DRC-2016-011529 - 0901a06880688536

ywefWiSte Mscisqerpen? 'irui Raqigtiqn Gonirpl'Energy Fuels Resources (USA) Inc.
iIenergyfuels
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.energyfuels.com
2016-01152^
November 17, 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
Re: Transmittal of 3rd 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 3rd Quarter of
2016 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly.
Energy Fuels Resources (USA) Inc.
Kathy Weinel
Quality Assurance Manager
CC: David C. Frydenlund
Harold R. Roberts
David E. Turk
Logan Shumway
Scott Bakken
November 17,2016
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.energyfuel .com
Re: Transmittal of 3rd 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 3rd Quarter of
2016 as required by the Stipulation and Consent Order, UDEQ Docket No. UGW-20-01 as well as two CDs,
that each contains a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
Yours very truly,
c/{rubf )v~
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
3rd Quarter
(July through September)
2016
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
November 17,2016
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 ....................................................................... 12
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions ........... 12
4.1.1 Current Site Groundwater Contour Map ................................................... 12
4.1.2 Comparison of Current Groundwater Contour Maps to Groundwater
Contour Maps for Previous Quarter. ........................................................ 17
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 .................................. 22
4.2.3 Interpretation of Analytical Data .............................................................. 22
5.0 LONG TERM PUMP TEST AT MW-4, MW-26, TW4-19, TW4-20, AND
TW4-4 OPERATIONS REPORT ..................................................................... 25
5.1 Introduction ....................................................................................................... 25
5.2 Pump Test Data Collection ............................................................................... 25
5.3 Water Level Measurements .............................................................................. 26
5.4 Pumping Rates and Volumes ............................................................................ 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 ............................................................. 28
7.1 Long Term Chloroform Plume Control.. .......................................................... 28
7.2 Well Construction, Maintenance and Operation ............................................... 28
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 .......................................................................................................... 29
8.0 CONCLUSIONS AND RECOMMENDATIONS ............................................ 29
9.0 ELECTRONIC DATA FILES AND FORMAT .............................................. 33
10.0 SIGNATURE AND CERTIFICATION ........................................................... 34
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
over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QA/QC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank 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
Tab N Exceedance Notices for the Reporting Period
iii
1.0 INTRODUCTION
The presence of chloroform was initially identified in groundwater at the White Mesa Mill (the
"Mill") as a result of split sampling performed in May 1999. The discovery resulted in the
issuance of State of Utah Notice of Violation ("NOV") and Groundwater Corrective Action
Order ("CAO") State of Utah Department of Environmental Quality ("UDEQ"), Division of
Waste Management and Radiation Control ("DWMRC") Docket No. UGW-20-01, which
required that Energy Fuels Resources (USA) Inc. ("EFRI") submit a Contamination Investigation
Plan and Report pursuant to the provisions of UAC R317-6-6.15(D). In response to the NOV,
EFRI submitted a series of documents outlining plans for investigation of the chloroform
contamination. This plan of action and preliminary schedule was set out in EFRI submittals
dated: September 20, 1999; June 30, 2000; April 14, 2005; and November 29, 2006. EFRI
submitted a draft Groundwater Corrective Action Plan ("GCAP") dated August 22, 2007. The
draft GCAP was reviewed by the Director, who advised EFRI in 2013 that modifications were
required. In an effort to expedite and formalize active and continued remediation of the
chloroform plume, both parties have agreed to the GCAP found in Attachment 1, of the final
Stipulation and Consent Order ("SCO") dated September 14, 2015.
This is the Quarterly Chloroform Monitoring Report for the third quarter of 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 7, 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 ofDI 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 wells is thus established. The list is included with the Field Data
Worksheets under Tab B. Mill personnel start purging with all of the non-detect wells and then
move to the wells with detectable chloroform concentrations staring with the lowest
concentration and proceeding to the wells with the highest concentration. One deviation to this
practice is made for the continuously pumping wells. These wells are sampled throughout the
sampling event and are not sampled in the order of contamination. This practice does not affect
the samples for this reason: the pumping wells have dedicated pumps and there will be no cross-
contamination resulting from the sampling order.
Samples are collected by means of disposable bailer(s) the day following the purging. The
disposable bailer is used only for the collection of a sample from an individual well and disposed
subsequent to the sampling. As noted in the approved QAP, 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 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. lfthe 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 rnl. 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 rnl. 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.
Three trip blanks were provided by A W AL and 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. TW 4-7R). 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
QAJQC evaluation of sample duplicates, a QC Control Limit check for analyses and blanks
including the DIFB and a rinsate sample check. Each evaluation is discussed in the following
sections. Data check tables indicating the results of each test are provided under Tab I.
3.4.1 Field Data QA/QC Evaluation
The QA Manager performs a review of the field recorded parameters to assess their adherence
with QAP requirements. The assessment involved review of two sources of information: the
Field Data Sheets and the Quarterly Depth to Water summary sheet. Review of the Field Data
Sheets addresses well purging volumes and measurement of field parameters based on the
requirements discussed in section 2.2.1 above. The purging technique employed determines the
requirements for field parameter measurement and whether stability criteria are applied. Review
of the Depth to Water data confirms that all depth measurements used for development of the
groundwater contour maps were conducted within a five-day period as indicated by the
measurement dates in the summary sheet under Tab D. The results of this quarter's review of
field data are provided under Tab I.
Based upon the review of the field data sheets, the purging and field measurements were
completed in conformance with the QAP requirements. A summary of the purging techniques
employed and field measurements taken is described below:
Purging Two Ca ing Volume with Stable Field Parameters (withinlO% RPD)
Wells TW4-5, TW4-7, TW4-8, TW4-9, TW4-13, 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 Dryness and Stability of a Limited List of Field Parameters
Wells TW4-3, TW4-6, TW4-10, 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 of pH, conductivity and temperature
were taken. The samples were then collected, and another set of measurements of pH,
conductivity and temperature were taken. Stabilization of pH, conductivity and temperature are
required within 10% RPD under the QAP, Revision 7.2. The QAP requirements for stabilization
were met.
Continuously Pumped WelJs
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 MW-4, TW4-2, TW4-4, TW4-5, TW4-7, TW4-8, TW4-9, TW4-13, MW-26, TW4-16,
MW-32, TW4-18, TW4-21, TW4-23, TW4-24, TW4-25, 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
9
interference and/or sample dilution. In these cases, the reported value for the analyte was higher
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 included
in Tab I.
3.4.9 Rinsate Sample Check
Rinsate blank sample checks are provided in Tab I. The rinsate blank sample concentration
levels were compared to the QAP requirements i.e., that rinsate sample concentrations be one
order of magnitude lower than that of the actual well. 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
10
control limits, (6) blanks are within QC limits, (7) special sample preparation and analytical
requirements have been met, and (8) documentation is complete. In addition to other laboratory
checks described above, EFRI's QA Manager rechecks QC samples and blanks (items (5) and
(6)) to confirm that the percent recovery for spikes and the relative percent difference for spike
duplicates are within the method-specified acceptance limits, or that the case narrative
sufficiently explains any deviation from these limits. Results of this quantitative check are
provided in Tab I.
The lab QA/QC results met these specified acceptance limits except as noted below.
The QAP Section 8.1.2 requires that a Matrix Spike/Matrix Spike Duplicate ("MS/MSD") pair
be analyzed with each analytical batch. The QAP does not specify acceptance limits for the
MS/MSD pair, and the QAP does not specify that the MS/MSD pair be prepared on EFRI
samples only. Acceptance limits for MS/MSDs are set by the laboratories. The review of the
information provided by the laboratories in the data packages verified that the QAP requirement
to analyze an MS/MSD pair with each analytical batch was met. While the QAP does not require
it, the recoveries were reviewed for compliance with the laboratory established acceptance limits.
The QAP does not require this level of review, and the results of this review are provided for
information only.
The information from the Laboratory QA/QC Summary Reports indicates that the MS/MSDs
recoveries and the associated RPDs for the samples were within acceptable laboratory limits for
the regulated compounds 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 QA/QC 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 QA/QC Summary Reports indicates that the Laboratory
Control Samples (the "LCS") recoveries were within acceptable laboratory limits for the LCS
compounds except as noted below.
The information from the Laboratory QA/QC Summary Reports indicates that the LCS
recoveries for the samples were within acceptable laboratory limits for the regulated compounds
as indicated in Tab I.
11
4.0 INTERPRETATION OF DATA
4.1 Interpretation of Groundwater Levels, Gradients and Flow Directions.
4.1.1 Current Site Groundwater Contour Map
The water level contour maps (See Tab D) indicate that perched water flow ranges from
generally southwesterly beneath the Mill site and tailings cells to generally southerly along the
eastern and western margins of White Mesa south of the tailings cells. Perched water mounding
associated with the wildlife ponds locally changes the generally southerly perched water flow
patterns. For example, northeast of the Mill site, mounding associated with formerly used
wildlife ponds disrupts the generally southwesterly flow pattern, to the extent that locally
norther! y flow occurs near MW -19 and PIEZ-1. The impact of the mounding associated with the
northern ponds, to which water has not been delivered since March 2012, is diminishing and is
expected to continue to diminish as the 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, resulted in changing
conditions that were expected to impact constituent concentrations and migration rates within the
plumes. Specifically, past recharge from the ponds helped limit many constituent concentrations
within the plumes by dilution while the associated groundwater mounding increased hydraulic
gradients and contributed to plume migration. Since use of the northern ponds was discontinued
in March, 2012, increases in constituent concentrations in many wells, and decreases in hydraulic
gradients within the plumes, are attributable to reduced recharge and the decay of the associated
groundwater mound. EFRI and its consultants anticipated these changes and discussed these and
other potential effects during discussions with DWMRC in March 2012 and May 2013.
The impacts associated with cessation of water delivery to the northern ponds were expected to
propagate downgradient (south and southwest) over time. Wells close to the ponds were
generally expected to be impacted sooner than wells farther downgradient of the ponds.
Therefore, constituent concentrations were generally expected to increase in downgradient wells
close to the ponds before increases were detected in wells farther downgradient of the ponds.
Although such increases were anticipated to result from reduced dilution, the magnitude and
timing of the increases were anticipated to be and have been difficult to predict due to the
complex permeability distribution at the site and factors such as pumping and the rate of decay of
the groundwater mound. Because of these complicating factors, some wells completed in higher
permeability materials were expected to be impacted sooner than other wells completed in lower
permeability materials even though the wells completed in lower permeability materials were
closer to the ponds.
In general, chloroform and nitrate concentrations within and in the vicinity of the chloroform
plume appear to have been impacted to a greater extent than nitrate concentrations within and
adjacent to the nitrate plume. This behavior is reasonable considering that the chloroform plume
is generally more directly downgradient of and more hydraulically connected (via higher
permeability materials) to the wildlife ponds.
12
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.
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 was anticipated to be more evident at
chloroform pumping wells MW-4, MW-26, TW4-4, TW4-19, and TW4-20; nitrate pumping
wells TW4-22, TW4-24, TW4-25, and TWN-2; and non-pumped wells adjacent to the pumped
wells. Impacts were also expected to occur over time at wells added to the chloroform pumping
network during the first quarter of 2015 (TW4-1, TW4-2, TW4-11), and to those added during
the second quarter of 2015 (TW4-21 and TW4-37). The overall impact was expected to be
generally higher constituent concentrations in these wells over time until mass reduction
resulting from pumping and natural attenuation eventually reduces concentrations. Short-term
changes in concentrations at pumping wells and wells adjacent to pumping wells are also
expected to result from changes in pumping conditions.
In addition to changes in the flow regime caused by wildlife pond recharge, perched flow
directions are locally influenced by operation of the chloroform and nitrate pumping wells. Well
defined cones of depression 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 during routine monitoring.
As discussed above, variable permeability conditions likely contribute to the lack of a well-
defined cone of depression near chloroform pumping well TW 4-4. Changes in water levels at
wells immediately south and southeast (downgradient) ofTW4-4 resulting from TW4-4 pumping
are expected to be muted because TW4-4 is located at a transition from relatively high to
13
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
complicated by the general, long-term increase in water levels in this area attributable to past
wildlife pond recharge.
Between the fourth quarter of 2007 and the fourth quarter of 2009 (just prior to the start of TW 4-
4 pumping), water levels at TW4-4 and TW4-6 increased by nearly 2.7 and 2.9 feet at rates of
approximately 1.2 feet/year and 1.3 feet/year, respectively. However, 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 TW4-6 is within the hydraulic influence of TW4-4.
Since the fourth quarter of 2013, water levels in all wells currently within the chloroform plume
south of TW4-4 (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, until the first quarter of 2016, water level trends were generally upward in
many wells located at the margin of the chloroform plume southeast of TW 4-4 (TW 4-14, TW 4-
27, TW4-30, and TW4-31). These wells appeared to be responding to past wildlife pond
recharge and expansion of the groundwater mound. Since the first quarter of 2016, however,
water levels at these wells appear to be stabilizing.
These spatially variable water level trends likely result from pumpmg conditions, the
permeability distribution, and distance from the wildlife ponds. Wells that are relatively
hydraulically isolated (due to completion in lower permeability materials or due to intervening
lower permeability materials) and that are more distant from pumping wells and the wildlife
ponds, are expected to respond more slowly to pumping and reduced recharge than wells that are
less hydraulically isolated and are closer to pumping wells and the wildlife ponds. Wells that are
more hydraulically isolated will also respond more slowly to changes in pumping.
The lack of a well-defined cone of depression at TW 4-4 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 5533.3 feet above mean sea level
["ft amsl"]), is more than 2 feet lower than the water level at TW4-6 (approximately 5535.5 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 TW4-14 and downgradient well TW4-27 (installed south of
TW4-14 in the fourth quarter of 2011) were similar (within 1 to 2 feet) until the third quarter of
2014; both appeared anomalously low. The current quarterly water level at TW4-27
(approximately 5528.3 ft amsl) is nearly 5 feet lower than the water level at TW4-14 (5533.3 ft
amsl). Recent increases in water level differences between 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
14
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 [!giL 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).
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 (5534.1
feet amsl) is, however, lower than water levels at adjacent wells TW4-6 (5535.5 feet amsl), and
TW4-23 (5537.1 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 ofTW4-27 (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 current quarter chloroform concentrations of
approximately 5 [!giL and 2.8 [!giL, respectively. In addition, the relatively low permeability and
comparative hydraulic isolation of these wells reduces their responses to changing hydraulic
conditions resulting from pumping and reduced wildlife pond recharge.
15
Chloroform exceeding 70 ~-tgiL 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
TW 4-26, 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 TW4-29 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.
Chloroform during the current quarter was detected at approximately 6.8 ~-tgiL 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 f.tg/L at TW4-29 is bounded by concentrations below 70 ~-tgiL 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 ofTW4-29.
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 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 TW4-4 pumping at the distal end of the plume is consistent with generally
decreasing water levels at both TW4-29 and TW4-33.
16
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 second quarter of 2016, as submitted with
the Chloroform Monitoring Report for the second quarter of 2016, is attached under Tab E.
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.
A comparison of the water table contour maps for the current quarter (third quarter of 2016) to
the water table contour maps for the previous quarter (second quarter of 2016) indicates similar
patterns of drawdowns associated with the pumping wells. Nitrate pumping wells TW 4-22,
TW4-24, TW4-25, and TWN-2 were brought into operation during the first quarter of 2013 and
their impact on water level patterns has been apparent since the fourth quarter of 2013. Although
a large expansion in capture occurred with the addition of chloroform pumping wells TW 4-1,
TW4-2, TW4-11, TW4-21 and TW4-37 in 2015, a significant cone of depression associated with
TW4-37 is not yet evident.
Drawdowns at chloroform pumping well MW-26 and nitrate pumping well TW4-22 increased by
more than 2 feet this quarter, with the drawdown at TW4-22 increasing by a substantial 26 feet.
Water level changes at other nitrate and chloroform pumping wells were less than 2 feet,
although both increases (decreases in drawdown) and decreases (increases in drawdown)
occurred. Water level fluctuations at pumping wells typically occur in part because of
fluctuations in pumping conditions just prior to and at the time the measurements are taken. The
reported water level for chloroform pumping well TW 4-11 is below the depth of the Brushy
Basin contact this quarter. Although both increases and decreases in drawdown occurred in
pumping wells, the overall apparent capture of the combined pumping system is larger than last
quarter primarily due to the relatively large increase in drawdown at TW4-22.
As discussed in Section 4.1.1, pumping at chloroform well TW4-4, 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.
Reported water level decreases of up to 0.75 feet at Piezometers 1, 2, 3A, 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 0.67 feet and 0.72 feet at Piezometers 4 and 5,
respectively, may also result from reduced recharge at the southern wildlife pond.
The reported water level at MW-20 increased by approximately 3.5 feet, and water levels at
MW-37 and TWN-19 decreased by approximately 3.1 and 3.5 feet, respectively. Water level
17
variability at MW-20 and MW-37 likely results from low permeability and variable intervals
between purging/sampling and water level measurement. The decrease at far upgradient well
TWN-19 compensates for the reported increase last quarter.
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.
4.1.3 Hydrographs
Attached under Tab F are hydrographs showing groundwater elevation in each chloroform
contaminant investigation monitor well over time.
4.1.4 Depth to Groundwater Measured and Groundwater Elevation
Attached under Tab F are tables showing depth to groundwater measured and groundwater
elevation over time for each of the wells listed in Section 2.1.1 above.
4.1.5 Evaluation of the Effectiveness of Hydraulic Capture
Perched water containing chloroform has been removed from the subsurface by operating
chloroform pumping wells MW-4, MW-26, 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 upgradient 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 TW 4-4. 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 and MW-26. Cones of
depression are also typically evident at TW4-19 and TW4-20, but are less apparent this quarter
due to the large increase in drawdown at nearby nitrate pumping well TW4-22. MW-4, MW-26,
TW4-19 and TW4-20 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; a cone of depression is also
evident 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 clearly evident. The lack of a well-defined cone of depression
near TW4-37 likely results from relatively recent start-up and close proximity to other pumping
18
wells. Overall, 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 TW4-4 became operational in 2010, the drawdown
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 TW 4-14.
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, MW-26,
TW4-1, TW4-2, and TW4-21 decreased by approximately 1.4, 2.5, 1.4, 1.6, and 1.0 feet
respectively, while the water levels in chloroform pumping wells TW4-4, TW4-11, TW4-19,
TW4-20 and TW4-37 increased by approximately 0.9, 0.8, 0.5, 1.0, and 0.3 feet, respectively.
The water levels in nitrate pumping wells TW4-22 and TW4-24 decreased by approximately 26
feet and 0.3 feet, respectively, while the water levels in nitrate pumping wells TW4-25 and
TWN-2 increased by approximately 0.4 and 1.4 feet, respectively. Overall, the apparent capture
of the combined pumping systems has increased compared to last quarter, primarily due to the
relatively large increase in drawdown at TW4-22.
The capture associated with nitrate pumping wells and chloroform pumping wells added in 2015
is expected to increase over time as water levels continue to decline due to cessation of water
delivery to the northern wildlife ponds and continued pumping. Slow development of hydraulic
capture in the vicinities of many wells is consistent with and expected based on the relatively low
permeability of the perched zone at the site.
The hydraulic capture effectiveness of both chloroform and nitrate pumping systems depends to
some extent on the continued productivity of chloroform and nitrate pumping wells. Decreases in
productivity have been noted since the third quarter of 2014 in chloroform pumping well TW 4-
19 and nitrate pumping well TW4-24. The impact of reduced productivity of these wells on
chloroform capture was discussed in Attachment N (Tab N) of the third quarter, 2015 report. The
report also included a discussion of the effectiveness of chloroform pumping on chloroform
capture. 'Background' flow through the chloroform plume was calculated in Attachment N as
approximately 3.3 gpm. A more refined 'background' flow calculation of 3.4 gpm was provided
in the CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah).
