 I Time 1 to!;.o I Gal. Purged 1100 I
Conductance I Pi111 I pH I ~:z.; I Conductance I lig-z. I pH I b.'Z8' I
Temp. oc I \ S.'l~ I Temp. oc 1 1~.-z.q I
Redox Potential Eh (m V) I 9 Z:'b I Redox Potential Eh (m V) I """Z7 I
Turbidity (NTU) I "3. ~ I Turbidity (NTU) I ~.~ I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged loo gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I 10.0
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca ing volumes (2V)
T = 2V /Q = I 7. 2 q I
l o
lo
Name of Certified Analytical Laboratory if Other Than Energy Labs L.:l A-'-\J.;.._;_A--=L;__ _____ __,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs [] D 3x40 ml D 1a HCL U9 D
Nutrients 11 D 100 ml D IB H2S04 ~ D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250m! D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) 10 D Sample volume D fJ D lJ
Ch lor ~je. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I ~b, IS Sample Time IL-o=-g.::!..:0:::.._"\_!___--1
Comment
,j See instruction
Aa;veJ. on ~i+G ~-t \038 lOJJtle!' MJ 6-Mr-in Preset'!+ -hr pv.~e . f'v.rje be_,s111, 1).-f IO'iO
'Pw(1€~ lt..)e)\ -Fo( 6o.. +o+CA.l or'\() P1inv..+e). Pu.~l\~ e:tlOeJ. oct" WSD
\0fJ.-tif t,.)~ L.\eo..r. LeH-" .srte ~::r )052.
/i<ri'oJe~ M' ~~.e "",y 0<60(. ~ne(' O'itl~ G-o-.rr;fl presen-1-+o Ct:>1!ed-.SaMples.
wo...-kr IN~s ~L\.[:{3 s.a.mplGS bo-.;led ~} oro~
TW4-05 03-16-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT l-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ rr Qv-.o.r+er Ch lot'l>'Fon•.., 'Z Dl'
Location (well name): ._1_~ __ '-\_-_0b _________ ____.
Field Sample ID 1 -rw9 -oG .... 63 zz:zo\1>
Sampler Name
and initials:
See instruction
Date and Time for Purging I 3/Z..I f"ZDI"b and Sampling (if different) 3/Z'Z./z.al-b
Well Purging Equip Used: ~pump or [QJ bailer Well Pump (if other than Bennet) I Gr-v..11CXotQS
Purging Method Used: IT!]2 casings [QJ3 casings
Sampling Event I Qv.o.r+<.rlj Ch \of"bforrV) I Prev. Well Sampled in Sampling Event I JWL\-O-b K
pH Buffer 7.0 L-1 _7_, O ___ _J pH Buffer 4.0
Specific Conductance IL..._l _Do_D ___ __,l ~-tMHOS/ em Well Depth(O.Olft): I en, 5D
Depth to Water Before Purging I ]'Z. '2.D Casing Volume (V) 4" Well:l\". 5'2 1(.653h)
3" Well: l5 (.367h) .._ ___ _,
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl._l l_l_0 __ _,
Time I I 7.7..~ I Gal. Purged 1 :~.2>3.. I Time I I Gal. Purged I I
'30·~
Conductance 1 ~03 I pH I '-.Yt I Conductance I I pHI I
Temp. °C I 15.)g I Temp. °C I I
Redox Potential Eh (m V) I YE3 I Redox Potential Eh (m V) I I
Turbidity (NTU) I LSD I Turbidity (NTU) I I
Time I Og5() I Gal. Purged I "0 I Time lo.85 -z I Gal. Purged 10 I
Conductance I '3"2.6-z... I pH I ?;:z."' I Conductance I '3-z.c:~ I pH I i':.'45 I
Temp. oc I i5.35 I Temp. °C I 15.3~ I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill· Groundwater Discharge Permit Date: 06·06-12 Rev. 7.2 ·Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 33.33 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I )0. 0 T=2V/Q=I3.30 I
Number of casing volumes evacuated (if other than two) 1-z..OI
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs OJ D 3x40 ml D [!I HCL ~ 0
Nutrients eft 0 100 ml 0 flJ H2S04 ~ D
Heavy Metals D 0 250 ml 0 D HN03 D 0
All Other Non Radiologies D D 250m! D D No Preserv. D 0
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume 0 ~ 0 [!'
C'h \or~d< If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I ~Y · $ Sample Time
Comment
, J.. See instruction
Au;ve~ on site. o..t l22lf --r;.nne• o.nJ. G-"'rf'•'n p("e.s.e.fl} fo r pv.r6e. Pv.r~~
?v-.,...~e~ vJell t;, o... .totCo\1 cr.P 3 M;V\v..T~ lS Sec.on6s.. Pu..r~f~ vJe.ll Jr.j1
-
l7.'Z.1, w~·hr ~~ c.loud~-L~* sit<: dt+ \'Z.'Z>"Z.
b~an cJ-}2'2.6
P ~.~.~ c enJ eJ. ttt"
A,r:"\Je-6. on &J'+e o..t O~'lK -r;l'ln-e.r M J. G-rArf";fl pre.~-efl~ ~
D~tl, ~ w~ter (,.)~ 7Z.?.J.. S."'«tp16 b~l'leJ ~t 08'.51
C..l> JJeJ-~~tVI?l~.s.
Le...ft s1te. ~t 08 53
TW4-06 03-21-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: \ ST Gv..o..rfc:r-Ch 1 orotorm ZDIJ..
Location (well name): 1 --;:~ "'TWI.\-D'-R
Sampler Name
and initials: Ffn"<f No ll•'J"lj /Tit
Field Sample ID
Date and Time for Purging ll-_3_/_-z._t/_'Z_o_J.4 ___ _J and Sampling (if different) L-1 r:_.:..~....:..-J_-__ M_V_A _____ __J
Well Purging Equip Used: ~pump or [QJ bailer Well Pump (if other than Bennet) I c:n-u..f\d:fo.s
Purging Method Used: [!!]2 casings (QJ3 casings
Sampling Event I Q\A~r+erE ChI Of'of~rtv~ Prev. Well Sampled in Sampling Event L-1_---r_w_Y_-_O_~ _____ _J
pH Buffer 7.0 7.0 pH Buffer 4.0 9.D
Specific Conductance Ll _l_oo_o ___ --.~I!!MHOS/ em Well Depth(O.Olft):
Depth to Water Before Purging!._ _6 ___ _, Casing Volume (V) 4" We.ll:,I--O----tl(.653h)
3" Well:. o (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)IL_\ l_6 __ _J
Time I 1 03_:3. I Gal. Purged I ~w-a. \Jt> I Time I I Gal. Purged I I
Conductance I S.J I pH I 7,"3,7.. I Conductance I I pHI I
Temp. oc I ji~,5~ I Temp. oc I I
Redox Potential Eh (m V) I q\3 I Redox Potential Eh (mV) I I
Turbidity (NTU) I l.o I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged \.S.D gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I I 0 .l>
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two casing volumes (2V)
T=2V/Q= I 0 I
0
Name of Certified Analytical Laboratory if Other Than Energy Labs AWAL
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs Ill D 3x40 ml D Ill HCL m D
Nutrients M D 100 ml D Ill H2S04 ~ D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) []j D Sample volume D Ill D J:!t
G h'oride... If preservative is used, specify
Type and Quantity of Preservative:
Final Depth l.___o ____ __. Sample Time \03'-l
Comment
' .-J See instruction
Arr;vej or. si+e a..+ \D\~ -,-;:nr~er o.t'l~ G-""(df\ pr~~~(\t --h;'r 'R;nsA..+e. 'R;1l~~+~ h\j'v'
li\.}.-10'2.0 'Pv.rVJpea Sb G-o..llortS at .Sbli:f w~+~r, '\,J IOO v;r.J/on.s oF' Dr
Wt>..+-cr~ Sc..rv~ples Go llec..+-eJ. G...+ \03L\, L~Ft-.s/-h:. o..t 1036
TW4-06R 03-21-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I l Sl Guo.rfer Ch lof"l>f6rm Zo I .C.
Location (well name): ._l_li_W_4_-_D_/ _________ __,
Field Sample ID I1"'W4 -o"7_rozzzol6
Sampler Name
and initials:
See instruction
Date and Time for Purging I ~/z 1/ zo It and Sampling (if different) 3/zi/zol Z::
Well Purging Equip Used: OO]pump or [QJ bailer Well Pump (if other than Bennet) I Gr\.)..na:fas
Purging Method Used: (!!]2 casings [QJ3 casings
Sampling Event I Qv.o..rtedj ~ Ghloi"lXJbfml Prev. Well Sampled in Sampling Event ~.-1_1\:_W_'-f_--_D_~ ____ ___.
pH Buffer 7.0 7.0 pH Buffer 4.0 L\.o
Specific Conductance ._I _lo_o_o ___ _,jl ~-tMHOS/ em Well Depth(O.Olft): ~.-1 ..:.....l'Z._O...:..,O:_O __ ____.
Depth to Water Before Purging I 7 b. Z 7 CasingVolume(V) 4"Well:l '2.3,55 1(.653h)
3" Wen:._. _o ___ ~.(.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)._ll5~0--~
Time I h .. s~ I Gal. Purged I '-i I Time I 12.5'1 I Gal. Purged I [:,l> I
Conductance I lG.os I pH I "· s, I Conductance l lbOD I pH I C,,5'2 I
Temp. °C I lq,qj I Temp. oc lllf,qt:. I
Redox Potential Eh (m V) I '1>5{:, I Redox Potential Eh (m V) I '353 I
Turbidity (NTU) I S{ I Turbidity (NTU) I CJ I
Time I 1;.oo I Gal. Purged I ,"0 I Time I 13£>, I Gal. Purged I :zo I
Conductance I )S.7'"1 I pH I G.5z I Conductance ll570 I pH I "·S3 I
Temp. °C I 1~.9~ I Temp. oc I \4 ·.:r1 I
Redox Potential Eh (m V) I "3EiZ I Redox Potential Eh (mV) I '35t> I
Turbidity (NTU) I ~ I Turbidity (NTU) I j I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Er.rata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 10 gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I \0.0
Time to evacuate two casing volumes (2V)
T=2V/Q= I 5 .7/ I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I A_~_,_1J=-L ______ __,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs (] D 3x40 ml D !] HCL []
Nutrients "[] D 100 ml D tJ H2S04 ,.LJ
Heavy Metals D D 250 ml D D HN03 D
All Other Non Radiologies D D 250 ml D D No Preserv. D
Gross Alpha D 0 1,000 ml D D HN03 D
Other (specify) ~ D Sample volume D 'f] D
Ch\o,,'J~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I \ l.S. J 'Z 0 Sample Time 0~8'
Comment
,_.J, See instruction
Arc-'.ve~ 0(1 .s+e "'t I'Z.5'Z. ---r;.f\1'\U MO. G~rr;f\ pre..S~,t +Dr pv..r~e. PIAr~~ be6~fl o..+ rzsy
Fv..r~d. well +or ,.,_ ·hJ,.) ot' 7 M·'n~~>. 'Pv..r~e <=ndeA ~ 1:301. ~+Gr U,)£4.$ clea..r
Le-A-~l+c::. A...Y )30~
~ Of{.!;.b -,--MIIt:f" If\(\~ cr~rr:n, pre.s.c~ +b c,o)lec.J-511tY/f l~s .
~"'Mple6 b~;lcA ~+ o &.s&' Le-.{+ s*c ~-1 o~oo
77, \'l.
TW4-07 03-21-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
D
D
D
~
2 of2
Mill-G.r.pundwater Discharge Permit (
Groundwater Mor;itonng Quality As~uranre Pta" (QAPI ·-( Date: 06-()6'12 Rev. 7.2-Errata
ATTACIL\fENT l-2
WHITE MESA URAl\llJM. MILL ' • See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Descr~tionofSamptingEvent ~~~l s_T~~~~~a~r~-~-r~C~h_lo_r_o_~~-r_M~2_0_/~~~~~~~~~~~~~~~~~
Location (well name): ._I T_._.W~4 ..... -_o=-· =~~---------"'
Sampler Name
and initials: 1--rP.nner }1j I •tl~,'lh1f
Field Sample ID I T '-'J4-0fL03 1T20lb
Date and Time for Purging IL.....-:3 c:.../.:...::i b=/_,2=~"'-=-~~~~--' and Sampling (if different) IL-'3/=--'J'-'7"'-'./_Z;..;..D""''''---~~---'
Well Purging Equip Used: ~pump or [Q] bailer Well Pump (if other than Bennet)! w G-""-'-r..:...""'.:..:;nJ:::...{).:..:.<..;s=--~~~-'
Purging Method Used: ~2 casings [9]3 casings
Sampling Event I Qv;o,rterl') ChI 0 rofort¥1 Prev. Well Sampled in Sampling Event ~-.l·-n_~_4_-_z_1 _____ ___.
pH Buffer 7.0 pH Buffer 4.0
Specific Conductance I~.......:.I;:..;OOc...:.u~~~--'IJ.IMHOS/ em Well Depth(O.Olft): I \Z'S.OO
Depth to Water Before Purging I ~0 , 07.. Casing Volume (V) 4" Well:l 2..C\ .37 1(.653h)
3" Well: o (_%711) ~~~~-'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)~-..1 .:..::1'3'-c __ _,
Time I ~~ik. I Gal. Purged I SD I Time I )SI7 I Gal. Purged !60 I
Conductance I 4~1Y I pH I b ,ll I Conductance 1 '-~ £<1Lf I pH I b . I'Z. I
Temp. °C I \~,04 I Temp. oc I l&,Oj I
Redox Potential Eh (mV) I ~zz I Redox Potential Eh (mV) I 4ZI I
Turbidity (NTU) I 3 I Turbidity (NTU) I 3 I
Time I ISI8 I Gal. Purged I ]() I Time I lS!j I Gal. Purged I go I
Conductance I :t~rz. I pH I b.l-z I Conductance I ~~I I I pHl 6 .. 1 z. I
Temp. oc ll;,,o4 I Temp. oc I 1!;.05 I
Redox Potential Eh (m V) I ~'2Z I RedoxPolentialEh(mV) 1 '-IZO I
Turbidity (NTU) I 3 I Turbidity (NTU) I .3 I
White Mesa Mill
Field Data Worksheet for Groundwater ~ 1 of2 capturx· COMP.TIPLE WITH~ .... f&/n.--FUNCTIDNALITY
Mill-'lroundwa~!'r Discharge Permit ( ( Date· 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurancf! Plan (QAPl
Volume of Water Purged gallon(s)
Pwnping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I Jo.o
Number of casing volumes evacuated (if other than two)
If well e\·acuated to dryness, number of gallons evacuated
Time to evacuate two casing volumes (2V)
T=2vtQ= L s.z<1 I
I o
l o
Name of Certified Analytical Laboratory if Other Than Energy Labs I._A...;....W.;...A:....:L-=----------J
Srunple Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if oiber than as Preservative Type
VOCs
Nutrients
Hea-rr_Metals
All Other Non Radiologies
Gross Alpha
Other (specify)
Chlor,t\e
t ~inal Depth I gf_. YD
~
5
~
:Comment
y
00
~
0
0
0
1!1
N specified below)
0 :1x40 ml
0 lOOm!
0 250ml
0 250m!
0 1,000 ml
0 Sample volume
Sample Timel ._ -'-0-'~=5;;..Y"--_ _.
y N y
0 fll HCL 1¥1
0 Ill H2S04 ~
0 0 HN03 D
0 0 No Prcserv. D
0 0 HN03 0
0 Ill D
If preservative is used, ~pecify
Type and Quantity of Preservative:
See instruction
: Arn-.J€0 on s;+e u.t ISO" ~n11ef'" t~-nO. G-Mrifl prese~~t f;,, pv.r~(. 'f\.,~..r~e be~~l\ "'-+ 1511
: Pu.~e~ lNell .for ~ +a+c:~.l cf & IYI;nvJe~ Pur~e enc:\e~ Oi.t IS l~
, LUo..fer w~ c.leo..c Lett S ,+e .,._ t )SZZ
. Aai \le<>. 01"\ Sl+e ~+ ofSS"L 1.\ntler .:.VJJ 6-~Arr i n pre:;,~f'l+ -h Coiled-Se\I'Y)pi~~-Der-+'h +o
wc.l.'"~r Wo..,> <60 ) 1g .Su..rYlple> b~";\~~ ""+-o~~ Le+:f 5 i~ '\t ogSL
l .... ~ .......... -----------_,lDo not touch this cell (SheetName)
White Mesa Mill
N
D
0
0
0
0
IE
Field Data Worksheet for Groundwater A 2 of2 capturx· COMPATIBlE WITH_../'-I,.U"~FUHCTIDNHITV
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL ~ ':J See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ ST Q\;:o:rter Gh lorOfO(/'YI -zoi.L.
Location (well name): Ll"1....a.....:.;W:.....Y....:...-.....:O~'f....:...._ ________ ____J
Sampler Name
and initials: 1=-r;.nn~r }}D II ;Jo..jh1d
Field Sample ID IJW'-\ -O'Lro I7Z01'=-
Date and Time for Purging I 3 /!VZDI.b and Sampling (if different) Ll ~_/_17.:....::/_'Z._O_I_b _____ --.J
Well Purging Equip Used: (IDpump or [QJ bailer Well Pump (if other than Bennet) I G-(I.Ar"'Cfto.s
Purging Method Used: 002 casings (QJ3 casings
Sampling Event I Q\)..o.r+er~ Chloro-FOrm Prev. Well Sampled in Sampling Event L--l_-r_~JJ_Y_--_1_8 _____ --.J
pH Buffer 7.0 7,0 pH Buffer 4.0 l..\.0
Specific Conductance L--1 ....:...1 0:...:0~0'----------'lllMHOS/ em Well Depth(O.Olft): I IZD.l>O
Depth to Water Before Purging I b'Z. 47 Casing Volume (V) 4" Well:' '31, 5G, ,(.653h)
3" Well: o (.367h) L...:...---.....J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)L-I1;...=0:_0 __ .....J
Time I )'Z.:!>g I Gal. Purged I {,D I Time I 1?. 31 I Gal. Purged l7o I
Conductance I 'l.'·\'-\l I pH I ~. ''2. I Conductance I z.~~s I pHI c;,J? I
Temp. °C l)q ,q~ I Temp. oc I lY ,Gf3 I
Redox Potential Eh (m V) I '-rz.o I Redox Potential Eh (mV) I Lj2o I
Turbidity (NTU) I 1q I Turbidity (NTU) I jq I
Time I IZYO I Gal. Purged I ~0 I Time I 124 / I Gal. Purged I 'to I
Conductance l 1.~~r.. I pH l f.,J3 I Conductance 1-z'-1'-li: I pH I G. l'Z I
Temp. °C I \q,q_) I Temp. oc l\4.q3 I
Redox Potential Eh (m V) I :iZ6 I Redox Potential Eh (m V) I 919 I
Turbidity (NTU) I }~ I Turbidity (NTU) I l9 I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I \0.0
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca ing volumes (2V)
T=2V/Q= 17.51 I
l o
lo
Name of Certified Analytical Laboratory if Other Than Energy Labs L.:l A...l.W~A~L::._ _____ __J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs m
Nutrients El
Heavy Metals D
All Other Non Radiologies D
Gross Alpha D
Other (specify) 'tl
G'n I on de
Final Depth I 7 5 r LS
Comment
An·i'\led. on s.i+e a...t 1230
fu..r~~ wel\ .for-q... +o+~\
~0\.fef' \-0~ Gleo..r.
N specified below) y N y
D 3x40 ml D 19 HCL 'f)
D 100 ml D ll H2S04 ~
D 250 ml D D HN03 D
D 250 ml D D No Preserv. D
D 1,000 ml D D HN03 D
D Sample volume D ~ 0
If preservative is used, specify
Type and Quantity of Preservative:
Sample Time
,-), See instruction
--("tMilt!r" tUIJ_ Go.rr:Y) f("e~e.Y'+ -\-~(" pv.r~. 'fv.r~(Z.. ~0.11 o..+ IZ'3Z
~ q ml"'"'-t~s. T'v..r~e.. ended o.+ lZY/
Le.-t}-~~4~ CA.} lZlJ~
N
D
D
0
D
D
'l!l
Acri\lec} £>n s.i+e. oo...Y o&-zo --(.,..,1'\ner Ma G-o.rritt pres.e-trf +o c.olle-c+ .s~Mf)~-D~pt~ +o
wo-1-er VJC)._> c';'Z.'-\ I S~fV~fle.> b,.;l~~ ~ 0~7.2 LeJ:t srt-~ o.f-0&2~
TW4-09 03-16-2016 loo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I )$1' Qv.o.r"hi a lor&Yor/'Yl ZD u,
See instruction
Location (well name): Ll _-r_W_'-1_-_IO _________ __J
Sampler Name
and initials: 1....,..-lkntl r/ Ho )] t~ ~hid'
Field Sample ID
Date and Time for Purging I '"b/'Ll/7.0 ).b and Sampling (if different) 3.lii/ z.ol b
Well Purging Equip Used: IT!) pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [![12 casings [QJ3 casings
Sampling Event I Qv.wfc:rb Gh lort>f~rrVj Prev. Well Sampled in Sampling Event I.__J_\rl_4_-_D_7 _____ __,
pH Buffer 7.0 pH Buffer 4.0 '""\.D
Specific Conductance ._I _I_O_O_Z> ___ _.I !J-MHOS/ em Well Depth(O.Olft): ._I ..;_\ 1_1._0_0 __ __.
Depth to Water Before Purging I b l. ZJ'2) Casing Volume (V) 4" Well:l "b'Z.DI 1(.653h)
3" Well: fJ (.367h) .__ ___ _.
Weather Con d. Ext'l Amb. Temp. oc (prior sampling eventl,_ll=&_11 __ _.
Time I l3LJ'-\ I Gal. Purged l iD I Time I I Gal. Purged I I
Conductance 1 -z.~g, I pH I S.(;~ I Conductance I I pHI I
Temp. °C 1 \s. \61 I Temp. oc I I
Redox Potential Eh (m V) I q2] I Redox Potential Eh (mV) I I
Turbidity (NTU) I zo I Turbidity (NTU) I I
Time I 0~0.5 I Gal. Purged I I) I Time I o'foo' I Gal. Purged I {) I
Conductance l 7..gb~ I pH I ~.3.1 I Conductance l?-8~l I pH l();z.1 I
Temp. °C 119 .\'1 I Temp. oc IJ9/3Z. I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 70 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I 10.0 T=2V/Q= I C>.YD I
Number of casing volumes evacuated (if other than two) 10
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs '-l :....:11'-'-\J-'Pr..:....::...L. _____ _,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y
VOCs (] 0 3x40 ml 0
Nutrients ~ 0 100 ml 0
Heavy Metals 0 0 250m! 0
All Other Non Radiologies 0 D 250 ml 0
Gross Alpha 0 0 1,000 ml D
Other (specify) ~ 0 Sample volume D
C 'n lor;~c
Final Depth I 10'1.8!. Sample Time 0'(0b
Comment
Au-:'IJe} on ~;.fe d-)33~ -rMr~er ~a G-D.rr.'n pre.settt' -hr pu.l'~e­
P\.\.r~f~ ~ell ~r o... 1-b-fA..l of 7 M11f1t.d-c..s. p\A,-~~tl we.ll Jr~~ \ND~.fcr l.Vt;..s,. Mo5.~ Cko.r. Le-ft 51i--c. dtJ-1'3Y7
N y
~ HCL ~
[ll H2S04 ~
0 HN03 0
0 No Preserv. 0
0 HN03 D
Ill 0
If preservative is used, specify
Type and Quantity of Preservative:
:1 See instruction
Pv.~e-bejo.f\ "\.t 1"337
P\Ar~e.. ~nJed. .... t \~ll~.
Affi-ve~ on srl-G tAt oq03 -r;11"er AAJ C.o..rr:(\ .pr~ to coJ/ecf .56-,p}e.S.
VJ6-5> t; 1.1 D .Se:.:rv~.pks b"'d-ea 01..+ oqo"' L~ s ttG e:J-oqDq
TW4-10 03-21-2016 I Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
0
D
D
Qlj
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I j5.1 Q\Ao.,rter C h lorO+'orm -z.olC:.
See instruction
Location (well name): .... 1 _"'T_vJ_l\__;__~....:\ \ _________ __.
Sampler N arne
and initials: I -TAnner Hoi} ,"d".!;\ h'H
Field Sample ID
Date and Time for Purging ._I _'3_{_9_/_z._o_\_C ____ ___. and Sampling (if different) I .N/A '-----------~
Well Purging Equip Used: ~pump or [gJ bailer Well Pump (if other than Bennet) I Gol1flnlAoU-,.S.
Purging Method Used: (][]2 casings [gJ3 casings
Sampling Event I G\ '-'.O.rt<.d:;1 Gh I O('Ootorm Prev. Well Sampled in Sampling Event I.__M_w_-_Zfo ______ __.
pH Buffer 7.0 7,0 pH Buffer 4.0 4,0
Specific Conductance .... I _1_0_0_0 ___ ___,1~-tMHOS/ em Well Depth(O.Olft): I 100,00
Depth to Water Before Purging I 'l3, 05, Casing Volume (V) 4" Well:' LtS3 ,(.653h)
3" Well: 0 (.367h) ,__ ___ _,
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventll._ .....:g_11 __ _,
Time l l 153 I Gal. Purged I a I Time I I Gal. Purged I I
Conductance l 35'ir.: I pH l i.~ I Conductance I I pHI I
Temp. oc I l6.cg3 I Temp. oc I I
Redox Potential Eh (mV) I 'Z::5l I Redox Potential Eh (m V) I I
Turbidity (NTU) I ~0 I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I l,,O
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca ing volumes (2V)
T=2V/Q= I 05, I
0
'0
Name of Certified Analytical Laboratory if Other Than Energy Labs IL-.:.,;AL.;.W"""A....,L=---------'
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs ~ D 3x40 ml D 'El HCL ll
Nutrients ID D 100 ml D fJ H2S04 f]
Heavy Metals D D 250 ml D D HN03 D
All Other Non Radiologies D D 250 ml D D No Preserv. D
Gross Alpha D D 1,000 ml D D HN03 D
Other (specify) m D Sample volume D lSI D
C'n \of'i~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I 'l..:....:~::....:'....:::2;..;..1 __ ___. Sample Time )lb:S
Comment
Arri\Jea on sl+~ a..+ n.so
So.tv1 ple~ ~}J ec.+-eJ tk+ ll53
Le..f} S,l+~ o..-T-ll!;.S
See instruction
-Jdnrlt-1"" (J..(l<k G-o..rdf'\ rr~~f\1-' ~ eoJlc:d-Sl),rnf'lG~
!,JtA+-e_r wc....s. f(l6~7~ cl~ar·
TW4-ll 03-09-2016 IDa not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
D
D
D
1!1
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I l !)I Q\Ao..C""f(:c-Gh I orof'o(JYl '20 1"-
l See instruction
Location (well name): ~....l_--ti_W_'-1_-_rz_. ________ _____.
Sampler N arne
and initials: I =t.11ner Ho /1/J~jtrJi
Field Sample ID I TW4-l2~D31S"ZOI.I.
Date and Time for Purging I ~/IL!/'201-C. and Sampling (if different) 13/ lS/ZO/C.
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) 1..!:1 <f~r-=W'\..:....:..:..J\--:.:f_1..:~;__ __ ----J
Purging Method Used: rn:]2 casings [QJ3 casings
Sampling Event I Qv-M+erb Ch lorOform Prev. Well Sampled in Sampling Event l~...._--rw __ 4_-_D.3 _____ ___,
pH Buffer 7.0 7.0 pH Buffer 4.0 Y.O
Specific Conductance ~...I ___;_;:ID_O..::..b ___ _,jJ..lMHOS/ em Well Depth(O.Olft): I 101. &1>
Depth to Water Before Purging I 45.70 Casing Volume (V) 4" Well:l ~b,'13 1(.653h)
3" Well:._ __ o ___ _,_(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! -=1~=-o--..J
Time I IY7>% I Gal. Purged I 50 I Time l l~3q I Gal. Purged I '0 I
Conductance I F\~Y I pH I b.3t> I Conductance I 1:i83 I pHj(,,41../ I
Temp. oc I l~.~q I Temp. °C ll4.'l& I
Redox Potential Eh (m V) I 9{~ I Redox Potential Eh (mV) I Yl7 I
Turbidity (NTU) I ~~.i I Turbidity (NTU) I \3,q I
Time I \940 I Gal. Purged I 70 I Time I \941 I Gal. Purged I 80 I
Conductance I l9~1 I pH I b.'17 I Conductance 1Jl:l7~ I pH I C\.51 I
Temp. oc 114.4& I Temp. °C I \9.'11 I
Redox Potential Eh (m V) I gli I Redox Potential Eh (m V) I Cl{L; I
Turbidity (NTU) I p.'l I Turbidity (NTU) I 111.l5 I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Cal ulation
Flow Rate (Q), in gpm.
S/60 = I )O.D
Time to evacuate two casing volumes (2V)
T=2V/Q= 17.2&' I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs AWltL.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs Ill
Nutrients [!!
Heavy Metals 0
All Other Non Radiologies D
Gross Alpha D
Other (specify)
C h \or;J{
Final Depth I 9Z.3Y L......:...;;......;;;..,_.:_ __ ___.
Comment
Ard\Je~ on $1+t: o..} I '-I 3D
P v.r~e~ \Nell -tbr ~ +otu-\
Leti-~;~ tAt-lYY3
r!J
N specified below) y
D 3x40 ml D
0 100 ml 0
0 250 ml 0
D 250m] D
D 1,000 ml 0
0 Sample volume D
Sample Time I._O_C:,_':::i_;-z. ___ _.
N
['II
rn
D
D
D
lJI
y
HCL ~
H2S04 ~
HN03 0
No Preserv. D
HN03 D
D
If preservative is used, specify
Type and Quantity of Preservative:
A See instruction
ol
-r;;,v1e,... And G-o.rr:fl pre.senf fo, puree. ?w~~ bes~n tJ:f
ot g ft'lt,l'll-'.-k~. Pu.r~:f ef!Je~ ""'t J~~/. \,.)ocfe.r t.U~ c..l(!o..r
1Y3'3
N
D
0
D
D
0
ria
Arrillt:~ on t,;·h~ J QC:,"\q -( ... ,net"' o.f\J G-tMrin pr-es,M} ..fr, collecf 541Y1f1e~. D-ep7J,., -h> L.)e..+~r
vJ"-6 4S,qo St;.Mp l~ ba..i\eA tA+ 06~'2. Letf sift: o..f o(:.5Y
TW4-12 03-14-2016 IDa not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I p..-r Qv..o.f4er Gmu:n-J C.hlorot~c-tt1 zolt.
See instruction
Location (well name): I,__"T....:...._w_y-'---.;.::l3=------------'
Sampler Name
and initials: I ::=r:nn~r HoiJ,"J';:1/1Jl
Field Sample ID
Date and Time for Purging I ~/ 15/z.. 01 G. and Sampling (if different)
Well Purging Equip Used: IT!] pump or [gJ bailer Well Pump (if other than Bennet)
Purging Method Used: [!]2 casings [QJ3 casings
Sampling Event I Qv..OJ=fe.rk\ ChlorOforM I Prev. Well Sampled in Sampling Event I "1'-JY-3 z
pH Buffer 7.0 pH Buffer 4.0 '-\. 0
Specific Conductance l.__l_Oo_o-=--__ __,1~-tMHOS/ em WellDepth(O.Olft): I IO-r.SD
Depth to Water Before Purging I 5?.. OS Casing Volume (V) 4" Well:l 6?.. ,2{9 1(.653h)
3" Well: 0 (.367h) ....__ ___ __,
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)._l _5_0 __ __,
Time I o~qs I Gal. Purged I -lC. b6 I Time I I Gal. Purged I I
Conductance I '"Z..\07 I pH I b. 57 I Conductance I I pHI I
Temp. oc I \\0\.99 I Temp. oc I I
Redox Potential Eh (mV) I gzz I Redox Potential Eh (m V) I I
Turbidity (NTU) I '/.z I Turbidity (NTU) I I
Time IO,YI I Gal. Purged I 0 I Time p l:.43 I Gal. Purged lo I
Conductance lzo:z.:\ I pH 17.01 I Conductance 1--z.o zj I pH I7.DD I
Temp. oc I F"\02 I Temp. °C 114.70 I
Redox Potential Eh (mV) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 6!5 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I ID.D
Time to evacuate two ca ing volumes (2V)
T = 2V/Q = I C> .555 I
Number of casing volumes evacuated (if other than two) l \.gz
If well evacuated to dryness, number of gallons evacuated 60
N arne of Certified Analytical Laboratory if Other Than Energy Labs AWAL
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y
VOCs ril 0 3x40 ml 0
Nutrients ~ 0 lOOm! 0
Heavy Metals 0 0 250 ml 0
All Other Non Radiologies D D 250m! 0
Gross Alpha D D 1,000 ml 0
Other (specify) IE D Sample volume D
C. h )or,·Je..
Final Depth I I 00 .~"!:> Sample Time
Comment
A,.-r,'ue~ on s,,'f.~ o-+ Qq'3b l o-41Mr o.nc1. G-c:Mril'l pres.er1+
r V..ff\-eO. wel\ ~r-"'-+o+o.l or b (Y1/rh.J-es. 'P\A.r~d Well O[j
tVG\.fe.r w~ u\eo.<'. ld+ 5-it~ 4'1.} D&l4f
N y
121 HCL ~
_17! H2S04 ~
0 HN03 0
0 No Preserv. D
D HN03 D
00 D
If preservative is used, specify
Type and Quantity of Preservative:
} See instruction
-t;;,-ru.r~c. Pu..r~e. b~S"
'Pu.r.1e ~nJeJ ott Dqy 5_
N
0
D
0
D
0
Ill
Arrive.~ Of\ s.;+e. o-.1-o~,o~q ~f1her (MJ. G-tArr,() rre.s.etri-'+o c.ol\ec.t S~f>l~. Dep1i. -k vJoo.+'O"'"
vj{).~ 5Z.l.S S.l11mp1es btA;IJ.. tA+ 064< L.e...fi-s.:t~ ~ (){,l{S
TW4-13 03-15-2016 I Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: \S:.""f Qv-o..r+er Gnloro:Gi"l"l ?.0 1l
Location (well name): .__I_"T_w_4_-_l~_,__ _________ __.
Field Sample ID
Sampler Name
and initials:
,-
1 See instruction
Date and Time for Purging .__13_/_1 f:....:./_'2.._o_l_..b _____ ....~ and Sampling (if different) L-1 _':!:>_/_1~...:./_z._o_t_C. _____ __J
Well Purging Equip Used: [![I pump or [gJ bailer Well Pump (if other than Bennet) I G-rW1J.+~S
Purging Method Used: [![)2 casings [QJ3 casings
Sampling Event I Qv.Wferb Ghlor~c-1'1"\ Prev. Well Sampled in Sampling Event IL.__"f_YJ_I.\_~_-z._~ _____ ___J
pH Buffer 7.0 7.0 pH Buffer 4.0 '1.0
Specific Conductance L-1 _IO_O_D ___ ___JI!!MHOS/ em Well Depth(O.Olft): .._I 4...!.:3=·-=-o_o __ ..--~
Depth to Water Before Purging I &O.oS Casing Volume (V) 4" We.ll:l ~.45 ,(.653h)
3" WeiJ: o (.367h) '-----'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)l._l_C>_11 __ _,
Time I lJ47 I Gal. Purged I \S I Time I I Gal. Purged I I
Conductance I 5. 14~ I pH I G.. 1 'Z I Conductance I I pHI I
Temp. °C I \S.l9 I Temp. °C I I
Redox Potential Eh (m V) I '1>39 I Redox Potential Eh (m V) I I
Turbidity (NTU) I \'Z.S I Turbidity (NTU) I I
Time I 072$? I Gal. Purged I o I Time I 07-:?.b I Gal. Purged 125 I
Conductance I S\f:.O I pH I f,."2.2 I Conductance I s1s3 I pH I {;,Z.I I
Temp. °C 11'Z.YS I Temp. °C I I:Z.5o I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill· Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2 ·Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 15 gallon(s)
Pump.ing Rate CaJculali n
Flow Rate (Q) in gpm.
S/60 = I )O .oD
Time to evacuate two ca ing volumes (2V)
T=2V/Q= II.G4 I
Number of casing volumes evacuated (if other than two) 11.77
If well evacuated to dryness, number of gallons evacuated l 15
Name of Certified Analytical Laboratory if Other Than Energy Labs wl A:....:.W::...:..L..AL.:L..:::...._ ____ ---J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs HI 0 3x40 ml 0 ~ HCL ll 0
Nutrients f!l 0 100 ml 0 l!J H2S04 ~ D
Heavy Metals D 0 250 ml 0 0 HN03 0 0
All Other Non Radiologies 0 0 250m! 0 0 No Preserv. 0 0
Gross Alpha 0 0 1,000 ml 0 D HN03 0 0
Other (specify) "[] 0 Sample volume 0 lJ 0 lil
Lh,or;d<: If preservative is used, specify
Type and Quantity of Preservative:
Final Depth L..l _:q _:_:).....:.O...:..l __ ___J Sample Time 07'29
Comment
... ). See instruction
Arr:\le~ Of\ ~~+e ~t I3'1'"Z. -r;_nnel ~M &t>.rril" lAnd G-o.r(;n f><e.S~tr+ -f'Dr-pv.r5e-Pu.r-~e., b~"'
~+ \3l.\(... Pu.r~ \Ne\\ ~~'" (}... i-~o..\ o.,\:' 1 M;n"'+G 3D Sec.oYlJ.~. Pv.r~ctl Well drj Pu.r~r-efl~~ ~P )3l..Jl. wt~~.hr ~~ (1.. ~;}tl<. c.louO!)· L~f} .s..t~ o..+ 1350
Arr;vd,. on srte lkt 07Zf... --r,_f\1'1-ef" o.~~O. &o.rrin ff'"e.SeM-to U>l\ed-..SAn1p1es.. De~ 1-o
vvu..-Ter \N~ go.)!, s."'t~'P~ bo..:lea ~+ o77."1 l.-ett .s.;t~ &~.1 0731
TW4-14 03-15-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT l-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: \~I' Qu.A.r::feOr C.h \ or~(m Wl6
See instruction
Location (well name): IL-...:M-'-W_-_-z._c.. __________ ___.
Sampler N arne
and initials: 1--r"'Mrter"" ~oli,Jo.._!:\ friJ
Field Sample ID
Date and Time for Purging I 3/ 't /WI C.. and Sampling (if different) ._I 1'1_/_ft ________ _.
Well Purging Equip Used: !][)pump or [ill bailer Well Pump (if other than Bennet) I GortfifiV.OlJ..S.
Purging Method Used: [!!]2 casings [ill3 casings
Sampling Event l lS:v.o:rt"er,b Gh)o<"CJ'or!VI Prev. Well Sampled in Sampling Event .... 1-r __ k.l_Y_-_z_o _____ __,
pH Buffer 7.0 ._I -'7-'-10::...._ ___ __. pH Buffer 4.0
Specific Conductance ._I \_o_o_o ___ ___.l~-tMHOS/ em Well Depth(O.Olft): I I ZZ,50
Depth to Water Before ·Purging I f:>2, gg Casing Volume (V) 4" Well :~3~ .13 1(.653h)
3" Well:L.. _o __ __J.(.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventl._l ..:::.8_6 __ __.
Time I \OYY I Gal. Purged I () I Time I I Gal. Purged I I
Conductance I ~'-rz.~ I pH 1 6.9tt I Conductance I I pHI I
Temp. oc I IS.'ZI I Temp. °C I I
Redox Potential Eh (mV) 1 z 76 I Redox Potential Eh (m V) I I
Turbidity (NTU) I 0 I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. °C I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate Cal.culation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
s16o = l.__q....:.;,o ___ __, T=2V/Q= I $.(,S I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs .... I A_W_A_L ______ __,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs 'll
Nutrients ~
Heavy Metals D
All Other Non Radiologies 0
Gross Alpha D
Other (specify) E
Gh )or;Je
Final Depth I q7 · t;S
Comment
Arri\Je~ 0(\ ~ih~ o..-T 1D'11
.S,o.Mple.s Golld~ ~-r
Le-t} ~l+e. o..} IOI.iC.
N specified below) y N y
0 3x40 ml 0 l!l HCL "EI
0 100 ml 0 ~ H2S04 ~
0 250ml 0 0 HN03 0
0 250 ml 0 0 No Preserv. D
0 1,000 ml 0 0 HN03 D
D Sample volume D ~ D
If preservative is used, specify
Type and Quantity of Preservative:
Sample Time
See instruction
-rtlM\<.( a.f\d. G-tUrl" pres.errr +o c.olled SC(mple>
toY4 w""i--er 1.0v..~ Gle~r
MW-26 03-09-2016 loo not touch this cell (SheetName)
White Me.sa Mill
Field Data Worksheet for Groundwater
N
D
0
0
D
0
tJ
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \s.,.-Q\):D:r'fer C.~ lorofo(fY) Zbl~
See instruction
Location (well name): l~.-11-'-w.:.__Y_-_1_6 _________ -.~ Sampler Name
and initials: fiCN111Gr' H.,l),JG\~frr}
Field Sample ID ll w4 -l~-0317ZOI '-
Date and Time for Purging I '3/ I b /zo \ '-and Sampling (if different) l~.-3-'/--'1_"1_/-z.._o..:....J ~::;....._--------~
Well Purging Equip Used: (!!]pump or [9J bailer Well Pump (if other than Bennet) I G"ru.ndfo:>
Purging Method Used: (ID2 casings (9]3 casings
Sampling Event I Q\)l)..rferh& Gh I oro:R>ri'V} Prev. Well Sampled in Sampling Event 1._-r\_\U_Y_-_o_q ____ ---J
pH Buffer 7.0 I.._/'-'-, 0.:;._ __ ---J pH Buffer 4.0 Y.D
Specific Conductance ._I '--'IO....::;.OO ____ _,l~MHOS/ em Well Depth(O.Olft): IL..:.l_,_YZ=.;_. o_c __ __,
Depth to Water Before Purging I b3, gq Casing Volume (V) 4" Well:' 51.DD ,(.653h)
3" Well:,__o __ __,_ (.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)._l1_2_0 __ _,
Time I )3/l:. I Gal. Purged I 9D I Time I 1317 I Gal. Purged I 100 I
Conductance I ~sc.. \ I pH I ~.DZ. I Conductance I?>S"'Z I pHI 6.oz I
Temp. °C I 15,t;;4 I Temp. oc 1 15,7z I
Redox Potential Eh (m V) I 3'-\~ I Redox Potential Eh (mV) l-:3q 8" I
Turbidity (NTU) I )'2.2-I Turbidity (NTU) I 1'2 I I
Time I 1'3.18 I Gal. Purged I llO I Time I \319 I Gal. Purged I \-zo I
Conductance I ~.Sb~ I pH I co.oz I Conductance I~E.'l I pH I hb3 I
Temp. °C I ) S.1li I Temp. oc I ls.75 I
Redox Potential Eh (m V) I '3~1 I Redox Potential Eh (mV) l'34z:; I
Turbidity (NTU) I '~ B I Turbidity (NTU) Il LS I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged l?.D gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I 10 .o
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two casing volumes (2V)
T = 2V/Q = I 10.'2.0 I
I o
l o
Name of Certified Analytical Laboratory if Other Than Energy Labs '-'1 A'-=--'-W'-'-A.:.-.:.L-==--------'
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs l1 D 3x40 ml D "KI HCL P!D D
Nutrients ll D 100 ml D fl H2S04 r:J D
Heavy Metals D D 250m] D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) '[] D Sample volume D f) D ~
C'h\or-,Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I )32. ~b Sample Time
Comment
,) See instruction
A<ri>Je~ on si+~ o..i-1303 ~~'Yie~ tAAd G(J..m·fl present ~r pu.r~r 'Fv..r~e be~~, o..t }3D7
f'~r~d well for (1.. 1-oh_\ of \'2. M;f'lv..+~!:>. fv.~e efldeJ. cJ..f )3l'J
W~+e~ WO.S d--\:f+IG lJD"b·let'} s l-1-e ~t }321
Arn~veO. on sife. t:A+ 08'21 'lo..f'lner o..na G-o-cr;f\ ?r-e..Sefl} +il coll-ec..+ so.mpJes. D~p-1-h +o
Wfk.fer wu-~ ,3. ~7. ~"'rvlP le.s. bo..;lu). ~t c~?.~ LeJ:f-site ~+ o ~JI
TW4-16 03-16-2016 loo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I ) ~,.. Q .... a..~r C.l-l \or-o-t1,m'} z.Ol (,
Location (well name): ._I ..:....M..:...;W:..=.--_3_2 _________ _..
Sampler Name
and initials:
Field Sample ID
Date and Time for Purging I 3./Z2/20 l.b and Sampling (if different)
Well Purging Equip Used: [!!]pump or [QJ bailer Well Pump (if other than Bennet)
See instruction
I 'AI/A
Purging Method Used: ~2 casings (QJ3 casings
Sampling Event I Gv-o...rte.c8 Gh lol"'o..foftvl Prev. Well Sampled in Sampling Event ._l_-rw __ 4_-_lD ______ ...J
pH Buffer 7.0 7,0 pH Buffer 4.0
Specific Conductance ._I _,_l.._ooo::J.L. ___ ___,I!!MHOS/ em Well Depth(O.Olft): I 12>2,50
Depth to Water Before Purging I 7b, g.5 Casing Volume (V) 4" Well:' ~b.'33 ,(.653h)
3" Well: 0 (.367h) .__ ___ ......J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._l ....:cG_() __ _.
Time I \?.7..7 I Gal. Purged I 77,~ I Time I l""Z."Z Sl I Gal. Purged 177. ~SI I
Conductance I 3g0b I pH I c:l.zo I Conductance I '3~1sr I pHI (,.1~ I
Temp. oc I ll1. ~q I Temp. oc 11~ ./~ I
Redox Potential Eh (m V) I q~l I Redox Potential Eh (mV) I ~~~ I
Turbidity (NTU) I \30 I Turbidity (NTU) I 13.5 I
Time I \'Z.'Z.Gl I Gal. Purged l 77.qO I Time l l23b I Gal. Purged 1 7s.Jz. I
Conductance I 'b~"Z./ I pH I b•IJ I Conductance 1 3~13 I pH I"· 15 I
Temp. oc I 19.~~ I Temp. oc 1 \4.7* I
Redox Potential Eh (mV) I l-lq~ I Redox Potential Eh (mV) I Ll~o I
Turbidity (NTU) I \:>'J I Turbidity (NTU) I ,q, I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2 -Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 1St 12. gallon(s)
Pumping Rate Cal ulation
Flow Rate (Q), in gpm.
S/60 = I .-z.n
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two casing volumes (2V)
T = 2V/Q =I 33'-l.f1'2, I
I o
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I ..:...;A:....W_A~L _____ ____,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs Ci!l D 3x40 ml D 00 HCL 121 D
Nutrients ~ D IOOml D ~ H2S04 ~ 0
Heavy Metals D D 250m) D D HN03 D D
All Other Non Radiologies D 0 250m) 0 D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) [2! D Sample volume D ~ D ~
Gh lor ;Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I &Z . '-\'Z.. Sample Time }7.30
See instruction
Comment
Acr:\l~d
fv..·~~
F v-f'~G
Let}
b(\ .S.lTc, a...+ D.bZ'---r;.n.,.e.f' o.nd. G-~rn'" pru.~1r:Y -G, pure;e ~,.,J. St:iNJf}l(j ev-err}:
b~~o.n ""t 0(.30~ f"'-r-~~~ ~ell fOr C1-. +o+oJ crt 3bD m•'fl1A+<-s.
er1J~ M~ So.tY~ples C6lled-~ t;,.~ IZ.'30, [,J~lj" WtA.S ~ l;H7~ G/o ... J~
S. l' te.. o.. t )"Zl..}S .
MW-32 03-22-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ST ~W>-t'fet G}1 \cro'form "'ZOIL
Location (well name): ._1...:.1\--"W=-Y...l....--l,_,~..__ ________ __.
Field Sample ID I t\tJ~-lg_ o'::> 17zo 1~
Sampler N arne
and initials:
See instruction
Date and Time for Purging I '3/1~/ZD)k, and Sampling (if different) .__I _;;~;:_,J..;._n_/_zt>__,_lb _____ __.
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) I Gn~nJJ~s
Purging Method Used: [f!]2 casings [9]3 casings
Sampling Event I Q\ko....rferk) G\, \orCT'Rc rv'l Prev. Well Sampled in Sampling Event l._--r1J __ y_ ..... _0_5 _____ _.
pH Buffer 7.0 7.0 pH Buffer 4.0 I Y.D
Specific Conductance .__I _)<.,;;0...;;..()-=.l) ___ _.l !!MHOS/ em Well Depth(O.Olft): 1 1~7,50
Depth to Water Before Purging I GS. Y <f> Casing Volume (V) 4" Well :l Y7. 62. 1(.653h)
3" Well: 0 (.367h) '-------'
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)!.__ 9-'-" __ __.
Time I 1'2..0..5 I Gal. Purged I 90 I Time I }"ZOf. I Gal. Purged I 1oa I
Conductance I p~~; I pH 15.9q I Conductance I '~ lr; I pH I S.'fS I
Temp. oc 1 I e;, 1~ I Temp. oc I \G, I I I
Redox Potential Eh (mV) 1 111 ~ I Redox Potential Eh (m V) I 9 17 I
Turbidity (NTU) I 'ZS I Turbidity (NTU) I z.=, I
Time I l'Z.C:q I Gal. Purged I 110 I Time 1 rz.o g I Gal. Purged I JZO I
Conductance l ll617 I pH p:;.'[5 I Conductance I IE'7~ I pH 15.9:5 I
Temp. oc I I C;, 7 7 I Temp. oc 11 CO, i 1 I
Redox Potential Eh (mV) 191(;; I Redox Potential Eh (m V) I q t5 I
Turbidity (NTU) I 'Z.Y I Turbidity (NTU) I '29 I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged )2D gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I ) o. D T=2V/Q= 1 q,qo 1
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I _,_fl.L:W..=..Jr.......:;.L. _____ _.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs ll D 3x40 ml D ~ HCL IE
Nutrients !11 D 100 ml D rn H2S04 rn
Heavy Metals D D 250m! D D HN03 D
All Other Non Radiologies D D 250m! D D No Preserv. D
Gross Alpha D D 1,000 ml D D HN03 D
Other (specify) ~ D Sample volume D rY.'I D
C..h \or11clc If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I C f), 7-' Sample Time
Comment
,) See instruction
Arr-;\l~ Ol'l ~34-e o..+ 11:0 -(o.t"l'l-e<' ~n£). 6-D.rr;f' p("eS,(fl+ for Fv...r~e. Pu.ref b~~o.fl ~t-1156
'Pu.r~~d. ~~ll fof" u.. +o-tl.\1 o.P \2 m;n""t-e~. Pu.r~c... el"\de~ "'+' lZD&
\)J6-..f-er-\.0~ c\eo.r Let+ s.,+c; ~t 1210
Acrive.O. or'\ 5-ii-~ o..t Mm. "lo.Mler o..t1~ &o.C"r;.., pr~~en1-to col lee.+ ~o.rYJp)e=:,. Derth -h
wo..+e(" IJ.)~~ bS.YS >'-'Y'f\.Pl-6 b~~.ika C'.} 0&0 Lef} .s.r+~ o.-t ogl5
TW4-18 03-16-2016 I Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
D
D
D
~
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: l S.T QVA.r::Rr Cl'\lorot~riVI ZO I-'
Location (well name): ._fd..._W-'-'-\_,_-___,_14...___ ________ _..
Sampler Name
and initials: I ==to:'1111e r-Ffo/l•do._:1/.,-l}
Field Sample ID
Date and Time for Purging 1.__:3......:/~~..:../:.-...=-zo~LL..__ ___ ----l and Sampling (if different) ._I _N_'/._J~~-________ _,
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) I CorJi'fllAOIJ..).
Purging Method Used: 002 casings [QJ3 casings
Sampling Event I Q"'o.r+~rl~ Chloraforr>'l Prev. Well Sampled in Sampling Event LI_"TW __ Y_-_c_~---------l
pH Buffer 7.0 7.0 pH Buffer 4.0 Y.O
Specific Conductance L-1 ~lO:....::O:...::O'------'I!J.MHOS/ em Well Depth(O.Olft): l lzs,oo
Depth to Water Before Purging I G>9 .II Casing Volume (V) 4" Well:~3~ • 7b 1(.653h)
3" Well: 0 (.367h) 1------'
Weather Cond. Ext'l Am b. Temp. ·c (prior sampling event)._! _I z_o __ __.
Time I lq3o I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I ?, 7bi I pH 17. Z'Z. I Conductance I I pHI I
Temp. oc I lG, c; 7 I Temp. oc I I
Redox Potential Eh (m V) I ~I I Redox Potential Eh (mV) I I
Turbidity (NTU) I v I Turbidity (NTU) L I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. °C I I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2 -Errata
Groundwater Monitoring Quality Assurance Plan (QAP}
Volume of Water Purged 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
s16o = I ~~.o
Time to evacuate lwo ca ing volumes (2V)
T = 2V /Q = I 9!"'1 ) I
Number of casing volumes evacuated (if other than two) lo
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs IL..:A..:..W:;,;,:_A:....;:L=--------l
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs ID 0 3x40 ml D ~ HCL 'P 0
Nutrients ltl D 100 ml D ~ H2S04 r:J 0
Heavy Metals D D 250 ml D 0 HN03 D D
All Other Non Radiologies D 0 250 ml 0 0 No Preserv. 0 0
Gross Alpha D D 1,000 ml D 0 HN03 D D
Other (specify) tJ D Sample volume D tl 0 il
Gh lor~Je. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I b {, 8 g Sample Time
Comment
,-J See instruction
A rri\led. on site ~+ l'-JZ-1 ""'o.nr~u· 11v1J. Go.rritl
SCAIVlpl~ collec.+eJ. o.-+ ll.\~0 1tJ01.ter VJC..S.
Le-~ ~lte-o.t IY~ z.
TW4-19 03-09-2016 IDa not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I I s.T Gl~o.rkr C.h lot"ofdriYl '2.01'
See instruction
Location (well name): l'-_--rw....:....__4_.__-_'Z._O ________ __,
Sampler Name
and initials: I ~~ner t/oli,J~/1]
Field Sample ID
Date and Time for Purging I 3/G!/'ZO}.b and Sampling (if different) I /11/A
Well Purging Equip Used: (IDpump or [gJ bailer Well Pump (if other than Bennet)
Purging Method Used: [1[]2 casings IQJ3 casings
Sampling Event I Gu.o..rferl~ c.hlorof'ortt'l Prev. Well Sampled in Sampling Event '--,_li_W_Y_-_3_/ _____ ___J
pH Buffer 7.0 7,0 pH Buffer 4.0 Y,O
Specific Conductance '-1 _IO_o_o ___ __,l !J.MHOS/ em Well Depth(O.Olft): 1'--'I:....;:Oc....;;b;.;._,OO ___ _,
Depth to Water Before Purging I 70.lf~ Casing Volume (V) 4" Well:' 22.gc:; ,(.653h)
3" Well:'-. _o ___ _J,(.367h)
Weather Con d. Ext'l Amb. Temp. oc (prior sampling event)jL-...:O<.g_D __ _,
Time I \031 I Gal. Purged l o I Time I I Gal. Purged I I
Conductance I ~~27 I pH I Co.'i~ I Conductance I I pHI I
Temp. oc I 16.,49 I Temp. oc I I
Redox Potential Eh (m V) I 3D~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I q,g I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume ofWaterPurged gallon(s)
Pumping Rate Calculati n
Flow Rate (Q) in gpm. Time to evacuate two casing volumes (2V)
S/60 = I 7.0 T = 2V/Q =I (;;,53 I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I _A-'W~A_l"----------'
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
VOCs
Nutrients
Heavy Metals
All Other Non Radiologies
Gross Alpha
Other (specify)
C..h \or1·Je
Final Depth I 7 5 , 33
Comment
S &\rv1p\es Cb/lechl
L~+t sJ-1--e. lA+
y
[!)
rtl
D
D
D
11!1
N specified below) y N y
D 3x40 ml D Ill HCL rn
D 100 ml D _m H2S04 ~
D 250m! D D HN03 D
D 250m! D D No Preserv. D
D 1,000 ml D D HN03 D
D Sample volume D ~ D
If preservative is used, specify
Type and Quantity of Preservative:
Sample Time 1031
See instruction
-r"AAMr "~'~~}. G-~rr:t'l F~'"~~erd-+o coiled-..S(Ampks..
10'3) LJ~+-cr (...)ct~ I'V)O~t~ GJear
TW4-20 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
D
D
D
[S
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I JST QIJ\o.rter C\1\ \orl>fOOV'! ZOl'
See instruction
Location (well name): l.__l\tJ--'-_L\'---z_L _________ __,
Sampler Name
and initials: I :::=(q.nnt:r Ro 11/J~ lrH
Field Sample ID
Date and Time for Purging ~..1 -~-~-~:....:./_z_o_J_.C.. ____ ___J and Sampling (if different) JV'/A ~---------~
Well Purging Equip Used: @]pump or [QJ bailer Well Pump (if other than Bennet) Gol\1"ftliADlA..S.
Purging Method Used: [ID2 casings (QJ3 casings
Sampling Event I Qv..o.r-fe("'J3 C..hloro+brm Prev. Well Sampled in Sampling Event I .N/A ~---------~
pH Buffer 7.0 7.0 pH Buffer 4.0 L\.D
Specific Conductance LI_IO_o_o ___ ___.~I~MHOS/ em Well Depth(O.Olft): l 121.00
Depth to Water Before Purging I 67. 50 Casing Volume (V) 4" Well:l 34.~3 1(.653h)
3" Well: lJ (.367h) ,__ ___ _,
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._l -=s"'-• __ _,
Time I O~Y!. I Gal. Purged l t> I Time l I Gal. Purged I I
Conductance I 4S7.% I pH I G:..4Y I Conductance I I pHI I
Temp. oc I lSo ~~ I Temp. oc I I
Redox Potential Eh (m V) I ~q'l I Redox Potential Eh (mV) I I
Turbidity (NTU) I Q I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I )b,D T = 2V/Q = I 4 .3.k, I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated I o
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I -'-A=-W.....:A...:..L.:...._ _____ __,
Sample Taken Sample Vol (indicate
Type of Sample if other than as
y
VOCs rlJ
Nutrients [!J
Heavy Metals 0
All Other Non Radiologies 0
Gross Alpha 0
Other (specify) dJ
G n\or1'Je
Final Depth I 70, 'Z. 7
Comment
Sc;..r\l)f )e.s. colle.c+d
le.~} Sli-e. ~ 0'1'19
N specified below)
0 3x40 ml
0 100 ml
0 250ml
0 250ml
0 1,000 ml
0 Sample volume
Sample Time 0'141
TW4-21 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
Filtered Preservative Type Preservative Added
y N y N
0 [!l HCL ~ 0
0 1!1 H2S04 r:J 0
0 0 HN03 0 0
0 0 No Preserv. D D
D 0 HN03 0 0
0 ~ D ltl
If preservative is used, specify
Type and Quantity of Preservative:
See instruction
G )~o...r
2 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \S.T' Q\A.O.rfer Gh lor0f'orl"1 2 0 /.b
Location (well name): ._I_:Y._W_L\_-_zz _________ ---J
Field Sample ID
Sampler Name
and initials:
See instruction
Date and Time for Purging Ll ....;3~/_'f...;.!/~~-0..;.;.1!:.;;....._ ___ _~ and Sampling (if different) I._M___;_V,_~ ________ ....J
Well Purging Equip Used: [f[Jpump or [QJ bailer Well Pump (if other than Bennet) Col'lftY'Jt.\OV...S
Purging Method Used: [1[]2 casings [QJ3 casings
Sampling Event I Gu.o.r+(J't~ G.~ loro:f'orm Prev. Well Sampled in Sampling Event I jWY-z '1
pH Buffer 7.0 7.0 pH Buffer 4.0 4.0
Specific Conductance ._I _IO_O_;.~ ___ _.I!!MHOS/ em Well Depth(O.Olft): I II~. bD
Depth to Water Before Purging I Sil,/.S Casing Volume (V) 4" Well:' ':55.7.5 ,(.653h)
3" Well: o (.367h) .___ ___ _J
Weather Con d. Ext'l Amb. Temp. ·c (prior sampling eventl._l 7_0 __ ....J
Time II0\8 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I S570 I pH I 7,05 I Conductance I I pHI I
Temp. °C l iS I '3. '"Z. I Temp. oc I I
Redox Potential Eh (m V) I 317 I Redox Potential Eh (mV) I I
Turbidity (NTU) I () I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 0 gallon(s)
Pumpin g Rare Calculati on
Flow Rate (Q), in gpm.
s16o = I n.o
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca ing volumes (2V)
T=2V/Q= 1 y.zo I
j o
l o
Name of Certified Analytical Laboratory if Other Than Energy Labs IL-A:........:..W;,;,A.;.;L;;;,_ _____ _J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below)
VOCs ltl 0 3x40 ml
Nutrients r::J 0 100 ml
Heavy Metals 0 0 250m!
All Other Non Radiologies D D 250 ml
Gross Alpha 0 0 1,000 ml
Other (specify) E 0 Sample volume
Ghlon'~e
Final Depth ._I \,;_00_. 7_g ___ _. Sample Time 101~
Comment
Arri".ea on. st+e. o.t 10 \S ~nn~,... M~ Go..rr•'n
~tM'If)e~ Go\ledd ~+ ID1<6 vJ""i-e.r Wt\~
Le. +'+-S ife ~+ l 0-z. I
TW4-22 03-09-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
y N y
0 ~ HCL ~
0 r:l H2S04 r::J
0 0 HN03 D
0 D No Preserv. 0
0 0 HN03 0
0 ~ D
If preservative is used, specify
Type and Quantity of Preservative:
l ~ See instruction
pre...s~+--to co I k.ct" S&~M p J~s
Gleo.r
N
0
D
D
D
0
tJ
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \5i' Q"'~Arfer Chl orO+i>rm 'ZOIL
See instruction
Location (well name): 1'---'-rw--'--_,L\_-_z_~ _________ _,J
Sampler Name
and initials: I :::r=:.m'l er Ro} J.'Jt:1lrJt
Field Sample ID
Date and Time for Purging I ?::)lS/zol-f. and Sampling (if different)
Well Purging Equip Used: IT!) pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [QJ2 casings [QJ3 casings
Sampling Event I Qv..l.lrf-ed~ Cl'll orO+~rM Prev. Well Sampled in Sampling Event I -(\t..) t;-35
pH Buffer 7.0 "7,0 pH Buffer 4.0 I Y.o
Specific Conductance!.._ _1;_0_0_0 ___ __.1 ~-tMHOS/ em Well Depth(O.Olft): ._I ....:....)):.......;4 ;,_,D_D __ __.
Depth to Water Before Purging I 69,35 Casing Volume (V) 4" Well :' '2. 4 .IS ,(.653h)
3" Well :._ __ o __ ___..(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventll,_l_o_e __ ___,
Time I l313 I Gal. Purged I 50 I Time I \31Y I Gal. Purged l bo I
Conductance I '3 G. 5 "2. I pH I r.:.' y I Conductance 1 3b"ii I pHI (,,I y I
Temp. oc I 19,3~ I Temp. °C I \4, '3:S I
Redox Potential Eh (mV) I '31t I Redox Potential Eh (mV) I ~14 I
Turbidity (NTU) I 1'Z.S I Turbidity (NTU) 1118' I
Time I l~ts I Gal. Purged I 70 I Time I 131(. I Gal. Purged I go I
Conductance I ":5~so I pH I c. ~g I Conductance 1 '3b41 I pH I b.Jl./ I
Temp. oc I !9.'39 I Temp. °C I lq,~q I
Redox Potential Eh (m V) I '::>II I Redox Potential Eh (mV) I 111 I
Turbidity (NTU) I n:s I Turbidity (NTU) I lf.J I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I lo.o
Time to evacuate two ca ing volumes (2V)
T = 2V/Q = I s. £.3 I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated j o
Name of Certified Analytical Laboratory if Other Than Energy Labs
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below)
VOCs gJ_ D 3x40 ml
Nutrients Ill D lOOm!
Heavy Metals D D 250 ml
All Other Non Radiologies D D 250m!
Gross Alpha D D 1,000 ml
Other (specify) r1! D Sample volume
Lh \o,ide.
Final Depth I Z9 • Z5 Sample Time OTZI
Comment
y N
D ~
D ~
D D
D D
D D
D 1!1
y
HCL 121
H2S04 ~
HN03 D
No Preserv. D
HN03 D
0
If preservative is used, specify
Type and Quantity of Preservative:
"" See instruction ..-;,•
A('ri-v~a 011 ::.1+~ u-.+ \'3.QS ---to.nr~~r tMtJ. 6-o.rri11 pr.!.sei\t t,r p~Ar~c . 'PtJ.~e. he(fn ~+-130g
P""r~eO \Nell for (/1, tof-.1 ot g f'Y\itlu-.+e>. 'Pv.~e. et'IJ~ ~+ )~1(,
N
D
D
D
D
D
~
(r.)~+cr :rr~+eJ. lUJi-h ~t'\ Oro.~e. c.olor b~Af SlO\..J~ c}ca?-d . LA ~l+e. a.+ l3lg
'-+ _... } '"-· t 1-II t s-~mo1-e~. p .... Qth to W'(t~r An-:"e~ of'l s\'Te... ()... 0119 J Nll"'a" o-rl(}. I..T"-ITII' pre~n TD c-o ec. Q '"I
wo-.~ b9,'-lD ~NV~ple~ bo-;1eJ. ~+ OTz.l LePf-Srte '\f' OlO
TW4-23 03-15-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
DescriptionofSamplingEvent: I )~1'" 6)\)\;M--<::r Gh\or()f'c)T"M 'Z.O]'
Location (well name): l.._--r_vJ-'--4'---z_q-'-----------____J
Sampler Name
and initials:
Field Sample ID 1-rwy -z'-i_ 030ctzot c..
Date and Time for Purging I ::./a./ zo I ~ and Sampling (if different)
Well Purging Equip Used: (!I] pump or [QJ bailer Well Pump (if other than Bennet)
See instruction
I AI/A
Purging Method Used: (!!]2 casings [QJ3 casings
Sampling Event I GN.o.rtc.d~ Ghlo10f'or111 Prev. Well Sampled in Sampling Event I JWY-'Z..5
pH Buffer 7.0 IL........:"..:....·o ____ _. pH Buffer 4.0 y,o
Specific Conductance .__I _J"--Oo:.....:o'----------'1 !!MHOS/ em Well Depth(O.Olft): I llZ..SD
Depth to Water Before Purging I 6'3 .7D Casing Volume (V) 4" Well:' '5). 8.b ,(.653h)
3" Well: 0 (.367h) '----------'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)II---L7_0 __ _,
Time I lODg I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I 7YbZ I pH I ~.2JZ: I Conductance I I pHI I
Temp. oc I 15.04 I Temp. oc I I
Redox Potential Eh (m V) I ~:sq I Redox Potential Eh (m V) I I
Turbidity (NTU) I 0 I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged {) gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I 16,0
Time to evacuate two ca ing volumes (2V)
T=2V/Q= I 3.9& I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I -=A..::..W.:.......!.J.4~...:L=---------'
Sample Taken Sample Vol (indicate Filtered Type of Sample if other than as
y N specified below) y
VOCs Ill 0 3x40 rnl D
Nutrients 1:!1 D 100 rnl D
Heavy Metals D 0 250ml D
All Other Non Radiologies D D 250ml D
Gross Alpha D D 1,000 ml D
Other (specify) ca 0 Sample volume D
G h lor i~e.
Final Depth I b ~ 1 Z 7.. Sample Time
Comment
Arr;ve.~ of\ site. o..t \ o DL
~ t~.M p ).e~ C.b lle.e,}e,J
Le.-\+ S \ te.. ~-f I 0 \I
11..+-l ooq
M~ ~o-rrin f~"~~11i-+o
Wv-t<r--vJ "~ c..te.or
TW4-24 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
~ rn
D
D
D
~
Preservative Type Preservative Added
y N
HCL li! 0
H2S04 1!1 0
HN03 D 0
No Preserv. D 0
HN03 D 0
D IZI
If preservative is used, specify
Type and Quantity of Preservative:
See instruction
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I )$r Gv.o-.rf(.r Gh1oro+ot'M ZO)!.
Location (well name): Ll_-r_\,J----'Lj!--_z_5 _________ __.
Field Sample ID l 1w4 -zs .. o3oqzon.
Sampler Name
and initials:
See instruction
Date and Time for Purging I 3/4/ 201G, and Sampling (if different) L-.,.1\./,_J'A ________ _.
Well Purging Equip Used: ~pump or [gJ bailer Well Pump (if other than Bennet) I Ccrtrifl V\ o IA3
Purging Method Used: @2 casings [gJ3 casings
Sampling Event I Qv,.<>.rfe.rB Ch\ orootorrn Prev. Well Sampled in Sampling Event IL-.-r_w_~_ ...... _-z..._f _____ _,
pH Buffer 7.01 ~.-_~;_.0 ____ _. pH Buffer 4.0 4.0
Specific Conductance ~.-1 _l_O_C>"O ____ _.I !!MHOS/ em Well Depth(O.Ol ft): I 1311, &0
Depth to Water Before Purging I b.l:,"ZD Casing Volume (V) 4" Well:l y4:7q 1(.653h)
3" Well: 0 (.367h) .___ ___ _,
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventJI~6" __ ___.
Time I 09S~ I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance 17.734 I pH 17,/4 I Conductance I I pHI I
Temp. °C I PtCS I Temp. oc I I
Redox Potential Eh (mV) I ~19 I Redox Potential Eh (m V) I I
Turbidity (NTU) I (} I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (mV) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculati n
Flow Rate (Q) in gpm.
S/60 = I 1 s .D
Time to evacuate two casing volumes (2V)
T=2V/Q= I s .q7 I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated D
Name of Certified Analytical Laboratory if Other Than Energy Labs ,_I _.A"""W,1.:...;Ac.:....::::L"------'
Type of Sample
VOCs
Nutrients
Heavy Metals
All Other Non Radiologies
Gross Alpha
Other (specify)
G"hlDn.Jc.
Final Depth 1._7.~.-.b=-:--' 4.._.'('--------'
Comment
Sample Taken Sample Vol (indicate Filtered if other than as
y N specified below) y N
111 0 3x40 ml D rll
[B 0 lOOml D l:!r
D D 250ml 0 D
0 D 250 ml D D
D D 1,000 ml D D
ta D Sample volume D [B
Sample Time ._I D;::,.,...o.4=S(..;:;..._ _ __,
0 q S3 -r;:nn ef"
"'~ D~SL.
0'1.5g
Md G-o.('r{ n pr~s.enf-·h
w u.--\--e.r \tJ 1A..5. G1 t:t>r
TW4-25 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
Preservative Type Preservative Added
y N
HCL tfl 0
H2S04 ~ 0
HN03 D 0
No Preserv. 0 D
HN03 D D
D ~
If preservative is used, specify
Type and Quantity of Preservative:
, cJ See instruction
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
'<~~ -.:;:-~IVEROYFCJJE:LS
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I p:;!' Q\Aar+er C})loraforrt'l ZOlb
See instruction
Location (well name): ._14'1_\J_Y_-z_-b __________ __,
Sampler Name
and initials: I ~nne:(' 'Ho I J;JG\~
Field Sample ID
Date and Time for Purging 1.__3_/_I_S_/_-z.o_l.b ___ _,~ and Sampling (if different)
Well Purging Equip Used: m:)pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Q\Ao.r+ed~ C\1\ Ol"'o::fonV') Prev. Well Sampled in Sampling Event I JLJ Lj-Z7 '-----------~
pHBuffer7.0 ._l_-,_.0 ___ __, pH Buffer 4.0 t.:},D
Specific Conductance ._ll_OD_D ____ ~I [-~.MHOS/ em Well Depth(O.Olft): I g(;,,DD
Depth to Water Before Purging I (;;C),/4 CasingVolume(V) 4"Well:,1Z.57 ,(.653h)
3" Well: D (.367h) '-------'
Weather Cond. Ext'l Am b. Temp. ·c (prior sampling event)l.__l_l_11
__ _,
Time I \S3b I Gal. Purged 1-zo I Time I I Gal. Purged I I
Conductance I l:'i Gt:i I pH I '5. qo I Conductance I I pHI I
Temp. oc I , 5 .0"7 I Temp. oc I I
Redox Potential Eh (m V) I qt;1 I Redox Potential Eh (m V) I I
Turbidity (NTU) I 'ZJ I Turbidity (NTU) I I
Time 1 o 741 I Gal. Purged I 1'5 I Time I Dlqq I Gal. Purged l l5 I
Conductance I ~Y4 1 I pH I y .zy I Conductance I b~~9 I pH I Y:zz I
Temp. oc 1rz:.~o I Temp. oc I lZ.<L<S I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
After
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged '2.0 gallon(s)
Pumping Rate CaJcuJalion
Flow Rate (Q) in gpm.
S/60 = I W.D
Time to evacuate two ca ing volumes (2V)
T=2V/Q= lz,51 I
Number of casing volumes evacuated (if other than two) 1!.59
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I -'-'A_W---'A~\.. _____ ___.1 /tWJt L
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs 1::! D 3x40 ml D rn HCL ~ D
Nutrients 1!1 D 100 ml D 0 H2S04 1!1 D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume D ~ D ~
G'h lofl.a( If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I --'-~_3.:._, l:J_-b __ ____. Sample Time I en q g'
Comment
-~ See instruction
A(r:\le~ 01\ ~i·h: 0\.1 \S32 --r;.,ner ~~~~ (;."-u;, pre.S.efl:P -h;r pu.r~-e . Pl-'~~ bej£\f1 ~+-J53Y
?v.re:f~ W-ell fC>r fi\. to-t"l ot z. M.,l.\tt:s._ 'Pv.r~~ Wdl ~r~1-?~ree et~deJ o.t' IS3h
ltJ a-f<.r lA) ~ c.leo.r. LJt-.51:}-~ u.. t I~ 3~
Arr,'-.Je~ 61\ .S ··f<:_ d D14S -r;.f\1\ef' OJ\~ &"-frln p1"'e.SetrY +o CDHeot .So.~tJples, Depfh -1 ~ft:r
\'.)t1..~ (,(,, q~ ~rYlp\es. bo.~le6 o..t 074g 1.-efr ~rte ~+ 07SI
TW4-26 03-15-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I p:.'l' Q""o.rfer Crdoro"fi>rJVl 'ZOI.b
[ " See instruction
Location (well name): LIJi_w_Y_~_z_-, __________ -.~ Sampler N arne
and initials: I =-f~nner 'No )1,Je IJ1j
Field Sample ID
Date and Time for Purging I.__;:._/_1_5_/_Z_b_l '-____ ___, and Sampling (if different) 3/1 fo/Z.o lk '-----------~
Well Purging Equip Used: CQ]pump or [QJ bailer Well Pump (if other than Bennet) I G(u.."O::ft;~
Purging Method Used: (Q]2 casings (Q]3 casings
Sampling Event I Q"'-o.r+.er~ CW oro'for M Prev. Well Sampled in Sampling Event I T\0L1-)~
pH Buffer 7.0 7.0 pH Buffer 4.0 I Y.D
Specific Conductance Ll _\_Oo_o ____ _.l !!MHOS/ em Well Depth(O.Olft): ._I -~-'-=-·o_o __ ____.
Depth to Water Before Purging I 7'1, 7Z Casing Volume (V) 4" Well:l \O.b3 ,(.653h)
3" Well:.__o __ _J_ (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! ...!..ll;_D __ ....~
Time I \4\ & I Gal. Purged liS I Time I I Gal. Purged I I
Conductance I s. -z:z~ I pH I s,.'l~ I Conductance I I rHI I
Temp. oc I l.s:z.~ I Temp. °C I I
Redox Potential Eh (mV) I 3"41 I Redox Potential Eh (m V) I I
Turbidity (NTU) I ~~ I Turbidity (NTU) l J
Time I C>73S I Gal. Purged I b I Time l oT37 I Gal. Purged l o I
Conductance I 51~& I pH I b.Z.9 I Conductance I SZ"Zb I pH I b ·3D I
Temp. oc I }2.. -z.l I Temp. °C I 1Z."37 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
Be~r<::. ABer
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 12 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I )Q.D
Time to evacuate two casing volumes (2V)
T = 2V/Q = I '2.. 1"2.. I
Number of casing volumes evacuated (if other than two) 11.91
If well evacuated to dryness, number of gallons evacuated I LS
Name of Certified Analytical Laboratory if Other Than Energy Labs I~..,;A_;,W:..._;__:ft...::;I...;...__ ____ ___,J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs m D 3x40 ml D ~ HCL l!J D
Nutrients IEl D 100m] D f] H2S04 El D
Heavy Metals D D 250m] D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) 1[] D Sample volume D !] D 1!!1
Ch 1orij~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I 9..:..~...;.;''--0_o __ __, Sample Time
Comment
,.~ See instruction
Arr;ve'a 01\ ~l+e o..+ )~13 -"f~nnu ~~J~d-&~crin p<eS.ef\1"' -fo<" pu.r~e.. ?~>..r~e. be~Cl.n ~t JY/7
fv.~"\-eb \N~ll -Gr-o... +o-to..\ J; ) Mlr~v,+<. "'3.0 ~GOY1~S. ?u.r~~ we\\ d.r~\ Pv.l"~ endd ~+ 1~Jg
V0~1l· VJ~~ de6.r. Let\-s1rc: ~t-l4'ZI
Arrl\le~ of\ Sffe J-b733 ~rttle( AA~ ~rrifl p(~+ -h Gollecf s~()lple5.. ~~ ·to '-'>CJ..te~"
'Wfi..S. SO, 2b 5ArvH''6 b.~b-~ ~} 07-:sf:, L~ S.~ o._} 6738
TW4-27 03-15-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
DescriptionofSamplingEvent: 11~7' Qv.o.r'hv Ghlo,-()J6(rr1 'ZOJ'
Location (well name): I.....___,T_w_4...;_J_'Z..;;;....:;;.g _________ __.