Pumping from wells within and immediately adjacent to the chloroform plume during the current
quarter (from wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20,
TW4-21, TW4-22, TW4-24, and TW4-37) is approximately 4.5 gpm. This calculation is based
on the total volume pumped by these wells over the 90 day quarter (581,560 gallons) and
accounts for times that the pumps are off due to insufficient water columns in the wells. Pumping
from these wells exceeds the calculated background flow by 1.1 gpm or 32%, and is considered
adequate at the present time even with the reduced productivities of some wells. In addition,
because of continued reductions in saturated thicknesses and hydraulic gradients resulting from
reduced wildlife pond recharge, 'background' flow through the plume is expected to continue to
diminish, thereby reducing the pumping needed to control the plume.
19
Chloroform concentrations at many locations have been or appear to be affected by changes
associated with reduced dilution from the wildlife ponds and nitrate pumping. For example,
increases in chloroform at TW4-22 and TW4-24 after these wells were converted to nitrate
pumping wells are attributable to westward migration of chloroform from the vicinity of TW 4-20
toward these wells. The increase in concentration at TW4-8 from non-detect to 100 [!giL in the
first quarter of 2014 (and to 522 [!giL this quarter) is likely related to reduced dilution. Although
the chloroform concentration in TW4-6 decreased from 486 [!giL to 433 [!giL this quarter,
concentrations at TW4-6 have increased from approximately 10 [!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 [.tg/L between the first quarter of
2009 and the third quarter of 2010, and remained below 70 [.tg/L 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
mass removal and lowers hydraulic gradients, thereby reducing the rate of downgradient
chloroform migration and allowing natural attenuation to be more effective. Pumping at TW4-4
was implemented during the first quarter of 2010 to improve capture downgradient of TW4-4 to
the extent allowable by the lower productivity conditions present in this area. The beneficial
effect of pumping TW 4-4 is demonstrated by the net decreases in TW 4-6 chloroform
concentrations from 1,000 [!giL to 10.3 [!giL, and in TW4-26 from 13 [.tg/L to 4.2 [!giL, 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 TW4-6 can be demonstrated to be within the hydraulic capture of TW4-4,
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 [!giL in the second
quarter of 2004 to less than 70 [!giL by the fourth quarter of 2005, and maintained concentrations
below 70 [!giL until the second quarter of 2014, even though TW4-16 appears to be beyond the
hydraulic capture of MW-26. Furthermore, the overall hydraulic capture of the chloroform
pumping system has expanded since initiation of pumping at wells TW4-1, TW4-2, TW4-11
TW4-21 and TW4-37 during the first half of 2015. Operation of these additional wells may have
reversed the increase in concentration at TW4-16 which dropped from 387 [!giL in the fourth
quarter of 2014 to less than 70 [!giL in the second quarter of 2015. Chloroform at TW4-16 was
detected at 49 [!giL this quarter.
20
Chloroform exceeding 70 !!giL was detected in the second quarter of 2013 at relatively recently
installed well TW4-29, located south of TW4-27 and east of TW4-26. With respect to historic
groundwater flow directions implied by historic groundwater elevations in this area, TW4-29 is
positioned generally cross-gradient of TW4-4 and TW4-6. As discussed in Section 4.1.1,
chloroform detected at TW4-29 may have migrated around the low permeability area defined by
TW4-27, TW4-14 and TW4-36. The apparent migration pathway from TW4-4 to TW4-29 is
consistent with chloroform exceeding 70 !!giL detected in the fourth quarter of 2013 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
TW 4-4 pumping. Such behavior is expected by analogy with the decreases in chloroform
concentrations at TW4-6 and TW4-26 that occurred once TW4-4 pumping began. However,
concentrations at both TW4-29 and TW4-33 were relatively stable (rather than decreasing) for
several quarters after installation. Concentrations at TW4-29 appear to be on an upward trend
since the third quarter of 2014. As discussed in Section 4.1.1, although decreasing concentration
trends at both wells are eventually expected to occur, relatively stable chloroform at TW4-33 and
increases in concentration at TW4-29 since the third quarter of 2014 suggest that chloroform
migration has been arrested at TW4-33 by TW4-4 pumping and that increasing chloroform at
downgradient well TW4-29 results from a remnant of the plume that continues to migrate
downgradient (toward TW4-30, which bounds to plume to the east). The influence of TW4-4
pumping at the distal end of the plume is consistent with generally decreasing water levels at
both TW4-29 and TW4-33.
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 TW 4-8.
4.2 Review of Analytical Results
4.2.1 Current Chloroform Isoconcentration Map
Included under Tab J of this Report is a current chloroform isoconcentration map for the Mill
site. Details of the gridding procedure used to generate the chloroform isoconcentration map
(consistent with Part III.B.2.a through Part III.B.2.c ofthe GCAP) are provided in Tab L.
21
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 and TW4-33;
b) Chloroform concentrations decreased by more than 20% in the following wells
compared to last quarter: TW4-4, TW4-5, TW4-16, TW4-19, TW4-20, TW4-22, TW4-
24, and TW4-26;
c) Chloroform concentrations have remained within 20% in the following wells compared
to last quarter: MW-4, TW4-1, TW4-2, TW4-6, TW4-7, TW4-8, TW4-9, TW4-10,
TW4-11, TW4-14, TW4-18, TW4-21, TW4-27, TW4-29, TW4-30, 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, TW4-4,
TW4-5, TW4-16, TW4-19, TW4-20, TW4-22, TW4-24, TW4-26, and TW4-33 had changes in
concentration greater than 20%. Of these, MW -26, TW 4-4, TW 4-19 and TW 4-20 are chloroform
pumping wells; and TW4-22 and TW4-24 are nitrate pumping wells. TW4-5 is located just
outside the plume margin and near chloroform pumping wells TW4-19 and TW4-20; 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 and TW4-33 is located just
within the southeast boundary of the plume. Fluctuations in concentrations at these wells are
expected based on their locations at the plume margins.
Chloroform pumping wells TW4-19, TW4-20 and TW4-37, and nitrate pumping well TW4-22,
had the highest detected chloroform concentrations of 6,040, 23,600, 15,900, and 5,840 !!giL,
22
respectively. Since last quarter, the chloroform concentration in TW4-19 decreased from 12,600
[!giL to 6,040 [!giL; TW4-20 decreased from 33,700 [!g/L to 23,600 [!giL; TW4-37 decreased
from 16,200 to 15,900 [!giL; and the concentration in nearby pumping well TW4-21 decreased
from 545 to 456 [!giL. The chloroform concentration in nitrate pumping well TW4-22 decreased
from 8,570 [!g/L to 5,840 [!giL. The chloroform concentration in nitrate pumping well TW4-24
decreased from 69.6 to 17.8 [!g/L and remains just 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 595 [!giL to 522 [!giL. TW4-8 is located immediately east of
chloroform pumping well MW-4, where chloroform was detected at a concentration of 1,430
[!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 (5 [!giL).
Chloroform at relatively recently installed well TW 4-29 (located at the southern tip of the plume,
to the east of TW4-26 and to the south of TW4-27) increased from 366 [!g/L to 401 [!g/L.
However, chloroform at TW4-30, located immediately downgradient of TW4-29, decreased
from approximately 7.2 [!giL to approximately 6.8 [!g/L, and chloroform at TW4-14 and TW4-
27 decreased from approximately 6.2 [!giL to 5 [!giL, and from approximately 3.2 [!g/L to
approximately 2.8 [!g/L, respectively. These decreases in concentration and the stabilization of
water levels at these wells suggest that the ongoing, but slow, downgradient migration of
chloroform at these locations may be slowing. Chloroform at TW4-29 is bounded to the north by
TW4-27 (2.8 [!giL), to the east by TW4-30 (6.8 [!g/L), to the southeast by TW4-35 (non-detect),
to the south by TW4-34 (non-detect), and to the west by TW4-26 (4.4 [!giL).
Chloroform at relatively recently installed well TW4-33 (located between TW4-4 and TW4-29)
showed an increase in concentration, from approximately 96 [!giL to 121 f,lg/L. Chloroform at
TW4-33 is bounded to the north by TW4-14 (5 f,tg/), to the east by TW4-27 (2.8 f,lg/L), to the
west by TW4-23 (non-detect), and to the south and west by TW4-26 (4.4 f,tg/L). This
chloroform distribution indicates that the plume southeast of TW 4-4 is very narrow compared to
more upgradient locations.
The chloroform concentration in TW4-6 decreased from 486 f,tg/L to 433 f,tg/L, and remains
within the chloroform plume boundary. Concentrations at TW4-6 exceeded 70 [!giL from the
first quarter of 2009 through the third quarter of 2010, and then remained below 70 f,tg/L 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 [!g/L
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
23
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.
Although changes in concentration have occurred in wells within the chloroform plume, the
boundaries of the plume have not changed significantly since the last quarter, except for slight
contractions near TW4-16 and TW4-24 (both outside the plume this quarter). The chloroform
concentration at TW4-9 increased slightly from approximately 76 [!giL to 77 [!giL, and remains
just within the plume. Except for the fourth quarter of 2014, TW4-9 was outside the plume prior
to the first quarter of 2016. The plume boundary remains between TW4-9 and TW4-12 (which is
non-detect for chloroform and cross-gradient of TW4-9). The increase at TW4-9 is attributable to
reduced recharge (and dilution) from the northern wildlife ponds.
Nitrate pumping generally caused the western boundary of the northern portion of the
chloroform plume to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-
24 has been both inside and outside the plume and remains outside the plume this quarter, likely
due to initiation of TW4-37 pumping in the second quarter of 2015 and reduced productivity at
TW4-24 (since the third quarter of 2014). Since the second quarter of 2014, generally increased
concentrations at TW4-6 and TW4-16 (both of which were within the chloroform plume in the
past) indicate that the plume boundary migrated to the southwest and re-incorporated both wells.
TW4-6 remains within the plume this quarter and TW4-16 (with a concentration decrease from
approximately 93 [!giL to 49 [!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, TW4-11, TW4-21 and TW4-37
to the chloroform pumping network in the first half of 2015 is expected to have a beneficial
impact. Generally reduced concentrations at TW4-6 (since the first quarter of2015) and TW4-16
(since the fourth quarter of 2014) after previous increases are likely the result of initiation of
TW4-1, TW4-2, and TW4-11 pumping.
24
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 TW4-21 and TW4-37 on June 9, 2015.
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
25
• 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.
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.
Unless specifically noted below, no operational problems were observed with the well or
pumping equipment during the quarter.
5.5 Mass Removed and Plume Residual Mass
Chloroform removal was estimated as of the first quarter 2007. Since that estimation, the mass
removed by well for each quarter has been compiled in Table G-2, which shows the pounds of
chloroform that have been removed to date. The mass of chloroform removed from the plume
this quarter is approximately 24.7 lb., which is 37% less than the approximately 39.4lb. removed
last quarter. The lower rate of mass removal is attributable to lower chloroform concentrations in
pumping wells, and reduced pumping rates this quarter compared to last quarter.
The residual mass of chloroform within the plume is estimated as 1,718 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
26
Method"). This is approximately 543 lb. less than last quarter's estimate of 2,261 lb. and is
attributable to lower average chloroform concentrations within the plume and slight contraction
of the plume near TW4-16 and TW4-24. As per Part III.B.2 of the GCAP, electronic files used in
calculating the mass estimate are provided with this report. Details of the procedure are provided
in Tab L.
The residual mass is plotted in Figure L.l. Since the third quarter of 2015 the trend is upward,
although the current quarter's estimate of 1,718 lb is about the same as the third quarter 2015
estimate of 1,712 lb. Subsequent residual plume mass estimates will be calculated quarterly,
added to the graph, and the trendline updated as per Part III.B.3 of the GCAP.
As discussed in the CACME Report, the calculated chloroform mass has been generally
increasing since the cessation of water delivery to the two northern wildlife ponds in the first
quarter of 2012. These ponds are located immediately upgradient of the chloroform plume. The
calculated mass has increased as the plume area and the average concentrations within the plume
have increased. The increases in plume area and average concentrations are both attributable to
reduced recharge and reduced dilution from chloroform-free wildlife pond seepage.
The decrease in the residual mass estimate this quarter suggests stabilization. In addition, the
general increase in residual mass estimates since the first quarter of 2012 was accompanied by a
general increase in the rate of mass removed per quarter by pumping, in particular since the
addition of 5 new pumping wells in the first half of 2015. Furthermore, although the pumping
system is not designed to hydraulically capture the entire plume, the proportion of the mass of
the plume under capture has historically been large. The proportion of the mass of the plume
under capture during the fourth quarters of 2012, 2013, 2014, and 2015 ranged from
approximately 84% to 93%. The approximate proportion of the mass of the plume under capture
this quarter is a relatively large 97%. The increase over last quarter's estimate of 91% is
attributable primarily to the increase in apparent capture near TW4-22.
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.
27
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
[.tg/L (Tab J). The plume is bounded to the north by TW4-25 (non-detect); to the west and
southwest by MW-31 (non-detect), MW-32 (non-detect), TW4-23 (non-detect), TW4-24 (69.6
[.tgiL), and TW4-26 (approximately 8.2 [.tg/L); to the east by TW4-3 (non-detect), TW4-5
(approximately 14 [.tg/L), TW4-12 (non-detect), TW4-13 (non-detect), TW4-14 (approximately
6.2 [.tg/L), TW4-18 (approximately 60 [.tg/L), TW4-27 (approximately 3.2 [.tgiL), TW4-30
(approximately 7.4 [.tgiL), 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.
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. An Exceedance Notice and Plan
and Time Schedule for TW4-9 were submitted on August 18, 2016 and September 9, 2016
respectively. The Plan and Time Schedule was approved by DWMRC by letter dated September
19, 2016. Because this exceedance is being addressed no further Exceedance Notices or Plans
are required.
28
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 1,718 lb. using the
methodology described in Appendix A of the GCAP ("Chloroform Plume Mass Calculation
Method"). This is approximately 543 lb. less than last quarter's estimate of 2,261 lb. and is
attributable to lower average chloroform concentrations within the plume and slight contraction
of the plume near TW4-16 and TW4-24. The mass of chloroform removed from the plume this
quarter is approximately 24.7 lb., which is 37% less than the approximately 39.4lb. removed last
quarter. The lower rate of mass removal is attributable to lower chloroform concentrations in
pumping wells and reduced pumping rates this quarter compared to 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
!lgiL. 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 was 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, or 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 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 larger than last quarter, with the increase attributable to the larger
drawdown and apparent increase in capture at TW4-22.
'Background' flow through the chloroform plume was calculated as approximately 3.4 gpm as
presented in CACME Report (See HGC, March 31, 2016: Corrective Action Comprehensive
Monitoring Evaluation Report, White Mesa Uranium Mill, Near Blanding, Utah). Pumping from
wells within and immediately adjacent to the chloroform plume during the current quarter (from
wells MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21, TW4-22,
TW4-24, and TW4-37) is approximately 4.5 gpm, which exceeds the calculated background flow
by 1.1 gpm or 32%, and is considered adequate at the present time.
29
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, TW4-4, TW4-5, TW4-16, TW4-19, TW4-20, TW4-22, TW4-24, TW4-26, and
TW4-33. Of these, MW-26, TW4-4, TW4-19 and TW4-20 are chloroform pumping wells; and
TW4-22 and TW4-24 are nitrate pumping wells. TW4-5 is located just outside the plume margin
and near chloroform pumping wells TW4-19 and TW4-20; 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 and TW4-33 is located just
within the southeast boundary of the plume. Fluctuations in concentrations at these wells are
expected based on their locations at the plume margins.
Chloroform pumping wells TW4-19, TW4-20 and TW4-37, and nitrate pumping well TW4-22,
had the highest detected chloroform concentrations of 6,040, 23,600, 15,900, and 5,840 [lg!L,
respectively. Since last quarter, the chloroform concentration in TW4-19 decreased from 12,600
[lg!L to 6,040 [lg!L; TW4-20 decreased from 33,700 [lg!L to 23,600 [lg!L; TW4-37 decreased
from 16,200 to 15,900 [lg/L; and the concentration in nearby pumping well TW4-21 decreased
from 545 to 456 [lg!L. The chloroform concentration in nitrate pumping well TW4-22 decreased
from 8,570 [lg!L to 5,840 [lg!L. The chloroform concentration in nitrate pumping well TW4-24
decreased from 69.6 to 17.8 [lg/L and remains just 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 595 [lg/L to 522 [lg!L. TW4-8 is located immediately east of
chloroform pumping well MW-4, where chloroform was detected at a concentration of 1,430
[lg!L. From the first quarter of 2005 through the fourth quarter of 2013, the plume boundary
remained between MW-4 and TW4-8. The occurrence of elevated chloroform at TW4-8 is likely
related to its location along the eastern plume boundary immediately east of pumping well MW-
4. Changes in the plume boundary near TW 4-8 are expected to result from changes in pumping
and reduced dilution resulting from cessation of water delivery to the northern wildlife ponds.
Chloroform at TW4-8 is bounded to the north by TW4-3 (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 (5 [lg!L).
Detectable chloroform concentrations at TW4-14 (since the fourth quarter of 2014) and TW4-27
(since the third quarter of 2015) are consistent with continued, but slow, downgradient migration
of chloroform from the distal end of the plume (defined by TW4-29 and TW4-33) into the low
permeability materials penetrated by TW4-14 and TW4-27.
30
Chloroform at relatively recently installed well TW4-29 (located at the southern tip of the plume,
to the east of TW4-26 and to the south of TW4-27) increased from 366 [!giL to 401 [!giL.
However, chloroform at TW4-30, located immediately downgradient of TW4-29, decreased
from approximately 7.2 [!giL to approximately 6.8 [!giL, and chloroform at TW4-14 and TW4-
27 decreased from approximately 6.2 [!giL to 5 [!giL, and from approximately 3.2 [!giL to
approximately 2.8 [!giL, respectively. These decreases in concentration and the stabilization of
water levels at these wells suggest that the ongoing, but slow, down gradient migration of
chloroform at these locations may be slowing. Chloroform at TW4-29 is bounded to the north by
TW4-27 (2.8 [!giL), to the east by TW4-30 (6.8 [!giL), to the southeast by TW4-35 (non-detect),
to the south by TW4-34 (non-detect), and to the west by TW4-26 (4.4 [!giL).
Chloroform at relatively recently installed well TW4-33 (located between TW4-4 and TW4-29)
showed an increase in concentration, from 96 [!giL to 121 [!giL. Chloroform at TW4-33 is
bounded to the north by TW4-14 (5 [-tg/), to the east by TW4-27 (2.8 [!giL), to the west by TW4-
23 (non-detect), and to the south and west by TW4-26 (4.4 [!giL). This chloroform distribution
indicates that the plume southeast of TW 4-4 is very narrow compared to more up gradient
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 slight
contractions near TW4-16 and TW4-24 (both outside the plume this quarter). The chloroform
concentration at TW4-9 increased slightly from approximately 76 [!giL to 77 [!giL, and remains
just within the plume. Except for the fourth quarter of 2014, TW 4-9 was outside the plume prior
to the first quarter of 2016. The plume boundary remains between TW4-9 and TW4-12 (which is
non-detect for chloroform and cross-gradient of TW4-9). The increase at TW4-9 is attributable to
reduced recharge (and dilution) from the northern wildlife ponds.
Nitrate pumping generally caused the western boundary of the northern portion of the
chloroform plume to migrate to the west toward TW4-24. Since the first quarter of 2014, TW4-
24 has been both inside and outside the plume and remains outside the plume this quarter, likely
due to initiation of TW4-37 pumping in the second quarter of 2015 and reduced productivity at
TW4-24 (since the third quarter of 2014). Since the second quarter of 2014, generally increased
concentrations at TW4-6 and TW4-16 (both of which were within the chloroform plume in the
past) indicate that the plume boundary migrated to the southwest and re-incorporated both wells.
TW4-6 remains within the plume this quarter and TW4-16 (with a concentration decrease from
approximately 93 [!giL to 49 [!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, TW4-11, TW4-21 and TW4-37
to the chloroform pumping network in the first half of 2015 is expected to have a beneficial
impact. Generally reduced concentrations at TW 4-6 (since the first quarter of 20 15) and TW 4-16
31
(since the fourth quarter of 2014) after previous increases are likely the result of initiation of
TW4-1, TW4-2, and TW4-11 pumping.
Continued operation of chloroform pumping wells MW-4, MW-26, TW4-19, and TW4-20 is
recommended. Pumping these wells, regardless of any short term fluctuations in concentrations
detected at the wells, helps to reduce downgradient chloroform migration by removing
chloroform mass and reducing hydraulic gradients, thereby allowing natural attenuation to be
more effective. Continued operation of chloroform pumping well TW4-4 is recommended to
improve capture of chloroform to the extent practical in the southern portion of the plume. The
overall decrease in chloroform concentrations at TW4-6 from 1,000 !!giL in the first quarter of
2010 to 10.3 !!giL in the second quarter of 2014 is likely related to pumping at TW4-4. The
decrease in the long-term rate of water level rise at TW 4-6 once TW 4-4 pumping began, which
suggests that TW 4-6 is within the hydraulic influence of TW 4-4, is also consistent with the
decrease in chloroform concentrations at TW 4-6 between the first quarter of 2010 and the second
quarter of 2014. The decreasing trend in water levels beginning in 2014 and the generally
decreasing chloroform concentrations since the first quarter of 2015 at TW 4-6 are also
attributable in part to TW4-4 pumping. 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 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 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
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
32
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.
33
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc. on November 17,2016
Energy Fuels Resources (USA) Inc.
By:
Scott A. Bakken
Senior Director Regulatory Affairs
34
Certification:
I certify, under penalty of law, that this document and all attachments were prepared
under my direction or supervision in accordance with a system designed to assure that qualified
personnel properly gather and evaluate the information submitted. Based on my inquiry of the
person or persons who manage the system, or those persons directly responsible for gathering the
information, the information submitted is, to the best of my knowledge and belief, true, accurate,
and complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations.
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
35
Tables
Table 1: Summary of Well Sampling for the Period
Well Sample Date Date of Lab Report
MW-04 7/25/2016 8/9/2016
TW4-01 7/25/2016 8/9/2016
TW4-02 7/25/2016 8/912016
TW4-03 7/27/2016 8/9/2016
TW4-03R 7/26/2016 8/9/2016
TW4-04 7/25/2016 8/9/2016
TW4-05 8/2/2016 8/17/2016
TW4-06 8/4/2016 8/17/2016
TW4-07 8/4/2016 8117/2016
TW4-08 8/4/2016 8117/2016
TW4-09 8/3/2016 8117/2016
TW4-IO 8/4/2016 8117/2016
TW4-11 7/25/2016 8/9/2016
TW4-12 7/27/2016 8/9/2016
TW4-13 7/28/2016 8/9/2016
TW4-14 8/3/2016 8117/2016
MW-26 7/25/2016 8/9/2016
TW4-16 8/3/2016 8/17/2016
MW-32 8117/2016 8/26/2016
TW4-18 8/3/2016 8/17/2016
TW4-19 7/25/2016 8/9/2016
TW4-20 7/25/2016 8/9/2016
TW4-21 7/25/2016 8/9/2016
TW4-22 7/25/2016 8/9/2016
TW4-23 8/3/2016 8/17/2016
TW4-24 7/25/2016 8/9/2016
TW4-25 7/25/2016 8/9/2016
TW4-26 8/3/2016 8117/2016
TW4-27 8/3/2016 8117/2016
TW4-28 7/27/2016 8/9/2016
TW4-29 8/4/2016 8/17/2016
TW4-30 8/3/2016 8/17/2016
TW4-31 7/28/2016 8/9/2016
TW4-32 7/28/2016 8/9/2016
TW4-33 8/4/2016 8117/2016
TW4-34 8/3/2016 8117/2016
TW4-34R 8/2/2016 8/17/2016
TW4-35 8/3/2016 8117/2016
TW4-36 7/28/2016 8/9/2016
TW4-37 7/25/2016 8/9/2016
TW4-60 7/25/2016 8/9/2016
TW4-65 7/27/2016 8/9/2016
TW4-70 8/3/2016 8117/2016
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 ofTW4-23.
Highlighted wells are continuous!)' pumped. ---~-~
INDEX OF TABS
Tab A Site Plan and Perched Well Locations White Mesa Site
Tab B Order of Sampling and Field Data Worksheets
Tab C Weekly and Monthly Depth to Water Data
Tab D Kriged Current Quarter Groundwater Contour Map, Capture Zone Map, Capture Zone Details
Map, and Depth to Water Data
Tab E Kriged Previous Quarter Groundwater Contour Map
Tab F Depths to Groundwater and Elevations and Hydrographs of Groundwater Elevations Over Time
for Chloroform Monitoring Wells
Tab G Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells Over Time
Tab H Laboratory Analytical Reports
Tab I Quality Assurance and Data Validation Tables
1-1 Field Data QA/QC Evaluation
1-2 Holding Time Evaluation
1-3 Receipt Temperature Check
1-4 Analytical Method Check
1-5 Reporting Limit Evaluation
1-6 Trip Blank Evaluations
1-7 QA/QC Evaluation for Sample Duplicates
1-8 QC Control Limits for Analyses and Blanks
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 N Exceedance Notices for the Reporting Period
Tab A
Site Plan and Perched Well Locations White Mesa Site
TW4-19
EB
PIEZ-3A ~
MW-5 •
TW4-12
0
TWN-7
¢
PIEZ-1
~
perched chloroform or
nitrate pumping well
May, 2016 replacement of
perched piezometer Piez-03
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
PERCHED WELLS AND PIEZOMETERS
APPROVED DATE FIGURE
HJ718000/aug16/Uwelloc0616.srf I A-1
TabB
Order of Sampling and Field Data Worksheets
( (
Order of Contamination for 3rd Quarter 2016 Chloroform Purging Event
Chloroform Water Well
Well Sample time Levels Rinsate date/time level Depth
TW4-03 7/2:7/ I& o 75Y ND 141
TW4-12 71"2.7/Jb ~~1::!! ND 101.5
TW4-2871Z7/jl. O~'Z~ ND 107
TW4-32 7/451114 OYJ2.?:> ND 115.1
1W4-13 '7123_/11, Q8Q1 ND 102.5
1W4-36 7/Z'5i~ D~l'( ND 99
TW4-31 7!2.KI/b (J?11j ND 106 l'w4-)4'R._DB02:Z.Dl(, 0725
1W4-34 '6/~/Jb OB01 ND 97.2
1W4-35 IS/3/Il. Q&l'-l ND 87.5
1W4-23 gj~jl(, 0'6"43 ND 114
MW-32 W11Jlfc. 1-z.~ ND 132.5 Bladder pump
TW4-25 ]/2.5/lt:-1')-z.io ND I 34.8 Cont. Pumping
TW4-27 $/3/1~ 03~ 3.16 96
TW4-14 i93/lk O~ljQ 6.15 93
TW4-30 't:J/3{.~ o~~ 7.38 92.5
TW4-26 '1;.131 1(2 Q'lOD 8.23 86
TW 4-05 1$/JI)b 0<102> 13.6 120
TW4-18 rJ3/lb 0'117 60 137.5
1W4-24 112;11/:, 1'~'-11 69.6 112.5 Cont. Pumping
TW4-09 '613/U. Q~U 76.2 120
TW 4-16 t?l:3fl{z Qj~Z 93.4 142
TW4-33 g/'1/lf. OISS 96.1 87.9
TW4-29 1'/'-1/ii:, Qf-~).!.2 366 93.5
TW4-06 ?>/4/16 0~1) 486 97.5
TW4-21 7/Z:.Jii. l"YZD 545 121
TW 4-08 ~Ju../Jb OfSiq 595 125
TW4-07 '6/~/it., 0~~ 909 120
TW4-01 1/ Z.S/Ih 1~37 1140 110
TW4-10 ~/1.1/lr.. 0~1 1510 Ill
MW -04 712.5/16 l'D2. 1580 124 Cont. Pumping
TW4-04 7/2.5/11:. IY'i.S 1780 112 Cont. Pumping
TW4-02 7/Z5/Ib 1~<.5 2070 120
MW-26 7/ZSiib 1417. 2220 122.5 Cont. Pumping
1W4-ll 1/1.91~ iYit.l 3340 100
1W4-22 7125/11, I :35!> 8570 113.5 Cont. Pumping
TW4-19r!'zS/i6 ISD'D 12600 125 Cont. Pumping
TW4-37 71?.5/lJ. !Y)I.. 16200 112 Cont. Pumping.
TW4-20 7/Zrdlb \YOY 33700 106 Cont. Pumping
1W4-60 D.l. Blank 7125/IC. l;}uC
TW4-65 Duplicate vf 2~ 7/27(/k. ogzo
1W4-70 Duplicate
Comments:
Name: Date: /
I
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 '3 r& Q""o-rter C\=11 DroforfY'I -zo l b
Location (well name): ._I "-M"-W_-_O_t.! _________ ___.
Sampler Name
and initials: I ~nner Noll ,"J,...jfrH
Field Sample ID
Date and Time for Purging I 7/'Z..S/-zo't/:. and Sampling (if different) ._I .M_rA ________ __,
Well Purging Equip Used: (jTipump or [QJ bailer Well Pump (if other than Bennet) I Go(!Hflv.ov...s
Purging Method Used: 002 casings [QJ3 casings
Sampling Event I lXv-a..rtu-E Cn lorJ"orm Prev. Well Sampled in Sampling Eventl L-_-r_w_~_-_6_-z _____ _..J
pH Buffer 7.0 ._I _7__._.__, o ___ __. pH Buffer 4.0
Specific Conductance IL-...!.l=-.;Oo::...O;:__ __ __JI~-tMHOS/ em Well Depth(O.Olft): I \'ZY. OD
Depth to Water Before Purging I Z\.DD
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl._l3=-=..3_"'_~
Time I 1431 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I \8qs I pH 1 6.57 I Conductance I I pHI I
Temp. oc I 16,Dt I Temp. °C I I
Redox Potential Eh (m V) I '3Zb I Redox Potential Eh (m V) I I
Turbidity (NTU) I S,_3 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. °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 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I q_~
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two cas.ing volumes (2V)
T=2V/Q= I 7.~Lj I
0
Name of Certified Analytical Laboratory if Other Than Energy Labs l~..oAu~.!..:...Lft~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
VOCs w D 3x40 ml 0 I[] HCL 1!1
Nutrients f) 0 100 rnl D ~ H2S04 ~
Heavy Metals D D 250 ml 0 0 HN03 0
All Other Non Radiologies D 0 250 ml 0 0 No Preserv. 0
Gross Alpha 0 0 1,000 ml D 0 HN03 D
Other (specify) (Q 0 Sample volume 0 ~ 0
G h 1or·~~e. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1......_8 _4 '.....;9:.....7 __ ____. Sample Time
Comment
' ~ See instruction
An;veA 0(1 si.fe o-.+ 14'2S -J:tlner' Md
SWill ple.S collecfeJ tA.t ILJ3Z LVo.Jcr
&o.rrr'fl prc=-.serrt +o coPed .. Sr.4mp/es
w~ L.\eo.r
L~tt ~J+t> o-. r IY33
MW-04 07-25-2016 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 See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
DescriptionofSamplingEvent: I 3~"'a Gu:aroffM~ Ql.A-&~r-+er"' Ghlort;for(Yl 201'-
Location (well name): ._I _1\~W_4_,_-_0_l ________ __.
Sampler N arne
and initials: I ~'ltl ~,.... ~ol I,·JA.::\JiH
Field Sample ID
Date and Time for Purging I 7/ZS/ZDJ.b and Sampling (if different) ._I _.t0_0_1'1 ________ _J
Well Purging Equip Used: @!]pump or [gJ bailer Well Pump (if other than Bennet) I Got'\fu'\v.ou,>
Purging Method Used: 002 casings [gJ3 casings
Sampling Event I Qv.o.r-i-ef"'b1 G'hloro::rorm Prev. Well Sampled in Sampling Event ._I_M_W_~_o_LJ _____ ___.
pH Buffer 7.0 7.0
Specific Conductance ._I ~lc.::OO=o ___ ___JI~-tMHOS/ em
Depth to Water Before Purging I ~Y. bb
Weather Cond.
Time I p .. \3(; I Gal. Purged I b
Conductance I '2.481 I pH I c..s~
Temp. oc I 16.19 I
Redox Potential Eh (mV) I ~qr;: I
Turbidity (NTU) I () I
Time I I Gal. Purged I
Conductance I I pH I
Temp. °C I I
Redox Potential Eh (mV) I I
Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater
I
I
I
I
pH Buffer 4.0 y,D
Well Depth(O.Olft): ._I ..uli=O-'-'. 0'-D __ ____.
Casing Volume (V) 4" Well:,]c;,sq ,(.653h)
3" Well:._ . ..:...o __ ----'·(.367h)
Ext'l Amb. Temp. •c (prior sampling event)L...;I .J::::....=-.3 _0 _ ___.
Time I I Gal. Purged I I
Conductance I I pHI I
Temp. °C 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 \b ,D
Time to evacuate two casing volumes (2V)
T = 2v1Q =I z, oro I
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs
Sample Taken Sample Vol (indicate
Type of Sample if other than as
y N specified below)
VOCs 1!1 0 3x40 ml
Nutrients r:!l D lOOm!
Heavy Metals 0 0 250m!
All Other Non Radiologies 0 D 250m!
Gross Alpha 0 0 1,000 ml
Other (specify) [] 0 Sample volume
Ghl .. riJe
Final Depth I ) D 4 .Y.3 Sample Time ._I ..:....J l.\..:...:3::::..1_._ __ _,
Comment
~oft\ples. Ce>llec:+d o..t }ll37
Le.+f-s,·-l-~ a.-\-143~
TW4-0l 07-25-2016 I Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
0
AWAL
Filtered
y N
0 111
0 [!J
0 D
0 0
0 0
0 rn
Preservative Type Preservative Added
y N
HCL 0 0
H2S04 ~ 0
HN03 D 0
No Preserv. 0 D
HN03 D 0
0 ~
If preservative is used, specify
Type and Quantity of Preservative:
1 ~ 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
DescriptionofSamplingEvent: I 3rho Gv..o.r:fer C\1\orD~Dri'V'l 'Zol'
See instruction
Location (well name): 1.__-n.v __ "I'----D....:Z~------------' Sampler N arne
and initials: 1:::-r t~~MU' HPJ I :J ".:3 l 'l'H
Field Sample ID
Date and Time for Purging ._I _7_/_Z.S_/_Z_C>_Ik ____ ____, and Sampling (if different) .NjA-.__ _________ ~
Well Purging Equip Used: [][]pump or [QJ bailer Well Pump (if other than Bennet) I Goflfln\AoU.S
Purging Method Used: @]2 casings [QJ3 casings
I -:f!AJ y-J) Sampling Event I Q\ll.o.rh:rB Ch\or"•\-'Ofr'V\ Prev. Well Sampled in Sampling Event L _________ _,~
pH Buffer 7 .ol ._ _7_._o ___ ____, pH Buffer 4.0 L.J. ()
Specific Conductance ll-_1 o_o_;:D ___ _JI ~-tMHOS/ em Well Depth(O.Olft): I lzo.oo
Depth to Water Before Purging I 80 , D5 Casing Volume (V) 4" Well:l 'ZC..og 1(.653h)
3" Weli:L...... _o __ ___j.(.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)LI3_.J_' __ _J
Time I 14'24 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I ~YZZ I pH I ,,4D I Conductance I I pHI I
Temp. oc 1 \5.~3 I Temp. oc I I
Redox Potential Eh (m V) I ~z~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I ~.s I Turbidity (NTU) I J
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. °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 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I /7,0 T = 2V /Q = I ':>I 0' I
Number of casing volumes evacuated (if other than two) D
If well evacuated to dryness, number of gallons evacuated D
Name of Certified Analytical Laboratory if Other Than Energy Labsl L.. _:A....:.VJ.:.....:....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 rn D 3x40 ml D 1!1 HCL rfJ 0
Nutrients m D 100 ml D 1!1 H2S04 In D
Heavy Metals D D 250 ml D 0 HN03 D 0
All Other Non Radiologies D D 250 ml D D No Preserv. D 0
Gross Alpha D 0 1,000 ml D 0 HN03 D 0
Other (specify) ~ D Sample volume D ~ D r!:l
Chloride If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I llb,DL{ Sample Time JYZS
Comment
1 rJ See instruction
Ar~•\Je.a on s;h~. 11-.-f )4'21 -r;._tltler tAf'J G-c..rr~t1 pre~e/1.} +~> Co II ecf .S"IYI p les .
~o.mp1Q (ollec.teJ u-t 1'-l"Z..S lAJC\ +er (,.)~ MtJ!lil~ c.lea:r
Let-)-site {At 1'127
TW4-02 07-25-2016 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 ::,rt} GW~-r}er Ch)orbfotM zor6
Location (well name): ~.-l-ri_W--....:.Y_-_0_3 _________ __,
Sampler Name
and initials: l~r~Mr H,J}.J1:!J}(H
Field Sample ID j -J\}54 -6.3_ OIZ7ZOilo
Date and Time for Purging l.__!_/_z_(,"-j-z._o_l~ ____ ___, and Sampling (if different) l~.-7.:....!/:....Z7._;_:_/_z_ot~'--------~
Well Purging Equip Used: (![]pump or [QJ bailer Well Pump (if other than Bennet) ..,16"--r'-1).-,_JR)_.s ____ _,
Purging Method Used: ~2 casings 11[]3 casings
Sampling Event I Qy..o.f"fe•b Gh l or~orrfl Prev. Well Sampled in Sampling Event L..l"11_iJ_'1_-_0_.3_R _____ ......~
pH Buffer 7.0 7,0 pH Buffer 4.0 y,o
Specific Conductance!...._ _1_00_0 ___ ___,1 !!MHOS/ em Well Depth(O.Olft): lL..-..:....JY...:...:I:....::' O:....:...D __ _J
Depth to Water Before Purging I 57, Y D Casing Volume (V) 4" Well:l S4 ,5'3 1(.653h)
3" WelJ: 0 (.367h) '-----_J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventll.__Z-'-'1-() _ __,
Time I )3\1 I Gal. Purged I IDO I Time I I Gal. Purged I I
Conductance I 1705 I pH I G.yo I Conductance I I pHI I
Temp. oc I JS.OO I Temp. °C I I
Redox Potential Eh (m V) I 3~G I Redox Potential Eh (mV) I I
Turbidity (NTU) I .ZD I Turbidity (NTU) I I
Time I 075.~ I Gal. Purged I 0 I Time I o/o.s I Gal. Purged I ~ I
Conductance ll7l5 I pH I b.'ZS I Conductance lnz~ I pH lb:Z7 I
Temp. oc I JC. so I Temp. °C l lb.4:S 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 loo gallon(s)
Pumping Rate Calculalion
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I \0.{) T = 2V /Q = I 10 I 'l J I
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated Lj\_D_O __ __.J
Name of Certified Analytical Laboratory if Other Than Energy Labs IL...;..A..:..;\1\}:...;._:._:ft'-=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
VOCs [] D 3x40 ml D [)I HCL [;]
Nutrients III D lOOml D Bl H2S04 ~
Heavy Metals D D 250 ml D D HN03 D
All Other Non Radiologies D D 250ml D D No Preserv. D
Gross Alpha D D 1,000 ml D D HN03 D
Other (specify) rn D Sample volume D ~ D
C h) oriJe. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 1~9 . 0~ Sample Time 07SY
Comment
,-j See instruction
Aai -veJ on SITt: AT lZ57 ---r;A11net" AA J G-~r(,·n pre.se 11r 1--;,r pv.ret· Puc~e 6~~ "'-;-
? v.r~e~ Well --hr A to+ tAl o-f' lo Miflv-+~~. P"'r~e:~ Well Jr~'. H.v8c -e11JeJ. o.:J-1'311
LV~ fer ir-'o..'::l Mt>.:>ii..j Clcc.u-. k.Jt s~t~ ~t-l~lL/
}'301
N
D
D
D
D
D
~
Arr·; \)d. 0(1 .Site Q..+ 0751 J;.,n(lel ~r'l~ G-o..r.-:11 pre sen+ +o Coiled·· SP.mpJes. . ..Dept-h -h wo..+er
Wo.~ S7.7z ~a.~r~s b_,·\d tll.t-0"15'i Le-Pt .s./1-<: ~+ 0"1.5-{.