Field Sample ID
Sampler Name
and initials:
!:( See instruction
Date and Time for Purging I 3/1 Y /z CJI (., and Sampling (if different) ._I _3_/_lf>_/_z_o_ll _____ ____.
Well Purging Equip Used: [l[jpump or [QJ bailer Well Pump (if other than Bennet) I G-rv.o()J(;s
Purging Method Used: (][]2 casings [QJ3 casings
Sampling Event I Qu.o..f"fql~ GniM·ofOnv, Prev. Well Sampled in Sampling Event Ll_-rw __ Lj_-_lz. _____ ____J
pH Buffer 7.0 7,0 pH Buffer 4.0
Specific Conductance Ll __,_) 0.:....0_0 ___ -JI ~-tMHOS/ em Well Depth(O.Olft): I )07. 00
Depth to Water Before Purging I 3't 1.5 CasingVolume(V) 4"Well:l '--l3.tf1 ,(.653h)
3" Well: o (.367h) L_ ___ _J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)l.__l:l_" __ _.
Time I ,~,g I Gal. Purged I 70 I Time 1 r3'1 I Gal. Purged I ~0 I
Conductance I )'~};~ I pH I c;.sE I Conductance 1 l3t.t4 I pH I b,bO I
Temp. °C 114-lf5 I Temp. °C I lct.q3 I
Redox Potential Eh (m V) 1 '38~ I Redox Potential Eh (m V) I '3 K:S I
Turbidity (NTU) I q~ I Turbidity (NTU) l cr5 I
Time 1 r:yzo I Gal. Purged L ~u J Time 11'3"2:1 I Gal. Purged I loCS I
Conductance I ''2>51 I pH I ?:; • b I I Conductance I 1.35~ I pHI b.63 I
Temp. °C I lq ,c.p I Temp. °C p4.'f 2 I
Redox Potential Eh (m V) 12&1 I Redox Potential Eh (m V) I '3go I
Turbidity (NTU) I 4q I Turbidity (NTU) I q3 I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged }00 gallon(s)
Pumping Rate CalculaLion
Flow Rate (Q) in gpm.
S/60 = I \o,D
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca ing volumes (2V)
T=2V/Q= I g.7g I
j o
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I A'-'-'-"W...:..I-1::....:L=-------'
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs IE 0 3x40 ml 0 cyJ HCL ril
Nutrients Ill 0 100 ml D rn H2S04 ~
Heavy Metals 0 0 250 ml 0 D HN03 D
All Other Non Radiologies 0 D 250 ml D D No Preserv. D
Gross Alpha 0 0 1,000 ml D D HN03 D
Other (specify) jj 0 Sample volume 0 ~ D
C 'n lofl,d<. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 75. C!4 Sample Time I ObSb .__ ____ __,
Comment
~· ;~ See instruction
Arr•'\Je~ of\ SJ·t~ o...t ISO~ -roMne,... Ma ~Mdn pr~~-et1i-+;,.. ?u.~e . Pu.r~~ b~~, o..t 13)}
p\Af"~-eJ. INGll .for "'-tot~l of ID 1-Y}iYlv·)tc~. 'PVIr~e ef!Je~ o..f \'3"ll . ~+~r v.Jttt. 11\. \;-}+!(:.
G \ov..d~. L~B S•i-e o..+ )3'Z.Y
N
0
0
0
0
0
6?!1
A rn'IJeb. Ot\ s lte 6..} 0 b5~ -r;.t111c!:r MJ. G-Mrin prt~;sen1-·h. Go ll~c.} .S&\/'VI pJe~' Dep7A .j-IJ wa..-hr
w6-.S 3'Lqb s~mpl.e.s .bt,,;J~ ~+ Db~ o(.Ef, Lef'-f s.:+t; a-.f o€:.5&
TW4-28 03-14-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2 -Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I ).S.T Gh~l+er C.h)orbform "Z.Olf.
Location (well name): ._II_\N_L\.:....J_z_q __________ ____,
Sampler N arne
and initials: I ~Mer' Holl.'at;/1'H
Field Sample ID
Date and Time for Purging ~.-I -=3:....:/...:.).=b_/_zo_I(.. ____ ___J and Sampling (if different) I ~/17/Z.Oif,. ~~----------------~
Well Purging Equip Used: rn]pump or [QJ bailer Well Pump (if other than Bennet) ._I G:::......r~.~._n_J_~..:...._ ________ __,
Purging Method Used: ~2 casings (QJ3 casings
Sampling Event I Qv..~rte("l:1 Cn\oro:Fon1 Prev. Well Sampled in Sampling Event ._l_--r_'¥-.) __ L\_-_33 ____________ ___.
pH Buffer 7.0 ._I _7.;_,_0 ___ _, pH Buffer 4.0
Specific Conductance ~.-I ....:.;H:....:>o~o ________ ...JI fA-MHOS/ em Well Depth(O.Olft): ~-.1 4..:..3=.:....• f,;;;...C __ ____~
Depth to Water Before Purging 173. (07 Casing Volume (V) 4" Well:~l_Z_,'I_'-l...:...__--il(.653h)
3" Well:_ 0 _(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)L..:j l-=3'--0 __ _,
Time 11 44~ I Gal. Purged I -z..D I Time I I Gal. Purged I I
Conductance IYZ.V I pH I 5.'\;> I Conductance I I pHI I
Temp. oc I \5.~-z. I Temp. oc I I
Redox Potential Eh (m V) I q£:g I Redox Potential Eh (m V) I I
Turbidity (NTU) I n I Turbidity (NTU) I I
Time I o~4~ I Gal. Purged I b I Time l o&4l> I Gal. Purged lo I
Conductance I :\Z~~ I pH I f:.,?_.:z. I Conductance l:\2'-13 I pH I b,"ZS I
Temp. oc H"],3.S I I ,~,15 Temp. oc l l3.~() I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I \0.0
Time to evacuate two ca ing volumes (2V)
T=2V/Q= I 2 .5g I
Number of casing volumes evacuated (if other than two) I \.sY
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs '-'1 A_W____.;:";..;;;L _____ ___.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs ID 0 3x40 ml 0 !] HCL f!]
Nutrients [I 0 100 ml 0 Ill H2S04 El
Heavy Metals 0 0 250 ml 0 0 HN03 0
All Other Non Radiologies 0 0 250 ml 0 0 No Preserv. 0
Gross Alpha 0 D 1,000 ml 0 0 HN03 0
Other (specify) Kl 0 Sample volume 0 ~ D
C\.1\oride_ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1.__4....~..:1'-'-. 4-'-7..__ __ __, Sample Time
See instruction (
Comment
Arf'"i\)eO. Ot\ S.1:i-e, 6-.+ l"i39 ~nner ~ G-o.r('it"\ f1"e~rrt -t;f" pur~e · fv-r~e. b~f) o..Y }l.J'iZ
fur~eO \Ne\\ -W fA +o-t~\ of z M;f\v..t~. Pv..r~~ ~ell Jr~-flAr~e enae6. o,.-t' lYY~
\01)..1-e,.-Wlk~ cleAr. Lc+t-sit~ ~t-14~1
Arri\}~ Of\ .SJ~ at.+ 6~4'7... ~nner M~ ~rein rre.serr} -h> collect ~,.,.,ple5, D~ +o
~o..+ec wtAS 7~. b4 S.tM\1\f>)t:S. co\\ecreA o..t O&lf) Le~ s.i}e or-.+ 0~47
TW4-29 03-16-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
0
0
0
D
D
~
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 1 ~~ Qv.~rfer Ch loro'Rn¥1 'GO /C.
See instruction
Location (well name):j._ _-r,;_W_l.\:....-....;::;;..:D:__ ________ __,~ Sampler N arne
and initials: 1-r-o.Me.r HoJJ.do..j /Ttl
Field Sample ID
Date and Time for Purging I '3/U)zo lk and Sampling (if different) I 3>/ 17 /zo/k
Well Purging Equip Used: IT!] pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [![]2 casings [QJ3 casings
Sampling Event I Qu.o-rfe.rJ~ Ch \oroforM Prev. Well Sampled in Sampling Event l.___--r'_W_Y_-_2._6 _____ ___,
pH Buffer 7.0 7.6 pH Buffer 4.0 4.0
Specific Conductance ._I --'I'-6....:;.{)-=.0 ___ _,j!!MHOS/ em Well Depth(O.Olft): I qz,.so
Depth to Water Before Purging I IS , 8S Casing Volume (V) 4" Well:l 10,87 1(.653h)
3" Well: 0 (.367h) ....__ ___ _,
Weather Cond. Ext'l Amb. Temp. •c (prior sampling event).__l 5=-0 __ _,
Time I lOll I Gal. Purged 1 zz.so I Time I I Gal. Purged I I
Conductance I '-13~8 I pH IY .Sj I Conductance I I pHI I
Temp. °C 114.30 I Temp. oc I I
Redox Potential Eh (m V) I .si::Z I Redox Potential Eh (mV) I I
Turbidity (NTU) 1 ~3 I Turbidity (NTU) I I
Time I o1111 I Gal. Purged I () I Time I olE.\ I Gal. Purged I a I
Conductance I ~~2.. I pH IY.'-5. I Conductance l"l3:1S I pH I g,()y I
Temp. °C 11 3.'19 I Temp. oc 1 13.'9~ I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill -Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged zz.so gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gp.m. Time to evacuate two ca ing volumes (2V)
S/60 = I IO,D T=2V/Q= 12.17 I
Number of casing volumes evacuated (if other than two) lo
If well evacuated to dryness, number of gallons evacuated 1-z:z.so
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I :....:/t_._W:..IA_,__L _____ _..
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs Ill D 3x40 ml D [l!l HCL ~ D
Nutrients ~ D lOOml D Ill H2S04 ~ 0
Heavy Metals D D 250ml D D HN03 D D
All Other Non Radiologies 0 D 250 ml D D No Preserv. 0 0
Gross Alpha 0 D 1,000 ml D 0 HN03 0 0
Other (specify) ~ D Sample volume D [! D ~
C}l\ on'Je.. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth IL-.'1_0_, _JS ___ _. Sample Time o/SD
Comment
,-j See instruction
Arri\lJ on .site ,J /DOS ~no« AA~ G-o-rp'n pre..sefl+ for pw-~e. PlAr~e. be~o.n o.+ 100~
Pv-r8-eJ. \N(..ll -hr "'-·\-otQl of Z Miflv.Je~ \S S-c:c.onJ..s. 'P~Ar~eJ. 1.0e\\ d.rtS. P'-'-r6e 01Jed ~t--H'
1011. w,.+er LV~ G\e:>-r. L~.R-s.:i·c: ~+ lO IY.
An-:ue~ on ~i+e ~+ DIYI lo.nner Md. G-o..rr1'fl ?re.s.err} +o coiled-5t.i.tl1ples_ D-ep~ +o
v.Jo..+e.r wo-s 75.7b S"Mf>les bo.;led !).+ 0;so Lef} ~ !'f-e o..t ors-c
TW4-30 03-16-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ Sl GWM'fer C.. h l o rl>\Ofm 'ZOIC:.
I ~ s . . 1 r ee wstructwn
Location (well name): Ll _1\_W__,Lj_-_:S_.:l _________ --'
Sampler Name
and initials: I =];.rltlel 1-J,, JI;J~J-nt
Field Sample ID
Date and Time for Purging I ""1J/15/ZoJ.b and Sampling (if different) ._I ~_/_1_-b....;../_Z_o.....:~..;:;...._ ____ _.
Well Purging Equip Used: [![)pump or [QJ bailer Well Pump (if other than Bennet) I GflM)J::R:;~
Purging Method Used: ffi]2 casings [QJ3 casings
Sampling Event I Q\1\0:f'+~b Cl1loro.Grm Prev. Well Sampled in Sampling Event I '1"'"1.0~-3C:
pH Buffer 7.0 r,D pH Buffer 4.0 4.0
Specific Conductance Ll _\..:D;..;;o_c ___ ___.l ~-tMHOS/ em Well Depth(O.Olft): ._ll_O_b_.OO_;:__ __ -'
Depth to Water Before Purging I 7Zi .10 Casing Volume (V) 4" Well:~_l('-,_l7 __ -il(.653h)
3" Well:_ D (.367h)
Weather Cond. Ext'l Amb. Temp. "C (prior sampling event)'-'1 b=--6 __ _.
Time I \o"5-z.. I Gal. Purged I 3D I Time I I Gal. Purged I I
Conductance 1 ~111 I pH I C,, '17 I Conductance I I pHI I
Temp. °C I ''"'·'~ I Temp. oc I I
Redox Potential Eh (m V) I ~3~ I Redox Potential Eh (mV) I I
Turbidity (NTU) I \~0 I Turbidity (NTU) I I
Time I Ob.Sb I Gal. Purged I () I Time I OG.5& I Gal. Purged lo I
Conductance I 967q I pH l b.7l I Conductance I GZ:j'Z.. I pH I b· b'l I
Temp. oc I 1~.'30 I Temp. °C 113:65 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
Before.
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan {QAP)
Volume of Water Purged gallon(s)
Pumping Rale Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I )0.0 T = 2V/Q =I 3.1..\3 I
Number of casing volumes evacuated (if other than two) I 1.14
If well evacuated to dryness, number of gallons evacuated I '3o
Name of Certified Analytical Laboratory if Other Than Energy Labs 1 ..... 8-""W:..:..L:IIA..::..L.'--------~
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below)
VOCs 1il 0 3x40 ml
Nutrients lJ D 100 ml
Heavy Metals D D 250 ml
All Other Non Radiologies D D 250 ml
Gross Alpha D D 1,000 ml
Other (specify) '[] D Sample volume
c'h' or\~~
Final Depth I l 01.\' o:> Sample Time ._I o_6_S_.]'-----"'
Comment
y N
0 Ml
D 1!1
D D
D D
D D
D m
y
HCL Yl
H2S04 f)
HN03 D
No Preserv. D
HN03 D
D
If preservative is used, specify
Type and Quantity of Preservative:
, _... See instruction I~~
N
D
D
D
D
D
~
Arrl\)e~ on s;:fe. crt 1DY1 -r;.nner IN\d. &o.rr:" pr~errr -tbr pv-c~~ · 'Yu.~ btlo.ll ~t-IDY1
f w-~ \,~Jell -hr f1,. to.J..P.l b+ 3 m:nvJe>. Pu.r~e~ \;le.ll ar~~ Pv.,~~ ende~ {)..t-Jo5<
lt.:>o.+er \.0"-5 ~ J;H-Ie.. L.low)j· Le~ ~·te ed-lo5Y.
Ar(i\)ed. 1)1'\ !:.rte lh.J-Ob5Y -(Mil~ MJ Gv.rri11 .pre~,J-}z, CoJied-Sr;.ynfJe.s . Pep-11 -h LUqT~r
VJfAb 79."14, So.YV~pl~ bo..:\-etl od-Ob57 Le..}}-.srte ~+ o~oj
TW4-31 03-15-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP}
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I j5.i'" Q~r.f-er Ch lorot6r,n "ZOIC.
Location (well name): Ll TW __ Y....:...._-3_Z _________ ____.
Field Sample ID ITW4-'3'2~ D3l5261b
Sampler N arne
and initials:
See instruction
Date and Time for Purging ._I "3_/_I_Y_/_z_o_l-f. _____ _, and Sampling (if different) I '3/lJ;/'Zol'-.___....:....__ ______ ~
Well Purging Equip Used: m:)pump or (ID bailer Well Pump (if other than Bennet) I ..... G~r'-"~'-"'11=0.:....:.~_o..:..S ___ _.
Purging Method Used: [![]2 casings (ID3 casings
Sampling Event I m-e.r8 C:Jlloco:f~(rv\ Prev. Well Sampled in Sampling Event ._l_li_w_4_..J_z._g ____ ~
pH Buffer 7.0 1._7_.0 ___ _. pH Buffer 4.0 '1.D
Specific Conductance ._I -'-lOO_O ___ _.IflMHOS/ em Well Depth(O.Olft): I )15.,) 0
Depth to Water Before Purging I S \. ()0 Casing Volume (V) 4" WeU:I '"II .g5 ,(.653h)
3" Well: 0 (.367h) .____ ___ _,
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)l._!_3_6 __ _,
Time I }{.0~ I Gal. Purged I 7{) I Time I J{.O I I Gal. Purged I 80 I
Conductance I IZ rz. I pH I '3, o_s I Conductance I '717~ I pH I "3.0'-I
Temp. oc I lq. ~(\ I Temp. oc I jq,~3 I
Redox Potential Eh (m V) I 5"Zo I Redox Potential Eh (m V) I s )g I
Turbidity (NTU) I ,~ I Turbidity (NTU) I rz I
Time I I'DZ. I Gal. Purged I '10 I Time I JL.o.3 I Gal. Purged I )Ol> I
Conductance I 7lgs I pH I '3.0C. I Conductance I72D f. I pH I '3.0~ I
Temp. oc I lq,g'Z.. I Temp. oc I l9, ~7. I
Redox Potential Eh (m V) I 51i I Redox Potential Eh (mV) I Sl7 I
Turbidity (NTU) I l£.. I Turbidity (NTU) I )'2 I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged loo gallon(s)
Pumpin g Rate Calculation
Flow Rate (Q), in gpm.
s16o = I lD.o
Time to evacuate two ca ·ing volumes (2V)
T=2V/Q= I g,37 I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated I o
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I _/t~W:!.;/t~L=-------.1
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs Nl D 3x40 ml D ~ HCL '"6!1 D
Nutrients 00 D 100 ml D ~ H2S04 21 D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume D ~ D ~
Ghlon~J~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 70. "Z..I Sample Time 070.5
Comment
i ~ See instruction
Arrived on s.rte o..t 15'1~ lNintlf""' OJ'd. G-o.(dn rreseru:r -tor pur~e. Pw-~e bc.jo.tl O..J t3-53J
0 ' 0 1553 ~ u,r~e~ \f0ell Fo(" tJo... -to+o..\ ot" 10 lY)lt'J,~A-+GS. Pv..r~-c. et~Jed. ~+-IC.D3.
~o..fer w~ dew-. LGf} s..·t~ a..t l'-O c.
Arri\)e~ on 5•'+<-J-' ()1()1._ IMnO .. MJ. Go.r6n pr~errf +o coiled-.5M1ple~. Depth -h ~o..-1-er
w~ 51.7.b ~~les. bo..dJ o..+ 07DS LM s.4e-~+ 07DI
TW4-32 03-14-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I }ST Qv.o.r*r 01laro:t6rm zo/(;.
See instruction
Location (well name): I.__1""_W_4_-_l>--'3;;;..._ ________ ____,
Sampler N arne
and initials: I ==fo.nne.t" ~ollJ'jtt1J11t
Field Sample ID
Date and Time for Purging I 3/ I C../zo I'=-and Sampling (if different) ._I 3..::...;_/_17_/z..::.D_I'-1. _____ __,
Well Purging Equip Used: [![)pump or [QJ bailer Well Pump (if other than Bennet) I G(u.r"'Jot~ >
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Q~()::C .. fed~ Ghloroform Prev. Well Sampled in Sampling Event ._I_~_W_~_-_)_6 _____ __,
pH Buffer 7.0 7,0 pH Buffer 4.0 Y,O
Specific Conductance ._I _I ~_o_o ___ __.l J..t.MHOS/ em Well Depth(O.Olft): l~87_;'_;t:j_O __ --'
Depth to Water Before Purging 112. S 0 Casing Volume (V) 4" Well:l 1 O,OS 1(.653h)
3" Well: 0 (.367h) '-----...J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)'-1 _,\=z_• ---~
Time l!:,l}S I Gal. Purged I \3,33 I Time I I Gal. Purged I I
Conductance I '-\'-\~~ I pH I S.ll I Conductance I I pHI I
Temp. oc I p:\. (;.I I Temp. oc I I
Redox Potential Eh (m V) I ~0'1 I Redox Potential Eh (m V) I I
Turbidity (NTU) I \b I Turbidity (NTU) I I
Time I og31 I Gal. Purged I 0 I Time I o8';:s~ I Gal. Purged Ia I
Conductance I ~3q'L. I pH 15.71 I Conductance ~~~QO I pH ls.7..3 I
Temp. oc I \;:.,63 I Temp. oc l l3·'' I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged )3.3~ gallon(s)
Pumping Rate Calculalion
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I )(),D T = 2V/Q = I '2.. 0 I I
Number of casing volumes evacuated (if other than two) I \.:s3
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs IL.......:.:/l:...JW..:...ALL...=:~=--------...J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs 1!!1 0 3x40 ml D (]) HCL I! D
Nutrients ~ D 100 ml D I] H2S04 Ill D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D 0 1,000 ml D D HN03 D D
Other (specify) 111 0 Sample volume D ~ D 12
C\-, lor\~~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth L-1 %..::...4_.~'15~---' Sample Time
Comment
, ~ See instruction
Acr i\ld on si-\--G o..t 1~41 ~'"'er "-~'&. 6-Mrir"l pre:~el'\+' h r -pur~ c. Pu..r~ ~~O.t1 o..r 134Y
Pu...f~-ed l.t.)el\ ~~ t1-.. ·h~+ea.l oF \ M•'t1v..-k zo ~-cc.on~S. Pv...r~d. w dl ~~! Pv..r,1e -etlJ-e4 ~t l3Y5
W~f~, IN~ Gl~. Le+f. .S.\1-e ~t 13'1/
Au·: -ve.O. O'f\ ~l'te: ext og.35 ~(lner' ~(\~ 6-b..rr;l\ f'~'"e.sefl+ +b c.ol\ec.+ S4mp1e~. o~r~ 1-o U)o.+~("
wo..S 72,4!. .sc..rr~ples. bo..:l~ o-1-6S.J8 Left-s~+~ ~t 0~~0
TW4-33 03-16-2016 Ina not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description ofSamplingEvent: I p.T Qv-w-'fer Cll\\orO'&crvt ZO\~
See instruction
Location (well name): ._I_T_W_q_._-_3_'"1.:....._ _______ __,
Sampler N arne
and initials: 1-l""rt,a-Nolltaw=n~
Field Sample ID Tw4~3'-I_0.31~ 'ZOlfo
Date and Time for Purging I 3 / I 5 /'ZO...U. and Sampling (if different)
Well Purging Equip Used: (!!]pump or IT!] bailer Well Pump (if other than Bennet) IGruflJ..,fos
Purging Method Used: (][]2 casings IT!J3 casings
Sampling Event I Qv..o..rf';r.\") G)\\orot~M Prev. Well Sampled in Sampling Event l --rw Y-3} L----------~
pH Buffer 7.0 7.0 pH Buffer 4.0 4.o
Specific Conductance .._I _l_o_oo ___ ___JI~-tMHOS/ em Well Depth(O.Olft): ._I _Gl7_._W ___ __.
Depth to Water Before Purging I 71. &S Casing Volume (V) 4" Well:! !'· S5 1(.653h)
3" Well:._. _o ___ __.(.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)!._ 7_0 __ __.
Time I )C. I\ I Gal. Purged I 3S I Time I I Gal. Purged I I
Conductance I 3'\&S I pH I r;,.~ I Conductance I I pHI I
Temp. oc I \q,q~ I Temp. °C I I
Redox Potential Eh (m V) I ':S53 I Redox Potential Eh (mV) I I
Turbidity (NTU) I ql I Turbidity (NTU) I I
Time I 0704 I Gal. Purged I 0 I Time I o7o~ I Gal. Purged le> I
Conductance I '3<fOq I pH I C..77 I Conductance I ~~-z.o I pH 16 ~73 I
Temp. °C I 13.08 I Temp. °C I 1'3, \ 1 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I )O.D T=2V/Q= 13.31 I
Number of casing volumes evacuated (if other than two) I Z.ll
If well evacuated to dryness, number of gallons evacuated ~-:I3,__S.._ _ _,
N arne of Certified Analytical Laboratory if Other Than Energy Labsl ,_ ...,.k'-\\J_/{\....::...,_L _____ _.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y
VOCs 3] D 3x40 ml D ~ HCL e
Nutrients lJ D 100 m1 D f) H2S04 ~
Heavy Metals 0 0 250 ml D D HN03 D
All Other Non Radiologies D 0 250 ml 0 D No Preserv. D
Gross Alpha D D 1,000 ml 0 D HN03 D
Other (specify) El 0 Sample volume D ~ 0
Gh \or ide.-If preservative is used, specify
Type and Quantity of Preservative:
Final Depth! L.. 9...:..q..:....;.,Cj...:..7~----' Sample Time L..l 0_7_ll5 ___ __,
Comment
, (J. See instruction
Ard\lcd. on 53+<: ~} I'Z.OS J;Mer ~1)0. G-o.c<'in pre&-Gtrt .-Rr fV\'<3e· Pu~e ~Qfl
~-t \ZD<&. t'v.refc\ l,tl)el\ ~ "" i-o-b.\ o-f 3 'MiY\lAt<.> 3D Sec.cm~s ?v.r6eJ W~ll dr.....,l.
Pu.r~-e.. ende~ ~+ l'ZII. WuJ~r wa.s MC).S~ cleo.f"' L.e.ft-.S•}e t'.:l-l'Zl~ -....l
N
D
0
0
D
D
~
Aroi\l~~ on s.l-\-e-~.} 070'l ~nner o.n~ G~(ri11 Pre~e.Jl} -}o Goll\'!:cl .Sc:~mpk.>. Dep~ 1t> W.~tter
INC\) 71.8S ~~rv'\ples b().,\e~ o.t D7DS \..eft srt!. 01.-d'-0107
TW4-34 03-15-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
See instruction
De~riptionclSamplingE~nt ~l~l-~~~Q~~~~~e~r~~~~~~~~~~~~~~~~~~~~~~~
Location (well name): ~l _;TW:._;__:Y_--=45::3..oo!.~~~~~~~~----~
Sampler Name
and initials: :=:ro.mlu R.~} ll ;Jt!fiH
Field Sample ID
Date and Time for Purging l "'1>/JS/zolL. and Sampling (if different) L----"3--=-/_lC.~/_"ZZ___;I./..=--~~~~__.
Well Purging Equip Used: ~pump or [gJ bailer Well Pump (if other than Bennet) I Grv.f\J£.s
Purging Method Used: [1[]2 casings [![]3 casings
Sampling Event I Q'-A.o..l'ter ~ G 'n l orotorrYJ Prev. Well Sampled in Sampling Event L~-.-r;~w-~~--3~~:.__~~~~---J
pH Buffer 7.0 pH Buffer 4.0
Specific Conductance ._I _l_O_DD:;__~_,_.l !J.MHOS/ em Well Depth(O.Olft): IL.....::...~7_,.=5_b __ __.
Depth to Water Before Purging I 74 ,I, Casing Volume (V) 4" Well:ll-g_,7_1 ----11(.653h)
3" Well:. o .C.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl~l j.L0 __ ___J
Time I \7.~1 I Gal. Purged I 1~.'?0 I Time I I Gal. Purged I I
Conductance I Yl\1.0 I pH I £;.4~ I Conductance I I pHI I
Temp. oc 119.66 I Temp. °C I I
Redox Potential Eh (m V) I ~bq I Redox Potential Eh (m V) I I
Turbidity (NTU) I zg I Turbidity (NTU) I I
Time I 071"2.. I Gal. Purged I () I Time 1 o71~ I Gal. Purged l o I
Conductance I Y3'=i3 I pH 1 ~.sg I Conductance I 4'32lD I pH I b·~3 I
Temp. oc I I3.CY I Temp. oc 11'3 .10 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate CaJculaLion
Flow Rate (Q) in gpm. Time to evacuate two casing volumes (2V)
S/60 = I 10. D T=2V/Q= I L7Y I
Number of casing volumes evacuated (if other than two) I '.s~
If well evacuated to dryness, number of gallons evacuated I I>.~
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I A....:..W"--A'-L _____ __.
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs ~ D 3x40 ml D (l!J HCL M D
Nutrients ILl D 100 ml D ~ H2S04 ra D
Heavy Metals D D 250m! D D HN03 D D
All Other Non Radiologies D D 250ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume D ~ D ~
C'nloribe If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1~.-S::..::S~-~07.....::..... __ _, Sample Time o-,,~
Comment
. ~ See instruction
A(ri-v~ on si-te o-+ \237 -fo.t~ne-r t~o.l\b-G-Mr;fl pr~-end-.for pur~€-?u..r~{-.beja.n Aj--)7..LJ()
?v.~~eJ. w-el l ~Of' ~>. -hf(i..\ o+ l t'Y1 in""+c:. zo SeCPt~~>. Pur~d v.>GI\ ~j. PlA,.~~ enJeJ (At-IZlfl
\,VG,_fer w~ mo~¢-~ C.l~or. Le.f\--s.i ~ ~t rz.y~.
A r(ivJ. on .5ite ,.,+ Ollb '),..Mer M~ &c1.rrin p<"e.serJ .Q. -k CDI!ed .S~M?les~ D~ +Z>
'-Vo..-t~c-w~ /Y.Jb ~mpl~ .bo.;lecL ~--r 0713 \,...-ef} .s.rtc 11..+ 0715
TW4-35 03-15-2016 Ina not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan {QAP)
·:r-e~ ATTACHMENT 1-2
' ·. .,-;;~ERG YFUELS WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I \ 5T Gv..o.f"+er ChI olot(;IIYI "ZO/ '-
Location (well name): ._I "1'_W____;li_-_:)_C. _________ _.
Sampler Name
and initials: l ;y;nll~r' H(j1),'J.-jJ1iJ
Field Sample ID I -rw 4-~'-03"' (.OIL
Date and Time for Purging I 3/ l S/ £.0 IL and Sampling (if different) I '3/IC../zo/c,
Well Purging Equip Used: a[] pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: IT[]2 casings [QJ3 casings
Sampling Event I Q v,()..r"te:r~ G'h loro+orWI Prev. Well Sampled in Sampling Event 1._-nJ __ LJ_ ... _D ______ _.
pH Buffer 7.0 7.0
Specific Conductance ._I _)_OO_O ___ ____.It-tMHOS/ em
Depth to Water Before Purging I SG, SO
Weather Cond.
Time I 1019 I Gal. Purged I 11.50
Conductance 1 -zsc:9 I pH I r;:~l
Temp. oc l l~.~z: I
Redox Potential Eh (m V) I Z:$3 I
Turbidity (NTU) I n3 I
Time I 0'-YK I Gal. Purged I l>
Conductance l -z.3!:>Y I pH I ,,go
Temp. oc I ]'3.bg I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater
I
I
I
I
pH Buffer 4.0 '1,0
Well Depth(O.Olft): ...... 1 __...q __,_q.;._o_o __ _J
Casing Volume (V) 4" Well:' Z7.75 ,(.653h)
3" Well:._ __ CJ __ _...(.367h)
Ext'l Amb. Temp. ·c (prior sampling event)l'-=5'--o--...J
Time I I Gal. Purged I I
Conductance I I pHI I
Temp. oc I I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
Time 1Db50 I Gal. Purged I a I
Conductance I Z37~ I pH I b.7C::. I
Temp. oc I 13.i3 I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged \7.SD gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I \0.0 T=2V/Q= I 5,0S I
Number of casing volumes evacuated (if other than two) },JI
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs 1'--'-'A:....:.W-'A_L _____ _,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below)
VOCs [1J D 3x40 ml
Nutrients rn 0 100 ml
Heavy Metals D 0 250m!
All Other Non Radiologies D D 250 ml
Gross Alpha 0 D 1,000 ml
Other (specify) 1!1 D Sample volume
C~\or; j.<
Final Depth l.__Cl...J...tO~.q...:....g __ __. Sample Time I.__O_b_q_q __ ___,
Comment
y N
D M
D m
D D
D D
D D
D [21
y
HCL f2t
H2S04 ~
HN03 D
No Preset-v. D
HN03 D
D
If preservative is used, specify
Type and Quantity of Preservative:
·" See instruction
I "Y'
Arrlvr.~ on site "'} }Dl'Z. ~~~tl~r Mt\. &a.rr:f\ pf"~.s-er'\+ -t='or fv.r~e. ?I.A'3e b~l\ o.+ 10 15
Pv..~e~ ~<II hr o,. i-o+C\\ o-t' 4 M:n"'i<-~ '-\S S~Lo11~S . ?w-ts~.J. wd\ ~r~. 'Pu-.f~e enJ.eJ o.:t
101'\. lrJA.+er w~ fA. \:t+le G\ovJ~. Le.J+ s.lk ~-t-lOZJ
N
D
D
D
D
D
IE
A rr i\.led on S1:..\-e Q\.1 O{:, ~b -r;_flne( tAr'\J G-o..r6n pres..efl+ +o coll.ec.-1 ..SG\1>1f\e~ Dep.Ji f.o l,..)eJ-cf'
Sc..~ple~ b,i)etA "--} Ob4'i L..ef} ~ rtt:: ~J Ob51 57, '2~
TW4-36 03-15-2016 lDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 1 S. 1" Gu..o-rier Gh loro:f~nYl "ZOI fo
Location (well name): ~..1 _-rtJ.:_:_:_L.!,_I ---'3:.....~.7 _________ --J
Sampler N arne
and initials: I ::YMr\~r Hollld4.j/1ll
Field Sample ID
Date and Time for Purging ._l_:3_;}_tt_,;./_;;;z;;.,;o;..:;:/i.=------J and Sampling (if different) ~..1 _M...;'/:.....:1\~-------_J
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) I Go.rrhnUl!V...S
Purging Method Used: 002 casings [QJ3 casings
I ~W4-Z-z. Sampling Event I Q v,<>..rte..-1.!::1 c.,h lorofOt'rY) Prev. Well Sampled in Sampling Event ._ _________ ___J
pH Buffer 7.0 7.0 pH Buffer 4.0 L\.0
Specific Conductance ._I _l'-=O~D=o ___ ___,JI f!MHOS/ em Well Depth(O.O 1ft): L,_l _,!li-=Z..:....:. o_o __ __J
Depth to Water Before Purging I b 7..'30 Casing Volume (V) 4" Well:l 32. 4.5 1(.653h)
3" Well: 0 (.367h) L....:, ___ _J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event) I gp '--'="-------'
Time I l0'2..5 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I 4YI/ I pH 17./S I Conductance I I pHI I
Temp. °C I \S,sq, I Temp. oc I I
Redox Potential Eh (m V) I ~LS I Redox Potential Eh (m V) I I
Turbidity (NTU) I 0 I Turbidity (NTU) I l
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. °C I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged D gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I \{,,0
Time to evacuate two casing volumes (2V)
T=2V/Q= I 9.05 I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated l o
Name of Certified Analytical Laboratory if Other Than Energy Labs AWAL
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs "'FJ D 3x40 ml D m HCL ID 0
Nutrients lJ D 100 ml D f] H2S04 lJ 0
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250ml D D No Preserv. 0 0
Gross Alpha D D 1,000 ml D D HN03 D 0
Other (specify) ~ D Sample volume D t1 0 11]
(., 'h \()~\ de.. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I b :5. %4 Sample Time 102.5
See instmction
Comment
A.~"e.d on s.tk o..+ }OZ'Z. lMtKI Mil G-o..cri" 'P'e~e..nr i-o c.olle.d So.n,pl~s.
So.n'\p\~s eo ll~+-ca o.+ Hrz.s
L~B-sit~ ~+ 10-z.~
Wo..t<.r wo..s.. C.}eo.r
TW4-37 03-09-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I I ~-r-Q"'o.r+c:r C..n l oro fOM"M -z.,o I G.
See instruction
Location (well name): ._1--r_w____.:L\'--..:::.C._D _________ __,
Sampler N arne
and initials: I ~"riel"" ffoll·d~~..j/'f/}
Field Sample ID
Date and Time for Purging I '3/"z:z./z.o)~ and Sampling (if different) ,__.N:_Y'A ________ _,
Well Purging Equip Used: IT!) pump or [QJ bailer Well Pump (if other than Bennet) ._I _..h_VA ______ ____.
Purging Method Used: [QJ2 casings [QJ3 casings
Sampling Event I Qv..a..r+e..rb Cb \oro .forM Prev. Well Sampled in Sampling Event ._I_M_w_-_3_z. ______ _,
pH Buffer 7.0 7.0 pH Buffer 4.0 ~.0
Specific Conductance L-1 --=--1 0.....:0;_:,0 ___ _,1 ~-tMHOS/ em Well Depth(O.Olft): L-1 _0 ____ _.
Depth to Water Before Purging 1.__6 __ _____, Casing Volume (V) 4" Well:~_D ___ -11(.653h)
3" Well:. o (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! ....:.;;\.5.=11 __ _,
Time I \4 sq I Gal. Purged I D I Time I I Gal. Purged I I
Conductance I 0 .& I pH I 7.~0 I Conductance I I pHI I
Temp. oc I \&, &D I Temp. oc I I
Redox Potential Eh (m V) I 3\0 I Redox Potential Eh (m V) I I
Turbidity (NTU) I 1.\ I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I () Time to evacuate two ca ing volumes (2V)
T = 2V/Q =I 0 I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated 0
Name of Certified Analytical Laboratory if Other Than Energy Labs
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs [11 0 3x40 ml 0 I:Zt HCL PI D
Nutrients C!l 0 100 ml 0 Ill H2S04 l!!l D
Heavy Metals 0 0 250 ml 0 0 HN03 0 D
All Other Non Radiologies D 0 250ml 0 0 No Preserv. D D
Gross Alpha D 0 1,000 ml 0 0 HN03 D D
Other (specify) L$ 0 Sample volume 0 [!I 0 f2g
Ch\o(l'ck If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I __ o ___ __, Sample Time
See instruction
Comment
TW4-60 03-22-2016 lDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I }Sr Gv-.o.ffer G~lorlrRlrm "Z.Oib
Location (well name): ~.-1 "1\~\.J---'-1.4~-..;;;.bS__; ________ __J
Sampler Name
and initials: I :::=r;rmer" Holl ."~/'T'B'
Field Sample ID
Date and Time for Purging 1._3;:_/'-'1'-4'--/_..:,z _O_Ib _____ _, and Sampling (if different) 3/IS/ZO/'-'----~--__; __________ _,
Well Purging Equip Used: ~pump or [QJ bailer Well Pump (if other than Bennet) l&ru.~~atos.
Purging Method Used: []]2 casings [QJ3 casings
Sampling Event I Qu_()..t='krlj GhlorOfOrM Prev. Well Sampled in Sampling Event ._I_Ji_YJ_L\_-_1_2. _____ ___.
pH Buffer 7.0 7.0 pH Buffer 4.0
Specific Conductance ._I ---'-lOOO ________ ___,IflMHOS/ em Well Depth(O.Olft): I ]071 0'0
Depth to Water Before Purging I ~q ,-,...5 Casing Volume (V) 4" Well:l '13,':tl 1(.653h)
3" Well: 0 (.367h) '--------'
Weather Con d. Ext'l Amb. Temp. oc (prior sampling event) I-I _13_0 __ __.
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. °C I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I 1
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. °C I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged IDO gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I \0,0 T=2V/Q= I <6.7g I
Number of casing volumes evacuated (if other than two) lo
If well evacuated to dryness, number of gallons evacuated l o
Name of Certified Analytical Laboratory if Other Than Energy Labs ._IA_W__;_A_L ______ __,
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs ffl D 3x40 ml D 'Ill HCL ~ D
Nutrients E D 100 ml D f) H2S04 f) D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) ~ D Sample volume D 'fJ D l!J
Ch \ot"IJc If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 7 S, 'I~ Sample Time
Comment
~ See instruction
o-f TWY-2g
TW4-65 03-14-2016 ID not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of 2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
?:;ji;!tl~ ~~~ER'GYFUELS
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
. See instruction
Description of Sampling Event: I I ~-r Qv.,..rfer-G"' lorof;;r"1 "ZOI(:, ~--------------------~------------------------------------~
Location (well name): ._I _JW __ 4..;...-_7..;.....;...D ________ ___,
Sampler N arne
and initials: I ==J:noer J},j/IJA.j/171
Field Sample ID
Date and Time for Purging I 3/zZ/Z.Otl.o and Sampling (if different) I"' IA L----~--------------~
Well Purging Equip Used: (![]pump or [QJ bailer Well Pump (if other than Bennet) ._I ...;;.G.-'E:........;..D __________ ..--~
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Qv-o.(""f~('h G'r'l) orofDirVl Prev. Well Sampled in Sampling Event 1/w y-ID .__ __________________ ~
pH Buffer 7.0 7,o pH Buffer 4.0 Y.D
Specific Conductance ._I _l_O_O_D ___ ~l!!MHOS/ em Well Depth(O.Olft): l l3z,.so
Depth to Water Before Purging 116. g.s Casing Volume (V) 4" Well:,3b..33 l(.653h)
3" Well:._ __ o ___ .....J_(.367h)
Weather Cond. Ext'l Am b. Temp. oc (prior sampling event) I (:/
~-----'
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) l I
Turbidity (NTU) I I Turbidity (NTU) I I
Time I I Gal. Purged I I Time I I Gal. Purged I I
Conductance I I pH I I Conductance I I pHI I
Temp. oc I I Temp. oc I I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged 7~.12 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I ,7_11
Time to evacuate two casing volumes (2V)
T=2V/Q=I'334 .'JZ I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated I Z~
N arne of Certified Analytical Laboratory if Other Than Energy Labs ~..I .!../'J_;W_..:~=L _____ ___J
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y N specified below) y N y N
VOCs Ill D 3x40 ml D ~ HCL ~ D
Nutrients 111 D 100 ml D ~ H2S04 ~ D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250 ml D D No Preserv. D D
Gross Alpha D D 1,000 ml D D HN03 D D
Other (specify) rN D Sample volume D UJ D '0
r Ch\onJc, If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I KZ..l-i'Z. Sample Time
Comment
[..-.1 See instruction
TW4-70 03-22-2016 ID not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
TabC
Weekly and Monthly Depth to Water Data
Weekly Inspection Form
Date J-!2 -'Z.Ql~ Name =::r;Y;n,~ lJo II,~Aj
System Operational (If no note
Time Well De~th* Comments anv problems/corrective actions}
lY1Z1 MW-4 7 fLI.{.S Flow 4.1.{ ( . 'iss .)\Jo
Meter '68/0 S~,·7q ( Ye~o
\4\/ MW-26 t;.Ll,g3 Flow ~.5 /""Y~No
Meter 5.C,Cf 7 J. ~ r-res ~-0
~-1W4-19 -~"t .3 f( Flow IKLO ff.e&._)No
Meter z-t·:Y:t-z.q :~ (Ye~ No
\ '"\ l '"\ 1W4-20 b4.1b Flow 7.0 (Yes)No
Meter l\ 4'Z. 7 1. q 0 {YeS) No
I
~~~ TW4-4 i'Z ~q Flow ll.b t: Yes..-~
Meter '2.59.;''Z.77. 0 ( Yes .blo
1400 TWN-2 'Z.S.'t'-1 Flow lk 5 r"Y~s ,.No
Meter ~ t;C:. '2. ~ o ./ f'Ye.VNo -\'101 TW4-22 5&.q1 Flow l~.o ~~~
Meter ·'Zf<!=-.1 H .4 ( TeW No
140L( TW4-24 '-4 .\l Flow l b.~ » Meter 'Z.03755Z...ll . '
13SL.. TW4-25 G.Y.43 Flow \.5.0 Q es tJO
_, ..
Meter IY ISII'Z.q <..xes ]to
l\..\')1 TW4-1 _go. liS Flow 15,0 (Yes) No
Meter 9Y~5G..D (Yes) No
~
\41.4 TW4-2 SC0 -0 't.. Flow \1,0 ( Yes )Jo
Meter £:1 I ~E-. I Z r TErs'\ No ,
I 1:.1 '2. I TW4-11 t.J/.32 Flow lb.5 (~No
Meter Z '31 be,. s< CY_eyNo
-..r-..
i~!>'Z TW4-21 b~rOb Flow l b·S fus) No
Meter 30~'i&./~ ( Ye~ No -.,.....
1410 TW4-37 bZ.i~ Flow li.O ~No
Meter <Z.."-'t rq o. f( (Ye!iJ No -
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): 7"-''1-Z'-f M~tci (.Veo.~ r~pbceJ
• * Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date d 11 /1 6
System Operational (If no note
1me Wll e D th* ep1 c t ommen s an~ Qro bl I t' . ) ems correc 1ve act1ons
\415 MW-4 go.32. Flow _t .. L_g ~.No
Meter ~'l3G\D.ot..t (feS\ No
IDZS. MW-26 fS,.6·g Flow s.o ~1\_No
Meter 5SZ.:SS~ 'io (fej) No
1145' TW4-19 63.qg Flow I S'.l-C{el) No
Meter •z.g\45~.10 ~No
ID\G TW4-20 76. f?D Flow 5.-z.. ~No
Meter IIS'Z5D.7't <::f_ii No
I I
14'2.3 TW4-4 76.4g Flow II.D (YeS) No
Meter 'Zl.2o :?.5. '4 0 (Ye~ No
M47 TWN-2 32. ~.s-Flow I«·Y (Yes) No
Meter .5S'13L14 .So (Ye~ No
IDilz. TW4-22 5<6. 'l6 Flow II (, J _(YeS) No
Meter 2~706'-\ 30 (.'(~ No
D'lS~ TW4-24 64.S'<~ Flow I b.D <Y~~ No
Meter gR"6L 46 ~~_No
"qc.t1 1W4-25 67.5~' Flow \5"6 Cl~ No
Meter tiA> 1"4ZZ{2.'Z.~ b ~e~_ No
IL.fl({ TW4-1 q·z.oo Flow 15.0 01..~ No
Meter qU>lZ.-.00 ~ No
Jl.!IL TW4-2 ~1.15" Flow Jg,4 ~No
Meter t}:Jl4'L~O ~No
IYOG 1W4-11 q I, t'l Flow 11.o ~ Ye3 No
Meter 234'2.4 '2/) <..Ye~ No
O'l3ti 1W4-21 68'.03 Flow \6.6 ~No
Meter :3'117"\S". 17 ~es No
loi.S 1W4-37 6?... I g Flow \ t. 4 -·~No
Meter z 7 ~ -z.Jl Zo \.,Yes\ No
ional Problems (Please list well number):
-'Z.b,
Corrective Action(s) Taken (Please list well number): Qc.fl V..c.d bw \ b> I-\ e..vV...p~. (r-w 4 -I~~ .AAW-zt)
C.. • Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
( Date Name
System Operational (If no note
r· 1me Wit e D th* ep· c t ommen s an~ ero bl s1 r r l em correc 1ve ac 1ons
1~1'-i MW-4 <6\.Z3 Flow 4.5 ('18$ No
Meter _9_0_0 2 () i 7 4 ~No
IYZl MW-26 63.~~ Flow ~.o ~ No
Meter 5'173'Z..OD ("Te} No
1:;1..\o TW4-19 6 4. 2.8 Flow 18.5 r<fe~ No
Meter zqo34S.so Q'e§) No
l'-\Z.'{ TW4-20 63.go Flow h.6 !Y'9~ No
MetE;}r 116 'Z. 2.5 • .39' Zfe~_ No I
I -I
140~ TW4-4 76.ZI Flow 1\.0 l'fe~ No
Meter Z.6.6SDO. 7o 'TeS) No
1440 TWN-2 ~z.t-tc Flow I~-~ if_ es':;_ No
Meter S72Dst6.6o 6£S;> No
I4Z'1 TW4-22 ~1.35 Flow I 17.3 ~No
Meter 'Z...~'f'Z.q6:. 70 -~No -
( \~~~ TW4-24 64.0~ Flow 16.0 l(~No
Meter l '1oZS.s~ /'{'8} No
1'1'-tb TW4-25 h3.Z3 Flow 15.D {fe§ No
Meter 1 '1317 se:.so i(es) No
1411 TW4-1 '12.3_'6._ Flow IS. L. )fe~ No
Meter '17552.. 30 ~No
1411 TW4-2 ~D ~~ Flow i/,c )reS) No
Meter 9~75'2..-.SC ~No -
141.0 TW4-11 q I, 'ir) Flow I !f. . .5 (f.JJ.S)No
Meter 237/0 !30 (Yes) No
14~ l. TW4-21 6~.Y I Flow lb· 4 fie§l No
Meter 32.1734. 13 ~No
l4 2.(; TW4-37 b4,Z.lf Flow 17.0 (1'a"j No
Meter "'Z.'itS'2.CJ£.CiD (re~ No
Operational Problems (Please list well number)
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest O.D1 feet.
(
Date , (zsft6
Weekly Inspection Form
Name 6a..r"'' ,.._ Pt-~-(~
System Operational (If no note
T' 1me Wll e D th* ep· c t ommen s b I ) an~ ~ro !ems correcttve acttons
12...48 MW-4 ~0.7.5' Flow L\.5 (.?eS) No
Meter qo7y zz. bD ~No
}555 MW-26 f,S,So Flow 2> .. 0 (YeS1 No
Meter 6112.Cf.Cfo O'el> No
1.55'1 TW4-19 6_.. 87 _')' . ._ Flow lB.\ ('Ye~ No
Meter Z. C( "il.t,O. 0 C:.: ~No
I 5 ')[J TW4-20 ,3_35 Flow 7.0 ("Yej No
Meter lli'Z. 2 '· '-12. eYe~ No
12L.{ 2.. TW4-4 -"]3. so Flow \\-5 (Yes· .... ~ No
Meter 2.7\053.60 c:Ye;=JNo
J5Zh TWN-2 33. 31..{ Flow (~ No
Meter 57b~'1B ~U · cYel No
IS6.S TW4-22 sca.~t Flow I S .. o ves No
Meter '2'111 y l. 40 {~ No
15LS TW4-24 b4.0"'1 Flow lb.Z... ,/YeS\. No
Meter '2.'i!S1S .~ (-Yes'• No
i5H TW4-25 6~.55 Flow P·L 4 (Ye's No
Meter li.\40bgLt_ 30 ~No ....... .
1211'-\ TW4-1 So,Gc Flow \6 .. 0 (Yes )No
Meter 'i<1o Llq. &o f{eS) No.
IZSI TW4-2 qg bq Flow If.. I..\ (lie~ No
Meter '1&1.{36 .. 40 tles\No
I 2.5:3 TW4-11 Cfl Sb Flow 16._n ( r'fes\ No
Meter 2.'-\.0£.) I. 70 Z_VeS) No
151l.{ TW4-21 67.8g Flow 16.2-f(e$) No
Meter 33\\ 'f.S.'ll CYAsJ No
I.SoZ.. TW4-37 5LZC Flow 1 g.o ~e..:s_ No
Meter 2'13701 .90 <:.Yes No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest O.D1 feet.
\\~1Z Monthly Depth Check Form
Date //-z7J 16 Name Gc..rriA.. Pei!N\.lf. TAt:y<'..(..C HoiLti~y
Time Well Depth* Time Well Depth*
I Z'Z.-'3 MW-4 ~o. t1... rz.so TWN-1 C::,Z,jD
\~V-\ TW4-1 ~1.4j 12£1 TWN-2 4.Z9.98
tz.:L'L TW4-2 CJo.6.S' }2.53 TWN-3 39.30
1325 TW4-3 56.96 \306 TWN-4 55. z.z_
I'Z..l..' TW4-4 7ht8.S I':'> I~ TWN-7 g5.40
l '3 "2. ""Z. TW4-5 ,t..[.bo 130'-1 TWN-18 E:.0.50
~~~I TW4-6 7Z.30 1~10 MW-27 ~~\3k. I
13Z9 TW4-7 7].1.0 IY3;;t MW-30 75.56
13'2.] TW4-8 81.l5 iY'Zc MW-31 f>3.56
1~23 TW4-9 (,Z..L\'t
\:3\Cf TW4-10 62. 10
I'Z.ZO TW4-11 @1-'ti.YQ
1407 TW4-12 ~.5::.76
1401 TW4-13 52. \'2... )YO~ TW4-28 39' ~L(
\357 TW4-14 8,Q. L..\Z. l~Sb TW4-29 73,'6~
J Z.l i TW4-15 67. 9Z. 1349 TW4-30 76.11
tZ.YI TW4-16 b~.DD 13118: TW4-31 8Q.QS
1Yl9 TW4-17 77.,35 I~QS TW4-32 Sl.3.!;
IZ47 TW4-18 6.5'.51 I~Lil. TW4-33 72 .s.::,
\'2..01 TW4-19 64. 07... I~Sj TW4-34 7!.5
LL\6. TW4-20 63.5'L L351 TW4-35 71..\.~0
1L..yS TW4-21 (:.'1.10 1359 TW4-36 56 .. 68
I'Z..I'=\ TW4-22 59#yg
1337 TW4-23 G'l.~5 I'Z..\5 TW4 -:57 6_4.D z
I'Z.t'L TW4-24 G_t..t.oo
t·Z.I 0 TW4-25 6.5t z:z.
13:?.'=1 TW4-26 66.67
l~YY TW4-27 gO. 6:>
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
System Operational (If no note
•me Wll e D h* ept c t ommen s anJl ero bl I ems corrective actions)
0~'-\< MW-4 ~'L'-\ '2.. Flow Ll. '-\ ?(e~ No
Meter ~ lb4 3\.66 t No rre~
02."!<;. MW-26 ~7. ~I Flow '7.Ci lYe~ No
Meter 6l.G2l oo ~No
011..\5' TW4-19 6'. 82. Flow ~~ ~ (f'eS\ No
Meter "3 1 os 2.~. \ '-\ ~No
OS3i TW4-20 6'5.1'-{ Flow /_Q (?e~ No
Meter i l 9b15. clc ()'e§) No
' J
oss~ TW4-4 75.~ Flow I\.~ ({e§; No
Meter 2/6-SI..'l..~ ~o (Y"eS) No
OSHL.i TWN-2 3'-\ · (O Flow \S 6 6e?)No
Meter 5~117~ /tJ tf'e~ No
a-az.~ TW4-22 A6, 7D Flow 1 s.a {YesJ No
Meter '2.. q '3.S 4 I . ~ c'Ves~·)No
O~Zi'l TW4-24 6L-L,0\ Flow ~-~ (Ve~ No
Meter ~qq kD ~-~ q"e~ No
Q9£)q rw4..:2s ~4,62'-Flow \S.o rYes ) No
Meter \4517 \.C.. "Z..C <Ye:§l No
og4q TW4-1 ~0,40 Flow 1 E>.o (Yes) No
Meter \ D I 0 9£. I{) ("{eiD No
0~~? TW4-2 eeL Yb Flow \I.e ((e:.sJ No
Meter £1t~5Tl .... 10 X§S'~ No
OS'!-'\ TW4-11 'l't. 7~ Flow u;z... (Yej)" No
Meter "Z..Y37 I nl':J ~ No
0Bo5 TW4-21 6• c. I'?." Flow 16~ 'L. ~No
Meter '3 i..J.30 43 f) 2... ~No
losu TW4-37 63.40 Flow 16.6 ,~No
Meter 30i...lbSZ.Yo ~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 2./1 0 /1 6 Name Ge..rq 4 fc..l ...... ~..c;.c
System Operational (If no note
1me W ll e 0 th* eDl c t ommen s anl£ ero bl sf I . ) em correct ve acttons
0~32.. MW-4 ~1-l'::>.S Flow u '-\. -~No
Meter _ q 2_3_6_ 'U . Z.o_ (!e]) No
0 '6Z..J MW-26 k3 .6Z.. Flow ~Lo (Yei.) No
Meter {;1-{Y)I. ~L '2.0 (Ye~ No
011.-\0 TW4·19 65 2-..2 Flow IS. z.. ~No
Meter 3i93bb l.o eYE® No
t_) ~ lD TW4·20 ~-I-t I lS Flow ~7 2 (YeS\ No
Meter II Cj 7 ~-5, '2.1 ~es':l No
o~~q TW4·4 7'-i 42.6 Flow \\,2... nre$ No
Meter ZSD'l52.(. CjD _Cf§.~No
DSoY TWN-2 33.'7l Flow \ ~.6 /?es\ No
Meter 5'l47So . .SO ("('6sj No
C) S i ! TW4·22 b~S·-~ Flow 17.u ~No
Meter 2.'l533o Cfo ('YeSi No
090'l TW4·24 64 3_6 Flow \t.D rY8S) No
Meter t-Hl?, I'\ I I (f9'§) No
t.>7S<r. TW4-25 {:.--t.o_a_ Flow \ S.o teS) No
Meter I '-1 b o o 6 7. zc ()'eS\ No -
0~37 TW4·1 q I. z.q Flow II. 0 cl'el' No
Meter I r-' z. 4 t..\ o oo ("fa§) No
D~Z.Ct TW4·2 9o.'z15 Flow 15. 0 (188) No
Meter \Do I \1 b6 (Ve~ No
l)~z(;. TW4·11 q ~ f.L2. Flow lh .Ll (Yes~ No
Meter V·\b'Z-0 .OD ~)No
6755 TW4·21 67.60 Flow I L\, g !Y'e~\ No
Meter '15Z.b ~ ~ . I $< tl:e] No
D5_t7 TW4·37 1-.{,()'-i Flow I(,\ (Yes )No
Meter 3L3J '30. 60 nes·J No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
(_ " Depth is measured to the nearest 0.01 feet
(
( )
Time Well
I 411 MW-4
I 4CO MW-26
i32.0 TW4-19
l Y.3o TW4-20
\YI't TW4-4
1147 TWN-2
t 43g TW4-22
\4~1 TW4-24
15'-13 TW4-25
141 _') TW4-1
1140~ TW4-2
l40t.f TW4-11
1337 TW4-21
JY-34 TW4-37
Weekly Inspection Form
Depth*
~0 2.3
{;3 60
6__3_. J'1
64.lU
7 '-I J62...
.3 7. ~3
60.3(
{;3.6'2..
63.$5
92.59
~I .34
ql.'"tg
6 '\ \ l
(.;3 75
Name Go..r.-•...-P~l~, TA.AA..~.r l:{oH;J.c-..y
System Operational (If no note
Comments anv oroblems/corrective actions)
Flow Y.5 (res) No
Meter qzqG Ll .53 ffe§) No
Flow 8.5 ~es)No
Meter !;_57 t7. c>o (Y"~No
~
Flow I g L l{ f)'_esj_No
Meter ~ z s 6 2.. ~ • S'o 7""'Y"es~ No
Flow ~. z_ (Ves)No
Meter I ZD7D.t=..C>g ""?(e?)No
~
Flow I I , l /Yes) No
Meter l. <if '-4 7 3 3 . zo (Ves:JNo
Flow ~~ <;( (Ye~ No
Meter 5~7~0'-\. bO CfeS) No
Flow 17. l /Yes') No
Meter Z'tl b I 4. 2-D ('r'"e~No
Flow lb .£ (fa~ No
Meter 5S33't V1 /feS')No
Flow J 5.o (Yes2No
Meter II.\ h~.5 ~~t. 2.0 ?re~No
Flow 16,0 f(es))No
Meter I 037«.47. t I I'Y~No
Flow i6 .. {; f?e?) No
Meter ID15'57.so ?feB) No
Flow 17.0 _{1e~No
Meter z ~.-lg7 ~' '20 O'e~ No
=
Flow lh.4 ('YesjNo
Meter 3{;11 97.q3 7Yes )No -
Flow 1/.L{ ('1'es.)No
1M_eter .3 2.0 $C>'t I 0 (Yes-s No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
( * Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date -z lzzlto Name c;o...-1'\.A.. Pe I M?£ \ rt?:.rw.'-C \:tal (; .A~ .. r
System Operational (If no note
T" 1me Wll e D th* eo· c t ommen s an}£ ero bl sJ I . ) em correct ve actions
13c>5 MW-4 '7'-{, 2'1 Flow l..(,S ('Yes\ No
Meter t:t J5~tss 4u ffe§) No
1'2.57 MW-26 tf,),q<( Flow 7 .D rves) No
Meter 66'isz. ·'6 ZVe'£ No
rz.:z. z.. TW4-19 64.z:z... Flow 1<6~0 ~No
Meter 336Z..q L \o cYe"E No
IZ.SJ TW4-20 70.\l Flow !..\. z._ (Vei) No
Meter I 'Z.I7 s·o. 5'2-(reS\ No
13o8 TW4-4 7Z,g5 Flow l \.0 (Yei) No
Meter Z.S~50Z IO {Vij No
I Z3l. TWN-2 bD. OL/ Flow \ 'iL ~ rY~bNo
Meter sqoqc,t ID (Ye~ No
\2. '"\b TW4-22 ~l. s-q Flow I '?.L.J ({e~ No
Meter Z.'l~b~I.'D (!lW No
( ) ., Z.t.t J TW4-24 7G. -z..J Flow 11.'-i (Vel> No
Meter t:L/24 06 ~No
I Z.'-lb TW4-25 98 57 Flow ll\,'2,_ t{e-9::, No
Meter l~7e\bliZ 3o (?"eS'')No -
1~0/ TW4-1 qo,·z-z._ Flow \ {,,() (<(e$) No
Meter \ 0 SO II ,_6'6 ?reD No
n, ..,. TW4-2 ·~-~5.1~ Flow 16 .6 /Ye§) No a-.: .
Meter \ o '-'1SI1 56 ?fes~No
IZ..S'l TW4-11 'lt.'tl Flow l6 .0 ~\No
Meter ZS'tl 'l-06 ~No
\Z.3D TW4-21 57.145 Flow 16-8 (Ye§)No
Meter 36~3/2.. 97 0~No
I'Z.'"i'l TW4-37 7 '-1. z. ~ Flow i6.o t(e~ No
Meter >ZSD"2.t.4o m.s:> No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
l • Depth is measured to the nearest 0.01 feet. '-
~&s-.s
<"oJ
Monthly Depth Check Form
Date '2-l ·z Lt ( 1 6 Name Ga.r6.A-pg:.,lt:M;s:..r-, JA--."'-Lc t-lP!l;o{""Y
Time Well Depth* Time Well Depth*
133~ MW-4 72.11 1'-IU TWN-1 62.'-15
13\Cf TW4-1 g~l33 ~~~~ TWN-2 3o.oz..
l3'2.l TW4-2 ~5.DS Q~D,3 TWN-3 3~.so
133~ TW4-3 SG.99 1'-13~ TWN-4 55.2.5
135~ TW4-4 /3 .o~ 0{52-TWN-7 qs.3s
133'Z. TW4-5 b~.bS tY:!:ll TWN-18 bO 4.)
1340 TW4-6 71..3~ lj:37 MW-27 S'-1 . zs
1~5:1 TW4-7 71.DD 1'-lll MW-30 75.50
)33"1 TW4-8 ~ ~o.?g ~~~~ MW-31 c;s.so
t3?-,j TW4-9 67..55
)33Q TW4-10 62. \\.{
1::3}7 TW4-11 4l. oz.
\40.5 TW4-12 '-{~. ~s
i L.\O'Z.. TW4-13 S:Z,\D I~ DC... TW4-28 ~q_qD
1~00 TW4-14 SO. I~ \')5~ TW4-29 73.81
I :31b TW4-15 ~L.(.\g 1352. TW4-30 16-05
( ) 1~2"t TW4-16 '~ oo 1~&1 TW4-31 7'L 8""1
14\Z, TW4-17 ]I.~~ \40'1 TW4-32 S\,?:,lf
i I..\ 'Z."l TW4-18 GS.5£ 13Y1 TW4-33 72.C.O
J300 TW4-19 6:1..4,71 l3S] TW4-34 1 t.-KS
I '3l~ TW4-20 7o.oz. 13&~ TW4-35 14,'24
1:13:2 TW4-21 67-70 I~OI TW4-36 56.{,2-
\3l~ TW4-22 6fr.~l 1317 TW4-37 6t1.-z2..
13~~ TW4-23 69~~9
I "1.1. y TW4-24 7 s. -40 •
14~ TW4-25 6 3, 61.
1~'{2... TW4-26 bb 15
13'19 TW4-27 7~. caq
Comments: (Please note the well number for any comments)
~l.lk!:::r±~t-1-..1 V\.l +t'c..-\ ~ ..s t....VV'\.,P ll ffi,~ WA.S oloJ\. c.. e> "-+-k 23('"'-Z'1~.
I
* Depth is measured to the nearest 0.01 feet
Date -z/ Z'l ( 16
Time Well
llit:N MW-4
1 45'4 MW-26
152.7 TW4-19
I '-tS7 TW4-20
_\Y2.~ TW4-4
135E. TWN-2
l 4 '17 TW4-22
P-1 ~ l.. TW4-24
1552 TW4-25
14 z.~ TW4-1
\Eo7 TW4-2
\5D'1 TW4-11
1347 TW4-21
Weekly Inspection Form
Name cJa.r-v-i""-P~{~
Depth* Comments
System Operational (If no note
any problems/corrective actions)
72 .oz. Flow Y. S
" Meter q Y.Z.~.< 1 .u. ~No
7 1. 40 Flow I ,D ('(es , No
Meter 6 g 2..1:.6 • S"o Cfe"W No
\ 65 7 .S Flow I_~..!) C(:es\'1 No
Meter ~~S373 to (Yes No
63.60 Flow
Meter {Yes:>No ,
I
7 4 fs''ir Flow iLO
Meter C'Ve s? No
Meter St:r'167£1 bO ire?) No
5~. 5"o Flow 17.() /Y'"es~No
Meter
7Lt.~-Z.. Flow
Meter
7D.7S_ Flow 15,~0 _cYes) No
Meter
S~ .. l'Z.. Flow I &.6 ("1eS\ No
Meter I065q.,CJ.oL> ~No
7 '!,5o Flow
Meter lo4t..(3S" so ~No
ctl. Z.Z Flow I{.. ,() ;'fe~ No
Meter
?,7 ~3/, Flow IG.6 r)'es) No
Meter 3788 \\ c; 6 _(Ye~ No
~~~-~~Z-rTW __ 4~-3~7--~6~3~,~~5~~FI~ow~--~~7~,5~~--~-----~~~~s¥)~!N~o~----~1 Meter :3 36~ 3 7. ~o 7Ye'S) No
Operational Problems (Please list v ell number):
Corrective Action(s) Taken (Please list well number): ------------------
• Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Date J -7-lb Name C.c...rr-1 V'-~ lvv\..e..r-
System Operational (If no note
1me Wll e D th* ep1 c omments . anl£ eroblems/correcttve actions}
143'1 MW-4 &/.cS: Flow L{, ,c; (Yes) No
Meter q...,tt i'7'-~~ 3e, ~No
I L-i 'Z. 7 MW-26 (-:2.~31 Flow ti.C) {feS) No
Meter St:tso5;~ 7c ~No -
\~"17 TW4-19 t. &.1. g~ Flow l $/ "L (Ye_i} No
Meter 354Cl4.30 des1 No
l4 'l.S-TW4-20 b "3-66 Flow '/, z_ .~~No
Meter \'Z."{"'i5 \6 ~No -
~~~ TW4-4 '73.q{; Flow lLO Cf.JiS 1 No
Meter Zcr?Z-67-co ~No
I "-ll ·z._ TWN-2 Ztrr .c Y Flow I ~. 8' ~No
Meter sq~z.~s. Yo ~0
14'2..6 TW4-22 ~_s-l'l Flow ll ,l) If~ No
Meter 3c l. 4 z_z., 40 ~No
I '-l LS TW4-24 &; :! . \c Flow I 6, t.t (YeS'-No
Meter .. 25.'-iL q . 7.5 C_Y~No
I40S' TW4-25 63.ZS Flow I5.D (Ve~ No
Meter \ y c, ~ill_b., ~No
\"\3] TW4-1 g'f,7C Flow t.s·. b ~e§) No
Meter 167Cc3K So C:{W No
'4:;1 TW4-2 '7'1. 7D Flow l ,, g tfeS) No
Meter t()-60f7 .3o_ ~No -= I c...t t.tj TW4-11 Cfl.olf Flow \6 .c (Ye~ No
Meter ·'2-S77.<.SQ Cf_e.i:)No
r-1423 TW4-21 Gb. 6.) Flow '"I R
Cfj~-... No
Meter 38~Lt S9 .. ~S e.-?re~ No
~ \~04 TW4-37 6G . '1C. Flow \ 6. L{ (Yes} No
Meter 3\.f .530 I. SCJ (Te~ 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
c Date Name () ti..rri .A.... P(A { VVL.e...r-
System Operational Clf no note
1me Wll e D th ' ep1 c t ommen s anl£ ero bl I f . ) ems correc 1ve actions
d.tt MW-4 ~D .04 Flow y,s I )(8~ No
Meter qt6Y. /')_oct ?fe$) No
l?...D7 MW-26 63.'3o Flow ct.o ('{e~ No
Meter liD 5Z.oo .xes\ No
\6 2.& TW4-19 {LL6Y Flow 18.0 (le~ No
Meter 36, z.. 716 ~c;"o (Ves) No
llo:> TW4-20 64.66 Flow /,{_ ;<ie~ No
Meter 1 "'Z.51() b t3_ JYe~ No
I I
I 'Z-2..3 TW4-4 7$ 3'2._ Flow II. 0 ~e)' No
Meter 3D 15'Z.O 'Z.D 71e?-; No -
\050 TWN-2 z.q.ss Flow I g, n ~~No
Meter 60iq\7_ ~() ~ No
liS~ TW4-22 5<1 .oz. Flow \7.6 (Ye-s> No
Meter '3o4~'1~. '-lo _tfeSj No
( lD55 TW4-24 6 4. Z6 Flow i ~ .o l{es_') No
Meter ':?>1Zt56 40 ~)No
\0'-t~ TW4-25 63. gg Flow \5/') ~ No
Meter t5o'l.5D6. 86 (ref No -
I Z.l~ TW4-1 g4 ~() Flow lb .c ('Yes~No
Meter I 0 ~ L{'Zl,. z..o ]{e~ No
1713 TW4-2 '7'LIS" Flow f(.c) Q'e~ No
Meter I D 7-:{70 26 ~No
\1.\l TW4-11 qz.64 Flow 16.0 (Yes:::t>Jo
Meter z5qs7. to ~No
1 o'-\'2... TW4-21 _h7.~_ Flow _ L6_. '2-CfesJ No
Meter 3'17'-121. C,.s-(Ye:§) No
l'Z-06 TW4-37 6'2-C} 3 Flow lf-0 (')'~No
I Meter .35.36 5 I • $30 (res) No
Operational Problems (Please list well mJmt er):
Corrective Action(s) Taken (Please list well number): ---------------
I \ • Depth is measured to the nearest O.D1 feet.
Weekly Inspection Form
Date ;;./zd t6
Time Well Depth* Comments
()q~ MW-4 Flow 4,5
Meter lf6Z'100 13
D'1 Z~ MW-26 Flow CZS . 6
Meter 7 Z5Z. r ~ 60
Dl1SO TW4-19 £7,Y'iFlow 18.o
Meter 57130 '3 , 10
D'\i'i TW4-20 b 4 :z.tt Flow (., 0
Meter 1 'l.6Z..o ~ _ 4 3
0'136 TW4-4 (1.. >b Flow ll.o
Meter 3oS~ 1 ~.50_
-, L 35 Flow I 'L 4
Meter 605571 .60
()Cljl.{ TW4-22 5~.Cfn Flow i/.0
Meter 3D-'17f1-70
D'i il-TW4-24 b?.. -b 5_ Flow I b. 6
Meter ~S73L 61
0'165 TW4-25 0, 2 . 1 2.. Flow I y . L{
Meter 15 i 1 Y 'Z.Z. t...t 0
D£1s3 TW4-1 g3.ss-Flow I G.o
C>'1ZZ TW4-2
Meter 1 l:J gq So -I D
oG ZS TW4-11 Cf6.~~ Flow I 6.0
Meter 262:W .. 50
J;7. 85_ Flow 1b z
Meter Yl)68G\ ~S
62.8o Flow ll.z...
Meter 3C.I ll7~ 7n
Operation al Problems (Please list well number):
System Operational (If no note
any problems/corrective actions}
~No
(re$) No
_..,
6'es\ No
~No
eYeS:> No
I
_('f_es) No
~No
(fes') No
(feS) No
((e~ No
~'No
6'e~ No
(reS) No
~No
/(eS\ No
~No
~No
YeS) No
~e~No
?Ye~ No
~No
{(~No
i'f_es:J No
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
(
Weekly Inspection Form
Date Name
T" •me Wll e D th* ep1 c
131..\5 MW-4 ~Z.ll Flow
Meter
\337 MW-26 C.7. 3b Flow
~ Meter
I 100 TW4-19 6_ L.\. \ (:) Flow
Meter
l33'1../ TW4-20 ~3_. 35 Flow
Meter
\3.5"1 TW4-4 7 1-!. Z2.. Flow
Meter
\ 31..\ TWN-2 Z.'L7o Flow
Meter
l3_ZS TW4-22 5~. 'Z.O Flow
Meter
IZZ4 TW4-24 62 .Z8 Flow
Meter
l3ih TW4-25 6~.3'-1 Flow
Meter
\3t.!~ TW4-1 '15-~I Flow
Meter
1_3_42... TW4-2 gz.oo Flow
Meter
133C} TW4-11 't z. 4{) Flow
Meter
1"31't. TW4-21 61-0LI Flow
Meter
1331 TW4-37 61 .q7 Flow
Meter
Operational Problems (Please list well number):
t ommen s
4.5"
(/bCj7'a7 fl~
g·,b
74Z.C65. 10
17-6
380'2..\~. '-10
'{.(l
I Z.74 5~L'l3
l\.0
Jlo470.KO
I Cl, I
6o '1 ~51 L{o
17,g
.so go,;~. -zo
\ (;,, 8
9DS_I5. 'lS'
15.o
1.5"20461-( ~0
)6.0
II 'Z. '2. ~ I• DO
17,0
H6t..l~7, q_6
\6.4
"Z.6~i '2. .96
J6.1
I-\ '~3 19 . 'l. 4
17.u
37D5~ g YfJ
I
System Operational (If no note
anl£ ero bl sf f ti ) em correc 1ve ac ons
(?e~ No em No
CY_ej) No
f{eS) No
(es No
~No
(Yes) No
?Yes "')No
_6~ No
-res) No
L'Y'eS) No
(Ye~ No
;<fe~ No
?Yeil_ No
ClW No
(Ves) No
(Y'eS') No
(res) No
t{es)) No
(Ve5J No
-"' (Yes..) No
_LYe]) No
('(e"S) No
?r"e]) No
(Y'eS) No
(YeS) No
(Y~]) No
(Yes~ No
Corrective Action(s) Taken (Please list well number): ---------------
C.. • Depth is measured to the nearest 0.01 feet.
TabD
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary
TIME WELL
1350 MW-1
1553 MW-2
923 MW-3
923 MW-3A
1549 MW-5
1606 MW-11
1547 MW-12
1527 MW-14
1530 MW-15
928 MW-17
1347 MW-18
1342 MW-19
817 MW-20
812 MW-22
1545 MW-23
1556 MW-24
1525 MW-25
740 MW-26
715 MW-27
1557 MW-28
1603 MW-29
1600 MW-30
1610 MW-31
1408 MW-32
1537 MW-33
1534 MW-34
1543 MW-35
1541 MW-36
1532 MW-37
DEPTH
TO
WATER
(ft.)
64.00
109.50
82.16
84.16
105.77
85.65
108.00
112.65
105.72
71.55
71.70
61.46
85.81
66.31
113.78
112.75
76.51
64.38
53.85
74.95
100.42
74.97
68.05
77.00
DRY
107.59
112.11
110.30
108.64
NAME: Garrin Palmer, Tanner Holliday
3/30/2016
TIME
754
806
803
1511
808
1508
1516
1515
1513
1510
1507
759
1318
1316
1312
740
701
1408
733
822
806
734
810
710
808
736
1517
1302
1319
1310
1305
1304
1320
1301
1309
1307
1314
809
DEPTH
TO
WATER
WELL (ft.) TIME
MW-4 80.23 1339
TW4-1 91.03 1344
TW4-2 82.50 728
TW4-3 56.61 1522
TW4-4 73.11 1519
TW4-5 64.40 735
TW4-6 72.02 731
TW4-7 75.99 718
TW4-8 79.40 724
TW4-9 62.21
TW4-10 61.60 1356
TW4-11 92.18 1352
TW4-12 45.70
TW4-13 51.55
TW4-14 79.65
TW4-15 64.38
TW4-16 63.10
TW4-17 77.00
TW4-18 65.23 1336
TW4-19 65.01
TW4-20 63.66 1334
TW4-21 67.54
TW4-22 58.72 721
TW4-23 69.08 936
TW4-24 64.14
TW4-25 65.49
TW4-26 66.53
TW4-27 79.35
TW4-28 39.75
TW4-29 73.50
TW4-30 75.55
TW4-31 79.26
TW4-32 50.99
TW4-33 72.40
TW4-34 71.54
TW4-35 73.86
TW4-36 56.06
TW4-37 62.05
DEPTH
TO
WATER
WELL (ft.)