TW4-03 07-26-2016 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 ~r-J 0\A.().rter ChlorOform Z01'
See instruction
Location (well name): ._I!--'--"WJI....Y..._-_0:....:3=..:....1\...___ _______ __,
Sampler N arne
and initials: IJ;;.r"'ne.r Aoli;J&~.;j/(1}
Field Sample ID
Date and Time for Purging I I /2.Cj-zot..t. and Sampling (if different) ._l..-v:--'-~-'-'14.___ _______ _,
Well Purging Equip Used: jiDpump or [QJ bailer Well Pump (if other than Bennet) I Gn.A(IJ:I'"a.s.
Purging Method Used: IT!]2 casings [QJ3 casings
Sampling Event I Qw:>.rf.erl,j Ch \ orof'or!Y\ Prev. Well Sampled in Sampling Event 1 1W4-l~ '------------'
pH Buffer 7.0 ._I _7...:...:':....::D'--------' pH Buffer 4.0 I Y.o
Specific Conductance!._ ~10:..::0'"""0'-------'h.tMHOS/ em Well Depth(O.Olft): I o '---------'
Depth to Water Before Purging ._I _o ___ _, Casing Volume (V) 4" Well:~_o ___ _,l(.653h)
3" Well:. o (.367h)
Weather Cond. Clo\Ad~ Ext'! Amb. Temp. ·c (prior sampling event)I._Z_'1_6 __ _,
Time I 1'2.3/ I Gal. Purged I 1ZO I Time I I Gal. Purged I I
Conductance I q,J I pH 1 7,5~ I Conductance I I pHI I
Temp. oc 1'2.5.77 I Temp. oc I I
Redox Potential Eh (mV) I 'S':>b I Redox Potential Eh (mV) I I
Turbidity (NTU) I D 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 \~0 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 0 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 ...LA..:..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 l:tl D 3x40 ml D IZl HCL k3
Nutrients ~ D 100 ml D ~ H2S04 ~
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 111 D
Grilof·,Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I _();....._ ___ __, Sample Time
Comment
~ See instruction
Arr'l\)ej on .s\te o-t \'Z.Z.D -r,.,nnef' ""'"'~ {r,..rri(l r•e.s.er~i-' for r:n.$d\.+e.
R;nso..te be~I'An o-.t \ZZ5. ?IAmreJ S.D Go..llcul.S .:r.J' SoOf> lt.)o..fer o.ntl
&"'llo~D of .{yr_ w~+er. ~c:hr'lr)e...) c.oJlec1-eJ ~r 1238'.
Le-ft s,'te tAt )Z'1 1
TW4-03R 07-26-2016 I no not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
}00
N
D
D
D
D
D
!gl
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
DescriptionofSamplingEvent: I ~<"6 G"'c:>-r+er C:hloro+orl'1 ZOI{.
Location (well name): ._I_T..;.._;_W_L-\.;...-_0_4-'-----------"
Sampler N arne
and initials: I '1;1'\t\(r FJ_, l I :(l (}._j 1711
Field Sample ID
Date and Time for Purging I 7/Z5/ZO l.b and Sampling (if different) .N/1) ~------------------~
Well Purging Equip Used: IT!] pump or @] bailer Well Pump (if other than Bennet) I C o()fl fl t.AO\A.S
Purging Method Used: [£!]2 casings @]3 casings
Sampling Event I Qu..o.rhr~ G'hiDrOforf't'J Prev. Well Sampled in Sampling Event I ~\,J 4-0 I
pH Buffer 7.0 7.0 pH Buffer 4.0 q.o
Specific Conductance ._I _I_DD_O ___ ___JI ~MHOS/ em Well Depth(O.Olft): I }IZ,o~
Depth to Water Before Purging I /3, 5'-j Casing Volume (V) 4" Well:I "Z 5.11 1(.653h)
3" Well: 0 (.367h) '--------1
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._l 3-"----:3_6 _----'
Time I 1'"144 I Gal. Purged I D I Time I I Gal. Purged I I
Conductance lzyoe> I pH I '· b.3 I Conductance I I pHI I
Temp. °C I 16,39 I Temp. °C I I
Redox Potential Eh (m V) l~b~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I ~.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. °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 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I II, 0
Time to evacuate two casing volumes (2V)
T = 2V/Q = I Ll, 5C 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 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 0
All Other Non Radiologies 0
Gross Alpha 0
Other (specify) tJ
Ch lor,'Je
Final Depth ._I -~-1-'-, -=qs:;;...._ __ _.
Comment
Arrived. on ~,+e o.+ \'441
So."'p1~~ Lollcc.+eJ o..+
Left ~;-k o-.1-\44 iS'
N specified below) y N y
0 3x40 ml 0 rJ HCL 0
0 lOOm! 0 ~ H2S04 _[]_
0 250 ml 0 0 HN03 0
0 250m! D 0 No Preserv. 0
0 1,000 ml 0 D HN03 D
D Sample volume 0 'tl 0
If preservative is used, specify
Type and Quantity of Preservative:
Sample Time l445
.~ See instruction
-(Anne~" tMc1 G-.:1rr;., pres.e(/f fo c.ol\ec....J-
l~4.S lA)o..+er (Na.s. MD.s+~ Clew
TW4-04 07-25-2016 lno not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
0
D
D
~
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 3rt\ &v.Wfer Gvdorb'Hrtt? Z61t.
Location (well name): Ll -r~w_'-\:.._~_0.:_6 _________ _.J
Field Sample ID
Sampler N arne
and initials:
,. See instruction
Date and Time for Purging I 8/z/zoJ G, and Sampling (if different) g}3/Zo)(. '---~~~~----~
Well Purging Equip Used: [Q]pump or [QJ bailer Well Pump (if other than Bennet) I Grv.flJR>i)
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Qu.l).tferlj Ch\orotJr)'V'l Prev. Well Sampled in Sampling Event I IW4-zc;.
pH Buffer 7.0 pH Buffer 4.0 '""\,o
Specific Conductance l.___l_()o_o ___ ____.l ~-tMHOS/ em Well Depth(O.Olft): I I'ZO,OD
Depth to Water Before Purging I f>S,Ol\ Casing Volume (V) 4" Well:I 3S. 35 1(.653h)
3" Well: 6 (.367h) '--------'
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventJLI _3_]_0 _ ___.
Time I ) '3,0l> I Gal. Purged I 60 I Time I 130) I Gal. Purged 170 I
Conductance I 1S~'1 I pH I ~.~o I Conductance I 153! I pH I 6,37 I
Temp. oc I ,S,G3> I Temp. oc I )~,b'Z I
Redox Potential Eh (m V) I se>l I Redox Potential Eh (mV) I 5DI I
Turbidity (NTU) I 13 I Turbidity (NTU) 113 I
Time I l3b'Z. I Gal. Purged I gl) I Time 11303 I Gal. Purged ljO I
Conductance I )5Zg I pH I (ol3t I Conductance I \51& I pHI ~.3H I
Temp. oc I IS.CZ I Temp. oc I l5.a;5 I
Redox Potential Eh (m V) I 5DD I Redox Potential Eh (mV) 15DD I
Turbidity (NTU) I !g I Turbidity (NTU) I Jl1 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 ca ·ing volumes (2V)
S/60 = I )0,0 T=2V/Q= I /./] I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated b
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 m 0 3x40 ml 0 [fJ HCL rn 0
Nutrients rn 0 100 ml 0 ~ H2S04 l!l 0
Heavy Metals 0 0 250ml 0 D HN03 0 0
All Other Non Radiologies 0 0 250 ml 0 D No Preserv. 0 D
Gross Alpha D 0 1,000 ml 0 0 HN03 0 0
Other (specify) ~ 0 Sample volume 0 Ill 0 1!3
C~lor;de If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I b(., 'ID Sample Time ._I 0.=:........:'1c.::.0....,8'-------'
Comment
-,., See instruction
Arr;ue~ of\ ~;te ~J 1'2..5). -ro.Mer ~11J GMr•.fl pr-ese,+ -tr pur3e-. f>u.'(Je b~an a.f--le5L/
fv-f'~6 I.Uell tor o-.. +o t"'l o+' 4 -m;t~u+e~. fur~e e11JeJ tA+ -tz:91 1360
lt.:l<A+er ~o.~ Glear. LM 5•te o.-l-l'3DL
Af'r:ve~ on s,'te ~+-O'lOS l~nnt( M~ G~Arr'.n pre..5eJ.. +o colled-..S~~J~f>l~5. Deyh f/) Wetter
VJa..S b!;,z"& .So.fl"\p)es b"':le~ ,J-o~og 1..-c:J) _s,·+~ ~J-oqro
TW4-05 08-02-2016 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)
r'' e£ER0YFCJELS ATTACHMENT 1-2
WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: 3t0: Q\):0:;4ii:r Gh Jorlifbrm "Z.o \L.
Location (well name): l._"n_W_'-1_-_D_, __________ __.
Sampler Name
and initials:
Field Sample ID
Date and Time for Purging I ~/3/ZOU. L----------~
Well Purging Equip Used: ~pump or @]bailer
Purging Method Used: ~2 casings @]3 casings
Sampling Event I QJ::o-rrerb ~f I
orl)OB)c(t)
pH Buffer 7.0 I 7 , 0 I
Specific Conductance ._I _l_oo_o ___ __.l fA-MHOS/ em
Depth to Water Before Purging I 72.8 2
Weather Cond.
Time I \L.S/ I Gal. Purged I ~
Conductance I "3lt>b~ I pH I ~.Z'3
Temp. oc I 15.7 8 I
Redox Potential Eh (m V) I 5~1 I
Turbidity (NTU) I 'lt;1'5 I
Time 1 6&1~ I Gal. Purged I 0
Conductance I 33/8 I pH I r;.LJ J.
Temp. oc I lq,gh I
Redox Potential Eh (m V) I I
Turbidity (NTU) I I
White Mesa Mill
Field Data Worksheet for Groundwater
I
I
I
I
and Sampling (if different) gJq/ZoJ' L-----------~
Well Pump (if other than Bennet) ._I G_r_<A_"J_~_~_-> ____ __.
Prev. Well Sampled in Sampling Event .... 1_11_W_y_ .... _Z_1 _____ __.
pH Buffer 4.0 1 4.6
Well Depth(O.Olft): I 'l /,SO
Casing Volume (V) 4" Well :~1--.b.-, 1_1 _ ___,, ( .653h)
3" Well:_ 0 (.367h)
Ext'l Amb. Temp. oc (prior sampling event) .... l z_7_0
__ _.
Time I I Gal. Purged I I
Conductance I I pHI I
Temp. oc I I
Redox Potential Eh (mV) I I
Turbidity (NTU) I I
Time I o~1 4 I Gal. Purged I ~ I
Conductance I 3~~~ I pH I C.tLS I
Temp. oc 119 · 84 I
Redox Potential Eh (mV) 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 gallon(s)
Pumping Rate CalculaLion
Flow Rate (Q) in gpm.
S/60 = I )D,Cl
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 '1:.:zz. I
I t &b
Name of Certified Analytical Laboratory if Other Than Energy Labs IL-..!..A.:...:\fj_;_A:....:....: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 lJ 0 3x40 ml 0 I!J HCL !] 0
Nutrients ~ 0 lOOml 0 r::J H2S04 :c:J 0
Heavy Metals 0 0 250ml 0 0 HN03 0 0
All Other Non Radiologies 0 0 250 ml 0 0 No Preserv. 0 0
Gross Alpha 0 0 1,000 ml 0 0 HN03 0 D
Other (specify) ~ 0 Sample volume 0 €1 0 m
Lh)o(;Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth Ll -=-" l\_ .. 3;;,;__ __ ___J Sample Time
Comment
J See instruction
Ar-ri~e~ 01"\ si-i-e: ().-r )2.51 -r;.l'lnU ~(lJ.. GD-{"r o(\ r-esen-l-.+o..-ru..r~e . f>w-ef' ~ o..t 12 5'-j
.fv.r~ec\ wel\ .fo"(" "' totuJ oF 3 "M;Y\"'-+e~. ?u.c~~~ wei) Jr-'6, P"'r~-c. MtJ.d o.:l-1'257
wo-.+cr \.2l~ WI\A.'('"v~, Left-~~t~ ~t J')Ol>
IJrr-;ve.d-on s.+e o..+ D&tb '~f\1\Cr IA.nJ.. G-o..c-r .·" pr~~(\} -Jo coJiec.t ~"'I'VI.P \e.s' D~pth To t.:~a..-T(r
\Vo..~ 7?J,"L1 ~~rv~ple~ b.o..:kJ. 4.}--O~IG Let:} ~~+~ ~1 D8.L.5
TW4-06 08-03-2016 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 ~y·J' Gv-.o.r-1-~r-Gh I ot'*'br-1"1 Z.OI4
Location (well name): ._l_"f,_w_'-1_-_0_7 _________ ____,
Sampler N arne
and initials: I ~~nne• Hol)IJ~/TH
Field Sample ID 1 TwL\-0/_ogoL\zC>t fo
Date and Time for Purging ._I ~-~-~_/z_o_l_b _____ __. and Sampling (if different) ~.--1 S(/_t.J_I:_z_o_lt.. ______ _,
Well Purging Equip Used: (IDpump or [QJ bailer Well Pump (if other than Bennet) 1 6'r-u.nCJOt~.:s:
Purging Method Used: [![]2 casings [QJ3 casings
Sampling Event I Gv..01A~r~ Ch l or~nv~ Prev. Well Sampled in Sampling Event ~.--I_Ji_~_Y_-_0_8 ______ __.
pH Buffer 7.0 L-1 _7:....;.'_0 ___ _. pH Buffer 4.0
Specific Conductance L-1 ..;.\.:....:oo;...:o:..__ __ _,l !J.MHOS/ em Well Depth(O.Olft): l lZD,Oo
Depth to Water Before Purging I 7 G..~{) Casing Volume (V) 4" Well:l z g, 5.3 1(.653h)
3" Well: o (.367h) '--------'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)L..I0_111 __ __J
Time I 1'3 5<6 I Gal. Purged I ~D I Time I 1'6.51 I Gal. Purged I 'Zl I
Conductance I \b'7.1 I pH I f:,5q I Conductance I l b '33 I pHI ~.~ I
Temp. oc I 15 .-z.' I Temp. oc I l S,"ZI I
Redox Potential Eh (m V) I 505 I Redox Potential Eh (mV) I 5()~ I
Turbidity (NTU) I 5tl I Turbidity (NTU) I l)y. I
Time I }"jOt> I Gal. Purged I 7D I Time I I ql) I I Gal. Purged I go I
Conductance I 1~5~ I pH I r:.s:s I Conductance I n:~~ I pH I b·57 I
Temp. oc I I !S I 'Z.!:> I Temp. oc I 15<Z5 I
Redox Potential Eh (m V) I Sr59 I Redox Potential Eh (mV) I 50'1 I
Turbidity (NTU) I 5::? I Turbidity (NTU) I !0 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. Time to evacuate two ca ing volumes (2V)
S/60 = I 10.11 T=2V/Q= I 5.7D 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 '-'-1 /J..:..W_IJ_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$1 D 3x40 rnl D ~ HCL !:1 D
Nutrients llJ D 100 ml D fl H2S04 f) ·D
Heavy Metals D D 250m! 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) ~ D Sample volume D flJ 0 tJ
C'h \o,~Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I \ I C:. b'Z. Sample Time
Comment
.. -), See instruction
Arr;ved on ~\i-e o-.t )";S\. -r,._nt~er l..f\~ (rf1..rr;" ?{'e~e~ for pu.r~e. ?u..r~< be~'\ "'t J353
Pu.r~e~ ~Nell for ,.. totDil oF ~ P);r1...,-t~..). Po..r~~ ef\d~~ o..1 l~DI. 1,\)~.:t.e.r \...)~ I'Y.ID~-t-l...v
G\aM"". Lill s;+~ a.t 1~03. 0
Acc:\)r::~ 01'\ si-t~ d\} 0622 -JN\fle't< ~{\J. Vo.rr~(l f>re.!>e~ 1o Coiled·~ .s ~~'>tv!p)e~' Der~ -k t.vo.+~
WtA.> 77. f{(. su-""rle~ bo..\le~ tA...J.-tJ8'4.5 t.e.-ft-.s t}-l!.. ""+ 08Z7
TW4-07 08-03-2016 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
DescriptionofSamplingEvent: I ~t"'t); Qv.o.4e,-Ghlorof6rrvl 'Z.O\(.
See instruction
Location (well name): ~..I =t\J __ Ll_-O:;_Z.::.__ ________ ____.
Sampler Name
and initials: I ~n n er Holl;J ... -!1/T/7
Field Sample ID
Date and Time for Purging ~~----~-/_5__,/_z:_o_J.l.. _____ _, and Sampling (if different) B/4 /2o1 C. 1....---------~
Well Purging Equip Used: IT[) pump or [QJ bailer Well Pump (if other than Bennet) I G(V\t'\JJ;;_s.