PIEZ-1 64.89
PIEZ-2 38.97
PIEZ-3 48.57
PIEZ-4 58.45
PIEZ-5 58.00
TWN-1 62.20
TWN-2 32.44
TWN-3 39.21
TWN-4 54.97
TWN-5 Abandoned
TWN-6 78.02
TWN-7 85.07
TWN-8 Abandoned
TWN-9 Abandoned
TWN-10 Abandoned
TWN-11 Abandoned
TWN-12 Abandoned
TWN-13 Abandoned
TWN-14 60.83
TWN-15 Abandoned
TWN-16 47.45
TWN-17 Abandoned
TWN-18 60.07
TWN-19 52.95
DEPTH
TO
WATER
TIME WELL (ft.)
NA DR-1 Abandoned
NA DR-2 Abandoned
823 DR-5 82.81
826 DR-6 94.11
1539 DR-7 91.94
835 DR-8 51.16
832 DR-9 86.22
830 DR-10 77.96
916 DR-ll 97.95
918 DR-12 90.95
926 DR-13 69.55
845 DR-14 76.00
840 DR-15 92.56
NA DR-16 Abandoned
848 DR-17 64.55
NA DR-18 Abandoned
851 DR-19 62.92
904 DR-20 55.1l
909 DR-21 100.74
855 DR-22 60.58
907 DR-23 70.22
858 DR-24 44.00
NA DR-25 Abandoned
@ estimated dry area
M.W-5 perched monitoring well showing
5503 elevation in feet amsl
TW4-12 . o5579 temporary perched monitonng well
showing elevation in feet amsl
TWN-7 hed . . . <>5564 temporary perc mtrate momtonng
well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5591 elevation in feet amsl
RUIN SPRING
b 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11 ,TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells; TW4·22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM,INC.
KRIGED 1st QUARTER, 2016 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/may16/WUUwl0316.srf D-1
estimated nitrate capture zone
boundary stream tubes resulting from
pumping. (note: combined capture for
TW4-22, and TW4-24 is shown)
estimated chloroform capture
zone boundary stream tubes
resulting from pumping
@ estimated dry area
MW-5 perched monitoring well showing e 5503 elevation in feet amsl
TW4-12 . . II 0 5579 temporary perc.he~ momtonng we
show1ng elevation 1n feet amsl
TWN-7 d . . . A 5564 temporary perche mtrate momtonng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5591 elevation in feet amsl
RUIN SPRING b 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11 ,TW4-19, TW4-20, TW4·21 and TW4-37 are chloroform pumping wells; TW4·22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM,INC.
KRIGED 1st QUARTER, 2016 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/may16/WUUwl0316ntcz2.srf I D-2
, estimated chloroform capture zone ,~;'~' ,• boundary stream tubes resulting from
',' , ,' ,' pumping. (note: combined capture for I 1 I 1 I !"'W-4,TW4-1 ,TW4-2, and TW4-11
I 1sshown)
MW-25
• 5537
TW4-7
0 5545
PIEZ-2
~ 5590
estimated nitrate capture
zone boundary stream tubes
resulting from pumping
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well
showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11 , TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells; TW4-11 water level is below the base of the Burro Canyon Formation
HYDRO
GEO
CHEM,INC.
KRIGED 1st QUARTER, 2016 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
TabE
Kriged Previous Quarter Groundwater Contour Map
@ estimated dry area
TW4-37 perched pumping well installed
......_5568 ~arch, 2015 showing elevation
T 1n feet amsl
MW-5 perched monitoring well showing e 5503 elevation in feet amsl
TW4-12 temporary perched monitoring well
0 5579 showing elevation in feet amsl
TWN-7 temporary perched nitrate monitoring ~ 5564 well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5591 elevation in feet amsl
TW4-35 temporary perched monitoring well
~5526 install~ ~ay, 2014 showing
elevation 1n feet amsl
RUIN SPRING b 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11,TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells; TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
TW4-11 wn.tet level Is below the base of the BurTo Canyon Formation
HYDRO
GEO
CHEM,INC.
KRIGED 4th QUARTER, 2015 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H :/718000/feb16/WUUwl1215.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 09/25179 94.70 93.14
5,527.63 10110179 94.70 93.14
5,528.43 01110/80 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 12/01184 94.00 92.44
5,528.13 02/01185 94.20 92.64
5,528.33 06/01185 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 11/01185 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 08114/87 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 06/21189 93.23 91.67
5,529.06 09/01189 93.27 91.71
5,529.21 11115/89 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
5.5~ 1.62 08118/94 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 12111195 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 05/11199 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 01103/00 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 05111100 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 06109100 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 08/31100 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 10112/00 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 11109/00 65.19 63.63
5,557.17 11114/00 65.16 63.60
5,556.95 11121100 65.38 63.82
5,557.08 11130/00 65.25 63.69
5,557.55 12/07/00 64.78 63.22
5,557.66 01114/01 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 05/31101 64.02 62.46
5,558.49 06/22/01 63.84 62.28
5,558.66 07110/01 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 11108/01 63.06 61.50
5,559.77 12/03/01 62.56 61.00
5,559.78 01103/02 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 09/11102 61.62 60.06
5,560.89 10/23/02 61.44 59.88
5,557.86 11122/02 64.47 62.91
5,561.10 12/03/02 61.23 59.67
5,561.39 01109/03 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 05/01103 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 09111103 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 01115/04 64.75 63.19
5,558.80 02110/04 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 09116/04 85.78 84.22
5,529.00 10/11104 93.33 91.77
5,541.55 11116/04 80.78 79.22
5,541.12 12/22/04 81.21 79.65
5,540.59 01118/05 81.74 80.18
5,542.85 02/28/05 79.48 77.92
5,537.91 03115/05 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 07129/05 77.17 75.61
5,544.67 09112/05 77.66 76.10
5,541.28 09127/05 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 11117/06 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 08113/07 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 12/11109 71.39 69.83
5,546.08 03/11110 76.25 74.69
5,550.98 05111/10 71.35 69.79
5,548.33 09/29110 74.00 72.44
5,551.01 12/21/10 71.32 69.76
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,547.00 02/28/11 75.33 73.77
5,557.54 06/21/11 64.79 63.23
5,551.14 09/20/11 71.19 69.63
5,550.32 12/21/11 72.01 70.45
5,551.22 03/27/12 71.11 69.55
5,551.29 06/28/12 71.04 69.48
5,550.29 09/27/12 72.04 70.48
5,549.31 12/28/12 73.02 71.46
5,552.30 03/28/13 70.03 68.47
5,550.18 06/27/13 72.15 70.59
5,552.55 09/27/13 69.78 68.22
5,553.23 12/20/13 69.10 67.54
5,551.91 03/27/14 70.42 68.86
5,552.93 06/25/14 69.40 67.84
5,552.23 09/25/14 70.10 68.54
5,552.08 12/17/14 70.25 68.69
5,551.13 03/26/15 71.20 69.64
5,556.02 06/22/15 66.31 64.75
5,543.38 09/30/15 78.95 77.39
5,551.13 12/02/15 71.20 69.64
5,542.10 03/30/16 80.23 78.67
......
N 0
......
0 0
Depth Below Measuring Point (ft.)
00 0 0\ 0 ~ N 0 0
09/25/79
-02/06/81
06/21182
11103/83
03117/85
07/30/86
12112/87
04/25/89
-09/07/90 ~
01120/92 ~ ... 06/03/93 ~ -10/16/94 ""'" ~ ""1
02/28/96 ~ ~
07/12/97 ~ ~
11124/98 0 -<
04/07/00 ~ ""1
~
08/20/01 ..... !3 ~
01102/03 ,.-_
?
05/16/04 r:r -09/28/05 !3 ~ ._
02110/07
06/24/08
11106/09
03/21111
08/02/12
12/15113
04/29/15
09110116
01/23118
06/07/19
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 1.02 111.04
5,537.23 11108/99 81.35 80.33
5,537.38 11109/99 81.20 80.18
5,537.48 01102/00 81.10 80.08
5,537.48 01110/00 81.10 80.08
5,537.23 01117/00 81.35 80.33
5,537.28 01124/00 81.30 80.28
5,537.28 02/01100 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 03/01100 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 05101100 81.00 79.98
5,537.88 05111100 80.70 79.68
5,537.58 05/15/00 81.00 79.98
5,537.88 05/25100 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 08/31100 80.25 79.23
5,539.18 09/01100 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 1.02 111.04
5,544.96 03/29/01 73.62 72.60
5,545.45 04/30/01 73.13 72.11
5,545.89 05/31101 72.69 71.67
5,546.19 06/21101 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 11108/01 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 11122/02 66.31 65.29
5,552.48 12/03/02 66.10 65.08
5,552.74 01109/03 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 05/01103 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 09111103 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 01115/04 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 5618.58 1.02 111.04
5,552.53 10111104 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 03115/05 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 07118/06 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 10110/07 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 03110/09 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 12111109 61.8 60.78
5,556.75 03/11/10 61.83 60.81
5,556.19 05/11110 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 06/21111 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 03/27112 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 12/28112 64.99 63.97
5,554.73 03/28/13 63.85 62.83
5,554.44 06/27113 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 1.02 111.04
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 09/25114 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
1.0 VI 1.0 0 00 VI
Depth Below Measuring Point (ft.)
00 0 --.l VI --.l 0 0\ VI VI VI ~ VI 0
11/08/99
04/06/00
09/03/00
01/31101
06/30/01
11/27/01
04/26/02
.. 09/23/02
• 02/20/03
07/20/03
12/17/03
05/15/04 1-3 .. 10/12/04 ~ 03/11105 ,.
I
,_ 08/08/05 ~
-01/05/06 ~
06/04/06 1""1' ~
11101106
..,
~ 03/31/07 ~ ~
08/28/07 1""1' =-~ 01/25/08 0
-06/23/08 ~ ~
11/20/08
..,
1-3 -04/19/09 .... a 09/16/09 ~ ,.-._
-02/13110 ?
07/13110 0"
12110/10 a
05/09/11 ~ ._
10/06/11
03/04112
08/01112
12/29/12
05/28/13
10/25/13
03/24/14
08/21/14
01/18115
06/17/15
,_ 11114/15
04/12/16
09/09/16
02/06/17
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 1.62 121.125
5,548.57 11108/99 76.15 74.53
5,548.57 11/09/99 76.15 74.53
5,548.32 01102/00 76.40 74.78
5,548.52 01110/00 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 03/01100 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 05101100 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 06116100 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 07113/00 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 08/31100 74.18 72.56
5,550.87 09/08/00 73.85 72.23
5,550.97 09113/00 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 01126/01 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 1.62 121.125
5,551.59 04/30/01 73.13 71.51
5,552.03 05/31101 72.69 71.07
5,552.33 06/21101 72.39 70.77
5,552.64 07110/01 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 11108/01 70.58 68.96
5,554.79 12/03/01 69.93 68.31
5,554.74 01103/02 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 09111102 68.47 66.85
5,556.72 10/23/02 68.00 66.38
5,556.42 11122/02 68.30 66.68
5,557.01 12/03/02 67.71 66.09
5,557.20 01109/03 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 05/01103 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 11107/03 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 04112/04 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 10/11104 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 1.62 121.125
5,549.89 11116/04 74.83 73.21
5,550.37 12/22/04 74.35 72.73
5,549.95 01118/05 74.77 73.15
5,550.09 02/28/05 74.63 73.01
5,550.13 03/15/05 74.59 72.97
5,550.18 04/26/05 74.54 72.92
5,550.32 05/24/05 74.40 72.78
5,550.21 06/30/05 74.51 72.89
5,550.11 07/29/05 74.61 72.99
5,550.33 09/12/05 74.39 72.77
5,550.29 12/07/05 74.43 72.81
5,551.30 03/08/06 73.42 71.80
5,551.42 06/14/06 73.3 71.68
5,550.52 07/18/06 74.20 72.58
5550.52 11107/06 74.20 72.58
5552.89 02/27/07 71.83 70.21
5,552.06 05/02/07 72.66 71.04
5,552.02 08/14/07 72.7 71.08
5,552.20 10/10/07 72.52 70.90
5,554.58 03/26/08 70.14 68.52
5,555.23 06/24/08 69.49 67.87
5,555.29 08/26/08 69.43 67.81
5,555.43 10/14/08 69.29 67.67
5,555.73 03/10/09 68.99 67.37
5,556.25 06/24/09 68.47 66.85
5,555.94 09/10/09 68.78 67.16
5,556.53 12/11/09 68.19 66.57
5,557.87 03/11110 66.85 65.23
5,557.63 05/11110 67.09 65.47
5,557.24 09/29/10 67.48 65.86
5,557.00 12/21110 67.72 66.10
5,557.61 02/28/11 67.11 65.49
5,557.58 06/21111 67.14 65.52
5,557.46 09/20/11 67.26 65.64
5,557.84 12/21111 66.88 65.26
5,557.86 03/27/12 66.86 65.24
5,557.87 06/28112 66.85 65.23
5,557.46 09/27/12 67.26 65.64
5,557.82 12/28/12 66.9 65.28
5,559.39 03/28/13 65.33 63.71
5,559.21 06/27/13 65.51 63.89
5,559.26 09/27/13 65.46 63.84
5,559.27 12/20/13 65.45 63.83
Water Levels and Data over Time
White Mesa Mill-Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 121.125
5,558.92 03/27/14 65.8 64.18
5,557.99 06/25/14 66.73 65.11
5,557.09 09/25/14 67.63 66.01
5,557.07 12117/14 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
\0 0 00 VI 00 0
Depth Below Measuring Point (ft.)
-...1 VI -...1 0 0\ VI 0\ 0 VI VI VI 0
11108/99
04/06/00
09/03/00
,_ 01131101
06/30/01
11127/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05115/04 ~ 10/12/04 ~ 03/11/05 ~ I
08/08/05 N
01/05/06 ~
06/04/06 -~
11/01106 ~
~ 03/31/07 ~ I'C
08/28/07 -=-01/25/08 0
,_ 06/23/08 ~ ~
11/20/08 ~
~ 04119/09 .... e 09/16/09 ~ --02/13/10 ?
07/13/10 0"' -12/10/10 e
05/09/11 I'C --10/06/11
03/04112
08/01/12
12/29112
05/28113
10/25/13
03/24/14
08/21/14
01118115
06/17/15
11/14/15
04/12/16
09/09116
02/06/17
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 1.02 141
5,565.78 11/29/99 66.45 65.43
5,566.93 01/02/00 65.30 64.28
5,567.03 01110/00 65.20 64.18
5,566.83 01117/00 65.40 64.38
5,567.13 01124/00 65.10 64.08
5,567.33 02/01100 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 03/01100 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 04/21100 64.20 63.18
5,568.23 04/28/00 64.00 62.98
5,568.13 05/01100 64.10 63.08
5,568.53 05111100 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 06109/00 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 08116/00 63.47 62.45
5,568.95 08/31100 63.28 62.26
5,568.49 09/08/00 63.74 62.72
5,568.67 09/13/00 63.56 62.54
5,568.96 09/20/00 63.27 62.25
5,568.93 10/05/00 63.3 62.28
5,569.34 11109/00 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 1.02 141
5,570.61 04/30/01 61.62 60.60
5,570.70 05/31101 61.53 60.51
5,570.88 06/21101 61.35 60.33
5,571.02 07110/01 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 01103/02 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 11122/02 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 05/01103 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 09/11103 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 10111104 52.11 51.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 l.02 141
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 03115105 51.66 50.64
5,580.86 04/26/05 51.37 50.35
5,581.20 05/24/05 51.03 50.01
5,581.51 06/30/05 50.72 49.70
5,581.55 07/29/05 50.68 49.66
5,581.68 09/12/05 50.55 49.53
5,581.83 12/07/05 50.4 49.38
5,564.92 03/08/06 67.31 66.29
5,582.73 06/13/06 49.50 48.48
5,582.33 07/18/06 49.90 48.88
5,582.75 11/07/06 49.48 48.46
5583.35 02/27/07 48.88 47.86
5,559.57 05/02/07 72.66 71.64
5,583.29 08/14/07 48.94 47.92
5,583.49 10/10/07 48.74 47.72
5,584.95 03/26/08 47.28 46.26
5,584.59 06/24/08 47.64 46.62
5,584.55 08/26/08 47.68 46.66
5,584.03 10/14/08 48.2 47.18
5,583.64 03/03/09 48.59 47.57
5,587.34 06/24/09 44.89 43.87
5,582.90 09/10/09 49.33 48.31
5,583.27 12/11/09 48.96 47.94
5,583.63 03111/10 48.6 47.58
5,583.82 05/11110 48.41 47.39
5,583.51 09/29/10 48.72 47.70
5,582.86 12/21110 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.M P) (blw.LSD) Total Depth Of Well
5 631.21 5,632.23 1.02 141
5,579.62 03/27114 52.61 51 .59
5,578.52 06/25/14 53.71 52.69
5,577.59 09/25114 54.64 53.62
5,577.40 12117114 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
-....1 Vl -....1 0
Depth Below Measuring Point (ft.)
0\ Vl ~ Vl
Vl
Vl 0 """' Vl """' 0
11/29/99
04/27/00
09/24/00
02/21101
07/21/01
12/18/01
-05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04 t-3 -11/02/04 ~ 04/01/05 ... I
08/29/05 (.N
01/26/06 ~ 06/25/06 -~
11/22/06 ~
~ 04/21107 ~ "C 09/18/07 ~
02/15/08 0
07/14/08 ~ ~
12/11/08 ~
t-3 05110109 ... a 10/07/09 ~
03/06/10 ..-.. ~
08/03/10 C" -~ 12/31/10 a
05/30/11 "C '-'
10/27/11
03/25/12
-08/22/12
01/19/13
06/18113
11/15/13
04114114
09/11/14
02/08115
07/08/15
12/05/15
05/03/16
09/30/16
02/27117
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 5,613.4 5 1.184 114.5
5,512.145 05/25/00 101.34 100.16
5,518.985 06/09/00 94.50 93.32
5,512.145 06/16/00 101.34 100.16
5,517.465 06/26/00 96.02 94.84
5,520.145 07/06/00 93.34 92.16
5,521.435 07/13/00 92.05 90.87
5,522.005 07/18/00 91.48 90.30
5,522.945 07/27/00 90.54 89.36
5,523.485 08/02/00 90.00 88.82
5,523.845 08/09/00 89.64 88.46
5,523.885 08/15/00 89.60 88.42
5,524.555 09/01/00 88.93 87.75
5,513.235 09/08/00 100.25 99.07
5,516.665 09/13/00 96.82 95.64
5,519.085 09/20/00 94.40 93.22
5,522.165 10/05/00 91.32 90.14
5,524.665 11/09/00 88.82 87.64
5,518.545 12/06/00 94.94 93.76
5,527.695 01/03/01 85.79 84.61
5,529.085 02/09/01 84.40 83.22
5,529.535 03/27/01 83.95 82.77
5,530.235 04/30/01 83.25 82.07
5,530.265 05/31101 83.22 82.04
5,534.405 06/22/01 79.08 77.90
5,533.145 07/10/01 80.34 79.16
5,534.035 08/20/01 79.45 78.27
5,534.465 09/19/01 79.02 77.84
5,533.285 10/02/01 80.20 79.02
5,533.865 11108/01 79.62 78.44
5,534.275 12/03/01 79.21 78.03
5,534.715 01/03/02 78.77 77.59
5,535.435 02/06/02 78.05 76.87
5,536.445 03/26/02 77.04 75.86
5,536.405 04/09/02 77.08 75.90
5,537.335 05/23/02 76.15 74.97
5,537.325 06/05/02 76.16 74.98
5,537.975 07/08/02 75.51 74.33
5,538.825 08/23/02 74.66 73.48
5,539.275 09/11102 74.21 73.03
5,539.765 10/23/02 73.72 72.54
5,540.205 11122/02 73.28 72.10
5,540.295 12/03/02 73.19 72.01
5,540.795 01/09/03 72.69 71.51
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5 612.301 5,613.485 1.184 114.5
5,540.985 02/12/03 72.50 71.32
5,541.675 03/26/03 71.81 70.63
5,541.765 04/02/03 71.72 70.54
5,541.885 05/01103 71.60 70.42
5,542.025 06/09/03 71.46 70.28
5,541.925 07/07/03 71.56 70.38
5,541.885 08/04/03 71.60 70.42
5,541.825 09/11103 71.66 70.48
5,541.885 10/02/03 71.60 70.42
5,541.995 11107/03 71.49 70.31
5,542.005 12/03/03 71.48 70.30
5,542.555 01/15/04 70.93 69.75
5,542.705 02/10/04 70.78 69.60
5,543.225 03/28/04 70.26 69.08
5,543.555 04/12/04 69.93 68.75
5,543.865 05113/04 69.62 68.44
5,543.915 06/18/04 69.57 68.39
5,544.655 07/28/04 68.83 67.65
5,544.795 08/30/04 68.69 67.51
5,544.845 09/16/04 68.64 67.46
5,544.705 10111104 68.78 67.60
5,544.525 11116/04 68.96 67.78
5,544.625 12/22/04 68.86 67.68
5,544.305 01118/05 69.18 68.00
5,544.585 02/28/05 68.90 67.72
5,544.685 03115/05 68.80 67.62
5,544.675 04/26/05 68.81 67.63
5,544.785 05/24/05 68.70 67.52
5,544.795 06/30/05 68.69 67.51
5,544.775 07/29/05 68.71 67.53
5,545.005 09/12/05 68.48 67.30
5,545.225 12/07/05 68.26 67.08
5,545.735 03/08/06 67.75 66.57
5,545.785 06/14/06 67.70 66.52
5,545.855 07/18/06 67.63 66.45
5,545.805 11107/06 67.68 66.50
5546.675 02/27/07 66.81 65.63
5,546.535 05/02/07 66.95 65.77
5,547.155 08/15/07 66.33 65.15
5,547.215 10/10/07 66.27 65.09
5,548.305 03/26/08 65.18 64.00
5,548.865 06/24/08 64.62 63.44
5,549.235 08/26/08 64.25 63.07
Water Levels and Data over Time
White Mesa Mill -Well TW 4-4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,612.301 5,613.485 1.184 ll4.5
5,549.305 10/14/08 64.18 63.00
5,549.725 03/03/09 63.76 62.58
5,549.905 06/24/09 63.58 62.40
5,549.695 09/10/09 63.79 62.61
5,549.865 12/11109 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 12/21110 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 12117/14 69.80 68.62
5,541.49 03/26/15 72.00 70.82
5,539.67 06/22115 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 03/30116 73.11 71.93
..... -0
.....
0 0
-
Depth Below Measuring Point (ft.)
~
\0 0 00 0 -...l 0 ~ Vl 0
.
05/25/00
09/02/00
12/11100
03/21101
06/29/01
10/07/01
01115/02
04/25/02
08/03/02
11111102
02/19/03
05/30/03
09/07/03
12/16/03
03/25/04
07/03/04
10/11/04 1-3 01/19/05 ~ 04/29/05
08/07/05 ~
I
11115/05 ~
02/23/06 ~ 06/03/06
09/11106 ;-
12/20/06 ~
03/30/07 ~
07/08/07 ~ ~ 10/16/07 -01/24/08 =-05/03/08 0
08/11108 <O!!l
11/19/08 ~ ~ 02/27/09 1-3 06/07/09 ....
09/15/09 a
12/24/09 ~ ,-... 04/03/10 ~ 07112110
10/20/10 0" -01/28111 a 05/08/11 ~ 08/16/11 '-'
11/24111
03/03/12
06/11112
09/19/12
12/28/12
04/07/13
07/16113
10/24/13
02/01/14
05/12114
08/20/14
11/28/14
03/08/15
06/16115
09/24115
01/02116
04/11/16
07120/16
10/28/16
02/05/17
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 1.95 121.75
5,579.30 01102/00 61.40 59.45
5,579.60 01110/00 61.10 59.15
5,579.35 01117/00 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 03/01100 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 04/21100 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 05111100 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 11109/00 59.04 57.09
5,581.63 12/06/00 59.07 57.12
5,581.92 01103/01 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 05/31101 57.98 56.03
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 1.95 121.75
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
5,583.28 09/19/01 57.42 55.47
5,583.36 10/02/01 57.34 55.39
5,583.49 11108/01 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 09/11102 55.68 53.73
5,585.20 10/23/02 55.50 53.55
5,585.15 11122/02 55.55 53.60
5,585.42 12/03/02 55.28 53.33
5,585.65 01109/03 55.05 53.10
5,585.65 02112/03 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 05/01103 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 09/11103 56.82 54.87
5,583.57 10/02/03 57.13 55.18
5,583.39 11107/03 57.31 55.36
5,583.97 12/03/03 56.73 54.78
5,585.28 01115/04 55.42 53.47
5,585.50 02110/04 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 06118/04 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 10/11104 55.53 53.58
5,584.64 11116/04 56.06 54.11
5,584.77 12/22/04 55.93 53.98
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 1.95 121.75
5,584.65 01118/05 56.05 54.10
5,584.98 02/28/05 55.72 53.77
5,585.15 03115/05 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
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 02127/07 54.89 52.94
5,585.20 05/02/07 55.50 53.55
5,586.66 08/14/07 54.04 52.09
5,586.80 10/10/07 53.90 51.95
5,588.48 03/26/08 52.22 50.27
5,586.51 06/24/08 54.19 52.24
5,586.45 08/26/08 54.25 52.30
5,585.40 10/14/08 55.3 53.35
5,584.80 03/03/09 55.9 53.95
5,584.73 06/24/09 55.97 54.02
5,584.36 09/10/09 56.34 54.39
5,585.02 12111/09 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 12/21110 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 09/20111 56.08 54.13
5,585.04 11/21111 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 12/28112 56.81 54.86
5,582.88 03/28113 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 12/20113 60.18 58.23
5,579.44 03/27114 61.26 59.31
5,578.11 06/25114 62.59 60.64
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 1.95 121.75
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
0\ 0\ ~ 0\ N
Depth Below Measuring Point (ft.)
0\ 0 Vl 00 Vl 0\ Vl ~ Vl N Vl 0
1-----1---+---6.~--+---+----1----+---+----+ 01102/00
04/11/00
07/20/00
10/28/00
02/05/01
05/16/01
08/24/01
12/02/01
03112/02
-06/20/02
09/28/02
01106/03
04/16/03
07/25/03
11/02/03
02/10/04
05/20/04
08/28/04
12/06/04
03/16/05
06/24/05
10/02/05
01110/06
04/20/06
07/29/06
11/06/06
02/14/07
05/25/07
09/02/07
~ 12/11107
03/20/08
06/28/08
10/06/08
01114/09
04/24/09
-08/02/09
11110/09
-02/18/10
05/29/10
09/06/10
-12/15110
03/25111
07/03/11
10/11111
01/19/12
-04/28/12
08/06/12
11114/12
02/22/13
06/02/13
09/10/13
12/19/13
03/29/14
07/07114
10115/14
01/23/15
05/03/15
08/11115
11119/15
02/27116
06/06/16
09/14/16
12/23116
L----1----"----'------1...----'-------L...--..J----..1. 04/02/17
~ ~
I Ul
~ ;'
"1
0 ('I)
"= ;.
0 < ('I)
"1
;.3 ....
!3 ('I) ---~
r:::1" 9 "= _..
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 98.55
5,522.28 05/25/00 86.50 85.05
5,521.51 06/09/00 87.27 85.82
5,522.35 06/16/00 86.43 84.98
5,522.14 06/26/00 86.64 85.19
5,522.25 07/06/00 86.53 85.08
5,522.13 07113/00 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 11109/00 86.36 84.91
5,522.29 12/06/00 86.49 85 .04
5,522.63 01103/01 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 05/31101 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 11108/01 85.53 84.08
5,523.46 12/03/01 85.32 83.87
5,523.36 01103/02 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 09/11102 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 01109/03 83.68 82.23
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 (b lw.MP) (blw.LSD) (blw.LSD)
5 607.33 5,608.78 1.450 98.55
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
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 09111103 82.36 80.91
5,526.30 10/02/03 82.48 81.03
5,526.41 11107/03 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 04112/04 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 09116/04 80.26 78.81
5,528.71 10/11104 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
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 98.55
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 09110/09 71.95 70.50
5,537.35 12/11/09 71.43 69.98
5,537.93 03111110 70.85 69.40
5,538.14 05/11/10 70.64 69.19
5,538.03 09/29/10 70.75 69.30
5,538.04 12121110 70.74 69.29
5,537.98 02/28111 70.8 69.35
5,538.46 06/21111 70.32 68.87
5,538.37 09/20111 70.41 68.96
5,538.87 12/21111 69.91 68.46
5,538.73 03/27112 70.05 68.60
5,538.80 06/28112 69.98 68.53
5,539.04 09127/12 69.74 68.29
5,538.74 12/28112 70.04 68.59
5,539.53 03/28/13 69.25 67.80
5,539.46 06/27113 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 03/27114 69.13 67.68
5,538.85 06/25/14 69.93 68.48
5,538.69 09/25114 70.09 68.64
5,538.71 12117114 70.07 68.62
5,538.03 03/26/15 70.75 69.30
5,537.78 06/22115 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 03/30116 72.02 70.57
\0 0 00 (Jl 00 0
Depth Below Measuring Point (ft.)
-....l (Jl -....l 0 0\ (Jl g (Jl
(Jl
(Jl
0
05/25/00
09/02/00
12111100
03/21101
06/29/01
10/07/01
01115/02
04/25/02
08/03/02
11111/02
02119/03
05/30/03
09/07/03
12116/03
03/25/04
07/03/04
10/11104 1-3 01119/05
04/29/05 ~
08/07/05 ~ I 11/15/05 0\
02/23/06 ~ 06/03/06
09/11106 '"""' ~ 12/20/06 "1
03/30/07 ~ 07/08/07 ~
10/16/07 "'C
01124/08 ~
05/03/08 0 08111108 -< 11/19/08 ~ "1 02/27/09 1-3 06/07/09 .....
09/15/09 a
12/24/09 ~
04/03/10 ---07/12/10 ?
10/20/10 0"
01128/11 §"
05/08/11 "'C 08116/11 '-"
11124/11
03/03/12
06111112
09/19112
12/28/12
04/07/13
07/16/13
10/24/13
02/01114
05/12/14
08/20/14
11128/14
03/08/15
06/16/15
09/24/15
01102/16
04/11116
07/20/16
10/28/16
02/05/17
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
5,552.37 11/29/99 68.70 67.50
5,553.57 01102/00 67.50 66.30
5,553.87 01/10/00 67.20 66.00
5,553.72 01117/00 67.35 66.15
5,553.97 01/24/00 67.10 65.90
5,553.87 02/01100 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 03/01100 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 04i04/00 66.80 65.60
5,554.57 04/13/00 66.50 65.30
5,554.77 04/21100 66.30 65.10
5,554.87 04/28/00 66.20 65.00
5,554.87 05101100 66.20 65.00
5,555.27 05/11100 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 08/31100 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 10112/00 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 11114/00 64.65 63.45
5,556.45 11130/00 64.62 63.42
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
5,556.15 12/06/00 64.92 63.72
5,556.89 01114/01 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 05/31101 63.30 62.10
5,557.84 06/21101 63.23 62.03
5,557.98 07110/01 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 11108/01 62.45 61.25
5,559.03 12/03/01 62.04 60.84
5,559.08 01103/02 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 09/11102 60.84 59.64
5,560.43 10/23/02 60.64 59.44
5,560.39 11122/02 60.68 59.48
5,560.61 12/03/02 60.46 59.26
5,560.89 01109/03 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 05/01103 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 09/11103 79.16 77.96
5,544.62 10/02/03 76.45 75.25
5,542.67 11107/03 78.40 77.20
5,549.96 12/03/03 71.11 69.91
5,557.17 01115/04 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
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
5,561.64 07/28/04 59.43 58.23
5,543.00 08/30/04 78.07 76.87
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 11107/06 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 12/11109 68.01 66.81
5,554.64 03/11110 66.43 65.23
5,554.20 05111/10 66.87 65.67
5,553.45 09/29/10 67.62 66.42
5,553.40 12/21110 67.67 66.47
5,553.93 02/28/11 67.14 65.94
5,553.67 06/21111 67.4 66.20
5,553.46 09/20/11 67.61 66.41
5,553.78 12/21111 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 09/27112 68.17 66.97
5,553.15 12/28112 67.92 66.72
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
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
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 03/26115 72.50 71.30
5,555.88 06/22/15 65.19 63.99
5,546.22 09/30115 74.85 73.65
5,539.47 12/02/15 81.60 80.40
5,545.08 03/30/16 75.99 74.79
00 VI 00 0
Depth Below Measuring Point (ft.)
-.I VI -.I 0 0\ VI 0\ 0 VI VI VI 0
r----t-----+----1-.~-+-----t------t---+ 11129/99
03/08/00
06/16/00
09/24/00
01102/01
04/12/01
07/21101
10/29/01
,_ 02/06/02
05117/02
08/25/02
12/03/02
03/13/03
06/21103
09/29/03
01107/04
04116/04
07/25/04
11102/04
02/10/05
05/21/05
08/29/05
12/07/05
03/17/06
06/25/06
10/03/06
01111/07
04/21/07
07/30/07
11107/07
02/15/08
-05/25/08
09/02/08
12/11/08
03/21/09
06/29/09
10/07/09
01115110
04/25/10
,_ 08/03110
11111110
02/19111
05/30111
09/07111
12/16111
03/25112
07/03/12
10/11112
01/19113
04/29113
08/07113
11115113
02/23114
-06/03/14
09/11/14
12/20/14
03/30115
07/08115
10116115
~ 01/24116
05/03/16
08/11116
11119/16
.___ __ _,__ __ ____.._ ___ .__ __ _.__ __ ____.._ __ ----J~---L 02/27117
~ ~ I "' ~ -~ "'1
~ ~ ~ ~
0 ~ "'1
~ ..... ~ -~
C" §"
~ ._,
Water Levels and Data over Time
White Mesa Mill -Well TW 4-8
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) (bhv.LSD Well
5,616.80 5,621.40 4.60 126.00
5,546.40 11129/99 75.00 70.40
5,546.20 01/02/00 75.20 70.60
5,546.50 01110/00 74.90 70.30
5,546.30 01117/00 75 .10 70.50
5,546.60 01124/00 74.80 70.20
5,546.50 02/01100 74.90 70.30
5,546.50 02/07/00 74.90 70.30
5,546.90 02114/00 74.50 69.90
5,546.95 02/23/00 74.45 69.85
5,547.05 03/01100 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 04/21100 73.80 69.20
5,547.70 04/28/00 73.70 69.10
5,547.70 05/01100 73.70 69.10
5,548.00 05/11/00 73.40 68.80
5,547.70 05115/00 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 08/31100 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 11109/00 72.40 67.80
5,548.85 12/06/00 72.55 67.95
5,549.47 01103/01 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 TW 4-8
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 4.60 126.00
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 11108/01 69.59 64.99
5,552.22 12/03/01 69.18 64.58
5,552.16 01103/02 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 09/11102 67.71 63.11
5,554.09 10/23/02 67.31 62.71
5,554.02 11122/02 67.38 62.78
5,554.23 12/03/02 67.17 62.57
5,554.43 01109/03 66.97 62.37
5,554.42 02112/03 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 05/01103 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 09/11103 75.16 70.56
5,546.38 10/02/03 75.02 70.42
5,546.40 11107/03 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 03128/04 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 07128/04 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 11116/04 73.12 68.52
Water Levels and Data over Time
White Mesa Mill -Well TW 4-8
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 4.60 126.00
5,548.80 12/22/04 72.60 68.00
5,548.43 01118/05 72.97 68.37
5,548.61 02/28/05 72.79 68.19
5,548.64 03115/05 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 11107/06 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 08114/07 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 12/11109 67.77 63.17
5,554.65 03/11/10 66.75 62.15
5,554.57 05/11110 66.83 62.23
5,554.34 09/29110 67.06 62.46
5,554.09 12/21110 67.31 62.71
5,554.50 02/28111 66.90 62.30
5,554.79 06/21111 66.61 62.01
5,554.63 09/20/11 66.77 62.17
5,555.01 12/21111 66.39 61.79
5,554.85 03/27/12 66.55 61.95
5,554.90 06/28/12 66.50 61.90
5,554.85 09/27112 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 TW 4-8
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 4.60 126.00
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 12/02115 81.18 76.58
5,542.00 03/30/16 79.40 74.80
\0 0 00 0 -....! 0
\
.!
Depth Below Measuring Point (ft.)
0'1 0 VI 0 +:-. 0 w 0
c ) ....
~
~
~
~ ~
'\
~
~
~
J LY ~ •
~ ...... 0 0
11129/99
03/08/00
-06/16/00
09/24/00
01/02/01
04/12/01
07/21101 -10/29/01
02/06/02
05/17/02
08/25/02
12/03/02
03/13/03
06/21/03
09/29/03
01/07/04
04/16/04
07/25/04 ~ 11102/04 ~ 02/10/05 ... 05/21/05 I
08/29/05 oc
12/07/05 ~ 03117/06
06/25/06 ""'" ~ 10/03/06 "'1
01111/07 ~ 04/21107 ~
07/30/07 "'C
11107/07 ~
-02/15/08 0 05/25/08 -< -
-
09/02/08 ~
12/11108 "'1
03/21/09 ~ .....
06/29/09 a 10/07/09 ~
01115/10 ,-....
04/25110 ?
08/03/10 0"' 11/11110 -02/19111 a
05/30/11 "'C '._/
09/07/11
12/16111
03/25112
07/03/12
10/11112
01119/13 -04/29/13
08/07113 -11115/13
02/23/14
-06/03/14
09/11/14
12/20114
03/30/15
07/08/15
10/16/15
01/24/16
05/03/16
08111116
11119/16
02/27/17
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 1.48 121.33
5 577.09 12/20/99 60.50 59.02
5,577.09 01/02/00 60.50 59.02
5,577.29 01110/00 60.30 58.82
5,577.09 01117/00 60.50 59.02
5,577.39 01124/00 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 02123/00 59.90 58.42
5,577.79 03/01100 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 03120/00 69.10 67.62
5,578.14 03/29/00 59.45 57.97
5,577.84 04104100 59.75 58.27
5,578.04 04113/00 59.55 58.07
5,578.24 04121100 59.35 57.87
5,578.39 04128/00 59.20 57.72
5,578.39 05101100 59.20 57.72
5,578.79 05/11100 58.80 57.32
5,578.39 05115100 59.20 57.72
5,578.79 05125100 58.80 57.32
5,578.81 06109100 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 09120100 58.13 56.65
5,579.44 10/05/00 58.15 56.67
5,579.79 11109/00 57.80 56.32
5,579.73 12/06/00 57.86 56.38
5,580.01 01103/01 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 1.48 121.33
5,581.04 05/31101 56.55 55.07
5,581.12 06/21101 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 01103/02 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 09/11102 53.77 52.29
5,584.01 10/23/02 53.58 52.10
5,583.88 11122/02 53.71 52.23
5,583.81 12/03/02 53.78 52.30
5,584.28 01109/03 53.31 51.83
5,584.41 02112/03 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 05/01103 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 09/11103 55.02 53.54
5,582.25 10/02/03 55.34 53.86
5,582.09 11107/03 55.50 54.02
5,582.48 12/03/03 55.11 53.63
5,583.69 01115/04 53.90 52.42
5,583.89 02/10/04 53.70 52.22
5,584.30 03/28/04 53.29 51.81
5,584.59 04/12/04 53.00 51.52
5,584.87 05/13/04 52.72 51.24
5,584.96 06/18/04 52.63 51.15
5,585.50 07/28/04 52.09 50.61
5,584.81 08/30/04 52.78 51.30
5,584.40 09/16/04 53.19 51.71
5,583.91 10/11/04 53.68 52.20
5,583.39 11/16/04 54.20 52.72
Water Levels and Data over Time
White Mesa Mill -Well TW 4-9
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,636.11 5,637.59 1.48 121.33
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 11107/06 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 10114/08 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 09110109 54.68 53.20
5,583.43 12/11109 54.16 52.68
5,584.00 03/11/10 53.59 52.11
5,583.27 05111110 54.32 52.84
5,582.92 09/29/10 54.67 53.19
5,583.08 12/21110 54.51 53.03
5,582.63 02/28111 54.96 53.48
5,583.62 06/21111 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 1.48 121.33
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 6l.ll 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
Depth Below Measuring Point (ft.)
-.] 0\ 0\ ~ 0\ 0\ VI VI VI VI VI 0 00 0\ N 0 00 0\ .j::>. N 0
12/20/99
03/29/00
07/07/00
10115/00
01/23/01
05/03/01
08/11101
11/19/01
02/27/02
06/07/02
09/15/02
12/24/02
04/03/03
07/12/03
10/20/03
01128/04
05/07/04
08/15/04 ~ 11123/04 ~ 03/03/05
06/11/05 .a. I 09/19/05 \0
12/28/05 ~ 04/07/06
07/16/06 -10/24/06 ~ ..,
02/01107 ~ 05/12/07 ~ 08/20/07 ~
11128/07 -=-03/07/08 0 06/15/08 ~ 09/23/08 ~ 01101109 ..,
04111109 ~
07/20/09 ... a 10/28/09 ~ 02/05110 ,-..,
05/16/10 ? 08/24110 0" 12/02110 -03/12111 a 06/20111 ~
09/28111 --01106112
04/15112
07/24112
11/01112
02/09113
05/20/13
08/28113
12/06113
03/16114
06/24114
10/02114
01/10/15
04/20115
07/29115
11106115
02/14116
05/24116
09/01116
12110116
03/20117
Water Levels and Data over Time
White Mesa Mill-Well TW4-10
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
5,631.99 5,634.24 2.25 111
5,576.75 01103/02 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 09/11102 56.00 53.75
5,578.49 10/23/02 55.75 53.50
5,578.43 11122/02 55.81 53.56
5,578.43 12/03/02 55.81 53.56
5,578.66 01109/03 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 05/01103 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 09/11103 57.48 55.23
5,576.36 10/02/03 57.88 55.63
5,576.05 11107/03 58.19 55.94
5,576.20 12/03/03 58.04 55.79
5,577.43 01115/04 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 10111/04 56.44 54.19
5,577.13 11116/04 57.11 54.86
5,576.96 12/22/04 57.28 55.03
5,576.63 01118/05 57.61 55.36
5,576.82 02/28/05 57.42 55.17
5,576.86 03/15/05 57.38 55.13
5,577.52 04/26/05 56.72 54.47
5,578.01 05/24/05 56.23 53.98
5,578.15 06/30/05 56.09 53.84
5,577.90 07/29/05 56.34 54.09
Water Levels and Data over Time
White Mesa Mill-Well TW4-10
Total or
Measuring Measured
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
5,631.99 5,634.24 2.25 111
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 11107/06 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 03126/08 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 03/11110 55.86 53.61
5,578.16 05111/10 56.08 53.83
5,577.85 09/29/10 56.39 54.14
5,577.28 12/21110 56.96 54.71
5,577.14 02128/11 57.10 54.85
5,578.09 06/21111 56.15 53.90
5,578.24 09/20/11 56.00 53.75
5,578.74 12121/11 55.50 53.25
5,577.89 03/27112 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 12/28112 56.37 54.12
5,577.92 03/28113 56.32 54.07
5,577.19 06/27/13 57.05 54.80
5,576.77 09127/13 57.47 55.22
5,576.22 12/20113 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 03/26115 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
0'1 VJ 0'1 N 0'1 .......
Depth Below Measuring Point (ft.)
0'1 0 Ul \0 Ul 00 Ul -....) Ul 0'1 Ul Ul Ul +=-Ul VJ
01103/02
04/13/02
07/22/02
10/30/02
02/07/03
-05/18/03
08/26/03
-12/04/03
03113/04
06/21104
09/29/04
-01107/05
04/17/05
07/26/05
11103/05
02/11/06 ~
-05/22/06 ~
08/30/06 .a. I
-12/08/06 ~
03118/07 =
-06/26/07 ~ 10/04/07 -01/12/08 ~ ,.,
04/21108 ~ 07/30/08 ~
11107/08 "C -02/15/09 =-
05/26/09 0
-09/03/09 ~ ~
12/12/09 ,.,
03/22/10 ~ ...
-06/30110 9
-10/08/10 ~
01116111 -~
04/26/11 .
08/04111 cr
11112/11 a
02/20112 "C '-' 05/30/12
,_ 09/07112
12/16112
03/26/13
07/04/13
10112113
01120114
04/30/14
08/08114
11116114
02/24/15
06/04/15
09112/15
12/21115
03/30/16
07/08/16
10/16/16
01/24/17
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 1.70 100
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 11122/02 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 05/01103 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 09116/04 70.61 68.91
5,553.11 10/11104 70.51 68.81
5,553.19 11116/04 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 1.70 100
5,553.86 09/12/05 69.76 68.06
5,555.30 12/07/05 68.32 66.62
5,556.20 03/08/06 67.42 65.72
5,556.48 06/14/06 67.14 65.44
5,556.37 07/18/06 67.25 65.55
5,556.94 11/07/06 66.68 64.98
5557.92 02/27/07 65.70 64
5,557.84 05/02/07 65.78 64.08
5,558.02 08/15/07 65.60 63.90
5,557.13 10/10/07 66.49 64.79
5,569.74 03/26/08 53.88 52.18
5,561.01 06/24/08 62.61 60.91
5,562.07 08/26/08 61 .55 59.85
5,562.47 10/14/08 61.15 59.45
5,563.80 03/10/09 59.82 58.12
5,564.27 06/24/09 59.35 57.65
5,564.32 09/10/09 59.30 57.60
5,564.70 12/11/09 58.92 57.22
5,565.14 03/11/10 58.48 56.78
5,565.61 05/11/10 58.01 56.31
5,565.67 09/29/10 57 .95 56.25
5,565.62 12/21/10 58.00 56.30
5,565.42 02/28111 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 12/21111 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 09/27113 57 .70 56.00
5,565.63 12/20113 57.99 56.29
5,565.03 03/27114 58.59 56.89
5,564.18 06/25/14 59.44 57.74
5,563.52 09/25114 60.10 58.40
5,563.37 12/17/14 60.25 58.55
5,532.62 03/26115 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
..... 8 \0 Ul \0 0
Depth Below Measuring Point (ft.)
00 Ul 00 0
-....)
Ul
-....)
0 0\ Ul 0\ 0 Ul Ul Ul 0
-
-
-
-
-
01/03/02
04/13/02
07/22/02
10/30/02
02/07/03
05/18/03
08/26/03
12/04/03
03113/04
06/21/04
09/29/04
01107/05
04/17/05
07/26/05
11/03/05
02111106 ~
05/22/06 ~
08/30/06 ~ I
12/08/06 1--" 1--" 03/18/07 ~ 06/26/07
10/04/07 ""' 01112/08 ~ "'1
04/21108 0
07/30/08 ~ "CS 11/07/08 ""' 02115/09 =-
05/26/09 0
09/03/09 < ~
12/12/09 "'1
03/22/10 ~
06/30/10 e·
10/08/10 ~
01116/11 -.. ~ 04/26/11 0" 08/04111 -11/12111 9
02/20112 "CS ._,
05/30/12
09/07112
12/16112
03/26/13
07/04/13
10/12113
01120/14
04/30/14
08/08114
11116/14
02/24/15
06/04/15
09/12115
12/21115
03/30116
07/08/16
10/16116
01/24/17
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 1.85 101.5
5,580.91 08/23/02 43 .32 41.47
5,581.54 09/11102 42.69 40.84
5,581.33 10/23/02 42.90 41.05
5,581.47 11122/02 42.76 40.91
5,581.55 12/03/02 42.68 40.83
5,582.58 01109/03 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 05/01103 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 09/11103 40.68 38.83
5,583.72 10/02/03 40.51 38.66
5,583.77 11107/03 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 10/11104 38.38 36.53
5,585.91 11116/04 38.32 36.47
5,586.35 12/22/04 37 .88 36.03
5,586.14 01118/05 38 .09 36.24
5,586.56 02/28/05 37 .67 35.82
5,586.95 03/15/05 37.28 35.43
5,587.20 04/26/05 37.03 35.18
5,587.35 05/24/05 36.88 35 .03
5,587.58 06/30/05 36.65 34.80
5,587.58 07/29/05 36.65 34.80
5,587.94 09/12/05 36.29 34.44
5,588.43 12/07/05 35 .80 33 .95
5,588.92 03/08/06 35 .31 33.46
5,588.34 06/13/06 35 .89 34.04
5,588.33 07/18/06 35.90 34.05
5,584.70 11/07/06 39.53 37.68
5588.85 02/27/07 35.38 33.53
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw~SD Well
5,622.38 5,624.23 1.85 101.5
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 12111109 38.46 36.61
5,585.88 03/11110 38.35 36.50
5,586.35 05111110 37.88 36.03
5,585.68 09/29110 38.55 36.70
5,585.09 12/21110 39.14 37.29
5,584.65 02/28/11 39.58 37.73
5,584.76 06/21111 39.47 37.62
5,584.32 09/20/11 39.91 38.06
5,584.22 12/21111 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 06/27113 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 03/27114 42.56 40.71
5,581.03 06/25/14 43.20 41.35
5,580.49 09/25114 43.74 41.89
5,580.33 12/17/14 43.90 42.05
5,579.28 03/26115 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
~ 00 ~ 0\
Depth Below Measuring Point (ft.)
t ~ N ~ 0 w 00 w 0\ w ~
1----+----t---+---t---+----t-------t---+ 08/23/02
12/01/02
03/11/03
06/19/03
09/27/03
01/05/04
04114/04
07/23/04
10/31/04
02/08/05
05/19/05
08/27/05
-12/05/05
03115/06
06/23/06
-10/01106
01/09/07
04119/07
-07/28/07
11/05/07
02/13/08
05/23/08
08/31/08
12/09/08
03/19/09
06/27/09
-10/05/09
01113/10
04/23/10
08/01/10
,_ 11/09110
02/17/11
05/28/11
09/05/11
12114/11
03/23/12
07/01112
10/09112
01/17/13
04/27/13
08/05/13
11/13/13
02/21114
06/01114
09/09/14
12/18/14
03/28/15
07/06/15
10/14/15
01/22/16
05/01/16
08/09/16
11/17/16 .__ __ _.__ __ __,_ ___ .__ __ __,__ __ __._ __ ___.'-----'-02/25/17
~ ~ I ~ N
~ ;-
"'1
~ ~ "= ;.
0 < ~ "'1
~ .... ~ -.. ~
'a' e "= '-"
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 1.85 102.5
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 05/01103 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 09/11103 78.69 76.84
5,541.34 10/02/03 78.60 76.75
5,541.69 11107/03 78.25 76.40
5,541.91 12/03/03 78.03 76.18
5,542.44 01115/04 77.50 75.65
5,542.47 02/10/04 77.47 75.62
5,542.84 03/28/04 77.10 75.25
5,543.08 04/12/04 76.86 75.01
5,543.34 05/13/04 76.60 74.75
5,543.40 06/18/04 76.54 74.69
5,544.06 07/28/04 75.88 74.03
5,544.61 08/30/04 75.33 73.48
5,545.23 09/16/04 74.71 72.86
5,546.20 10/11/04 73.74 71.89
5,547.43 11/16/04 72.51 70.66
5,548.96 12/22/04 70.98 69.13
5,549.02 01/18/05 70.92 69.07
5,550.66 02/28/05 69.28 67.43
5,551.26 03/15/05 68.68 66.83
5,552.23 04/26/05 67.71 65.86
5,552.87 05/24/05 67.07 65.22
5,553.42 06/30/05 66.52 64.67
5,554.00 07/29/05 65.94 64.09
5,555.21 09/12/05 64.73 62.88
5,558.13 12/07/05 61.81 59.96
5,562.93 03/08/06 57.01 55.16
5,564.39 06/13/06 55.55 53.70
5,562.09 07/18/06 57.85 56.00
5,565.49 11/07/06 54.45 52.60
5571.08 02/27/07 48.86 47.01
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (bhv.LSD) Well
5,618.09 5,619.94 1.85 102.5
5,570.63 05/02/07 49.31 47.46
5,565.24 08114/07 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 09/29110 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 06/28112 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 06/27113 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 03/27114 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
-8 \0 0
Depth Below Measuring Point (ft.)
00 0 --.1 0 g VI 0 +:-0
1----------4.-----+-----+----+-----+----+ 08/23/02
12/01/02
03/11103
06119/03
09/27/03
01105/04
04/14/04
07/23/04
10/31104
02/08/05
-05/19/05
08/27/05
12/05/05
03/15/06
06/23/06
10/01/06
• 01/09/07
04/19/07
07/28/07
11105/07
-02/13/08
05/23/08
08/31108
12/09/08
03/19/09
06/27/09
10/05/09
01113110
-04/23/10
08/01110
-11109/10
02/17111
05/28111
~ 09/05111
12/14/11
03/23112
07/01112
10/09112
01117113
04/27/13
08/05/13
11113113
-02/21114
06/01114
09/09114
12/18/14
03/28115
07/06/15
10/14115
01122/16
05/01116
08/09/16
11117116
'-------'-----L------'------'----.....L.-----'-02/25117
~ ~ I
io-6 ~
~ ;-
'"1
0 ~ ;.
0 ~
'"1
~ .... a ('tl
~ ??
'a' e ~ ._..,
Water Levels and Data over Time
White Mesa Mill-Well TW4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5 612.77 1.85 93
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 11122/02 92.45 90.60
5,520.42 12/03/02 92.35 90.50
5,520.70 01109/03 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 05/01103 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 09/11103 91.47 89.62
5,521.35 10/02/03 91.42 89.57
5,521.36 11107/03 91.41 89.56
5,521.16 12/03/03 91.61 89.76
5,521.29 01115/04 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 10/11104 90.98 89.13
5,521.80 11116/04 90.97 89.12
5,521.82 12/22/04 90.95 89.10
5,521.82 01118/05 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 11107/06 92.60 90.75
5522.24 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 93
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 12111109 89.23 87.38
5,522.98 03/11110 89.79 87.94
5,524.01 05/11110 88.76 86.91
5,524.37 09/29/10 88.40 86.55
5,524.62 12/21110 88.15 86.30
5,524.78 02/28/11 87.99 86.14
5,525.23 06/21111 87.54 85.69
5,525.45 09/20111 87.32 85.47
5,525.72 12/21111 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 12/28112 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 03/27114 84.02 82.17
5,529.21 06/25114 83.56 81.71
5,529.78 09/25/14 82.99 81.14
5,530.41 12117/14 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
\0 0\ \0 .j:::.. \0 N
Depth Below Measuring Point (ft.)
\0 0 00
00 00 0\
00 .j:::.. 00 N 00 0 -...l
00
08/23/02
12/01/02
03/11/03
06119/03
09/27/03
-01105/04
04/14/04
07/23/04
10/31104
02/08/05
05/19/05
08/27/05
12/05/05
03/15/06
06/23/06 ~ 10/01106 ~ 01/09/07 ~
04/19/07 I
""'"" 07/28/07 ~
11/05/07 ~ 02/13/08 """ 05/23/08 ~ "'1 08/31/08 ~ 12/09/08 ~
~ 03/19/09 ~
06/27/09 :;.
10/05/09 0
01113110 -< ~
04/23/10 "'1
08/01/10 ~ ...
-11/09/10 e
-02/17111 ~ ,-._
05/28111 ~ 09/05/11 0"" 12/14/11 -03/23112 e "CC 07/01/12 ._,
10/09/12
01/17113
04/27/13
08/05/13
11/13/13
02/21114
06/01114
09/09/14
-12118/14
03/28/15
07/06115
10/14/15
01122/16
05/01116
08/09116
11117/16
02/25/17
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 11122/02 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 05/01103 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 09111/03 64.51 63.21
5,560.63 10/02/03 64.82 63.52
5,560.56 11107/03 64.89 63.59
5,564.77 12/03/03 60.68 59.38
5,570.89 Ol/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 09116/04 97.98 96.68
5,553.97 11116/04 71.48 70.18
5,562.33 12/22/04 63.12 61.82
5,550.00 Ol/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 11107/06 74.57 73.27
5558.77 02/27/07 66.68 65.38
5,548.54 05/02/07 76.91 75.61
5,551.33 10/10/07 74.12 72.82
5,545.56 03/26/08 79.89 78.59
5,545.56 06/25/08 79.89 78.59
Water Levels and Data over Time
White Mesa Mill-Well MW-26
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,624.15 5,625.45 1.30 121.33
5,545.82 08/26/08 79.63 78.33
5,545.64 10/14/08 79.81 78.51
5,544.45 03/03/09 81.00 79.70
5,545.32 06/24/09 80.13 78.83
5,544.61 09/10/09 80.84 79.54
5,549.33 12/11/09 76.12 74.82
5,543.78 03/11110 81.67 80.37
5,545.61 05/11110 79.84 78.54
5,547.43 09/29/10 78.02 76.72
5,544.14 12/21110 81.31 80.01
5,546.77 02/28/11 78.68 77.38
5,537.60 06/21111 87.85 86.55
5,551.46 09/20/11 73.99 72.69
5,549.12 12/21111 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 03/27114 68.80 67.50
5,552.23 06/25/14 73.22 71.92
5,554.05 09/25114 71.40 70.10
5,550.65 12/17114 74.80 73.50
5,557.55 03/26115 67.90 66.60
5,558.51 06/22/15 66.94 65.64
5,560.81 09/30115 64.64 63.34
5,560.25 12/02/15 65.20 63.90
5,561.07 03/30/16 64.38 63.08
-8 1.0 0
Depth Below Measuring Point (ft.)
00 0 -..l 0 0'1 0 Ul 0 ~
1--------+----+----1-----t-------<w-----+ 08/23/02
12/01/02
03/11/03
06/19/03
09/27/03
01105/04
04114/04
07/23/04
-10/31104
02/08/05
05/19/05
08/27/05
12/05/05
1-03/15/06
-06/23/06
10/01106
01/09/07
04/19/07
07/28/07
11/05/07
-02/13/08
-05/23/08
08/31108
12/09/08
-03119/09
-06/27/09
-10/05/09
01113/10
04/23/10
08/01110
'-11/09/10
02117/11
05/28/11
09/05/11
12/14111
03/23/12
07/01112
10/09/12
01117/13
04/27113
08/05113
-11113/13
02/21/14
06/01/14
09/09114
12/18/14
03/28/15
07/06/15
10/14115
01122/16
05/01116
08/09/16
-11117116
L-------l.------1...-----'------'------L------'-02/25/17
~ N 0"1
~ ~ "'1
0 ~ "= ;.
0 < ~ "'1
1-3 .... ~ ,-.
~
0"" 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
5,622.19 5,624.02 1.83 142
5,562.91 08/23/02 61.11 59.28
5,563.45 09/11/02 60.57 58.74
5,563.75 10/23/02 60.27 58.44
5,563.68 11122/02 60.34 58.51
5,563.68 12/03/02 60.34 58.51
5,564.16 01109/03 59.86 58.03
5,564.25 02/12/03 59.77 57.94
5,564.53 03/26/03 59.49 57.66
5,564.46 04/02/03 59.56 57.73
5,564.79 05/01103 59.23 57.40
5,564.31 06/09/03 59.71 57.88
5,563.29 07/07/03 60.73 58.90
5,562.76 08/04/03 61.26 59.43
5,561.73 09/11/03 62.29 60.46
5,561.04 10/02/03 62.98 61.15
5,560.39 11/07/03 63.63 61.80
5,559.79 12/03/03 64.23 62.40
5,561.02 01115/04 63.00 61.17
5,561.75 02/10/04 62.27 60.44
5,562.98 03/28/04 61.04 59.21
5,563.29 04112/04 60.73 58.90
5,564.03 05/13/04 59.99 58.16
5,564.09 06/18/04 59.93 58.10
5,565.08 07/28/04 58.94 57.11
5,564.56 08/30/04 59.46 57.63
5,563.55 09/16/04 60.47 58.64
5,561.79 10/11104 62.23 60.40
5,560.38 11/16/04 63.64 61.81
5,559.71 12/22/04 64.31 62.48
5,559.14 01118/05 64.88 63.05
5,558.65 02/28/05 65.37 63.54
5,558.54 03/15/05 65.48 63.65
5,558.22 04/26/05 65.80 63.97
5,558.54 05/24/05 65.48 63.65
5,559.24 06/30/05 64.78 62.95
5,559.38 07/29/05 64.64 62.81
5,559.23 09/12/05 64.79 62.96
5,557.67 12/07/05 66.35 64.52
5,557.92 03/08/06 66.10 64.27
5,558.47 06/13/06 65.55 63.72
5,558.42 07118/06 65.60 63.77
5,558.09 11/07/06 65.93 64.10
5557.34 02/27/07 66.68 64.85
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
5 622.19 5,624.02 1.83 142
5,547.11 05/02/07 76.91 75.08
5,558.52 08/14/07 65.50 63.67
5,559.02 10/10/07 65.00 63.17
5,561.04 03/26/08 62.98 61.15
5,560.06 06/24/08 63.96 62.13
5,559.32 08/26/08 64.70 62.87
5,558.89 10/14/08 65.13 63.30
5,558.40 03/03/09 65.62 63.79
5,558.32 06/24/09 65.70 63.87
5,558.03 09/10/09 65.99 64.16
5,558.81 12/11109 65 .21 63.38
5,559.80 03/11/10 64.22 62.39
5,559.85 05/11110 64.17 62.34
5,560.54 09/29/10 63.48 61.65
5,558.65 12/21110 65 .37 63.54
5,559.26 02/28/11 64.76 62.93
5,560.48 06/21111 63.54 61.71
5,561.52 09/20/11 62.50 60.67
5,562.95 12/21111 61.07 59.24
5,563.76 03/27/12 60.26 58.43
5,563.90 06/28/12 60.12 58.29
5,564.65 09/27/12 59.37 57.54
5,563.77 12/28/12 60.25 58.42
5,564.74 03/28/13 59.28 57.45
5,563.66 06/27/13 60.36 58 .53
5,562.27 09/27/13 61.75 59.92
5,562.17 12/20/13 61.85 60.02
5,561.17 03/27/14 62.85 61.02
5,559.53 06/25/14 64.49 62.66
5,558.36 09/25/14 65.66 63.83
5,558.00 12/17/14 66.02 64.19
5,559.02 03/26/15 65.00 63.17
5,560.62 06/22/15 63.40 61.57
5,560.62 09/30/15 63.40 61.57
5,560.85 12/02/15 63.17 61.34
5,560.92 03/30/16 63.10 61.27
00 0
-..,J
lJl
Depth Below Measuring Point (ft.)
-..,J
0 0\ lJl 0\ 0 lJl lJl
lJl 0
1-----+----+----+------+oa+-----t-----+ 08/23/02
12/01/02
03/11/03
06/19/03
09/27/03
01/05/04
04/14/04
07/23/04
10/31/04
02/08/05
05/19/05
08/27/05
12/05/05
03/15/06
06/23/06
l0/01/06
01/09/07
04/19/07
07/28/07
11/05/07
02/13/08
05/23/08
08/31/08
12/09/08
03/19/09
06/27/09
10/05/09
01/13/10
04/23110
08/01/10
11/09/10
02/17111
05/28/11
09/05/11
12/14/11
03/23/12
07/01/12
l0/09/12
01/17/13
04/27/13
08/05/13
11/13/13
02/21/14
06/01/14
09/09/14
12/18/14
03/28/15
07/06/15
10/14/15
01/22/16
05/01116
08/09/16
11117/16
L--------1------J..-----'-------'------L-----'-02/25/17
~ ~ ""' I
~ 0'\
~ ;-
"'1
~ ('D
"'0 ;.
0 < ('D
"'1
~ ..... ~ --?
r::r ! .._
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 09/11102 82.85 81.02
5,542.61 10/23/02 82.63 80.80
5,542.49 11122/02 82.75 80.92
5,542.82 12/03/02 82.42 80.59
5,543.03 01109/03 82.21 80.38
5,543.04 02/12/03 82.20 80.37
5,543.41 03/26/03 81.83 80.00
5,543.69 04/02/03 81.55 79.72
5,543.77 05/01103 81.47 79.64
5,544.01 06/09/03 81.23 79.40
5,544.05 07/07/03 81.19 79.36
5,543.99 08/04/03 81.25 79.42
5,544.17 09/11/03 81.07 79.24
5,544.06 10/02/03 81.18 79.35
5,544.03 11107/03 81.21 79.38
5,543.94 12/03/03 81.30 79.47
5,543.98 01115/04 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 06118/04 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 10111104 79.63 77.80
5,545.46 11116/04 79.78 77.95
5,545.66 12/22/04 79.58 77.75
5,545.33 01118/05 79.91 78.08
5,545.51 02/28/05 79.73 77.90
5,545.57 03115/05 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 09112/05 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 07118/06 79.30 77.47
5,546.24 11/07/06 79.00 77.17
5546.81 02/27/07 78.43 76.6
Water Levels and Data over Time
White Mesa Mill -Well MW -32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5546.56 05/02/07 78.68 76.85
5546.81 08/15/07 78.43 76.6
5546.96 10/10/07 78.28 76.45
5547.9 03/26/08 77.34 75.51
5548.08 06125/08 77.16 75.33
5548.42 08/26/08 76.82 74.99
5548.05 10/14/08 77.19 75.36
5548.29 03/03/09 76.95 75.12
5548.09 06/24/09 77.15 75.32
5547.79 09/10/09 77.45 75.62
5548.09 12/11109 77.15 75.32
5,548.50 03/11110 76.74 74.91
5,548.89 05/11110 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 09/20111 76.05 74.22
5,550.06 12/21111 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 12/28112 74.95 73.12
5,551.54 03/28/13 73.70 71.87
5,550.34 06/27113 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 03/26115 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
Depth Below Measuring Point (ft.)
00 00 00 -.1 -.1 -.1 -.1 .j::>. N 0 00 0\ .j::>. N
08/23/02
12/01102
03/11/03
06/19/03
09/27/03
01/05/04
04114/04
07/23/04
10/31104
02/08/05
05/19/05
08/27/05
-12/05/05
03/15/06
06/23/06 3: 10/01/06
01109/07 ~ I 04119/07 ~
07/28/07 N
11105/07 ~ 02/13/08 -05/23/08 ~ "1 08/31108 ~ 12/09/08 ~
03119/09 "C -06/27/09 =:r
10/05/09 0
01113/10 -< ~
04/23/10 "1
08/01/10 1-3 ....
-11109/10 a
02/17/11 ~ -05/28111 ~ 09/05/11 0"" 12/14111 --03/23/12 e "C 07/01112 -10/09112
01117/13
04/27/13
08/05113
11113113
02/21114
06/01114
09/09114
12/18114
03/28115
07/06115
10114115
01122/16
05/01116
08/09116
11117116
02/25117
Water Levels and Data over Time
White Mesa Mill -Well TW 4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5 639.13 5,641.28 2.15 137.5
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 11122/02 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 05/01103 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 09/11103 57.27 55.12
5,583.67 10/02/03 57.61 55.46
5,583.50 11107/03 57.78 55.63
5,584.08 12/03/03 57.20 55.05
5,585.45 01115/04 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 10111104 56.06 53.91
5,584.70 11116/04 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 03115/05 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 09112/05 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 06113/06 55.35 53.20
5,585.40 07118/06 55.88 53.73
5,585.38 11/07/06 55.90 53.75
5585.83 02/27/07 55.45 53.30
Water Levels and Data over Time
White Mesa Mill -Well TW 4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,639.13 5,641.28 2.15 137.5
5585.15 05/02/07 56.13 53.98
5586.47 06/24/08 54.81 52.66
5586.3 08/26/08 54.98 52.83
5585.21 10/14/08 56.07 53.92
5584.47 03/03/09 56.81 54.66
5584.35 06/24/09 56.93 54.78
5583.88 09/10/09 57.4 55.25
5584.43 12/11/09 56.85 54.70
5,585.26 03/11110 56.02 53.87
5,584.17 05111/10 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 09/20111 56.57 54.42
5,585.03 12/21111 56.25 54.10
5,584.63 03/27112 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 09/27113 59.90 57.75
5,579.71 12/20/13 61.57 59.42
5,579.26 03/27114 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 09/30115 64.65 62.50
5,576.20 12/02/15 65.08 62.93
5,576.05 03/30/16 65.23 63.08
Depth Below Measuring Point (ft.)
-.J 0\ Ul ~ V.l N ......
0 0 0 0 0 0 0 0
08/23/02
12/01102
03/11103
-06/19/03
-09/27/03
01/05/04
04/14/04
07/23/04
-10/31/04
02/08/05
-05/19/05
08/27/05
12/05/05
'03/15/06
06/23/06 ~
10/01106 ~ 01109/07 ......
04/19/07 I ,.....
07/28/07 00
11105/07 ~ 02/13/08 f"'''
-05/23/08 ~ ..,
08/31108 0 12/09/08 ~
03/19/09 "=
06/27/09 ~
10/05/09 0
01113/lO < ~
04/23/10 ..,
-08/01110 ~ ....
11109/10 a
02117/11 ~ -.. 05/28/11 ~ 09/05/11 'c::J' 12/14/11 -03/23/12 a "= 07/01/12 '-'
10/09/12
01/17/13
04/27/13
08/05/13
11113/13
02/21114
06/01/14
09/09/14
12/18/14
03/28/15
07/06/15
10/14/15
01122116
05/01116
08/09/16
11/17/16
02/25/17
Water Levels and Data over Time
White Mesa Mill -Well TW 4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 121.33
5,581.88 08/23/02 49.51 47.65
5,582.14 09111102 49.25 47.39
5,582.06 10/23/02 49.33 47.47
5,582.07 11122/02 49.32 47.46
5,582.16 12/03/02 49.23 47.37
5,582.28 01109/03 49.11 47.25
5,582.29 02/21103 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 05/01103 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 10/11104 81.59 79.73
5,546.04 11116/04 85.35 83.49
5,547.34 12/22/04 84.05 82.19
5,548.77 01118/05 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 11107/06 82.58 80.72
5543.59 02/27/07 87.80 85.94
5544.55 05/02/07 86.84 84.98
5558.97 08/15/07 72.42 70.56
5559.73 10/10/07 71.66 69.8
5569.26 03/26/08 62.13 60.27
5535.47 06/25/08 95.92 94.06
5541.41 08/26/08 89.98 88.12
5558.45 10/14/08 72.94 71.08
5536.9 03/03/09 94.49 92.63
5547.76 06/24/09 83.63 81.77
5561.48 09/10/09 69.91 68.05
5548.14 12/11109 83.25 81.39
5,570.58 03/11/10 60.81 58.95
Water Levels and Data over Time
White Mesa Mill · Well TW 4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 121.33
5,561.35 05/11110 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
......
8 \0 0
Depth Below Measuring Point (ft.)
00 0 -.J 0 0\ 0
(Jl
0 +:-. 0
1-----+----+----t-----t-----..-----+ 08/23/02
12/01102
03/11103
06/19/03
09/27/03
01105/04
04114/04
07/23/04
10/31/04
02/08/05
-05119/05
08/27/05
12/05/05
03/15/06
06/23/06
10/01/06
01109/07
04119/07
07/28/07
11105/07
02113/08
05/23/08
,_ 08/31108
12/09/08
03/19/09
06/27/09
-10/05/09
01113110
-04/23/10
08/01110
11/09/10
02117/11
05/28111
09/05111
12114/11
03/23/12
07/01112
10/09/12
01/17/13
04/27/13
08/05/13
11/13113
02/21114
06/01114
09/09/14
12118/14
03/28/15
07/06/15
10/14/15
01122/16
05/01/16
08/09/16
11117116
~..-._ __ ---~. ___ --~... ___ ___J_ ___ ....l.-___ ..J..._ ___ _._ 02/25/17
1-3 ~ .&;.
I ~ \C
~ ;-
~
~ ('D
"C g.
0 < ('D
~
1-3 ...
9 ('D ,-.,
~ .
r:::1"
! '-'
Water Levels and Data over Time
White Mesa Mill -Well TW4-20
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.52 5,629.53 1.01 106.0
5,565.70 07/29/05 63.83 62.82
5,546.53 08/30/05 83.00 81.99
5,540.29 09/12/05 89.24 88.23
5,541.17 12/07/05 88.36 87.35
5,540.33 03/08/06 89.20 88.19
5,530.43 06113/06 99.10 98.09
5,569.13 07/18/06 60.40 59.39
5,547.95 11/07/06 81.58 80.57
5,549.25 02/27/07 80.28 79.27
5,550.58 05/02/07 78.95 77.94
5,563.60 08/14/07 65.93 64.92
5,555.85 10/10/07 73.68 72.67
5,569.10 03/26/08 60.43 59.42
5,560.00 06/25/08 69.53 68.52
5,539.64 08/26/08 89.89 88.88
5,539.51 10/14/08 90.02 89.01
5,553.00 03/03/09 76.53 75.52
5,534.18 06/24/09 95.35 94.34
5,558.39 09/10/09 71.14 70.13
5,560.99 12/11109 68.54 67.53
5,564.09 03/11110 65.44 64.43
5,564.22 05/11/10 65.31 64.30
5,560.33 09/29/10 69.20 68.19
5,561.35 12/21110 68.18 67.17
5,560.18 02/28/11 69.35 68.34
5,576.23 06/21111 53.30 52.29
5,548.50 09/20/11 81.03 80.02
5,558.58 12/21111 70.95 69.94
5,567.73 03/27/12 61.80 60.79
5,567.77 06/28/12 61.76 60.75
5,569.58 09/27/12 59.95 58.94
5,572.58 12/28/12 56.95 55.94
5,571.52 03/28113 58.01 57.00
5,569.93 06/27/13 59.60 58.59
5,568.53 09/27/13 61.00 59.99
5,559.44 12/20/13 70.09 69.08
5,562.17 03/27114 67.36 66.35
5,558.98 06/25/14 70.55 69.54
5,561.03 09/25/14 68.50 67.49
5,559.39 12/17114 70.14 69.13
5,565.65 03/26/15 63.88 62.87
5,568.25 06/22115 61.28 60.27
Water Land
Elevation Surface
(WL) (LSD)
5,628.52
5,566.78
5,565.43
5,565.87
Water Levels and Data over Time
White Mesa Mill-Well TW4-20
Total or
Measuring Measured
Point Depth to
Elevation Length Of Date Of Water
(MP) Riser (L) Monitoring (blw.M P)
5,629.53 1.01
09/30/15 62.75
12/02/15 64.10
03/30116 63.66
Total Depth Total
to Water Depth Of
(bhv.LSD) Well
106.0
61.74
63.09
62.65
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 1.15 120.92
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 11107/06 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 12111109 59.36 58.21
5,582.81 03/11110 56.54 55.39
5,582.23 05/11110 57.12 55.97
5,576.60 09/29/10 62.75 61.60
5,581.14 12/21110 58.21 57.06
5,579.53 02/28/11 59.82 58.67
5,584.17 06/21111 55.18 54.03
5,584.80 09/20/11 54.55 53.40
5,585.68 12/21111 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 06/27113 57.56 56.41
5,580.89 09/27/13 58.46 57.31
5,577.45 12/20113 61.90 60.75
5,576.01 03/27/14 63.34 62.19
5,574.08 06/25114 65.27 64.12
5,573.20 09/25/14 66.15 65.00
5,576.13 12117114 63.22 62.07
5,578.19 03/26/15 61.16 60.01
5,574.85 06/22115 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 1.1 5 120.92
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
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 1.17 113.5
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 03126/08 55.95 54.78
5,573.04 06/24/08 55 .96 54.79
5,573.04 08126/08 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 12111/09 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 12/21110 54.56 53.39
5,574.49 02/28/11 54.51 53.34
5,574.97 06/21111 54.03 52.86
5,575.06 09/20111 53.94 52.77
5,575.69 12121/11 53.31 52.14
5,575.61 03/27112 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 06/27113 56.55 55.38
5,572.25 09/27/13 56.75 55.58
5,569.93 12/20113 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 06/22115 58.07 56.90
-
-
-
-~
-
-
~
~ -~
-•
•
-
-~ -
---
0 0 .....
' t
~
~
~
~
~
~
4
• ----.-----~
0 00
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 1.60 113.5
5,538.89 09113/07 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 12111107 67.88 66.28
5,539.19 01108/08 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 11126/08 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 07/31109 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 03111110 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 03/28113 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 11 3.5
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 09/30115 68.55 66.95
5,538.28 12/02/15 69.09 67.49
5,538.29 03/30/16 69.08 67.48
-..1 0 0\ \0
Depth Below Measuring Point (ft.)
0\ 00 0\ -..1 0\ 0\ 0\ Ul 0\
"""
0\ w
l-----l----,-i..._---+--------1---+----+--------l---+ 09/13/07
11/02/07
12/22/07
02110/08
03/31108
05/20/08
07/09/08
08/28/08
10/17/08
12/06/08
01125/09
03/16/09
05105109
06/24/09
08/13/09
10/02/09
11121109
01/10/10
-03/01/10
04/20/10
06/09/10
07/29/10
09/17/10
11/06/10 ~-12/26/10
-02/14/11
-04/05/11
05/25/11
07114/11
09/02/11
10/22/11
12/11111
01130/12
-03/20/12
05/09112
06/28/12
08117/12
10/06/12
11125/12
01114/13
·-03/05/13
-04/24/13
06/13113
08/02/13
-09/21113
11110/13
-12/30/13
02/18/14
04/09/14
05/29/14
07/18/14
09/06/14
10/26/14
12/15/14
02/03/15
03/25/15
05/14115
07/03/15
08/22/15
10111115 11130/15
01119116
03/09/16
04/28/16
06/17116
08/06/16
l...----....L..-----1------1---...J.,._-----l....-----L------'-09/25/16
~ ~ I N ~
~ ;-
"'1
0 ~ "CC ~
0 < ~ "'1
~ .... ~ -~
-a' §"
"CC '-'
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 2.13 113.5
5,570.61 09113/07 57.22 55.09
5,570.53 10/10/07 57.30 55.17
5,571.16 11130/07 56.67 54.54
5,571.30 12/11107 56.53 54.40
5,571.03 Ol/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 1l/26/08 56.88 54.75
5,570.92 12/29/08 56.91 54.78
5,571.65 Ol/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 05129109 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 08/31109 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 05111110 55.92 53.79
5,572.18 09129/10 55.65 53.52
5,571.86 12/21110 55.97 53.84
5,571.78 02/28/11 56.05 53.92
5,572.40 06/21111 55.43 53.30
5,572.19 09/20/11 55.64 53.51
5,573.02 12/21111 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 2.13 113.5
5,563.43 06/25/14 64.40 62.27
5,563.43 09/25/14 64.40 62.27
5,560.97 12/17114 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
00 0 0
-....)
0 0
Depth Below Measuring Point (ft.)
~ 0
~
~
~
~
t
4
~
~
~
"
v
?
(
!
~
Ul 0 0
(!:;
0
v.> 0 0 ~ 0
...... 0
0
0 0
--
09/13/07
11102/07
12/22/07
02/10/08
03/31/08
05/20/08
07/09/08
08/28/08
10117/08
12/06/08
01125/09
03/16/09 05105109
06/24/09
08/13/09
10/02/09
11/21109
01110/10
03/01110
04/20/10
06/09110
07/29/10
09117/10
11106/10
12/26/10
02/14/11
04/05/11
05/25/11
07/14/11
09/02111
10/22/11
12/11111
01130/12
03/20112
05/09/12
06/28/12
08/17/12
10/06/12
11/25/12
01/14/13
03/05/13
04/24/13
06/13/13
08/02/13
09/21113
11/10113
12/30/13
02/18/14
04/09/14
05/29114
07/18/14
09/06/14
10/26114
12/15114
02/03115
03/25/15
05/14/15
07/03/15
08/22115
10111115
11130/15
01119/16
03/09/16
04/28/16
06/17/16
08/06/16
09/25/16
~ ~ I N ~
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0 -< ~ "'1
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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) (L D) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5 627.83 5,644.91 17.08 134.8
5,601.86 09/13/07 43.05 25.97
5,601.89 10110/07 43.02 25.94
5,602.57 11130/07 42.34 25.26
5,602.82 12111107 42.09 25.01
5,601.94 01108/08 42.97 25.89
5,599.13 02/18/08 45.78 28.70
5,597.11 03/26/08 47.80 30.72
5,595.51 04/23/08 49.40 32.32
5594.42 05/30/08 50.49 33.41
5,594.26 06/24/08 50.65 33.57
5,586.67 07116/08 58.24 41.16
5,594.17 08/26/08 50.74 33.66
5,594.23 09/10/08 50.68 33.60
5,594.12 10/14/08 50.79 33.71
5,594.06 11126/08 50.85 33.77
5,594.87 12/29/08 50.04 32.96
5,595 .89 01126/09 49.02 31.94
5,596.27 02124/09 48.64 31.56
5,596.47 03/06/09 48.44 31.36
5,596.74 04/07/09 48.17 31.09
5,597.55 05/29/09 47.36 30.28
5,598.11 06/30/09 46.80 29.72
5,598.22 07/31109 46.69 29.61
5,598.52 08/31109 46.39 29.31
5,598.49 09/10/09 46.42 29.34
5,599.48 12/11109 45.43 28.35
5,599.75 03111/10 45.16 28.08
5,599.63 05/11/10 45.28 28.20
5,598.68 09/29/10 46.23 29.15
5,598.66 12/21110 46.25 29.17
5,598.18 02/28/11 46.73 29.65
5,598.61 06/21111 46.30 29.22
5,598.08 09/20/11 46.83 29.75
5,598.23 12/21/11 46.68 29.60
5,597.41 03/27/12 47.50 30.42
5,597.41 06/28/12 47.50 30.42
5,595.60 09/27/12 49.31 32.23
5,597.41 12/28/12 47.50 30.42
5,597.43 03/28/13 47.48 30.40
5,587.61 06127/13 57.30 40.22
5,585.91 09/27/13 59.00 41.92
5,561.00 12/20/13 83.91 66.83
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
5,627.83 5,644.91 17.08 134.8
5,584.79 03/27/14 60.12 43.04
5,582.44 06/25114 62.47 45.39
5,583.95 09/25/14 60.96 43.88
5,581.13 12117/14 63.78 46.70
5,587.40 03/26/15 57.51 40.43
5,581.91 06/22/15 63.00 45.92
5,581.40 09/30/15 63.51 46.43
5,578.42 12/02/15 66.49 49.41
5,579.42 03/30/16 65.49 48.41
1.0 0
Depth Below Measuring Point (ft.)
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09/13/07
11102/07
12/22/07
02/10/08
03/31108
05/20/08
07/09/08
08/28/08
10/17/08
12/06/08
01/25/09
03/16/09
05/05/09
06/24/09
08/13/09
10/02/09
11121109
01/10110
03/01110
04/20/10
06/09/10
07/29/10
09/17/10
11106/10
12/26/10
02/14/11
04/05/11
05/25111
07114/11
09/02/11
10/22111
12/11111
01130112
03/20112
05/09/12
06/28112
08/17112
10/06/12
11/25112
01/14/13
03/05113
04/24/13
06/13/13
08/02/13
09/21113
11110/13
12/30/13
02/18/14
04/09/14
05/29/14
07/18/14
09/06/14
10/26/14
12115/14
02/03115
03/25115
05/14/15
07/03/15
08/22115
10/11115
11/30/15
01119/16
03/09116
04/28116
06/17116
08/06/16
09/25/16
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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 86
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 06/21111 64.11 62.41
5,537.59 09/20111 64.09 62.39
5,538.16 12/21/11 63.52 61.82
5,538.18 03/27112 63.50 61.80
5538.23 06/28/12 63.45 61.75
5,538.57 09/27112 63.11 61.41
5,538.20 12/28/12 63.48 61.78
5,539.13 03/28113 62.55 60.85
5,539.00 06/27/13 62.68 60.98
5,538.94 09/27113 62.74 61.04
5,538.97 12/20/13 62.71 61.01
5,538.53 03127/14 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 09/30115 65.92 64.22
5,535.23 12/02/15 66.45 64.75
5,535.15 03/30116 66.53 64.83
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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 96
5,517.78 12/21/11 90.16 88.41
5,524.84 03/27/12 83.10 81.35
5,524.93 06/28/12 83.01 81.26
5,525.59 09/27/12 82.35 80.60
5,524.86 12/28/12 83.08 81.33
5,526.37 03/28/13 81.57 79.82
5,526.29 06/27/13 81.65 79.90
5,527.04 09/27/13 80.90 79.15
5,527.14 12/20/13 80.80 79.05
5,527.55 03/27/14 80.39 78.64
5,527.43 06/25/14 80.51 78.76
5,527.48 09/25/14 80.46 78.71
5,527.81 12/17/14 80.13 78.38
5,527.71 03/26/15 80.23 78.48
5,527.86 06/22/15 80.08 78.33
5,528.13 09/30/15 79.81 78.06
5,527.92 12/02115 80.02 78.27
5,528.59 03/30/16 79.35 77.60
~
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Depth Below Measuring Point (ft.)
00 "' b 0
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09/14/11
04/01/12
10/18/12
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01/31/16
08/18/16
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 3.48 105
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
91/81/80
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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 3.48 105
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 06/22115 73.11 69.63
5,532.79 09/30/15 73.25 69.77
5,532.34 12/02115 73.70 70.22
5,532.54 03/30/16 73.50 70.02
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Water Levels and Data over Time
White Mesa Mill -Well TW 4-30
Total or
Measurin Measured Total
Water Land g 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 3.48 105
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
91/81/80 ....----.---.-------.--------;,------,------,------,
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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 3.48 105
5,520.17 03/28/13 84.41 80.93
5,520.36 06/27/13 84.22 80.74
5,521.22 09/27113 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 09/30115 80.24 76.76
5,524.29 12/02/15 80.29 76.81
5,525.32 03/30/16 79.26 75 .78
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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 1.64 113
5,564.43 09/27/13 47.41 45.77
5,563.74 12/20113 48.10 46.46
5,563.24 03/27/14 48.60 46.96
5,562.43 06/25114 49.41 47.77
5,561.90 09/25/14 49.94 48.30
5,560.93 12/17114 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
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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 84.7
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 06/25114 70.67 69.14
5,535.73 09/25114 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 09/30115 71.92 70.39
5,534.34 12/02115 72.39 70.86
5,534.33 03/30/16 72.40 70.87
91/SI/80
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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 94
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 06/25114 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
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Water Levels and Data over Time
White Mesa Mill -Well TW 4-35
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,598.67 5,599.87 1.20 85.3
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
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Water Levels and Data over Time
White Mesa Mill -Well TW 4-36
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,615.18 5,616.59 1.41 98
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
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Water Levels and Data over Time
White Mesa Mill -Well TW 4-37
Total or
Measuring Measured
Water Point Depth to Total Depth
Elevation Land Surface Elevation Length Of Date Of Water to Water Total Depth
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Of Well
5,630.13 5,631.85 1.72 112
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
91/01/~0
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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 lW~lS (formerly MW-26)
Total Pumped Total Pumped Total Total Pumped Total Pumped Total
Quarter {gal) Cone (liters) Total (ug) Total (grams) (pounds) (gal) Cone (liters) Total (ug) Total (grams) (pounds)
Q12007 1307110 3370.0 4947411.4 1.667E+10 16673 36.8 930510 1660.0 3521980.4 5.846E+09 5846 12.9
Q2 2007 81230 2000.0 307455.6 614911100 615 1.4 54400 300.0 205904.0 61771200 62 0.1
Q3 2007 100700 2600.0 381149.5 990988700 991 2.2 72080 1400.0 272822.8 381951920 382 0.8
Q4 2007 90830 2300.0 343791.6 790720565 791 1.7 61750 2000.0 233723.8 467447500 467 1.0
Q12008 83950 2400.0 317750.8 762601800 763 1.7 47780 930.0 180847.3 168187989 168 0.4
Q2 2008 62780 2500.0 237622.3 594055750 594 1.3 44840 1300.0 169719.4 220635220 221 0.5
Q3 2008 81400 1800.0 308099.0 554578200 555 1.2 61280 630.0 231944.8 146125224 146 0.3
Q4 2008 91320 1700.0 345646.2 587598540 588 1.3 55700 630.0 210824.5 132819435 133 0.3
Q12009 90710 2200.0 343337.4 755342170 755 1.7 52970 950.0 200491.5 190466878 190 0.4
Q2 2009 450040 1800.0 1703401.4 3.066E+09 3066 6.8 58050 410.0 219719.3 90084893 90 0.2
Q3 2009 90420 2000.0 342239.7 684479400 684 1.5 57610 850.0 218053.9 185345773 185 0.4
Q4 2009 322380 1800.0 1220208.3 2.196E+09 2196 4.8 61960 1100.0 234518.6 257970460 258 0.6
Q12010 68125 1600.0 257853.1 412565000 413 0.9 61320 780.0 232096.2 181035036 181 0.4
Q2 2010 84005.33 2100.0 317960.2 667716366 668 1.5 60500 1900.0 228992.5 435085750 435 1.0
Q3 2010 79859.1 1900.0 302266.7 574306718 574 1.3 63850 2200.0 241672.3 531678950 532 1.2
Q4 2010 90042.2 1500.0 340809.7 511214591 511 1.1 60180 970.0 227781.3 220947861 221 0.5
Q12011 76247.6 1700.0 288597.2 490615182 491 1.1 55130 450.0 208667.1 93900173 94 0.2
Q2 2011 85849.3 1700.0 324939.6 552397321 552 1.2 55800.6 1800.0 211205.3 380169488 380 0.8
Q3 2011 85327.7 1700.0 322965.3 549041086 549 1.2 65618 720.0 248364.1 178822174 179 0.4
Q4 2011 89735.0 1600.0 339647.0 543435160 543 1.2 50191.3 1800.0 189974.1 341953327 342 0.8
Q12012 90376.4 1500.0 342074.7 513112011 513 1.1 31440.1 2400.0 119000.8 285601868 286 0.6
Q2 2012 90916.5 1400.0 344118.8 481766269 482 1.1 26701.2 3000.0 101064.1 303192353 303 0.7
Q3 2012 91607.0 1500.0 346732.5 520098743 520 1.1 25246 3100.0 95556.1 296223941 296 0.7
Q4 2012 78840.0 1300.0 298409.4 387932220 388 0.9 30797 1200.0 116566.6 139879974 140 0.3
Q12013 62943.7 1670.0 238241.9 397863981 398 0.9 22650.7 2120.0 85732.9 181753747 182 0.4
Q2 2013 71187.3 1490.0 269443.9 401471456 401 0.9 25343.4 4030.0 95924.8 386576819 387 0.9
Q3 2013 72898.8 1520.0 275922.0 419401376 419 0.9 25763 2940.0 97513.0 286688088 287 0.6
Q4 2013 70340.4 1410.0 266238.4 375396164 375 0.8 24207.6 1410.0 91625.8 129192330 129 0.3
Q12014 69833.8 1390.0 264320.9 367406097 367 0.8 23263.1 1400.0 88050.8 123271167 123 0.3
Q2 2014 71934.9 1390.0 272273.6 378460299 378 0.8 23757.5 1960.0 89922.1 176247390 176 0.4
Q3 2014 74788.2 1490.0 283073.3 421779272 422 0.9 24062.4 2120.0 91076.2 193081510 193 0.4
Q4 2014 63093.0 1440.0 238807.0 343882087 344 0.8 21875.8 2090.0 82799.9 173051797 173 0.4
Q12015 76454.3 1400.0 289379.5 405131336 405 0.9 24004.9 1980.0 90858.5 179899922 180 0.4
Q2 2015 60714.7 1300.0 229805.1 298746681 299 0.7 27804.6 1980.0 105240.4 208376014 208 0.5
Q3 2015 89520.8 1290.0 338836.2 437098734 437 1.0 21042.0 2350.0 79644.0 187163330 187 0.4
Q4 2015 99633.4 1200.0 377112.4 452534903 453 1.0 19355.6 2680.0 73260.9 196339335 196 0.4
Q12016 90882.1 1240.0 343988.7 426546048 427 0.9 19150.8 2650.0 72485.8 192087312 192 0.4
Totals 4838026.48 87.3 2447985.6 31.2
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-19 TW4-20 I
I
Total Pumped Total Pumped Total Total Pumped Total Pumped Total
Quarter (gal) Cone (liters) Total (ug) Total (grams) (pounds) (gal) Cone (liters) Total (ug) Total (gramst (pounds)
012007 6768986 2660 25620612.0 6.815E+10 68151 150.2 642290 16240 2431067.7 3.948E+10 39481 87.0
02 2007 605400 8 2291439.0 18331512 18 0.0 163520 1800 618923.2 1.114E+09 1114 2.5
03 2007 316080 1100 1196362.8 1.316E+09 1316 2.9 70360 5200 266312.6 1.385E+09 1385 3.1
04 2007 334350 1100 1265514.8 1.392E+09 1392 3.1 63630 9000 240839.6 2.168E+09 2168 4.8
012008 304784 1800 1153607.4 2.076E+09 2076 4.6 66520 13000 251778.2 3.273E+09 3273 7.2
02 2008 380310 1000 1439473.4 1.439E+09 1439 3.2 39360 30000 148977.6 4.469E+09 4469 9.9
03 2008 529020 3600 2002340.7 7.208E+09 7208 15.9 53260 21000 201589.1 4.233E+09 4233 9.3
04 2008 589620 4200 2231711.7 9.373E+09 9373 20.7 50230 1000 190120.6 190120550 190 0.4
012009 469100 1100 1775543.5 1.953E+09 1953 4.3 52050 8200 197009.3 1.615E+09 1615 3.6
02 2009 450040 990 1703401.4 1.686E+09 1686 3.7 49270 6800 186487.0 1.268E+09 1268 2.8
03 2009 200650 6600 759460.3 5.012E+09 5012 11.1 51030 13000 193148.6 2.511E+09 2511 5.5
04 2009 454205 4700 1719165.9 8.08E+09 8080 17.8 208790 15000 790270.2 1.185E+10 11854 26.1
012010 348550 940 1319261.8 1.24E+09 1240 2.7 14490 3500 54844.7 191956275 192 0.4
02 2010 453340 1800 1715891.9 3.089E+09 3089 6.8 39014.86 18000 147671.2 2.658E+09 2658 5.9
03 2010 116899.2 2000 442463.5 884926944 885 2.0 39098.3 15000 147987.1 2.22E+09 2220 4.9
04 2010 767970.5 1200 2906768.3 3.488E+09 3488 7.7 36752.5 24000 139108.2 3.339E+09 3339 7.4
012011 454607.9 3400 1720690.9 5.85E+09 5850 12.9 37187.5 31000 140754.7 4.363E+09 4363 9.6
02 2011 159238.9 4000 602719.2 2.411E+09 2411 5.3 67907.7 8100 257030.6 2.082E+09 2082 4.6
03 2011 141542.6 970 535738.7 519666579 520 1.1 72311.2 6800 273697.9 1.861E+09 1861 4.1
04 2011 147647.2 2200 558844.7 1.229E+09 1229 2.7 72089.3 7900 272858.0 2.156E+09 2156 4.8
012012 148747 650 563007.4 365954807 366 0.8 76306 11000 288818.2 3.177E+09 3177 7.0
02 2012 172082.03 460 651330.5 299612022 300 0.7 22956.43 36000 86890.1 3.128E+09 3128 6.9
03 2012 171345 950 648540.8 616113784 616 1.4 22025 13000 83364.6 1.084E+09 1084 2.4
04 2012 156653 1500 592931.6 889397408 889 2.0 20114 19000 76131.5 1.446E+09 1446 3.2
012013 210908 4210 798286.8 3.361E+09 3361 7.4 18177 18500 68799.9 1.273E+09 1273 2.8
02 2013 226224 2070 856257.8 1.772E+09 1772 3.9 20252.4 26300 76655.3 2.016E+09 2016 4.4
03 2013 329460.1 8100 1247006.5 1.01E+10 10101 22.3 19731 26800 74681.8 2.001E+09 2001 4.4
04 2013 403974 942 1529041.6 1.44E+09 1440 3.2 19280.2 15700 72975.6 1.146E+09 1146 2.5
012014 304851 586 1153861.0 676162567 676 1.5 18781.6 17800 71088.4 1.265E+09 1265 2.8
02 2014 297660.0 810 1126643.1 912580911 913 2.0 18462.4 22100 69880.2 1.544E+09 1544 3.4
03 2014 309742.0 1410 1172373.5 1.653E+09 1653 3.6 17237.9 12400 65245.5 809043599 809 1.8
04 2014 198331.0 4310 750682.8 3.235E+09 3235 7.1 16341.8 23300 61853.7 1.441E+09 1441 3.2
012015 60553.0 4660 229193.1 1.068E+09 1068 2.4 15744.7 19900 59593.7 1.186E+09 1186 2.6
02 2015 75102.8 1570 284264.1 446294634 446 1.0 18754.1 17600 70984.3 1.249E+09 1249 2.8
03 2015 116503.9 7860 440967.3 3.466E+09 3466 7.6 17657.3 17000 66832.9 1.136E+09 1136 2.5
04 2015 112762.7 7840 426806.8 3.346E+09 3346 7.4 15547.4 17000 58846.9 1E+09 1000 2.2
012016 116597.0 7780 441319.6 3.433E+09 3433 7.6 14353.5 21600 54328.0 1.173E+09 1173 2.6 - -------·-
Totals 17403837.83 360.5 2260884.09 261.3
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-4 TW4-22
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Q12007 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
Q12008 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
Q12009 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
Q12010 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2010 84513.9 2000.0 319885.1 6.4E+08 640 1.4 NA NA NA NA NA NA
Q3 2010 76916.8 2100.0 291130.1 6.1E+08 611 1.3 NA NA NA NA NA NA
Q4 2010 86872.1 1700.0 328810.9 5.6E+08 559 1.2 NA NA NA NA NA NA
Q12011 73360.0 1800.0 277667.6 5.0E+08 500 1.1 NA NA NA NA NA NA
Q2 2011 80334.6 1700.0 304066.5 5.2E+08 517 1.1 NA NA NA NA NA NA
Q3 2011 97535.0 1500.0 369170.0 5.5E+08 554 1.2 NA NA NA NA NA NA
Q4 2011 109043.5 1500.0 412729.6 6.2E+08 619 1.4 NA NA NA NA NA NA
Q12012 101616.8 1200.0 384619.6 4.6E+08 462 1.0 NA NA NA NA NA NA
Q2 2012 87759.1 1500.0 332168.2 5.0E+08 498 1.1 NA NA NA NA NA NA
Q3 2012 80006.0 1600.0 302822.7 4.8E+08 485 1.1 NA NA NA NA NA NA
Q4 2012 71596 1400.0 270990.9 3.8E+08 379 0.8 NA NA NA NA NA NA
Q12013 58716.8 1460.0 222243.1 3.2E+08 324 0.7 16677.4 10600.0 63124.0 669113965.4 669.1 1.5
Q2 2013 65603.4 1330.0 248308.9 3.3E+08 330 0.7 25523.2 12500.0 96605.3 1207566400.0 1207.6 2.7
Q3 2013 63515.4 1380.0 240405.8 3.3E+08 332 0.7 25592.9 9640.0 96869.1 933818379.5 933.8 2.1
Q4 2013 60233.6 1360.0 227984.2 3.1E+08 310 0.7 24952.2 13300.0 94444.1 1256106224.1 1256.1 2.8
Q12014 58992.9 1260.0 223288.1 2.8E+08 281 0.6 24532.0 12100.0 92853.6 1123528802.0 1123.5 2.5
Q2 2014 60235.3 1220.0 227990.6 2.8E+08 278 0.6 24193.9 12400.0 91573.9 1135516502.6 1135.5 2.5
Q3 2014 69229.4 1320.0 262033.3 3.5E+08 346 0.8 24610.9 12400.0 93152.3 1155087980.6 1155.1 2.5
Q4 2014 64422.6 1130.0 243839.5 2.8E+08 276 0.6 23956.9 12400.0 90676.9 1124393144.6 1124.4 2.5
Q12015 36941.3 1350.0 139822.8 1.9E+08 189 0.4 22046.9 12700.0 83447.5 1059783459.6 1059.8 2.3
Q2 2015 68162.8 1280.0 257996.2 3.3E+08 330 0.7 23191.6 8050.0 87780.2 706630658.3 706.6 1.6
Q3 2015 64333.0 1220.0 243500.4 3.0E+08 297 0.7 24619.9 7810.0 93186.3 727785170.9 727.8 1.6
Q4 2015 59235.1 1190.0 224204.9 2.7E+08 267 0.6 23657.6 7530.0 89544.0 674266440.5 674.3 1.5
Q12016 57274.0 1190.0 216782.1 2.6E+08 258 0.6 24517.8 6070.0 92799.9 563295229.1 563.3 1.2
Totals 1736449.4 21.3 308073.2 27.2
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)
012007 NA NA NA NA NA NA NA NA NA NA NA NA
02 2007 NA NA NA NA NA NA NA NA NA NA NA NA
03 2007 NA NA NA NA NA NA NA NA NA NA NA NA
04 2007 NA NA NA NA NA NA NA NA NA NA NA NA
012008 NA NA NA NA NA NA NA NA NA NA NA NA
02 2008 NA NA NA NA NA NA NA NA NA NA NA NA
03 2008 NA NA NA NA NA NA NA NA NA NA NA NA
04 2008 NA NA NA NA NA NA NA NA NA NA NA NA
012009 NA NA NA NA NA NA NA NA NA NA NA NA
02 2009 NA NA NA NA NA NA NA NA NA NA NA NA
03 2009 NA NA NA NA NA NA NA NA NA NA NA NA
04 2009 NA NA NA NA NA NA NA NA NA NA NA NA
012010 NA NA NA NA NA NA NA NA NA NA NA NA
02 2010 NA NA NA NA NA NA NA NA NA NA NA NA
03 2010 NA NA NA NA NA NA NA NA NA NA NA NA
04 2010 NA NA NA NA NA NA NA NA NA NA NA NA
012011 NA NA NA NA NA NA NA NA NA NA NA NA
02 2011 NA NA NA NA NA NA NA NA NA NA NA NA
03 2011 NA NA NA NA NA NA NA NA NA NA NA NA
04 2011 NA NA NA NA NA NA NA NA NA NA NA NA
012012 NA NA NA NA NA NA NA NA NA NA NA NA
02 2012 NA NA NA NA NA NA NA NA NA NA NA NA
03 2012 NA NA NA NA NA NA NA NA NA NA NA NA
04 2012 NA NA NA NA NA NA NA NA NA NA NA NA
012013 144842.6 5.7 548229.2 3124906.7 3.1 0.0 99369.9 0.0 376115.1 0.0 0.0 0.0
02 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
03 2013 267703.5 21.8 1013257.7 22089018.9 22.1 0.1 145840.9 0.0 552007.8 0.0 0.0 0.0
04 2013 260555.3 32.5 986201.8 32051558.8 32.1 0.1 126576.5 0.0 479092.1 0.0 0.0 0.0
012014 229063.9 78.5 867006.9 68060038.6 68.1 0.2 129979.2 0.0 491971.3 0.0 0.0 0.0
02 2014 216984.1 62.7 821284.8 51494558.1 51.5 0.1 124829.8 0.0 472480.8 0.0 0.0 0.0
03 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
04 2014 178468.7 25.8 675504.0 17428004.0 17.4 0.04 107416.1 0.0 406569.9 0.0 0.0 0.0
012015 92449.3 49.2 349920.6 17216093.5 17.2 0.04 71452.4 0.0 270447.3 0.0 0.0 0.0
02 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
03 2015 66313.2 46.90 250995.5 11771687.2 11.8 0.026 124137.1 0.0 469858.9 0.0 0.0 0.0
04 2015 107799.1 25.30 408019.6 10322895.7 10.3 0.023 116420.1 0.0 440650.1 0.0 0.0 0.0
012016 100063.2 22.80 378739.2 8635254.0 8.6 0.019 115483.2 0.0 437103.9 0.0 0.0 0.0
Totals 2128068.9 0.75 1520464.8 0.0
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-01 TW4-02
Total Total Total Total
Pumped Pumped Total Total Pumped Pumpad Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
Q12007 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
Q12008 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
Q12009 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
Q12010 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
Q12011 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q12012 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
Q12013 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
Q12014 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
Q12015 24569.2 1130.0 92994.4 105083696.9 105.1 0.23 24156.7 1840.0 91433.1 168236921.5 168.2 0.37
Q2 2015 23989.9 1260.0 90801.8 114410232.1 114.4 0.25 22029.9 1650.0 83383.2 137582233.0 137.6 0.30
Q3 2015 23652.0 1060.0 89522.8 94894189.2 94.9 0.21 21586.9 1310.0 81706.4 107035405.6 107.0 0.24
Q4 2015 20764.3 1040.0 78592.9 81736590.5 81.7 0.18 21769.8 2070.0 82398.7 170565294.5 170.6 0.38
Q12016 19255.6 974.0 72882.4 70987502.4 71.0 0.16 20944.6 1970.0 79275.3 156172362.7 156.2 0.34
Totals un3l.o 1.03 110487.9 1.6
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)
Q12007 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
Q12008 NA NA NA NA NA NA NA NA NA NA NA NA I
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 !
Q12009 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
Q12010 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
Q42010 NA NA NA NA NA NA NA NA NA NA NA NA
Q12011 NA NA NA NA NA NA NA NA NA NA NA NA
Q2 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q3 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q4 2011 NA NA NA NA NA NA NA NA NA NA NA NA
Q12012 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
Q12013 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
Q12014 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
Q12015 9898.7 2450.0 37466.6 91793119.8 91.8 0.20 NA NA NA NA NA NA
Q2 2015 5243.3 2710.0 19845.9 53782363.3 53.8 0.12 30743.7 366.0 116364.9 42589555.0 42.6 0.09
Q3 2015 3584.4 1120.0 13567.0 15194988.5 15.2 0.03 125285.4 281.0 474205.2 133251672.2 133.3 0.29
Q4 2015 4110.3 2730.0 15557.5 42471935.4 42.5 0.09 134774.9 339.0 510123.0 172931695.8 172.9 0.38
Q12016 3676.2 266Q.Cl_ 13914.4 37012349.2 37.0 0.08 125513.3 390.0 475067.8 185276457.8 185.3 0.41 -
Totals 26512.9 0.53 416317.3 1.18
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
1W4-37
'
Total Total Total Volume
Pumped Pumped Total Total Total Pumped
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (pounds) (gallons)
Q12007 NA NA NA NA NA NA 286.9 9648896.0
Q2 2007 NA NA NA NA NA NA 4.0 904550.0
Q3 2007 NA NA NA NA NA NA 9.0 559220.0
Q4 2007 NA NA NA NA NA NA 10.6 550560.0
Q12008 NA NA NA NA NA NA 13.8 503034.0
Q2 2008 NA NA NA NA NA NA 14.8 527290.0
Q3 2008 NA NA NA NA NA NA 26.8 724960.0
Q4 2008 NA NA NA NA NA NA 22.7 786870.0
Q12009 NA NA NA NA NA NA 10.0 664830.0
Q2 2009 NA NA NA NA NA NA 13.5 1007400.0
Q3 2009 NA NA NA NA NA NA 18.5 399710.0
Q4 2009 NA NA NA NA NA NA 49.4 1047335.0
Q12010 NA NA NA NA NA NA 4.5 492485.0
Q2 2010 NA NA NA NA NA NA 16.5 721374.1
Q3 2010 NA NA NA NA NA NA 10.6 376623.4
Q4 2010 NA NA NA NA NA NA 17.9 1041817.3
Q12011 NA NA NA NA NA NA 24.9 696533.0
Q2 2011 NA NA NA NA NA NA 13.1 449131.1
Q3 2011 NA NA NA NA NA NA 8.1 462334.5
Q4 2011 NA NA NA NA NA NA 10.8 468706.3
Q12012 NA NA NA NA NA NA 10.6 448486.3
Q2 2012 NA NA NA NA NA NA 10.4 400415.2
Q3 2012 NA NA NA NA NA NA 6.6 390229.0
Q4 2012 NA NA NA NA NA NA 7.1 358000.0
012013 NA NA NA NA NA NA 13.7 634286.1
Q2 2013 NA NA NA NA NA NA 13.5 768953.4
Q3 2013 NA NA NA NA NA NA 31.1 950505.6
Q4 2013 NA NA NA NA NA NA 10.3 990119.8
Q12014 NA NA NA NA NA NA 8.6 859297.5
Q2 2014 NA NA NA NA NA NA 9.9 838057.9
Q3 2014 NA NA NA NA NA NA 10.2 852987.2
Q4 2014 NA NA NA NA NA NA 14.6 673905.9
Q12015 NA NA NA NA NA NA 9.9 458271.4
Q2 2015 29206.0 30200.0 110544.7 3338450242.0 3338.5 7.4 15.3 539592.9
Q3 2015 118063.9 19100.0 446871.9 8535252554.7 8535.3 18.8 33.4 816299.8
Q4 2015 111737.5 19500.0 422926.4 8247065531.3 8247.1 18.2 32.3 847567.8
Q12016 111591.0 17500.0 422371.9 7391508862.5 7391.5 16.3 30.6 819302.3
Totals 370598.4 60.7 854.5 33679937.8
Table G-2
Chloroform Mass Removal Per Well Per Quarter
TW4-15
MW-4 (MW-26) TW4-19 TW4-20 TW4-4 TW4-22 TW4-24 TW4-25 TW4-0l TW4-02 TW4-ll TW4-21 TW4-37 Quarter
Quartet'*" (lbs.) (lbs.) Qbs.) (lbs.} (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) Totals (lbs.)
Ql 2007 36.8 12.9 150.2 87.0 NA NA NA NA NA NA NA NA NA 286.9
Q2 2007 1.4 0.1 0.0 2.5 NA NA NA NA NA NA NA NA NA 4.0
Q3 2007 2.2 0.8 2.9 3.1 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 10.6
Ql 2008 1.7 0.4 4.6 7.2 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 14.8
Q3 2008 1.2 0.3 15.9 9.3 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 22.7
Q1 2009 1.7 0.4 4.3 3.6 NA NA NA NA NA NA NA NA NA 10.0
02 2009 6.8 0.2 3.7 2.8 NA NA NA NA NA NA NA NA NA 13.5
Q3 2009 1.5 0.4 11.1 5.5 NA NA NA NA NA NA NA NA NA 18.5
Q4 2009 4.8 0.6 17.8 26.1 NA NA NA NA NA NA NA NA NA 49.4
Q1 2010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA 4.5
Q2 2010 1.5 1.0 6.8 5.9 1.4 NA NA NA NA NA NA NA NA 16.5
Q3 2010 1.3 1.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA 10.6
Q4 2010 1.1 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA 17.9
Q1 2011 1.1 0.2 12.9 9.6 !.1 NA NA NA NA NA NA NA NA 24.9
Q2 2011 1.2 0.8 5.3 4.6 1.1 NA NA NA NA NA NA NA NA 13.1
Q32011 1.2 0.4 1.1 4.1 1.2 NA NA NA NA NA NA NA NA 8.1
Q4 2011 1.2 0.8 2.7 4.8 1.4 NA NA NA NA NA NA NA NA 10.8
Q1 2012 1.1 0.6 0.8 7.0 1.0 NA NA NA NA NA NA NA NA 10.6
Q2 2012 1.1 0.7 0.7 6.9 1.1 NA NA NA NA NA NA NA NA 10.4
Q3 2012 1.1 0.7 1.4 2.4 1.1 NA NA NA NA NA NA NA NA 6.6
Q4 2012 0.9 0.3 2.0 3.2 0.8 NA NA NA NA NA NA NA NA 7.2
Q1 2013 0.9 0.4 7.4 2.8 0.7 1.5 0.0 0.0 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 13.5
Q3 2013 0.9 0.6 22.3 4.4 0.7 2.1 0.1 0.0 NA NA NA NA NA 3!.1
Q4 2013 0.8 0.3 3.2 2.5 0.7 2.8 0.1 0.0 NA NA NA NA NA 10.3
Ql2014 0.8 0.3 1.5 2.8 0.6 2.5 0.2 0.0 NA NA NA NA NA 8.6
Q2 2014 0.8 0.4 2.0 3.4 0.6 2.5 0.1 0.0 NA NA NA NA NA 9.9
Q3 2014 0.9 0.4 3.6 1.8 0.8 2.5 0.1 0.0 NA NA NA NA NA 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 14.6
Q1 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 9.9
Q2 2015 0.7 0.5 1.0 2.8 0.7 1.6 0.00 0.0 0.25 0.30 0.12 0.09 7.4 15.3
Q3 2015 1.0 0.4 7.6 2.5 0.7 1.6 0.03 0.0 0.21 0.24 0.03 0.29 18.8 33.4
Q4 2015 1.0 0.4 7.4 2.2 0.6 1.5 0.02 0.0 0.18 0.38 0.09 0.38 18.2 32.3
Q1 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 30.6
Well Totals 87.3 31.2 360.5 261.3 21.3 27.2 0.75 0.00 1.03 1.63 0.53 1.!8 60.7 854.5
* Ql 2007 represents the cumulative total prior to and including Ql 2007.
Table G-3 Well Pumping Rates and Volumes
Volume of Water Pumped
Pumping Well N arne During the Quarter (gals) Average Pump Rate (gpm)
MW-4 90,882.1 4.5
MW-26 19,150.8 8.2
TW4-4 57,274.0 11.1
TW4-19 116,597.0 18.1
TW4-20 14,353.5 6.2
TW4-22 24,517.8 17.5
TW4-24 100,063.2 15.9
TW4-25 115,483.2 14.8
TWN-2 47,670.2 18.6
TW4-01 19,255.6 15.8
TW4-02 20,944.6 16.8
TW4-ll 3,676.2 16.3
TW4-21 125,513.3 16.3
TW4-37 111,591.0 17.0
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Laboratory Analytical Reports
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: lst Quarter Chloroform 2016
Lab Sample ID: 1603259-006C
Client Sample ID: MW-04_03092016
Collection Date: 3/9/2016 1210h
Received Date: 3/1112016 1030h
Analytical Results
Analyzed: 3/14/2016 1854h
Units: Jlg/L
Compound
Chloroform
Dilution Factor: 20
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 1,240
Surrogate 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
1,050
1,030
1,010
1,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1345h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4 17060-07-0 51.6
Surr: 4-Bromofluorobenzene 460-00-4 51.1
Surr: Dibromofluoromethane 1868-53-7 48.6
Surr: Toluene-d8 2037-26-5 49.9
1,000 105 72-151
1,000 103 80-152
1,000 101 80-124
1,000 101 77-129
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 103 72-151
50.00 102 80-152
50.00 97.1 80-124
50.00 99.9 77-129
Report Date: 3/28/2016 Page II of 40
All anal) ses applicoble to the CWA SDWA. and RCRA are performed in A.Ccordance to NELAC protocols Pertinent sampling iMornuuion is located on the altached COC Confidential Business Information: This report is provided ror the exclusi\·e use or the ~ddressee Pri\ ile~es or sub .. seq~ent ~~e oft he ~~e or this .cm~pany or an~ r~~mbel of its slnrf, or reproducli~ ~fthis repo~ in ~Oil~eclion,. \\·illl the D~\ ertisement P~?motio.n ~r sale of ?J!~ ~rod~ct or Pl.ocess, ~r in :onn:c~ion "!lh th~ r:·publicntion of this leporl
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-006
Client Sample ID: MW-04_03092016
lAaoRATOR I Es Collection Date: 3/9/2016 1210h
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: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/16/2016 2122h E300.0 10.0 42.2
3/12/2016 ]]J8h E353.2 0.100 5.15
Report Date: 3/28/2016 Page 25 of 40
All analyses applicnble to the CWA, SDWA, and RCRA are perl'om1ed in accordwtce to NELAC protocols Pertinent sampling information is located on the atlached COC Confidential Business Information: This report is pro\'ided fort he exclusi\e use of the
~ddressee p.;, ile~es o_f sub .. seq~ent ~·~e of the ~~~e of this .co•~ pan~ or nn~ 1~mbe1 of its starr. or reproductio~ ~f this repo~ in ~on~ection,_ "ith the a<!ver1isemenl, P~?molio.n ~r sale of~~~ ~rod1~L or PJ.ocess, ~r in ~onn:c~ion "!Lh 1h7 r~·publicntion of lhis report
American West ANALYTICAL LADORATORI~S
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 2016
Lab Sample ID: 1603259-004C
Client Sample ID: TW4-01_03092016
Collection Date: 3/9/2016 1217h
Received Date: 3/ll/2016 1030h
Analytical Results
Analyzed: 3114/2016 173 5h
Units: J.lg/L Dilution Factor: 20
Compound
Chloroform
Surrogate
Surr: 1,2-Dich1oroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
1,050
1,030
1,020
995
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1305h
Units: J.lg/L Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 974
Amount Spiked %REC Limits Qual
1,000 105 72-151
1,000 103 80-152
1,000 102 80-124
1,000 99.5 77-129
Method: SW8260C
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 CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 52.4 50.00 105 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.3 50.00 103 80-152
Surr: Dibromofluoromethane 1868-53-7 48.2 50.00 96.4 80-124
Surr: Toluene-d8 2037-26-5 50.2 50.00 100 77-129
Report Date: 3/28/2016 Page 9 of 40
All annlyses applicable to the CWA. SDWA. and RCRA rue perfom1ed in accordance 10 NELAC prolocols Per1inenl sampling information is located ou the nUached COC Conlidentinl Business Information: This repor1 is pro,•ided for the exclusi,-e use oflhe
~ddressee Pri' ile~es o,r sub .. seq~ent ~1;e or the ~~e or this .c01~puny or nny ~~~r:nbe1 or its starr, or reproductio~ ~~I his repo~ in ~on~1ection~ ''ilh I he a~vertisement, P~?motio.n or saJe of :-u~Y ~rodL~cl or p1.ocess, ~r in c;onm;c!ion w!lh th~ n;-publication or this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-004
Client Sample ID: TW4-01_03092016
Collection Date: 3/9/2016 1217h
Received Date: 3/1112016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 2048h
3/23/2016 1642h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 41.7
E353.2 0.100 0.148
Report Date: 3/28/2016 Page 23 of 40
All anal~ ses applic~ble to the CWA. SDWA. and RCRA rue performed in accordance lo NELAC protocols Pertinent sampling information is locnted on the auached COC Conridentlnl Business lnformalion: This report is pro\'ided for the exclusive use of the
~ddressee Prh ile~es o,r sub .. seq~enl ~~e of the ~~e of this .cot~pany or any J~mber of its stnfT, or reproductio~ ~~this repo~ in ~o~eclion ... "ilh the U~\'CiiisemenL P~?motio.n ~· sale of~!) ~rod~cl or pt:ocess, ~r in ~onm;_c~ion w~lh 1h~ n;-publicalion of this 1epon
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 2016
Lab Sample ID: 1603259-007C
Client Sample ID: TW4-02_03092016
Collection Date: 3/9/2016 1201h
Received Date: 3/1112016 1030h
Analytical Results
Analyzed: 3/14/2016 1913h
Units: 1-1g/L
Compound
Chloroform
Dilution Factor: 20
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 1,970
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: To1uene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,050
1,030
1,000
1,010
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1404h
Units: llg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 51.8
Surr: 4-Bromofluorobenzene 460-00-4 51.4
Surr: Dibromofluoromethane 1868-53-7 48.9
Surr: Toluene-d8 2037-26-5 49.6
1,000 105 72-151
1,000 103 80-152
1,000 100 80-124
1,000 101 77-129
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 1.20
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 104 72-151
50.00 103 80-152
50.00 97.8 80-124
50.00 99.2 77-129
Report Date: 3/28/20 16 Page 12 of 40
All nnal~ ses apj)licable to the CWA, SDWA. and RCRA are perfom1ed in accordance to NELAC protocols, Pertinent sampling infonnalion is located on the a11ached COC Conlid~ntial Business lnformalion: This report is pro\·ided for the e.xclusi\e use of the
~ddressee Pri' ile~es o_f su~seq~ten1 ~~e of the ~~e of this .cot~pan~ or nny '~'."bet of its staff, or reproducti~ ~~this repo~ in ~~ection~ \\ilh lhe a~vertisement, p~~motio_n or saJe of~) ~rod~\ or pt.ocess, ~r in ~onm;c~ion w!th th~ r~-p~blication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-007
Client Sample ID: TW4-02_03092016
Collection Date: 3/9/2016 120lh
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 2139h
3/12/2016 1119h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 43.4
E353.2 0.100 5.30
Report Date: 3/28/2016 Page 26 of 40
All nnulyses applicable to the CWA, SDWA, Md RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on Lhe altached COC Confidential Business lnformation: 1l1is report is pro,•ided for the e..xclusi\ e use of the
~ddressee pfi,·ile~es o,r su~seq~ent ~e of the ~~e of this .co~pm1y or any ~mber of its Sl:lff, or reproductio~ ~f this repo~ in ~oR?eclion .. with the ~vertisernent P~?motio;n ~r sale of :U~) ~rodt~ct or p~ocess, ~r in ~nn~!ion '''!th th? r~-publica1ion of 1his repor1
3440 South 700 West
;aJt 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 2016
Lab Sample ID: 1603400-002C
Client Sample ID: TW4-03_03152016
Collection Date: 3/15/2016 639h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1345h
Units: ~giL
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
49.0 50.00 98.0 72-151
51.4 50.00 103 80-152
49.0 50.00 98.1 80-124
50.7 50.00 101 77-129
Report Date: 4/11120 16 Page 31 of 62
All an<~lyses applicable to the CWA~ SOW A. and RCRA are perforn1ed in accordance to NELAC protocols. Pertinent sampling information is locnted on the au ached COC Conlidentio.l Business Information: This report is pro"ided for the exclush e use of the ~ddressee, Pri,ile~es o.r sub_:;eq~enl ~~e of the ~~e of this .co~pany or an) ~mber of its stnfT, or reproductio~~ ~[this repo~ in ~on~1eclion~ with the n~vertisement, P~?motio.n ~r sa1e of ?J!~. ~rodt~ct or p~ocess, ~r in ~onn~c~ion w~th th~ n;-publication of this repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-002
Client Sample ID: TW4-03_03152016
Collection Date: 3/15/2016 639h
Received Date: 3118/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
312 3/2016 l309h
3/24/2016 1609h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
EJOO.O 10.0 32.8
E353 .2 0.100 5.83
Report Date: 4/11/2016 Page 8 of62
All unal)ses applicable to lhe CWA, SDWA. and RCRA are perfom1ed in accordance to NELAC protocols~ Pertinent sampling information is located on the atlached COC Confidential Business lnfonnalion: This report is provided for the exclusi,-e use of the
~ddressee P1i\ ile~es o_fsub,.seq~enl ~~e oflhe ~~e oflhis .con:pnny or an~·1~mbe1 of its st..Uf, or reproductio~ ~~lhis repo~ in ~n~eclion,. with the v~ver1isemenL, P~?motio.n o.r ~ale of~ ~rod~ct or P~?cess, ~r in ~nm;c~ion "!lh th~ r~-p~blicalion of I his repon
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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-00IC
Client Sample ID: TW4-03R_03142016
Collection Date: 3/14/2016 1329h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1325h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
48.2
52.6
49.1
50.3
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 96.3 72-151
50.00 105 80-152
50.00 98.3 80-124
50.00 101 77-129
Report Date: 4/11/2016 Page 30 of62
All anal) ses applico.ble to lhe CWA_ SOW A. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is locnted 011 Lhe aU ached COC Confidenrial Business Information: This report is pro\'ided for the exclusi\'e use of the
~ddrcssee Pri\ ile~es orsub ... seq~enl ~~e of the ~~e oflhis.cor~pany or an) ~~~ber ofilS stnff, or reproductio~ ~fthis repo~ in ~on~ection~ \\"ilh Lhe o~vertisemenl, P~?motio.n or sale or ?J!Y ~rodl~Cl or P•,?cess, ~r in ~onm;_c~ion "!Lh th~ r~-publication or this l"t!pOrl
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 2016
Lab Sample ID: 1603400-001
Client Sample ID: TW4-03R_03142016
Collection Date: 3/14/2016 1329h
Received Date: 3118/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/23/2016 2316h
3/24/2016 1606h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 4/11/2016 Page 7 of62
All Wlnlyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols_ Pertinent sampling information is located on the au ached COC Confidential Business lnfonmuion: This report is provided for the exclusi\e use of the
~ddressee P1i\ ile~es o.fsub ... seq~ent ~~e of the ~~e of this .co1~pany or nny 1~mbe1 of its starr, or reproductio~ ~f this repo~ in .con~Jection ... with the a~vertisement, ~~?motio.n or sale of :U!' ~rodL~ct or p~~ess, ~r in ~nn~c~ion '''!lh lh~ n;_-publicaJ.ion of this report
American West ANALYTICAL LABORATORIES
3440 South 700 West
;a It Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-00SC
Client Sample ID: TW4-04_03092016
Collection Date: 3/9/2016 1225h
Received Date: 3/11/2016 1030h
Analytical Results
Analyzed: 3/14/2016 1834h
Units: Jlg/L
Compound
Chloroform
Dilution Factor: 20
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
1,050
1,030
1,010
997
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1325h
Units: Jlg/L Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 20.0 1,190
Amount Spiked %REC Limits Qual
1,000 105 72-151
1,000 103 80-152
1,000 101 80-124
1,000 99.7 77-129
Method: SW8260C
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 CAS Result Amount Spiked %REC 'Limits Qual
Surr: I ,2-Dich1oroethane-d4 17060-07-0 52.0 50.00 104 72-151
Surr: 4-Bromotluorobenzene 460-00-4 51.8 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 49.3 50.00 98.7 80-124
Surr: To1uene-d8 2037-26-5 50.6 50.00 101 77-129
Report Date: 3/28/2016 Page I 0 of 40
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordMce to NELAC protocols Pertinent sampling information is located on lhe altached COC ConfidentiDI Business Information: This repon is provided for the exclushe use of the
~ddressee Pri\ ile~es o.r sub~seq~enl ~~e or the ~~e of I his .con;.pany or M) ~:mber of its staff, or reproductio~ ~rthis repo~ in .con~1ec1ion~ \\~Lh the a~ver1isement, P~?motio.n or sale of :u;~ ~rod~cl or p1:ocess, ~r in :onn:_c~ion w~th th~ r~·publication of this report
3440 South 700 West
;;att 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 Chlorofonn 2016
Lab Sample ID: 1603259-005
Client Sample ID: TW4-04_03092016
Collection Date: 3/9/2016 1225h
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 2105h
3/12/2016 1117h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 39.7
E353.2 0.100 6.71
Report Date: 3/28/2016 Page 24 of 40
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordtmce to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusi'e use of the
~ddressee Pri\ ile~es or sub .. seq~enl ~~e of the ~~e of this .co~p:my or nn~ ·~mber of ils stnff. or reproductio~ ~f this repo~ ill ~OI~lection~ \\ilh the 11~\·ertisemenl. P~?motio.n or sale of~!~ ~rod~t::l or P•.ocess, ~r in ~onm~c~ion W!lh lh~ n;-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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-016C
Client Sample ID: TW4-05_03172016
Collection Date: 3/17/2016 804h
Received Date: 3118/2016 1 040h
Analytical Results
Analyzed: 3/18/2016 1922h
Units: !!g/L Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
56-23-5
67-66-3
74-87-3
75-09-2
Result Amount Spiked
50.3 50.00
51.9 50.00
48.6 50.00
50.6 50.00
1.00 < 1.00
1.00 11.0
1.00 < 1.00
1.00 < 1.00
%REC Limits Qual
101 72-151
104 80-152
97.2 80-124
101 77-129
ReportDate: 4/ll/2016 Page45of62
All analyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinenl sampling information is loculed on the attached COC. Confidential Business lnfonnalion: This report is provided for the exclusi,·e use of the
~ddressee, Pri\ ile~es o.fsub~seq~ent ~~e of the ~~e of this .co1~pany or rul) 1!!.7mbe1 of its sl:-tff, or reproduclio~ ~f this repo~ in .co~Jeclion,.. \Vilh the ll~\'er1isemenl, P~?moli~n <:r sale of?J!Y ~IOdl~ct or p1_ocess, ~r in ~onn~c~ion \\'~lh 1h~ r~-publication of this report
3440 South 700 West
:lalt 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.
I st Quarter Chloroform 2016
1603400-016
ClientSampleiD: TW4-05 03172016
Collection Date: 3/17/2016 804h
Received Date: 3/18/2016 I 040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 123h
3/24/2016 1646h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 44.7
E353.2 0.100 10.2
Report Date: 4/11/2016 Page 22 of62
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling iniOrma.tion is locoted on lhe atta.ched COC Confidenriol Business Information: This repor1 is pro,•ided for I he exclusi\ e use of the
~ddressee Pri,·ile~es o:sub ... seq~.enl ~e of the ~~e of this.col~pany or any ~mber of its staff, or reproducti~ ~fthis repo~ in ~ection ... wilh lhe tu!'·ertisemenl P~?moli~ ~r sa1e of:u!)~~rodl~ct or p~ocess, ~r in ~onn~c.lion w~th th~ r~-p~blicalion of this report
American West ANALYTICAL LABORATORIES
3440 South 700 West
;a It 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 2016
Lab Sample ID: 1603479-003C
Client Sample ID: TW4-06_03222016
Collection Date: 3/22/2016 851h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1633h
Units: Jlg/L Dilution Factor:
Compound
Chloroform
Surrogate
Surr: 1,2-Dich1oroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
10
Result
482
526
510
519
--The reporting limits were raised due to high ana lyle concentrations.
Analyzed: 3/23/2016 1340h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dich1oroethane-d4 17060-07-0 50.6
Surr: 4-Bromofluorobenzene 460-00-4 53.1
Surr: Dibromofluoromethane 1868-53-7 50.3
Surr: To1uene-d8 2037-26-5 51.1
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 834
Amount Spiked %REC Limits Qual
500.0 96.3 72-151
500.0 105 80-152
500.0 102 80-124
500.0 104 77-129
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 101 72-151
50.00 106 80-152
50.00 101 80-124
50.00 102 77-129
Report Date: 3/30/2016 Page 7 of27
All o.nalyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the allached COC Confidential Business Information: This repon is provided for 1he e:\:clusin' use oft he ~ddressee P1i' ile~es o,r sub .. seq~ent ~~e of the ~:u:ne of this .co1~p<U1~ or M~' J~mber of its staff, or reproductio~ ~~this repo~ in ~on~1ection ... \\ith the a~~ ertise•"!1ent, P~?motio,n ~r· sale of ?J!Y ~rod~ct or pt:?Cess, ~r in ~onn~c~ion w~th th~ r~·publicalion of I his t13pOrt
3440 South 700 West
)alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603479-003
Client Sample ID: TW4-06_03222016
Collection Date: 3/22/2016 85lh
Received Date: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 93lh
3/24/2016 1722h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 42.3
E353.2 0.100 6.79
Report Date: 3/30/2016 Page 15 of27
All amllyses npplict~ble to the CWA, SOWA. and RCRA are perrom1ed in accordance to NELAC protocols Pertinent sampling informal ion is located on lhe aUached COC Confrdentinl Business lnrormation: This reporl is prO\'ided for the e.\clusi\ e use of the
~ddressee, Pri\"ile~es o[sub .. seq~ent ~~~e of the ~~e of this .coJ~pany or an~· ~mbe1 of its still. or reproduclio~ ~fthis repo~ in .co~ection .. with the a~~ertisement P~?motio_n ~r sale of~!~ ~rodt~cl or p1.ocess, ~r in ~onn:c~ion w~lh lh~ n;_-publicalion of 1his report
American West ANAlYTICAL LABORATORI[8
3440 South 700 West
;aJt Lake City, UT 84II9
Phone:(80I)263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laborat01y Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: I st Quarter Chloroform 2016
Lab Sample ID: 1603479-001C
Client Sample ID: TW4-06R_032120I6
Collection Date: 3/21/2016 1034h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1301h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 48.2
460-00-4 53.3
1868-53-7 50.0
2037-26-5 51.9
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 96.3 72-151
50.00 107 80-152
50.00 100 80-124
50.00 104 77-129
Report Date: 3/30/2016 Page 5 of 27
All analyses applicable to the CWA. SDWA. Md RCRA are I'Jerl'ormerl in accordance to NELAC protocols Pertinent sampling information is located on the aU~ched COC Confidential Business lnfonnntion: This report is provided r,u the exclusiYe use oft he
~ddressee Pli\ ile~es or sub .. seq~Jent ~~~e of the ~~\e or this .con~pnny or MY ~~~ber of its stnff, or reproductio~ ~~this repol; in ~on~u~ction .. with I hell~\ erlise~ent. P~?molio.n or sole of ~~y ~IOdl~Cl or P~?cess, ~r in ~onn~c~ion w~lh th~ ~-publication or this repOrl
ANALVTICAL I ABORATOR i fS
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 16034 79-001
Client Sample ID: TW4-06R_03212016
Collection Date: 3/2112016 1034h
Received Date: 3/23/2016 930h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 3/25/2016 1112h E300.0 1.00 < 1.00
Nitrate/Nitrite (as N) mg/L 3/24/2016 1719h E353.2 0.100 <0.100
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 3/30/2016 Page 13 of 27
All ann!~ ses applicable to the CWA SDWA. and RCRA me perfom1ed in accordance to NELAC protocols, Pertinent snmpliny information is located on the atlached COC Confidential Business lnfonnation: This report is pro' ided for the exclusi,·e use of the
~ddressee. Pri,·ile~es o_rsub;eq~enl ~~e oithe ~~e of this .em~ puny or M) ~~:mber of its staff, or reproductio~ ~~this repo~ in ~~~1ection .. "ith the a~vertisement, P~?moti~ ~r sale of~~~ ~rod~ct or p•:ocess, ~r in ~onn~c~ion w~th th~ r~-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 841 19
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603479-004C
Client Sample ID: TW4-07 _ 03222016
Collection Date: 3/22/2016 858h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1652h
Units: j.tg/L Dilution Factor: 10
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
509
519
501
508
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/23/2016 1400h
Units: j.tg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.0
Surr: 4-Bromofluorobenzene 460-00-4 51.5
Surr: Dibromofluoromethane 1868-53-7 49.8
Surr: Toluene-d8 2037-26-5 50.5
67-66-3 10.0 834
Amount Spiked %REC Limits Qual
500.0 102 72-151
500.0 104 80-152
500.0 100 80-124
500.0 102 77-129
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.9 72-151
50.00 103 80-152
50.00 99.6 80-124
50.00 101 77-129
Report Date: 3/30/2016 Page 8 of27
All onalyses applic;)ble lo the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent srunpling information is locuted on the atlnched COC Conrirlentiol Business lnfonnalion: This report is pro,•ided for the exclusi\ e use oft he
~ctdressee Pri,·ite~es o,r sub_.seq~ent ~;e oft he ~~ne oflhis .co•~p1:my or nn) ~mbel of iLS SIOlff, or reproducti~ ~f this repo~ in ~on~eclion ... with the o~''ertisemenl, P~?moli~n ~r saJe of~~. p10dt~cl or P•.ocess, ~r in ~onn~~ion \\'!lh th~ r~publication 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 2016
Lab Sample ID: 1603479-004
Client Sample ID: TW4-07_03222016
Collection Date: 3/22/2016 858h
Received Date: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 948h
3/24/2016 1723h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 42.4
E353.2 0.100 4.43
Report Date: 3/30/2016 Page 16 of 27
All analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling informo1ion is located on the attached COC_ Contidentlal Business Jnfonni)\ion: This repon is provided for the exclusi\ e w:e of the ~ddressce Pri,·ile~es o~ sub .. seq~tent ~~~e of the ~~e of this .co•~pany or M) 1~mbe1 of its staff, or reproductio~ ~fthis repo~ in ~~ection .. \\·ith the~' ertisement, P~?moli~n ~r saJe of~!~ ~rodt~ct or p~ocess, ~r in ~nn~c~ion \\'~lh th~ r~-publication of this report
Client:
Project:
Lab Sample ID:
Client Sample ID:
ORGANIC ANALYTICAL REPORT
Energy Fuels Resources, Inc.
I st Quarter Chloroform 2016
1603400-022C
TW4-08 03172016
Contact: Garrin Palmer
ANALYTICAL LABoRAroR I~s Collection Date: 3/17/2016 854h
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: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1713h
Units: llg/L
Compound
Chloroform
Dilution Factor: 10
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 634
Surrogate 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
493
540
497
512
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/18/2016 1530h
Units: !!giL Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 47.8
Surr: 4-Bromofluorobenzene 460-00-4 51.1
Surr: Dibromofluoromethane 1868-53-7 49.2
Surr: Toluene-d8 2037-26-5 49.8
500.0 98.5 72-151
500.0 108 80-152
500.0 99.5 80-124
500.0 102 77-129
Method: SW8260C
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 < l.OO
Amount Spiked %REC Limits Qual
50.00 95.6 72-151
50.00 102 80-152
50.00 98.4 80-124
50.00 99.5 77-129
Report Date: 4111/2016 Page 51 of 62
All analyses applicable to lhe CWA. SOW A. and RCRA are perfom1ed in accordance to NELAC protocols, Pertinent sampling information is located on lhe allached COC Confidential Business lnfonn;~lion: This report is pto"ided for the e.."<clusi' e use of the
~ddressce PriYile~es or sub__seq~t ~e or the ~~e of this .con;pany or anr T~mb61 of its staff, or reproducli~ ~r this repo~ in .c~leclion .. with the a~l·ertisernen~ P~?motio.n ~r sale of~!) ~rodl~Cl or p~ocess, ~r in ~onn~c~ion "'!lh th~ r~-publication of this report
3440 South 700 West
:lalt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratmy Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-022
Client Sample ID: TW4-08_03172016
Collection Date: 3/17/2016 854h
Received Date: 3/18/2016 1 040h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/23/2016 2242h
3/24/2016 1703h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 54.2
E353.2 0.100 2.48
Report Date: 4/11/2016 Page 28 of62
All anal) ses applicable to the CWA, SOW A. and RCRA are perl'om1ed in accordance to NELAC p(Otocols. Pertinent sampling infomw.Lion is located on the auached COC Conridenlial Business lnfonnalion: This report is provided for the exclusi\ e use oflhe
~rldressee Pri' ile~es o~ sub .. seq~nt ~;e of the ~:u:ne of this .con.lpany or any ·~mber of iLS struT, or reproducti~ ~r this repo~ in ~n?ection .. "ith the ~vertisement, P~?motio_n ~r sale of ~y ~rod~ct or p~ocess, ~r in ~nn~~ion w!th th~ r~-p~blication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-018C
ClientSampleiD: TW4-09_03172016
Collection Date: 3/17/2016 822h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 200lh
Units: ~giL Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
50.5
52.5
48.7
51.1
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 74.3
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 101 72-151
50.00 105 80-152
50.00 97.4 80-124
50.00 102 77-129
Report Date: 4/1112016 Page 47 of62
All an-. lyses applicable to the CW A. SDWA. and RCRA are .,.erfomted in accordance to NELAC ptolocols Pertinent sampling information is located on the allached COC Confidential Business Informal ion: This report is prol•ided for the exclusin usc oflhe
~ddressee Pri,·ile~es o: sub ... seq~ent ~e of the ~~e of lhis .co1~pn.ny or M) ~mbet of its stnff, or reproductio~ ~~this repo~ in ~on~ection~ with the a~' erlisemenl, P~?motio.n or sa1e of~!) ~rod~ct or p~ocess, ~r in ~nn~c~ion "!th th~ r~-P'!blica1ion o( 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 Chlorofonn 2016
Lab Sample ID: 1603400-018
ClientSampleiD: TW4-09_03172016
Collection Date: 3/17/2016 822h
Received Date: 3/18/2016 1 040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 156h
3/24/2016 1648h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 33.6
E353.2 0.100 2.51
Report Date: 4/11/2016 Page 24 of62
All analyses applicable to the CWA. SOW A. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling infom\ation is located on lhe nl!;~ched COC Confidential Business lnformarion: This report is pro,•ided for the exclusi\ e use of the
~ddressee Pri,ile~es or sub ... seq~l ~e of the ~~e of lhis .co•~pmty or any ~mber of its stnfT, or reproductio~ ~f this repo~ in .con?eclion .. with the ~~er1isemenL p~~motio.n ~r ~ale of~~~.~~ odl~l or p~~cess, ~r in ~onn~c~ion w!th th~ r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
)alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (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 2016
Lab Sample ID: 1603479-005C
Client Sample ID: TW4-10_03222016
Collection Date: 3/22/2016 906h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1712h
Units: f..lg/L Dilution Factor: 20
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 1,020
460-00-4 1,050
1868-53-7 1,000
2037-26-5 1,010
--The reporting limits were raised due to high ana lyle concentrations.
Analyzed: 3/23/2016 1420h
Units: !lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 49.9
Surr: 4-Bromofluorobenzene 460-00-4 52.0
Surr: Dibromofluoromethane 1868-53-7 50.0
Surr: Toluene-d8 2037-26-5 50.6
67-66-3 20.0 1,430
Amount Spiked %REC Limits Qual
1,000 103 72-151
1,000 105 80-152
1,000 100 80-124
1,000 101 77-129
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.9 72-151
50.00 104 80-152
50.00 100 80-124
50.00 101 77-129
Report Date: 3/30/2016 Page 9 of27
All analyses applic<1ble ro the CWA. SDWA. and RCRA we performed in accordance to NELAC protocols Pertinent sampling information is located on the aU ached COC Confidential Business lnformalion: This report is pro\'ided for the e:xclusi\e use of the
~ddressee Pri' ile~es of' sub ... seq~ent ~~e of the ~~e of this .cot~pany or ru1~ 1~mbe1 of its stnff, or reproducli~ ~~ Lhis repm~ in .cm~ection ... with the a~''er1isement. P~?motio.n 01 sale of ~!Y rroc.h~cl or P•.ocess, ?r in :onnt;_c~ion "~th th~ r:-publica!ion 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 2016
Lab Sample ID: 1603479-005
Client Sample ID: TW4-10_03222016
Collection Date: 3/22/2016 906h
Received Date: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 1005h
3/24/2016 1724h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 84.1
E353.2 0.100 17.3
Report Date: 3/30/2016 Page 17 of27
All anal) ses applicnble to the CWA. SDW A, and RCRA rue perfom1ed in accordance to NELAC protocols Pertinent sampling infonnation is locoted 011 Lhe aU ached COC Confidential Business lnfonnution: This report is prol'ided for the exclusi\ e use of the
~ddressee Pri\ ile~es or su~seq~l ~~e of the !~~t.ne of this .con.lpany or M): ~'!1be1 of its Slllff; o~ reproduclio~ ~~.this rep01~ in ;on~ection~ \\ilh the a<!"er1isemenl, P~?moti~n ~r saJe of~~) ~ro<h~cl or p~ocess, ~r in ?mn:c~ion w~th th~ r:publication of this report
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (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: lst Quarter Chloroform 2016
Lab Sample ID: 1603259-009C
Client Sample ID: TW4-11_03092016
Collection Date: 3/9/2016 1153h
Received Date: 3/11/2016 1030h
Analytical Results
Analyzed: 3/15/2016 1415h
Units: Jlg/L Dilution Factor: 50
Compound
Chloroform
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 2,480
460-00-4 2,520
1868-53-7 2,430
2037-26-5 2,470
~ -The reporting limits were raised due lo high analyte concentralions.