Purging Method Used: [![)2 casings [QJ3 casings
Sampling Event I OV:o-rferb C'h I orotJrf"') Prev. Well Sampled in Sampling Event ._I_Ji_W_L\_-_O_b _____ __,
pH Buffer 7.0 7.0 pH Buffer 4.0 y,o
Specific Conductance!._ _l_oo_o ___ __,l !!MHOS/ em Well Depth(O.Olft): I 12 b.oo
Depth to Water Before Purging I 7'l '3(., CasingVolume(V) 4"Well :l 2'1.80 1(.653h)
3" Well:._ __ o ___ .....J_(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event) I 30~>
Time I r~-z."' I Gal. Purged I '50 I Time I l~Z/ I Gal. Purged I 60 I
Conductance I S03q I pH I ~, 1,(., I Conductance I &?"3D I pHI (,.17 I
Temp. oc I \~,z~ I Temp. °C I \S;Z.I I
Redox Potential Eh (mV) I !;'1q I Redox Potential Eh (mV) I ~N'i I
Turbidity (NTU) I \l.~ I Turbidity (NTU) I I t . .l. I
Time I I~Z.~ I Gal. Purged I 70 I Time I \3'Z.Gf I Gal. Purged I g_o I
Conductance I 5031 I pH I G,,\K I Conductance I 5075 I pH I C.,Jq I
Temp. °C I I 5 I Z"t. I Temp. °C I lS• 'Z I I
Redox Potential Eh (mV) l 5q3 I Redox Potential Eh (m V) I sq3 I
Turbidity (NTU) I ll:Z: I Turbidity (NTU) I }l_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 ~D gallon(s)
Pumping Rate CalculaLion
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
s16o = 1 lO,o T = 2V /Q = I 5 ,lfl:) 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
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 D 3x40 ml D [!] HCL 1!1 D
Nutrients [!] D 100 ml D 1!1 H2S04 ~ D
Heavy Metals D D 250ml 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!1 D Sample volume D ~ D ~
{_~ loride If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 8 S.oo Sample Time O~lj
Comment
.;) See instruction
A!"f"I1\Je~ 01'\ s;fe CAt \~\g, -r~llflt:("" (}I.I')J. G-o.n•:n preserrt'-for rv..r~e. Pv..r~E' be-3"'" A-t )3>'2.)
flArl()e~ ~ell ~~ u... to+u.l of' ~ Jl'l;,w-+~s. PL\r~ t:,.Je! "'y )JZ~. 11-)~ta-~s ...-t>s1-l~ cJcor.
lef} ~ltc ~t \3"j\
Arr'lve:~ on srt~ o-.t ogU:. -rc:nl\er o:nJ Go--rr:ll
vvo..s. 7q, £> l ~o.Mpl-es. bu-. -le2~ v..} C> g 1~
fr-es.eV'I+ +o co))ec} .s~'V!fl-e-s.
l---e? s. :·h: IA,-1 og z/
TW4-08 08-03-2016 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
DescriptionofSamplingEvent: 13,.-t) G\A~rfc,.. C,}dorofOrnll
Location (well name): ._I _.,-w"---~'---O_~-----------'
Field Sample ID I "T~4-D'i .... 080::!>'ZD1'-
Sampler Name
and initials:
I' See instruction
Date and Time for Purging L-1 _;?l:::;,....:;.z..;..)_'Z_ol_:.b _____ _~ and Sampling (if different) IL......;;.;~)'-3"'----/_Zo_/_lo _____ __,
Well Purging Equip Used: ~pump or [QJ bailer Well Pump (if other than Bennet) I Uf'~n JJ.;:...s
Purging Method Used: [ID2 casings [QJ3 casings
Sampling Event I Q\A.ar+erb G\., I oroFo rm Prev. Well Sampled in Sampling Event L-1_-n_k>_Y_-_,_~ _____ _J
pH Buffer 7.0 {,0 pH Buffer 4.0 4.0
Specific Conductance I ~ \OOD 1~-tMHOS/ em Well Depth(O.Olft): I )ZO,OO
\000
Depth to Water Before Purging r--1 -:::rs=:z,.....,. 'l"""~:=------. Casing Volume (V) 4" Well:' ~ 3,7fc, ,(.653h)
3" Well: () (.367h) L------'
Weather Cond. Ext'l Amb. Temp. "C (prior sampling event) I 33°
Time I 146~ I Gal. Purged I 70 I Time I IY lo I Gal. Purged I go I
Conductance I -z.sos I pH I c. :z.t> I Conductance I Z4g~ I pH I c; I -z ::J I
Temp. °C I \~.-:>-z I Temp. oc I IS.3D I
Redox Potential Eh (m V) I Ll%7 I Redox Potential Eh (m V) I qg7 I
Turbidity (NTU) I 3D I Turbidity (NTU) L \._) 1 3o
Time 11 1 ll I Gal. Purged I qo I \'-II J
Conductance I7.LJ9g I pH I C..'Z'3> I
Time 114 I'Z I Gal. Purged 1100 I
Conductance 1 -z~~~ I pH I b.'2~ I
Temp. °C I IS,;Z.j I Temp. oc I ls.'Z:j I
Redox Potential Eh (m V) I ~St. I Redox Potential Eh (mV) I qg(; I
Turbidity (NTU) I '3>0 I Turbidity (NTU) I 3Z'> 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 IOO gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I 10,D T=2V/Q= I 3.75 I
Number of casing volumes evacuated (if other than two) I o
If well evacuated to dryness, number of gallons evacuated 0
Name of Certified Analytical Laboratory if Other Than Energy Labs L-1 ..:..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 Ill 0 3x40 ml 0 [j HCL IJI D
Nutrients [] 0 100 ml 0 rn H2S04 1!1 D
Heavy Metals 0 D 250ml 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) Ill D Sample volume D 1!1 D 1!1
L. \., lo r-;de If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 7.51 50 Sample Time
Comment
, ::} See instruction
Arr:ve~ on s;+e 0\.+ l~OO J"~r~nu IMI~ VM'f':fl Pre_s("nr tl>r pv.r~e . H.Are:,e .b~<tr'\ o.t' IYOZ
fv..r~e~ Well ~r o.. ·toi-o.l of 10 M;t'\v.+e~. f'v.r~e endeJ 01.+ l~ l'Z.
~No-.1ec-!.-\)~.~ rv1o~11~ cJe~r. LJ:f s:-tc t:d-JLJI~
Arfl\k~ of' .sit~ ,..+ 0'\'ZJ J:..Me-r (Ill'\~ G-Arr:fl r•e.sel1} to co nee+-Sea.tr~p Je~. DeJ>fh -to vJ()..fer
v..:>c..s b-3.~ So.l"lple.> 'b,.n~~ ~-t o~'Z.~ t.J'.f _s,f~ ~ 6'\~~~
TW4-09 08-02-2016 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 3rO:: Qv.G\rh.r C.h l oro"f~rm 'Q>lb
: (J, See instruction
Location (well name): L...I_I_I.V_4_-....:.f_O _________ ____J
Sampler N arne
and initials: 1-fo.ntrer Ro )I,·J't3hJt
Field Sample ID -rw 1.\-ID ... ogo Y 'ZD\ c,
Date and Time for Purging ._I ....::~:..:.../...;:::;3_/:_v:._J..b _____ _J and Sampling (if different)
Well Purging Equip Used: []!]pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: ~2 casings IQJ3 casings
I 'JWLJ-0/ Prev. Well Sampled in Sampling Event ._ _________ ___J
pH Buffer 7.0 pH Buffer 4.0
Specific Conductance ._I _,o_o_o ___ _,l~-tMHOS/ em Well Depth(O.Olft): ._I -=-ll:....;_I._O_o __ ___J
Depth to Water Before Purging I bZ, 55 Casing Volume (V) 4" Well:l 3}. '::3 ,(.653h)
3" Well: o (.367h) L,_ ___ _J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventl._l _3_l_D _ ___.
Time I \l.\W I Gal. Purged I I Time I I Gal. Purged I I
Conductance I ~o~} I pH I 5,14 I Conductance I I pHI I
Temp. °C I 1?.~ I Temp. oc I I
Redox Potential Eh (m V) I ~==-.s I :,'lb Redox Potential Eh (m V) I I
Turbidity (NTU) I sq I Turbidity (NTU) I I
Time I ~~31 I Gal. Purged I 0 I Time I ~~~ 7., I Gal. Purged I 0 I 6~3Z
Conductance I '30Z.S I pH I "."3:) I Conductance l 3i)2S I pH 16· 'Z<j I
Temp. °C 115,6$ I Temp. oc I lS.o5 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
A f-+er
White Mesa Mill
Field Data Worksheet for Groundwater 1 of2
Mill ·Groundwater Dlschilfll! Permit Date: 06-06-12 Re\1. 7.2-Errata
Ground~atet" Mon.itorins Quality Assurance Plan (QAP)
Volume of Water Purged 60,75 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), 1n gpm. Time to evacuate two casing volumes (2V)
S/60 = I \'0.0 T= 2V/Q =I ~.'32. I
Number of casing volumes evacuated (if other than two) Q
If well evacuated to dryness. number of gallons evacuated 60 .1s l
Name of Certified Analytical Laboratory if Other Than Energy Labs l. "-...... A....;.W""'A...,L::;;........ ____ _,
Sample Vol (indicate
Type of Sample Sample Taken if other than as Filtered Preservative Type Preservative Added
VOCs
Nutrients
Heavy Metals
A11 Other Non Radiologies
Gross Alpha
Other (specify)
c/ ~lor ;~(
~inaJ Depth I 1'0 S. '16
~
.li
11 :comment
y
Iii
" 0
0
D
[lJ
N specified below)
0 3x40 ml
0 lOOm!
0 150ml
' 0 250 ml
0 1,000 ml
D Sample volume
.~
Sample Time
y N y N
0 f,i HCL Ill 0
0 IB H25Q4 I!J 0
0 p PIN OJ 0 Cl
0 0 No Presen'. D D
0 D HN03 D D
0 ID D l'i1
If prcscrvntive is used, specify
Type and Quantity ofPn:senrative:
See instruction
.Lkr:ve.J e-n ~Jte a.t IYZZ "T:.nner ~r'l~ Go.rri11 pre'.le-"f for rv.r,se. Pu.r-% e
fu..~~ed welt .fc;r o.. totG\l o ~· b vYl;n .... tc 4S S~c:.c<'~h, ?~~ LUell dr~.
~oc ~r I.Vt:l::, L\. \ ,+tl~ /l'lo.r~
h~Q~~ ~ -J-IY2Y
Pu.re,~ e.,tJeJ A.+ }Lj'JO
AN"';ued Ol't ..s:te a+ OfSZ~ ~Tlner ~m;}. G-a:rr-111 pr-e51:'11r iu cciJec.t Scvr?plts . Oepfh }., wo.fe,...
WrAS 6'Z..Sb ~Mples 6..-1~~ q-.} Of,:bJ Ldl sl+e &it 0'&33
-.
..__ _______ ---JDo not touch this cell (ShcetNarne)
White Mesa Mill
Field Datil Worksheet for Groundwater ..A 2 of2 Capturx· COMPATIBLE WITH./"-'I,..,ln,--FUNCTIONALITV
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: 3 ra G u.o.r:fer Gh lorof;;rfYl ZD! b
Location (well name): ._I =i____,I,J'-Y-'----'-11 _________ ___.
Field Sample ID
Sampler Name
and initials:
See instruction
Date and Time for Purging I 7/z5/20I-b and Sampling (if different) I._M_VA-________ __,
Well Purging Equip Used: [Q]pump or [QJ bailer Well Pump (if other than Bennet) I CoflfifliAOv-.S
Purging Method Used: [![]2 casings [QJ3 casings
Sampling Event I Qv..,.~'""1"Gr]j Gh 1 o ro:\brm Prev. Well Sampled in Sampling Event ._1_-f ___ /JI_W_~_z_'-___ _.
Mw-Zb
pH Buffer 7 .ol ._ 7_,o ____ _, pH Buffer 4.0 LJ.o
Specific Conductance L--1 _lo_oo ____ ~l ~-tMHOS/ em Well Depth(O.Olft): 100 ,Ol>
Depth to Water Before Purging I qz,5<. Casing Volume (V) 4" Well:l [\, gg 1(.653h)
3" Well: 0 (.367h) .._ ___ __,
Weather Con d. Ext'l Amb. Temp. oc (prior sampling event)._l3_3_" __ _,
Time I l~l K I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance 13 7 7~ I pH I b,'3S I Conductance I I pHI I
Temp. oc Jl~·/7 I Temp. oc I I
Redox Potential Eh (mV) 1 z93 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. Time to evacuate two casing volumes (2V)
S/60 = I /C.,D T = 2V /Q = I 0 I"\ 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 ._I _A_IA)__;_fl _L ______ _,
Sample Taken Sample Vol (indicate
Type of Sample if other than as
y
VOCs III
Nutrients 11:1
Heavy Metals D
All Other Non Radiologies D
Gross Alpha D
Other (specify) !e)
Chlor;de
Final Depth I Gf$','39
Comment
A rr ;vea on s1'+e tAt IY L5
s{;.(Vlple.> collec.+d lA+
lefJ-S rte ~+ ) 4'20
N specified below)
D 3x40 ml
D lOOml
D 250 ml
D 250 ml
D 1,000 ml
D Sample volume
Sample Time 1.___14_1 ~-'-------'
TW4-11 07-25-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
Filtered Preservative Type Preservative Added
y N y N
D IE HCL 1!1 D
D ~ H2S04 1!1 D
D D HN03 D D
D D No Preserv. D D
D D HN03 D D
D ~ D ~
If preservative is used, specify
Type and Quantity of Preservative:
l J, 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 3rll Gv..o.r'fer C:.n I orOforrn 2 b 16
Location (well name): I ""!'WLJ -IZ ~------------------------~
Field Sample ID I 1W4-I'Z._07Z7ZDI'-
Sampler Name
and initials:
See instruction
Date and Time for Purging I 7/'Zb/'Z.o I C.. and Sampling (if different) 71Z7 /zoJ '-~~~~~----------~
Well Purging Equip Used: [![)pump or IQJ bailer Well Pump (if other than Bennet) I GrWllX+~~
Purging Method Used: rnJ2 casings IQJ3 casings
Sampling Event I Gu..o.rl-t:cb C.l-doro:Form Prev. Well Sampled in Sampling Event I Jlt.)Lj-0~ ~------------------~
pH Buffer 7.0 '-1 _7_,_0 ___ __, pH Buffer 4.0 L.\,0
Specific Conductance ._I ..:..:}0=0-'-D ___ ___,I ~-tMHOS/ em Well Depth(O.Olft): I 1D}.50 ~--'--------'
Depth to Water Before Purging I 96:3D Casing Volume (V) 4" Weii:I .:3C,OLj ,(.653h)
3" Well: 0 (.367h) ~---_J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)'-13__._]" __ ~
Time 11395 I Gal. Purged I 70 I Time I I Gal. Purged I I
Conductance I \!;~g I pH I C).ss I Conductance I I pHI I
Temp. oc I I~ alb I Temp. oc I I
Redox Potential Eh (mV) I C\17 I Redox Potential Eh (m V) I I
Turbidity (NTU) I 'l~ I Turbidity (NTU) I I
Time I 081.> I Gal. Purged I 0 I Time I 0814 I Gal. Purged I 0 I
Conductance IIS::\g I pH I b·S7 I Conductance I 1 ~4'1 I pH I C. . .5, I
Temp. oc l l.S . ljS I Temp. oc 115.4:3 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 70 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 7,2D I
Number of casing volumes evacuated (if other than two) I l.Gf9
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I .wA~,.:.;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 In 0 3x40 ml D IB HCL f) 0
Nutrients m D 100 ml D ~ H2S04 (!!) 0
Heavy Metals D 0 250 ml 0 D HN03 D D
All Other Non Radiologies 0 0 250 ml D D No Preserv. 0 0
Gross Alpha 0 D 1,000 ml D D HN03 D 0
Other (specify) fliJ 0 Sample volume D Ill 0 ~
Chlo.-;J~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 99,1 ~ Sample Time 08}.3
Comment
See instruction j
ltn·:\Jed on ~,'te tA..r 1335. ~nne; oJlJ G-"'rr:tl present ~r puree. fu~e .b~C\'7 '\T 133t
Fvr~e~ IA)e\1 -PM" f"-+o-t~l of' 7 IYJ;n~,~.1.~~-Pur~t"a ~ell dr~'-P~r~e ~ndeJ. o.J-J'3t.l5
\Ne1.ter t..>o..~ Mo~t\.j L.l~o..r. L~f+-si+e ~ t J~yg.
A~r ;\)~~ I>Y\ ~,·tl! go.} ogo~ I'Anner '-ria C-o.rrif) r('eSe(J-r -to coiled-So.Mp les. P~p+h +o tNo..+er
w~~ LJ'-.31 SfAI'r'lple.> b;J~J. o-.~ 08!.3 Len .st+c= "'-+ DESI.S
TW4-12 07-26-2016 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 '3r3 Qv-o..1f er Chloroform ZOib
Location (well name):l .__ ==r_,__W_y..._-__.l3-=--------------'
Field Sample ID
Sampler Name
and initials:
See instruction
Date and Time for Purging I 7/27/ZOI.f.o and Sampling (if different) l'--'7c:../.=Zc::'i:)"-/_z_o.;_).b _____ _~
Well Purging Equip Used: (![]pump or [ID bailer Well Pump (if other than Bennet) ._IG_r_u._n.=....J_+o_," so<...-___ _.
Purging Method Used: ~2 casings (ID3 casings
I "TWY-3Z Sampling Event IG.,a-~"'"+~rt~ Chloro-Form Prev. Well Sampled in Sampling Event .__ _________ __J
pH Buffer 7.0 ._I _!_._o ___ ----' pH Buffer 4.0 Ll.O
Specific Conductance ~...1 --l.l.;:;..OD_o ___ ---JI !!MHOS/ em Well Depth(O.Olft): l lOZ.SO
Depth to Water Before Purging I {;'Z • .S 1 Casing Volume (V) 4" WeU:I z c;, 11 1(.653h)
3" Well:~.... _o ___ _J_(.367h)
Weather Con d. Ext'l Amb. Temp. ·c (prior sampling eventl~..-1 Z_$_~ ----1
Time I IOZ.3, I Gal. Purged I ""l:l0 I Time I /0 2.1 I Gal. Purged I 1./0 I
Conductance 1 zng I pH I <;;.~I I Conductance I -z'z 1 I pHI CO.£/ I
Temp. oc I 15,5'-I Temp. oc I IS.3Y I
Redox Potential Eh (m V) I 3 59 I Redox Potential Eh (mV) I '31>5 I
Turbidity (NTU) I lS l5 I Turbidity (NTU) I It ~ I
Time I \030 I Gal. Purged I 5.D I Time I Jo:J, I Gal. Purged 166 I
Conductance I Zl 'i I I pH I ,,,/ I Conductance I Zl .5Z I pHI r,.{;J I
Temp. oc I [5 . :so I Temp. oc I )S.ZJ I
Redox Potential Eh (m V) I :.s:S~ I Redox Potential Eh (m V) I '55L I
Turbidity (NTU) I Jr;,o I Turbidity (NTU) l li.o 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 IO.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=2VJQ= 1 5.zz I
D
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
VOCs I[) D 3x40 ml D !1 HCL ~
Nutrients D D 100 ml D 'tJ H2S04 fJ
Heavy Metals D D 250 ml D D HN03 D
All Other Non Radiologies D D 250ml D D No Preserv. D
Gross Alpha D D 1,000 ml D D HN03 D
Other (specify) ~ D Sample volume D Itl D
Gh\ariJe If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1'---'9_3_.1 .:....) __ __. Sample Time l.__o'--'8!"-"0::._.j1"----'
Comment
,.j See instruction
Arrive.J Of\ ~i'te. t:~~.+ I()Z3 ~nner o.nd. <i-Mr;n
Pv..r~c~ w~\1 +or "'-+o+o.l of b m;rw.}t"~.
Le.tr ~j·h·(A r 1033
pre~~,t -fo.,.. P'-'•~e. ?u.r~e. be~~" ,J-IOZ5
Pur~G c"'dtJ ,..t" 103/. Q,Jcr \.No--S deAr
Arr: \Jej on !)Jte A.t O[fo~ ""f..t1ne..-MJ c.#.JT1°fl pr-c_sef\t ·h collec.:l-_s,.I'Vlf)e.;.
IIJ~;~S 6Z.'S~ So.mpleS bo.:JeJ A+ ~0807l...eft ..s}fe dlj 0801
TW4-13 07-27-2016 lno 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
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I .3~"0 Qv.o.rfer ChlorJD(fV\ '2.0/L
See instruction
Location (well name):l L.. _J\,.)..:......:..._4.:...-'....:l....:Y _________ ---'
Sampler Name
and initials: FfMei HoJl,J,\"/'111
Field Sample ID
Date and Time for Purging I 3/zlzoJ).. and Sampling (if different)
Well Purging Equip Used: (![]pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [1[]2 casings [QJ3 casings
Sampling Event I Q~rfcr LJ C\, \orotbrM Prev. Well Sampled in Sampling Event L...I_T'_w_Y_-_2_7 _____ ....~
pH Buffer 7.0 pH Buffer 4.0
Specific Conductance L-1 _lo_(JO ___ --.-JI[.tMHOS/ em Well Depth(O.Olft): Ll _q:..=3...:.....D_l> __ ___J
Depth to Water Before Purging I 7'1. S:S Casing Volume (V) 4" Well:l g,7~ 1(.653h)
3" Well:L.. . ....:o ___ ....J.(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)L-1 Z_Lj..:...1> __ _.
Time I 64 4'1 I Gal. Purged I LS I Time I I Gal. Purged I I
Conductance I f,3 \~ I pH 1 6.17 I Conductance I I pHI I
Temp. oc I lc; ,'YZ. I Temp. oc I I
Redox Potential Eh (m V) I q'1 ~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I }00 I Turbidity (NTU) I l
Time I oK9Z> I Gal. Purged I {) I Time I ogy1 I Gal. Purged l o I
Conductance I 53~~ I pH I t;.37 I Conductance ls~~8 I pH 16.38 I
Temp. oc I 15.\0 I Temp. oc 1 \5 ~o'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 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
Volume of Water Purged IS gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I 10.C> T = 2V /Q = I ,, 75 I
Number of casing volumes evacuated (if other than two) I ,,1o
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) y N y
VOCs I] D 3x40 ml D [J HCL 111
Nutrients I] D 100 rnl D C!l H2S04 1!1
Heavy Metals D D 250ml 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) fil D Sample volume D rn D
Gn \or;J~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1._-'-q 0-''=K3=-----~ Sample Time ._I _D"""Es'-'4c::....b __ _.
See instruction
Comment
Arrived Of\ 5i+G "':t o~~s lo.tlner ttnJ. Go.rri" rf~('l\t .for ?v.r~-e . H ... r~e b~~~~ ~~~t 04Ll8
f'w~f~ IM'!ll -for u... to+4l o-f 1 M~flv..+e 3<> ~cc.on~s . fu.r~·d (JJe)} Jr~'· ?ur~e ended ~t
C>CJqq_ tNJ-e-r W1-s, mv..r\<~, L~ ~~-+c: tA1 095)
Arri'l)e~ on si+e ~+ 0'637 -ro..llner o-TlJ Go.rr•'n f<"~~nt fo co/J~G+ ~"'""P't'"s . Deffl, 1 ~cr
wOo,) 1 Gl. G,(:, So.M p1c:::a "bo.•'le-a ~+ ogryb Lef1' .:lite ll{t Dg~ z
TW4-14 08-02-2016 lDo 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
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I '3 1a Qv.Q./}e(" Ch lcro+OffV'I ZOJ(..
See instruction
Location (weJI name): I.__M~W-=---z.b~----------.1
Sampler Name
and initials: I :::y;,ner Ho!L~~/1}f
Field Sample ID
Date and Time for Purging I //ZS/Z0\4 and Sampling (if different) .___/l/.....:..Y,_:A ________ ....~
Well Purging Equip Used: [![}pump or [QJ bailer Well Pump (if other than Bennet) I Co(l tinv.ov...S
Purging Method Used: 002 casings [QJ3 casings
Sampling Event I Ov.arferl~ c~ I orOforrVl Prev. WeJI Sampled in Sampling Event l.__w __ L_l-_2_0 _____ ___,
pH Buffer 7.0 7.0 pH Buffer 4.0 I 4.o
Specific Conductance L..l _\_0_0_6 ___ __.1~-tMHOS/ em Well Depth(O.Olft): }2'2.5D
Depth to Water Before Purging I G,4.7D Casing Volume (V) 4" Wcll:l ~ 1,1'""\ ,(.653h)
3" Well: l> (.367h) .___ ___ _,
Weather Cond. Ext' IAmb. Temp. ·c (prior sampling event)._l '3.:...'3-"--0 _ ___,
Time I IYII I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance 1 ~srz. I pH I b. '2.~ I Conductance I I pHI I
Temp. oc IJ{;,qq I Temp. oc I I
Redox Potential Eh (mV) 1 -z.sl I Redox Potential Eh (m V) I I
Turbidity (NTU) 17.! 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 7, b
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 q.q5 I
D
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I __,_A,_\-)_,A..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 N
VOCs Ill D 3x40 ml D 111 HCL [ll D
Nutrients IB D 100 ml D 1:!:1 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) IE D Sample volume D rtJ D ~
L hlofl'de If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 'iS ). 33 Sample Time
Comment
1 rJ See instruction
Arr;vej on ~~+e d\-t 140fS --r;_llner a/\a G-lilrr·'n rre.serJ +o Golled-So.mp1es .
.SI\rYlfJo collected (}..+ 141'l. \A)ct+er w~ clea-r
Left s,1t: /)\+ J 414
MW-26 07-25-2016 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 3r6 G I.Ao..("ter C\1\\onJorm 20 lk
See instruction
Location (well name): ._I _Ji_W----'l.J'----'1 C.;;.__ ________ ~ Sampler N arne ~
and initials: I =r;.fln~l"' Ro JJ1 ~ 77}}
Field Sample ID
Date and Time for Purging L-1-~_/_z_/_-z._o_l"-____ _____. and Sampling (if different) 8/..3/?Dl' ~--------~
Well Purging Equip Used: [l[)pump or [QJ bailer Well Pump (if other than Bennet) I Gcu.f1Jfc>s
Purging Method Used: 002 casings IQJ3 casings
Sampling Event I Q uCArt~~~ Chl onfonYl I Prev. Well Sampled in SamplingEvent._l_'l"_W_LJ_-_0_~ ____ -.~
pH Buffer 7.0 7.0 pH Buffer 4.0 4.o
Specific Conductance ._I _1 C>_o_o ___ _,l 11MHOS/ em Well Depth(O.Olft): I J9 Z,D D
Depth to Water Before Purging I GLJ . 6~ Casing Volume (V) 4" Well:l S0$"1 1(.653h)
3" Well:~..-. _o __ ----l_(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventll._ 3_3_0
_ _____.
Time p9q) I Gal. Purged I gv I Time llYL\'Z. I Gal. Purged I q~ I ~
Conductance I ~q-zs I pH I k-.17 I Conductance I :)'j'Z.(. I pHI 6.19 I
Temp. oc I 15.\g I Temp. ac 1,5.1Z I
Redox Potential Eh (m V) I 9~ 7 I Redox Potential Eh (m V) I qqj I
Turbidity (NTU) I 119 I Turbidity (NTU) I 1_.6 I IZO
Time I )I:Jq:s I Gal. Purged I t05 I Time li;{ I Gal. Purged I liD I
Conductance I ~9-:)0 I pH I ,,Jq I Conductance l3j~~ I pH 1 {;,zo I
Temp. oc I 15 ,1 5 I Temp. oc 115.!4 I
Redox Potential Eh (mV) I qq1 I Redox Potential Eh (m V) I g~ I
Turbidity (NTU) I 1~1 I Turbidity (NTU) I '~3 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 110 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60= I )O .D
Time to evacuate two ca ing volumes (2V)
T = 2V/Q = I 10 I I I 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 ..:..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) y N y N
VOCs IE 0 3x40 ml 0 rn HCL ~ 0
Nutrients 0 0 lOOm! 0 1!1 H2S04 [!] 0
Heavy Metals D D 250m! D D HN03 D 0
All Other Non Radiologies 0 0 250 ml 0 D No Preserv. 0 0
Gross Alpha 0 0 1,000 ml 0 D HN03 0 0
Other (specify) ~ 0 Sample volume D 01 0 ~
Ch)or:Jc If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1 1~7 • IZ Sample Time L..l O.:........!q _-:s_z __ _J
Comment
rJ See instruction
Arfi\)e.J on St+e ~.t· lY7:>Z ~ o.nner IMJ. &~rr•'(\ pre.sent +~r '?LA("~~. P~r~~ b~d"" 11\J }L)33
P~A.r~~c) well ~r o.. +ot~J ~ ll M i nvJe~. P\Ar~e e~Jc~ o..r )t..\Y~
INtA..ter \NO...s. o.. 1itfl-c or~,~~ mu.r)(~, L"Cfr srt~ 4-lY47
Arr;ve~ on s;te ,J CY-lza..lo.l'lntr o.f)O. G-o.r<i" p rt!Se.'\+ +o coll("c.} 5~f'l"'rle.s. De;>-11, fo wo..hr
wa.....s b~.ZL\ . So.YV\ple~ bo,.;\ea a-.1-a<f3Z Le..rl ~tte a-.+ oq3y,
TW4-16 08-02-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater 2 of2
Mill-Groundwater Discharge Permit Groundwat,')Monlto:~rlg Qualitv Assurance Plan (QAP) (
Date: 06.{)6-12 Rev. 7.2. Errata
ATTACHMENT l-2 e#,..,.,,_...,._L. WHITE MESA URANIUM MILL "./ See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description ofSamplingEvent: I '01"0 Ql.kD..rhr C:hloco£rrr1 Z DI~
Sampler Name
Location(wellname): I MW -~Z and initials: I =--t;:,HH:r HeiJ ,Jt.!j /=fll
Field Sample ID
Date and Time for Pmgiog IL--~~:.;.../.:....oi7....!./..:::Z~O~Ik;.._ __ ____. and Sampling (if different)
Well Purging Equip Used: ~pump or I 0 I bailer Well Pmnp (if other than Bennet) IGED
Purging Method Used: ~2. casings (£]3 casings
Sampling Event I GN.0. rh,rl"\ ChI oro forM Prev. Well Sampled in Sampling Event ._I T_· _W_L_1-_/_D _____ _,
pH Buffer 7.0 1...........,.,_.7_,_,1 Q.,__ __ _, pH Buffer 4.0
Specific Conductance l.__....:.io""'o:.ooc.,__ __ _.lllMHOS/ em WellDepth(O.Olft): l l3'2'.5D
Depth io Water Before Purging I -n . i I Casing Volume (V) 4" Wel l:l 3 5,77 ,(.653h)
3" Well: o (.367h) ,___ ___ _.
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)'-j .:..114:::..~--...J
Time I \"2.3>72. I Gal. Purged I 7o.jS I Time I IZ~3 I Gal. Purged l 7l .1] I
Conductance I :)9L\1 I pH I ~.4Y I Conductance I 3"l ~l I pH I b.3~ I
Temp. oc I lf),L.\b I Temp. oc I I'S/3~ I
Redox. Potential Eh (m V) I !J OI I Redox Potential Eh (mV) I Y93 I
Turbidity (NTU) I l.l .~. jl Turbidity (NfU) I rz, G.. I
Time I f"i:~lj I Ga I. Purged 1:7 1.3:\ I Time I 1-z.3z, I Gal. Purged I :z ,_, \ I
Conductance I Sj'Z.l. I pH I C,;3jD I Conductance I ~~J:~O I pH I ,,'Z,fl ·I
Temp. oc I rS.Z7 I Temp. °C I IE-..1 '-I
Redox Potential Eh {mV) I '1'~'3 I Redox Potential Eh (rnV) I y:z; I
Turbidity (NTU) I J'~.o I Turbidily (NTU) l r~.o I
White Mesa Mill
Field Data Worksheet for Groundwater .A 1 of2 capturx• COMPATIBLE Y!ITM~ .... oJ.tr-FUNCTIONALITY
Mill-Groundwater Discharge Permit Date: 06-0f>-12 Rev. 7.2-Errata
Groundw~s~ Monitroing Quality Assurance Plan (QAP)
Volume of Water Purged 71. b l gallon(s)
Pumping Rate Calculation
Number of casing volumes evacuated (if otber than two) o '------'
If wen evacuated to dryness. number of gallons evacuated .... 1 c-___ __.
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 ll:ZI ·o · 3x40 ml 0 ~ .HCL ua D
Nutrients ~ D lOOm! 0 [II H2S04 fEI 0
Hcm'Y :Metals 0 0 ;25Qm1 0 c;J H'N:03 D 0
All Other Non Radiologies 0 0 , f2.5Qml 0 . 0 No Preserv. 0 0
Gross Alpha 0 0 1,000 ml 0 0 NN03 0 D
Other (specify) Sample volume I
liJ 0 0 .ril 0 B
C h \or ;Jc If preservative is used, spccity
Type and Qunntity of Preservative:
l ~Final Depth I K'!;?, 0 I Sample Time
See instruction
~Comment
An-i\le~ on s;te a.t c?7Dl. --r:_o1n~r o.ntA G"..._n-:~ f'e~n+ ~;c-·pv.r~e and Sa.""pl...-.~ event.
Pv.r:~e be~a.(\ lA~ 07DS. ?w~e:J We)\ -+;·<'" ""-+ot.,.l o+' '3.3D )'Y7lfHATeS.
P\.Ar ~e en~eJ cv1e\ S~Aw,p)e~ Co He c.tccJ "-t JZ35 t.J"-+el'"' Wa...S rnos.16 C )eetr
lett s,'-J--e CA+ JZYY
'------------------~ Do not toucl1 this cell (SheetName)
White Mesa Mill
-
Field O.al:a Worksheet for Groundwater ~ 2 of2 capturx· COMPATIHE WITH,/'-,_..pli;r-fUNCTIONALITV
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: 1 ~r~ Q:AO:r:f~ Chloro:Porfl"1 zolrt>
See instruction
Location (well name): ._IIW_:_:__Y,;_-_I_S _________ __J
Sampler N arne
and initials: t'f:nn~r Ho 11:d<t17JJt
Field Sample ID 11'W~ -)<g_ 0&03"20/1 ..
Date and Time for Purging L-1 _8_;z_7_·z_o_l.f. _____ _J and Sampling (if different) '--18_7_.3_/_zo __ I"' _____ ____J
Well Purging Equip Used: [Q]pump or [QJ bailer Well Pump (if other than Bennet) IGrvnatb 5
Purging Method Used: ~2 casings [QJ3 casings
~------.---;--:--,...,.~-f"-f"r::----, 1 )\A.) y-o s
Sampling Event I Qu.~r'fer8 CllfllorOTDri'VJ Prev. Well Sampled in Sampling Event '-----------__J
pH Buffer 7.0 ._I 7_,_o ___ _~ pH Buffer 4.0 q.o
Specific Conductance ._I _IOOo ____ ___,~l~-tMHOS/ em Well Depth(O.Olft): I \3 7, SO
Depth to Water Before Purging I bb. OD CasingVolume(V) 4"Well:I4G;.Gg 1(.653h)
3" Well: D (.367h) '-----_J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventll._ 33_<~> __ _,
Time I 133Ll I Gal. Purged I go I Time 11332 I Gal. Purged I· .ct~ 90 I 90
Conductance I \q~7 I pH I f,,'f3 I Conductance 1 11~3 I pH I 5/15 I
Temp. °C I l5ai5 I Temp. oc l l~·'' I
Redox Potential Eh (m V) I '471 I Redox Potential Eh (mV) I q7b I
Turbidity (NTU) I 3~ I Turbidity (NTU) I ~7 I
Time I l':>3l: I Gal. Purged I \00 I Time I tY37 I Gal. Purged I Hli I
Conductance I 1qzo I pH Is.~" I Conductance 11~'-q I pH I S/f.(. I
Temp. °C I 15,77... I Temp. ac I l5,7l I
Redox Potential Eh (m V) I q6~ I Redox Potential Eh (mV) I 4~8 I
Turbidity (NTU) I 7:>]_ I Turbidity (NTU) I 37 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 Ito gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
s16o = ~.-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 casing volumes (2V)
T=2V/Q= 14.53 I
lo
Name of Certified Analytical Laboratory if Other Than Energy Labs L-1 ~A_IJ_,il\_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 1!1 HCL 'f]
Nutrients t:l D 100 ml D 0 H2S04 Ll
Heavy Metals D D 250ml D D HN03 D
All Other Non Radiologies D D 250ml D D No Preserv. D
Gross Alpha D D 1,000 ml D D HN03 D
Other (specify) lJ D Sample volume D r:J D
Chlo,;Je. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I b', 28 Sample Time ~-1 ...:...D.....:.q..:....l7:...__ _ __,
See instruction
Comment
Arrive~ Of\ ~rte Ai' \524, -Jo-nner ~n~ Go.n··;"' pr-e.selli-for 'P"'"f~f -Y:t ... r-5-e b~~{"'l ~A.+ )3U
Pv..r~::fa (l.)e)l tor 0\ +.J~I 6r n )'Y);)11A+6 I ?v..c-(JG endeJ o..+ +:ilt \337
wo.:fer (;,)~ ().. \:Hlc. Mv.('k~ Left .srtc "t' \'3YO A(c:\)e~ on _s1'te ~+ 0'1\Y ""lo.nn~ Mc.l G-o-rrin pre.S~f1+ fo collec.} ~~nf]~5. · .Dep-fh to
wo.-h:r wo.S ~C:..O.S ~o..Wl~/6 btl\ile-d o..+ oq17 LeJ} s1+e ~t oq1~
TW4-18 08-02-2016 loo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
D
D
D
tJ
2 of2
Mill-Groundwater Discharge Permit Date: 06-06-12 Rev. 7.2-Errata
Groundwater Monitoring Quality Assurance Plan (QAP)
ATTACHMENT 1-2 R""e,;;NERGYFU'EU WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 3 r 0: Qu.o..rfer 01 I 0 roform ZD I b
Location (well name): I._1\--=--W_4--'----=-l1,__ ________ _,
Sampler Name
and initials: 1-r.;.nne:r Holl ,'J"'.j/nJ
Field Sample ID I TW4-Ij_ 07Z5'ZOI(.
Date and Time for Purging I 7/25/ZDib and Sampling (if different) .__/V_I._:4 ________ _J
Well Purging Equip Used: [![]pump or [QJ bailer Well Pump (if other than Bennet) lun+•nv..ov...S
Purging Method Used: [![)2 casings [QJ3 casings
Sampling Event I Qv..~Arte:rb GnlorO\"orm Prev. Well Sampled in Sampling Event l..__-n.> __ Y_-_0_4 _____ -J
pH Buffer 7.0 /,D pH Buffer 4.0 Y.D
Specific Conductance Ll .....:..::\o_o.=.o ___ _.l !!MHOS/ em Well Depth(O.Olft): I 12.5, Oil
Depth to Water B~fore Purging I bY . 1 '2. Casing Volume (V) 4'' Well:' ~'1.15 ,(.653h)
3'' Well: 0 (.367h) ..__ ___ _J
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)l._.3_i3_li __ _J
Time I l\.\ 5~ I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I '2.qo-z I pH l c;,.z.& I Conductance I I pHI I
Temp. °C I \J,\5 I Temp. oc I I
Redox Potential Eh (m V) I I...\D8 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. °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 Cal ulaLion
Flow Rate (Q), in gpm. Time to evacuate two asing volumes (2V)
S/60 = I 1 g,D T = 2V /Q = I L). 41 I
Number of casing volumes evacuated (if other than two) D
If well evacuated to dryness, number of gallons evacuated 0
Name of Certified Analytical Laboratory if Other Than Energy Labs Ll !...:lt~VJ:.:.It..:..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 B 0 3x40 ml 0 'El HCL f) D
Nutrients E 0 100 ml 0 !] H2S04 E) D
Heavy Metals D D 250 ml D 0 HN03 D D
All Other Non Radiologies D 0 250ml D 0 No Preserv. D D
Gross Alpha 0 D 1,000 ml D 0 HN03 0 D
Other (specify) ~ D Sample volume 0 ~ D ~
Chlor;Je. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 6g ,y(. Sample Time lSOb
See instruction
Comment
Acr'l\)e~ 0{\ s~h~ ~+ )4.SC. -r=.nner o-nJ G.,.rr:n pre~e'lt +o collec.t ~--r>1rle.s.