Analyzed: 3/14/2016 1444h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 52.6
Surr: 4-Bromofluorobenzene 460-00-4 51.9
Surr: Dibromofluoromethane 1868-53-7 49.9
Surr: Toluene-d8 2037-26-5 50.4
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 50.0 2,660
Amount Spiked %REC Limits Qual
2,500 99.3 72-151
2,500 101 80-152
2,500 97.1 80-124
2,500 98.9 77-129
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 1.20
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 105 72-151
50.00 104 80-152
50.00 99.8 80-124
50.00 101 77-129
Report Date: 3/28/2016 Page 14 of 40
All anal) ses applicnble to tile CWA. SDWA. and RCRA are perfonned in accordance to NELAC prOiocols Pertinent sampling information is located on the attached COC~ Confidentio\ Business Information: This report is provided for the e.xclusive use of the
~ddressee Pri\ ile~es o.r sub .. seq~1ent ~·~e or the ~~,e of I his .co"_lpntly or M) ~mber of ils slaff, or reproduclio~ ~fthis repo~ in .con~leclion .. "ilh lhe a~' ertisemen1, P~?mo1io.n ~r sale of~!) ~fOdl~cl or P•.?cess, ~r in ~nn~c~ion w~lh lh~ r~-p~blicaJiOtl of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-009
Client Sample ID: TW4-11_03092016
Collection Date: 3/9/2016 1153h
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 2212h
3/12/2016 1121h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 55.5
E353.2 0.100 7.13
Report Date: 3/28/2016 Page 28 of 40
All anal~ses applicOJ.ble to the CW~ SDWA. and RCRA are performed in accordMce to NELAC protocols. Pertinent sampling itlformation is located on the altnched COC Conlidential Business Information: This report is pro\·ided for the esclusi\'e use of the
~ddressee Pri\ ile~es of' sub ... seq~enl _u~e of the ~:u,ne of this .co~pany or an) 1~mber of its slaJi, or reproductio.~ ~f this repo~ in ~n~lection~ \Vilh the a~vet1isemenl, P~?moli~ ~r ~ale of~). ~rodl~cl or P':?Cess, ~r in ~nn~c.tion w!lh th7 n;·p~blicalion of lhis report
3440 South 700 West
'alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-003C
Client Sample ID: TW4-12_03152016
Collection Date: 3/15/2016 652h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1404h
Units: J..Lg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Brornofluorobenzene
Surr: Dibromofluorornethane
Surr: Toluene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
48.3
51.8
47.4
49.9
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method:
CAS Reporting
Number Limit
56-23-5 1.00
67-66-3 1.00
74-87-3 1.00
75-09-2 1.00
Amount Spiked %REC
50.00 96.6
50.00 104
50.00 94.8
50.00 99.8
SW8260C
Analytical
Result
< 1.00
< 1.00
< 1.00
< 1.00
Limits
72-151
80-152
80-124
77-129
Qual
Qual
Report Date: 4/11/2016 Page 32 of62
All analyses applicable to the CWA.. SDWA_ and RCRA are per fanned in accordance to NELAC protocols Per1inent sampling inrormation is located on the attached COC Confidential Business lnforml.llion: This repon is pro\'ided for1he exclusi\e use of the
~ddressee Pridle~es o_fsub .. seq~•ent ~~e of the ~~e or this .cm~pany or M) ·~mber of its stafT, or reproductio~ ~fthis repo~ in .con~ection ... witJ1 the u~vertisemenl, P~?moti~ ~r sale of~!). ~r<xh~l or p~ocess, ~r in ~onm;_c~ion w~lh th~ n;_-publication of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-003
Client Sample ID: TW4-l2_03152016
Collection Date: 3/15/2016 652h
Received Date: 3/18/2016 l040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3123/2016 1400h
3/24/2016 1650h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 56.2
E353.2 0.200 34.8
Report Date: 4/11/2016 Page 9 of62
All onnlyses applicable to the CW A. SDWA. and RCRA are performed in accordance to NELAC protocols J>ertineru sampling infommlion is located on the aUached COC Confidential Business Inform;~! ion: This repor1 is pro\•ided for lhe exclusi\ e use of the
~ddressee p,;, ile~es or sub~seq~ent ~~e of the ~~e of this _cot~pany or an, ~r_nber of its st:UT, or reproductio.~ ~f this repo~ in ~~ection~ , ... ith lhe n~vertisement, p~~moti~ or sa1e of?'!) ~rod~cl or p~ocess, ~r in :onn~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: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-006C
Client Sample ID: TW4-13_03162016
Collection Date: 3/16/2016 642h
Received Date: 3/18/2016 1 040h
Analytical Results
Analyzed: 3/18/2016 1523h
Units: J.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 49.6
460-00-4 51.8
1868-53-7 48.7
2037-26-5 50.8
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.1 72-151
50.00 104 80-152
50.00 97.3 80-124
50.00 102 77-129
Report Date: 4/11/2016 Page 35 of62
All analyses applicnble to the CWA. SDWA. and RCRA ore performed in accordMce to NELAC protocols Pertinent sampling information is located onlhe attached COC Confidential Business Information: This report is pro\'ided for the exclusi'e use oft he
~ddressee Pri\ ile~es o[ sub__seq~enl ~~e or the ~~e of this .cot~pany or M) ~mber of its slaiT, or re!)roducti~ ~fthis repo~ in ~on~ eel ion .. \\ilh the~' ertisemenl, P~?molio~ ~r sale of~. ~nxh~cl or p~ocess, ~r in ~"":C~ion w~th th~ r:-publication or this report
American West ANALYTICAL LABORATORIES
3440 South 700 West
;;altLakeCity, 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 2016
Lab Sample ID: 1603400-006
Client Sample ID: TW4-13_03162016
Collection Date: 3/16/2016 642h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
3/23/2016 1450h
3/24/2016 1612h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 69.4
E353.2 0.100 7.97
Report Date: 4/1112016 Page 12 of 62
All analyses applicable to the CWA SDWA, and RCRA are periOm1ed in accordance to NELAC pro locals Pertinent sampling ill formation is located on Lhe auached COC Confidential Business lnfonnolion: This repon is prO\•ided for lhe exclusi\·e use of the
~ddressee Prh ile~es o,r sub .. seq~enl ~~e of the ~~e of1his .con.lpany or anr ~mbe1 of its starT, or reproducli~ ~fthis repo~ in .co~ection .. "~lh the D~\ ertisemenl, P~?motio.n or snJe of ?J;) ~rodl~cl or p~ocess, ~r in ~nm;.c~ion w~lh 1h~ r~-p~blication or 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-012C
Client Sample ID: TW4-14_03162016
Collection Date: 3/16/2016 729h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1803h
Units: J.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
50.2
51.8
47.6
50.1
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 4.49
74-87-3 1.00 < 1.00
75-09-2 1.00 2.18
Amount Spiked %REC Limits Qual
50.00 100 72-151
50.00 104 80-152
50.00 95.3 80-124
50.00 100 77-129
Report Date: 4/11/2016 Page41 of62
All antll) ses applicable to the CWA, SDWA. and RCRA are 1Jerfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the all ached COC Confidential Business lnfonnalion: This report is provided for the exclusire use of the
~ddressee Pri\ ile~es o; sub .. seq~•ent ~~e of the ~:u:"e of this .co•~pon~· or nn.\ 1~7mber or its slnff, or reproductio~ ~f this repo~ in ~on~ection ... \vith the a~~enise~enl, P~?motio:n ~r saJe of~·. ~rO<h~cL or p~ocess, ~r in ?'nn:_c~ion w~th 1h~ r:·publication or 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 2016
Lab Sample ID: 1603400-012
Client Sample ID: TW4-14_03162016
Collection Date: 3/16/2016 729h
Received Date: 3/18/2016 1 040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
3/24/2016 2308h
3124/2016 1633h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 42.4
E353.2 0.100 2.94
Report Date: 4/11/2016 Page 18 of 62
AU anal~ ses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordam:e to NELAC protocols Pertinent sampling information is located on the altached COC Confidential Business lnfonnution: This report is pro,•ided for the esclusi' e use of the
~ddressee Pri\·ile~es ofsub~seq~l ~?e of the ~~e of this .col~pnt\y or an~· ~mbe1 of its stnlT. or reproductio~ ~fthis repo~ in ~O~lCCtion~ \\"ilh the n~vertisemenl. P~?moti~ or sale of~!) ~rodL~r:l or pl.ocess, ~r in ~onn:c~ion w~th th~ r:-publicaJion of this repon
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-008C
Client Sample ID: MW-26_03092016
Collection Date: 3/9/2016 1044h
Received Date: 3/11/2016 1030h Test Code: 8260-W-DENlOO
Analytical Results VOAs by GC/MS Method 8260C/5030C
Analyzed: 3/14/2016 1933h
Units: J.Lg/L Dilution Factor: 20 Method: SW8260C
3440 South 700 West
;;a!t Lake City, UT 84119 CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 20.0 2,650
Phone: [phone] Surrogate CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone] Surr: I ,2-Dichloroethane-d4 17060-07-0 1,040 1,000 104 72-151
Surr: 4-Bromofluorobenzene 460-00-4 1,020 1,000 102 80-152
Fax: [phone] Surr: Dibromofluoromethane 1868-53-7 1,010 1,000 101 80-124
~-mail: [e-mail] Surr: Toluene-d8 2037-26-5 997 1,000 99.7 77-129
--The reporting limits were raised due to high analyte concentrations.
web: www.awa1-1abs.com Analyzed: 3/14/2016 1424h
Units: J.Lg/L Dilution Factor: Method: SW8260C
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 4.66
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 53.6 50.00 107 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.3 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 50.7 50.00 101 80-124
Surr: Toluene-d8 2037-26-5 51.1 50.00 102 77-129
Report Date: 3/28/2016 Page 13 of 40
All annl)ses applicable lo the CWA, SDWA. and RCRA me perfonned m accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is pro,ided for1he exclushe use of the
~ddressee Pri,·ile~es o.f sub~seq~tenl ~~~e of the ~~1e of this .em~ pony or anr ~~~be1 of its stnlT. or reproductio.~ ~~this repm; in ~on~eclion,.. \\ith then~~ ertisemenl, P~?motio.n ~r ~ille of ?J!). ~rodL~Cl or p~ocess, ~r in :onn:c!ion w!th th~ r~-p~blication of this report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-008
Client Sample ID: MW-26_03092016
Collection Date: 3/9/2016 1044h
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 215611
3/12/2016 1120h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 68.3
E353.2 0.100 1.45
Report Date: 3/28/2016 Page 27 of 40
All analyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling informal ion is locnted on the allached COC Confidential Business Information: This report is provided for the e:xclusiYe use of the
~ddressee Pri, ile~es o.r sub~seq~tenl ~~e of the ~~e of this .c01~pany or any ~mber of its stafT. or reproductio~ ~~this repo~ in .con~ection~ \\ilh the a~~ertisement, P~?motio.n ~r saJe of ?J!) ~rodt~cl or pt:?cess, ~r in :onm~.c~ion w!lh th~ r:-publicalion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 20 16
Lab Sample ID: 1603400-019C
American West Client Sample ID: TW4-16_03172016
ANAL vr1 cAL LAB o RAro R 1 E s Collection Date: 3/17/2016 829h
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: 3/18/2016 1040h
Analytical Results
Analyzed: 3118/2016 2021h
Units: Jlg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
50.6
52.5
49.3
51.2
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 45.9
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 101 72-151
50.00 105 80-152
50.00 98.5 80-124
50.00 102 77-129
Report Date: 4/1112016 Page 48 of 62
All anal) ses applicoble to the CWA. SDWA. and RCRA rue performed in 1\Ccordilnce to NELAC protocols Pertinent sampling information is locDLed on the auached COC Confidential Business lnformalion: This report is prm•ided fort he e:o;:clusi\e use oflhe
~ddressee Pri\ ile~es o[su~seq~lenl ~~e of the ~~1e ofthis.cOI~pany or M~ 1~mber of its slnff, or reproductio~ ~~this repo~ in .con~ection .. with lhe a~:enisemenL p~omotiOfl or sale of~~ ~fO<h~cl or p~ocess, ~r in ';'nn:c.Lion ''!th th~ r~-publica1ion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-019
Client Sample ID: TW4-16_03172016
Collection Date: 3/17/2016 829h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 213h
3/24/2016 1649h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 56.5
E353.2 0.100 1.63
Report Date: 4/11/2016 Page 25 of62
All anab ses applicable 10 the CWA. SDW A. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on lhe aU ached COC Conlidential Business [nformation: This repor1 is prm ided for the exclusi\e use of the
~ddressee. Pri,·ile~es o_rsub ... seq~enl ~;e of the ~:u:ne of this .cOI~pany or ffil) ~mbeJ' of its slalT, or reproductio~ ~flhis repo~ in ~on~lection. with the a~vertisement. p~omotio.n ~r sale of:u~·. rrodl!CI or p~ocess, ~r in ~onn':.c~ion w!th th~ r:_-publicalion of1his report
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
16034 79-002C
MW-32 03222016
Collection Date: 3/22/2016 1230h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1321h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 51.0
460-00-4 52.8
1868-53-7 50.0
2037-26-5 51.0
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 102 72-151
50.00 106 80-152
50.00 100 80-124
50.00 102 77-129
Report Date: 3/30/2016 Page 6 of 27
All nnnl) ses applicable to the CWA. SDWA, Md RCRA ate perfom1ed in accordance to NELAC protocols Pertinent sampling infonnation is located on the allnched coc_ Confidential Business lnfonnnlion: This tepon is pro\'ided for the exclusi\e use of the
~ddressee Prh ile~es or SU~seq~enl ~~e of the ~~e of this .cot~pany or any l~mber of its Sl:lff, or reproducli~ ~f this repo~ in ~n~eclion .. \\ilh the O~l'enisement, p~~motio;n or ~aJe of ~~Y. ~rodl~Ct or Pl.ocess, ~r in ~nn:c~ioo w~th th~ n;-p~blicntion of lhis l'tporl
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603479-002
Client Sample ID: MW-32_03222016
ANALYTICAL LABoRAToRIEs Collection Date: 3/22/2016 1230h
3440 South 700 West
;a)t 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: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/25/2016 841h EJOO.O 10.0 36.7
3/24/2016 1722h E353.2 0.100 <0.100
Report Date: 3/30/2016 Page 14 of27
All analyses applicable to the CW A. SDWA. and RCRA are perlbm1ed in accordance to NELAC protocols. Pertinent sampling information is located on the al1nched COC Coolidenlial Business Information: This repon is provided for the exclusiYe use of the
~ddressee Pri\·ile~es o! su~q~enl ~~e of the ~~1e of this .coi~J)UilY or an)" 1~mber of ilS staff, or reproductio~ ~f this repo~ in ~Ot~eclion~ with the a~vertise1!lent P~?moti~ or sale of :U!Y ~rodt~ct or p~ocess, ~r in ~onn~c~ion \\'!lh lh~ r:-publicaLion of I his reporl
American West
ANALYTICAL LABORATORIES
3440 South 700 West
'alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-017C
Client Sample ID: TW4-18_03172016
Collection Date: 3/17/2016 813h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 194lh
Units: 11g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
50.3
52.5
49.0
51.2
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 56.6
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 101 72-151
50.00 105 80-152
50.00 98.0 80-124
50.00 102 77-129
ReportDate: 4/11/2016 Page46of62
All analyses applicable to the CWA SDWA. and RCRA are perfonned in accordance to NELAC protocols Pe11inent sampling informalion is located on the attached COC Confidential Business [nformalion: This repon is proyided for the exclliSi\·e use oft he
~ddressee Pri' ile~es o: su~seq~enl ~~e of the ~~e of this ~co1~pany or M) J~mber of its staff, or reproductio~ ~fthis repo~ in ~on~ection~ \\ith them!~ ertisement, P~?motio.n ~r ~ale of~!)~ ~rodl~ct or P~?cess, ~r in ~onn:c~ion w~lh 1h7 r~-p~blica!ion of lhis report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
LabSampleiD: 1603400-017
Client Sample ID: TW4-18_03172016
ANAlYTICAl lAooRATORIEs Collection Date: 3/17/2016 813h
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: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/25/2016 !39h E300.0 10.0 40.7
3/24/2016 164711 E353.2 0.100 5.96
Report Date: 4/11/2016 Page 23 of 62
All ann]~ ses applicable to the CWA. SDW A. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the aU ached COC Confidential Business Information: This report is prO\ ided for the exclusi\ e use of the
~ddressee Pri' ile~es o_Fsub~seq~enl ~;;e of the ~~e of this .co~pmty or an) ~mber of its stnJT, or reproduclio~ ~fthis repo~ in ~on~tection~ \\~lh the a~vertisemenl, P~?motio.n OI"Sale of~~).~IOdl~cl or p~ocess, ~r in :onn:c~ion "!lh th~ r:_-publicalion of I his report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-0llC
Client Sample ID: TW4-19_03092016
Collection Date: 3/9/2016 1430h
Received Date: 3/11/2016 1030h Test Code: 8260-W-DENlOO
Analytical Results VOAs by GC/MS Method 8260C/5030C
Analyzed: 3/15/2016 1454h
Units: J..tg/L Dilution Factor: 50 Method: SW8260C
3440 South 700 West
;;alt Lake City, UT 84119 CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 50.0 7,780
Phone:[phone] Surrogate CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone] Surr: I ,2-Dichloroethane-d4 17060-07-0 2,520 2,500 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 2,570 2,500 103 80-152
Fax: [phone] Surr: Dibromofluoromethane 1868-53-7 2,440 2,500 97.8 80-124
~-mail: [e-mail] Surr: Toluene-d8 2037-26-5 2,500 2,500 100 77-129
--The reporting limits were raised due to high analyte concentrations.
web: www.awal-labs.com Analyzed: 3/14/2016 1523h
Units: J..lg/L Dilution Factor: Method: SW8260C
Kyle F. Gross CAS Reporting Analytical
Compound Number Limit Result Qual
Laboratmy Director
Carbon tetrachloride 56-23-5 1.00 13.5
Jose Rocha Chloromethane 74-87-3 1.00 1.40
QA Officer Methylene chloride 75-09-2 1.00 < 1.00
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 51.9 50.00 104 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.3 50.00 103 80-152
Surr: Dibromofluoromethane 1868-53-7 48.0 50.00 95.9 80-124
Surr: Toluene-d8 2037-26-5 49.8 50.00 99.7 77-129
Report Date: 3/28/2016 Page 16 of 40
All anal) ses applicable to the CWA. SDWA. and RCRA rue performed in accordance to NELAC protocols Pertinent sampling information is located on Lhe altnched COC Confidential Business Jnformalion: This repon is provided for the exclusi\ e use of the
~ddressee Pti' ile~es o.r sub ... seq~ent ~~e of the ~:u,ne of this .co':-pany or any 1~mber of its slaiT, or reproductio~ .~f this repo~ in ~~lechon~ \\ith the a~~~ertisemenl, P~?molio.n ~r sale of~!): ~rod~ct or p~ocess, ~r in 7onn~c~ion w~lh th~ r~-publicution 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 2016
Lab Sample ID: 1603259-011
Client Sample ID: TW4-19_03092016
Collection Date: 3/9/2016 1430h
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 1907h
3/12/2016 1123h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 276
E353.2 0.100 15.7
Report Date: 3/28/2016 Page 30 of 40
All anal) ses applicnble to lhe CWA. SDWA. and RCRA we perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached CDC Confidential Business lnfonntllion: This report is provided for the exclusiYe ~e of the
~ddressee Pri,•ile~es o[sub_seq~enl ~~e of the ~~e oflhis .co~pany or nil) ~mber of its staff, or reproductio~ ~[this repo'1 in ~o1~1ection~ with the ~vertisemenL P~?motio.n or ~aJe of?J!) ~rod~cl or pl.ocess, ~r in ~mmt;c~ion w~Lh th~ n;_-publicalion or Lhis 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-012C
Client Sample ID: TW4-20_03092016
Collection Date: 3/9/2016 103lh
Received Date: 3/11/2016 1030h
Analytical Results
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Analyzed: 3/15/2016 1514h
Units: !!giL Dilution Factor: 100 Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 100 21,600
Surrogate 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
5,090
5,260
4,890
5,040
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1543h
Units: !!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 52.3
Surr: 4-Bromofluorobenzene 460-00-4 50.3
Surr: Dibromofluoromethane 1868-53-7 49.6
Surr: Toluene-d8 2037-26-5 49.7
5,000 102 72-151
5,000 105 80-152
5,000 97.9 80-124
5,000 101 77-129
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 20.2
74-87-3 1.00 4.09
75-09-2 1.00 1.16
Amount Spiked %REC Limits Qual
50.00 105 72-151
50.00 101 80-152
50.00 99.2 80-124
50.00 99.4 77-129
Report Date: 3/28/2016 Page 17 of 40
All anal~ ses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confident in! Business lnformalion: This report is pro\'ided fort he exclusive use of the
~ddressee Pri \ ile~es or sub~seq~enl ~~e of the ~~e of this .cm~pru1y or an)' ~~~her or ils stafT, or reproductio~ ~~this repo~ in ~on~eclion ... \\·ith the a~~~ertisemenl. P~?molio.n ~r :aJe of~!~: ~rodt~cl or p1.ocess, ~r in ~onn:c~ion \\!th th~ r~-publicalion of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-012
Client Sample ID: TW4-20_03092016
ANALYTICAl LABoRAToRIEs Collection Date: 3/9/2016 103lh
3440 South 700 West
;;a!t 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: 3/1112016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/16/2016 1924h E300.0 100 293
3/12/2016 1124h E353.2 0.100 10.3
Report Date: 3/28/20 16 Page 31 of 40
All anah ses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the auached COC Confidentlal Business Jnformation: This report is provided fort he exclush-e use of the
~ddressee Prh ile~es o!' sub,..seq~enl ~~e of the ~~e of this .cm~pany or any t~mbet· of its slaiT, or reproduclio~ ~f this repo~ in .co~eclion~ \\ilh the a~vertise~enl, P~?motio.n ':r sale of ~,!Y. ~rod~cl or pt:?cess, ~r in ~nn~c!ion \\ ~lh th~ r~-p~blication or this report
3440 South 700 West
;a!t 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 2016
Lab Sample ID: 1603259-003C
Client Sample ID: TW4-21_03092016
Collection Date: 3/9/2016 947h
Received Date: 3/11/2016 1030h
Analytical Results
Analyzed: 3/14/2016 1716h
Units: !!g/L
Compound
Chloroform
Dilution Factor: 10
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 390
Surrogate 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
517
509
505
500
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1245h
Units: !!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4 17060-07-0 52.8
Surr: 4-Bromofluorobenzene 460-00-4 51.7
Surr: Dibromofluoromethane 1868-53-7 47.3
Surr: Toluene-d8 2037-26-5 50.4
500.0 103 72-151
500.0 102 80-152
500.0 101 80-124
500.0 100 77-129
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 106 72-151
50.00 103 80-152
50.00 94.6 80-124
50.00 101 77-129
Report Date: 3/28/2016 Page 8 of40
All anal) ses applicnble to the CWA. SDWA. and RCRA rue perfom1ed in accordance to NELAC protocols Pertinent sampling inrormation is located on the attnched COC, Confidential Business Information: This repor1 is provided for the exclusi\e use of the
~ddressee Pri\ ile~es o.r sub,.seq~Jent ~~~e of the ~~e of this .con_1pnny or nn~ •~mbcr of its slaff, or reproductio~ ~f this repm; in .con~leclion .. '"ith the "~' ertisemenl, P~?moti~n or sale of ?J~Y ~rodl~cl or p~ocess, ~r in ~nn~c~ion \\'!lh th~ r~·publication of this report
American West
ANALYTICAL LABORATOR IES
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-003
Client Sample ID: TW4-21_03092016
Collection Date: 3/9/2016 94 7h
Received Date: 3/11/2016 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg!L 3116/2016 1800h E300.0 100 452
Nitrate/Nitrite (as N) mg!L 3/12/2016 1109h E353.2 0.100 14.6
Report Date: 3/28/2016 Page 22 of 40
All an<ll~ ses applicable to the CW A. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on lhe aU ached COC Confidential Business Information: This report is provided for the exclusiYe use of the
~ddressee Pri\•ile~es o.rsub.seq~ent ~~e of the ~~e of this .co':lpo.ny or nn)' 1~';lbe1·ofils stniT, or reproductio.~ ~flhis repo~ in ~o1~ection ... \\iil1 the a~vertisemenl. P~?motio.n or sale of~!~: ~IOdl~cl or P~?cess, ~r in 7onn:c~ion w!lh lh~ r~-p~blicalion of this 1eport
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-0lOC
American West
ANALYTICAl LABORATORIES
Client Sample ID: TW4-22_03092016
Collection Date: 3/9/2016 1018h
Received Date: 3/11/2016 1030h Test Code: 8260-W-DENlOO
Analytical Results VOAs by GC/MS Method 8260C/5030C
Analyzed: 3/15/2016 1434h
Units: j.tg/L Dilution Factor: 50 Method: SW8260C
3440 South 700 West
~alt Lake City, UT 84119 CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 50.0 6,070
Phone: [phone] Surrogate CAS Result Amount Spiked %REC Limits Qual
Toll Free: [phone] Surr: 1,2-Dichloroethane-d4 17060-07-0 2,520 2,500 101 72-151
Surr: 4-Bromofluorobenzene 460-00-4 2,530 2,500 101 80-152
Fax: [phone] Surr: Dibromofluoromethane 1868-53-7 2,480 2,500 99.4 80-124
~-mail: [e-mail] Surr: Toluene-d8 2037-26-5 2,530 2,500 101 77-129
--The reporting limits were raised due lo high analyte concentrations.
web: www.awal-labs.com Analyzed: 3/14/2016 1503h
Units: j.tg/L Dilution Factor: Method: SW8260C
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 CAS Result Amount Spiked %REC Limits Qual
Surr: 1,2-Dichloroethane-d4 17060-07-0 52.6 50.00 105 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.4 50.00 105 80-152
Surr: Dibromofluoromethane 1868-53-7 49.5 50.00 99.0 80-124
Surr: Toluene-d8 2037-26-5 50.5 50.00 101 77-129
Report Date: 3/28/2016 Page 15 of 40
All uno lyses applicable to the CWA, SDW A. and RCRA ure perfonned in accordance lo NELAC protocols. Pertinent sampling information is located on the allached COC Confidential Business Jnformntion: This reporl is provided for the exclushe use of the
~ddressee Pri,·ile~es o~sub.seq~enl ~;e of the ~~e of this .co"_lpDny or an) ~;';!bel of its slaiT, or reproduclio~ ~f this repo~ in ~on~1ection .. \\-ilh the a~vertisemenl, P~?moLi<:n ~r ~ale of ?J~). ~rodl~cl or P•:?cess, ?r in ~nn:c~ion \\'!th th: r;·publication of' this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-010
Client Sample ID: TW4-22_03092016
Collection Date: 3/9/2016 1018h
Received Date: 3/11/2016 1030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 1850h
3/21/2016 1539h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 583
E353.2 0.500 31.1
Report Date: 3/28/2016 Page 29 of 40
All anal~ ses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on lhe allached COC Confidential Business Infermalion: This report is provided for the exclusi\e use oft he
~ddressee Pri,·ile~es o.r sub .. seq~ent ~?e of the ~~e of this .co~pany or anr 1~mber of its staff, or reproductio~ ~f this repo~ in ~o~eclion .. with the a~''er1isemenl P~?moti~n or sale of~!~ ~rodl~cl or p~ocess, ~r in ~onn:c~ion w!th th~ n;-publication of this report
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-0llC
Client Sample ID: TW4-23_03162016
Collection Date: 3/16/2016 721h
Received Date: 3/18/2016 1 040h
Analytical Results
Analyzed: 3/18/2016 1743h
Units: Jlg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dich1oroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: To1uene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
51.1
53.1
48.8
51.3
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 102 72-151
50.00 106 80-152
50.00 97.7 80-124
50.00 103 77-129
Report Date: 4/11/2016 Page 40 of62
All analyses applicable to the CWA. SOW A. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling it1formation is located on the attached COC Conlidential Business Information: This report is provided fort he exclusi\e w;e of the
~ddressee Pri' ile~es o.r sub__seq~enl ~~e of I he ~:u:"e of this .c01~pany or nn~ t~mber of its stalT, or reproduclio~ ~f this repm; in .co~echon~ \vith the ~vertise~ent, P~?motio.n or sale of~!) ~rodl~CI or p~ocess, ~r in ~nn~c.tion w!th 1~ r~-publicahon of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-011
Client Sample ID: TW4-23_03162016
ANALYTICAL tAnoRAToRtrs Collection Date: 3116/2016 721h
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/24/2016 2251h E300.0 10.0 49.1
3/24/2016 1632h E353.2 0.100 < 0.100
Report Date: 4/11/2016 Page 17 of 62
All analyses applicable to the CWA SDWA_ and RCRA are performed in accordance to NELAC protocols Pertinent swnpling information is located on the attached COC Conlidenllal Business lnformation: This report is provided for the exclusi \ e use orthe
~ddressee Pri\ile~es o~ su~seq~enl ~e oft he ~~e of Lhis .cm~pany or nn) ~7mber ofils staff, or reproductio~~ ~f this repo~ in ~on~eclion ... with the a~~~ertisemenl, P~?motio.n ~r sale of ~y ~rodL~cl or p1:?cess, ~r in :onn~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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-002C
Client Sample ID: TW4-24_03092016
Collection Date: 3/9/2016 1009h
Received Date: 3/11/2016 1030h
Analytical Results
Analyzed: 3/14/2016 1226h
Units: jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
52.1
51.0
47.0
49.4
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 22.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 104 72-151
50.00 102 80-152
50.00 94.1 80-124
50.00 98.7 77-129
Report Date: 3/28/2016 Page 7 of 40
All analyses applicable to the CWA. SDWA. and RCRA ore perfom1ed in accordance to NELAC protocols Pertinent sampling information is locnled on the aU ached COC. Confidential Business lnformDlion: This report is provided for the exclllSil'e use of1he
~ddressee Pririle~es o~ sub ... seq~Jenl ~~~e of the ~~1e of this ,cm~pony or any ·~'!lber of its staff, or reproduclio~ ~f this repo~ in .con~lection,.. "ith the u~: ertisemenl. P~?motio.n or sale or~!) ~~ od~cl or pt:?cess, ~r in 7onn:c.tion \\'!th th~ P~-publication or 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. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-002
Client Sample ID: TW4-24_03092016
Collection Date: 3/9/2016 1009h
Received Date: 3/ll/2016 l030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 3/16/2016 1709h £300.0 100 989
Nitrate/Nitrite (as N) mg/L 3/23/2016 1639h E353.2 0.200 29.1
3 -Matrix spike recoveries and/or high RPDs indicate suspected sample non-homogeneity. The method is in control as indicated by the LCS.
Report Date: 3/28/2016 Page 21 of 40
All analyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC Confidential Business Jnformation: This report is proYided for the exclusi\·e use of the
~ddressee Pri' ile~es or sub~seq~ent ~~~e of the ~~e of this _coil!pany or any ~~ber of its slafT, or reproduclio~ ~fthis repo~ in .con~1ection ... with the a~:ertisement. P~?motio.n ':J ~ale of~~). ~rodt~cl or P~?cess, ~r in ;onn:c~ion "!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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603259-001C
Client Sample ID: TW4-25_03092016
Collection Date: 3/9/2016 956h
Received Date: 3/11/2016 1 030h
Analytical Results
Analyzed: 3/14/2016 1206h
Units: J!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 51.9
460-00-4 51.4
1868-53-7 47.9
2037-26-5 49.9
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method:
CAS Reporting
Number Limit
56-23-5 1.00
67-66-3 1.00
74-87-3 1.00
75-09-2 1.00
Amount Spiked %REC
50.00 104
50.00 103
50.00 95.7
50.00 99.8
SW8260C
Analytical
Result
< 1.00
< 1.00
< 1.00
< 1.00
Limits
72-151
80-152
80-124
77-129
Qual
Qual
Report Date: 3/28/2016 Page 6 of 40
All anol~ ses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the allached COC Confidential Business lnformalion: This repon is pro\'ided for 1he exclusi\·e use of the
~ddressee Pri,·iJe~es o,r sub .. seq~tenl ~~e or the ~?':'e of this .cor1_1pany or M) '~'!lber of its starr, or reproductio~ ~f this repo~ in ~0~1ection .. \\ilh then~~ ertiset"!lent ~J~?motio,n ~~ sale of ?J!Y ~rod~cl or P•.ocess, ~r in 7onn:_c~ion w!Lh th~ r~-publicaLion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84I19
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: I st Quarter Chloroform 20 I6
Lab Sample ID: I603259-00I
Client Sample ID: TW4-25_030920I6
Collection Date: 3/9/20I6 956h
Received Date: 3/Il/20I6 1030h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg!L 3/16/2016 2031h E300.0 IO.O 62.7
Nitrate/Nitrite (as N) mg/L 3/12/2016 1103h E353.2 O.IOO 0.837 '@
@-High RPD due to suspected sample non-homogeneity or matrix interference.
1 -Matrix spike recovery indicates matrix inteiference. The method is in control as indicated by the LCS.
Report Date: 3/28/2016 Page 20 of 40
All annlyses applicable to the CWA. SOW A. and RCRA are per:IOm1ed in accordance to NELAC protocols Pertinent sampling infonnation is locuted on Lhe aU ached COC Confidential Business [nformu1ion: This report is provided for the exclush e use of I he ~ddressee Pri\·ile~es or sub~seq~enl ~1?e of the ~~e of this .co~pany or any ~mber of its staff, or reproductio~ ~~this repo~ in .co~eclion .. \\ilh the <l~vertisement. P~?moti~n or sale of ?J~) ~rodL~cl or P~?cess, ~r in ~nn~c.tion '\!th th~ n~-publicalion of this report
3440 South 700 West
;;a!t 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 2016
Lab Sample ID: 1603400-014C
Client Sample ID: TW4-26_03162016
Collection Date: 3/16/2016 748h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1842h
Units: !!giL Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.2
Surr: 4-Bromofluorobenzene 460-00-4 52.6
Surr: Dibromofluoromethane 1868-53-7 47.7
Surr: Toluene-dB 2037-26-5 50.1
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 1.80
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 100 72-151
50.00 105 80-152
50.00 95.4 80-124
50.00 100 77-129
Report Date: 4/1112016 Page 43 of 62
All analyses applicable to the CWA SDWA_ and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on a1e aU ached COC. Confidential Business Information: This report is prO\•ided for the exclusi' e use of the
~ddressee Pri\ ile~es orsub .. seq~ent ~~e of the ~~e ofthis.COI~pany or M) ~mber ofils staff, Of reproductio~ ~fthis repo~ in ~on~ection .. \\iUl the n~vertisemenl, P~?moti~n or sale or:u~~ ~rodl~Cl or P~?cess, ~r in ~onn~c~ion \\'!lh lh~ r:-publicalion of this report
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
1603400-014
Client Sample ID: TW4-26 03162016
ANALvncAL LABoRATORIEs Collection Date: 3/16/2016 748h
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: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg!L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/25/2016 015h E300.0 10.0 13.7
3/24/2016 1635h E353.2 0.100 16.9
Report Date: 4/11/2016 Page 20 of62
All analyses applicable to the CW A. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on tl1e allached COC Conlldential Business Information: This report is prO\ ided for the exclusi\ e use of1he
~ddressee Pri' ile~es o_f sub .. seq~ent ~~~e of the ~~e of this .cot~pany or an) ~mber of its staff, or reproductio~ ~~this repo~ in ~on~leclion .. with the a~:ertisemenl, P~?motio.n ~r ~ale of~~ ~rod~cl or P~?Cess, ~r in ~nn:_c~on w~th 1h7 ~p~blicaJion of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
I st Quarter Chloroform 2016
1603400-0 13C
Client Sample ID: TW4-27 03162016
Collection Date: 3/16/2016 736h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1822h
Units: j.!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
49.8
51.4
47.9
49.7
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 2.11
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 99.7 72-151
50.00 103 80-152
50.00 95.9 80-124
50.00 99.5 77-129
Report Date: 4/11/2016 Page 42 of 62
All annl) ses applicnble to the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infomtation is located on the aUached COC Confidential Business Jnform:Jiion: This report is pro' ided for the e.xclusi' e use of the
~ddressee Pri' ile~es or sub ... seq~l ~~~e or the ~~e or this .COI~p•my or M) ~mber of its slafT, or reproducfio~ ~r this repo~ in ~n~eclion .. \\ilh lhe :J~'ertisemenl, p~~molio.n or sale or ~y ~rodl~Cl or p~ocess, ~r in ~onn~c!ion \\'!lh 1h~ r~-publicalion of this repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-013
Client Sample ID: TW4-27 _03162016
"""I vrlcAL LA oonAr oR IEs Collection Date: 3/16/2016 736h
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: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/24/2016 2325h E300.0 10.0 28.0
3/24/2016 1634h E353.2 0.500 25.0
Report Date: 4/11/2016 Page 19 of62
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is locnled on the aU ached COC Confidential Business Information: This report is provided for the exclusi\e use of the
~cldressee. Pri,·ile~es of'sub .. seq~enl ~~e of the ~~e of this .co~pany or nn) 1~mbe1 of its staff, or reproductio~ ~f this repo~ in ~o~ection ... "ith lhe a~vertisement. P~?moti~n or saJe of:U~~-~•odl~ct or P~?cess, ~r in ~onn~c~ion w~th 1h~ r~-publication orlhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-004C
Client Sample ID: TW4-28_03152016
s Collection Date: 3/15/2016 656h
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: 3/18/2016 1 040h
Analytical Results
Analyzed: 3118/2016 1424h
Units: J.lg/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
46.0
50.8
48.6
50.8
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 91.9 72-151
50.00 102 80-152
50.00 97.1 80-124
50.00 102 77-129
Report Date: 4/11/2016 Page 33 of62
All analyses applicable ro the CWA. SDWA. and RCRA are perrom1ed in accordam:e to NELAC protocols. Pertinent sampling information is locnted on the au ached COC Confirlentio.l Business Information: This report is prO\'ided ror the exclusiYe use of the
~ddressee Pri\ ile~es or sub;eq~enl .u:e or the ~~le or this .cOl~lpa.ny or anr J~mber of its slnlT, or reproduclio.~ ~fthis repo~ in ~on~lectioo ... \\ilh the D~ver1isemenl, p~~motio.n ~r sale of :U!}, ~rodl~Cl or p~ocess, ~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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-004
Client Sample ID: TW4-28_03152016
Collection Date: 3/15/2016 656h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/23/2016 1416h
3/24/2016 1651h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 61.6
E353.2 0.200 34.0
Report Date: 4/11/2016 Page 10 of62
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the altached COC Confidentiul Business Information: This report is provided for the exclusi\ e use of the
~ddressee. Pri\ ile~es o~sub .. seq~ent ~~e oft he ~:u:"e of this .co~pany or an) ~mber ofiiS staff, or reproduclio~ ~f this repo~ in .con~ection,.. \\ilh t.he a~\ertisemenl, P~?motio.n or sale of~~~. ~rodl~ct or P•,?cess, ~r in ~nn~c~ion w~th th~ r~-publication of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-021C
Client Sample ID: TW4-29 _ 03172016
Collection Date: 3/17/2016 845h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1614h
Units: ~-tg/L Dilution Factor: 10
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
482
553
494
518
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/18/2016 1510h
Units: ~-tg/L Dilution Factor:
67-66-3 10.0 335
Amount Spiked %REC Limits Qual
500.0 96.3 72-151
500.0 Ill 80-152
500.0 98.8 80-124
500.0 104 77-129
Method: SW8260C
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 CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 47.7 50.00 95 .4 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.9 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 48.9 50.00 97.8 80-124
Surr: Toluene-d8 2037-26-5 49.2 50.00 98.5 77-129
Report Date: 4/11/2016 Page 50 of62
All anal} ses applicable 10 1he CWA. SOW A. and RCRA are periOrmed in accordance to NELAC protocols. Pertinenl sampling information is located 011 the atlached COC. Confidential Business Jnformation: This repor1 is pro\'ided for the exclusin~ use of lhe ~ddressee Pri' ile~es o.r sub .. seq~ent ~~e or lhe ~~e of this .co•~pw1y or any ~mber of its staff, or reproducli~ ~~this repo~ in ~on~eclion .. with the a~'ertisemenl. P~?moli~n or sale of?'!~: ~rod~cl or P~?cess, ~r in ~onn~c!ion w!th th~ r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: I st Quarter Chloroform 2016
Lab Sample ID: 1603400-021
Client Sample ID: TW4-29 _03172016
Collection Date: 3/17/2016 845h
Received Date: 3/18/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg!L 3/23/2016 2225h E300.0 10.0 40.3
Nitrate/Nitrite (as N) mg/L 3/24/2016 1700h E353.2 0.100 2.92
1-Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 4/1112016 Page 27 of62
All anal)ses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnfonnation: Ths report is prO\·ided for the exclusi'e use of the
~ddressee Pri\ ile~es o:sub~seq~enl ~~e of the ~:u:ne ofthis.cOI~pany or an) ~~ber of its staff, or reproduclio~ ~fthis repo~ in ~o~eclion. "'ith the a~~·ertisement, P~?moti'-!n ~rsale of~!). ~roch~cl or p~~s, ~r in ~nn;c~on ''!'h 1h~ r:_-p~blicalion oflhis report
3440 South 700 West
;a It 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 Chloroform 2016
1603400-0 15C
Client Sample ID: TW4-30_03172016
Collection Date: 3117/2016 750h
Received Date: 3/18/2016 I 040h
Analytical Results
Analyzed: 3/18/2016 1902h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
49.8
52.0
47.4
50.5
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 5.16
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 99.7 72-151
50.00 104 80-152
50.00 94.9 80-124
50.00 101 77-129
Report Date: 4/11/2016 Page 44 of 62
All anal) ses applicable to lhe CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is locnted on lhe allached COC Confidential Business Information: This report is prm•ided for the e."clusi\ e use of the
~ddressee. Pri,·ile~es or su~seq~enl ~of the ~:u:"e or this _cot~pnny or nn~ 1~mber of its stnlT, or reproductio~ ~f this repo~ in ~01~ection~ with the o~veniser~ent, P~?motio.n or saJe of~!) ~ro<h~ct or P~?Cess, ~r in ~nn~c~ion w!th th~ r:_-publication of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-015
Client Sample ID: TW4-30_03172016
CollectionDate: 3/17/2016 750h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 106h
3/24/2016 1645b
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 39.6
E353.2 0.100 2.74
Report Date: 4/11/2016 Page 21 of62
AIJ anal) ses applicable to the CWA. SDWA. and RCRA are perfomred in accordance to NELAC protocols. Pertinent sampling infonnatiOil is locnted on the auached COC Con£idenllnl Business Information: This repon is PJO\ ided for I he exclusi\ e use of the
~ddressee Pri' ile~es o.r su~seq~Jenl ~~e of the ~~1e of this .con,lpany or M) 1~mber of its stnff, or reproductio~ ~f this repo~ in ~on?eclion .. widt lhe a~~ertisemenl. P~?motio,n or sale of~~~ ~rodl~t or p~ocess, ~r in ~nn~c~011 w~lh lh~ r~-publication of this repon
3440 South 700 West
;;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax:[phone]
~-mail: [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 2016
Lab Sample ID: 1603400-008C
Client Sample ID: TW4-31_03162016
Collection Date: 3/16/2016 657h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1643h
Units: 11g/L
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor:
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
49.9
52.4
47.9
50.1
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.8 72-151
50.00 105 80-152
50.00 95.7 80-124
50.00 100 77-129
Report Date: 4/11/2016 Page 37 of62
All analyses applicable to the CWA SOW A. and RCRA are perfomted in accordance to NELAC protocols_ Pertinent sampling infonmuion is located on the allached COC. Confidential Business Information: This report is pro\'ided for the exclushe use of the
~ddressee Pri\ ile~es o.f sub .. seq~enl ~e of the ~~e of this .co1~pa.ny or nny ~mber of its stnff, or reproductio~ ~f this repo~ in ~on~\ection ... \\ilh the ~' ertisemenl, P~?motio.n or sale of~!~ ~rodl~CL or p•:ocess, ~r in ~nn:_c~ion \\'~th th~ r~·publicalion of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2016
Lab Sample ID: 1603400-008
Client Sample ID: TW4-31_03162016
Collection Date: 3/16/2016 657h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/24/2016 2127h
3/24/2016 1629h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 31.5
E353.2 0.100 1.84
Report Date: 4/1112016 Page 14 of 62
All nnnl~ ses applic:J.ble to the CWAr SOW A. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infomlation is located on the aU ached COC. Confidential Business lnfonnalion: This report is pro' ided for the e:'Cclush e use of1he
~ddressee Pri\ ile~es o,r sub .. seq~Jent ~~e of the ~~e of this .co1~pany or n.nr ~mber of its slafT, or reproduclio~ ~fthis repo~ in ~ll~lection .. wlth lhe ~Yertisemenl, p~~motio.n or sa1e of ~~y ~rodl~l or p~ocess, ~r in ~nn:C.tion \\'~lh th~ r~·publicaJion of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
:lalt 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 2016
Lab Sample ID: 1603400-005C
Client Sample ID: TW4-32_03152016
Collection Date: 3/15/2016 705h
Received Date: 3/18/2016 1 040h
Analytical Results
Analyzed: 3/18/2016 1444h
Units: J.tg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
49.9
50.6
49.2
50.3
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.8 72-151
50.00 101 80-152
50.00 98.4 80-124
50.00 101 77-129
ReportDate: 4/11/2016 Page34of62
All anal) ses applicable to the CW A. SOW A.. and RCRA are perfom1ed in Clccordance to NELAC protocols. Pertinenl sampling information is localed on the allached COC. Confidential Business lnfonnalion: This report js pro\'ided for the exclusi\ e use of the
~ddressee Pri\ ile~es o.fsub~seq~enl .u~e orthe ~~e oflhis.cOI~puny or anr ~mber of its staff, or reproductio~ ~fthis repo~ in ~on?ection ... with the~' ertisemenl, P~?motio.n or sale of~~· ~rodl~CI or p~ocess, ~r in ':"nm;_c~ion w!th 1h~ r:-publication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-005
Client Sample ID: TW4-32_03152016
ANotvneAt LAoonAronlta Collection Date: 3/15/2016 705h
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: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/23/2016 1433h E300.0 10.0 64.2
3/24/2016 1652h E353.2 0.100 4.48
Report Date: 4/11/2016 Page II of62
All anal)ses applicable to the CWA_ SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Per1inent sampling information is located on the atlached COC. Confidential Business lnformalion: This reporl is proYided for the exclusi\ e use of the
~dressee Pri,-ile~es or su~seq~enl ~~e of the ~~e of this ~CO!~pany or anr J~mbel of its staff, or reproductio~ ~f this repo~ in ~OI~ection~ with lhe a~\ er1isemenl, P~?motio.n or saJe of~!~~ ~rodl~CI or p~ocess, ~r in ~onn~c~ion w~th 111~ r~-publicalion of Ill is 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
Laboratmy Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-020C
Client Sample ID: TW4-33_03172016
Collection Date: 3/17/2016 838h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1451h
Units: 11g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
48.0
51.1
49.8
49.9
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 < 1.00
67-66-3 1.00 122
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 96.1 72-151
50.00 102 80-152
50.00 99.6 80-124
50.00 99.9 77-129
Report Date: 4/11/2016 Page 49 of 62
All analyses applicable lo the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located onlhe aU ached COC Conlidentinl Business rnfonmtlion: This report is provided for the exclusi' e use of the
~ddressee. Pri,·ile~es or sub ... seq~ent ~~e of the ~~e of this .co':'pruly or rul) J~mber of its staff, or reproduclio~ ~r lhis repo~ in ~~eclion~ \\iLh Lhe ~\ertisemenl, P~?molio.n ~r :ale of~;.~' ~rodL~CL or P•,ocess, ~· in ~nn;c~ion "'!'h th~ r:_-publication of this •eport
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 2016
Lab Sample ID: 1603400-020
Client Sample ID: TW4-33_03172016
Collection Date: 3/17/2016 83 8h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3123/2016 2135h
3/24/2016 1653h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 46.2
E353.2 0.200 2.13
Report Date: 4/11/2016 Page 26 of62
All anal) ses opplicnble to the CWA, SOWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the auached COC ('onfidenlinl Business lnformalion: This report is proYided for the exclusi\e use of1he
~ddressee Pri' ile~es of' su~seq~ent ~e of the ~~~e of this .co1~pm1y or an) r~mber of its staff, or reproduclio~ ~fthis repo~ in .con~ecfion~ wilh the rte!"ertise~tent p~~moti~n or sale of~!), ~lodl~CI or p~ocess, ~r in ~~c!ion w~th th~ r~-p~bfication of 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
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
1603400-009C
TW4-34 03162016
Collection Date: 3/16/2016 705h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1703h
Units: !!giL Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzcne
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
51.1
53.6
49.5
51.3
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 102 72-151
50.00 107 80-152
50.00 99.0 80-124
50.00 103 77-129
Report Date: 4/11/2016 Page 3 8 of 62
All anal~ses applicable to the CW A. SDWA. and RCRA me performed in accordance to NELAC protocols Pertinent sampling information is localed on the attached COC Confidential Business Information: This repon is pro\•ided for the exclusi\ e use of the
~ddressce. Pri,·ile~es or su~eq~nt ~e of the ~~le of this .cor~pany or any J~mber of its staff, or reproductio~ ~f l.his repo~ in 7o~ection ... "~th the ~~ertisemenL P~?motio,n o.r sale of~!) ~rodl~Cl or p~ocess, ~r in ~nn~c~ion w!th 1h~ r~-publication of this reporl
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 2016
Lab Sample ID: 1603400-009
Client Sample ID: TW4-34_03162016
Collection Date: 3/16/2016 705h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
3/24/2016 2217h
3/24/2016 1630h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 17.3
E353.2 0.100 0.925
Report Date: 4/11/2016 Page 15 of62
All anab ses applicoble to the CW A. SDWA. and RCRA are performed in RCcordance to NELAC protocols Pertinent sampling infomullion is located on the auached COC Confidential Business lnformotion: This report is provided for the exclusi' e use of the
~ddressee Pri\ ile~es o,r sub .. seq~enl ~~~e of the ~~e of this .cm~pany or an) ~mber of its staff, or reproductio~ ~f this repo~ in ~oO?ecliOI~ with the a~' ertisement. P~?moli":" ~r sale of ~Y. ~rodl~cl or p~ocess, ~r in ~nn~~ion w~th th? r:·publica!ion of this report
American West ANALYTICAL lABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-0lOC
Client Sample ID: TW4-35_03162016
Collection Date: 3/16/2016 713h
Received Date: 3/18/2016 1 040h
Analytical Results
Analyzed: 3/18/2016 1723h
Units: 1-lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 50.4
460-00-4 52.0
1868-53-7 48.1
2037-26-5 50.6
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 101 72-151
50.00 104 80-152
50.00 96.1 80-124
50.00 101 77-129
Report Date: 4/11/2016 Page 39 of62
All anab ses applicable to the CWA SDWA, and RCRA me perfonned in accordance to NELAC protocols Peninenl sampling information is Jocoted on a1e atlached COC Confidential Business Information: This repon is provided for the exclusive use of the
~ddressee Pri\ ile~es o: sub .. seq~enl ~~e of the ~~e of this .co"_lpuny or tul)' 1~mber of its stall, or reproductio~ ~f this rep01~ in ~Oil~leclion .. \\ilh the at!' ertisement, P~?motio.n or saJe of ?J!Y ~rodl~ct or p~ocess, ~r in ~onn:_c~ion w~lh th7 n;-publicaJion of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chlorofonn 2016
Lab Sample ID: 1603400-0 I 0
Client Sample ID: TW4-35_03I620I6
ANALYTICAl LABORATORI Es Collection Date: 3/l6/20I6 713h
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: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/24/2016 2234h E300.0 10.0 35.4
4/7/2016 l529h E353.2 0.100 0.521
Report Date: 4/11/20 16 Page 16 of 62
All analyses applicable to the CWA. SDWA_ and RCRA are performed in accordance to NELAC protocols Pertinent sampling infonnalion is located on the attached COC Confidential Business Information: This report is pro\'ided for the exclusi\ e l!'>e of the
~ddressee Pri\ ile~es o_fsub .. seq~enl ~~e of the ~~e of this.cot~pany or M)' ~mber of its struT, or reproductio~ ~~this repo~ in .co"'?eclion~ \\ilh Lhe a~vertise~enl, P~?motio.n ~r sa1e of?J!Y ~rodl~CI or pt:ocess, ~r in ~nm;c~ion w~lh th~ r~-publicalion of 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 2016
Lab Sample ID: l603400-007C
Client Sample ID: TW4-36_03162016
Collection Date: 3/1 6/2016 649h
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3/18/2016 1543h
Units: J.lg/L Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
56-23-5
67-66-3
74-87-3
75-09-2
Result Amount Spiked
49.8 50.00
51.8 50.00
48.5 50.00
50.9 50.00
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
%REC Limits Qual
99.5 72-151
104 80-152
97.0 80-124
102 77-129
Report Date: 4/11/2016 Page 36 of 62
All analyses applicable to lhe CWA, SDWA. and RCRA are perfom-.ed in accordance to NELAC protocols. Pertinent sampling information is located on the allached COC Conridenrial Business Jnformation: This repor1 js provided for the exclusi,·e use of lhe
~ddressee Pri\ ile~es or sub,seq~enl ~e of the ~~1e of this .co1~pru1y or nn.\• ~'!lber of ilS staff, or reproductio~ ~~ Lhis repo~ in ~~eclion~ with the ~vertisement P~?motio,n or sale of ?'!Y ~rodt~ct or p~ocess, ~r in ~nn~c~ion \\'!lh 1h~ r~-p~blication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-007
Client Sample ID: TW4-36 03162016
Collection Date: 3/16/2016 649h
Received Date: 3/18/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 3/23/2016 1507h E300.0 10.0 67.1
Nitrate/Nitrite (as N) mg/L 417/2016 1527h E353.2 0.100 < 0.100
1-Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 4/1112016 Page 13 of 62
All anal) ses applicnble lo lhe CWA. SDWA. and RCRA are perfomled in accordance to NELAC protocols. Pertinent sampling information is located on the allached COC Confidential Business lnformution: This repor1 is pro\ ided for the exclusi\e use of the
~ddressee Pli\·ile~es or su~seq~enl ~~e of the ~~e of !his .co~1pany or arl)' ~mbe1 of its slruf, or reproduclio!~ ~f this repo~ in ~0/~leclion ... with the U~\ ertiset~nL P~?molio.n ~r sale of~!_). ~rod~cl or p~ocess, ~r in ~nn~c.tioll w~th lh~ r:publica.tion of this repon
American West
ANALYTICAL LABORATOR I ES
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: lst Quarter Chloroform 2016
Lab Sample ID: 1603259-013C
Client Sample ID: TW4-37_03092016
Collection Date: 3/9/2016 1025h
Received Date: 3/11/2016 1030h
Analytical Results
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Analyzed: 3/15/2016 1533h
Units: J.Lg/L Dilution Factor: 100 Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 100 17,500
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,080
5,030
4,880
5,000
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 3/14/2016 1602h
Units: J.Lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 52.0
Surr: 4-Bromotluorobenzene 460-00-4 51.8
Surr: Dibromotluoromethane 1868-53-7 49.9
Surr: Toluene-d8 2037-26-5 49.7
5,000 102 72-151
5,000 101 80-152
5,000 97.5 80-124
5,000 99.9 77-129
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 15.8
74-87-3 1.00 3.57
75-09-2 1.00 1.34
Amount Spiked %REC Limits Qual
50.00 104 72-151
50.00 104 80-152
50.00 99.8 80-124
50.00 99.4 77-129
Report Date: 3/28/2016 Page 18 of 40
All anolrses applicable to the CWA_ SDW A. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling informnlion is located on the attached COC. Confidential Business Information: This report is provided for 1he exclusi' e use of the
~ddressee Pri\ ile~es o~sub,..seq~enl ~~e oft he ~~e of this .co~pany or nn) l'~_:~ber of its staff, or reproduclio~ ~fthis repo~ in ~o~teclion .. \\ilh lhe a~\·ertisemenl, P~?molio.n o_r sale of~~y ~rod~cl or p~ocess, ~r in ~onm;c~ion w~th 1h~ r~-p~blicalion of !his report
3440 South 700 West
~alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Client Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
1603259-013
TW4-37 03092016
Collection Date: 3/9/2016 1 025h
Received Date: 3/ll/2016 l030h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/16/2016 1941h
3/23/2016 1643h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 332
E353.2 0.200 28.4
Report Date: 3/28/2016 Page 32 of 40
All anal~ ses applicnble to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infonnation is located on the allached COC Confidential Business lnformalion: This report is pro\'ided for the exclusiYe use oflhe
~ddressee Pri\ ile~es o.f sub ... seq~enl ~?e of the ~~':ne of this .co1~pm1y or an) ~mbe1 of its staff, or reproductio~ ~~this repo~ in 7o~ection ... \ViLh the ru_!~ertise~ent, P~?motio_n ~r ~aJe of~!~. ~rod~cl or P~?cess, ?r in ~nn~c~ion w~th 1h~ r~-publicat.ion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 16034 79-006C
Client Sample ID: TW4-60_03222016
Collection Date: 3/22/2016 1500h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1439h
Units: Jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 51.6
460-00-4 51.8
1868-53-7 50.0
2037-26-5 51.0
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 103 72-151
50.00 104 80-152
50.00 99.9 80-124
50.00 102 77-129
Report Date: 3/30/2016 Page 10 of27
All anal~ses applicable to the CWA~ SDWA. and RCRA are l)erfom1ed in accordance to NELAC protocols Pertinent sompling information is locoted on the aU ached COC Confidential Business lnfonnation: This report is provided fort he exclusi\e use of the
~ddressee Pri,·ile~es o!sub .. seq~ent ~~e of the ~~e of this .co1~pany or any 1~mbeJ of its staff, or reproductio~ ~fthis repo~ in ~on~eclion~ \\·ith the a~vertisemenl, P~?motio.n o.r sale or~!) ~rodl~l or p~ocess, ~r in c;onnt;c~ion w~lh th~ r:·publicaJion or this report
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
16034 79-006
Client Sample ID: TW4-60 03222016
ANALYTICAL LABoRATOR I Es Collection Date: 3/22/2016 1500h
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: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
3/25/2016 1129h E300.0 1.00 < 1.00
3/24/2016 1733h E353.2 0.100 <0.100
Report Date: 3/30/2016 Page 18 of27
All analyses applicable to the CWA. SDWA, and RCRA we performed in accordance to NELAC protocols Pertinent sampling information is located on l11e aU ached COC Confidential Business lnformation: This report is provided fort he exclusi\ e use oft he
~ddressee Pri\ i\e~es o.fsub~seq~enl ~~~e of the ~~e of this .co1~pru1y or an~ ~~~~her of its staff, or reproductio_~ ~!this repo~ in ~~1ection ... ''~Lh lhe a~vertisement, P~?motio.n ~r ~aJe of~!~. ~rodt~cl or P:?cess, ?r in ~onm;c~ion w~lh th~ n~-p~blication of Ill is report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603400-024C
Client Sample ID: TW4-65_03152016
Collection Date: 3/15/2016 656h
Received Date: 3/18/2016 I 040h
Analytical Results
Analyzed: 3/18/2016 1550h
Units: 1-1g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
48.3
50.6
49.3
50.7
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 96.5 72-151
50.00 101 80-152
50.00 98.7 80-124
50.00 101 77-129
Report Date: 4/1112016 Page 53 of62
All anal)ses applicable lo I he CW A. SDW A. and RCRA are performed in accordance to NELAC protocols. Pe1tinen1 sampling infonnalion is located on the allached COC. Confidential Business Information; This report is provided fort he exclusi,·e use of the
~ddressee Pri,·ile~es o_f sub ... seq~ent ~~e of I he ~:u:ne of this .cm~pany or rul)' ~mber of its staff, or reproductio~ ~fthis rep01! in ~on~ection,.. with the a~vertisemenl, P~?molio.n or ~ale of ~~y ~rodL~CL or P~?cess, ~r in ~nn~c~ion w~lh th~ r~-publicalion of this report
3440 South 700 West
:lalt 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 2016
Lab Sample ID: 1603400-024
Client Sample ID: TW4-65_03152016
Collection Date: 3/15/2016 656h
Received Date: 3/18/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/23/2016 2259h
3/24/2016 1735h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 61.4
E353.2 0.200 32.6
Report Date: 4/1112016 Page 29 of62
All uno\~ ses applicable to the CW A. SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on lhe attached COC, Confidential Business lnformalion: This report is provided for the exclusi' e use of the
~ddressee Pri' ile~es o.r sub .. seq~enl ~~e of the ~~e of this .con;pany or an) ~mber ofils slaJT, or reproduclio~ ~f lhis repo~ in ;o~ection ... nilh lhe ~vertisement, P~?molio.n or sale of~!) ~rodL~cl or p~cess, ~r in ~onn~c~ion w!th th: r:_-publicalion of this 1epor1
3440 South 700 West
)a It 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 2016
Lab Sample ID: 1603479-007C
Client Sample ID: TW4-70_032220!6
Collection Date: 3/22/2016 1230h
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1459h
Units: J..lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 50.1
Surr: 4-Bromofluorobenzene 460-00-4 51.0
Surr: Dibromofluoromethane 1868-53-7 48.8
Surr: Toluene-d8 2037-26-5 49.7
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 100 72-151
50.00 102 80-152
50.00 97.5 80-124
50.00 99.5 77-129
Report Date: 3/30/2016 Page II of 27
All ann lyses applicnble to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located 011 the allached COC Conlidential Business Information: This report is provided for the exch1si\ e use of the
~ctdressee Pri\ ile~es o~ su~seq~enl ~e of the ~~e of this .con.lpany or an) 1~mbe1 of its staff, or reproductio~ ~ftJlis repo~ in ~~eel ion~ \\ith the rn!vertisemenL P~?moti~ or saJe of~!) ~rodL~Cl or P•.ocess, ~r in c;:onm;_c~ion \\ !th th~ r:-publication of this 1eport
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
Laborat01y Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 1st Quarter Chloroform 2016
Lab Sample ID: 1603479-007
Client Sample ID: TW4-70_03222016
Collection Date: 3/22/2016 1230h
Received Date: 3/23/2016 930h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
3/25/2016 1022h
3/24/2016 1734h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 36.4
E353.2 0.100 0.119
Report Date: 3/30/2016 Page 19 of27
All anal~ ses applicable to the CWA. SDWA. and RCRA are perfomled in accordance to NELAC protocols Pertinenl sampling information is located on the atlnched COC Confidential Business lnfonnalion: This report is pro\•ided for the e~clusi,·e use o[lhe
~ddressee Pri,·ite~es or sub ... seq~ent ~e of the ~~1e of this _coL~p<Uly or art) l~mber of its stn.IT, or reproductio~ ~f this repo~ in ~o~eclion ... \\ith the a<!' ertisement P~?motio.n or sale of ?J!~ ~nxf~ct or P•.ocess, ~r in ~onn~c~ion w~lh th~ r~-publication of this rt:por1
3440 South 700 West
;;a It Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
16034 79-008A
Client Sample ID: Trip Blank
Collection Date: 3/21/2016
Received Date: 3/23/2016 930h
Analytical Results
Analyzed: 3/23/2016 1519h
Units: J.!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 49.9
460-00-4 49.3
1868-53-7 49.2
2037-26-5 49.2
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 99.8 72-151
50.00 98.6 80-152
50.00 98.4 80-124
50.00 98.3 77-129
Report Date: 3/30/2016 Page 12 of27
All anab ses applicable lo the CWA. SDWA. and RCRA llre performed in accordance to NELAC protocols Pertinenl sampling information is localed on the allached COC Conlidenliul Business Jnf01malion: TI1is report is pro,·ided for the e:xclusi' e use of 1he ~ddressee Pri\ ile~es o.r sub .. seq~enl ~~e of Lhe ~~e of this .c01~pany or an~ r~mbe1 of its si[IIT, or reproduclio~ ~f this repo~ in ~Jeclion .. ''ilh the ~vertisemenL P~?motio.n o.r saJe of ?J!) ~rodl~cl or P'.ocess, ~r in ~onn~~ion w~lh th~ r~-publication or this 1epon
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 Chloroform 2016
1603400-023A
Client Sample ID: Trip Blank
Collection Date: 3/14/2016
Received Date: 3/18/2016 1040h
Analytical Results
Analyzed: 3118/2016 143lh
Units: J.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
47.6
53.9
49.3
50.2
Contact: Garrin Palmer
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
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
Amount Spiked %REC Limits Qual
50.00 95.2 72-151
50.00 108 80-152
50.00 98.6 80-124
50.00 100 77-129
Report Date: 4/11/2016 Page 52 of 62
All anal~ ses appliC<Jble to Lhe CWA, SDWA. and RCRA are perfom1ed in accordMce to NELAC protocols Pertinent sampling information is locoled on the allached COC Confidential Business lnformalion: This repon is provided for the exclush e use of I he
~ddressee. Pri\·ile~es o_r sub ... seq~enl ~~e of the ~~e of this .cm~pany or any J~mbe1 of its starr, or reproductio~ ~fthis repo~ in ~on~eclion~ \\ilh the a~\ ertisemenl, P~?molio.n ':r srue or ?J~Y ~rod~cl or p~~cess, ~r in ~onn~c~ion w~lh th~ n;_·publication or I his 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
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
1603259-014A
Client Sample ID: Trip Blank
Collection Date: 3/9/2016
Received Date: 3/11/2016 1030h
Analytical Results
Analyzed: 3/14/2016 ll46h
Units: 11g/L Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
51.5
51.7
48.6
50.4
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
Amount Spiked %REC Limits Qual
50.00 103 72-151
50.00 103 80-152
50.00 97.1 80-124
50.00 101 77-129
Report Date: 3/28/20 16 Page 19 of 40
All annl)ses !lpplicoble to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on Lhe al1ached COC Conridentwl Business Jnfonnation: This report is proYided for the exclush e use of the
~ddressee Pri' ile~es o_f sub__seq~ent ~~e or the ~~Ie of this .cot~ pan) or any 1~mber or its staff, or reproductio~ ~~this repo~ in .co~ection~" ilh !he D~vertisemenl p~omolio.n ~r ~ale of~). ~rodl~cl or p1:?cess, ~r in ~01m~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
Garrin Palmer
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2016
Dear Garrin Palmer: Lab Set ID: 1603259
American West Analytical Laboratories received sample(s) on 3/11/2016 for the analyses
presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
Thank You, Digitally signed by Jose G.
G Rocha
DN: cn=Jose G. Rocha,
• o=American West Analytical Jose
Rocha
Laboratories, ou,
email=[e-mail],
c=US
Date: 2016.03.28 13:36:58 Approved by: .__ _______ -os_·o_o· ____ __.
Laboratory Director or designee
Report Date: 3/28/2016 Page 1 of 40
All anal~ ses applicnble to the CWA. SDWA. and RCRA !lfe performed in accordtmce to NELAC protocols Pertinenl sampling information is locflted on the attached COC ConfidentiDI Business Information: This report is prorided for the c"'iclusin use of the
~ddressee Pri,·ile~es o,r sub~seq~enl ~e of lhe ~~e of this .con;pnny or any 1~mber of its stniT, or reproduclio~ ~f this repm; in .con?eclion ... \\ilh then~\ ertisement, P~?molio.n or saJe of :U2Y ~~ odl~CI or p~ocess, ~r i11 :onn:c~ion w!th th~ r~-puhtic:auou or this report
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
ANALYTICAL LABORATOR IES Project: I st Quarter Chlorofonn 20 I6
Lab Set 10: I603259
Date Received: 3/11/2016 I030h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1603259-00IA TW4-25 030920I6 3/9/2016 956h Aqueous Anions, E300.0
;a(t Lake City, UT 84119 I603259-00IB TW4-25 03092016 3/9/20I6 956h Aqueous Nitrite/Nitrate (as N), E353.2
1603259-00IC TW4-25 03092016 3/9/2016 956h Aqueous VOA by GC/MS Method
8260C/5030C
Phone: [phone] I603259-002A TW4-24 03092016 3/9/2016 1009h Aqueous Anions, E300.0
I603259-002B TW4-24 030920I6 3/9/2016 I009h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] I603259-002C TW4-24 030920I6 3/9/2016 1009h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260C/5030C
~-mail: [e-mail] I603259-003A TW4-21_030920I6 3/9/20I6 947h Aqueous Anions, E300.0
1 603259-003B TW4-21 03092016 3/9/20I6 947h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1603259-003C TW4-21 _03092016 3/9/20I6 947h Aqueous VOA by GC/MS Method
8260C/5030C
I603259-004A TW4-01 030920I6 3/9/2016 1217h Aqueous Anions, E300.0
Kyle F. Gross I603259-004B TW4-01 030920I6 3/9/2016 1217h Aqueous Nitrite/Nitrate (as N), E353.2
I603259-004C TW4-01_030920I6 3/9/20I6 I217h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
I603259-005A TW4-04 030920I6 3/9/20I6 I225h Aqueous Anions, E300.0
Jose Rocha 1603259-005B TW4-04 030920I6 3/9/2016 1225h Aqueous Nitrite/Nitrate (as N), E353 .2
QA Officer 1603259-005C TW4-04 030920I6 3/9/2016 1225h Aqueous VOA by GC/MS Method
8260C/5030C
1603259-006A MW-04 030920I6 3/9/2016 1210h Aqueous Anions, E300.0
1603259-006B MW-04 03092016 3/9/20I6 1210h Aqueous Nitrite/Nitrate (as N), E353.2
I603259-006C MW-04 03092016 3/9/20I6 I210h Aqueous VOA by GC/MS Method
8260C/5030C
1603259-007A TW4-02 030920I6 3/9/2016 I201h Aqueous Anions, E300.0
I603259-007B TW4-02 03092016 3/9/20I6 I20Ih Aqueous Nitrite/Nitrate (as N), E353.2
I603259-007C TW4-02 03092016 3/9/2016 120Ih Aqueous VOA by GC/MS Method
8260C/5030C
I603259-008A MW-26 030920I6 3/9/2016 1044h Aqueous Anions, E300.0
1603259-008B MW-26 03092016 3/9/2016 1044h Aqueous Nitrite/Nitrate (as N), E353.2
1603259-008C MW-26 03092016 3/9/2016 1044h Aqueous VOA by GC/MS Method
8260C/5030C
1603259-009A TW4-11 03092016 3/9/2016 1153h Aqueous Anions, E300.0
1603259-009B TW4-11 03092016 3/9/2016 1153h Aqueous Nitrite/Nitrate (as N), E353.2
1603259-009C TW4-11 03092016 3/9/2016 1153h Aqueous VOA by GC/MS Method
8260C/5030C
1603259-0IOA TW4-22 03092016 3/9/2016 1018h Aqueous Anions, E300.0
I603259-010B TW4-22 03092016 3/9/2016 1018h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 3/28/2016 Page 2 of40
All analyses applicable to the CWA, SDWA. and RCRA me perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the all~ched COC Conridential Business Information: This report is provided for the exclusi,·e use oft he
~ddressee Pri\ ile~es ofsub .. seq~lenl ~~~e or the ~~e or this .co1~pony or on~ l'~mbe1 of its stnff, or reproductim~ ~f this repo~ in .con?ection~ with the 11'!_\ ertisemenl. P~?molio.n or sale of~!~ ~•Odl~Cl or P•.ocess, ~r in ~onn~c~ion w~th th? r:-publicaliotl of this report
Client:
Project:
American West Lab Set ID:
ANAL vT 1 cAL LA eo R A ToR 1 E s Date Received:
Lab Sample ID
1603259-010C
3440 South 700 West 1603259-011A
)alt Lake City, UT 84119 1603259-0118
1603259-011 c
Phone: [phone] 1603259-012A
1603259-0128
Toll Free: [phone] 1603259-012C
Fax: [phone]
~-mail: [e-mail] 1603259-013A
1603259-0138
web: www.awal-1abs.com 1603259-0 13C
1603259-014A
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Energy Fuels Resources, Inc.
1st Quarter Chloroform 2016
1603259
3/11/2016 1030h
Client Sample ID
TW4-22 03092016
TW4-19 03092016
TW4-19 03092016
TW4-19 03092016
TW4-20 03092016
TW4-20 03092016
TW4-20 03092016
TW4-37 03092016
TW4-37 03092016
TW4-37 03092016
Trip Blank
Contact: Garrin Palmer
Date Collected Matrix Analysis
3/9/2016 1018h Aqueous VOA by GC/MS Method
8260C/5030C
3/9/2016 1430h Aqueous Anions, E300.0
3/9/2016 1430h Aqueous Nitrite/Nitrate (as N), E353.2
3/9/2016 1430h Aqueous VOA by GC/MS Method
8260C/5030C
3/9/2016 1031h Aqueous Anions, E300.0
3/9/2016 1031h Aqueous Nitrite/Nitrate (as N), E353.2
3/9/2016 1031h Aqueous VOA by GC/MS Method
8260C/5030C
3/9/2016 1025h Aqueous Anions, E300.0
3/9/2016 1025h Aqueous Nitrite/Nitrate (as N), E353.2
3/9/2016 1025h Aqueous VOA by GC/MS Method
8260C/5030C
3/9/2016 Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 3/28/2016 Page 3 of 40
All nnnl)ses applicable to the CWA, SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols.. Pertinent sampli11g inforn\.'\liO&\ is located on the attached COC. Conlidential Business Information: This repon is provided lOr the exclliSiYe use of the ~ddressee Pli\ ile~es or sub ... seq~ent ~~e of the ~:u:ne of this 'COI~pnny or nny J~mber of its stnrT, or ft.."JUoductio~ ~f this repo~ in ~011~1(."(11~ \\ith the u~vertise~enl. P~?motio.n ~r saJe of ?J!): -~rodL~I or P~?cess, ~r in :onn~c~iOII '''!lh ~~ r~~publicntion 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 Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
I st Quarter Chloroform 2016
1603259
3111 /2016
3/9/2016
Intact
None
Holding Time and Preservation Requirements: The analysis and preparation for the
samples were performed within the method holding times. The 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, DUP:
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 I Matrix Spike Duplicates (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, with the
following exceptions:
Sample ID Analyte QC Explanation
1603259-0018 Nitrate/Nitrite MS/RPD Sample matrix interference and
suspected sample non-homogeneity
or matrix interference.
1603259-0028 Nitrate/Nitrite MS/MSD Suspected sample non-homogeneity.
Corrective Action: None required.
Report Date: 3/28/2016 Page 4 of 40
All analyses applicable to the CWA. SDWA. and RCRA we performed in accordnnce to NELAC protocols. Peninent sampling information is located on the auached coc_ Conlirlentinl Business Information: This repon is provided for the exclusi, e use of the
~ctdressee Prh ile~es o.r sub .. seq~ent ~~e of the ~~e of this .co"_lpilllY or nnr ~mbeJ of its stnff, or reproductio~ ~f this repOJ~ in .c01~ection~ with I he n~vertisemenl, P~?motio.n ~r sale of~!) ~rodl~ct or p1.~ess, ~r in ~onn~c~ion w~th 1h? n~-publicn1ion 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
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab SetiD:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
1st Quarter Chloroform 20 16
1603259
3/1112016
3/9/2016
Intact
None
SW-846 8260C/5030C
Volatile Organic Compounds
General Set Comments: Multiple target analytes were observed above reporting limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike I 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: 3/28/2016 Page 5 of 40
All anolyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is locuted on the attached COC Confidential Business Information: This repon is provided for the exclusi' e use of the
~ddressee. Pri,·ile~es o.r su~se<t~tent ~~~e of the ~~r_ne of this .cor~pnny or any r~ml>er of its stnff, or reproduclio~ ~f lhis repo~ in ~~~eclion .. \'vilh lhe a~\enise1~en1. P~?molio_n ~r ~aJe of ~~Y. ~rod~cl or P':?Cess, ~r in ~onm;_c~ion '''!th th~ n;-publication of lhis repon
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: LCS-R88289 Date Analyzed:
Test Code: 300.0-W
Chloride 4.80
Lab Sample ID: LCS-R88185 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.01
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: Garrin Palmer
Dept: we
QC Type: LCS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/16/2016 957h
mg!L E300,0 0.00516 0.100 5.000 0 96.0
03/12/2016 1102h
mg!L E353.2 0.00833 0.0100 1.000 0 101
Lab Sample ID: LCS-R88439 Date Analyzed: 03/21/2016 1454h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.916 mg!L E353.2 0.00833 0.0100 1.000 0 91.6
Lab Sample ID: LCS-R88521 Date Analyzed: 03/23/2016 1629h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.901 mg!L E353,2 0.00833 0.0100 1.000 0 90.1
Limits
90-110
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/28/2016 Page 33 of 40
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnfonnation; This repon is provided for the exclusive use of the addressee Privileges of subsequent use oftt-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertlsement promotlon or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: I st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R88289 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-R88185 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-R88439 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-R88521 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: Garrin Palmer
Dept: we
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/16/2016 940h
mg/L E300.0 0.00516 0.100
03/12/2016 1101h
mg/L E353.2 0.00833 0.0100
03/21/2016 1453h
mg/L E353.2 0.00833 0.0100
03/23/20 16 1628h
mg!L E353.2 0.00833 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 3/28/2016 Page 34 of 40
analyses applicable to the CWA_ SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnformation: This report is provided for the exclusive use of the addressee. Privileges of subsequent use oftt
ne of this company or any member of its statT, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publlcation 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
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chloroform 2016
Contact: Garrin Palmer
Dept: we
QCType: MS
Analyte Result Units Method MDL
Lab Sample ID: 1603259-002AMS Date Analyzed: 03/16/2016 1726h
Test Code: 300.0-W
Chloride 2,000 mg/L E300.0 1.03
Lab Sample ID: 1603259-003AMS Date Analyzed: 03/16/2016 1816h
Test Code: 300.0-W
Chloride 1,440 mg/L E300.0 1.03
Lab Sample ID: 1603259-001BMS Date Analyzed: 03/12/2016 1104h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 12.7 mg/1 E353.2 0.0833
Lab Sample ID: 1603290-00ICMS Date Analyzed: 03/21/2016 1535h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 15.6 mg/L E353.2 0.0833
Lab Sample ID: 1603259-002BMS Date Analyzed: 03/23/2016 1640h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 73.7 mg/1 E353.2 0.417
1-Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Reporting
Limit
20.0
20.0
0.100
0.100
0.500
Amount
Spiked
1,000
1,000
10.00
10.00
50.00
1 -Matrix spike recoveries and/or high RPDs indicate suspected sample non-homogeneity. The method is in control as indicated by the LCS.
Spike Ref.
Amount %REC
989 102
452 99.2
0.837 119
1.48 141
29.1 89.2
Limits
90-110
90-110
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/28/2016 Page 35 of 40
analyses applicable to the CWA, SDWA, and RCRA are performed ln accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information· This report is provided for the exclusive use of the addressee Privileges of subsequent use oftl"
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL
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
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1603259 Dept: we
Project: 1st Quarter Chloroform 2016 QC Type: MSD
Reporting Amount Spike Ref.
Analyte Result Units Method MDL Limit Spiked Amount %REC
Lab Sample ID: 1603259-002AMSD Date Analyzed: 03/16/2016 1743h
Test Code: 300.0-W
Chloride 2,010 mg/L E300.0 1.03 20.0 1,000 989 102
Lab Sample ID: 1603259-003AMSD Date Analyzed: 03/16/2016 1833h
Test Code: 300.0-W
Chloride 1,450 mg/L E300.0 1.03 20.0 1,000 452 100
Lab Sample ID: 1603259-001BMSD Date Analyzed: 03/12/2016 1105h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.3 mg/L E353 2 0.0833 0.100 10.00 0.837 105
Lab Sample ID: 1603290-001CMSD Date Analyzed: 03/21/2016 1536h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 14.3 mg/L E353.2 0.0833 0.100 10.00 1.48 128
Lab Sample ID: 1603259-002BMSD Date Analyzed: 03/23/2016 1641 h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 73.2 mg/L E353 2 0.417 0.500 50.00 29.1 88.1
@-High RPD due to suspected sample non-homogeneity or matrix interference.
1-Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
3 -Matrix spike recoveries and/or high RPDs indicate suspected sample non-homogeneity. The method is in control as indicated by the LCS.
Limits
90-110
90-110
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit
2000 0.241 20
1440 0.669 20
12.7 11.5 10
15.6 8.83 10
73.7 0.735 10
Qual
@
Report Date: 3/28/2016 Page 36 of 40
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftl"
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANAlYTICAl LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chlorofonn 2016
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-Jabs.com
OC SU.l.VIMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-2 031416A Date Analyzed: 03/14/20 16 1 048h
Test Code: 8260-W-DEN100
Chloroform
Methylene chloride
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-2 031516A
Test Code: 8260-W-DENIOO
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.6 llg/L SW8260C
20.0 llg/L SW8260C
49.7 llg/L SW8260C
48.4 !lg/L SW8260C
48.4 !lg/L SW8260C
48.7 llg/L SW8260C
Date Analyzed: 03/15/2016 1119h
20.6 llg/L SW8260C
52.9 !lg/L SW8260C
50.2 llg/L SW8260C
50.8 llg/L SW8260C
49.6 IJg/L SW8260C
0.153 1.00 20.00 0 98.0
0.172 1.00 20.00 0 100
50.00 99.5
50.00 96.9
50.00 96.9
50.00 97.4
0.153 1.00 20.00 0 103
50.00 106
50.00 100
50.00 102
50.00 99.2
Limits
85-124
81-135
80-122
85-121
80-116
81 -123
85-124
80-122
85-121
80-116
81-123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/28/2016 Page 37 of 40
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnfonnation: This repon is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or ln connection with the re-publication of this report for any purpose other than for the addressee will be b'Tanted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB VOC-2 031416A Date Analyzed:
Test Code: 8260-W -DEN! 00
Carbon tetrachloride < 1.00
Chloroform < 1.00
Chloromethane < 1.00
Methylene chloride < 1.00
Surr: 1 ,2-Dich1oroethane-d4 51.7
Surr: 4-Bromofluorobenzene 51.5
Surr: Dibromofluoromethane 48.6
Surr: Toluene-d8 50.6
Lab Sample ID: MB VOC-2 031516A Date Analyzed:
Test Code: 8260-W-DEN100
Chloroform < 1.00
Surr: 1,2-Dichloroethane-d4 53.2
Surr: 4-Bromofluorobenzene 52.2
Surr: Dibromofluoromethane 50.9
Surr: Toluene-d8 50.6
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: MSVOA
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/14/2016 1127h
!{giL SW8260C 0.504 1.00
!{giL SW8260C 0.153 1.00
!{giL SW8260C 0.163 1.00
!{giL SW8260C 0.172 1.00
J.lg/L SW8260C 50.00 103
!{giL SW8260C 50.00 103
!{g/L SW8260C 50.00 97.2
!{giL SW8260C 50.00 101
03/15/2016 1158h
!{giL SW8260C 0.153 1.00
!{giL SW8260C 50.00 106
!{giL SW8260C 50.00 104
!{giL SW8260C 50.00 102
!{giL SW8260C 50.00 101
Limits
80-122
85 -121
80-116
81-123
80-122
85-121
80-116
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/28/2016 Page 38 of 40
analyses applicable to the CWA. SDWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information; This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
i' ANAlYTlCIIL LAB011Af0RIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chloroform 2016
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Method MDL
Reporting
Limit
Contact:
Dept:
QCType:
Amount
Spiked
Garrin Palmer
MSVOA
MS
Spike Ref.
Amount %REC
Lab Sample ID: 1603259-004CMS Date Analyzed: 03/14/2016 1755h
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 1603259-0lJCMS
Test Code: 8260-W-DEN100
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
1,380 J.lg/L SW8260C
442 J.lg/L SW8260C
1,050 J.lg/L SW8260C
977 J.lg/L SW8260C
1,020 J.lg/L SW8260C
982 J.lg/L SW8260C
Date Analyzed: 03/15/2016 1553h
19,200 J.lg/L SW8260C
5,000 J.lg/L SW8260C
4,910 J.lg/L SW8260C
4,860 J.lg/L SW8260C
4,810 J.lg/L SW8260C
3.06 20.0 400.0 974 102
3.44 20.0 400.0 0 110
1,000 105
1,000 97.7
1,000 102
1,000 98.2
15.3 100 2,000 17500 80.8
5,000 99.9
5,000 98.3
5,000 97.2
5,000 96.2
Limits
50-146
30-192
72-151
80-152
80-124
77-129
50-146
72-!51
80-152
80-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/28/2016 Page 39 of 40
analyses applicable to the CWA. SOW A, and RCRA are ptrl'omu~d in accordance tO NELAC PfQIOcols Pertinent sampllng information is located on the attached COC Confidential Business Infonnation: This repon is provided for the exclusive use of the addressee Privileges of subsequent use oftt
ne of this company or any member of its staff, or reproduction orth1s report in connec:tion wuh the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603259
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1603259-004CMSD Date Analyzed:
Test Code: 8260-W-DENIOO
Chlorofonn 1,320
Methylene chloride 430
Surr: 1,2-Dichloroethane-d4 1,040
Surr: 4-Bromofluorobenzene 953
Surr: Dibromofluoromethane 1,010
Surr: Toluene-d8 952
Lab Sample ID: 1603259-0lJCMSD Date Analyzed:
Test Code: 8260-W-DEN100
Chlorofonn 19,900
Surr: 1,2-Dichloroethane-d4 5,040
Surr: 4-Bromofluorobenzene 4,900
Surr: Dibromofluoromethane 4,920
Surr: Toluene-d8 4,920
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
Units Method MDL
03/14/2016 1815h
llg/L SW8260C 3.06
llg/L SW8260C 3.44
llg/L SW8260C
llg/L SW8260C
!lg/L SW8260C
llg/L SW8260C
03/15/2016 1612h
llg/L SW8260C 15.3
llg/L SW8260C
Jlg/L SW8260C
!lg/L SW8260C
Jlg/L SW8260C
Reporting
Limit
20.0
20.0
100
Contact:
Dept:
QCType:
Amount
Spiked
400.0
400.0
1,000
1,000
1,000
1,000
2,000
5,000
5,000
5,000
5,000
Garrin Palmer
MSVOA
MSD
Spike Ref.