Su-Mfb c..o llec+~J o..i l SOD ~ter L.)el.S Mo~t~ cleo/
letr sit~ a.-.4-l so~
TW4-19 07-25-2016 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 3 •3 Gv;zu leFtS Q J.Arfer C.h I o nH:;, rm ZC>Ib
Location (well name): l.__~_w_y_ ... _Z_D _________ ___,
Field Sample ID
Sampler N arne
and initials:
See instruction
Date and Time for Purging L..l ....:..7/~z.s----=.:....;/z:;;;..._o;.;;;lt.;__ ___ --l and Sampling (if different) .__N.;.:;V...:..:4:....._ _______ ...J
Well Purging Equip Used: [f[Jpump or [QJ bailer Well Pump (if other than Bennet) I G1vJ ;tll}.Oo.J.S
Purging Method Used: [f[]2 casings [QJ3 casings
Sampling Event I Qv..o.r:fer~ C.), Joro.f'orM Prev. Well Sampled in Sampling Event I._Jt_W_LJ_-_3_7 _____ --.~
pH Buffer 7.0 1.__7,;_:,,_1> ___ _, pH Buffer 4.0 y,D
Specific Conductance ._I ___,:,1.::....:06:..:0=------~~ ~-tMHOS/ em Well Depth(O.Olft): I 106.00
Depth to Water Before Purging I b3, BD Casing Volume (V) 4" Well:l '2..7,S05 1(.653h)
3" Well:L.. . ....:::o ___ _,_(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)I._3.:....;:S_D __ _,
Time I \q0.3 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I ~7Yo I pH I l::)\ I Conductance I I pHI I
Temp. oc I \7. :z:o I Temp. oc I I
Redox Potential Eh (m V) IJ>&Y I Redox Potential Eh (m V) I I
Turbidity (NTU) l id~ 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 = L--1 ___;:G::;,_'..:...I __ _..
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 q.6,3 I
0
0
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I ..... Jr_,_\J_,A.o..;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 ~ 0
Nutrients tl D 100 ml D ~ H2S04 ~ D
Heavy Metals D D 250ml 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 1!1 D ~
Ch )or;Je-If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 7 Z. 17.. Sample Time
See instruction
Comment
A(r;.Je~ on f, i fe o-t I~Ol> -r;:.nne<'" MJ G-~rr; f\ pf'"eS~tlf f o c.o)/-ec.+ ~"\""rlc.c;.
t0o.te(" \A)~_> c.o\\ec.+eJ o-.+ llJ0'-1 1...)"'-+er-I.A)O\.-S. Mtl~t~ C.lc~r-
Left srt~ cA.f )l.JDI
TW4-20 07-25-2016 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 3'(): Q v..o..r"fer Chloco*~rtvl '20 II.:.
See instruction
Location (well name): ._I_"TW __ ~_-_'Z._) _________ ___.
Sampler Name
andinitials: I ::Y~fll'\er ~cli,Jqjh/1
Field Sample ID I 'TIJ4-'ZI_ oTz5zo f'
Date and Time for Purging I 7/'ZS/ZOI.b and Sampling (if different) Ll N:....::!..V..:..:I:!:..__ _______ _J
Well Purging Equip Used: IT[] pump or [QJ bailer Well Pump (if other than Bennet) I Gor'lf, t11Aov.S
Purging Method Used: ~2 casings 11[]3 casings
Sampling Event I Quo.Mer~ Gh l of'"otor!Yl Prev. Well Sampled in Sampling Event 1-r W Y-£0
pH Buffer 7.0 . 7.0 pH Buffer 4.0 4.0
Specific Conductance ._I _1_0_tJ_o ___ _.JI~-tMHOS/ em Well Depth(O.Olft): I l2J.OZ)
Depth to Water Before Purging I bi, g5 Casing Volume (V) 4" Well:l ~l.\."70 1(.653h)
3" Well:~.-. _b __ -J.(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)o.;:;IS2=..:;." __ _.
Time l l3 l4 I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance l 4b'lg I pH I S.lf9 I Conductance I I pHI I
Temp. °C l l7r )5 I Temp. oc I I
Redox Potential Eh (m V) I slll I Redox Potential Eh (mV) I I
Turbidity (NTU) 1 z .~ 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 (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 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I Jb,O
Time to evacuate two ca in o-volumes (2V)
T=2V/Q= I y,~ I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs IL....!...;A:....:.W.:..:Il....:...._L _____ ____.J
Sample Taken Sample Vol (indicate
Type of Sample if other than as
VOCs
Nutrients
Heavy Metals
All Other Non Radiologies
Gross Alpha
Other (specify)
c'n)or~Jc
Final Depth I 7Y. 'i5
Comment
1~14
o.t ~~f(lp)~.s collec.t~a
Le fi .S. ;+c "J 13 'Z"Z
y
Ill
[B
D
D
D
~
N specified below)
D 3x40 ml
D 100 ml
D 250 ml
D 250 ml
D 1,000 ml
D Sample volume
Sample Time 1320
TW4-21 07-25-2016 Ina not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
Filtered Preservative Type Preservative Added
y N y N
rn ~ HCL ~ D re ra H2S04 ~ D
D D HN03 D D
D D No Preserv. D D
D D HN03 D D
~ ttl D ~
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 WORKSHEETFORGROUNDWATER
Description of Sampling Event: I ~rO: G\.Ao.f"fer C hlorOfo rM ZO/.b
Location (well name):l ._ _'Tc...v.:J_Y_-_zz __________ __,
Field Sample ID l 111-)LJ-zz_07ZS7.oJ{.
Sampler Name
and initials:
See instruction
Date and Time for Purging I 7/Z::S/ZOl-b and Sampling (if different) ~..-M____;.v.4 ________ ...J
Well Purging Equip Used: !][)pump or [QJ bailer Well Pump (if other than Bennet) I G of\'f , rl~
Purging Method Used: [!]2 casings (QJ3 casings
Sampling Event I GWJ.rfer6 ;\) ;fr~fe Prev. Well Sampled in Sampling Event IL-_--nu __ '-l_-_2_4 _____ _)
pH Buffer 7.0 7,0 pH Buffer 4.0 Y.D
Specific Conductance ._I_IO_O.....:O=--. __ __JI!J.MHOS/ em Well Depth(O.Olft): ~--~ ..:..;11-=3;.;.;.5=-0--___.J
Depth to Water Before Purging I 5$ · 18 CasingVolume(V) 4"Well:l 3t'D.)Z 1(.653h)
3" Well: 0 (.367h) .._ ___ _J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._l :3-=0:;_0 __ __,
Time I l 3'1~ I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I t; /1'1.. I pH I ~.3b I Conductance I I pHI I
Temp. oc I n;.zl I Temp. oc I I
Redox Potential Eh (mV) I qzz I Redox Potential Eh (mV) I I
Turbidity (NTU) I ;,,; 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. 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 lB.D
Time to evacuate two casing volumes (2V)
T=2V/Q= I Y.DI 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 IL-L-A_,_,W'-'-L..AL..:L::...._ ____ _..
Sample Taken Sample Vol (indicate Filtered Type of Sample if other than as
y N specified below) y
VOCs 1}:1 0 3x40 ml 0
Nutrients Ill 0 100 ml D
Heavy Metals D 0 250 ml D
All Other Non Radiologies D 0 250 ml D
Gross Alpha D 0 1,000 ml D
Other (specify) IE 0 Sample volume D
C hlor idL
Final Depth I 'l g. 3S Sample Time 13.5l>
Comment
Arr;v~~ ~n ~,'te o..f 13Y-b ~nner
~o..Mpks c/)11€t)eJ ""} l3SD
LeD .s I+~ ~+-l3SL-
ttnJ G~~.;rit') fre..s.~(l f-ft>
lVOi. .J-et" w~.s.. Lleo.,.(.
TW4-22 07-25-2016 loo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
111
1!3
D
0
0
[)
Preservative Type Preservative Added
y N
HCL Ill D
H2S04 rJ D
HN03 0 0
No Preserv. 0 0
HN03 D 0
D ~
If preservative is used, specify
Type and Quantity of Preservative:
tl 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 y(J... Q'->.o.r+er C..h loroForrYJ ZOl(.
See instruction
Location (well name): L.lli__;_,;_l-)_l1.:..'_0 __________ __,
Sampler Name
and initials: l~nner Hoi ),J~/r}}
Field Sample ID
Date and Time for Purging 143 &/z./zo}f., and Sampling (if different) IVYZOI-f.
Well Purging Equip Used: m::Jpump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: [][}2 casings [9]3 casings
Sampling Event I Gv.o..rftd; C. h \oro+orm Prev. Well Sampled in Sampling Event ~...l_--r\-) __ 4_-_3S ______ _J
pH Buffer 7.0 7,0 pH Buffer 4.0
Specific Conductance! L.... ....:..lo:..::o_o ___ __,~IJ.lMHOS/ em Well Depth(O.Olft): Ll !..!.ll~..!.!'..:..oo __ _.~
Depth to Water Before Purging I b 9, 41 Casing Volume (V) 4" W 11:1 -z.g, 75 ,(.653h)
3" Well: 0 (.367h) L----.......l
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl.._l Z_l;.....0 __ ......J
Time I 6 ~l.\q I Gal. Purged I bO I Time I 08SO I Gal. Purged 170 I
Conductance I ~/4Z I pH I ro,-z"' I Conductance I ~1Y7 I pH I ,,z:s I
Temp. oc I ]q,~q I Temp. °C I ~~.91: I
Redox Potential Eh (m V) I 9 n; I Redox Potential Eh (m V) I tnz I
Turbidity (NTU) I g~ I Turbidity (NTU) f 11Z l
Time I 0~~1 I Gal. Purged I go I Time I o ssz. I Gal. Purged I 10 I
Conductance I '':>79/ I pH I b,Z.S I Conductance 1 31~1 I pH I C:z.tt I
Temp. °C I Ill ,9 (; I Temp. °C 1 14.4g I
Redox Potential Eh (m V) 1970 I Redox Potential Eh (m V) I Y"7 I
Turbidity (NTU) I '1'Z I Turbidity (NTU) I qo 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 qo gallon(s)
Pumping Rate Calculalion
Flow Rate (Q) in gpm.
S/60 = I \Q,O
Time to evacuate two ca ·ing volumes (2V)
T = 2V /Q = I 5 .7_5 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.._.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 tl D 3x40 ml D ll HCL ~ D
Nutrients t:l 0 100 ml D 1!1 H2S04 ~~ D
Heavy Metals D 0 250 ml 0 0 HN03 0 0
All Other Non Radiologies 0 D 250 ml 0 D No Preserv. D D
Gross Alpha 0 D 1,000 ml D D HN03 D D
Other (specify) lJ 0 Sample volume 0 1J 0 ~
Gh lor ;d< If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 86.40 Sample Time
Comment
.-j See instruction
An-;ve~ Otl Sitt! ll.t 08~0 ,;.1111e.,.. MJ. Go.rri,., presef'J+ ~. fu-.r~~ _ ?u.o~~ bc~·~Ci" ~+ ()gLO
Pu.r~b, INd\ tor "' -}J,..[ of' ~ m jnv..t<s.. Hu~e e~Je~ o.+ ~ 0&52
\o.!)o._hr ~GI.~ 0,(\ Of"M~e c.olor \ L..)~+~r S\o~\~ WO.!> L'~o.r·n~ "~ flu.r~e ~ef'\t 011 . Lc:t-1-sih u..+ og:ss
Arr; \.Je~ on ~i·h~ ,J O~t.tl -r;_11t\e~" 11\tld. G-""rr;fl ?re~<!!"} -h c.ollecf s.o.mpks. Depth +o Ui.fer
1..36.!::. b9,q~. ~"mp\e~ ~;It'd o..t O~'Z~ L.J1 s.rJ-c o..J-ogz.s
TW4-23 08-02-2016 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 ~ ~ ra Qv.~rfer ChI Of'"C>tbrm ZOI.l:.
See instruction
Location (well name):l ,_ TW __ Y_-_2_4 _________ _.. Sampler Name j
and initials: I ==r;.llfl '' t}o/), ~ li'H
Field Sample ID liW4 -z9_D7252e>lt
Date and Time for Purging I 7/25/ZOtOb and Sampling (if different) l._M_0_::4 ________ __,
Well Purging Equip Used: @pump or [QJ bailer Well Pump (if other than Bennet) I Cor1f•fliAC>lA.S.
Purging Method Used: @2 casings [QJ3 casings
Sampling Event I Qv..o.r+utj Ch\oiofor(Y) Prev. Well Sampled in Sampling Event I WY-Z.5
pH Buffer 7.0 7,0 pH Buffer 4.0
Specific Conductance ._I _lo_o_o ____ _,IJlMHOS/ em Well Depth(O.Olft): I JIZ.SD
Depth to Water Before Purging I 61. 85 Casing Volume (V) 4" Well:l :S3.07 1(.653h)
3" Well: 0 (.367h) .___ ___ _,
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)l._'3_Z_0 __ _,
Time 1 ,3,o I Gal. Purged l o I 1390
Time I I Gal. Purged I I
Conductance I ~S91 I pH I ~;;,19 I Conductance I I pHI I
Temp. °C I lt;.zz I Temp. oc I I
Redox Potential Eh (mV) 1 q53 I Redox Potential Eh (m V) I I
Turbidity (NTU) I '25 I Turbidity (NTU) I J
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 6 gallon(s)
Pumping Rate Calculation
Flow Rate (Q) in gpm.
S/60 = I 1 b ,'()
Number of casing volumes evacuated (if other than two)
If well evacuated to dryness, number of gallons evacuated
Time to evacuate two ca i ng volumes (2V)
T = 2v /Q = 1 9. r:s 1
l o
N arne of Certified Analytical Laboratory if Other Than Energy Labs Ll .:...: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) y N y N
VOCs lJ 0 3x40 ml D ~ HCL !J D
Nutrients [I 0 100 ml D ~ H2S04 1:1 D
Heavy Metals D 0 250m] D 0 HN03 D 0
All Other Non Radiologies 0 0 250m] 0 0 No Preserv. 0 0
Gross Alpha 0 0 1,000 ml 0 0 HN03 D D
Other (specify) ~ D Sample volume 0 ~ 0 ~
C. hlor;Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I b <'!, l!f f! Sample Time l3YI
See instruction
Comment
A('r~ve~ ol'\ sl.fe "'1-1~36 ..,.;.1\0('1" ""~ CTGrr:(\ pre.ien+ -h celled ~-.mpJe~.
~""'P\e~ c.oHed~j o-.1-13YJ INo..--Ter v.:>~ I'YlostS cJ<:t:.if'
Lc\1 s'1+e Q..t \~LL5
TW4-24 07-25-2016 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 ::srdl 0v.o.r+er Ch lo.-Of6rm co }-f.
~-See instruction
Location (well name): I T\JJ~-2...5 ~--~--------------------~
Sampler Name
and initials: I lo..nner 8o JI,J(1.~ ln~
Field Sample ID
Date and Time for Purging I 7/2S/-zo/C... and Sampling (if different)
Well Purging Equip Used: !]]pump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event IQ\).(Ac+er~ Lh\orooto(f'V\ Prev. Well Sampled in Sampling Event .__I_'T_IJ_Y_-_2_1 _____ ~
pH Buffer 7.0 7.0 pH Buffer 4.0 4.0
Specific Conductance!'--_\_00_() ___ __,11-lMHOS/ em Well Depth(O.Olft): I )34.80
Depth to Water Before Purging I b9. 8Zf Casing Volume (V) 4" Well:l YS. C.S 1(.653h)
3" Well: 0 (.367h) ~-----'
Weather Cond. Ext' IAmb. Temp. oc (prior sampling event),__j :3--=2-D _ ____.
Time I 13'26 I Gal. Purged I ~· 0 I Time I I Gal. Purged I I 0
Conductance l z.g-z.o I pH I G:),Lj'Z I Conductance I I pHI I
Temp. °C I lb rSq I Temp. oc I I
Redox Potential Eh (mV) I CJi~ I Redox Potential Eh (m V) I I
Turbidity (NTU) I S.3 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 6 gallon(s)
Pumping Rale Calculation
Flow Rate (Q), in gpm.
S/60 = I 14.4
Time to evacuate two ca ing volumes (2V)
T = 2V/Q =I C>.'Jj I
Number of casing volumes evacuated (if other than two) 0
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
y N specified below) y N y N
VOCs El D 3x40 ml D f!] HCL f) D
Nutrients ~ D 100 ml D IEl H2S04 E1 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) tsJ D Sample volume D El D tJ
Ch)or ;Jr If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I \05, \7.. Sample Time
See instruction
Comment
Arr··\J~~ 01'\ s.ite ~t l'3'Z.3 -r;.Mer tM~ &o.rr~n y:>re~e(li-to collect s~rl~
( \ ll I \ + \37-'-• '"ter w~.s c.J~a.r ..::>Q((tf e..s co e cr eO 0\. w v--
Le\1 S i+ e o-4--13 3 J
TW4-25 07-25-2016 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: ~rJ: Gu.orfer Ch lorefc>'rm ZOl'
See instruction
Location (well name): I~.-I\J __ 4_-_z_, __________ ___. Sampler Name
and initials: I'"Tih.nn-e.r '11.,11 ;J~!T1}
Field Sample ID
Date and Time for Purging ~.-I _~_/z_/_z_o_l c.. _____ _. and Sampling (if different) 8/'s/zoH. ~-------------'
Well Purging Equip Used: (![]pump or [QJ bailer Well Pump (if other than Bennet) L...l 6"_,-_""_"_J_"t_~.=S ____ ___.
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Qv.o...-"krl.~ C.h lorO'torW' Prev. Well Sampled in Sampling Event ~..-l_-r_LJ_Y_-_30 ______ --J
pH Buffer 7.0 ~.-I -'7'-'-,_o ___ ___. pH Buffer 4.0 I 4,D
Specific Conductance ._I _l oo_D ____ _JI ~-tMHOS/ em Well Depth(O.Olft): ._I _8_b_/J_o __ ___,
Depth to Water Before Purging I b7, <.:3 Casing Volume (V) 4" Wcll:l lZ,'Z.S 1(.653h)
3" Well:~.-. _o ___ _,.(.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl~..-1 Z_&_6
__ _,
Time I lZZ9 I Gal. Purged I ZD I Time I I Gal. Purged I I
Conductance I C.Lj'Z.8 I pH I 3.71 I Conductance I I pHI I
Temp. oc I 'C..41 I Temp. °C I I
Redox Potential Eh (mY) I 61!. I Redox Potential Eh (m V) I I
Turbidity (NTU) I 7..7.. I Turbidity (NTU) I I
Time I oqoo I Gal. Purged I 0 I Time 1oqo1 I Gal. Purged l o I
Conductance I i:~97 I pH 1 g.n I Conductance I <::5 Z 7 I pH I Y.O~ I
Temp. oc I 15.53 I Temp. oc 115:50 I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
Af+er
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 ZD gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
s/60 = I IO.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 z.,qs I
zo
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I ..:..A_w_r,....;..._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 Il D 3x40 ml D 1:1 HCL ~ D
Nutrients f] D 100 ml D ~ H2S04 'r:J 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) "[I D Sample volume D lm D ~
C \t lor~dc:: If preservative is used, specify
Type and Quantity of Preservative:
Final Depth L.::.I&..:::.3_;_;."S=:...'C/.._ _ ____, Sample Time oqoD
Comment
,-) See instruction
Arr~\Je~ 01'\ s;.}e ~-t I22Y -r;.fll!el'" /Ml~ ~(r;(\ pr-e~el)+ t. f'-Ar~<'. ?v.'j~ ~'\1) 1:(-J 1227
'Pu..r-~ea Well ~r o-. +otcJ 0--\' Z Wlinv..t<'~. ?v.r~~~ w~UJr~. '?lA.r~c et>deJ. o.f-l<-'21 t;)4+~
w~ ~o::.~ Cl-etro.r. L£tt s;·h. a..+ l'Z32
Arr.•\Je~ on .S•~e. ~+ 0~5b, -ra-Mer "'nd G-Mr;"..-.f~~Seflt to col/ed· .S.o.lYip1e..s, Depth -Jr. t-.>D~.--kr ltJ4 S
b7,t...Js. s~~.VV'ple.s b~:leJ (1\t o~oo Le+f ..sit~ "'t oqo-z.