Amount %REC
974 85.8
0 107
104
95.3
101
95.2
17500 118
101
97.9
98.4
98.5
Limits
50-146
30-192
72-151
80-152
80-124
77-129
50-146
72-151
80-152
80-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
1380 4.73 25
442 2.80 25
19200 3.76 25
Report Date: 3/28/2016 Page 40 of 40
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftt-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West Analytical Laboratories UL
Denison
WORK ORDER Summary Work Order: 1603259 Page 1 of3
Client:
ClientiD:
Project:
Comments:
SampleiD
1603259-001A
1603259-001B
1603259-001C
1603259-002A
1603259-002B
1603259-002C
1603259-003A
1603259-003B
1603259-003C
1603259-004A
1603259-004B
1603259-004C
1603259-00SA
1603259-005B
1603259-00SC
Printed: 3/1112016
Energy Fuels Resources, Inc. Due Date: 3/22/2016
DENIOO Contact: Garrin Palmer
1st Quarter Chloroform 2016 QC Level: III WO Type: Project
PA Rush. QC 3 (Summary/No chromatograms). RL of 1 ppm for Chloride and VOC and 0.1 ppm for N02/N03-Run N02/N03 at a lOX dilution. Expecte
levels provided by client-see Jenn. J-flag what we can't meet. ElM Locus and EDD-Denison. Email Group.;
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage --
1W4-25_03092016 3/9/2016 0956h 3/11/2016 1030h 300.0-W Aqueous df-wc
1 SELAnalytes: CL ---
N021N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N -8260-W-DENlOO VOCFridge
Test Group: 8260-W-DENIOO; #of Ana/ytes: 4 I# ofSurr: 4 -1W4-24_03092016 3/9/2016 1 009h 3/11/2016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL ---N021N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
1W4-21_03092016 3/9/2016 0947h 3/1112016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL ---
N021N03-W-353.2 df -no2/no3
1 SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN100; #of Analytes: 4 I# of Surr: 4
1W4-01_03092016 3/9/2016 1217h 3/11/2016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL ---N021N03-W-353.2 df -no2/no3
1 SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DENIOO; # ofAnalytes: 4 I# ofSurr: 4 -TW4-04_03092016 3/9/2016 1225h 3/11/2016 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL ---N021N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN/00; #of Analytes: 4 I# ofSurr: 4
FOR LABORATORY USE ONLY [fill out on page 1]: %M 0 RT 0 CN 0 TAT 0 QC 0 HOK __ _ HOK __ _ HOK___ COG Emailed-!.._ ___ _
3
3
3
3
3
WORK ORDER Summary WorkOrder: 1603259 Page2of3
Client: Energy Fuels Resources, Inc. Due Date: 3/22/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603259-006A ~-04_03092016 3/9/2016 1210b 3/11/2016 1030b 300.0-W Aqueous df-wc
I SEL Analytes: CL
1603259~068 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
1603259-006C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DENIOO; #of A11alytes: 4 I# of Su": 4
1603259-007 A TW4-02_03092016 3/9/2016 120 1h 3/11/2016 1 030h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1603259-0078 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603259~07C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Ana[ytes: 4 I# of Surr: 4
1603259-00SA ~-26_03092016 3/9/2016 1044h 3/1112016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603259~088 N02/N03-W-353.2 df -no2/no3
1 SEL Analytes: N03N02N
1603259~08C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analyies: 4 I# of Surr: 4
1603259~09A TW4-11_03092016 3/9/2016 1153h 3/11/2016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603259-0098 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603259~09C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN100; #of Alla/ytes: 4 I# of Su": 4
1603259-010A TW4-22_03092016 3/912016 1018h 3/1112016 1030h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603259-0108 N021N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603259-010C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
1603259~11A 11YV4-19_03092016 3/9/2016 1430h 3/1112016 1030h 300.0-W Aqueous df-wc
I SEL Analytes: CL
1603259~118 N02/N03-W -353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603259-011C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN 1 00; # of Analytes: 4 I # of Surr: 4
1603259-012A 11YV4-20_03092016 3/912016 1031h 3/1112016 1030h 300.0-W Aqueous df-wc
1 SEL Ana~vtes: CL
PriDted: 3/11/2016 FOR LABORATORY USE ONLY [fill out on page 1]: %M 0 RTO CNO TAT 0 aco HOK __ HOK __ HOK __ COC Emailed
WORK ORDER Summary Work Order: 1603259 Page 3 of3
Client: Energy Fuels Resources, Inc. Due Date: 3/22/2016
SampleD> Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603259-0 12B ~4-20_03092016 3/9/2016 103lh 3/11/2016 1030h N02/N03-W-353.2 Aqueous df-no2/no3
1 SEL Analytes: N03N02N
1603259-012C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 4 1 # ofSurr: 4
1603259-013A ~4-37_03092016 3/9/2016 1025h 3/11/2016 1030h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1603259-013B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603259-0 13C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 41 # ofSurr: 4
1603259-014A Trip Blank 3/9/2016 3/11/2016 1 030h 8260-W-DENIOO Aqueous VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 / #of Surr: 4
Printed: 3111/2016 FOR LABORATORY USE ONLY [fill out on page 1]: %M 0 RT 0 CN 0 TAT 0 QC 0 HOK __ _ HOK __ _ HOK___ COC Emailed. ____ _
American West
Analytical Laboratories CHAIN OF CUSTODY 1~ (js2..:sr
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Toll Free# [phone]
All analysis will be conducted using NEU\P accrediled methods and all data will be reported using AWAL's standard anelyte lists and reporting
limits (POL) unless specifically requested otherwise on this Chain ol Custody and/or attached documentation.
AWAL Lab Sample Set#
Page 1 of 2
Fax# [phone] Email [e-mail]
www.awal-labs.com
I ac ~evel: I
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84!5 11
Contact Garrin Palmer
Phone#: [phone] Cell#:
[e-mail]; KWelnel®enerllYfu-'e:ls~.c~o~m:-:;-------­
Email: d-II:Aten~ls.cam
ProJect Name: TANNER HOLLIDAY
Project#: 1ST QUARTER CHLOROFORllrf 2016
PO#: ---------------------------------------------
Sampler Name: TANNER HOLLIDAY
Sample ID:
Date
Sampled
'l'W4-25_03092016 1 3/9/2016
s ITW4-04_03092016 I 3/9/2016
6IMW-o4_03092016 I 3/9/2016
TW4-02_03092016 I 3/9/2016
MW-26_03092016 I 3/9/2016
liTW4-20_03092016 I 3/9/2016
ZITW4-37_03092016 I 3/9/2016
Time
Sampled
956
1009
--
947
1217
1225
1210
1201
1044
1153
1018
1430
1031
1025
!!! <D c: ]i
" 0 ll
0 ..
5
5
5
5
5
5
5
5
5
5
5
5
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w X X X
w X X X
w X X X
w X X X
w X X X
w X X X
w X X X
w X X X
w v v v
w
WI
w X X X
w lxlxlx
Tum Around Time:
Standard
Unless other arrangements have been made, IIOue Date:Vz~ /;
signed reports will be emalled by 5:00 pm on · ;) /'-
the day they are duB. . VI 2.-2--1 '\:'
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
D SDWA
D ELAPIA2LA
D NLLAP
0 Non-Compliance
0 Other.
Known Hazards
&
Sall!Qie Comments
Laboratory. Use O,nly
lsampJ .. w.,.tJ.)I!?':
~ handdelivered 1v:::;;r' 2A~e~·c 3 T emperalure
4 Received Bro~O<V'Loaldng
(tmpnl!>l!flys_eaJ~
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4 Urmmlmncn San-4>1o i!fJ
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PrintNomo: TANNER HOUtDAY
r ollnqtQnedby::-::J . ~~~ I: fecelvedby: ~to: IISpeciallnstructions: I Slpna!uno ...._ (A J\!ll!;.-~/ 3/t0/2at Sl!j11a!UJe .
' 1300 1me:
Prlnl Nome: /
Aollnqult/la11>r,
'S!gMI.unl
PrintNill'nO:
RelinqUiSiiod l>r.
Slgnaturu
Print Name:
Relinquished by: ~J1.nalure
Prill Name:
Dar a:
JThn"'
Date:
lllmo:
Date:
Time:
Roodvod by: Jl7--::./T ·--/
$1Qnatur• ~-~ ~
Print Name:
Received ~Jr.
lslqnature
Print Name:
Recetved by:
Signature
Print Name:
z. ;;I'J_ -& -t!'~ __z
7
o.., -I /-1 (a
fhmo: /a ?.. 11
Date:
Time:
Date:
:nme:
See the Analytical Scope of Work for Reportlng !Jmits and VOC
analyte list.
American West
Analytical Laboratories
463W.3600S. SaltlakeCity,UT 84115
Phone# [phone] Toll Free II [phone]
~ Fax# [phone] Email awaiOawal-labs.com
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] CeU#:
gp&lm.,..elle;g;:/uds.com: B:WdnolOeoetgyfuels.com:
Email: dturl<@eaergyfuela.com
Project Name: TANNER HOLLIDAY
Project#: 1ST QUARTER CHLOROFORM 2016
PO#:
Sampler Neme: TANNER HOLLIDAY
Date
Sample ID: Sampled
TRIP BLANK 3/9/2016
'TEMPBLANK 3/10/2016
I
i
I
I
I
0
1
z
Aofin<llll<lled by: L"-)t.ANJ(.. ftf1.1. / Dolo: lsl-tuno 311012016
/ Timo: 130C
PrtniNarno: TAfoo'NER HOLLIDAY
Rol~ohedby: Dolo:
IS19na1cn
n me·
Print Name:
Relinquished by: Date:
Signature
llme:
Print Name:
RElinquished by: Date:
Signature
Tlme:
Prinl Name:
I
Time
Sampled
Received -by:
SiCJnature
Prinl Name:
CHAIN OF CUSTODY
All analysis wll be conducted using NEL.AP accredited methods and all data will be reported using AW/>J..'s standard analyto lists and repoftlng
limits (POL) urless specifically requested otherwise on this Chain of Custody 8l'dlor attaJ:hed documonlalioo.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed reports will be emalled by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
D ELAP/A2LA
c 0 NLLAP
"~' c:i 0 Non-Compflance
~ 0 D Other: l1l 0') u ~ !:?. I.. 0 "' X 0 (0 " '" C'l :e ;; 0 0 C'l ::;; 0 ~ Known Hazards " z l1l 0 Q! ..... :::t ., tl a N 0 & 0 E 0 0 0 "' Sample Comments .. rJ) z >
3 w X
1 w
Date: Special Instructions:
Time:
,/
/C,G?J2. Ji
AWAL Lab Sample Set#
Page 2 of 2
1"00"""' I
Laboratory Use Only
~~ .
3 TGfT'4>0'l'!..., . ~'G •c
• RO<:el-led Btololnlleal<lng
(Improperly Seal~ • ·
y N) ' s·cn.,ry Presenred y . N
ked·at-.
y N -
6 Received WHhin
eTim~ . N
ieee T'!f'• was:
Y N NA 10'" on OlJ!Ot Pac1<3ge
2 ron OUter Package
Y N NA
3 P~nt on Sa~pl~
y N f!51 •
4' Unbroken on Sample El y N
~Between Siunple
y N' ~andCOC(3
Rocelvod~Jj Slonau.n 1;_ 'Jil.. ~ ./ Oate'J-//-/0 See the Analytical Scope of Work for Reporting Umits and VOC
analyte list.
Print Name: £/VI_ A£x.--l/ [Time: /o~ C
ReceNeu oy: I I Date:
Signature
ime:
Prlnl Name:
Received by: Dale:
Signature
Time:
Print Name: -
I
....
A WAL-Analytical Scope of Work
White Mesa Mill Blanding Utah
Page 11 of 13
Contaminant Analytical
Methods
to be Used
~llnorganics
Chloride ---------A4500-CI
B or
~
or E3 00.0
Sulfate ~ r ----E300.0
Carbon~03 A2320 B
...Bi6rbonate as HC03 A2320 B
Reporting
Limit
1 mg/L
~
rtffig/L
1 mg/L
1 mg/L
Volatile Organic Compounds -Chloroform Program
Carbon Tetrachloride SW8260B 1.0 11g/L
or
SW8260C
Chloroform SW8260B 1.0 jlg/L
or
SW8260C
Dichloromethane SW8260B 1.0 jlg/L
(Methylene Chloride) or
SW8260C
Chloromethane SW8260B 1.0 jlg/L
or
SW8260C
~OCs-Tailings Ttnpoundment Samples Only
1 ,2,~ch1orobenzene SW8270D <10 ug/L
1,2-Dich~enzene SW8270D <10 ug/L
1 ,3-Dichlorob~ne SW8270D <10 ug/L
1,4-Dichlorobenzen~ SW8270D <10 ug/L
1-Methy1naphthalene ~ SW8270D <10 ug/L
2,4,5-Trich1orophenol ~8270D <10 ug/L
2,4,6-Trichlorophenol sw&:N.Qp <10 ug/L
2,4-Dichlorophenol SW8270:[)'-. <10 ug/L
2, 4-Dimethy !phenol SW8270D <~g/L
2,4-Dinitropheno I SW8270D <20u~
2,4-Dinitrotoluene SW8270D <J.e'llg/L
2,6-Dinitrotoluene SW8270D/ ....-<10 ug/L
2-Chloronaphthalene SW8).?(}D <10 ug/L
2-Chlorophenol ~8270D <10 ug/L
2-Methy )naphthalene / SW8270D <10 ug/L
2-Methylphenol / SW8270D <10 ug/L
2-Nitrophenol / SW8270D <10 ug/L
3&4-Meth~enol SW8270D <10 ug/L
3,3 '-~lorobenzidine SW8270D <10 ug/L
~initro-2-methylphenol SW8270D <10 ug/L
/
Maximum Sample Sample
Holding Preservation Temperature
Times Requirements Requirements ----28 days None ~ --------~
~ None :S 6°C
-------14 days None ~
14 days None ~
14 days HCI topH<2 :S 6°C
14 days HCl to pH<2 :S 6°C
14 days HCI topH<2 :S 6°C
14 days HCI to pH<2 :S 6°C
/
7/40 days None <f}C
7/40 davs None _A6°C
7/40 days None / v <6°C
7/40 days Nony <6°C
7/40 days )>ffine :S 6°C
7/40 days V None <6°C
7/40da~ None <6°C
7 /40-tfays None <6°C
/7140 days None <6°C
7/40 days None <6°C
~40days None <6°C
7/4~s None <6°C
7/40da~ None <6°C
7/40 days ~None <6°C
7/40 days ~e <6°C
7/40 days Non~ <6°C
7140 days None '-.. :S 6°C
7/40 days None ~6°C
7/40 days None <6~
7/40 days None <6°C ~
Analysis
Ammonia
COD
Cyanide
Metals
N02&N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s le Set E
Preservative I }.__ .) tf s-b
pH<2H2S04
oH<ZH2S04
pH>l2
NaOH
oH<2HN03
pH<2H2S04 Yr~ tk~ /k.c;; k> j/cs t/'~(
pH<2HCL I I' / I/
pH<2H2S04
pH>9NaOH,
ZnAcetate
pH<2HzS04
pH<2 H2S04
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
f
Yes
doH
f5 I
~5 ~5
I/ ,
IG I/
,/e-r t£,.c:;
7
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
A
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH> __ due to the sample matrix interference .
Lab SetiD: /(c 0,2 Z~y
IZ--/~
lk_~ ver-
17 7
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail : [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Garrin Palmer
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2016
Dear Garrin Palmer: Lab Set ID: 1603400
American West Analytical Laboratories received sample(s) on 3/18/2016 for the analyses
presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
Thank You, Digitally signed by Jose G.
Jose G ~~~~=JoseG.Rocha,
• o=American West Analytical
Laboratories, au, R 0 c h 8 ~~~~=[e-mail].
Date: 2016.04.11 14:20:14 Approved by: .___ _______ -os_·o_o· ____ ___.
Laboratory Director or designee
Report Date: 4111/2016 Page I of 62
All analyses applicable to the CWA. SDWA. and RCRA are perfomted in accordance to NELAC prolocols. Pertinent sampling information is locnted on the auached COC Conliden\ial Business (n(orm::~tion: This reporl is prol'ided for the exclush e use of the
~ddressce Pri' ile~es of sub,seq~nt ~~e or the ~~1e of this .coJ~pony or uny 1~mber of its st:~ff, or reproductio~ ~r this repo~ in ~on~ection .. wilh the ~~ertisei"?enL, P~?motio.n or sale of~!) ~ro<h~cl or p~ocess, ~r in ~nm;c~ion w~th 1h~ r~-publication of this rtporL
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Set ID: 1603400
Date Received: 3/18/2016 1040h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1603400-001A TW4-03R 03142016 3/14/2016 1329h Aqueous Anions, E300.0
;;att Lake City, UT 84119 1603400-00 1 8 TW4-03R 03142016 3/14/2016 1329h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-001 c TW4-03R 03142016 3/14/2016 1329h Aqueous VOA by GC/MS Method
8260C/5030C
Phone:[phone] 1603400-002A TW4-03 03152016 3/15/2016 639h Aqueous Anions, E300.0
1603400-002B TW4-03 03152016 3/15/2016 639h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1603400-002C TW4-03 03152016 3/15/2016 639h Aqueous VOA by GC/MS Method
Fax: [phone]C/5030C
~-mail: [e-mail] 1603400-003A TW4-12 03152016 3/15/2016 652h Aqueous Anions, E300.0
1603400-003B TW4-12 03152016 3/15/2016 652h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1603400-003C TW4-12 03152016 3/15/2016 652h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-004A TW4-28 03152016 3/15/2016 656h Aqueous Anions, E300.0
Kyle F. Gross 1603400-004B TW4-28_03152016 3/15/2016 656h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-004C TW4-28_03152016 3/15/2016 656h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1603400-005A TW4-32_03152016 3/15/2016 705h Aqueous Anions, E300.0
Jose Rocha 1603400-005B TW4-32 03152016 3/15/2016 705h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1603400-005C TW4-32_03152016 3/15/2016 705h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-006A TW4-13 03162016 3/16/2016 642h Aqueous Anions, E300.0
1603400-0068 TW4-13 03162016 3/16/2016 642h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-006C TW4-13_03162016 3/16/2016 642h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-007 A TW4-36 03162016 3/16/2016 649h Aqueous Anions, E300.0
1603400-007B TW4-36 03162016 3/16/2016 649h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-007C TW4-36 03162016 3/16/2016 649h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-008A TW4-31 03162016 3/16/2016 657h Aqueous Anions, E300.0
1603400-0088 TW4-31 03162016 3/16/2016 657h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-008C TW4-31 03162016 3/16/2016 657h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-009A TW4-34 03162016 3/16/2016 705h Aqueous Anions, E300.0
1603400-009B TW4-34 03162016 3/16/2016 705h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-009C TW4-34 03162016 3/16/2016 705h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 1 OA TW4-35 03162016 3/16/2016 713h Aqueous Anions, E300.0
1603400-0IOB TW4-35_03162016 3/16/2016 713h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 4/1112016 Page 2 of62
All anal) ses applico.ble to the CWA SDWA, and RCRA are performed in accordance to NELAC protocols_ Pertinent sampling information is located on the auached COC Confidenllnl Business Information: This report is provided for the e.'\Ciusi,·e use of the
~cldressee P1i\ ile~es o_f sub~seq~ent ~~e or the ~~1e of this .cm~prn1y or anr ~mber of its stnff, or reproductio~ ~~this repo~ in ~n~ection~ \\ilh then~' ertisement, P~?motio.n ~r sale of ?J!) ~rodt~cl or p~~cess, ~r in ~nm;c~ion w~lh th~ n;-publiccuion of this report
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: lst Quarter Chloroform 2016
Lab Set ID: 1603400
Date Received: 3118/2016 1 040h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
1603400-01 oc TW4-35 03162016 3/16/2016 713h Aqueous VOA by GC/MS Method
3440 South 700 West 8260C/5030C
1603400-011A TW4-23_03162016 3/16/2016 721h Aqueous Anions, E300.0
;a It Lake City, UT 841 19 1603400-0 11 B TW4-23 03162016 3/16/2016 721h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-011 c TW4-23 03162016 3/16/2016 72lh Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 12A TW4-14 03162016 3/16/2016 729h Aqueous Anions, E300.0 Phone: [phone] 1603400-0 12B TW4-14 03162016 3/16/2016 729h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1603400-0 12C TW4-14 03162016 3/16/2016 729h Aqueous VOA by GC/MS Method
Fax: [phone]C/5030C
~-mail: [e-mail] 1603400-0 13A TW4-27 03162016 3/16/2016 736h Aqueous Anions, E300.0
1603400-0BB TW4-27_03162016 3/16/2016 736h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1603400-013C TW4-27 03162016 3/16/2016 736h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 14A TW4-26 03162016 3/16/2016 748h Aqueous Anions, E300.0
1603400-0148 TW4-26 03162016 3/16/2016 748h Aqueous Nitrite/Nitrate (as N), E353.2 Kyle F. Gross 1603400-014C TW4-26 03162016 3/16/2016 748h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1603400-015A TW4-30 03172016 3/17/2016 750h Aqueous Anions, E300.0
Jose Rocha 1603400-0 15B TW4-30 03172016 3/17/2016 750h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1603400-0 15C TW4-30 03172016 3/17/2016 750h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 16A TW4-05_03172016 3/17/2016 804h Aqueous Anions, E300.0
1603400-0 16B TW4-05 03172016 3/17/2016 804h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-0 16C TW4-05 03172016 3/17/2016 804h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-017 A TW4-18 03172016 3117/2016 8l3h Aqueous Anions, E300.0
1603400-0 17B TW4-18 03172016 3/17/2016 813h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-017C TW4-18 03172016 3/17/2016 813h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 18A TW4-09 03172016 3/17/2016 822h Aqueous Anions, E300.0
1603400-0 18B TW4-09_03172016 3/17/2016 822h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-0 18C TW4-09 03172016 3/17/2016 822h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-0 19 A TW4-16 03172016 3/17/2016 829h Aqueous Anions, E300.0
1603400-0 19B TW4-16 03172016 3/17/2016 829h Aqueous Nitrite/Nitrate (as N), E353.2
1603400-0 19C TW4-16 03172016 3/17/2016 829h Aqueous VOA by GC/MS Method
8260C/5030C
1603400-020A TW4-33 03172016 3/17/2016 838h Aqueous Anions, E300.0
1603400-020B TW4-33 03172016 3/17/2016 838h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 4/11/2016 Page 3 of62
Aliano lyses applicable to the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on IJ1e attached COC ConOdential Business lnfonnalion: This report is provided for the exclusi,·e use of the
~ddressee Pri\'ile~es o_f sub .. seq~enl ~~e of the ~:u:ne of this .co~pany or M) 1~mber of its staff, or reproductio~~ ~f this rep01; in .con~ection ... with the D~~ ertisemenl, P~?motio.n or saJe of :u;~ ~rOdl~cl or p1.ocess, ~r in :onn~c~ion w!lh th~ r~-publicatiotl of this reporl
3440 South 700 West
;;art 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
Client:
Project:
Lab Set ID:
Date Received:
Lab Sample ID
1603400-020C
1603400-021 A
1603400-021B
1603400-021 c
1603400-022A
1603400-022B
1603400-022C
1603400-023A
1603400-024A
1603400-024B
1603400-024C
Energy Fuels Resources, Inc.
lst Quarter Chloroform 2016
1603400
3/18/2016 1 040h
Client Sample ID
TW4-33 03172016
TW4-29 03172016
TW4-29 03172016
TW4-29_03172016
TW4-08_03172016
TW4-08 03172016
TW4-08 03172016
Trip Blank
TW4-65 03152016
TW4-65 03152016
TW4-65 03152016
Contact: Garrin Palmer
Date Collected Matrix Analysis
3/17/2016 838h Aqueous VOA by GC/MS Method
8260C/5030C
3/17/2016 845h Aqueous Anions, E300.0
3/17/2016 845h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2016 845h Aqueous VOA by GC/MS Method
8260C/5030C
3/17/2016 854h Aqueous Anions, E300.0
3/17/2016 854h Aqueous Nitrite/Nitrate (as N), E353.2
3/17/2016 854h Aqueous VOA by GC/MS Method
8260C/5030C
3/14/2016 Aqueous VOA by GC/MS Method
8260C/5030C
3/15/2016 656h Aqueous Anions, E300.0
3/15/2016 656h Aqueous Nitrite/Nitrate (as N), E353.2
3/15/2016 656h Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 4/ll/2016 Page 4 of62
All una\) ses applicable to Lhe CWA SOW A. and RCRA are performed in accordance to NELAC protocols_ Pertinent sampling information is located on the nllached COC Confidential Business Jnfonnation: This report is prm•ided for the exclusi,·e use oft he
~ddressee Pri' ile~es o.f sub,.seq~ent ~~e of the ~~1e of this .cm~pany or nny 1~mber of its stnff, or reproduclio~ ~f this repo~ in ~OJ~eclion,.. \Vith the~~ ertisemenl, P~?motio.n or sale of ?J!~ ~· od~ct or P~?cess, ~r in ~onn~c~ion w!th th~ n;-publicalion of lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
1st Quarter Chloroform 2016
1603400
3/18/2016
3/14-3/17/2016
See Chain of Custody
None
Holding Time and Preservation Requirements: The analysis and preparation for the
samples were performed within the method holding times. The 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, DUP:
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 I Matrix Spike Duplicates (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, with the
following exceptions:
Sample ID Analyte QC Explanation
1603400-007B Nitrate/Nitrite MS/MSD Sample matrix interference
1603400-021 B Nitrate/Nitrite MS/MSD Sample matrix interference
16034 79-001 B Nitrate/Nitrite MS/MSD Sam_l)_le matrix interference
Duplicate (DUP): The parameters that required a duplicate analysis had RPDs
within the control limits.
Corrective Action: None required.
Report Date: 4/11/2016 Page 5 of62
All analyses applicable to the CWA. SDWA. and RCRA are perfom•ed in accordance 10 NELAC pruuxoJs. Pettulent sampling information is Jocoted on the attached COC. Conlidentlol Business lnfonootion: This repon is pro\'ided ror the exclush·e use of the
~ddressee. Pri\ ile~es or sub .. seq~enl ~~e of the ~~e of this .con.lpnny or any 1~mber of its staff, or rcproduct1~ ~f lhis repo~ in ~on~echon ... wilh lhe n<!vertisemenl. p~~motio.n ~r sale of ~!Y ~rod~cl or p~ocess, ~r in ~onn~c~ion w~th lh~ ~publication of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab SetiD:
Sample Receipt Information:
Date ofReceipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
1st Quarter Chloroform 2016
1603400
3/18/2016
3/14-3/17/2016
See Chain of Custody
None
SW-846 8260C/5030C
Volatile Organic Compounds
General Set Comments: Multiple target analytes were observed above reporting limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike I 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: 4/11/2016 Page 6 of62
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols_ Pertinent sllmpling information is located on the alt3ched COC Confidential Business Jnfonmuion: This repon is prol'ided for the exclusi\e use of1he
~ddressee Pri\ ile~es or su~seq~ent ~e of the ~:u,ne of this .con.tpnny or M)" ·~mber of ils starr, or reproducli~ ~fthis repory in .c~ection .. with the D~\'er1isemenl, P~?motio.n ~r ~a1e of~;~-~rod~ct or p~ocess, ~r in ?>nn:c!ion w!lh th~ r:·p~blication of lhis report
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1603400
Project: 1st Quarter Chloroform 2016
Analyte
Lab Sample ID: 1603400-007BDUP
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N)
Lab Sample ID: 1603400-0IOBDUP
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N)
Result Units Method
Date Analyzed: 04/07/2016 1528h
< 0.100 mg/L E353.2
Date Analyzed: 04/07/2016 1530h
0.507 mg/L E353.2
MDL
0.0833
0.0833
Reporting
Limit
0.100
0.100
Dept: we
QC Type: DUP
Amount
Spiked
Spike Ref.
Amount %REC Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
0 0 20
0.521 2.84 20
Report Date: 4/11/2016 Page 54 of 62
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infom1ation is located on the attached COC. Confidential Business Information: Th1s report is provided for the exclusive use of the addressee Privileges of subsequent use of tt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee \\-·ill be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603400
Project: 1st Quarter Chloroform 2016
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
Method MDL
Reporting
Limit
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS-R88552 Date Analyzed: 03/23/2016 1252h
Test Code: 300.0-W
Chloride 4.93 mg!L E300.0 0.00516 0.100 5.000 0 98.7
Lab Sample ID: LCS-R88572 Date Analyzed: 03/24/2016 2051h
Test Code: 300.0-W
Chloride 4.91 mg!L E300.0 0.00516 0.100 5.000 0 98.2
Lab Sample ID: LCS-R88553 Date Analyzed: 03/24/2016 1605h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.06 mg!L E353.2 0.00833 0.100 1.000 0 106
Lab Sample ID: LCS-R88554 Date Analyzed: 03/24/2016 1659h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.09 mg!L E353.2 0.00833 0.0100 1.000 0 109
Lab Sample ID: LCS-R88933 Date Analyzed: 04/07/2016 1526h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.971 mg!L E353.2 0.00833 0.0100 1.000 0 97.1
Limits
90-110
90-110
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 4/11/2016 Page 55 of62
analyses applicable to the CWA. SDWA, and RCRA are perfonned in accordance to NElAC protocols Pertinent samphng informat•on is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff. or reproduction of this report in connection with the advertisement,. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603400
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R88552 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R88572 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R88553 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) <0.100
Lab Sample ID: MB-R88554 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-R88933 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa'<: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/23/2016 1235h
mg/L E300.0 0.00516 0.100 -03/24/2016 2034h
mg/L E300.0 0.00516 0.100
03/24/2016 1604h
mg/L E353.2 0.00833 0.100
03/24/2016 165 8h
mg/L E353.2 0.00833 0.0100
04/07/2016 1525h
mg/L E353.2 0.00833 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit Qual
Report Date: 4/11/2016 Page 56 of62
analyses applicable to the CW A. SDW A, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidentia1 Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tf
ne of this company or any member of its staff. or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this repon for any purpose other than for the addressee will be granted only on contact, This
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: Garrin Palmer
Lab Set ID: 1603400 Dept: we
Project: 1st Quarter Chloroform 2016 QCType: MS
-
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1603400-002AMS Date Analyzed: 03/23/2016 1326h
Test Code: 300.0-W
Chloride 125 mg/L E300.0 0.103 2.00 100.0 32.8 92.1 90-110
Lab Sample ID: 1603400-020AMS Date Analyzed: 03/23/2016 215lh
Test Code: 300.0-W
Chloride 142 mg/L E300.0 0.103 2.00 100.0 46.2 95.3 90-I 10
Lab Sample ID: 1603400-00SAMS Date Analyzed: 03/24/2016 2144h
Test Code: 300.0-W
Chloride 128 mg/L E300.0 0.103 2.00 100.0 31.5 96.9 90-110
Lab Sample ID: 1603400-014AMS Date Analyzed: 03/25/2016 032h
Test Code: 300.0-W
Chloride Ill mg/L E300.0 0.103 2.00 100.0 13.7 97.5 90-110
Lab Sample ID: 1603400-00IBMS Date Analyzed: 03/24/2016 1607h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 10.9 mg/L E353.2 0.0833 0.100 10.00 0.0198 109 90-110
Lab Sample ID: 1603400-007BMS Date Analyzed: 03/24/2016 1627h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.2 mg/L E353,2 0.0833 0.100 10.00 0.0109 112 90-110
Lab Sample ID: 1603400-02IBMS Date Analyzed: 03/24/2016 170lh
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 25.9 mg/L E353.2 0.167 0.200 20.00 2.92 115 90-110
Lab Sample ID: 1603479-001BMS Date Analyzed: 03/24/2016 1720h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.5 mg/L E353.2 0.0833 0.100 10.00 0 115 90-110
1-Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 4/1112016 Page 57 of62
analyses applicable to the CWA. SDWA, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee. Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
American West QC SUMMARY REPORT ANALYTICAL LABORATORIES
C lient: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1603400 Dept: we
Project: 1st Quarter Chlorofonn 2016 QC Type: MSD
-
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1603400-002AMSD Date Analyzed: 03/23/2016 1343h
Test Code: 300.0-W
Chloride 125 mg!L E300.0 0.103 2.00 100.0 32.8 91.8 90-110 125 0.294 20
Lab Sample ID: 1603400-020AMSD Date Analyzed: 03/23/20 16 2208h
Test Code: 300.0-W
Chloride 141 mg!L E300.0 0.103 2.00 100.0 46.2 95.2 90-110 142 0.0937 20
Lab Sample ID: 1603400-00SAMSD Date Analyzed: 03/24/2016 2200h
Test Code: 300.0-W
Chloride 128 mg!L E300,0 0.103 2.00 100.0 31.5 96.6 90-110 128 0.226 20
Lab Sample ID: 1603400-014AMSD Date Analyzed: 03/25/2016 049h
Test Code: 300.0-W
Chloride 112 mg!L E300.0 0.103 2.00 100.0 13.7 98.4 90-110 Ill 0.810 20
Lab Sample ID: 1603400-001BMSD Date Analyzed: 03/24/2016 1608h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 10.8 mg!L E353.2 0.0833 0.100 10.00 0.0198 108 90-110 10.9 0.460 10
Lab Sample ID: 1603400-007BMSD Date Analyzed: 03/24/2016 1628h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.1 mg!L E353.2 0.0833 0.100 10.00 0.0109 Ill 90-110 11.2 0.717 10
Lab Sample ID: 1603400-021BMSD Date Analyzed: 03/24/2016 1702h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 25.2 mg!L E353.2 0.167 0.200 20.00 2.92 111 90-110 25.9 2.86 10
Lab Sample ID: 1603479-001BMSD Date Analyzed: 03/24/2016 172lh
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.5 mg!L E353.2 0.0833 0.100 10.00 0 115 90-110 11.5 0.261 10
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Report Date: 4/11/2016 Page 58 of 62
analyses applicable to the CWA. SDWA, and RCRA arc porfonned in accordance to NELAC protoo:ols Penlnent sampling information is located on the attached COC. Confidential Bu$iness Information: This report is provtdcd for the exclusive use of the addressee. Privileges of subsequent use oftt
ne of this company or any member of its statT, or reproduction of this report in connection with the advcntscment, 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: 1603400
Project: 1st Quarter Chloroform 2016
Analyte
Lab Sample ID: LCS VOC-2 031816A
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-1 031816A
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Result
Date Analyzed:
21.7
20.4
48.2
48.3
48.6
48.4
Date Analyzed:
20.7
20.0
51.5
51.3
50.8
50.2
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: Garrin Palmer
Units Method
03118/2016 1504h
j.!g/L SW8260C
j.!g/L SW8260C
!J.g/L SW8260C
!J.g/L SW8260C
j.!g/L SW8260C
j.!g/L SW8260C
03/18/2016 1033h
!J.g/L SW8260C
j.!g/L SW8260C
j.!g/L SW8260C
j.!g/L SW8260C
j.!g/L SW8260C
j.!g/L SW8260C
MDL
0.153
0.172
0.153
0.172
Reporting
Limit
1.00
1.00
1.00
1.00
Dept: MSVOA
QC Type: LCS
Amount
Spiked
20.00
20.00
50.00
50.00
50.00
50.00
20.00
20.00
50.00
50.00
50.00
50.00
Spike Ref.
Amount
0
0
0
0
%REC
109
102
96.4
96.6
97.2
96.9
103
99.8
103
103
102
100
Limits
85 -124
81 -135
80-122
85-121
80-116
81 -123
85 -124
81 -135
80-122
85-121
80-116
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 4/11/2016 Page 59 of 62
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftr
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re·publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603400
Project: 1st Quarter Chlorofonn 2016
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: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QC Type: MBLK
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: MB VOC-2 031816A Date Analyzed: 03/18/2016 1118h
Test Code: 8260-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-1 031816A
Test Code: 8260-W-DEN100
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
49.5
51.5
494
50.2
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
54.3
53.5
51.8
50.6
llg!L SW8260C 0.504 1.00
llg!L SW8260C 0.153 1.00
llg!L SW8260C 0.163 1.00
llg!L SW8260C 0.172 1.00
llg!L SW8260C 50.00 99.1
llg!L SW8260C 50.00 103
llg!L SW8260C 50.00 98.8
llg!L SW8260C 50.00 100
03/18/2016 1112h
J.lg/L SW8260C 0.504 1.00
J.lg/L SW8260C 0.153 1.00
J.lg/L SW8260C 0.163 1.00
J.lg/L SW8260C 0.172 1.00
llg/L SW8260C 50.00 109
llg!L SW8260C 50.00 107
llg!L SW8260C 50.00 104
J.lg/L SW8260C 50.00 101
Limits
80-122
85-121
80-116
81-123
80-122
85-121
80-116
81-123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 4/11/2016 Page 60 of62
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
I ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603400
Project: I st Quarter Chloroform 2016
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], ToJI Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: MS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1603400-021CMS Date Analyzed: 03/18/2016 1633h
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 1603400-00ICMS
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
536
249
475
491
493
500
Date Analyzed:
21.3
21.1
49.0
48.6
48.8
48.7
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C -03/18/2016 1603h
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C
~giL SW8260C
1.53 10.0 200.0 335 101
1.72 10.0 200.0 0 125
500.0 95.0
500.0 98.2
500.0 98.7
500.0 100
0.153 1.00 20.00 0 107
0.172 1.00 20.00 0 106
50.00 98.1
50.00 97.3
50.00 97.7
50.00 97.4
Limits
50-146
30-192
72-151
80-152
80-124
77-129
50-146
30-192
72-151
80-152
80-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 4/11/2016 Page 61 of62
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC' protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
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: Garrin Palmer
Lab Set ID: 1603400 Dept: MSVOA
Project: 1st Quarter Chloroform 2016 QC Type: MSD
Reporting Amount Spike Ref. RPD Ref. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1603400-021CMSD Date Analyzed: 03/18/2016 1653h
Test Code: 8260-W-DEN100
Chloroform 522 ~giL SW8260C 1.53 10.0 200.0 335 93.5 50-146 536 2.65 25
Methylene chloride 241 ~giL SW8260C 1.72 10.0 200.0 0 121 30-192 249 3.22 25
Surr: 1,2-Dichloroethane-d4 472 ~giL SW8260C 500.0 94.4 72-!51
Surr: 4-Bromofluorobenzene 490 ~giL SW8260C 500.0 98.0 80-I 52
Surr: Dibromofluoromethane 491 ~giL SW8260C 500.0 98.2 80-124
Surr: Toluene-d8 502 ~giL SW8260C 500.0 100 77-129
Lab Sample ID: 1603400-00lCMSD Date Analyzed: 03118/2016 1623h
Test Code: 8260-W-DEN100
Chloroform 20.8 ~giL SW8260C 0.153 1.00 20.00 0 104 50-146 21.3 2.37 25
Methylene chloride 19.3 ~giL SW8260C 0.172 1.00 20.00 0 96.5 30-192 21.1 9.06 25
Surr: I ,2-Dichloroethane-d4 48.8 ~giL SW8260C 50.00 97.6 72-151
Surr: 4-Bromofluorobenzene 50.6 ~giL SW8260C 50.00 101 80-!52
Surr: Dibromofluoromethane 48.4 ~giL SW8260C 50.00 96.8 80-124
Surr: Toluene-d8 48.9 ~giL SW8260C 50.00 97.8 77-129
Report Date: 4/11/2016 Page 62 of 62
analyses applicable to the CWA_ SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft~
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process. or in connection with the re-publication of this repon for any purpose other than for the addressee will be granted only on contact This
American West Analytical Laboratories UL
Denison
WORK ORDER Summary 'Work Order: 1603400 Page 1 of4
Client: Energy Fuels Resources, Inc. Due Date: 3/29/2016
Client ID: DENlOO Contact: Garrin Pabner
Project: 1st Quarter Chloroform 2016 QC Level: III WO Type: Project
Comments: PA Rush. QC 3 (Summary/No chromatograms). RL of 1 ppm for Chloride and VOC and 0.1 ppm forN02/N03-Run N02/N03 at a lOX dilution. Expected
levels provided by client-see Jenn. J-flag what we can't meet. ElM Locus and EDD-Denison. Email Group.; D
,.LL[l
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage --
1603400-00 1A TW4-03R_03142016 3/14/2016 1329h 3/18/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL --1603400-00lB N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-001 c 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENIOO; #of AJwlytes: 41 # ofSurr: 4
1603400-002A TW4-03_03152016 3/15/2016 0639h 3/18/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL --
1603400-0028 N021N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N ---
1603400-002C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Analytes: 4 / # ofSurr: 4
1603400-003A TW4-12_03152016 3/15/2016 0652h 3/18/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL ---1603400-0038 N02/N03-W-353.2 df-no21no3
I SELAnalytes: N03N02N ---
1603400-003C 8260-W-DENlOO VOCFridge
Test Group: 8260-W-DENI 00; # qf Analytes: 41 # of Surr: 4 -1603400-004A TW4-28_03152016 3/15/2016 0656h 3/18/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL ---
1603400-0048 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N --1603400-004C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 41 # ofSurr: 4 -1603400-00SA TW4-32_03152016 3/15/2016 070Sh 3/18/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL ---1603400-0058 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N ---
1603400-005C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENIOO; #of Analytes: 41 # ofSurr; 4
'.Printed: 3/1812016 ...... ' FORLABORATORYUSEONLY[fillouton-page1]: %M_ 0 RTO Cf\10 TAT.O_, __ QCO -·'-'" HOK ____ ,_-_HOK __ _ HOK_-_____ COC Em_a.iled,__ ___ _
WORK ORDER Summary Work Order: 1603400 Page2of4
Client: Energy Fuels Resources, Inc. Due Date: 3/29/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603400-006A TlV4-13_03162016 3/16/2016 0642h 3/1812016 1040h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1603400-006B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-006C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DENIOO; #of Analytes: 41# ofSurr: 4
1603400-007 A TlV4-36_03162016 3116/2016 0649h 3/18/2016 1040h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1603400-007B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-007C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DENJOO; #ofAnalytes: 4l#ofSurr: 4
1603400-008A TlV4-31_03162016 3/16/2016 0657h 3/18/2016 1040h 300.0-W Aqueous elf-we
I SELAnalytes: CL
1603400-00BB N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-00BC 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4 I# of Surr: 4
1603400-009A TlV4-34_03162016 3/16/2016 070Sh 3/18/2016 1040h 300.0-W Aqueous elf-we
1 SELAnalytes: CL
1603400-009B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-009C 8260-W-DENIOO VOCFridgc 2
Test Group: 8260-W-DEN100; #of Analytes: 4 I # ofSurr: 4
1603400-010A TlV4-35_03162016 3/16/2016 0713h 3/18/2016 1040h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
1603400-010B N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-010C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Analytes: 4 I # of Surr: 4
1603400-0llA TlV4-23_03162016 3/16/2016 0721h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-0llB N02/N03-W-353.2 elf-no2/no3
1 SEL Analytes: N03N02N
1603400-0 llC 8260-W-DENIOO VOCFridge 2
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
1603400-012A TlV4-14_03162016 3/16/2016 0729h 3/18/2016 1040h 300.0-W Aqueous elf-we
1 SEL Analytes: CL
,Printed: 3/1&/2016 FOR LABORATORY USE: ONLY [fill out on page 1]: 'Z'11.M 0 RID CNO TAT.O aco ·,c !:iOK~ HOK __ , HO.K_. __ COC ~f!lailed . --'~
WORK ORDER Summary WorkOrder: 1603400 Page Jof4
Client: Energy Fuels Resources, Inc. Due Date: 3/29/2016
Sample I» Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603400-012B TlV4-14_03162016 3/16/2016 0729h 3/18/2016 1040h N02/N03-W-353.2 Aqueous df-no2/no3
1 SEL Analytes: N03N02N
1603400-0 12C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Surr: 4
1603400-0 13A TlV4-27_03162016 3/16/2016 0736h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-0 13B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-0 13C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # ofSurr: 4
1603400-014A TlV4-26_03162016 3/16/2016 0748h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-014B N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
1603400-0 14C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# ofSurr: 4
1603400-015A TlV4-30_03172016 3/17/2016 0750h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-015B N02/N03-W-353.2 df-no21no3
1 SEL Analytes: N03N02N
1603400-015C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
1603400-016A TW4-05_03172016 3/17/2016 0804h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-016B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-016C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; # of A11alytes: 4 I# of Surr: 4
1603400-017A TlV4-18_03172016 3/17/2016 0813h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-0 17B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-017C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Analytes: 4 I# of Surr: 4
1603400-018A TlV4-09_03172016 3/17/2016 0822h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-018B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
!gin ted: 3/18/2016 FOR LABQRA TORY USE, ONLY [fill out on page -1]: %M 0 RT 0 CN 0 TAT~O QCO .... HOK __ HOK __ ._ .. HOK_, __ CQCEmailed
WORK ORDER Summary WorkOrder: 1603400 Page4 of4
Client: Energy Fuels Resources, Inc. Due Date: 3/29/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603400-0 18C 1W4-09_03172016 3/1712016 0822h 3/18/2016 1040h 8260-W-DENlOO Aqueous VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 4 I# ofSurr: 4
1603400-019A 1W4-16_03172016 3/17/2016 0829h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-019B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-019C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Analytes: 4 I # of Surr: 4
1603400-020A 1W4-33_03172016 3/17/2016 0838h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-020B NOUNOJ..W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-020C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; # of. Analytes: 4 I # of Surr: 4
1603400-021A 1W4-29_03172016 3/17/2016 0845h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-021B NOUNOJ..W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-021C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 4 I # ofSurr: 4
1603400-022A 1W4-08_03172016 3/17/2016 0854h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-022B NOUNOJ..W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-022C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 4 I# ofSurr: 4
1603400-023A Trip Blank 3/1412016 3/18/2016 1040h 8260-W-DENlOO Aqueous VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 4 I# of Surr: 4
1603400-024A 1W4-65_03152016 3/15/2016 0656h 3/18/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1603400-024B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1603400-024C 8260-W -DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# ofSurr: 4
l'tint~: 3/1812016 FORLABORATORYUSEONLY[filloutonpage1]:c %M 0 RTO _ CN0 TATD. QCO 1:-!0K ___ ., H()K_. __ HOK__ _coc Email~~---
American West
Analytical Laboratories
463W.3600S. Saltl.akeCJty,UT 84115
Phone# [phone] Ton Free# [phone]
L~ Fax # [phone] Email awal@ awa~Jabs.com
www.awal-labs.com
Client Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] Cell#:
[e-mail]; KWelnel®energyfuels.com;
Email: dturk@enerlll!!!els.com
Project Name: TANNER HOLLIDAY
1ST QUARTER 2016 Project#:
chl!lro'V'orm PO#:
Sampler Name: TANNER HOLLIDAY
Date
Sample 10: Sampled
TW4-03R_03142016 3/14/2016
TW4-03_03152016 3/15/2016
'fW4-12_03152016 3/15/2016
TW4-28_03152016 3/15/2016
TW4-32_03152016 3/15/2016
: TW4-13_03162016 3/16/2016
T1V4-36_03162016 3/16/2016
I TW4-31_03162016 3/16/2016
I TW4-34_03162016 3/16/2016
~ T\\>"4-35_03162016 3/16/2016
r TW4-23_03162016 3/16/2016
l TW4-14_03162016 3/16/2016
~ TW4-27_03162016 3/16/2016
~=-.:."""'~ -) llMQJ(. .J.-4_} 'f./. A
Ooto: ~/111-z.O!b
Prlnl Namo: -! IVl ner ·~oil; la . .A tf nmo: rz.~o.
Rellnqui>tlod by. ._) 01110:
Slp!Ut9 [nmo:
Print /lafllD:
ROilnqulohod by: DDio:
;IQM~Un>
!Timo:
f'rint Nome:
Relinquished oy: Date:
>lgnature
Time:
PrinlNam~ -
I
Time
Sampled
1329
639
652
656
705
642
649
657
705
713
721
729
736
Received by:
SiQnature
Pdnt Na_me;
CHAIN OF CUSTODY
All analysis will be conducted using NELAP accredited methods and all data will be reported using AWAL's standard anatyte lists and reporting
limits (POL) unless specifically requested otherwise on lhls Chajn of Custody andfor attached documentation.
QC Level: I Turn Around Time: Unless other arrangements have been made,
signed reports will be email-3d by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAP/A2LA
c 0 NLLAP
~ 0 0 Non-Compliance
o-i 0 0 Other. It) e<:l u ~ X !2. ... 0 CD 0 to c: ·c: Cl'l ~ 1;i 0 0 C'l :::;; 0 rQ Known Hazards c: z It) 0 " ...... ~ ., (.) a. C'l 0 & 0 E 0 0 ~ "' Sample Comments .. Ul z
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X .....
5 w X X X "t vr'a{ ~(.... f}n:,/e...._
5 w X X X
5 w X X X f, v /.._I re..L I? n-.L -5 w X X X
5 w X X X
Date: Special Instructions:
Time:
/
I G o3 Cfoo
AWAL Lab Sample Set#
Page 1 of 2
I"'"M"' I --
· Laboratmy.Use Only
SlunplasWi!ta: 1).~5
~a hand delivered
2 orile
3 Temperature ll-c
4 Roa!ivod Bmi!Onl\.oaklng
~~~ N
s ~Y r~_orvoo
. y . N
ClK!d<od ol ~
y N
6 .Rec!!lived Within
(!)ngTimes
N
COC Tape Was:
l (!]"on Oulor Poa!olgo
Y N NA
2. von OW!< P<t<~oage
V N NA
3 Present on Somp!o 0) y N .
~ .Uri>r1lkcn.on Sample ~
Y N Nil
~es Between Sample 1-abols and CO.C Record?
v ~
ReceiYoo0Q; 1. SlgnaJum ; · 'v1. ~ 7 Date: J , Jk-/ {n See the Analytical Scope of Work for Reporting Limits and VOC
Print Name: z..tvv. ... ..i/,;. 9:,~ _j lftme: / (\ r (\ analyte list •
Received by: ( 7 Date:
Slooature
lme:
Print Name:
Received by: i Dale:
Signature
Time:
Print Name: -
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# [phone] Tol Free# [phone]
~ Fax # [phone] Email awal@ awal-labs.com
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] Cell II:
gpalmer@r.:ne:rgyfuels.com; [e-mail];
Email: [e-mail]
Project Name: TANNER HOLLIDAY
Project#: 1ST QUARTER CHLOROFORM 2016
POll:
Sampler Name: TANNER HOLLIDAY
Date
SampleiD: Sampled
1 TW4-26_03162016 3/16/2016
TW4-30_03172016 3/17/2016
! TW4-05_03172016 3/17/2016
TW4-18_03172016 3/17/2016
; TW4-09_03172016 3/17/2016
r TW4-16_o3172016 3/17/2016
1 TW4-33_03172016 3/17/2016
TW4-29_03172016 3/17/2016
TW4·08_03172016 3/17/2016
• TRIP BLANK 3/14/2016
TEMP BLANK 3/17/2016
TW4-65_03152016 3/1!'1/2016
!
Relinquished by:.::'\,.u\ 171.£ 0.3 fll/zO lk. Slonaturo ....., li\l..X. 'A
Print Nama; ~Me./' all;~-{ nme\"Z.:3a
Relinquished by: .._) Dote:
Sl nature
Time:
Prin1 Name;
Relinquished by: Date:
SignatLrB
nme:
PrlntNamo:
Aellnqojshod by: Oat a:
Signature
Tlme:
Print Name:
I
Time
Sampled
748
750
804
813
822
829
838
845
854
656
Received by:
Sl~nature
Print Name:
Received by:
Signature
Print Name;
Received by:
Sig_n_ature
Print Name:
Received by:
Signature
Print Name:
CHAIN OF CUSTODY
Al analysis .,.II be condooted using NB.AP accredhed methods and all data will be reported using AWAL 's standerd analytellsts and mportlng
llm"s (POL) unless specifiCBily requested otherwise on this Chain of Custody aOO'or alla<:hed docunentallon.
ac Level: I Tum Around Time: Unless other arrangements have been made,
signed reports .,;n be emelled by 5:00 pm on
3 Standard the day they are due.
fx Include EDD:
LOCUS UPLOAD
EXCEL
Field Fl"ered For:
For Compliance With:
D NELAP
0 RCRA
D CWA
0 SDWA
0 ELAP/A2LA
0 NLLAP
c::t c 0 Non-Compliance 0 tri 0 0 Other: ttl 0') G' !!! )( <2 ... 16 " 0 c: "' (') ]! 1ii 0 0 C'l ::; 0 ~ Known Hazards c: z ttl 0 " ..... ~ Ill 0 Q. eo~ 0 & 0 E 0 a 0 "' Sample Comments .. (/) z >
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 ~ X X X
5 w X X X
5 w X X X
5 w X X X
3 w X
l w
5 w X X X
pate: Special Instructions:
Time:
;G 03 'f()(\
AWAL Lab Sample Set#
Page 2 of 2 I""· ... ., I
Labor<~tory Use Only
isn"'PI.,. Were: (). PJ , e llanddGllv~
2 Ambi ... e
3 l'ornperoturo ~c
~ ~odlll~or/l.!lalclng
~m~ScWed) 6 N
sdl~P-.od y N
klldatbonch
y N
G ·R~ved Wllhin c;nr,'llmos
. N
lcoc T-W:as:
1 Pl'esonl an Ou!M Paclcaga CJ N• NA
2 ~011 on OUter Paclalge
Y, N NA
3 . Pr»sent on 53tnplo Q y N
4 Unbro!lm on&!mplo e
y N
Di~es Between Sa"mple
Labols ar<l coc P.eoold?
'( C)
Date: See the Analytical Scope of Work for Reporting Limits and VOC
analyte list.
Tlme:
Date:
Time:
Date:
Time:
-
....
AWAL-Analytical Scope ofWork
White Mesa Mill Blanding Utah
Page 11 of 13
Contaminant Analytical
Methods
to be Used
~I Inorganics
Chloride ----------.... A4500-CI
B or
~
or £300.0
Sulfate ~ r
-------E300.0
Carbon~03 A2320 B
~bonate as HC03 A2320 B
Reporting
Limit
I mg/L
~-><
Hlng/L
I mg/L
I mg/L
Volatile Organic Compounds -Chloroform Program
Carbon Tetrachloride SW8260B 1.0 11g/L
or
SW8260C
Chloroform SW8260B 1.0 11g/L
or
SW8260C
Dichloromethane SW8260B 1.0 11g/L
(Methylene Chloride) or
SW8260C
Ch ]oro methane SW8260B 1.0 11g/L
or
SW8260C
~OCs-Tailings JmpounGment Samples Ool.y
I ,2,4~chlorobenzene SW8270D <10 ug/L
1,2-Dich~enzene SW8270D <10 ug/L
1,3-Dichlorob~ne SW8270D <10 ug/L
1,4-Dichlorobenzen~ SW8270D <10 ug/L
1-Methy lna_p_hthalene ~ SW8270D <10 ug/L
2,4,5-Trichlorophenol ~8270D <10 ug/L
2,4,6-Trichlorophenol SWrn.QD <10 ug/L
2,4-Dichlorophenol SW82700"-....._<10 ug/L
2,4-Dimethylphenol SW8270D <~g/L
2,4-Dinitrophenol SW8270D <20u~
2,4-Dinitrotoluene SW8270D <]..e'Ug/L
2,6-Dinitrotoluene SW8270JY ~-'<10 ug/L
2-Chloronaphthalene SW8,)?6D <10 ug/L
2-Chlorophenol ~8270D <10 ug/L
2-Methy !naphthalene / SW8270D <10 ug/L
2-Methylphenol / SW8270D <10 ug/L
2-Nitrophenol ./ SW8270D <10 ug/L
3&4-Meth~enol SW8270D <10 ug/L
3,3 '-Ok1llorobenzidine SW8270D <10 ug/L
~initro-2-methylphenol SW8270D <10 ug/L
Maximum Sample Sample
Holding Preservation Temperature
Times Requirements Requirements
_.... --28 days None ~
------------~
2~ None :S 6°C
~
14 days None ~
14 days None ---
14 days HCI topH<2 :S 6°C
14 days HCI to pH<2 :S 6°C
14 days HCI to pH<2 :S 6°C
14 days HCI to pH<2 :S 6°C
/
7/40 days None <,PC
7/40 days None _A6°C
7/40 days None /,/ <6°C
7/40 days Nony :S 6°C
7/40 days ..Nbne <6°C
7/40 days / None <6°C
7/40da~ None <6°C
7 I 4J)-d'ay s None :S 6°C
~/40 days None <6°C
7/40 days None <6°C
~40days None <6°C
7/4~s None <6°C
7/40da~ None <6°C
7/40 days ~None <6°C
7/40 days NsQe <6°C
7/40 days None~ <6°C
7/40 days None ................. <6°C
7/40 days None ~6°C
7/40 days None :S6~
7/40 days None :S6°C ...............
Analysis
Ammonia
COD
Cyanide
Metals
NOz&N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s
Preservative I 2_ 3 tf s ~
pH<2HzS04
pH<2HzS04
pH>12
NaOH
pH<2HN03
pH<2HzS04 V..c5 t/6 V.o 1/.d vc.f Vh
pH<2HCL -,. r , II I
pH<2HzS04
pH>9NaOH,
ZnAcetate
pH<2HzS04
pH<2HzS04
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
SetE doH
7. f 7
~5 IVc> ~/)
II
10 J/
u tk5
I
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+
...
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference.
Jt..
iZ-f
7
LabSetm: !&C?) tfo 0
ltfv
/,3 JL( ;s-/u /7
4 Jf'~-ll~ .. --·1/15 (ks h.-4
7 7 ,
~~
VcJ
1/ I
I
Analysis
Ammonia
COD
Cyanide
Metals
N02&N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s ~--·le Set Ext•
Preservative /9 )(\ 2( ,z:z_ J..t;
pH<2H2S04
pH<2H2S04
pH>12
NaOH
pH<2HN03
pH<2H2S04 VeS V,:;e. ~5 11/5 /.,(
pH<2HCL I I It I'
pH<2H2S04
pH>9NaOH,
ZnAcetate
pH<2 H2S04
pH<2H2S04
·-
Pour a small amount of sample in the sample lid
Pour sample from Lid gently over wide range pH paper
Do Not dip the pH paper in the sample bottle or lid
doH -----------
I
1)
2)
3)
4)
5)
6)
1)
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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GARRINPALMER 49 LBS 4356782221
ENERGY FUI!I.S-WHITE MESA MILL
6425 S HWY 191
BLANDING ur 84511
SHIP TO:
RECEMNG
801-263-8686
AMERJCAN WEST ANALITICAL LABS
3440 SOUI'H 700 WEST
SALT LAKE CllY UT 84119
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I!NERGYFUELS-WHITEMESAMILL
6425 S HWY 191
BLANDING Uf 84511
SHIP TO:
RECEIVING
801-263-8686
AMERICAN WEST ANALYTICAL LABS
3440 SOUTH 700 WEST
SALT LAKE CITY UT 84119
1 OF 1
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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
Garrin Palmer
Energy Fuels Resources, Inc.
6425 South Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 1st Quarter Chloroform 2016
Dear Garrin Palmer: Lab SetiD: 1603479
American West Analytical Laboratories received sample(s) on 3/23/2016 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:
Digitally signed by Jose G.
J 0 S e G ~~~~~=Jose G, Rocha,
• o=American West Analytical
Laboratories, ou, R 0 c h a ~~~=[e-mail].
Date: 2016.03.30 12:56:39
-06'00'
Laboratory Director or designee
Report Date: 3/30/2016 Page I of27
All analyses applicnble 10 the CWA. SDWA, and RCRA are performed in accordance to NELAC pfO\ocoll. l)ellment stunpling. iniOnnJUfan is located on the nttnched COC. Conlidenlinl Business lnfnrmation: This report is pro\•ided for the exclusi\·e use of the
~ddressee. PriYi\e~es 0~ sub .. seq~ent ~~e or the ?.~le of this .cOI~pnny or nny 1~7mber or its stnff, or rquOtluctl~~ ~~this ~pol! in ~Oil~h.'CilOI~ \\~th the (l~~·eltisement. P~?moti~ ~r ~~le or~!~. ~rod~ct or P':?Cess, ~r in 7onn:c~ion w!th th~ r~-publicution or this report
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 1st Quarter Chloroform 2016
Lab Set ID: 1603479
Date Received: 3/23/2016 930h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1603479-001A TW4-06R 03212016 3/2112016 1034h Aqueous Anions, E300.0
;alt Lake City, UT 84119 1603479-00IB TW4-06R 03212016 3/21/2016 1034h Aqueous Nitrite/Nitrate (as N), E353.2
16034 79-00 I C TW4-06R 03212016 3/21/2016 1034h Aqueous VOA by GC/MS Method
8260C/5030C
Phone: [phone] 79-002A 11W-32 03222016 3/22/2016 1230h Aqueous Anions, E300.0
16034 79-002B MW-32 03222016 3/22/2016 1230h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 16034 79-002C MW-32 03222016 3/22/2016 1230h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260C/5030C
!-mail: [e-mail] 1603479-003A TW4-06 03222016 3/22/2016 85lh Aqueous Anions, E300.0
16034 79-003B TW4-06 03222016 3/22/2016 851h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 16034 79-003C TW4-06 03222016 3/22/2016 851h Aqueous VOA by GC/MS Method
8260C/5030C
1603479-004A TW4-07 03222016 3/22/2016 858h Aqueous Anions, E300.0
Kyle F. Gross 1603479-004B TW4-07 03222016 3/22/2016 858h Aqueous Nitrite/Nitrate (as N), E353.2
1603479-004C TW4-07 03222016 3/22/2016 858h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1603479-005A TW4-10 03222016 3/22/2016 906h Aqueous Anions, E300.0
Jose Rocha 16034 79-005B TW4-10 03222016 3/22/2016 906h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 16034 79-005C TW4-10 03222016 3/22/2016 906h Aqueous VOA by GC/MS Method
8260C/5030C
16034 79-006A TW4-60 03222016 3/22/2016 1500h Aqueous Anions, E300.0
1603479-006B TW4-60 03222016 3/22/2016 1500h Aqueous Nitrite/Nitrate (as N), E353.2
16034 79-006C TW4-60 03222016 3/22/2016 1500h Aqueous VOA by GC/MS Method
8260C/5030C
1603479-007A TW4-70 03222016 3/22/2016 1230h Aqueous Anions, E300.0
16034 79-007B TW4-70 03222016 3/22/2016 1230h Aqueous Nitrite/Nitrate (as N), E353.2
1603479-007C TW4-70 03222016 3/22/2016 1230h Aqueous VOA by GC/MS Method
8260C/5030C
1603479-008A Trip Blank 3/21/2016 Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 3/30/2016 Page 2 of27
All analyses applicable to the CWA. SDWA. Md RCRA rue performed in accordnnce to NELAC protocols. Pertinent sampling informntion is locnted on the ntlncht.'<l COC. Conlidentinl Bm;iness Information: This report is pro"ided for the exclushc use of the ~cldressee. Pririle~es o,r su~seq~renl ~~~e or the ~~e of this ,cor~JlDil~ or nny ~~~'!lber of its stnff, or reproductio~ ~~·this repm3 in ~on~u~clion" \\ilh the a~verliser~ent. P~?motio.n ~I' ~ale of ~U!} ~rodr~ct or PI,?Cess, ~r in ~nn~c~ion w!th th~ r~·publication or this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awaf-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
1st Quarter Chloroform 2016
1603479
3/23/2016
3/21 & 3/22/2016
Intact
None
Holding Time and Preservation Requirements: The analysis and preparation for the
samples were performed within the method holding times. The 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 I Matrix Spike Duplicates (MS/MSD): All percent recoveries and
RPDs (Relative Percent Differences) were inside established limits, with the
following exceptions:
Sample ID Analyte QC Explanation
1603400-021B Nitrate/Nitrite MS/MSD Sample matrix interference
1603479-001B Nitrate/Nitrite MS/MSD Sample matrix interference
Corrective Action: None required.
Report Date: 3/30/2016 Page 3 of27
All ann lyses applicnble to the CWA. SDWA. and RCRA a1e perfom1erl in accordance to NELAC p1olocols Pe11inent sa.mpling information is locnted on the attached COC Conlirlentinl Business lnfonnal10n: This report is provided for the exclush·e use of1he
~ctdressee. P11\'ile~es o; sub .. seq~Jent ~~~e or the ~~le of this .con.•pntl~ or nn) l~'!lbel of its stnrr, or reproduclio~ ~~'this repl..)l~ in ,con~\I!Ction .. \\ith the D~verlisement, p~omotlo,n ~I sale of ~!Y riC'Idl~CI or Pl,ocess, ~r in ~nn:c~ion \\'!th th~ r~-publication 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.awai-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
1st Quarter Chloroform 20 16
1603479
3/23/2016
3/21 & 3/22/2016
Intact
None
SW-846 8260C/5030C
Volatile Organic Compounds
General Set Comments: Multiple target analytes were observed above reporting limits.
Holding Time and Preservation Requirements: All samples were received in appropriate
containers and properly preserved. The analysis and preparation of all samples were
performed within the method holding times following the methods stated on the analytical
reports.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Batch QC Requirements: MB, LCS, MS, MSD, RPD, and Surrogates:
Method Blanks (MBs): No target analytes were detected above reporting limits,
indicating that the procedure was free from contamination.
Laboratory Control Sample (LCSs): All LCS recoveries were within control
limits, indicating that the preparation and analysis were in control.
Matrix Spike I 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: 3/30/2016 Page 4 of27
All analyses o.p~licnble to the CWA. SDWA. and RCRA o.re ~erl'ormed in accordance to NELAC protocols. Pcr11R"'I sampling information is located on the aunched COC Confidential Business lnfonnnlion: This repon is pro\'ided ror1he exclusive use of the ~dtiressee. Privile~es o,rsub .. seq~Ient ~~~e oflhe ~~te of this ,con~pany or nny ~~~~bcr of its :'llnff, or reproducti~ ~r this repo~ in .con~u~clion .. '"ilh the ll~\erlisemenl, P~?moti~n ~r sale of ?J!Y ~rodL~ct or P~?ccss, ~r in ~nn~c~ion w!th 1h~ r:-p~blication of this rl!port
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa"\: (801 ) 263-8687
e-mail: [e-mail], web: www.awal-labs.com
jlC SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
Method MDL
Reporting
Limit
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount o/oREC
Lab Sample ID: LCS-R88598 Date Analyzed: 03/25/2016 806h
Test Code: 300.0-W
Chloride 4.80 mg/L E300.0 0.00516 0.100 5.000 0 95.9
Lab Sample ID: LCS-R88554 Date Analyzed: 03/24/2016 1659h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.09 mg/L E353.2 0.00833 0.0100 1.000 0 109
Limits
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 3/30/2016 Page 20 of27
analyses applicable to the CWA. SDW A, and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tr
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R88598 Date Analyzed:
Test Code: 300.0-W
Chloride <0.100
Lab Sample ID: MB-R88554 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa;:: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/25/2016 749h
mg/L EJOO.O 0.00516 0.100
03/24/2016 1658h
mg/L E353.2 0.00833 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/30/2016 Page 21 of 27
analyses applicable to the CWA. SDWA~ and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the anached COC. Confidential Business Infonnation; This report is provided for the exclusive use of the addressee Privileges of subsequent use oftl"
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sa1e of any producr or process. or in connection with the re-publication of this repon for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1603479-002AMS Date Analyzed:
Test Code: 300.0-W
Chloride 134
Lab Sample ID: 1603400-021BMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 25.9
Lab Sample ID: 1603479-00IBMS Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.5
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa"X: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Reporting
Units Method MDL Limit
03/25/2016 857h
mg/L E300.0 0.103 2.00
03/24/2016 170lh
mg/L E353.2 0.167 0.200
03/24/2016 1720h
mg/L E353.2 0.0833 0.1 00
Contact: Garrin Palmer
Dept: we
QCType: MS
Amount Spike Ref.
Spiked Amount %REC
100.0 36.7 96.9
20.00 2.92 115
10.00 0 115
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/30/2016 Page 22 of27
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infom1ation is located on the attached COC_ Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use oftt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisemenl promotion or sale of any product or process., or in connection with the re-publication of this report for any purpose olher than for the addressee will be granted only on contact Thls
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 16034 79
Project: l st Quarter Chloroform 20 16
Analyte Result
Lab Sample ID: 1603479-002AMSD Date Analyzed:
Test Code: 300.0-W
Chloride 133
Lab Sample ID: 1603400-021BMSD Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 25.2
Lab Sample ID: 1603479-00IBMSD Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.5
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa'l:: [phone]
e-mail: [e-mail]. web: www.awal-labs.com
_QC SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount
Units Method MDL Limit Spiked
03/25/2016 914h
mg/L E300.0 0.103 2.00 100.0
03/24/2016 1702h
mg/L E353.2 0.167 0.200 20.00
03/24/2016 172lh
mg!L E353.2 0.0833 0.100 10.00
Garrin Palmer
we
MSD
Spike Ref.
Amount %REC
36.7 96.7
2.92 Ill
0 115
1 -Matrix spike recovery indicates matrix interference. The method is in control as indicated by the LCS.
Limits
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPD Ref. RPD
Amt %RPD Limit
134 0.161 20
25.9 2.86 10
11.5 0.261 10
Qual
Report Date: 3/30/2016 Page 23 of27
anaJyses applicabJe to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC Confidential Business lnfonnation This report is pro~,o·ided for the exclusive use of the addressee Privileges of subsequent use oft}
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee wtll be granted only on contact This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: LCS VOC-2 032316A Date Analyzed:
Test Code: 8260-W-DEN100
Chloroform 18.6
Methylene chloride 18.3
Surr: 1 ,2-Dichloroethane-d4 47.2
Surr: 4-Bromofluorobenzene 50.0
Surr: Dibromofluoromethane 48.9
Surr: Toluene-d8 49.5
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: MSVOA
QC Type: LCS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/23/2016 1103h
J.lg/L SW8260C 0.153 1.00 20.00 0 93.2
J.lg/L SW8260C 0.172 1.00 20.00 0 91.7
J.lg/L SW8260C 50.00 94.5
J.lg/L SW8260C 50.00 100
J.lg/L SW8260C 50.00 97.7
J.lg/L SW8260C 50.00 99.1
Limits
85 -124
81 -135
80-122
85 -121
80-116
81 -123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/30/2016 Page 24 of27
analyses apphcable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent samp1ing information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee_ Privileges of subsequent use oftt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or ln connection wlth the re-publication of this report for any purpose other than for the addressee wll1 be granted only on contact This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB VOC-2 032316A Date Analyzed:
Test Code: 8260-W-DEN100
Carbon tetrachloride < 1.00
Chloroform < 1.00
Chloromethane < 1.00
Methylene chloride < 1.00
Surr: 1 ,2-Dichloroethane-d4 49.0
Surr: 4-Bromofluorobenzene 51.6
Surr: Dibromofluoromethane 48.6
Surr: Toluene-d8 50.5
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
Method MDL Limit Spiked
Garrin Palmer
MSVOA
MBLK
Spike Ref.
Amount %REC
03/23/2016 1142h
llg!L SW8260C 0.504 1.00
llg!L SW8260C 0.153 1.00
llg!L SW8260C 0.163 1.00
llg!L SW8260C 0.172 1.00
llg!L SW8260C 50.00 98.0
llg!L SW8260C 50.00 103
llg!L SW8260C 50.00 97.2
llg!L SW8260C 50.00 101
Limits
80-122
85 -121
80-116
81-123
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/30/2016 Page 25 of27
analyses applicable to the CWA. SDW A, and RCRA are perfom1ed ln accordance to NELAC protocols Pertinent sampling infonnation is located on the attached COC Confidential Business Information: This repon is provided for the e.xclusive use of the addressee Privileges of subsequent use oft}
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any produd 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
ANA LYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1603479-00SCMS Date Analyzed:
Test Code: 8260-W-DENIOO
Chloroform 1,850
Methylene chloride 380
Surr: 1,2-Dichloroethane-d4 999
Surr: 4-Bromofluorobenzene 1,010
Surr: Dibromofluoromethane 995
Surr: Toluene-d8 988
Lab Sample ID: 1603480-00IAMS Date Analyzed:
Test Code: 8260-W-DENIOO
Chloroform 20.9
Methylene chloride 18.2
Surr: I ,2-Dichloroethane-d4 47.0
Surr: 4-Bromofluorobenzene 49.9
Surr: Dibromofluoromethane 50.4
Surr: Toluene-d8 50.1
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Contact: Garrin Palmer
Dept: MSVOA
QCType: MS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/23/2016 1732h
J.!g/L SW8260C 3.06 20.0 400.0 1430 107
J.!g/L SW8260C 3.44 20.0 400.0 0 95.1
J.!g/L SW8260C 1,000 99.9
J.!g/L SW8260C 1,000 101
J.!g/L SW8260C 1,000 99.5
Jlg/L SW8260C 1,000 98.8
03/23/2016 1553h
J.!g/L SW8260C 0.153 1.00 20.00 0 105
J.!g/L SW8260C 0.172 1.00 20.00 0 90.9
J.!g/L SW8260C 50.00 94.0
J.!g/L SW8260C 50.00 99.8
J.!g/L SW8260C 50.00 101
J.!g/L SW8260C 50.00 100
Limits
50-146
30-192
72-151
80-152
80-124
77-129
50-146
30-192
72-!51
80-152
80-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 3/30/2016 Page 26 of27
analyses applicable IO the CW A. SDW A, and RCRA are performed in acCO<dance lo NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information This report is provided for the e.xclusive use of the addressee Privilege.s of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the adverrisement, promotioo or sale of any product or process. or in connection with the re-publication of this repon for any pwpose other than for the addressee will be granted only on contact. This
ANALYTICAL
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1603479
Project: 1st Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1603479-00SCMSD Date Analyzed:
Test Code: 8260-W-DEN100
Chloroform 1,840
Methylene chloride 405
Surr: 1 ,2-Dichloroethane-d4 1,010
Surr: 4-Bromofluorobenzene 1,010
Surr: Dibromofluoromethane 993
Surr: Toluene-d8 993
Lab Sample ID: 1603480-00IAMSD Date Analyzed:
Test Code: 8260-W-DENIOO
Chloroform 19.4
Methylene chloride 18.7
Surr: I ,2-Dichloroethane-d4 50.6
Surr: 4-Bromofluorobenzene 50.0
Surr: Dibromofluoromethane 50.2
Surr: Toluene-d8 49.3
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: Garrin Palmer
Dept: MSVOA
QCType: MSD
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
03/23/2016 1752h
J.lg/L SW8260C 3.06 20.0 400.0 1430 103
flg/L SW8260C 3.44 20.0 400.0 0 101
J.lg/L SW8260C 1,000 101
J.lg/L SW8260C 1,000 101
J.lg/L SW8260C 1,000 99.3
J.lg/L SW8260C 1,000 99.3
03/23/2016 1613h
J.lg/L SW8260C 0.153 1.00 20.00 0 97.0
J.lg/L SW8260C 0.172 1.00 20.00 0 93.4
J.lg/L SW8260C 50.00 101
J.lg/L SW8260C 50.00 99.9
J.lg/L SW8260C 50,00 100
J.lg/L SW8260C 50.00 98.5
Limits
50-146
30-192
72-151
80-!52
80-124
77-129
50-146
30-192
72-151
80-152
80-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit
1850 0.758 25
380 6.26 25
20.9 7.58 25
18.2 2.77 25
Qual
Report Date: 3/30/2016 Page 27 of27
analyses applicable to the CWA~ SDVv"A, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling infom1a.tion is located on the attached COC Confidential Business Information: TI1is reJXIn is provided for the exclusive use of the addressee. Privileges of subsequent use oftt
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of an)' product or process. or in connection with the re-publication of this report for any purpose other than for the addressee ,~..-111 be granted only on contact, This
American West Analytical Laboratories UL
Denison
WORK ORDER Summary WorkOrder: 1603479 Page 1 of2
Client:
Client ID:
Project:
Comments:
SampleiD
1603479-001A
1603479-00IB
1603479-001C
1603479-002A
1603479-002B
1603479-002C
1603479-003A
1603479-003B
1603479-003C
1603479-004A
16034 79-004B
16034 79-004C
1603479-00SA
16034 79-00SB
1603479-00SC
Printed: 3/23/2016
Energy Fuels Resources, Inc. Due Date: 4/1/2016
DEN100 Contact: Garrin Palmer
1st Quarter Chloroform 2016 QC Level: ill WO Type: Project
PA Rush. QC 3 (Summary/No chromatograms). RL of 1 ppm for Chloride and VOC and 0.1 ppm for N02/N03 -Run N02/N03 at a 1 OX dilution. Expected
levels provided by client-see Jenn. J-flag what we can't meet. ElM Locus and BOD-Denison. Email Group.;
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1W4-06R_ 03212016 3/2112016 1034h 3/23/2016 0930h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 41 #of Surr: 4
MW-32_03222016 3/2212016 1230h 3/23/2016 0930h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SELAnalyJes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 4/ #of Surr: 4
1W4-06_03222016 312212016 085lh 312312016 0930h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DENJ 00; #of Anaiytes: 4/ #of Surr: 4
1W4-07 _03222016 3/22/2016 0858h 3/2312016 0930h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN100; # ojAnaJytes: 4 I# ofSurr: 4
1W4-10_03222016 3/2212016 0906h 3/23/2016 0930h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
FOR LABORATORY USE ONLY [fill out on page 1]: %M 0 RT 0 CN 0 TAT 0 QC 0 HOK __ _ HOK __ _ HOK___ COG Emailed, ____ _
3
3
3
3
3
WORK ORDER Summary WorkOrder: 1603479 Page2of2
Client: Energy Fuels Resources, Inc. Due Date: 4/1/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1603479-006A 1W4-60_03222016 3/22/2016 1500h 3/23/2016 0930h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1603479-006B N02JN03-W-353.2 df-no2/no3
1 SEL Ana/ytes: N03N02N
1603479-006C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; # pf Anaiytes: 4 I# of Surr: 4
1603479-007A 1W4-70_03222016 3/22/2016 1230h 3/23/2016 0930h 300.0-W Aqueous df-wc
I SEL Analytes: CL
16034 79-007B N02/N03-W-353.2 df -no2/no3
I SEL Ana/ytes: N03N02N
1603479-007C 8260-W-DENlOO VOCFridgc 3
Test Group: 8260-W-DENIOO; #of Analytes: 4 I # ofSu": 4
1603479-00&A Trip Blank 3/21/2016 3/23/2016 0930h 8260-W-DENlOO Aqueous VOCFridge 3
Test Group: 8260-W-DENI OQ; II of Analytes: 4 I # of Su": 4
Printed: 3/2312016 FORLABORATORYUSEONLY[filloutonpage1]: %M 0 RT 0 CN 0 TAT 0 QCO HOK __ _ HOK __ _ HOK___ COC Emailed. ____ _
American West
Analytical Laboratories
4e3W.3600S. SaltLakeCity,UT 84115
Phone# (601) 263-$86 Tott Free# [phone]
L~ Fax# [phone] Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] Cell#:
[e-mail]; [e-mail];
Email: dturlt@ene'I!J'{uels.com
Project Name: 1ST QUARTER CHLOROFORM 2016
Project#:
PO #:
Sampler Name: TANNER HOLLIDAY
Date
Sample iD: Samoled
I TW4-06R_03212016 3/21/2016
• MW-32_03222016 3/22/2016
I TW4-06_03222016 3/22/2016
I TW4-07_03222016 3/22/2016
; TW4-10_03222016 3/22/2016
I TW4-60_03222016 3/22/2016
' TW4-70_03222016 3/22/2016
I TRIPBLANK 3/21/2016
I TEMPBLANK 3/22/2016
1G Q
1
2
Relinquished by: &ev--·~ Oat a:
SI!JO'lltn 3/2312()16
P~nl Name: GARRIN PALMER [Timo: C> t; :SO
RelinqUished by: ODie:
Signature
&me:
P~ntName:
Relinquished by: Pate:
Sl nature
(Time:
Print Name:
Re11nqulshed by: Date:
Signature
Time:
Print Name:
I
T ime
S amoted
1034
1230
851
858
906
1500
1230
CHAIN OF CUSTODY
All analysis will be conducted using NELAP accredited methods and all data will be reported using AWAL's standard analytellsts and reporting
lim~s (POL) unless specifically requested otherwise on this Chain of Custody and/or attached docUmenlalion.
QC Level: I Tum Around Time: Unless other arrangements have been made,
signed reports will be emailed by 5:00pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA -0 ELAP/A2LA
0 NLLAP
~ c 0 Non·Compliance ci M 0 0 Other: tn l') u ~ )( >2. ... ~ " c c: ~ t'l ~ 0 0 C'1 ::;; 0 <£ Known Hazards 0 " 1!: tn ...... :t Ill I.J a. C'il u & 0 E g tl ~ "' Sample Comments .. Cll
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
l5 w X X X
3 w X
1 w .
/
=~~ .~ _J Do}'/,,_#6. Special Instructions:
Print Nama~ L:(a_ 1-/:U~~ rm6; n~,
/~Q) t-() 7'
AWAL Lab Sample Set#
Page 1 of 1
1'"'"1L ee I
laboratory Use Only
---~ 1 Shipped lwlddoilvor
2 Arnbiont CMied
3 Temperulln :.{ 'tf •c
4 Received Brol<en/Leaking
(lmpropefiy Sealed)
y . ®
S~rl)'Prcsetvod y N
l<ed at bench
y N
6 Received Within
0ngTimes N
COCTopoWas: , Present on O<llor PacJoo,go
y N eJ
2 Urtlrolo!n on Outer Packa~ Y N A
3 Present on Sample G) y N
4 Unbroken on Sample 0 y N
Discrepancies Bet~ ~amPle
Labels and COC Record?
y C)
Roa>!oiacl llyl ( Oato: See the Analytical Scope of Work for Reporting Umlts and VOC
Slgno.ture ,. analyte llst.
Time:
Print: Name:
RecsNedlly: . Date:
Signature
; &me:
Print Name:
Aece!VO<l by: Oate:
SignatLWll
Tlme:
PrlniName:
A W AL -Analytical Scope of Work
White Mesa Mill Blanding Utah
Page 11 of 13
Contaminant Analytical
Methods
to be Used
~1 Inorganics
Chloride----------A4500-CI
B or
~
or E300.0
Sulfate ~ r ------E300.0
Carbon~03 A2320 B
~bonate as HC03 A2320 B
Reporting
Limit
1 mg/L
~
Hlllg/L
1 mg/L
1 mg/L
Volatile Organic Compounds -Chloroform Program
Carbon Tetrachloride SW8260B 1.0 flg/L
or
SW8260C
Chloroform SW8260B 1.0 flg/L
or
SW8260C
Dichloromethane SW8260B 1.0 flg/L
(Methylene Chloride) or
SW8260C
Chloromethane SW8260B 1.0 flg/L
or
SW8260C
~OCs-Tailings Impoundment Samples Only
1 ,2,~chlorobenzene SW8270D <10 ug/L
1,2-Dich~enzene SW8270D <10 ug/L
1,3-Dichlorob-ne SW8270D <10 ug/L
1,4-Dichlorobenzen~ SW8270D <10 ug/L
1-Methy !naphthalene ~ SW8270D <10 ug/L
2,4,5-Trichlorophenol ~8270D <10 ug/L
2,4,6-Trichlorophenol SWS'NQD <10 ug/L
2,4-Dichlorophenol SW8270ft-. ,....._ <10 ug/L
2,4-Dimethy lpheno 1 SW8270D ~g/L
2,4-Dinitrophenol SW8270D <20u~
2,4-Dinitrotoluene SW8270D <,J..e""ug/L
2,6-Dinitrotoluene SW8270IV <10 ug/L
2-Chloronaphthalene SW~D <10 ug/L
2-Chlorophenol ~8270D <10 ug/L
2-Methy !naphthalene / SW8270D <10 ug/L
2-Methylphenol / SW8270D <10 ug/L
2-Nitrophenol / SW8270D <10 ug/L
3&4-Methy}t)henol SW8270D <10 ug/L
3,3 · -Qicli"lorobenzidine SW8270D <10 ug/L
~initro-2-methylphenol SW8270D <10 ug/L
Maximum Sample Sample
Holding Preservation Temperature
Times Requirements Requirements
_.. v
28 days None ~ ~ ~
2~ None :S 6°C r------_
14 days None ~
14 days None ----
14 days HCl to pH<2 :S 6°C
14 days HCl to pH<2 :S 6°C
14 days HCl to pH<2 :S 6°C
14 days HCl to pH<2 :S 6°C
/
7/40 days None <j)S-C
7/40 days None A6°C
7/40 days None / v <6°C
7/40 days Not? <6°C
7/40 davs ~ne <6°C
7/40 days I/ None <6°C
7/40d~ None <6°C
7/4J}t(ays None <6°C
~/40 days None <6°C
7/40 days None <6°C
~40days None <6°C
7/~s None <6°C
7/4oda~ None <6°C
7/40 days ~None <6°C
7/40 days ~e <6°C
7/40 days Non~ <6°C
7/40 days None """!'--.. <6°C
7/40 days None ~6°C
7/40 days None <6~
7/40 days None <6°C ~
Analysis
Ammonia
COD
Cyanide
Metals
NOz&N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s --le Set Ext' --
Preservative ( z_ 3 I( ,) (r.
pH<2HzS04
pH<2HzS04
pH>12
NaOH
pH<2HN03
pH<2 HzS04 Jlc.; tl-l'; wh i?_"J ~~5 vcr
pH<2HCL I {< I' I
pH<2H2S04
pH>9NaOH,
ZnAcetate
pH<2HzS04
pH<2HzS04
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
7
~ II
doH
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate column above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+ ...
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference .
Lab SetiD: /G,(IJ ~~L
-
---
Tab I
Quality Assurance and Data Validation Tables
1-1 : Field QA/QC Evaluation
1x Casing 2x Casing
Location Volume Volume Pumped Volume Volume Check Conductivity RPD pH RPD Temp RPD Redox Potential RPD Turbidity
MW-04 NA Continuously pumped well --1858 N/A 7.37 N/A 14.78 N/A 256
TW4-01 NA Continuously pumped well -2335 N/A 7.25 N/A 15.26 N/A 268
TW4-02 NA Continuously pumped well -3408 N/A 7.23 N/A 15.14 N/A 257
TW4-03 55.04 110.00. 110 Pumped Ocy 1709 1714 0.29 5.97 6.01 0.67 14.21 14.18 0.21 NM
TW4-04 NA C0nlinu<;lusly pumped well .. 2301 N/A 7.11 N/A 16.02 N/A 292
TW4-05 36.20 100.00 72 OK 1491 1482 0.61 6.27 6.28 0.16 15.24 15.24 0.00 428 427
TW4-06 16.52 33.33 33 Pumped Dry 3652 3268 11.10 6.20 6.25 0.80 15.35 15.38 0.20 NM
TW4-07 28.55 70.00 57 OK 1577 1570 0.44 6.52 6.53 0.15 14.96 14.97 0.07 352 350
TW4-08 29.37 80.00 59 OK 4812 4811 0.02 6.12 6.12 0.00 15.04 15.05 0.07 422 420
TW4-09 37.56 90.00 75 OK 2446 2446 0.00 6.13 6.12 0.16 14.93 14.93 0.00 420 419
TW4-10 32.01 70.00 64 Pumped D ry 2866 2891 0.87 6.31 6.29 0.32 14.19 14.32 0.91 NM
TW4-11 NA Continuously pumped well --3596 N/A 7.25 N/A 16.83 N/A 231
TW4-12 36.43 80.00 73 OK 1481 1479 0.14 6.47 6.51 0.62 14.98 14.97 0.07 417 416
TW4-13 32.94 60.00 66 Pumped Dry 2024 2029 0.25 7.01 7.00 0.14 14.72 14.70 0.14 NM
TW4-14 8.45 15.00 17 Pumpc~d Drcy 5150 5163 0.25 6.22 6.21 0.16 12.45 12.50 0.40 NM
MW-26 NA Continuously pumped well --3425 N/A 6.99 N/A 15.21 N/A 276
TW4-16 51.00 120.00 102 OK 3561 3561 0.00 6.02 6.03 0.17 15.74 15.75 0.06 347 346
MW-32 36.33 78.12 73 OK 3827 3819 0.21 6.17 6.15 0.32 14.80 14.78 0.14 449 440
TW4-18 47.02 120.00 94 OK 1877 1875 0.11 5.95 5.95 0.00 16.77 16.77 0.00 416 415
TW4-19 NA Continuously pumped well -3768 N/A 7.22 N/A 16.67 N/A 331
TW4-20 NA Continuously pumped well ·-3927 N/A 6.94 N/A 15.49 N/A 306
TW4-21 NA Continuously pumped well --4528 N/A 6.44 N/A 15.81 N/A 349
TW4-22 NA Continuously pumped well -5570 N/A 7.05 N/A 15.32 N/A 317
TW4-23 29.15 80.00 58 OK 3650 3641 0.25 6.14 6.14 0.00 14.34 14.34 0.00 311 311
TW4-24 NA Continuously pumped well --7462 N/A 6.92 N/A 15.04 N/A 334
TW4-25 NA Continu0usl,y pumped well -2739 N/A 7.14 N/A 14.63 N/A 314
TW4-26 12.57 20.00 25 Pumped Dry 6441 6459 0.28 4.24 4.22 0.47 12.80 12.85 0.39 NM
TW4-27 10.63 15.00 21 Pumped Dry 5188 5226 0.73 6.29 6.3 0.16 12.27 12.37 0.81 NM
TW4-28 43.91 100.00 88 OK 1351 1354 0.22 6.61 6.63 0.30 14.93 14.92 0.07 381 380
TW4-29 12.94 20.00 26 Pump_ed Dry 4235 4243 0.19 6.22 6.25 0.48 13.75 13.80 0.36 NM
TW4-30 10.87 22.50 22 Pumped Dry 4342 4345 0.07 4.65 4.64 0.22 13.94 13.98 0.29 NM
TW4-31 17.17 I 30.00 34 Pumped Dry 4679 4692 ' 0.28 6.71 6.69 0.30 13.30 13.35 0.38 NM
TW4-32 41.85 100.00 84 OK 7185 7206 0.29 3.06 3.06 0.00 14.82 14.82 0.00 517 517
TW4-33 10.05 13.33 20 Pumped Dry 4392 4400 0.18 5.71 5.73 0.35 13.63 13.66 0.22 NM
TW4-34 16.55 35.00 33 Pumped Dry 3909 3920 0.28 6.77 6.73 0.59 13.08 13.11 0.23 NM
TW4-35 8.71 13.33 17 PumRCdDry 4363 4390 0.62 6.54 6.53 0.15 13.04 13.10 0.46 NM
TW4-36 27.75 17.50 56 Pumped Dry 2354 2379 1.06 6.80 6.76 0.59 13.68 13.73 0.36 NM
TW4-37 NA Continuously pumped well -4417 N/A 7.15 N/A 15.58 N/A 315
MW-4, TW4-01, TW4-02, TW4-4, TW4-11, MW-26, TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, TW4-25, and TW4-37 are contmually pumped wells. TW4-22, TW4-24, and TW4-25 are pumped under the mtrate program.
TW4-03, TW4-06, TW4-10, TW4-13, TW4-14, TW4-26, TW4-27, TW4-29, TW4-30, TW4-31, TW4-33, TW4-34, TW4-35, and TW4-36 were pumped dry and sampled after recovery.
NM =Not Measured. The QAP does not require the measurement of redox potential or turbidity in wells that were purged to dryness.
RPD = Relative Percent Difference
N/A
N/A
N/A
NC
N/A
0.23 3.8
NC
0.57 9
0.48 3.0
0.24 19
NC
N/A
0.24 13.9
NC
NC
N/A
0.29 118
2.02 139
0.24 24
N/A
N/A
N/A
N/A
0.00 115
N/A
N/A
NC
NC
0.26 44
NC
NC
NC
0.00 12
NC
NC
NC
NC
N/A
The QAP states that turbidity should be less than 5 Nephelometric Turbidity Units ("NTU") prior to sampling unless the well is characterized by water that has a higher turbidity. The QAP does not require that turbidity measurements be less than 5
NTU prior to sampling. As such, the noted observations regarding turbidity measurements less than 5 NTU are included for information purposes only.
0.0
1.2
1.0
NM
11.0
3.8
NM
9
3.0
19
NM
30
14.0
NM
NM
0.00
115
141
24
0
4.4
0
0
113
0
0
NM
NM
43
NM
NM
NM
12
NM
NM
NM
NM
0.0
RPD
N/A
N/A
N/A
NC
N/A
0.00
NC
0.00
0.00
0.00
NC
N/A
0.72
NC
NC
N/A
2.58
1.43
0.00
N/A
N/A
N/A
N/A
1.75
N/A
N/A
NC
NC
2.30
NC
NC
NC
0.00
NC
NC
NC
NC
N/A
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 3/9/2016 3/14/2016 5 14 OK
Trip Blank Chloroform 3/9/2016 3/14/2016 5 14 OK
Trip Blank Chloromethane 3/9/2016 3/14/2016 5 14 OK
Trip Blank Methylene chloride 3/9/2016 3/14/2016 5 14 OK
Trip Blank Carbon tetrachloride 3/14/2016 3/18/2016 4 14 OK
Trip Blank Chloroform 3/14/2016 3/18/2016 4 14 OK
Trip Blank Chloromethane 3/14/2016 3/18/2016 4 14 OK
Trip Blank Methylene chloride 3/14/2016 3/18/2016 4 14 OK
Trip Blank Carbon tetrachloride 3/2112016 3/23/2016 2 14 OK
Trip Blank Chloroform 3/2112016 3/23/2016 2 14 OK
Trip Blank Chloromethane 3/21/2016 3/23/2016 2 14 OK
Trip Blank Methylene chloride 3/21/2016 3/23/2016 2 14 OK
MW-04 Chloride 3/9/2016 3/16/2016 7 28 OK
MW-04 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
MW-04 Chloroform 3/9/2016 3114/2016 5 14 OK
MW-04 Chloromethane 3/9/2016 3/14/2016 5 14 OK
MW-04 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
MW-04 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
TW4-01 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-01 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-01 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-01 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-01 Methylene chloride 3/9/2016 3114/2016 5 14 OK
TW4-01 Nitrate/Nitrite (as N) 3/9/2016 3/23/2016 14 28 OK
TW4-02 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-02 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-02 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-02 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-02 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-02 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
TW4-03 Chloride 3/15/2016 3/23/2016 8 28 OK
TW4-03 Carbon tetrachloride 3115/2016 3/18/2016 3 14 OK
TW4-03 Chloroform 3115/2016 3/18/2016 3 14 OK
TW4-03 Chloromethane 3/15/2016 3118/2016 3 14 OK
TW4-03 Methylene chloride 3/15/2016 3118/2016 3 14 OK
TW4-03 Nitrate/Nitrite (as N) 3/15/2016 3/24/2016 9 28 OK
TW4-03R Chloride 3114/2016 3/23/2016 9 28 OK
TW4-03R Carbon tetrachloride 3/14/2016 3118/2016 4 14 OK
TW4-03R Chloroform 3114/2016 3118/2016 4 14 OK
TW4-03R Chloromethane 3/14/2016 3/18/2016 4 14 OK
TW4-03R Methylene chloride 3/14/2016 3/18/2016 4 14 OK
TW4-03R Nitrate/Nitrite (as N) 3114/2016 3/24/2016 10 28 OK
TW4-04 Chloride 3/9/2016 3116/2016 7 28 OK
TW4-04 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-04 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-04 Chloromethane 3/9/2016 3114/2016 5 14 OK
TW4-04 Methylene chloride 3/9/2016 3114/2016 5 14 OK
TW4-04 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter N arne Sample Date Analysis Date (Days) Time (Days) Check
TW4-05 Chloride 3/17/2016 3/25/2016 8 28 OK
TW4-05 Carbon tetrachloride 3/17/2016 3118/2016 1 14 OK
TW4-05 Chloroform 3/17/2016 3/18/2016 1 14 OK
TW4-05 Chloromethane 3/17/2016 3/18/2016 1 14 OK
TW4-05 Methylene chloride 3117/2016 3/18/2016 1 14 OK
TW4-05 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-06 Chloride 3/22/2016 3/25/2016 3 28 OK
TW4-06 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
TW4-06 Chloroform 3/22/2016 3/23/2016 1 14 OK
TW4-06 Chloromethane 3/22/2016 3/23/2016 1 14 OK
TW4-06 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
TW4-06 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
TW4-06R Chloride 3/21/2016 3/25/2016 4 28 OK
TW4-06R Carbon tetrachloride 3/2112016 3/23/2016 2 14 OK
TW4-06R Chloroform 3/21/2016 3/23/2016 2 14 OK
TW4-06R Chloromethane 3/2112016 3/23/2016 2 14 OK
TW4-06R Methylene chloride 3/21/2016 3/23/2016 2 14 OK
TW4-06R Nitrate/Nitrite (as N) 3/21/2016 3/24/2016 3 28 OK
TW4-07 Chloride 3/22/2016 3/25/2016 3 28 OK
TW4-07 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
TW4-07 Chloroform 3/22/2016 3/23/2016 1 14 OK
TW4-07 Chloromethane 3/22/2016 3/23/2016 1 14 OK
TW4-07 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
TW4-07 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
TW4-08 Chloride 3/17/2016 3/23/2016 6 28 OK
TW4-08 Carbon tetrachloride 3/17/2016 3/18/2016 1 14 OK
TW4-08 Chloroform 3/17/2016 3/18/2016 1 14 OK
TW4-08 Chloromethane 3117/2016 3118/2016 1 14 OK
TW4-08 Methylene chloride 3/17/2016 3/18/2016 1 14 OK
TW4-08 Nitrate/Nitrite (as N) 3117/2016 3/24/2016 7 28 OK
TW4-09 Chloride 3/17/2016 3/25/2016 8 28 OK
TW4-09 Carbon tetrachloride 3/17/2016 3/18/2016 1 14 OK
TW4-09 Chloroform 3117/2016 3/18/2016 1 14 OK
TW4-09 Chloromethane 3/17/2016 3/18/2016 1 14 OK
TW4-09 Methylene chloride 3/17/2016 3/18/2016 1 14 OK
TW4-09 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-10 Chloride 3/22/2016 3/25/2016 3 28 OK
TW4-10 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
TW4-10 Chloroform 3/22/2016 3/23/2016 1 14 OK
TW4-10 Chloromethane 3/22/2016 3/23/2016 1 14 OK
TW4-l0 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
TW4-10 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
TW4-11 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-11 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-11 Chloroform 3/9/2016 3115/2016 6 14 OK
TW4-11 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-1l Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-11 Nitrate/Nitrite (as N) 3/9/2016 3112/2016 3 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter N arne Sample Date Analysis Date (Days) Time (Days) Check
TW4-12 Chloride 3115/2016 3/23/2016 8 28 OK
TW4-12 Carbon tetrachloride 3115/2016 3118/2016 3 14 OK
TW4-12 Chloroform 3115/2016 3/18/2016 3 14 OK
TW4-12 Chloromethane 3115/2016 3118/2016 3 14 OK
TW4-12 Methylene chloride 3115/2016 3/18/2016 3 14 OK
TW4-12 Nitrate/Nitrite (as N) 3115/2016 3/24/2016 9 28 OK
TW4-13 Chloride 3116/2016 3/23/2016 7 28 OK
TW4-13 Carbon tetrachloride 3116/2016 3118/2016 2 14 OK
TW4-13 Chloroform 3116/2016 3118/2016 2 14 OK
TW4-13 Chloromethane 3116/2016 3/18/2016 2 14 OK
TW4-13 Methylene chloride 3116/2016 3118/2016 2 14 OK
TW4-13 Nitrate/Nitrite (as N) 3/16/2016 3/24/2016 8 28 OK
TW4-14 Chloride 3116/2016 3/24/2016 8 28 OK
TW4-14 Carbon tetrachloride 3/16/2016 3118/2016 2 14 OK
TW4-14 Chloroform 3116/2016 3/18/2016 2 14 OK
TW4-14 Chloromethane 3116/2016 3/18/2016 2 14 OK
TW4-14 Methylene chloride 3116/2016 3/18/2016 2 14 OK
TW4-14 Nitrate/Nitrite (as N) 3116/2016 3/24/2016 8 28 OK
MW-26 Chloride 3/9/2016 3116/2016 7 28 OK
MW-26 Carbon tetrachloride 3/9/2016 3114/2016 5 14 OK
MW-26 Chloroform 3/9/2016 3114/2016 5 14 OK
MW-26 Chloromethane 3/9/2016 3114/2016 5 14 OK
MW-26 Methylene chloride 3/9/2016 3114/2016 5 14 OK
MW-26 Nitrate/Nitrite (as N) 3/9/2016 3112/2016 3 28 OK
TW4-16 Chloride 3117/2016 3/25/2016 8 28 OK
TW4-16 Carbon tetrachloride 3/17/2016 3118/2016 1 14 OK
TW4-16 Chloroform 3117/2016 3/18/2016 l 14 OK
TW4-16 Chloromethane 3/17/2016 3118/2016 1 14 OK
TW4-16 Methylene chloride 3117/2016 3/18/2016 1 14 OK
TW4-16 Nitrate/Nitrite (as N) 3117/2016 3/24/2016 7 28 OK
MW-32 Chloride 3/22/2016 3/25/2016 3 28 OK
MW-32 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
MW-32 Chloroform 3/22/2016 3/23/2016 1 14 OK
MW-32 Chloromethane 3/22/2016 3/23/2016 1 14 OK
MW-32 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
MW-32 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
TW4-18 Chloride 3117/2016 3/25/2016 8 28 OK
TW4-18 Carbon tetrachloride 3/17/2016 3118/2016 1 14 OK
TW4-18 Chloroform 3117/2016 3118/2016 1 14 OK
TW4-18 Chloromethane 3117/2016 3/18/2016 1 14 OK
TW4-18 Methylene chloride 3/17/2016 3/18/2016 1 14 OK
TW4-18 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-19 Chloride 3/9/2016 3116/2016 7 28 OK
TW4-19 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-19 Chloroform 3/9/2016 3115/2016 6 14 OK
TW4-19 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-19 Methylene chloride 3/9/2016 3114/2016 5 14 OK
TW4-19 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-20 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-20 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-20 Chloroform 3/9/2016 3/15/2016 6 14 OK
TW4-20 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-20 Methylene chloride 3/9/2016 3114/2016 5 14 OK
TW4-20 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
TW4-21 Chloride 3/9/2016 3116/2016 7 28 OK
TW4-21 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-21 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-21 Chloromethane 3/9/2016 3114/2016 5 14 OK
TW4-21 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-21 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
TW4-22 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-22 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-22 Chloroform 3/9/2016 3/15/2016 6 14 OK
TW4-22 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-22 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-22 Nitrate/Nitrite (as N) 3/9/2016 3/21/2016 12 28 OK
TW4-23 Chloride 3/16/2016 3/24/2016 8 28 OK
TW4-23 Carbon tetrachloride 3/16/2016 3/18/2016 2 14 OK
TW4-23 Chloroform 3/16/2016 3/18/2016 2 14 OK
TW4-23 Chloromethane 3116/2016 3118/2016 2 14 OK
TW4-23 Methylene chloride 3116/2016 3/18/2016 2 14 OK
TW4-23 Nitrate/Nitrite (as N) 3/16/2016 3/24/2016 8 28 OK
TW4-24 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-24 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-24 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-24 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-24 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-24 Nitrate/Nitrite (as N) 3/9/2016 3/23/2016 14 28 OK
TW4-25 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-25 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-25 Chloroform 3/9/2016 3/14/2016 5 14 OK
TW4-25 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-25 Methylene chloride 3/9/2016 3/14/2016 5 14 OK
TW4-25 Nitrate/Nitrite (as N) 3/9/2016 3/12/2016 3 28 OK
TW4-26 Chloride 3/16/2016 3/25/2016 9 28 OK
TW4-26 Carbon tetrachloride 3116/2016 3/18/2016 2 14 OK
TW4-26 Chloroform 3/16/2016 3/18/2016 2 14 OK
TW4-26 Chloromethane 3/16/2016 3118/2016 2 14 OK
TW4-26 Methylene chloride 3/16/2016 3118/2016 2 14 OK
TW4-26 Nitrate/Nitrite (as N) 3/16/2016 3/24/2016 8 28 OK
TW4-27 Chloride 3/16/2016 3/24/2016 8 28 OK
TW4-27 Carbon tetrachloride 3/16/2016 3/18/2016 2 14 OK
TW4-27 Chloroform 3/16/2016 3/18/2016 2 14 OK
TW4-27 Chloromethane 3/16/2016 3/18/2016 2 14 OK
TW4-27 Methylene chloride 3/16/2016 3/18/2016 2 14 OK
TW4-27 Nitrate/Nitrite (as N) 3116/2016 3/24/2016 8 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location 10 Parameter N arne Sample Date Analysis Date (Days) Time (Days) Check
TW4-28 Chloride 3/15/2016 3/23/2016 8 28 OK
TW4-28 Carbon tetrachloride 3115/2016 3/18/2016 3 14 OK
TW4-28 Chloroform 3115/2016 3118/2016 3 14 OK
TW4-28 Chloromethane 3/15/2016 3/18/2016 3 14 OK
TW4-28 Methylene chloride 3115/2016 3/18/2016 3 14 OK
TW4-28 Nitrate/Nitrite (as N) 3115/2016 3/24/2016 9 28 OK
TW4-29 Chloride 3/17/2016 3/23/2016 6 28 OK
TW4-29 Carbon tetrachloride 3/17/2016 3/18/2016 1 14 OK
TW4-29 Chloroform 3/17/2016 3/18/2016 l 14 OK
TW4-29 Chloromethane 3117/2016 3/18/2016 1 14 OK
TW4-29 Methylene chloride 3117/2016 3118/2016 1 14 OK
TW4-29 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-30 Chloride 3/17/2016 3/25/2016 8 28 OK
TW4-30 Carbon tetrachloride 3/17/2016 3/18/2016 I 14 OK
TW4-30 Chloroform 3117/2016 3/18/2016 1 14 OK
TW4-30 Chloromethane 3/17/2016 3/18/2016 1 14 OK
TW4-30 Methylene chloride 3/17/2016 3/18/2016 1 14 OK
TW4-30 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-31 Chloride 3/16/2016 3/24/2016 8 28 OK
TW4-3l Carl;JOn tetrachloride 3116/2016 3/18/2016 2 14 OK
TW4-31 Chloroform 3116/2016 3/18/2016 2 14 OK
TW4-31 Chloromethane 3/16/2016 3/18/2016 2 14 OK
TW4-31 Methylene chloride 3/16/2016 3118/2016 2 14 OK
TW4-31 Nitrate/Nitrite (as N) 3/16/2016 3/24/2016 8 28 OK
TW4-32 Chloride 3115/2016 3/23/2016 8 28 OK
TW4-32 Carbon tetrachloride 3/15/2016 3/18/2016 3 14 OK
TW4-32 Chloroform 3/15/2016 3/18/2016 3 14 OK
TW4-32 Chloromethane 3/15/2016 3118/2016 3 14 OK
TW4-32 Methylene chloride 3/15/2016 3/18/2016 3 14 OK
TW4-32 Nitrate/Nitrite (as N) 3115/2016 3/24/2016 9 28 OK
TW4-33 Chloride 3/17/2016 3/23/2016 6 28 OK
TW4-33 Carbon tetrachloride 3117/2016 3/18/2016 1 14 OK
TW4-33 Chloroform 3/17/2016 3118/2016 1 14 OK
TW4-33 Chloromethane 3/17/2016 3/18/2016 1 14 OK
TW4-33 Methylene chloride 3/17/2016 3/18/2016 1 14 OK
TW4-33 Nitrate/Nitrite (as N) 3/17/2016 3/24/2016 7 28 OK
TW4-34 Chloride 3/16/2016 3/24/2016 8 28 OK
TW4-34 Carbon tetrachloride 3116/2016 3118/2016 2 14 OK
TW4-34 Chloroform 3116/2016 3/18/2016 2 14 OK
TW4-34 Chloromethane 3/16/2016 3/18/2016 2 14 OK
TW4-34 Methylene chloride 3116/2016 3/18/2016 2 14 OK
TW4-34 Nitrate/Nitrite (as N) 3/16/2016 3/24/2016 8 28 OK
TW4-35 Chloride 3116/2016 3/24/2016 8 28 OK
TW4-35 Carbon tetrachloride 3116/2016 3/18/2016 2 14 OK
TW4-35 Chloroform 3/16/2016 3/18/2016 2 14 OK
TW4-35 Chloromethane 3/16/2016 3118/2016 2 14 OK
TW4-35 Methylene chloride 3116/2016 3/18/2016 2 14 OK
TW4-35 Nitrate/Nitrite (as N) 3116/2016 417/2016 22 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
TW4-36 Chloride 3/16/2016 3/23/2016 7 28 OK
TW4-36 Carbon tetrachloride 3/16/2016 3/18/2016 2 14 OK
TW4-36 Chloroform 3/16/2016 3/18/2016 2 14 OK
TW4-36 Chloromethane 3/16/2016 3/18/2016 2 14 OK
TW4-36 Methylene chloride 3/16/2016 3118/2016 2 14 OK
TW4-36 Nitrate/Nitrite (as N) 3/16/2016 417/2016 22 28 OK
TW4-37 Chloride 3/9/2016 3/16/2016 7 28 OK
TW4-37 Carbon tetrachloride 3/9/2016 3/14/2016 5 14 OK
TW4-37 Chloroform 3/9/2016 3115/2016 6 14 OK
TW4-37 Chloromethane 3/9/2016 3/14/2016 5 14 OK
TW4-37 Methylene chloride 3/9/2016 3114/2016 5 14 OK
TW4-37 Nitrate/Nitrite (as N) 3/9/2016 3/23/2016 14 28 OK
TW4-60 Chloride 3/22/2016 3/25/2016 3 28 OK
TW4-60 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
TW4-60 Chloroform 3/22/2016 3/23/2016 1 14 OK
TW4-60 Chloromethane 3/22/2016 3/23/2016 1 14 OK
TW4-60 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
TW4-60 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
TW4-65 Chloride 3115/2016 3/23/2016 8 28 OK
TW4-65 Carbon tetrachloride 3/15/2016 3/18/2016 3 14 OK
TW4-65 Chloroform 3/15/2016 3118/2016 3 14 OK
TW4-65 Chloromethane 3115/2016 3/18/2016 3 14 OK
TW4-65 Methylene chloride 3/15/2016 3/18/2016 3 14 OK
TW4-65 Nitrate/Nitrite (as N) 3115/2016 3/24/2016 9 28 OK
MW-70 Chloride 3/22/2016 3/25/2016 3 28 OK
MW-70 Carbon tetrachloride 3/22/2016 3/23/2016 1 14 OK
MW-70 Chloroform 3/22/2016 3/23/2016 1 14 OK
MW-70 Chloromethane 3/22/2016 3/23/2016 1 14 OK
MW-70 Methylene chloride 3/22/2016 3/23/2016 1 14 OK
MW-70 Nitrate/Nitrite (as N) 3/22/2016 3/24/2016 2 28 OK
Table 1-3 Recipt Temperature"Check
Sample Batch Wells in Batch Temperature
1603259 MW-04, MW-26, TW4-01, TW4-02, TW4-04, TW4-ll, 3.6 "C
TW4-19, TW4-20, TW4-21, TW4-22, TW4-24, TW4-25,
TW4-37, Trip Blank
1603479 MW-32, TW4-06, TW4-06R, TW4-07, TW4-10, TW4-60, 2.8 "C
TW4-70, Trip Blank
1603400 TW4-03, TW4-03R, TW4-05, TW4-08, TW4-09, TW4-12, 0.8 "C
TW4-13, TW4-14, TW4-16, TW4-18, TW4-23, TW4-26,
TW4-27, TW4-28, TW4-29, TW4-30, TW4-31, TW4-32,
TW4-33, TW4-34, TW4-35, TW4-36, TW4-65, Trip Blank
1-4 Analytical Method Check
Parameter Method Method Used by Lab
SW8260B or
Carbon Tetrachloride SW8260C SW8260C
A4500-Cl B or
A4500-Cl E or
Chloride E300.0 E300.0
SW8260B or
Chloroform SW8260C SW8260C
SW8260B or
Chloromethane SW8260C SW8260C
SW8260B or
Methylene chloride SW8260C SW8260C
Nitrogen E353.1 or E353.2 E353.2
All parameters were analyzed using the reporting method specificied in the QAP
-eporung Im!t ec I 5 R L .. Ch k
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
Trip Blank Carbon tetrachloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u I 1 OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 u~ u 1 1 OK
Trip Blank Carbon tetrachloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
Trip Blank Carbon tetrachloride 1 ug/L u 1 1 OK
Trip Blank Chloroform 1 ug/L u 1 1 OK
Trip Blank Chloromethane 1 ug/L u 1 1 OK
Trip Blank Methylene chloride 1 ug/L u 1 1 OK
MW-04 Chloride 10 mg/L 10 1 OK
MW-04 Carbon tetrachloride 1 ug/L u 1 1 OK
MW-04 Chloroform 20 ug/L 20 1 OK
MW-04 Chloromethane I ug/L u 1 1 OK
MW-04 Methylene chloride 1 ug/L u 1 1 OK
MW-04 Nitrate/Nitrite (as N) 0.1 mg/L 10 O.I OK
TW4-01 Chloride 10 mg/L 10 1 OK
TW4-01 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-01 Chloroform 20 ug/L 20 1 OK
TW4-01 Chloromethane 1 ug/L u 1 1 OK
TW4-01 Methylene chloride 1 ug_IL u 1 1 OK
TW4-0I Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-02 Chloride 10 mg/L 10 1 OK
TW4-02 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-02 Chloroform 20 ug/L 20 1 OK
TW4-02 Chloromethane 1 ug/L u 1 1 OK
TW4-02 Methylene chloride 1 ug/L u 1 1 OK
TW4-02 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-03 Chloride 10 mg/L 10 1 OK
TW4-03 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-03 Chloroform 1 ug/L u 1 1 OK
TW4-03 Chloromethane 1 ug/L u 1 1 OK
TW4-03 Methylene chloride 1 ug/L u 1 1 OK
TW4-03 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-03R Chloride 1 mg/L u 1 1 OK
TW4-03R Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-03R Chloroform 1 ug/L u 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 10 mg/L 10 1 OK
TW4-04 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-04 Chloroform 20 ug/L 20 1 OK
TW4-04 Chloromethane 1 ug/L u 1 1 OK
TW4-04 Methylene chloride 1 ug/L u 1 1 OK
TW4-04 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-05 Chloride 10 mg/L 10 1 OK
I 5 R L .. Ch k -eporung I mit ec
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
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 10 0.1 OK
TW4-06 Chloride 10 mg/L 10 1 OK
TW4-06 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-06 Chloroform 10 ug/L 10 I OK
TW4-06 Chloromethane 1 ug/L u 1 1 OK
TW4-06 Methylene chloride 1 ug/L u 1 1 OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-06R Chloride 1 mg/L u 1 1 OK
TW4-06R Carbon tetrachloride 1 ugjL u 1 1 OK
TW4-06R Chloroform 1 ug/L u 1 l OK
TW4-06R Chloromethane 1 ug/L u 1 1 OK
TW4-06R Methylene chloride 1 ug/L u 1 l OK
TW4-06R Nitrate/Nitrite (as N) 0.1 mg/L u 10 0.1 OK
TW4-07 Chloride 10 mg/L 10 1 OK
TW4-07 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-07 Chloroform 10 ug/L 10 1 OK
TW4-07 Chloromethane 1 ug/L u 1 1 OK
TW4-07 Methylene chloride 1 ug/L u 1 1 OK
TW4-07 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-08 Chloride 10 mg/L 10 1 OK
TW4-08 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-08 Chloroform 10 ug!L 10 l OK
TW4-08 Chloromethane 1 ug/L u 1 1 OK
TW4-08 Methylene chloride 1 ug/L u 1 l OK
TW4-08 Nitrate/Nitrite (as N) 0.1 mg/L 5 0.1 OK
TW4-09 Chloride 10 mg/L 10 1 OK
TW4-09 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-09 Chloroform 1 ug/L 1 1 OK
TW4-09 Chloromethane 1 ug/L u 1 l OK
TW4-09 Methylene chloride 1 ug/L u 1 1 OK
TW4-09 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-10 Chloride 10 mg/L 10 1 OK
TW4-10 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-10 Chloroform 20 ug/L 20 1 OK
TW4-10 Chloromethane 1 ug/L u 1 1 OK
TW4-10 Methylene chloride 1 ug/L u 1 1 OK
TW4-10 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-11 Chloride 10 mg/L 10 1 OK
TW4-11 Carbon tetrachloride 1 ug/L 1 1 OK
TW4-11 Chloroform 50 ug!L 50 1 OK
TW4-11 Chloromethane 1 ug/L u 1 1 OK
TW4-11 Methylene chloride 1 ug/L u l l OK
TW4-11 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-12 Chloride 10 mg/L 10 1 OK
TW4-12 Carbon tetrachloride 1 ug/L u 1 1 OK
I 5 R L' . Ch k -eportmg mut ec
Lab Required
Reporting Dilution Reporting
Location Ana1yte Limit Units Qualifier Factor Limit RLCheck
TW4-I2 Chloroform I ug/L u I I OK
TW4-I2 Chloromethane I ug/L u I 1 OK
TW4-I2 Methylene chloride I ug/L u 1 1 OK
TW4-I2 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-I3 Chloride 10 mg/L 10 1 OK
TW4-13 Carbon tetrachloride I ug/L u I 1 OK
TW4-I3 Chloroform I ug/L u I 1 OK
TW4-13 Chloromethane I ug/L u I 1 OK
TW4-I3 Methylene chloride 1 ug/L u 1 1 OK
TW4-I3 Nitrate/Nitrite (as N) 0.1 mg/L IO 0.1 OK
TW4-14 Chloride IO mg/L 10 1 OK
TW4-I4 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-I4 Chloroform I ug/L 1 1 OK
TW4-I4 Chloromethane I ug/L u 1 1 OK
TW4-I4 Methylene chloride I ug/L I 1 OK
TW4-I4 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
MW-26 Chloride 10 mg/L IO I OK
MW-26 Carbon tetrachloride 1 ug/L u 1 I OK
MW-26 Chloroform 20 ug/L 20 1 OK
MW-26 Chloromethane I ug/L u I 1 OK
MW-26 Methylene chloride I ug/L 1 1 OK
MW-26 Nitrate/Nitrite (as N) O.I mg/L 10 O.I OK
TW4-I6 Chloride 10 mg/L 10 1 OK
TW4-I6 Carbon tetrachloride I ug/L u 1 I OK
TW4-16 Chloroform I ug/L 1 1 OK
TW4-I6 Chloromethane I ug/L u 1 I OK
TW4-16 Methylene chloride 1 ug!L u 1 1 OK
TW4-16 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
MW-32 Chloride IO mg/L 10 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 I 1 OK
MW-32 Methylene chloride 1 ug/L u 1 I OK
MW-32 Nitrate/Nitrite (as N) O.I mg/L u IO 0.1 OK
TW4-18 Chloride 10 mg/L IO 1 OK
TW4-18 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-18 Chloroform 1 ug/L 1 1 OK
TW4-I8 Chloromethane I ug/L u I 1 OK
TW4-18 Methylene chloride 1 ug/L u I 1 OK
TW4-18 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-19 Chloride 100 mg/L IOO 1 OK
TW4-I9 Carbon tetrachloride I ug/L I I OK
TW4-I9 Chloroform 50 ug/L 50 I OK
TW4-I9 Chloromethane 1 ug/L 1 I OK
TW4-19 Methylene chloride 1 ug!L u I 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.1 mg/L 10 O.I OK
TW4-20 Chloride 100 mg/L 100 I OK
TW4-20 Carbon tetrachloride I ug/L 1 I OK
TW4-20 Chloroform 100 ug/L 100 I OK
-eporung I mit ec I 5 R L' . Ch k
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-20 Chloromethane 1 ug/L 1 1 OK
TW4-20 Methylene chloride 1 ug!L 1 1 OK
TW4-20 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-21 Chloride 100 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 ugjL u 1 1 OK
TW4-21 Methylene chloride 1 ug!L u 1 1 OK
TW4-21 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-22 Chloride 100 mg!L 100 1 OK
TW4-22 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-22 Chloroform 50 ug!L 50 1 OK
TW4-22 Chloromethane 1 ug!L u 1 1 OK
TW4-22 Methylene chloride 1 ug!L u 1 1 OK
TW4-22 Nitrate/Nitrite (as N) 0.5 mg/L 50 0.1 OK
TW4-23 Chloride 10 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 1 0.1 OK
TW4-24 Chloride 100 mg!L 100 1 OK
TW4-24 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-24 Chloroform 1 ug!L 1 1 OK
TW4-24 Chloromethane 1 ug!L u 1 1 OK
TW4-24 Methylene chloride 1 ug!L u 1 1 OK
TW4-24 Nitrate/Nitrite (as N) 0.2 mg!L 20 0.1 OK
TW4-25 Chloride 10 mg/L 10 1 OK
TW4-25 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-25 Chloroform 1 ug!L u 1 1 OK
TW4-25 Chloromethane 1 ug!L u 1 1 OK
TW4-25 Methylene chloride 1 ug!L u 1 1 OK
TW4-25 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-26 Chloride 10 mg!L 10 1 OK
TW4-26 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-26 Chloroform 1 ug/L 1 1 OK
TW4-26 Chloromethane 1 ug!L u 1 1 OK
TW4-26 Methylene chloride 1 ug!L u 1 1 OK
TW4-26 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-27 Chloride 10 mg!L 10 1 OK
TW4-27 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-27 Chloroform 1 ug!L 1 1 OK
TW4-27 Chloromethane 1 ug!L u 1 1 OK
TW4-27 Methylene chloride 1 ug/L u 1 1 OK
TW4-27 Nitrate/Nitrite (as N) 0.5 mg/L 50 0.1 OK
TW4-28 Chloride 10 mg/L 10 1 OK
TW4-28 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-28 Chloroform 1 ug!L u 1 1 OK
TW4-28 Chloromethane 1 ug!L u 1 1 OK
-eporllng lmlt ec I 5 R L .. Ch k
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-28 Methylene chloride I ug!L u 1 1 OK
TW4-28 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
TW4-29 Chloride 10 mg!L 10 1 OK
TW4-29 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-29 Chloroform 10 ug/L 10 1 OK
TW4-29 Chloromethane 1 ug!L u 1 1 OK
TW4-29 Methylene chloride 1 ug!L u 1 1 OK
TW4-29 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-30 Chloride 10 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 ug!L u 1 1 OK
TW4-30 Methylene chloride 1 ug!L u 1 1 OK
TW4-30 Nitrate/Nitrite (as N) 0.1 mg/L 2 0.1 OK
TW4-31 Chloride 10 mg!L 10 1 OK
TW4-31 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-31 Chloroform 1 ug!L u 1 1 OK
TW4-31 Chloromethane 1 ug!L u 1 1 OK
TW4-31 Methylene chloride 1 ug!L u 1 1 OK
TW4-31 Nitrate/Nitrite (as N) 0.1 mg/L 1 0.1 OK
TW4-32 Chloride 10 mg!L 10 1 OK
TW4-32 Carbon tetrachloride I ug!L u 1 1 OK
TW4-32 Chloroform 1 ug/L u l 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 10 0.1 OK
TW4-33 Chloride 10 mg!L 10 1 OK
TW4-33 Carbon tetrachloride 1 ug/L u l 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) 0.2 mg!L 20 0.1 OK
TW4-34 Chloride 10 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 1 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 10 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 1 ug/L u 1 1 OK
TW4-35 Methylene chloride 1 ug!L u 1 1 OK
TW4-35 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-36 Chloride 10 mg!L 10 1 OK
TW4-36 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-36 Chloroform 1 ug!L u 1 1 OK
TW4-36 Chloromethane 1 ug!L u 1 1 OK
TW4-36 Methylene chloride 1 ug!L u 1 1 OK
-eportmg tmtt ec I 5 R L .. Ch k
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-36 Nitrate/Nitrite (as N) O.I mg!L u IO 0.1 OK
TW4-37 Chloride IOO mg!L 100 I OK
TW4-37 Carbon tetrachloride 1 ug!L I I OK
TW4-37 Chloroform IOO ug!L IOO I OK
TW4-37 Chloromethane 1 ug!L I I OK
TW4-37 Methylene chloride I ug!L 1 I OK
TW4-37 Nitrate/Nitrite (as N) 0.2 mg!L 20 O.I OK
TW4-60 Chloride I mg!L u I I OK
TW4-60 Carbon tetrachloride I ug/L u 1 1 OK
TW4-60 Chloroform I ug!L u I 1 OK
TW4-60 Chloromethane I ug!L u I I OK
TW4-60 Methylene chloride 1 ug!L u I 1 OK
TW4-60 Nitrate/Nitrite (as N) O.I mg!L u 10 0.1 OK
TW4-65 Chloride 10 mg!L 10 I OK
TW4-65 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-65 Chloroform 1 ug!L u 1 1 OK
TW4-65 Chloromethane 1 ug!L u 1 I OK
TW4-65 Methylene chloride 1 ug!L u I 1 OK
TW4-65 Nitrate/Nitrite (as N) 0.2 mg!L 20 O.I OK
MW-70 Chloride 10 mg/L 10 I OK
MW-70 Carbon tetrachloride 1 ug!L u I I OK
MW-70 Chloroform 1 ug!L u 1 1 OK
MW-70 Chloromethane I ug!L u I I OK
MW-70 Methylene chloride I ug!L u I I OK
MW-70 Nitrate/Nitrite (as N) 0.1 mg!L IO O.I OK
1-6 Trip Blank Evaluation
Lab Report Constituent Result
1603259 Carbon tetrachloride ND ug/L
Chloroform ND ug!L
Chloromethane ND ug!L
Methylene chloride ND ug/L
1603400 Carbon tetrachloride ND ug/L
Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
1603479 Carbon tetrachloride ND ug/L
Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug/L
1-7 QA/QC Evaluation for Sample Duplicates
Coll,9tituea,t
Chloride (mg/L)
Nitrate +Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
C~>nstituent
Chloride (mg/L)
Nitrate+ Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
RPD = Relative Percent Difference
ND = The analyte was not detected
TW4-2&
61.6
34.0
ND
ND
ND
ND
MW-32
36.7
ND
ND
ND
ND
ND
TW4-6S .$1oRPD
61.4 0.3
32.6 4.2
ND NC
ND NC
ND NC
ND NC
TW4•70 %1WD
36.4 0.8
0.119 NC
ND NC
ND NC
ND NC
ND NC
I-8 QC Control Limits for Analysis and Blanks
Method Blank Detections
All Method Blanks for the quarter were non-detect.
Matrix Spike % Recovery Comparison
MSD -.me
LabR~rt Lab Sample ID wen A~!te MS%REC %RE;C Range RPb
1603400 1603400-007BMS TW4-36 Nitrate 112 111 90-110 0.72
1603400 1603400-021BMS TW4-29 Nitrate 115 111 90-110 2.86
1603400 16034 79-001 BMS TW4-06R Nitrate 115 115 90-110 0.261
1603259 1603259-00lBMS TW4-25 Nitrate 119 105 90-110 11.50
1603259 1603290-001CMS N/A Nitrate 141 128 90-110 8.83
1603259 1603259-002BMS TW4-24 Nitrate 89.2 88.1 90-110 0.735
N/ A: QC was not performed on an EFRI sample.
Laboratory Control Sample
All Laboratory Control Samples were within acceptance limits for the quarter.
Surrogate % Recovery
All Surrogate recoveries were within acceptance limits for the quarter.
I-9 Rinsate Evaluation
All rinsate blanks results were nondetect for the
quarter.
TabJ
Kriged Current Quarter Chloroform Isoconcentration Map
NS = not sampled; NO = not detected
....._70
MW-32
e ND
TW4-7
0 834
TWN-1
¢Ns
PIEZ-1
Q NS
kriged chloroform isocon and label
perched monitoring well showing
concentration in llQ/L
temporary perched monitoring well
showing concentration in 1Jg/L
temporary perched nitrate monitoring
well (not sampled)
perched piezometer (not sampled)
NOTE: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11,TW4-19, TW4-20, TW4-21, and TW4-37 are chloroform pumping wells; TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
HYDRO
GEO
CHEM,INC.
KRIGED 1st QUARTER, 2016 CHLOROFORM (IJg/L)
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/May16/chloroform/Uchl0316.srf J-1
NS = not sampled; ND = not detected
--70 kriged chloroform isocon and label
MW-32
e ND
TW4·7
0 834
PIEZ·2
(0) NS
perched monitoring well showing
concentration (~giL)
temporary perched monitoring well
showing concentration (~giL)
perched piezometer showing
concentration (~giL)
•
TW4-25 ·~~
I •-;.
NOTE: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11 , TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
HYDRO
GEO
CHEM,INC.
KRIGED 1st QUARTER, 2016 CHLOROFORM (llQL)
WHITE MESA SITE
APPROVED DATE
(detail map)
REFERENCE H:/718000/
May16/chloroform/Uchl0316det.srf
FIGURE
J-2
NS =not sampled; NO= not detected
-.._ 70 kriged chloroform isocon and label
MW-32
e ND
TW4·7
0 834
PIEZ-2
101 NS
perched monitoring well showing
concentration (~g/L)
temporary perched monitoring well
showing concentration (~giL)
perched piezometer showing
concentration (~g/L)
NOTE: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells;
TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
HYDRO
GEO
CHEM,INC.
APPROVED
1st QUARTER, 2016 CHLOROFORM
GREATER THAN OR EQUAL TO 70 IJQL GRID
WHITE MESA SITE
DATE REFERENCE H:/718000/
May16/chloroform/Uchl0316ge70.srf
FIGURE
J-3
TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs Over Time
CbJorafeJW ·CaPbsn Chierometlli e ~ Rtr, Cld ide MW-4 Ten-eblo · e ~ ) (,wtn ~g4~ ( {~ {mgn) {mwt)
28-Sep-99 6200
28-Sep-99 5820
28-Sep-99 6020
15-Mar-00 5520
15-Mar-00 5430
2-Sep-00 5420 9.63
30-Nov-00 6470 9.37
29-Mar-01 4360 8.77
22-Jun-01 6300 9.02
20-Sep-01 5300 9.45
8-Nov-01 5200 8
26-Mar-02 4700 8.19
22-May-02 4300 8.21
12-Sep-02 6000 8.45
24-Nov-02 2500 8.1
28-Mar-03 2000 8.3
30-Apr-03 3300 NA
30-May-03 3400 8.2
23-Jun-03 4300 8.2
30-Jul-03 3600 8.1
29-Aug-03 4100 8.4
12-Sep-03 3500 8.5
15-0ct-03 3800 8.1
8-Nov-03 3800 8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 3300 6.71
17-Nov-04 4300 7.5
16-Mar-05 2900 6.3
25-May-05 3170 NA NA NA 7.1 NA
31-Aug-05 3500 <10 <10 <10 7.0 NA
1-Dec-05 3000 <50 <50 <50 7.0 NA
9-Mar-06 3100 <50 <50 50 6 49
14-Jun-06 3000 <50 <50 50 6 49
20-Jul-06 2820 <50 <50 <50 1.2 48
9-Nov-06 2830 2.1 1.4 <1 6.4 50
28-Feb-07 2300 1.6 <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 <1 6.36 35
15-0ct-08 2100 1.7 <1 <1 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
14-Dec-09 1800 1.6 ND ND 5.8 44
Chloroform Carbon Chloromethane Methylene Nitrate Chloride MW-4 Tetrachloride (ug/1) (uflll.) (ugl)) Chloride (ugll) (mgll~ (mg/1)
17-Feb-10 1600 1.2 ND ND 4 45
14-Jun-10 2100 1.2 ND ND 5.1 41
16-Aug-10 1900 1.5 ND ND 4.8 38
11-0ct-10 1500 1.4 ND ND 4.9 41
23-Feb-11 1700 1.5 ND ND 4.6 40
1-Jun-11 1700 1.4 ND ND 4.9 35
17-Aug-11 1700 1.1 ND ND 4.9 41
16-Nov-11 1600 1.3 ND ND 5.1 40
23-Jan-12 1500 1 ND ND 4.8 41
6-Jun-12 1400 1.2 ND ND 4.9 39
4-Sep-12 1500 1.5 ND ND 5 41
4-0ct-12 1300 1 ND ND 4.8 42
11-Feb-13 1670 1.49 ND ND 4.78 37.8
5-Jun-13 1490 1.31 ND ND 4.22 44
3-Sep-13 1520 1.13 ND ND 4.89 41.4
29-0ct-13 1410 5.58 ND ND 5.25 40.1
27-Jan-14 1390 4.15 ND ND 4.7 38.5
19-May-14 1390 5.21 ND ND 4.08 39.9
24-Aug-14 1490 ND 7.6 ND 3.7 41
21-0ct-14 1440 ND ND ND 5.07 41.5
9-Mar-15 1400 1.26 ND ND 5.75 40.7
8-Jun-15 1300 ND ND ND 2.53 43.1
31-Aug-15 1290 ND ND ND 4.79 44.3
19-0ct-15 1200 ND ND ND 4.43 40.8
9-Mar-16 1240 ND ND ND 5.15 42.2
0
0 0 0
1\)
0 0 0
(ug/L)
w 0 0 0
.j:>.
0 0 0
Sep-99 •
Dec-99
Mar-00
Jun-00
Sep-00
Dec-00
Mar-01 -
Jun-01
Sep-01
Dec-01
Mar-02
Jun-02
Sep-02
Dec-02
Mar-03
Jun-03
Sep-03 r;~~~f i--+~--+~--11-. -z7l_
01 0 0 0
m 0 0 0
......,
0 0 0
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 ~~--~----~----~----L-----~----~--~
s:: :E ~ I ()
'=:!'
0 a -0 ..... 3
~ c
CD en
Chlorofonn Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ug/1) (ug/1)
28-Jun-99 1700 7.2
JO-Nov-99 5.8
15-Mar-00 1100
10-Apr-00 1490
6-Jun-00 1530
2-Sep-00 2320 5.58
30-Nov-00 3440 7.79
29-Mar-01 2340 7.15
22-Jun-01 6000 8.81
20-Sep-01 12.8
8-Nov-01 3200 12.4
26-Mar-02 3200 13.1
22-May-02 2800 12.7
12-Sep-02 3300 12.8
24-Nov-02 3500 13.6
28-Mar-03 3000 12.4
23-Jun-03 3600 12.5
12-Sep-03 2700 12.5
8-Nov-03 3400 11.8
29-Mar-04 3200 11
22-Jun-04 3100 8.78
17-Sep-04 2800 10.8
17-Nov-04 3000 11.1
16-Mar-05 2700 9.1
25-May-05 3080 NA NA NA 10.6 NA
31-Aug-05 2900 <10 <10 <10 9.8 NA
1-Dec-05 2400 <50 <50 <50 9.7 NA
9-Mar-06 2700 <50 <50 <50 9.4 49
14-Jun-06 2200 <50 <50 <50 9.8 48
20-Jul-06 2840 <50 <50 <50 9.7 51
8-Nov-06 2260 1.4 <1 <1 9.4 47
28-Feb-07 1900 1.2 <1 <1 8.9 47
27-Jun-07 1900 1.4 <1 <1 9 45
15-Aug-07 2300 1.3 <1 <1 8.4 43
10-0ct-07 2000 1.3 <1 <l 7.8 43
26-Mar-08 2000 1.3 <1 <1 7.6 39
25-Jun-08 1900 1.1 <1 <1 8.68 39
10-Sep-08 1700 1.3 <1 <1 8.15 35
15-0ct-08 1700 1.3 <1 <1 9.3 41
11-Mar-09 1700 1.1 <1 <1 7.5 37
24-Jun-09 1500 1 <1 <1 6.9 37
15-Sep-09 1700 <1 <1 <1 7.3 36
CltlO'refGFm Carbon C:Mwemeth Methylene Nitrate Chloride T 4-1 T~>tmebfuri e e Clllor· c (ugtl) (ugl) (ugll) (u.gtt) (mg/1~ (~)
29-Dec-09 1400 <1 <1 <1 6.8 41
3-Mar-10 1300 <1 <1 <1 7.1 35
15-Jun-10 1600 1.2 <1 <1 6.8 40
24-Aug-10 1500 <1 <1 <1 6.8 35
14-0ct-10 1500 <1 <1 <1 6.6 40
24-Feb-11 1300 ND ND ND 6.6 41
1-Jun-11 1200 ND ND ND 7 35
18-Aug-11 1300 ND ND ND 6.8 36
29-Nov-11 1300 ND ND ND 6.6 37
19-Jan-12 1300 ND ND ND 6.8 38
14-Jun-12 1000 ND ND ND 7.1 42
13-Sep-12 1000 ND ND ND 5 39
4-0ct-12 1100 ND ND ND 6.5 40
13-Feb-13 1320 3.66 ND ND 6.99 37.6
19-Jun-13 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
en CD :l
C'G >
E ...
0 -0 ...
.2 .c:
0 .,..
I ~ 1-
r------.------r----.-----,----,-----,----..-L ~-das-cc
-v~-oaa-a
6o-1nr-g
90-PO·O~
vo-uer-v~
1-------+------1---+-----+---+----+----+ 86-lnr-vc
0 0 0 t--
0 0 0 <0
0 0 0 I{)
0 0 ~
0 0 0 (")
0 0 0 C\1
0 0 0 ..-
0
Chlotoform Carbea CllkJ~methane Methyleae Nitr te Ollttritk 4-Z Tetra kn"M ~ride (ug/11} (tmn} (Ugat) (q1!fl(} (mgll} ~)
10-Nov-99 2510
2-Sep-00 5220
28-Nov-00 4220 10.7
29-Mar-01 3890 10.2
22-Jun-01 5500 9.67
20-Sep-01 4900 11.4
8-Nov-01 5300 10.1
26-Mar-02 5100 9.98
23-May-02 4700 9.78
12-Sep-02 6000 9.44
24-Nov-02 5400 10.4
28-Mar-03 4700 9.5
23-Jun-03 5100 9.6
12-Sep-03 3200 8.6
8-Nov-03 4700 9.7
29-Mar-04 4200 9.14
22-Jun-04 4300 8.22
17-Sep-04 4100 8.4
17-Nov-04 4500 8.6
16-Mar-05 3700 7.7
25-May-05 3750 8.6
31-Aug-05 3900 <10 <10 <10 8 NA
1-Dec-05 3500 <50 <50 <50 7.8 NA
9-Mar-06 3800 <50 <50 <50 7.5 56
14-Jun-06 3200 <50 <50 <50 7.1 56
20-Jul-06 4120 <50 <50 <50 7.4 54
8-Nov-06 3420 2.3 <1 <1 7.6 55
28-Feb-07 2900 1.8 <1 <1 7.3 54
27-Jun-07 3000 2.5 <1 <1 7.8 50
15-Aug-07 340 2.2 <1 <1 7.3 49
10-0ct-07 3200 2.1 <1 <1 6.9 51
26-Mar-08 3300 2.3 <1 <1 6.9 48
25-Jun-08 3100 2.2 <1 <1 7.44 46
10-Sep-08 2800 2.4 <1 <1 7.1 42
15-0ct-08 3200 2.4 <2 <2 7.99 47
11-Mar-09 3100 2.2 <1 <1 6.5 46
24-Jun-09 2800 2 <1 <1 6.4 44
15-Sep-09 3000 2 <1 <1 6.6 43
29-Dec-09 1600 2 <1 <1 6.4 46
3-Mar-10 2600 2 <1 <1 6.8 42
15-Jun-10 3300 2.6 <1 <1 6.7 43
16-Aug-10 3300 2.5 <1 <1 6.6 43
14-0ct-10 3000 2.1 <1 <1 6.5 41
ehloroform Carbon Vhlorometbane Melhylene Nitrate Chlollide TW4·2 (ugll) Tetrachlodde (ug/1) Chloride (mg/1) (mg/1) (u211) (u211)
24-Feb-11 3100 2.4 ND ND 7 46
2-Jun-11 3000 2.2 ND ND 6.8 42
17-Aug-11 2400 1.6 ND ND 6 48
29-Nov-11 3900 2.8 ND ND 7 49
24-Jan-12 2500 2 ND ND 7.1 49
14-Jun-12 2500 2.1 ND ND 7.7 52
13-Sep-12 2900 1.8 ND ND 4 76
4-0ct-12 3100 2 ND ND 7.6 49
13-Feb-13 3580 5.17 ND ND 8.1 46
19-Jun-13 3110 2.65 ND ND 7.51 46.9
12-Sep-13 3480 2.41 ND ND 9.3 44.9
14-Nov-13 3740 3.15 ND ND 8.39 43.9
6-Feb-14 3180 7.1 ND ND 7.87 45.9
23-May-14 2930 6.05 ND ND 9.11 45.4
27-Aug-14 3170 1.4 3.6 ND 6.2 45
30-0ct-14 3580 2.6 ND ND 8.45 45.5
9-Mar-15 1840 1.44 ND ND 5.32 44.9
8-Jun-15 1650 ND ND ND 4.3 48.1
31-Aug-15 1310 ND ND ND 3.76 50.0
19-0ct-15 2070 ND ND ND 5.18 41.9
9-Mar-16 1970 1.20 ND ND 5.30 43.4
TW4-2 Chloroform Values
7000 ~-------------------------------------------------------------------------------------,
6000 +------------------.------------------------------------------------------------------~
sooo r---~--~-~~~~~----------------------------------------------------__J
4000 -·~----~~-~~--------~~~~~--~----------------------~------------------------4
-..J a,
:::J
-3000 '!\I ' • ~I I T .... V \ I
2000 +----------------------------------------+~--------H---------------------~r-~-------4
Data point represented corresponds
to laboratory results. The value is
1000 -t------llikely underestimated due to
laboratory error not considering the
dilution factor of 1 0.
o +-----~~========~====~--~--------~------~--------~------~
OJ q>
"3 "'"') ct
,....
0 ~ a. <{ I Ol
"<!" 0 c co
"'"') I "<!" ,...
<.0 9 t5 0 6
Ol 0 I "3 "'"')
I <.0
C\1 "<!" ..... ,... ,... ,....
I I 6.. ._ (.) a. Q) Q) <{ 0 (/) I I c\J ..... C\1 C\1
Chlorofonn Carbon Chloromethane Methylene Nitrate Chloride TW4-3 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (oWl) (oWl)
28-Jun-99 3500 7.6
29-Nov-99 102
15-Mar-00 834
2-Sep-00 836 1.56
29-Nov-00 836 1.97
27-Mar-01 347 1.85
21-Jun-01 390 2.61
20-Sep-01 300 3.06
7-Nov-01 170 3.6
26-Mar-02 11 3.87
21-May-02 204 4.34
12-Sep-02 203 4.32
24-Nov-02 102 4.9
28-Mar-03 0 4.6
23-Jun-03 0 4.8
12-Sep-03 0 4.3
8-Nov-03 0 4.8
29-Mar-04 0 4.48
22-Jun-04 0 3.68
17-Sep-04 0 3.88
17-Nov-04 0 4.1
16-Mar-05 0 3.5
25-May-05 <1 NA NA NA 3.7 NA
31-Aug-05 <1 <1 6.4 <1 3.5 NA
1-Dec-05 <1 <1 2.3 <1 3.3 NA
9-Mar-06 <1 <1 2.2 <1 3.3 26
14-Jun-06 <1 <1 <1 <1 3.2 26
20-Jul-06 <1 <1 1.6 <1 2.9 26
8-Nov-06 <1 <1 <1 <1 1.5 23
28-Feb-07 <1 <1 <1 <1 3.1 22
27-Jun-07 <1 <1 <1 <1 3.3 23
15-Aug-07 <1 <1 <1 <1 3.1 24
10-0ct-07 <1 <1 <1 <1 2.8 27
26-Mar-08 <1 <1 <1 <1 2.8 21
25-Jun-08 <1 <1 <1 <1 2.85 19
10-Sep-08 <1 <1 <1 <1 2.66 19
15-0ct-08 <1 <1 <1 <1 2.63 22
4-Mar-09 <1 <1 <1 <1 2.5 21
24-Jun-09 <1 <1 <1 <1 2.9 20
15-Sep-09 <1 <1 <1 <1 2.8 21
16-Dec-09 <1 <1 <1 <1 2.5 22
23-Feb-10 <1 <1 <1 <1 2.8 23
8-Jun-10 <1 <1 <1 <1 3 24
Chloroform Carbo Cltlo'Nlll1 Methyl e Mate CJd . e TW4-3 '£etracldemle · nc (), Me (uf!/<~) .tum'D (ugA') !uelll (mgll) ~mgiJ
10-Aug-10 <1 <1 <1 <1 3.1 22
5-0ct-10 <1 <1 <1 <1 3.3 26
15-Feb-11 ND ND ND ND 3.5 23
25-May-11 ND ND ND ND 3.7 23
16-Aug-11 ND ND ND ND 4 23
15-Nov-11 NO ND ND ND 4.4 23
17-Jan-12 ND ND ND ND 4.3 21
31-May-12 ND ND ND ND 4.4 24
29-Aug-12 ND ND ND ND 4.9 25
3-0ct-12 ND ND ND ND 4.8 25
7-Feb-13 ND ND ND ND 5.05 23.7
29-May-13 ND ND ND ND 5.83 23.8
29-Aug-13 ND ND ND ND 6.26 24.0
6-Nov-13 ND ND ND ND 5.89 24.1
22-Jan-14 ND ND ND ND 6.66 24.9
19-May-14 ND ND ND ND 6.01 24.4
13-Aug-14 ND ND ND ND 5.3 26
23-0ct-14 ND ND ND ND 6.07 26.7
11-Mar-15 ND ND ND ND 6.64 26.2
10-Jun-15 ND ND ND ND 5.71 27.5
2-Sep-15 ND ND ND ND 3.88 27.4
21-0ct-15 ND ND ND ND 5.37 25.6
15-Mar-16 ND ND ND ND 5.83 32.8
Jun-99
Nov-99
Apr-00
Sep-00
Feb-01
Jul-01
Dec-01
May-02
Oct-02
Mar-03
Aug-03
Jan-04
Jun-04
Nov-04
Apr-05
Sep-05
Feb-06
Jul-06
Dec-06
May-07
Oct-07
Mar-08
Aug-08
Jan-09
Jun-09
Nov-09
Apr-10
Sep-10
Feb-11
Jul-11
Dec-11
May-12
Oct-12
Mar-13
Aug-13
Jan-14
Jun-14
Nov-14
Apr-15
Sep-15
Feb-16
01 0 0 0 0 0
(ug/L)
1\) 1\)
0 01 0 01 0 0 0 0 0 0 0 0 0 0 0 0
VJ 0 0 0
0
a..
t1) ,....
t1) n ,.... -· 0 :::J --· 3 -· ,....
Cl'l -· :::J n t1)
s
Q,J
'"'I n ::r
N 0
0 w
VJ """' 01 0 0 0 0 0
0 0
i I w
0 ::::r
0 ..,
0 0 ..,
3
< !!. c
(I)
(/)
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-4 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ue/1) (ue/1)
6-Jun-00 0
2-Sep-00 0
28-Nov-00 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 <1 10.1 49
28-Feb-07 2200 1.5 <1 <1 9 49
27-Jun-07 2400 1.7 <1 <1 9.4 47
15-Aug-07 2700 1.5 <1 <1 9.5 45
10-0ct-07 2500 1.5 <1 <1 9.5 47
26-Mar-08 2800 1.6 <1 <1 9.2 43
25-Jun-08 2500 1.5 <1 <1 10.8 42
10-Sep-08 2200 1.4 <1 <1 8.83 39
15-0ct-08 2500 2 <2 <2 10.1 44
4-Mar-09 2200 1.2 <1 <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
17-Feb-10 1700 I <1 <1 6.6 48
10-Jun-10 2000 1.2 <1 <1 7.6 35
16-Aug-10 2100 1.3 <1 <1 7.3 36
11-0ct-10 1700 1.3 <1 <1 7.1 38
Oliie ufo_rm Carbon Chloromethane 1\tethylene Nitrate Chlqride Tw-4 .. 4 Tetrachloride Oldo:ride GugA) (nell) (ug/1) (-u"') (mgll) ~mg/1)
23-Feb-11 1800 1.4 ND ND 7 41
1-Jun-11 1700 1.2 ND ND 7 35
17-Aug-11 1500 ND ND ND 6.6 40
16-Nov-11 1500 1 ND ND 7 39
23-Jan-12 1200 ND ND ND 7.1 38
6-Jun-12 1500 ND ND ND 7.1 43
4-Sep-12 1600 1.2 ND ND 7.1 39
3-0ct-12 1400 1 ND ND 7 38
11-Feb-13 1460 1.12 ND ND 7.36 39
5-Jun-13 1330 ND ND ND 6.3 39.6
3-Sep-13 1380 ND ND ND 7.22 38.8
29-0ct-13 1360 5.3 ND ND 7.84 43.9
27-Jan-14 1260 3.88 ND ND 7.28 37.4
19-May-14 1220 5 ND ND 5.91 47.5
11-Aug-14 1320 ND 7 ND 5.30 40.0
21-0ct-14 1130 ND ND ND 7.02 40.0
9-Mar-15 1350 1 ND ND 7.70 37.6
8-Jun-15 1280 ND ND ND 6.33 41.3
31-Aug-15 1220 ND ND ND 6.45 45.8
19-0ct-15 1190 ND ND ND 6.27 38.5
9-Mar-16 1190 ND ND ND 6.71 39.7
t/)
G)
~ "i >
E ...
0 -0 ...
..2 .c
0
~ I ~ 3: 1-
r-----.-----.----,----r---r------.-----.---,----.-L ~ -das-~~
t>~-oaa-a
60-lnr-g
-90-lOQ-O~
t>o-uer-t> ~
lr-t~~t--+--~~--J __ J-~O-JdV-6 ~
1----+---+---r---+---t----+---+----+---+ B6-1nr-t>~
0 0 I!) '¢
0 0 0 '¢
0 0 I!)
C')
0 0 0 C')
0 0 I!)
C\1
0 0 0 C\1
(1J6n)
0 0 I!)
0 0 0
0 0 I!)
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-5 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ue/1) (ue/1)
20-Dec-99 29 .5
15-Mar-00 49.0
2-Sep-00 124
29-Nov-00 255
28-Mar-01 236
20-Jun-01 240
20-Sep-01 240
7-Nov-01 260
26-Mar-02 260
22-May-02 300
12-Sep-02 330
24-Nov-02 260
28-Mar-03 240
23-Jun-03 290
12-Sep-03 200
8-Nov-03 240
29-Mar-04 210
22-Jun-04 200
17-Sep-04 150
17-Nov-04 180
16-Mar-05 120
25-May-05 113 NA NA NA 3.7 NA
31-Aug-05 82.0 <2.5 5.8 <2.5 6 NA
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 <1 <1 <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 <1 8.2 39
26-Mar-08 11.0 <1 <1 <1 7.4 36
25-Jun-08 9.3 <1 <1 <1 8.7 37
10-Sep-08 11.0 <1 <1 <1 7.91 34
15-0ct-08 10.0 <1 <1 <1 9.3 37
4-Mar-09 12.0 <1 <1 <1 7.9 34
24-Jun-09 13.0 <1 <1 <1 7.5 37
15-Sep-09 12.0 <1 <1 <1 8.3 48
22-Dec-09 8.5 <1 <1 <1 7.5 41
25-Feb-10 13.0 <1 <1 <1 6.8 43
9-Jun-10 12.0 <1 <1 <I 7.1 28
11-Aug-10 12.0 <1 <1 <1 7 38
ChmrllfmD CarhOD Oloreme Methylene Nitrate Chl:eride TW4·5 Tetr eWoride Chloride ~ugll) (ueB\ (ug4) Cul!fl) (mg/1) (mgf.f:)
13-0ct-10 11.0 <1 <1 <1 7.2 41
22-Feb-11 10.0 ND ND ND 7 34
26-May-11 9.0 ND ND ND 7.2 35
17-Aug-11 10.0 ND ND ND 7.5 37
7-Dec-11 7.9 ND ND ND 6 30
18-Jan-12 7.6 ND ND ND 5.8 22
6-Jun-12 8.4 ND ND ND 8 39
11-Sep-12 12.0 ND ND ND 8.1 37
3-0ct-12 8.0 ND ND ND 7.7 38
13-Feb-13 10.8 ND ND ND 8.24 34.3
13-Jun-13 11.2 ND ND ND 10.7 36.5
5-Sep-13 11.6 ND ND ND 7.79 39.1
13-Nov-13 14.4 ND ND ND 7.75 41.1
30-Jan-14 12.5 ND ND ND 9.16 40.5
22-May-14 13.4 ND ND ND 7.78 51.4
14-Aug-14 12.0 ND ND ND 7.2 44
28-0ct-14 14.6 ND ND ND 8.31 45.1
12-Mar-15 13.8 ND ND ND 9.32 45.1
10-Jun-15 13.3 ND 1.07 ND 7.08 47.3
3-Sep-15 12.9 ND ND ND 8.1 52.2
28-0ct-15 11.0 ND ND ND 8.03 43.6
17-Mar-16 11.0 ND ND ND 10.2 44.7
0 Cl)
~ "i >
E ...
0 -0 ...
..2 .c 0
It) I
'111:1' 3: t-
0 1.{)
(')
0 0 (')
0 1.{)
C\1
0 0 C\1
0 1.{) ,....
(1J6n)
0 0 ,.... 0 1.{)
5o-1nr-9
90-PO-O~
vo-uer-v~
~O-JdV-6~
0
Chl'cw Cmibe UJ:cw&JDetha· • M.e1hyleae ...... ,. ~ Vhloldlhl TW4.-6 ll'm 'JiletJmdt Ol!'J:tl Cblorid (~ ~uutm ~~ .~g/1) ( ~)
6-Jun-00 0
2-Sep-00 0
28-Nov-00 0 ND
26-Mar-01 0 0.13
20-Jun-01 0 ND
20-Sep-01 4 ND
7-Nov-01 1 ND
26-Mar-02 0 ND
21-May-02 0 ND
12-Sep-02 0 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 0 ND
12-Sep-03 0 ND
8-Nov-03 0 ND
29-Mar-04 0 ND
22-Jun-04 0 ND
17-Sep-04 0 ND
17-Nov-04 0 ND
16-Mar-05 0 0.2
25-May-05 2.5 NA NA NA 0.4 NA
31-Aug-05 10.0 <1 2.8 <1 0.8 NA
1-Dec-05 17.0 <1 1.3 <1 0.9 NA
9-Mar-06 31.0 <1 <1 <1 1.2 31
14-Jun-06 19.0 <1 <1 <1 1 30
20-Jul-06 11.0 <1 <1 <1 0.6 37
8-Nov-06 42.8 <1 <1 <1 1.4 65
28-Feb-07 46.0 <1 <1 <1 1.5 32
27-Jun-07 11.0 <1 <1 <1 0.6 38
15-Aug-07 18.0 <1 <1 <1 0.7 36
10-0ct-07 18.0 <1 <1 <1 0.8 38
26-Mar-08 52.0 <1 <1 <1 1.1 33
25-Jun-08 24.0 <1 <1 <1 0.9 35
10-Sep-08 39.0 <1 <1 <1 1.14 35
15-0ct-08 37.0 <1 <1 <1 1.01 33
11-Mar-09 81.0 <1 <1 <1 2.2 35
24-Jun-09 120 <1 <1 <1 2.7 37
15-Sep-09 280 <1 <1 <1 5.0 37
22-Dec-09 250 <1 <1 <1 6.1 41
25-Feb-10 1000 <1 <1 <1 1.6 45
10-Jun-10 590 <1 <1 <1 2.5 33
12-Aug-10 630 <1 <1 <1 3.9 31
13-0ct-10 420 <1 <1 <1 4.3 41
23-Feb-11 47 ND ND ND 0.7 40
26-May-11 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
Chloroform Catrbtm Chhwomeltane M;etllflene Nitrate Chloride TW4·6 'fetcacld.'Qr,ide Chloritle (u~ (uttllj (u~ i.wtl (mgll) (mgt!}
18-Jan-12 38 ND ND ND 0.7 38
13-Jun-12 4.7 ND ND ND 0.2 40
11-Sep-12 6.9 ND ND ND 0.1 21
3-0ct-12 9.0 ND ND ND 0.2 41
13-Feb-13 6.9 ND ND ND 0.154 40.4
13-Jun-13 4.9 ND ND ND 0.155 37.9
5-Sep-13 5.9 ND ND ND 0.157 40.6
13-Nov-13 5.5 ND ND ND 1.52 40.2
29-Jan-14 5.7 ND ND ND 0.184 40.6
22-May-14 10.3 ND ND ND 0.312 37
14-Aug-14 202.0 ND ND ND 4.2 40
24-Sep-14 260.0 ND ND ND N/A N/A
29-0ct-14 723.0 ND ND ND 6.92 41.1
18-Mar-15 1180.0 ND ND ND 5.25 41.2
11-Jun-15 1040.0 ND ND ND 5.87 41.6
10-Sep-15 1040.0 ND ND ND 6.75 47.0
29-0ct-15 843.0 ND ND ND 5.61 40.2
22-Mar-16 834.0 ND ND ND 6.79 42.0
t/)
Cl)
::::J
ca >
E ... 0 -0 ... .2 .c 0
CD I -.::1' 3: 1-
..------r----,------,-----.--------r---..,..----..-L ~/ll/60
v~!Llll~
l~HO/vO
60/90/LO
90/0~/0~
voJv~J~o
, ~OJ6~Jvo
1-----t----+----+----t-----+---+-----+ 86/vl/LO
0 0 -.:!"
0 0 C\J
0 0 0
0 0 CXl
0 0 <0
(1J6n)
0 0 -.:!"
0 0 C\J
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-7 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) huz/1) (ul!ll)
29-Nov-99 256
15-Mar-00 616
2-Sep-00 698
29-Nov-00 684 1.99
28-Mar-01 747 2.46
20-Jun-01 1100 2.65
20-Sep-01 1200 3.38
8-Nov-01 1100 2.5
26-Mar-02 1500 3.76
23-May-02 1600 3.89
12-Sep-02 1500 3.18
24-Nov-02 2300 4.6
28-Mar-03 1800 4.8
23-Jun-03 5200 7.6
12-Sep-03 3600 7.6
8-Nov-03 4500 7.1
29-Mar-04 2500 4.63
22-Jun-04 2900 4.83
17-Sep-04 3100 5.59
17-Nov-04 3800 6
16-Mar-05 3100 5.2
25-May-05 2700 NA NA NA 5.4 NA
31-Aug-05 3100 <10 <10 <10 5.2 NA
1-Dec-05 2500 <50 <50 <50 5.3 NA
9-Mar-06 1900 <50 <50 <50 1 48
14-Jun-06 2200 <50 <50 <50 4.5 47
20-Jul-06 2140 <50 <50 <50 4.7 51
8-Nov-06 2160 1.5 <1 <1 4.6 49
28-Feb-07 1800 1.1 <1 <1 5 47
27-Jun-07 2600 1.5 <1 <1 5.1 45
14-Aug-07 2300 1.4 <1 <1 4.7 44
10-0ct-07 1900 1.2 <1 <1 4.7 45
26-Mar-08 2200 1.3 <1 <1 4.2 43
25-Jun-08 1800 1.3 <1 <1 4.8 43
10-Sep-08 1600 1.4 <1 <1 4.16 35
15-0ct-08 1900 <2 <2 <2 4.01 40
11-Mar-09 1800 1.2 <1 <1 3.1 35
24-Jun-09 1400 <1 <1 <1 3.8 37
15-Sep-09 1500 1.0 <1 <1 4.1 37
29-Dec-09 1300 <1 <1 <1 4.2 37
3-Mar-10 1200 <1 <1 <1 3.8 36
10-Jun-10 1100 <1 <1 <1 3.9 31
18-Aug-10 1500 1.1 <1 <1 3.9 36
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-7 Tetrachloride Chloride
I• (ugll) (u2/l) (ugll) (u2/l) (mgll) (mgll)
13-0ct-10 1100 1.1 <1 <1 4 38
23-Feb-11 1300 ND ND ND 3.6 45
1-Jun-11 1200 ND ND ND 4 35
18-Aug-11 1200 ND ND ND 4.1 37
29-Nov-11 1000 ND ND ND 3.8 37
19-Jan-12 1000 ND ND ND 3.9 37
14-Jun-12 790 ND ND ND 4 41
13-Sep-12 870 ND ND ND 3.8 40
4-0ct-12 940 ND ND ND 3.8 41
13-Feb-13 1080 3.51 ND ND 3.9 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 2.9 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
Ul CD ::::s 'i >
E ... 0 -0 ...
.2 .c
0 ...... I 'll:t 3: 1-
0 0 0 <0
0 0 0 lO
0 0 0
"""
0 0 0 (V)
(1J6n)
0 0 0 C\1
0 0 0
p~-oaa-a
60-lnr-g
90-lOO-O~
vo-uer-v~
0
Ch1orofonn Carbon Chloromethane Methylene Nitrate Chloride TW4-8 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (uWJ) (uWJ)
29-Nov-99 0
15-Mar-00 21.8
2-Sep-00 102
29-Nov-00 107 ND
26-Mar-01 116 ND
20-Jun-01 180 ND
20-Sep-01 180 0.35
7-Nov-01 180 ND
26-Mar-02 190 0.62
22-May-02 210 0.77
12-Sep-02 300 ND
24-Nov-02 450 ND
28-Mar-03 320 0.8
23-Jun-03 420 ND
12-Sep-03 66.0 ND
8-Nov-03 21.0 0.1
29-Mar-04 24.0 0.65
22-Jun-04 110 0.52
17-Sep-04 120 ND
17-Nov-04 120 ND
16-Mar-05 10.0 ND
25-May-05 <1 NA NA NA 0.2 NA
31-Aug-05 1.1 <1 1.7 <1 <0.1 NA
30-Nov-05 <1 <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 <1 <0.1 37
20-Jul-06 <1 <1 <1 <1 0.1 39
8-Nov-06 <1 <1 <1 <1 <0.1 40
28-Feb-07 2.5 <1 <1 <1 0.7 39
27-Jun-07 2.5 <1 <1 <1 0.2 42
15-Aug-07 1.5 <1 <1 <1 <0.1 42
10-0ct-07 3.5 <1 <1 <1 0.5 43
26-Mar-08 <1 <1 <1 <1 0.1 46
25-Jun-08 <1 <1 <1 <1 <0.05 45
10-Sep-08 <1 <1 <1 <1 <0.05 39
15-0ct-08 <1 <1 <1 <1 <0.05 44
4-Mar-09 <1 <1 <1 <1 <0.1 42
24-Jun-09 <1 <1 <1 <1 <0.1 44
15-Sep-09 <1 <1 <1 <1 <1 44
17-Dec-09 <1 <1 <1 <1 <0.1 51
24-Feb-10 <1 <1 <1 <1 <0.1 57
9-Jun-10 <1 <1 <1 <1 <0.1 42
11-Aug-10 <1 <1 <1 <1 <0.1 45
~m C.h0 Chiw0.1JU!6ane Meth}!bme NitJ!a1e Chteride TW4-8 (ugt)) 'f'etracb· •• (txg!J} Cld e (in#~) ~~ tu.:21J~ tuldn
5-0ct-10 <1 <1 <1 <1 <0.1 46
16-Feb-11 ND ND ND ND ND 52
25-May-11 ND ND ND ND 0.1 45
16-Aug-11 ND ND ND ND 0.1 46
7-Dec-11 ND ND ND ND 0.2 45
18-Jan-12 ND ND ND ND 0.3 45
31-May-12 ND ND ND ND 0.2 44
29-Aug-12 ND ND ND ND 0.1 48
3-0ct-12 ND ND ND ND ND 47
7-Feb-13 ND ND ND ND 0.411 46.6
30-May-13 ND ND ND ND ND 45.5
5-Sep-13 ND ND ND ND ND 47.5
7-Nov-13 ND ND ND ND ND 46.1
23-Jan-14 63.8 ND ND ND 0.166 48.5
6-Feb-14 100 ND ND ND 0.165 46.6
22-May-14 122 ND ND ND 0.538 53
27-Aug-14 107 ND ND ND 0.6 47
29-0ct-14 191 ND ND ND 0.914 46.7
12-Mar-15 961 ND ND ND 2.34 49.6
11-Jun-15 981 ND ND ND 1.88 53
10-Sep-15 747 ND ND ND 1.96 59.6
29-0ct-15 770 ND ND ND 2.2 52.0
17-Mar-16 634 ND ND ND 2.48 54.2
rn Cl)
::l c; >
E "-0 0 "-.2 .c 0
co I -.:t 3: ....
0 0 C\1
I ~
0 0 0
0 0 co
0 g
(1J6n)
I
~
~
~
\:,..-A
Cl .. c:> ..::::: ~
0 0 '<t
~ ~~
0 0
C\1
0
L~-das-cc
vo-uer-v~
Chloroferm Carlte Gh omethaue. Mefh lene Mkate Cti .
TW4-9 Tetra ' "de c ri e
W;g11} (uJdJl WJI) ChWil (mg/1) gil)
20-Dec-99 4.2
15-Mar-00 1.9
2-Sep-00 14.2
29-Nov-00 39.4 ND
27-Mar-01 43.6 ND
20-Jun-01 59.0 0.15
20-Sep-01 19.0 0.4
7-Nov-01 49.0 0.1
26-Mar-02 41.0 0.5
22-May-02 38.0 0.65
12-Sep-02 49.0 0.2
24-Nov-02 51.0 0.6
28-Mar-03 34.0 0.6
23-Jun-03 33.0 0.8
12-Sep-03 32.0 1.1
8-Nov-03 46.0 1.1
29-Mar-04 48.0 0.82
22-Jun-04 48.0 0.75
17-Sep-04 39.0 0.81
17-Nov-04 26.0 1.2
16-Mar-05 3.8 1.3
25-May-05 1.2 NA NA NA 1.3 NA
31-Aug-05 <1 <1 2.9 <1 1.3 NA
1-Dec-05 <1 <1 <1 <1 1.3 NA
9-Mar-06 <1 <1 2.6 <1 1.5 38
14-Jun-06 <1 <1 2.7 <1 1.5 39
20-Jul-06 <1 <1 <1 <1 0.9 41
8-Nov-06 <1 <1 <1 <1 0.7 44
28-Feb-07 <1 <1 <1 <1 0.6 44
27-Jun-07 21 <1 <1 <1 1.3 42
15-Aug-07 9.5 <1 <1 <1 1.8 38
10-0ct-07 8.7 <1 <1 <1 2 40
26-Mar-08 1.3 <1 <1 <1 2.1 35
25-Jun-08 1.0 <1 <1 <1 2.3 35
10-Sep-08 <I <1 <1 <1 2.79 28
15-0ct-08 <1 <1 <1 <1 1.99 58
4-Mar-09 <1 <1 <1 <1 2.5 30
24-Jun-09 <1 <1 <1 <1 2.3 30
15-Sep-09 <1 <1 <1 <1 2.5 30
17-Dec-09 <1 <1 <1 <1 1.7 37
23-Feb-10 <1 <1 <1 <1 1.7 47
9-Jun-10 <1 <1 <1 <1 1.5 33
11-Aug-10 <1 <1 <1 <1 1.2 40
Chloroform Carbou Chl&r.emetlume MetayleAe Nitrate Cklmide 'fW4·9 Tetracblmi:de ChloFlde (uglt) ,(llVA) (' gil} ful!ln (mgll) (mg/1)
6-0ct-10 <1 <1 <1 <1 1.8 34
17-Feb-11 ND ND ND ND 1.3 41
25-May-11 ND ND ND ND 3.4 38
16-Aug-11 ND ND ND ND 4 21
7-Dec-11 ND ND ND ND 2.3 38
18-Jan-12 ND ND ND ND 2.3 28
31-May-12 ND ND ND ND 4 23
30-Aug-12 ND ND ND ND 3.9 22
3-0ct-12 ND ND ND ND 3.8 21
7-Feb-13 ND ND ND ND 4.12 20.6
30-May-13 ND ND ND ND 4.49 21.4
5-Sep-13 ND ND ND ND 4.03 22.7
7-Nov-13 ND ND ND ND 4.87 23.6
29-Jan-14 ND ND ND ND 4.36 22
21-May-14 6.9 ND ND ND 3.44 24
14-Aug-14 46.9 ND ND ND 2.7 27
29-0ct-14 101 ND ND ND 4.27 25
12-Mar-15 53.5 ND ND ND 3.28 29.5
11-Jun-15 35.1 ND ND ND 1.83 35.3
3-Sep-15 48.2 ND ND ND 1.44 39.5
28-0ct-15 68.4 ND ND ND 2.89 29.2
17-Mar-16 74.3 ND ND ND 2.51 33.6
rn Q)
:J ~
E ...
~ 0 :c
0
0')
I ~ t-
0 C\1 0 0 0 (()
..... __ -
c
5
~
0 co
(1f6n)
~
~
[1
p.
...
~
/ • ~
.......--~
0 C\1
~
0
L~-daS-G2
v~-oaa-a
5o-1nr-9
90-lOQ-O~
vo-uer-v~
i~0i'.orm Carb:on Cbl ·mdhao:e Metliylene Nitrate abt(:)rii.e N 4·M 'f.*acbiDrlde Ch .. e
(ugtl) (,a!!'/t)J (~~ (.uefl) { fl!~ (lmgl,t)
21-Jan-02 14
26-Mar-02 16 0.14
21-May-02 17 0.11
12-Sep-02 6 ND
24-Nov-02 14 ND
28-Mar-03 29 0.2
23-Jun-03 110 0.4
12-Sep-03 74 0.4
8-Nov-03 75 0.3
29-Mar-04 22 0.1
22-Jun-04 32 ND
17-Sep-04 63 0.46
17-Nov-04 120 0.4
16-Mar-05 140 1.6
25-May-05 62.4 NA NA NA 0.8 NA
31-Aug-05 110 <2.5 6.2 <2.5 1.1 NA
1-Dec-05 300 <2.5 <2.5 <2.5 3.3 NA
9-Mar-06 190 <5 <50 <50 2.4 50
14-Jun-06 300 <5 <50 <50 3.5 54
20-Jul-06 504 <5 <50 <50 6.8 61
8-Nov-06 452 <1 1.6 1 5.7 58
28-Feb-07 500 <1 <1 1 7.6 62
27-Jun-07 350 <1 <1 1 5.1 54
15-Aug-07 660 <1 <1 1 7.3 59
10-0ct-07 470 <1 <1 1 6.7 59
26-Mar-08 620 <1 <1 1 7.3 55
25-Jun-08 720 <1 <1 1 9.91 58
10-Sep-08 680 <1 <1 1 9.23 51
15-0ct-08 1200 <2 <2 2 10.5 61
11-Mar-09 1100 <1 <1 1 11.6 64
24-Jun-09 1200 <1 <1 1 9.8 62
15-Sep-09 910 <1 <1 1 8.1 51
22-Dec-09 300 <1 <1 <1 3.5 51
3-Mar-10 460 <1 <1 <1 5 49
10-Jun-10 220 <1 <1 <1 1.6 42
12-Aug-10 100 <1 <1 <1 0.8 38
13-0ct-10 1100 <1 <1 <1 11 52
23-Feb-11 620 ND ND ND 9 62
1-Jun-11 280 ND ND ND 3.3 42
17-Aug-11 180 ND ND ND 1.9 41
16-Nov-11 110 ND ND ND 1.1 45
19-Jan-12 76 ND ND ND 0.9 40
13-Jun-12 79 ND ND ND 0.8 46
Chloroform CaFbon Chhw0mdllane Methylene •trat C.bloride TW4-10 (ugltl) Tetr.achJ .de
(ug/1.) CJ:tbJ ii.e (mWJ) (mgll) .(Wi'tlJ) (_B,e/t}
12-Sep-12 130 ND ND ND 1.0 44
3-0ct-12 140 ND ND ND 1.6 45
13-Feb-13 154 ND ND ND 1.2 49.1
13-Jun-13 486 ND ND ND 5.6 51.5
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-15 1350 ND ND ND 13.5 79.9
22-Mar-16 1430 ND ND ND 17.3 84.1
rn G)
::::J
ca >
E
""" 0 -0
""" ..2 J:
0
0 ,..
I "d' 3: ~
.------.....-------.-----,-----.-------,..------,---,----, L ~ -das-~~
17~-oaa-a
6o-1nr-g
90-~00-0~
-17o-uer-17 ~
t----+----t----+----+---+------!---+------+ ~O-JdV-6 ~
0 0 <0
0 0
""'"
0 0 C\1
0 0 0
0 0 C()
0 0 <0
(1J6n)
0 0
""'"
0 0 C\1
0
CW'erofGmi Cathen Chl&rmnetll: rm Ni1Fate .'CbloWde TW4·11 Tetr dtll\JJ'id.e e
tugffl {ulfl) ~n~l) Cld tide(~ (mgAI) (mg/A)
21-Jan-02 4700
26-Mar-02 4900 9.6
22-May-02 5200 9.07
12-Sep-02 6200 8.84
24-Nov-02 5800 9.7
28-Mar-03 5100 9.7
23-Jun-03 5700 9.4
12-Sep-03 4600 9.9
8-Nov-03 5200 9.3
29-Mar-04 5300 9.07
22-Jun-04 5700 8.74
17-Sep-04 4800 8.75
17-Nov-04 5800 9.7
16-Mar-05 4400 8.7
25-May-05 3590 NA NA NA 10.3 NA
31-Aug-05 4400 <10 <10 <10 9.4 NA
1-Dec-05 4400 <100 <100 <100 9.4 NA
9-Mar-06 4400 <50 <50 <50 9.2 56
14-Jun-06 4300 <50 <50 <50 10 56
20-Jul-06 4080 <50 <50 <50 10 55
8-Nov-06 3660 1.7 2.7 1.3 10 55
28-Feb-07 3500 1.3 <1 1.6 10.1 54
27-Jun-07 3800 1.6 <1 1.1 10.6 53
15-Aug-07 4500 1.7 <1 1.1 10.2 53
10-0ct-07 4400 1.6 <1 1.2 9.8 53
26-Mar-08 340 <1 <1 <1 7.7 63
25-Jun-08 640 <1 <1 <1 7.28 46
10-Sep-08 900 <1 <1 <1 7.93 42
15-0ct-08 1000 <2 <2 <2 9.46 47
11-Mar-09 1100 <1 <1 <1 7.3 49
24-Jun-09 980 <1 <1 <I 6.8 44
15-Sep-09 1000 <1 <1 <1 7 49
29-Dec-09 860 <1 <1 <1 6.6 46
3-Mar-10 820 <1 <1 <I 6.8 42
10-Jun-10 820 <1 <1 <1 6.9 40
12-Aug-10 800 <1 <1 <1 6.7 43
13-0ct-10 720 <1 <1 <1 6.4 49
23-Feb-11 1000 ND NO ND 6.5 46
1-Jun-11 930 NO ND ND 7.3 49
17-Aug-11 820 ND ND NO 7.1 48
16-Nov-11 1500 ND ND NO 7.1 46
24-Jan-12 610 ND ND ND 6.8 43
13-Jun-12 660 ND ND NO 6.7 52
Chl Ai'fOrDl Carlmn CMDrome*haae Mefh, Nitrate Cklorille TW4-11 T trachler.ld e
(ugtl) (!De/A') (ugll) Cllbni«<e t'Ugtl) (mgll) (m~l)
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 ll20 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
0 Cl)
::J
C'IS >
E ...
0 -0 ...
.2
J:
0
'I"'"
'I"'" I ~ ~ 1-
.--------r----.,....-------.----.....-------r----r------r L ~-das-c::c::
v~-oaa-a
5o-1nr-g
· 90-PO·O~
vo-uer-v~
r----+-----t---+-----t----+----+----+ ~O-JdV-6~
0 0 0 ,.....
0 0 0 <0
0 0 0
1.0
0 0 0 "<t
0 0 0 (')
0 0 0 C\1
0 0 0
0
<B•tD:nn 'Car;J)QD t~r0'lil'ldb Jre
;Met -"'-~ Ghlomde --· TWU2 11 ~· . (Dkfu ~ (ugfl) I ~u.wt) t . ~ (mgll~ _hJ.If1) f:.u:«JJ,
12-Sep-02 2 2.54
24-Nov-02 0 2.2
28-Mar-03 0 1.9
23-Jun-03 0 1.8
12-Sep-03 0 1.8
9-Nov-03 0 1.6
29-Mar-04 0 1.58
22-Jun-04 0 1.4
17-Sep-04 0 1.24
17-Nov-04 0 1.5
16-Mar-05 0 1.4
25-May-05 <1 NA NA NA 1.6 NA
31-Aug-05 <1 <1 5.8 <1 1.5 NA
1-Dec-05 <1 <1 1.9 <2 1.4 NA
9-Mar-06 <1 <1 2.6 <I 1.3 19
14-Jun-06 <1 <1 1.4 <1 1.4 16
20-Jul-06 <1 <1 <1 <1 1.4 16
8-Nov-06 <1 <1 <1 <1 1.4 16
28-Feb-07 <1 <1 <1 <1 1.5 16
27-Jun-07 <1 <1 <1 <1 1,5 18
15-Aug-07 <1 <1 <1 <1 1.4 29
10-0ct-07 <1 <1 <1 <1 1.4 16
26-Mar-08 <1 <1 <1 <1 1.6 16
25-Jun-08 <1 <1 <1 <1 2.69 19
10-Sep-08 <1 <1 <1 <1 2.65 18
15-0ct-08 <1 <1 <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 <1 <1 <1 <1 5.1 22
16-Dec-09 <1 <1 <1 <1 3.6 23
23-Feb-10 <1 <1 <1 <1 4 22
8-Jun-10 <1 <1 <1 <1 11 29
10-Aug-10 <1 <1 <1 <1 9 35
5-0ct-10 <1 <1 <1 <1 8 31
15-Feb-11 ND ND ND ND 6.5 31
25-May-11 ND ND ND ND 7 32
16-Aug-11 ND ND ND ND 6.8 31
15-Nov-11 ND ND ND ND 8 30
17-Jan-12 ND ND ND ND 7.7 28
31-May-12 ND ND ND ND 10 34
29-Aug-12 ND ND ND ND 13 39
3-0ct-12 ND ND ND ND 13 39
7-Feb-13 ND ND ND ND 12.6 36.7
Chlol'oform Car bOB Cblerotnethune Methyl e Nitrate Chloride TW~l2 Tetrachlorlde Cldol'l , ugM) (itf!l.l~ (ag/1~ (uflli) {mg/1} (mg/1)
29-May-13 ND ND ND ND 14.2 38.6
29-Aug-13 ND ND ND ND 17.4 41.7
6-Nov-13 ND ND ND ND 16.4 41.4
22-Jan-14 ND ND ND ND 18.4 41.6
21-May-14 ND ND ND ND 17 40.2
27-Aug-14 ND ND ND ND 13 47
23-0ct-14 ND ND ND ND 16.1 50.2
11-Mar-15 ND ND ND ND 19.2 50.6
10-Jun-15 ND ND ND ND 18.8 56
2-Sep-15 ND ND ND ND 16.4 60.2
21-0ct-15 ND ND ND ND 18 51.0
15-Mar-16 ND ND ND ND 34.8 56.2
tn Q) ~ m >
E ...
0 2
0 ::c
0
N ,....
I ~
0
C\i
(1J6n)
~
~
~
~
0
0
L~-das-cc
v~-oaa-a
60-lnr-g
90-PO-O~
vo-uer-v~
OdDrofG:mr c r1lJtm Met'bylene Nikate · orltfe ~-ll Tetra ' j PO ane --" ._.,
~~
..
~ ~~ ~uf!fJ) (ud} < ell)
12-Sep-02 ND ND
24-Nov-02 ND ND
28-Mar-03 ND 0.2
23-Jun-03 ND 0.2
12-Sep-03 ND ND
9-Nov-03 ND 0.9
29-Mar-04 ND 0.12
22-Jun-04 ND 0.17
17-Sep-04 ND 4.43
17-Nov-04 ND 4.7
16-Mar-05 ND 4.2
25-May-05 <1 NA NA NA 4.3 NA
31-Aug-05 <1 <1 3.1 <1 4.6 NA
1-Dec-05 <1 <1 <1 <1 4.3 NA
9-Mar-06 <1 <1 1.7 <1 4.2 67
14-Jun-06 <1 <1 1.4 <1 4.9 66
20-Jul-06 <1 <1 <1 <1 4.3 65
8-Nov-06 <1 <1 <1 <1 0.8 33
28-Feb-07 <1 <1 <1 <1 4 59
27-Jun-07 <1 <1 <1 <1 4.6 59
15-Aug-07 <1 <1 <1 <1 4.4 58
10-0ct-07 <1 <1 <1 <1 4.1 58
26-Mar-08 <1 <1 <1 <1 3.8 54
25-Jun-08 <1 <1 <1 <1 4.24 58
10-Sep-08 <1 <1 <1 <1 4.26 50
15-0ct-08 <1 <1 <1 <1 4.63 58
4-Mar-09 <1 <1 <1 <1 3.7 58
24-Jun-09 <1 <1 <1 <1 1.2 57
15-Sep-09 <1 <1 <1 <1 4.7 63
16-Dec-09 <1 <1 <1 <1 4.1 60
24-Feb-10 <1 <1 <1 <1 4.3 53
8-Jun-10 <1 <l <1 <1 5.2 52
10-Aug-10 <1 <1 <1 <1 5.6 55
5-0ct-10 <1 <1 <1 <1 5.8 55
15-Feb-11 ND ND ND ND 5.5 60
25-May-11 ND ND ND ND 5.4 56
16-Aug-ll ND ND ND ND 5.2 60
15-Nov-11 ND ND ND ND 5.9 54
17-Jan-12 ND ND ND ND 5.5 55
31-May-12 ND ND ND ND 6 59
29-Aug-12 ND ND ND ND 6.2 60
3-0ct-12 ND ND ND ND 5.9 60
7-Feb-13 ND ND ND ND 6.31 59.3
29-May-13 ND ND ND ND 6.84 56
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-13 Tetrachloride Chloride (ugll) ~ue/1), (ug/1) fuell5 m,g/1~ (mgll)
29-Aug-13 ND ND ND ND 7.16 63.5
6-Nov-13 ND ND ND ND 6.48 58.5
22-Jan-14 ND ND ND ND 7.09 63.1
21-May-14 ND ND ND ND 5.99 56.1
13-Aug-14 ND ND ND ND 4.8 62
23-0ct-14 ND ND ND ND 6.28 66.1
11-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 5.7 76.5
21-0ct-15 ND ND ND ND 5.78 65.5
16-Mar-16 ND ND ND ND 7.97 69.4
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
0
1
j
1
1
1
1
1
j
j
j
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j
j
j
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j
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Cl referm Coohen Cldwem ·• Me.fh!d e Nitrate Chleride TW4·14 T'ek mitle Chla.
(ug/1) (u/j) (Ugll} Ludl mgf!) ~mgA)
8-Nov-06 <1 <1 <1 <1 2.4 37
28-Feb-07 <1 <1 <1 <1 2.3 38
27-Jun-07 <1 <1 <1 <1 1.4 38
15-Aug-07 <1 <1 <1 <1 1.1 36
10-0ct-07 <1 <1 <1 <1 0.8 36
26-Mar-08 <1 <1 <1 <1 0.04 57
25-Jun-08 <1 <1 <1 <1 1.56 35
10-Sep-08 <1 <1 <1 <1 1.34 34
15-0ct-08 <1 <1 <1 <1 0.76 40
4-Mar-09 <1 <1 <1 <1 1.6 35
24-Jun-09 <1 <1 <1 <1 1.4 36
15-Sep-09 <1 <1 <1 <1 1.5 38
16-Dec-09 <1 <1 <1 <1 1.4 34
3-Mar-10 <1 <1 <1 <1 2.5 33
8-Jun-10 <1 <1 <1 <1 2.9 49
10-Aug-10 <1 <1 <1 <1 2.8 35
6-0ct-10 <1 <1 <1 <1 2.9 29
15-Feb-11 ND ND ND ND 1.8 25
16-Aug-11 ND ND ND ND 2.6 33
15-Nov-11 ND ND ND ND 1.7 15
17-Jan-12 ND ND ND ND 1.9 20
31-May-12 ND ND ND ND 3.3 35
29-Aug-12 ND ND ND ND 3.9 37
3-0ct-12 ND ND ND ND 4.2 37
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 4.1 38
23-0ct-14 1.68 ND ND ND 5.22 38.9
12-Mar-15 1.71 ND ND ND 5.22 40.1
10-Jun-15 1.82 ND ND ND 3.55 41.8
3-Sep-15 ND ND ND ND 2.77 42.4
21-0ct-15 1.46 ND ND ND 2.45 40.6
16-Mar-16 4.49 ND ND 2.18 2.94 42.4
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Chlm'O c_.~wn 1'8 ,.~>."&. Methylene """" Chloride MW-26 Ml T Ia (""'~ "-, . , ... -'"'·"-(ng11) t (u,gtl} {mgt~!) ~ €-u~n (ui!IJ~
12-Sep-02 3 ND
24-Nov-02 0 ND
28-Mar-03 0 0.1
23-Jun-03 7800 14.5
15-Aug-03 7400 16.8
12-Sep-03 2500 2.7
25-Sep-03 2600 2.5
29-0ct-03 3100 3.1
8-Nov-03 3000 2.8
29-Mar-04 NA NA
22-Jun-04 NA NA
17-Sep-04 1400 0.53
17-Nov-04 300 0.2
16-Mar-05 310 0.3
30-Mar-05 230 0.2
25-May-05 442 NA NA NA 0.2 NA
31-Aug-05 960 <5 5.4 <5 0.2 NA
1-Dec-05 1000 <50 <50 <50 0.3 NA
9-Mar-06 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 <1 <1 2.8 0.3 54
28-Feb-07 570 <1 <1 5.5 0.5 56
27-Jun-07 300 <1 <1 13 0.4 49
15-Aug-07 1400 <1 <1 36 1 57
10-0ct-07 2000 <1 <1 14 0.6 57
26-Mar-08 930 <1 <1 40 0.1 49
25-Jun-08 1300 <1 <1 53 0.56 57
10-Sep-08 630 <1 <1 24 0.24 44
15-0ct-08 1700 <1 <1 100 0.65 64
4-Mar-09 950 <1 <1 51 0.4 49
24-Jun-09 410 <1 <1 12 0.2 48
15-Sep-09 850 <1 <1 30 0.1 46
14-Dec-09 1100 <1 <1 40 2.3 60
17-Feb-10 780 <1 <1 19 0.2 57
9-Jun-10 1900 <1 <1 28 1.1 58
16-Aug-10 2200 <1 <1 21 0.6 49
11-0ct-10 970 <1 <1 6.5 0.7 65
23-Feb-11 450 ND ND 3.6 0.5 57
31-May-11 1800 ND ND 1.3 0.4 88
17-Aug-11 720 ND ND 7.2 0.9 58
5-Dec-11 1800 ND ND 2.9 2 69
7-Feb-12 2400 ND ND 16 1.7 98
Cbl&roftmn Carbo Ohleromethane MethyJ De Nitrate Chloride MW-26 (ugtl) 'fetr :c o ide €uglf) Chl~ri ~mgll) (mgt} (ud) (.txf!{,J:)
6-Jun-12 3000 ND ND 21 2.5 73
4-Sep-12 3100 ND ND 31 2.6 73
4-0ct-12 1200 ND ND 4 1.8 68
11-Feb-13 2120 ND ND 9.34 2.27 81.9
5-Jun-13 4030 ND ND 52.4 2.11 77.9
3-Sep-13 2940 ND ND 33.2 1.18 60.5
29-0ct-13 1410 ND ND 4.03 1.38 72.3
27-Jan-14 1400 ND ND 13.8 0.549 59.4
19-May-14 1960 ND ND 15.4 0.928 53.4
11-Aug-14 2120 ND 8.7 26 0.7 59
21-0ct-14 2090 ND ND 23.2 0.934 60.1
9-Mar-15 1980 ND ND 27.4 0.732 56.5
8-Jun-15 1980 ND ND 11.2 0.419 62
31-Aug-15 2350 ND 4.05 11.6 0.684 69.6
19-0ct-15 2680 ND 1.32 8.28 0.991 62.6
9-Mar-16 2650 ND 1.32 4.66 1.45 68.3
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I'' Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ue/1) (nell)
12-Sep-02 140 ND
24-Nov-02 200 ND
28-Mar-03 260 ND
23-Jun-03 370 ND
12-Sep-03 350 ND
8-Nov-03 400 ND
29-Mar-04 430 ND
22-Jun-04 530 ND
17-Sep-04 400 ND
17-Nov-04 350 ND
16-Mar-05 240 ND
25-May-05 212 NA NA NA <0.1 NA
31-Aug-05 85 <1 3.2 43 <0.1 NA
1-Dec-05 14 <2.5 2.6 5.9 1.4 NA
9-Mar-06 39.0 <1 1.1 21 3 60
14-Jun-06 13.0 <1 2.4 8.9 1.9 55
20-Jul-06 5.2 <1 <1 2.7 2.7 60
8-Nov-06 13.6 <1 <1 9.2 5.6 62
28-Feb-07 8.7 <1 <1 6.5 12.3 79
27-Jun-07 2.6 <1 <1 1.8 9.9 75
15-Aug-07 7.1 <1 <1 5.1 5.4 66
10-0ct-07 1.4 <1 <1 <1 4.4 69
26-Mar-08 11.0 <1 <1 26 ND 52
25-Jun-08 <1 <1 <I <1 1.46 58
10-Sep-08 10 <1 <1 14 10.5 71
15-0ct-08 3.9 <1 <1 6.6 9.82 89
4-Mar-09 <1 <1 <1 <1 9.6 78
24-Jun-09 <1 <1 <1 <1 8.9 76
15-Sep-09 <1 <1 <1 <1 8.8 79
17-Dec-09 <1 <1 <1 <1 5.2 76
24-Feb-10 <1 <1 <1 <1 4.2 77
9-Jun-10 2.1 <1 <1 <1 4.7 64
24-Aug-10 4.3 <1 <1 <1 4.6 72
6-0ct-10 3.0 <1 <1 <1 3.3 72
22-Feb-11 15.0 ND ND ND 7 86
26-May-11 16.0 ND ND ND 5 81
17-Aug-11 9.2 ND ND ND 1.7 63
16-Nov-11 ND ND ND 1.4 0.4 38
18-Jan-12 ND ND ND 1.7 0.1 48
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
Clderof8l'Rl Carbon Cb:lo11o eftlaue Methylene Nitrate Chloride TW4-~6 (ugtl) Te1lnlchloti.tfe (ug:ll) Chlol'id (mgll) (mg/1) (ualJ) (u21J)
30-May-13 ND ND ND 4.21 ND 49.8
5-Sep-13 ND ND ND ND ND 54.4
7-Nov-13 13.4 ND ND ND 1.37 56.6
29-Jan-14 6.9 ND ND ND 3.16 66.8
22-May-14 14.6 ND ND ND 4.94 80.7
14-Aug-14 229.0 ND ND ND 5.1 80
24-Sep-14 371.0 ND ND ND NIA NIA
29-0ct-14 387.0 ND ND ND 8.40 92.1
12-Mar-15 153.0 ND ND ND 4.30 65.3
11-Jun-15 65.3 ND ND ND 1.06 61
3-Sep-15 82.0 ND ND ND 1.18 65.8
28-0ct-15 112.0 ND ND ND 1.69 58.3
17-Mar-16 45.9 ND ND ND 1.63 56.5
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12-Sep-02 1.6 ND
24-Nov-02 ND ND
28-Mar-03 ND ND
23-Jun-03 ND ND
12-Sep-03 ND ND
8-Nov-03 ND ND
29-Mar-04 ND ND
22-Jun-04 ND ND
17-Sep-04 ND ND
17-Nov-04 ND ND
16-Mar-05 ND ND
30-Mar-05 ND ND
25-May-05 <1 NA NA NA <0.1 NA
31-Aug-05 <1 <1 3.2 <1 <0.1 NA
1-Dec-05 <1 <1 <1 <1 <0.1 NA
9-Mar-06 <1 <1 <1 <1 <0.1 32
14-Jun-06 <1 <1 3.5 <1 <0.1 30
20-Jul-06 <1 <1 1.8 <1 <0.1 32
8-Nov-06 <1 <1 1.5 <1 <0.1 31
28-Feb-07 <1 <1 <1 <1 <0.1 32
27-Jun-07 <1 <1 <1 <1 <0.1 32
15-Aug-07 <1 <1 <1 <1 <0.1 31
10-0ct-07 <1 <1 <1 <1 <0.1 32
26-Mar-08 <1 <1 <1 <1 <0.1 31
25-Jun-08 <1 <1 <1 <1 <0.05 29
10-Sep-08 <1 <1 <1 <1 <0.05 30
15-0ct-08 <1 <1 <1 <1 <0.05 26
4-Mar-09 <1 <1 <1 <1 <0.1 30
24-Jun-09 <1 <1 <1 <1 <0.1 31
15-Sep-09 <1 <1 <1 <1 <0.1 33
16-Dec-09 <1 <1 <1 <1 <0.1 34
17-Feb-10 <1 <1 <1 <1 <0.1 38
14-Jun-10 <1 <1 <1 <1 <0.1 32
16-Aug-10 <1 <1 <1 <1 <0.1 28
6-0ct-10 <1 <1 <1 <1 <0.1 24
23-Feb-11 ND ND ND ND ND 40
25-Mav-11 ND ND ND ND ND 31
16-Aug-11 ND ND ND ND ND 33
6-Dec-11 ND ND ND ND ND 32
18-Jan-12 ND ND ND ND ND 21
4-Jun-12 ND ND ND ND ND 32
5-Sep-12 ND ND ND ND ND 33
10-0ct-12 ND ND ND ND ND 35
Chloreform Carbon Cbl'eromdhane Me~lene Nitrrate Chloride MW-32 Tetraehlomde Cldemte tut/t) Jlll!hl ~ug/1) _(u.u/1) (mgll) (mg11)
13-Feb-13 NO NO NO NO NO 34.3
18-Jun-13 NO NO NO NO NO 34.9
4-Sep-13 NO NO NO NO NO 33
29-0ct-13 NO NO NO NO NO 35.7
29-Jan-14 NO NO NO NO NO 34
23-May-14 NO NO NO NO NO 39.7
26-Aug-14 NO NO NO NO NO 34
29-0ct-14 NO NO NO NO NO 34.9
17-Mar-15 NO NO NO NO NO 36.3
11-Jun-15 NO NO NO NO NO 35.8
9-Sep-15 NO NO NO NO NO 37.7
28-0ct-15 NO NO NO NO NO 34.7
22-Mar-16 NO NO NO NO NO 36.7
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Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-18 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (u2/l) _(ul!/l)
12-Sep-02 440 1.49
24-Nov-02 240 13.3
28-Mar-03 160 13.1
23-Jun-03 110 19
12-Sep-03 68.0 19.9
9-Nov-03 84.0 20.7
29-Mar-04 90.0 14
22-Jun-04 82.0 12.2
17-Sep-04 38.0 14.5
17-Nov-04 51.0 17.3
16-Mar-05 38.0 14.1
25-May-05 29.8 NA NA NA 12.9 NA
31-Aug-05 39 <1 2.8 <1 13.3 NA
1-0ec-05 14 <1 1.1 <1 7.3 NA
9-Mar-06 12.0 <1 1.1 <1 5.9 5.9
14-Jun-06 12.0 <1 1.6 <1 4.7 35
20-Jul-06 10.8 <1 2.7 <1 6.1 35
8-Nov-06 139 <1 <1 <1 8.7 34
28-Feb-07 9.2 <1 <1 <1 5.1 30
27-Jun-07 8.0 <1 <I <1 4.9 28
15-Aug-07 8.9 <1 <1 <1 5 32
10-0ct-07 7.4 <1 <1 <1 4.4 27
26-Mar-08 6.4 <1 <I <1 0.7 23
25-Jun-08 5.7 <1 <1 <1 4.55 23
10-Sep-08 8.0 <1 <1 <1 4.68 26
15-0ct-08 9.4 <1 <I <1 5,15 30
4-Mar-09 11.0 <1 <1 <1 5.2 29
24-Jun-09 16.0 <1 <1 <1 6.2 30
15-Sep-09 13.0 <1 <I <1 5.9 26
22-Dec-09 8.2 <1 <1 <1 5.4 30
24-Feb-10 69.0 <1 <1 <1 5.1 41
9-Jun-10 29.0 <1 <I <1 9 35
12-Aug-10 29.0 <1 <1 <1 9 37
13-0ct-10 30.0 <1 <1 <1 10 50
22-Feb-11 39.0 ND ND ND 10 52
26-May-11 26.0 ND ND NO 9 36
17-Aug-11 29.0 ND ND ND 4.6 23
7-0ec-11 28.0 NO ND NO 6.3 23
19-Jan-12 25.0 ND NO NO 4.4 18
13-Jun-12 24.0 ND ND ND 6.6 30
11-Sep-12 38.0 ND ND NO 6.6 26
3-0ct-12 30.0 ND NO ND 6 27
13-Feb-13 34.9 ND ND ND 5.58 23.1
ChloJToform Car. bon CWorometbane Metb)"'eJle Nitrate, Clllodde TW4·18 (ugtlj Tetraclt!oride (rog{l) Chl'Oride (lngll) mgR) Curti~ (U2ft)'
13-Jun-13 37.9 ND ND ND 8.86 22.9
5-Sep-13 41.0 ND ND ND 12.1 36.2
13-Nov-13 44.3 ND ND ND 14.2 37.1
30-Jan-14 38.9 ND ND ND 12.8 40.9
22-May-14 34.8 ND ND ND 12.2 47
14-Aug-14 32.8 ND ND ND 9.8 49
28-0ct-14 33.0 ND ND ND 11.1 40.8
12-Mar-15 32.0 ND ND ND 11.7 41.6
11-Jun-15 30.5 ND ND ND 9.69 43.5
3-Sep-15 28.7 ND ND ND 15.7 47.6
28-0ct-15 52.9 ND ND ND 6.24 39.4
17-Mar-16 56.6 ND ND ND 5.96 40.7
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Chi rnffmm CBJ6m CMD , dba 1 .j\4~th I Nitrate ·Citforide TW4-9 (llgfl) ~ a 6 •cte (ug/1; CM icle {mg/1) (mg$1) ·etu!!/0 (nd)
12-Sep-02 7700 47.6
24-Nov-02 5400 42
28-Mar-03 4200 61.4
15-May-03 4700 NA
23-Jun-03 4500 11.4
15-Jul-03 2400 6.8
15-Aug-03 2600 4
12-Sep-03 2500 5.7
25-Sep-03 4600 9.2
29-0ct-03 4600 7.7
9-Nov-03 2600 4.8
29-Mar-04 NA NA
22-Jun-04 NA NA
16-Aug-04 7100 9.91
17-Sep-04 2600 4.5
17-Nov-04 1800 3.6
16-Mar-05 2200 5.3
25-May-05 1200 5.7
31-Aug-05 1400 <5 <5 <5 4.6 NA
1-Dec-05 2800 <50 <50 <50 <0.1 NA
9-Mar-06 1200 <50 <50 <50 4 86
14-Jun-06 1100 <50 <50 <50 5.2 116
20-Jul-06 1120 <50 <50 <50 4.3 123
8-Nov-06 1050 1.6 2.6 <1 4.6 134
28-Feb-07 1200 1.3 <1 <1 4 133
27-Jun-07 1800 2.3
15-Aug-07 1100 1.9 <1 <1 4.1 129
10-0ct-07 1100 1.9 <1 <1 4 132
26-Mar-08 1800 2.9 <1 <1 2.2 131
25-Jun-08 1000 1 <1 <1 2.81 128
10-Sep-08 3600 8.6 <1 <1 36.2 113
15-0ct-08 4200 12 <1 <1 47.8 124
4-Mar-09 1100 1.2 <1 <1 3.2 127
24-Jun-09 990 1.2 <1 <1 2.4 132
15-Sep-09 6600 15 <1 <1 0.1 43
14-Dec-09 4700 16 <1 <1 26.7 124
17-Feb-10 940 1.3 <1 <1 2 144
9-Jun-10 1800 4.2 <1 <1 4.4 132
16-Aug-10 2000 4.9 <1 <1 5.9 142
11-0ct-10 1200 1.3 <1 <1 2.7 146
17-Feb-11 3400 17 ND ND 17 135
7-Jun-11 4000 8.3 ND ND 12 148
17-Aug-11 970 2.1 ND ND 3 148
Chlorofonn Cal' bon CIOOrometb Methylene Nitrate Chlollide TW4-19 (ug/1) Tetraehlo i(t (ugll) Chl&ridi (mg/1:) (mg/1) '•(Wlfj~ .(W!/t~
5-Dec-11 2200 5.4 ND ND 5 148
23-Jan-12 650 1.5 ND ND 0.6 138
6-Jun-12 460 1.1 ND ND 2.4 149
5-Sep-12 950 3.5 ND ND 2.5 149
3-0ct-12 1500 4 ND ND 4.1 150
11-Feb-13 4210 5.15 ND ND 7.99 164
5-Jun-13 2070 5.15 ND ND 2.95 148
3-Sep-13 8100 20.7 ND ND 17.6 179
29-0ct-13 942 6.42 ND ND 4.7 134
27-Jan-14 586 4.05 ND ND 1.62 134
19-May-14 810 5.51 ND ND 1.34 152
11-Aug-14 1410 1.9 8.3 ND 1.6 140
21-0ct-14 4310 4.8 ND ND 4.72 130
9-Mar-15 4660 8.92 ND ND 8.56 238
8-Jun-15 1570 2.62 ND ND 0.916 180
4-Sep-15 7860 7.78 ND ND 11.6 326
19-0ct-15 7840 12.2 5.46 ND 10.6 252
9-Mar-16 7780 13.5 1.40 ND 15.7 276
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1 Cltla GfQD1 Carlt:G • Chloride tDb em (" ,__-"· .... . te TW4-& T'.etr '. •! • .,. I e
~gij) (~) (a¥J) , ~· ~ ' ~)
25-May-05 39000 NA NA NA 10.1 NA
31-Aug-05 3800 <10 <10 <10 2.9 NA
1-Dec-05 19000 <250 <250 <250 1.8 NA
9-Mar-06 9200 <500 <500 <500 3.8 120
14-Jun-06 61000 <500 <500 <500 9.4 Z35
20-Jul-06 5300 <1000 <1000 <1000 2.9 134
8-Nov-06 11000 7.1 1.9 2.2 3.5 124
28-Feb-07 4400 3.1 <l 1.1 4.2 124
27-Jun-07 1800 2.2 <1 <1 2.3 112
15-Aug-07 5200 3.5 <1 1.8 2.1 117
10-0ct-07 9000 6.8 <1 1.9 5.6 170
26-Mar-08 13000 9 <1 1.5 0.9 132
25-Jun-08 30000 13 <1 1.2 7.96 191
10-Sep-08 21000 15 <1 3.7 4.44 156
15-0ct-08 NA NA NA NA 5.51 166
4-Mar-09 8200 5.7 <1 5.2 5.1 164
24-Jun-09 6800 4.9 <2 4.2 2.9 164
15-Sep-09 13000 8.4 <2 4.4 3.3 153
14-Dec-09 15000 14 <1 3 5.3 187
17-Feb-10 3500 2.7 <1 3.2 2 179
14-Jun-10 18000 11 <1 3.7 5.6 200
16-Aug-10 15000 12 <1 2.2 5.3 196
11-0ct-10 24000 20 <1 5.5 4.6 203
23-Feb-11 31000 27 ND 19 4.4 220
1-Jun-11 8100 10 ND 2.1 4.8 177
17-Aug-11 6800 7.3 ND 3.1 6.5 207
16-Nov-11 7900 7.2 ND 2.5 4.2 186
23-Jan-12 11000 10 ND 1.3 7.9 207
6-Jun-12 36000 33 ND ND 11 262
4-Sep-12 13000 26 ND ND 10.8 289
3-0ct-12 19000 22 ND ND 11 302
11-Feb-13 18500 19.6 ND 1.21 9.07 252
5-Jun-13 26300 32.5 ND 1.13 9.76 250
3-Sep-13 26800 25.7 ND 2.14 8.65 260
29-0ct-13 15700 17.3 ND 1.37 9.64 272
27-Jan-14 17800 18.4 ND 2.04 7.56 254
19-May-14 22100 22.1 2.31 3.98 5.95 269
11-Aug-14 12400 14.1 55.2 2.2 4.3 299
21-0ct-14 23300 18.5 4.04 2.38 7.67 292
9-Mar-15 19900 20.8 4.85 1.38 9.8 290
8-Jun-15 17600 16.2 13.4 1.73 5.76 296
31-Aug-15 17000 15.1 12.3 ND 9.27 365
19-0ct-15 17000 14.5 10.8 1 6.23 293
Chloroform Carbon Chloromethane Methylene Nitrate ,Chloride TW4-20 Tetrachloride Chloride (ug/1) (uWJ) (ug/1) (uelf) (mg/1) (mg/1)
9-Mar-16 2 1600 20.2 4.09 1.16 10.3 293
.-----.-----.-----....-----.-----.-------.------.-L ~ -das-cc
9 ~-liBII\I-0 ~
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vo-uer-v~
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 I'-co 10 "¢ C') C\1
(1!5n)
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I'Wf-21 'f.dr. ~lmi e u Cllhmble (ugfit: ~ ~~ '&1«11~ (Nid' ~--)
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 <1 <1 8.7 306
27-Jun-07 300 5.8 <1 <1 8.6 327
15-Aug-07 140 <1 <1 <1 8.6 300
10-0ct-07 120 <1 <1 <1 8.3 288
26-Mar-08 380 7 <1 <1 14.3 331
25-Jun-08 160 1.7 <1 <1 8.81 271
10-Sep-08 120 1.6 <1 <1 7.57 244
15-0ct-08 170 2 <1 <2 8.00 284
11-Mar-09 180 <1 <1 <1 8.3 279
24-Jun-09 200 <1 <1 <1 8.1 291
15-Sep-09 140 <1 <1 <1 9.2 281
22-Dec-09 160 <1 <1 <1 8.4 256
25-Feb-10 170 <1 <1 <1 8.4 228
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-11 230 1.2 ND ND 9 303
28-Jun-11 290 4.8 ND ND 12 290
17-Aug-11 460 6.3 ND ND 14 287
7-Dec-11 390 6.7 ND ND 13 276
19-Jan-12 420 6.4 ND ND 15 228
13-Jun-12 400 5.4 ND ND 11 285
13-Sep-12 410 6 ND ND 13 142
4-0ct-12 390 7 ND ND 14 270
13-Jan-13 282 5.25 ND ND 11.8 221
18-Jun-13 328 3.49 ND ND 13.8 243
12-Sep-13 244 2.13 ND ND 10.3 207
13-Nov-13 204 ND ND ND 9 206
5-Feb-14 220 6.23 ND ND 11.4 200
22-May-14 240 4.73 ND ND 11.5 243
27-Aug-14 204 ND ND ND 7.1 230
29-0ct-14 229 1.04 ND ND 10 252
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
ChJorofotm Caa~bon ChJoromet'ban-e Methylene Nitrate Chlollide TW4 .. 21 (ug/1) Tetr.acbloride (ugll~ Chloride (mg/1) ~mgll} (uflll) (uflll)
9-Mar-16 390 ND ND ND 14.6 452
rn Q)
.2 ca >
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0 LO ~
0 0 ~
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ILGhl0.Fd Cad)on 1\kt!hf.lene Nitrate Chloride~ 4-U DJ ., ru:fitod e .. t)J" :ume c ide u:W'J (udl ('ll~ {u/l} (mg/1) ~)
25-May-05 340 NA NA NA 18.2 NA
31-Aug-05 290 <5 <5 <5 15.7 NA
1-Dec-05 320 <5 <5 <5 15.1 NA
9-Mar-06 390 <10 <10 <10 15.3 236
14-Jun-06 280 <10 <10 <10 14.3 221
20-Jul-06 864 <10 <10 <10 14.5 221
8-Nov-06 350 <1 1.6 <1 15.9 236
28-Feb-07 440 <1 <1 <1 20.9 347
27-Jun-07 740 <1 <1 <1 19.3 273
15-Aug-07 530 <1 <1 <1 19.3 259
10-0ct-07 440 <1 <1 <1 18.8 238
26-Mar-08 1400 <1 <1 <1 39.1 519
25-Jun-08 1200 <1 <1 <1 41.9 271
10-Sep-08 6300 1.3 <1 <1 38.7 524
15-0ct-08 630 <2 <2 <2 36.3 539
11-Mar-09 390 <1 <1 <1 20.7 177
24-Jun-09 730 <1 <1 <1 20.6 177
15-Sep-09 2300 <1 <1 <1 40.3 391
29-Dec-09 380 <1 <1 <1 17.8 175
3-Mar-10 2200 <1 <1 <1 36.6 427
15-Jun-10 540 <1 <1 <1 19 134
24-Aug-10 340 <1 <1 <1 15 130
13-0ct-10 340 <1 <1 <1 16 134
23-Feb-11 1300 ND ND ND 18 114
1-Jun-11 210 ND ND ND 17 138
17-Aug-11 450 ND ND ND 15 120
7-Dec-11 400 ND ND ND 19 174
19-Jan-12 200 ND ND ND 14 36
13-Jun-12 120 ND ND ND 12.8 35
12-Sep-12 940 ND ND ND 7 121
4-0ct-12 330 ND ND ND 14 130
11-Feb-13 10600 3.24 ND ND 58 635
5-Jun-13 12500 3.35 ND ND 50.2 586
3-Sep-13 9640 3.25 ND ND 29.7 487
29-0ct-13 13300 8.09 ND ND 45.2 501
27-Jan-14 12100 6.06 ND 2.83 54.6 598
19-May-14 12400 6.65 ND ND 47.2 614
11-Aug-14 12400 1.9 40 ND 41.5 540
21-0ct-14 12400 3.32 1.61 ND 54.9 596
9-Mar-15 12700 3.77 4.31 ND 69.2 675
8-Jun-15 8050 2.42 3.42 ND 47.1 390
31-Aug-15 7810 ND 5.47 ND 64.7 557
19-0ct-15 7530 ND 5.1 ND 56.1 567
Ohlorofonn Carbon Chloromethane Meth}'len~ Nitntte Chloride TW4·22 Tetrachloride Chloride (ug/1:) '(ue/1) (ug/1) (u~/m (mgll) ~mg/1)
9-Mar-16 6070 ND ND ND 3 1.1 583
tn Cl) :::s 'i >
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9 ~ -ABVIJ-0 ~
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0 0 0 .q-
0 0 0 C\1
0 0 0 0
0 0 0 co
0 0 0 <0
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0
c D.fOf«JJIm Car & Chi Methyl~ e Nitrate-ChfJ ride 4-%3 T: r chfo 'de "~ Ch18ri (uglil) (tlaffl <uglli {~); (mgll) -~
27-Jun-07 <1 <1 <1 <1 <0.1 47
15-Aug-07 <1 <1 <1 <1 <0.1 46
10-0ct-07 <1 <1 <1 <1 <0.1 43
26-Mar-08 <1 <1 <1 <1 <0.1 41
25-Jun-08 <1 <1 <1 <1 <0.05 41
10-Sep-08 <1 <1 <1 <1 <0.05 35
15-0ct-08 <2 <2 <2 <2 <0.05 51
4-Mar-09 <1 <1 <1 <1 <0.1 41
24-Jun-09 <1 <1 <1 <1 <0.1 43
15-Sep-09 <1 <1 <1 <1 <0.1 43
16-Dec-09 <1 <1 <1 <1 <0.1 37
24-Feb-10 <1 <1 <1 <1 <0.1 45
8-Jun-10 <1 <1 <1 <1 <0.1 40
10-Aug-10 <1 <1 <1 <1 <0.1 40
5-0ct-10 <1 <1 <1 <1 <0.1 34
16-Feb-11 ND ND ND ND ND 44
25-May-11 ND ND ND ND ND 44
16-Aug-11 ND ND NO ND ND 41
15-Nov-11 ND NO 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 NO 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
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
0 0
~
~
~
~
~
~
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~
~
~
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(ug/L)
0 0 0 ......
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(~ ~gil) 6ud~ (mg¢Jl) fllij
27-Jun-07 2.6 <1 <1 <1 26.1 770
15-Aug-07 2.2 <1 <1 <1 29 791
10-0ct-07 1.5 <l <1 <1 24.7 692
26-Mar-08 1.5 <1 <1 <l 24.4 740
25-Jun-08 1.4 <1 <1 <1 45.3 834
10-Sep-08 2.9 <1 <1 <1 38.4 1180
15-0ct-08 <2 <2 <2 <2 44.6 1130
4-Mar-09 1.4 <1 <1 <1 30.5 1010
24-Jun-09 1.5 <1 <1 <1 30.4 759
15-Sep-09 1.4 <1 <1 <1 30.7 618
17-Dec-09 1.2 <1 <1 <1 28.3 1080
25-Feb-10 1.3 <1 <1 <1 33.1 896
9-Jun-10 1.7 <1 <1 <1 30 639
24-Aug-10 1.8 <1 <1 <1 31 587
6-0ct-10 1.4 <1 <1 <1 31 522
17-Feb-11 1.8 ND ND ND 31 1100
26-May-11 1.1 ND ND ND 35 1110
17-Aug-11 1.7 ND ND ND 34 967
7-Dec-11 1.2 ND ND ND 35 608
18-Jan-12 ND ND ND ND 37 373
6-Jun-12 ND ND ND ND 37 355
30-Aug-12 1.1 ND ND ND 37 489
3-0ct-12 1.0 ND ND ND 38 405
11-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
11-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
0 c:i en
---~ ~
0 c:i 00
0 c:i .....
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Chl0110f'o11m CM"hon Chtor.ome ane Meth,lene Mate Chloride TW4-l5 1'eilrachl i ' ChJ d {ugtl) {umQJ (ng{J) :(:u,d) (~ (~)
27-Jun-07 <1 <1 <1 <1 17.1 395
15-Aug-07 <1 <1 <1 <1 16.7 382
10-0ct-07 <1 <1 <1 <1 17 356
26-Mar-08 <1 <1 <1 <1 18.7 374
25-Jun-08 <1 <1 <1 <1 22.1 344
10-Sep-08 <1 <1 <1 <1 18.8 333
15-0ct-08 <2 <2 <2 <2 21.3 366
4-Mar-09 <1 <1 <1 <1 15.3 332
24-Jun-09 <1 <1 <1 <1 15.3 328
15-Sep-09 <1 <1 <1 <1 3.3 328
16-Dec-09 <1 <1 <1 <1 14.2 371
23-Feb-10 <1 <1 <1 <1 14.4 296
8-Jun-10 <1 <1 <1 <1 16 306
10-Aug-10 <1 <1 <1 <1 14 250
5-0ct-10 <1 <1 <1 <1 15 312
16-Feb-11 ND ND ND ND 15 315
25-May-11 NO NO ND ND 16 321
16-Aug-11 ND ND ND ND 16 276
15-Nov-11 ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 NO ND ND ND 16 287
11-Sep-12 ND ND ND ND 17 334
3-0ct-12 ND ND ND ND 17 338
11-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
11-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 NO ND 0.837 62.7
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
0
~
~
~
~
~
~
~
~
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~
~
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~
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Od~ Cal'hn. OllfG'r tba Mettt,leue Nitrate Cb1n Ide 'r.W4-26 TetradlletJI!i OJderid'e ~u,gft.) _(1JJ!ll) (ugtll} mt!M'> (mg/1) (mg/1~
15-Jun-10 13 <1 <1 <1 7.9 33
11-Aug-10 5 <1 <1 <1 9 17
6-0ct-10 5.4 <1 <1 <1 9.6 22
22-Feb-11 2.0 ND ND ND 10 30
26-May-11 2.9 ND ND ND 10 15
17-Aug-11 2.8 ND ND ND 11 19
7-Dec-11 5.2 ND ND ND 10 26
18-Jan-12 7.0 ND ND ND 11 17
6-Jun-12 4.1 ND ND ND 12 19
11-Sep-12 4.9 ND ND ND 9 19
3-0ct-12 6.0 ND ND ND 12 19
7-Feb-13 5.0 ND ND ND 12.5 16.6
13-Jun-13 2.1 ND ND ND 13.6 14.5
5-Sep-13 2.8 ND ND ND 11.7 17.6
7-Nov-13 3.4 ND ND ND 15.9 15.9
29-Jan-14 1.4 ND ND ND 14.2 16.9
21-May-14 4.2 ND ND ND 12.5 15.4
11-Aug-14 1.3 ND ND ND 10.8 15
28-0ct-14 2.45 ND ND ND 12.3 14.6
12-Mar-15 2.37 ND ND ND 14.4 14.4
10-Jun-15 6.12 ND 1.17 ND 11.3 14.4
3-Sep-15 4.77 ND ND ND 14.2 14.0
28-0ct-15 3.45 ND ND ND 13.9 13.3
16-Mar-16 1.80 ND ND ND 16.9 13.7
0 N """ 0)
(ug/1)
00 ...... 0 ...... N
~~~=~8 ~ I • II I I I •
Sep-10
Oct-10
Nov-10
Dec-10
Jan-11
Feb-11
Mar-11
Apr-11
May-11
Jun-11
Jul-11
Aug-11
Sep-11
Oct-11
Nov-11
Dec-11
Jan-12
Feb-12
Mar-12
Apr-12
May-12
Jun-12
Jul-12
Aug-12
Sep-12
Oct-12
Nov-12
Dec-12
Jan-13
Feb-13
Mar-13
Apr-13
May-13
Jun-13
Jul-13
Aug-13
Sep-13
Oct-13
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
......
"""
Mar-16~------~--------~------~--------~------~--------~------~
~ .j::o I N en
n :::r
0 ... 0 0' ... 3
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Chloroform Cartiou Clltommetltane Mdl!a)4eae Nitrate Chloride 1'W4-27 Tetr cMGride (ug(l) (ov/1) (ugA~ ChtoTide < u:g:ll) (mg11) (mgJt)
24-Jan-12 9 ND ND ND 24 11
13-Jun-12 ND ND ND ND 41 17
30-Aug-12 ND ND ND ND 37 21
3-0ct-12 ND ND ND ND 36 18
7-Feb-13 ND ND ND ND 31.2 18.8
30-May-13 ND ND ND ND 29.4 20.3
29-Aug-13 ND ND ND ND 27.2 19
6-Nov-13 ND ND ND ND 29.8 21.8
23-Jan-14 ND ND ND ND 31.3 21.8
21-May-14 ND ND ND ND 31.1 20.6
13-Aug-14 ND ND ND ND 27.0 23
23-0ct-14 ND ND ND ND 28.2 24.4
11-Mar-15 ND ND ND ND 26.5 26.2
10-Jun-15 ND ND ND ND 24.0 26.8
2-Sep-15 1.30 ND ND ND 20.9 26.8
28-0ct-15 1.60 ND ND ND 23.5 26.2
16-Mar-16 2.11 ND ND ND 25.0 28.0
Jan-12
Feb-12
Mar-12
Apr-12
May-12
Jun-12
Jul-12
Aug-12
Sep-12
Oct-12
Nov-12
Dec-12
Jan-13
Feb-13
Mar-13
Apr-13
May-13
Jun-13
Jul-13
Aug-13
Sep-13
Oct-13
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0 ...... N
I
~ -~ .,......
~
4
~
0
~
-
-
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4'-,,
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Clllorofomn CarJjon Chi I'Oifte&ane Metltyteae Nitm1e €hlotide TW4-18 (qg/1), Tetracbroritle. {ut/1) Old i.te (rng/1~ (mg/1) (l121J), .(.tO
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
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Chlorof~NR CarbOR Chloromethane Methylene Nitrate Chloride TW4;29 (ug/1) Tetr-acklorkle (ug/1) Chlo ide ~mgll) (mgtl) (uJdl) {u~l:)
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
11-Jun-15 329 ND ND ND 2.95 42.5
3-Sep-15 276 ND ND ND 2.19 47.3
29-0ct-15 631 ND ND ND 2.74 39.8
17-Mar-16 335 ND ND ND 2.92 40.3
Jun-13
Jul-13
Aug-13
Sep-13
Oct-13
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0
.....
0 0
N 0 0
(ug/1)
UJ 0 0
'\
~
~
~
~~
\ v L
""' 0 0
VI 0 0
0'\ 0 0
//
/7"
-...J 0 0
~ ~ I N U)
n ::r
0 ... 0 0' ... 3
< Q)
c tl)
Ill
Chloroform Carbon ChkiroJRe&me Methylene Nitrate Chloride TW4·30 ~ug/1) Tetrachloride (ugll:) Chloride (mg(l) (mgll) (,uf!/:1) CHit),
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
I 1\:)
0
I .......
0
Mar-14
Apr-14
May-14
p
0
Jun-141 Jul-14
Aug-14
Sep-14
D~-14 1 Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
(ug/L)
0
1
!"
0
~1
(,)
0
.j::.
0
(]1
0
(J)
0
~ ~ I w 0
0 :::T
0 ..,
0 -0 ..,
3
< m
2'
CD tn
Chlorotom~ Cittbon Chloromethane Methylene Nitrate Chloride TW4-31 1'.trackleride Otloride {ug/1), .(ufl[d') (ugll) (W!/J) (mgll) (mgll)
19-Jun-13 ND ND NO NO 1.26 28.4
5-Sep-13 NO ND ND NO 1.1 29.4
7-Nov-13 ND ND NO NO 1.33 28
23-Jan-14 ND NO ND ND 1.32 28.5
21-May-14 NO NO ND NO 1.22 26.3
13-Aug-14 NO ND NO NO 1.1 30
28-0ct-14 NO NO NO NO 1.23 30
11-Mar-15 NO NO ND NO 1.33 30.6
10-Jun-15 ND ND NO NO 1.19 31.1
2-Sep-15 NO NO NO NO 0.916 30.4
21-0ct-15 NO NO ND NO 0.953 29.1
16-Mar-16 NO ND NO NO 1.84 31.5
Jun-13
Jul-13
Aug-13
Sep-13
Oct-13
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0
~
~
~
~ -
-
-
~ -
-
-
-
-
-
0 0 0 0
(ug/L)
0
~
0
""""' 0 --... 0
""""' 3
~
Q)
C/)
:::J
0 -0'"
CD
CD
:::J
a.
CD -CD (') -CD a.
:::J
-;
:E ~ I
(,.)
....L
I
I
'
-4 :E ~ I (A) .....
0 :::r 0 2. 0 ..,
3
< !. c CD en
Chloroform Carbon C.hloJTomethane Methylene Nitrate Chloride TW4·32 Tetrachloride (ugll) (lqz/1), (ug/1) Chloride (ug/1) (mg/1) (mgll)
14-Nov-13 ND ND ND ND 4.26 52.1
22-Jan-14 ND ND ND ND 5.11 54.5
21-May-14 ND ND ND ND 5.63 54.9
13-Aug-14 ND ND ND ND 4.2 64
23-0ct-14 ND ND ND ND 2.14 62.6
11-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
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0
-
-
-
(ug/L)
0 0 0 0
()
::::r
0
~ 0 -0
~ 3
::::r
Sl>
(/)
:::J
0 .....
C"'
CD CD
:::J
a.
CD .....
CD
(") .....
CD a.
:::J
-I :E ~ I
VJ
1\)
_. _.
-t :e ol:lo I w 1\)
0 :::J' 0 ""' 9. 0 ""' 3
< m
2" CD 0
Chloroform C;u;,b&R Chloromethane ethr e Nitrate Chloride TW4·33 Tetraehloricle (ug!t) (u1!'fin (ug/1~ Cbledcie (UWJI) (mg/0 ~gil)
14-Nov-13 126 NO NO NO 1.82 47.2
30-Jan-14 124 NO NO NO 2.56 43.5
22-May-14 121 NO NO NO 1.63 46.8
27-Aug-14 104 NO NO NO 1.5 43
29-0ct-14 124 NO NO NO 2.22 44.2
12-Mar-15 134 NO NO NO 1.91 44.2
11-Jun-15 127 NO ND NO 1.62 46.4
3-Sep-15 123 NO NO NO 1.64 53.4
29-0ct-15 129 NO NO NO 1.92 44.5
17-Mar-16 122 NO NO NO 2.13 46.2
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0
1\)
0
.j::.
0
(J)
0
(ug/L)
(X)
0 0 0
_.
1\)
0
4
r
~
1
t
.j::.
0
(J)
0
~ I w w
0 ::::r
0 9. 0 ...
3
< !!. c Cl) en
~hloroform Caliloa CltiOIUled .. Mdh'leae Nitrate Chloride 'F\¥4~34 TetraceMoride cw.rttte (ug!O (ut!A1 (agll) (ltd) (mgll) (mg/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
11-Mar-15 ND ND ND ND 1.21 17.7
10-Jun-15 ND ND ND ND 0.868 17.4
3-Sep-15 ND ND ND ND 0.458 15.1
21-0ct-15 ND ND ND ND 0.368 15.8
16-Mar-16 ND ND ND ND 0.925 17.3
Nov-13
Dec-13
Jan-14
Feb-14
Mar-14
Apr-14
May-14
Jun-14
Jul-14
Aug-14
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
0
-
-
(ug/L)
0 0 0 0 ......
0 ::r
0 ....,.
0 ~ 0 ....,.
3
::r
Jl)
CJ)
:::J
0 .-+
C'"
CD CD
:::J
a.
CD .-+
CD (")
.-+ CD a.
:::J
-I ~ ~ I w ~
--'-
~ ol:lo I (,)
ol:lo
0 :::r 0 ""' 9. 0 ""' 3
< !!!.. c CD 0
Ch1oJtOfotrn Catihon Chloromethane Methylene Nitrate Chloride a'W~·lS Tetrachloride C~g/1) :<uWJ) (ug/1) Chlo.rjde ( ugll) {mg/1) (mg/1)
27-Aug-14 ND ND ND ND 0.2 34
28-0ct-14 ND ND ND ND 0.351 34.1
11-Mar-15 ND ND ND ND 0.436 34.9
10-Jun-15 ND ND ND ND 0.452 35.2
3-Sep-15 ND ND ND ND 0.304 35.9
28-0ct-15 ND ND ND ND 0.419 33.4
16-Mar-16 ND ND ND ND 0.521 35.4
0 Cl)
::::s ca >
E ...
0 0 ...
.2 .c
0
In ('I)
I ~ 1-
LO
('I)
I ~ s .....
c ·--o
Q)
+-' (.)
Q)
+-' Q) -o
c
Q)
Q)
.0
+-' 0 c
~ .c.
E ~
0 -0 ~
0 -.c.
()
(1J6n)
-
9~-qa.:J
-
9~-uer
g~-oaa
g~-AON
g~-das
9k6nv
9kunr
4 g ~ -JBV\1
g~-uer
v~-oaa
v~-AON
-
v~-das
v ~-6nv
0 0 0 0 0
€blo.t:oform C.arbon Ohlorometbane Methylene Nitrate Chloride TW4•36 Tetl'achlol!.ide (ug/1) (ugl]) (ugtl) Chloride (ugll~ (mg/1) (mg/1~
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
U)
CD
::::s ca >
E ...
0 0 ...
.2 .c 0
co ('I)
I ~ ~
<0 ('I)
I ~ s I-
c ·-
"'0 Q)
+""' (.)
Q)
+""' Q)
"'0
c Q)
Q) ..c
+""' 0 c
en
ctS ..c
E ~
0 ~ 0 ~
0 -..c
(.)
0
(1J6n)
g~-qa.:1
9~-uer
9~-oao
9~-das
9~-6nv
9~-unr
9 ~ -JBV\1
9~-uer
17~-oao
17 ~-/\ON
17~-das
17 ~-6nv
-
0 0 0 0
Chloroform Ca111bon ChloJ"omethane Methylene Nitrate O.hloride TW4·37. (ug/1~ Tett3Chlollide (ugl)J Chloride (mg!Q ~mgfl) {ue/l) 1lle/l)
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
t/)
C1)
::::J 'i >
E .... 0 -0 ....
.2 ~ 0
......
('I)
I "':t 3: 1-
0 0 0 LO ('I)
.Vi
0 0 0 0 ('I)
0 0 0 LO C\J
I~
0 0 0 0 0 0 ~ (1J6n) ~
0 0 0 0
0 0 0 LO
0
9~-Jev-.l
9~-qa.::1
9~-uer
9k090
9~-AON
9~-PO
9~-das
9~-6nv
9~-unr
TabL
Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
TABLE L.1
Chloroform Plume Residual Mass
Since Third Quarter 2015
Residual
Plume Mass
Quarter (lbs)
0315 1712
0415 1869
01 16 1946
Notes:
lbs =pounds
H:\718000\may16\chloroform\resid_chl_mass\MassEstTimeSeries.xls: Table L.l
2000 --..... ----1800 --.....
1600
:Q' 1400 -Qj .. "' E ... 1200 Ill w
Ill Ill "' ~
E 1000 ... 0 .... 0 ... 0 ::c 800 u
"'iii ::J ~ 'iii Qj 600 Ill:
400
200
y = 117x + 1608.3
0
Q\.s
o?'V
Q\.s
o.Do 'V
Q\.'0
o.\.'V
*-...
~Series! --linear (Series!) ·-HYDRO TIME SERIES OF RESIDUAL CHLOROFORM MASS
· GEO ESTIMATES
.CHEM,INC. Approved I Date i I Author I Date ' I File Name 'Figure SJS 4/21/16 GEM 4121/16 M•nEsiTim.S...;"·''' l.1
H:\718000\may16\chloroform\resid_chl_mass\MassEstTimeSeries.xls: FL.1 Resid CHL Mass
CHLOROFORM RESIDUAL MASS ESTIMATE DETAILS:
Chloroform Data File: CHL_Surferlnput_Q1_16.xls
Gridding details:
1) kriging parameters: SURFER TM default parameters (point kriging, linear
variogram, slope= 1, no anisotropy [anisotropy= 1], no search constraints [all data
used])
2) minx, max x (UTME[m]): 631900, 633043
3) min y, may y (UTME[m]): 4154240,4155550.64
4) grid spacing in x, y (m): 15.24, 15.24
5) artificial or pseudo-data: none
6) Q4, 2015 (previous quarter) data used at wells: MW-1, MW-2, MW-3, MW-5,
MW-12, MW-15, MW-17 through MW-20, MW-22 through MW-24, MW-27
through MW -29 (all non-detect).
Chloroform residual mass estimate kriged grid files (ascii format):
Ucm1Q16wl.grd: first quarter, 2016 Water Level Grid (ft amsl)
Ucm1Q16bb.grd: first quarter, 2016 Aquifer Base Grid (ft amsl)
Ucm1Q16sat.grd: first quarter, 2016 Saturated Thickness Grid (ft)
Ucm1Q16logchl.grd: first quarter, 2016log of chloroform grid (log of ug/L)
Ucm1Q16chl.grd: first quarter, 2016 Chloroform Concentration Grid (ug/L)
Ucm1Q16ge70.grd: first quarter, 2016 Chloroform Concentration GE 70 Grid (ug/L)
Ucm1Q16volm3.grd: first quarter, 2016 Groundwater Volume Grid (m3)
Ucm1Q16masslb.grd: first quarter, 2016 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii format):
Ucm1Q16wl.dat: first quarter, 2016 Water Level Grid XYZ file (ft amsl)
Ucm1Q16bb.dat: first quarter, 2016 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm1Q16sat.dat: first quarter, 2016 Saturated Thickness Grid XYZ file (ft)
Ucm1Q16logchl.dat: first quarter, 2016 log of chloroform grid XYZ file (log of ug/L)
Ucm1Q16chl.dat: first quarter, 2016 Chloroform Concentration Grid XYZ file (ug!L)
Ucm1Q16ge70.dat: first quarter, 2016 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm1Q16volm3.dat: first quarter, 2016 Groundwater Volume Grid XYZ file (m3)
Ucm1Q16masslb.dat: first quarter, 2016 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate file: Ucm1Q16result.xls
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Thursday, May 19, 2016 7:52 AM
Goble, Phillip
'Dean Henderson'; Harold Roberts; Danny Flannery; David Turk; Scott Bakken; Logan
Shumway
Transmittal of CSV Files White Mesa Mill 2016 Q1 Chloroform Monitoring
1603259-EDD.csv; 1603400-EDD.csv; 1603479-EDD.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 2016, 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 1 t: 303.389.4125
225 Union Blvd., Suite 600
Lakewood, CO 80228
http://www.energyfuels.com
This e-mail is intended for the exclusive use of person(s) mentioned as the recipient(s). This message and any attached files with it are confidential and may
contain privileged or proprietary information. If you are not the intended recipient(s) please delete this message and notify the sender. You may not use, distribute
print or copy this message if you are not the intended recipient(s).
1