TW4-26 08-02-2016 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 3,..-j; Quo.rfcr Gl1lof"oHrfl"l 20/'
Location (well name): ._l_ll..):....;;__4_~2_7 _________ __.
Sampler N arne
and initials: ~~1111er +JoJ/,J~JiH
Field Sample ID
Date and Time for Purging Ll _g_;_z_/_zo_l_b ____ ___. and Sampling (if different) 8/3/zo/.l:. L---------~
Well Purging Equip Used: (IDpump or @] bailer Well Pump (if other than Bennet) IL-~_r_u_n_(Jf.:....-;,.....;;S=------_J
Purging Method Used: [QJ2 casings @]3 casings
Sampling Event I Qu.o.r-t~r-b C'hl orOform Prev. Well Sampled in Sampling Event Ll ~ __ Y_-_2_3 ______ __.
pH Buffer 7.0 l._r.:...;'..;:.o ___ ___, pH Buffer 4.0
Specific Conductance Ll_lo_oo ___ ___.l~-tMHOS/ em Well Depth(O.Olft):l L _q~_._O_D __ ~
Depth to Water Before Purging I 7'1' ,57 Casing Volume (V) 4" Well:I I6,7Z.. 1(.653h)
3" We.ll: o (.367h) '-------'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventll._z_y_• _ ___.
Time I O'j'ZD I Gal. Purged I 15 I Time I I Gal. Purged I I
Conductance I 52Js 1 I pH I 1:. 'Z 1 I Conductance I I pHI I
Temp. oc I IC.9i I Temp. oc I I
Redox Potential Eh (mV) I tjgS I Redox Potential Eh (m V) I I
Turbidity (NTU) I q~ I Turbidity (NTU) I I
Time I Dl?:>q I Gal. Purged I 0 I Time 1 o835 I Gal. Purged l o I
Conductance I 52.35 I pH I b,'2.e:. I Conductance I sz~t. I pH I {;,27 I
Temp. oc I IS.rzi I Temp. oc I 1:5.25 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 )5 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60 = I \D,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=2VIQ= I z.J4 I
I J ,~~
Jl5
Name of Certified Analytical Laboratory if Other Than Energy Labs L.:J A~iJ_A_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
VOCs El 0 3x40 ml D ~ HCL lrJ
Nutrients lrJ 0 lOOm! 0 ~ H2S04 ~
Heavy Metals 0 0 250m! 0 0 HN03 0
All Other Non Radiologies 0 D 250m! D D No Preserv. D
Gross Alpha 0 0 1,000 ml D D HN03 D
Other (specify) 'e:J 0 Sample volume D ~ D
Cn \or: de If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1._'\.:....:~_,o_z ___ _. Sample Time
See instruction
Comment
A((:•'Ve~ on ~;tc tA-t-oq I b . -,;filler o.rJ G-Arr ;YJ f..-esen:l-for fl.\rte . flAr~e
H . .~.r~J Vl~11 for (}... to.f~l ot \ Min""+~ :/J s~coYlJs . PIA.r~eJ Wd}
O~'ZD , LVc,.tcr INIJ0 rA kHl~ YVlWK~. L-e-fl. Site tit O'tZ3.
bt)d\f1 o..1 0911,
Jr~~ Pur~<:. zmded at
A ff;\)e~ 01"1 s,'+e a,_} og~ -ro.Ylner o-no ~('r;(\ .r,r6~nt to C6lled .St\mfles.. Dep-1A -); wa.+er
\No.~ 79, q 1 St\mr1es.. bO\; leJ ~+ OfS:)~ L~Vr .sd·e o..+ 05~
TW4-27 08-02-2016 JDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
D
D
0
0
0
~
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 3 ( i5' Q\1\o.rter Gn I or~rm '2.0\'-
Location (well name): L-1 -=-r-=W:..::........:Y_--z~g _________ __~
Field Sample ID
Sampler N arne
and initials:
See instruction
Date and Time for Purging I 1/Z~/'l.Oib and Sampling (if different) IL7_/_z_1_:J_z _o;_)b _____ ___J
Well Purging Equip Used: OO]pump or [ID bailer Well Pump (if other than Bennet) 16rv.nJOJt;~ ~--~--------~
Purging Method Used: ~2 casings [ID3 casings
Sampling Event I Q-A~>.(f..:C"b; Gh loc~rm Prev. Well Sampled in Sampling Event IL_Ti_W_Y_-_J_? _____ ___J
pH Buffer 7.0 pH Buffer 4.0 4.0
Specific Conductance ~-~ --"lo:...:oc.::::o ______ __,IJ.tMHOS/ em Well Depth(O.Olft): I 107,00
Depth to Water Before Purging I q 0, ~ l5 Casing Volume (V) 4" Well:l LJ3,55 1(.653h)
3" Well: 0 (.367h) L---------'
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)IL;:::3::.;:e::...o ____ __J
Time I lLI'Z.I I Gal. Purged I bD I Time llf2Z I Gal. Purged ,...,0 I
Conductance I 1~2~ I pH I (o ,I.{ I I Conductance I 14S~ I pH I ,,47 I
Temp. oc I IS .IO I Temp. oc 115,61 I
Redox Potential Eh (m V) I 4:5~ I Redox Potential Eh (mV) I 438 I
Turbidity (NTU) I 9t I Turbidity (NTU) t ...)7 l
Time I llt~ I Gal. Purged I ~ I Time I l4L.Y I Gal. Purged I qo I
Conductance I 1451 I pH I 6.53 I Conductance I lq.57 I pH I C).s7 I
Temp. oc I I f).OOJ I Temp. oc I IS.Oi I
Redox Potential Eh (m V) I q'3i I Redox Potential Eh (m V) I 9:St: I
Turbidity (NTU) I ~'j I Turbidity (NTU) I 3k 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 40 gallon(s)
Pumping Rate Calculati n
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60= I 10,0 T=2V/Q= 18.71 I
Number of casing volumes evacuated (if other than two) l o
If well evacuated to dryness, number of gallons evacuated I O
Name of Certified Analytical Laboratory if Other Than Energy Labs ._I ..r,;/J:..."'-l...;.:Vt:.......;;;.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 E D 3x40 ml D 1!:1 HCL f)
Nutrients Ll D lOOm! D ~ H2S04 tJ
Heavy Metals D D 250m! 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) [] D Sample volume D El D
Ch loriJt: If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 8-b .SO Sample Time O[SZD
Comment
/I See instruction
Arr;\1~~ On ~·i-e ~1 1417.. ' -r;.llner IM~ cr~rr i, f('~,J -\-or p\Ar~e. Pv.r~eo be~<=~l'l P,.r I L\ \5
Pu.1~c:-6 \Nell -Por 1\. hl,..l ot' '\ I'Y}~flv.Jo, Pu.r~G ~I'IOl'J.. "'} lY'llf. wata-~ t\. L'Hk. tv~I)Jtj
wkte b"'-t-Slo~t-:>6 C::\e.o.rl/A. 1...<-fi-S1f(. ~ )~Z8
Ar(; '\Je~ ol'\ ~i-te ~+ 6~ 17 -r,.11ner (.1((16 G-().rd, pr~eflr -f., eollec.1-.so.(VIpl~~. ncpth +o 1Na..1er
LjD,3<b. S(}.Mfl~ b~:\~ ().t ogzo L~ $1+e o.} OZZLJ
TW4-28 07-26-2016 !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
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: ~('~ Gu..().f+e.r G11lor!>~(/'Vi Z.OJ.b
See instruction
Location (well name): ._lli_\.-0.;:....;;_4..:...-_2:_,~ _________ __.
Sampler Name
and initials: I =t"Mner JJo JJ 1(/g,:J /!If
Field Sample ID
Date and Time for Purging l.__W_Y_z_o_l"'-_____ _, and Sampling (if different) 1~.--..:...€/_Lj.!,_/_z_o_J{:. ______ __.
Well Purging Equip Used: ~pump or [gJ bailer Well Pump (if other than Bennet) l6rv.t\3fos
Purging Method Used: 00]2 casings [9]3 casings
Sampling Event I G\1\o-rtet""l"\ C.'hlof'of'orm Prev. Well Sampled in Sampling Event ._l_li_W_Y_-_:3_B ______ ....J
pH Buffer 7.0 7.0 pH Buffer 4.0 L-l.D
Specific Conductance ._I --'\_() [)_t:> ___ _.I!!MHOS/ em Well Depth(O.Olft): L..l ~....:..::)._S_o __ __,
Depth to Water Before Purging I/L\,}4 Casing Volume (V) 4" We.ll:l l2. • GA ,(.653h)
3" Well: O (.367h) 1-----....J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)L..I Z_b_0
_ ___.
Time I 1'Z.t~ I Gal. Purged I zo I Time I I Gal. Purged I I
Conductance I q'50Z I pH I (;;:z.o I Conductance I I pHI I
Temp. °C I l~.~'Z I Temp. °C I I
Redox Potential Eh (m V) I :s;c.;:·z I Redox Potential Eh (mV) I I
Turbidity (NTU) I "-;~ I Turbidity (NTU) I I
Time I i580S I Gal. Purged I () I Time I OWb I Gal. Purged I 0 I
Conductance I q:ss~ I pH I l:. -:>3 I Conductance 1 1:13~8 I pH IZ::~9 I
Temp. oc I 'l~.·z:o I Temp. °C 1 1s,, o I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
rf-1er
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. Time to evacuate two ca ·ing volumes (2V)
S/60 = I lO ,o T = 2V /Q = I 2 '52. I
Number of casing volumes evacuated (if other than two) 1 1,5~
If well evacuated to dryness, number of gallons evacuated I z.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 IE D 3x40 ml 0 IJ!I HCL fZI D
Nutrients Ill D lOOml 0 _IE_ H2S04 ~ 0
Heavy Metals 0 0 250ml 0 0 HN03 0 0
All Other Non Radiologies 0 D 250ml 0 D No Preserv. 0 D
Gross Alpha 0 D 1,000 ml D D HN03 D D
Other (specify) lEI D Sample volume 0 Iii 0 ~
G'hlort'Je. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I .....:~...:..\ .:....::' ;:,:.::;2.....:,.._ __ -J Sample Time 0805
Comment
.--) See instruction
Ar ri\)J on S.•te a.+ l214
Pu.r~-e.J. well ~r fA. -fo+t?.t
l-0o..1er ~'\) o.. \i H)c.-
J;.fl()er rMa G-d'.r r i () pr ~Sto-llt fOr f"'r ~-e ·
of' 2 Mifl"'-tt:5, 'P\.\r~~~ wdl d.rtJ~ fu.r~
Pur8e bev<{r'l (}. t-12.1b
O'lt:kJ_ ~~ lZ18.
An'.\J~J o1\ s.lte. o..:t
vJa-..1-er lN~ 7Y.ID
)'Y\v.r~ ,
Dl~O'Z.. -r;,rtM.f" 0.(1~ ~rr,'f') preser~t-~ coiled .S'-""'pJe.~ ..
SO\r~~pJ~ bo..~l~J P D&-05 I.-e;~ sJJ..e ~ ogo7 ·
L~.tt ~J~ o.t IZZ.l
TW4-29 08-03-2016 ID 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 ?:f3 Q\).(Ar:fer c\'\lorl>to('M -zo )&
I' See instruction
Location (well name): I.__I.:....:W;...._:q_-36~---------'
Sampler Name
and initials: l ~nner H~>ll,'d'!jlf}:l
Field Sample ID
Date and Time for Purging ._I ....:::8/::......:::;z _/_Z_O_Ih _____ __. and Sampling (if different) I..._V_~_!z_o_l_t.. _____ ___,
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet) IGfl..<.nJ.!. .... ~ ~
Purging Method Used: 002 casings [QJ3 casings
Sampling Event I Qu()l+e.rJ"\ G\, lorl*1 rm Prev. Well Sampled in Sampling Event .._l--rw __ Y_-_2_7 _____ ___.
pH Buffer 7.0 /.o pH Buffer 4.0 1.1.0
Specific Conductance Ll --ll~OO::..!:O:.__ __ ----'h.t.MHOS/ em Well Depth(O.Olft): I t1Z,5D
Depth to Water Before Purging I '75,/ S Casing Volume (V) 4" Well:l l 0.'1:3 ,(.653h)
3" Well: 'D (.367h) .___ ___ _,
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventl._lz_(.;;;;...6 __ _,
Time I JZDD I Gal. Purged 1 zo I Time I I Gal. Purged I I
Conductance I '37 \~ I pH I S.l) I Conductance I I pHI I
Temp. oc 1 zS.o3 I Temp. °C I I
Redox Potential Eh (m V) I !;53 I Redox Potential Eh (mV) I I
Turbidity (NTU) I t;S .D I Turbidity (NTU) I I
Time I o~s.o I Gal. Purged I 0 I Time I Ol$51 I Gal. Purged I J I
Conductance I qg:~n I pH I S,ZD I Conductance I 9qq9 I pHis.IJ I
Temp. oc 1 lS.91i I Temp. oc I I'S.j) I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
A+'+e.~
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 zo gallon(s)
Pumping Rate Calculalion
Flow Rate (Q), in gpm. Time to evacuate two ca ing volumes (2V)
S/60 = I 10.0 T = 2V/Q =I z. \g. I
Number of casing volumes evacuated (if other than two) IL&z
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs Ll -'-A.J...: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) y N y N
VOCs I5J D 3x40 ml D 1:3 HCL 5J D
Nutrients []j D 100 ml D [}I H2S04 D 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) Ill D Sample volume D 1!1 D ~
Chloride If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1~--t\=O::....:.'..:.:::IS:::<....,_ _ _,J Sample Time
Comment
rJ See instruction
An:\l(~ OY\ .sif~ oJ. l !SS -r;_tii'IU M~
? v.r~~ V)e]l ~ tJ.. }cJ.J oJ' Z M;n~A-4-~.s.
~o..r~, L.Jt. ~;+e ,} 120~
G-Mrin pre..s~rrY tor pur~~{' Pur~~ be~"ll "'} 1 l52
'Fur~~~ IA)e)} c\r~\ ?u.ree ~nJed. ~+ )'Ux:l. Wt;(:h:r ~"S
Arr; IJc~ Of\ site J 084b -r~n(ler (Af)J G-~rf;,., !p<'~.Sent ~ (ollecJ S&1tl1pl-t'.S. Dept~ -h. wcJ~r
\Jj6,) 7S,f>l S~rvlplc~ be1-~)e~ ~.} ogsn Lett SJI.}!. a] OB&Z
TW4-30 08-02-2016 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 (OAP)
ATTACHMENT 1-2
WHITE MESA URANIUM MILL
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 3/JI Qv-o.r'fer Gh lorCff6rll"l 'Zol.G.
Location (well name): Ll _-r;_w_L.{_:__-3_;__1 -----------'
Sampler Name
and initials:
Field Sample ID
Date and Time for Purging I ? 7 /Z.7 / ZO/ '-and Sampling (if different)
Well Purging Equip Used: [Q]pump or [QJ bailer Well Pump (if other than Bennet)
· See instruction
Purging Method Used: (![]2 casings [QJ3 casings
Sampling Event 1Qu.o-der6 C,~ lorofbrfYl Prev. Well Sampled in Sampling Event Ll_--r;_0_4_-_3_' _____ ___J
pH Buffer 7.0 IL__7_.o ____ __J pH Buffer 4.0 I y.o
Specific Conductance Ll_lo_o_o ___ _.l~-tMHOS/ em Well Depth(O.Olft): I IOb,OO
Depth to Water Before Purging I 7'f. 15 Casing Volume (V) 4" Well:l l7. 55 1(.653h)
3" Well: t> (.367h) L__ ___ __J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)l._ _3_2° __ __.
Time I I'Z.3~ I Gal. Purged I 27.~0 I Time I I Gal. Purged I I
Conductance I 4 33-z. I pH I CJl: I Conductance I I pHI I
Temp. oc I /6 .38 I Temp. °C I I
Redox Potential Eh (m V) I '3>c;::, I Redox Potential Eh (m V) I I
Turbidity (NTU) I -zl..\o I Turbidity (NTU) I I
Time I O'b19 I Gal. Purged I l> I Time I o.sz.o I Gal. Purged I 0 I
Conductance I ~g1"~ I pH I z;,G;Y I Conductance I yg,g I pH I '·'-' I
Temp. oc I \5,39 I Temp. oc I 15. ~ZJ 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 27,50 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I 10 ,D T=2V/Q= I 3 50 I
Number of casing volumes evacuated (if other than two) I.S'
If well evacuated to dryness, number of gallons evacuated '27. s'b
Name of Certified Analytical Laboratory if Other Than Energy Labs 1._-'-A.:..;.'IJ....:.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 ~ 0 3x40 ml D £] HCL ~
Nutrients !J 0 100 ml D t:l H2S04 £1
Heavy Metals D 0 250 ml 0 D HN03 0
All Other Non Radiologies D 0 250 ml 0 D No Preserv. 0
Gross Alpha 0 D 1,000 ml 0 D HN03 D
Other (specify) [] 0 Sample volume 0 !l D
Ghlor; de If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1.__1 0_3_,_"1_1 __ .....~ Sample Time
See instruction
Comment
Arriv~d til'\ s.it~ lilt JZ3Z -r;.nner ~>-M &Mr'•(\ pre~ell+ for f'I.A.~~.
P~r~~6. v>ell tor "' +ot""' ot 2. m:niA.t~ 4S ~et::.or1J~. Pu.r~~
\Z~K lr)tA-+tr Wtk~ MIA,..~.:)· L~.fi.. ~i+e ~t lZY 1
Pv.r~~ beS'n .,._} )23 5
well Jrjl· PlAr~e entkJ o.f-
Arr:IJe~ ol'\ ~j}e .,J-0?>1~ 1MIIu· o.n~ G-~~~.rr;., Pr-~senf fo c..ollec..-1---~"'"fles.
Soo.tv~'f'le5-b,.;,~~ tt-r 08 I~ LJ)-~H-e o-t O&C./
TW4-31 07-27-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
0
0
0
0
D
tl
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 '31 ~ Q"";;+~r C\'\ I o,.-o forYl') ZO I b
Location (well name): ._I_'T\0 __ 9_-_~_'Z _________ --.J
Sampler N arne
and initials: 1---r,..nner Jlo J1/J;.,:1)if}
Field Sample ID
Date and Time for Purging I 7/z 7/ Zb Jl and Sampling (if different) 71ZttJzolt.. L--~-------~
Well Purging Equip Used: IT[) pump or [QJ bailer Well Pump (if other than Bennet) I GrunOofuos
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Q~r'fer8 Ch lo rootonr}
pH Buffer 7.0 I 7, 0
Prev. Well Sampled in Sampling Event LI_W_4_-_z_f5 _____ __J
'------------' pH Buffer 4.0 LJ.o
Specific Conductance .__I _l_D_oo ___ __,l ~-tMHOS/ em Well Depth(O.Olft): Ll .:....:.11..::...5 _. l_o __ _~
Depth to Water Before Purging I S \ · z;; ~ CasingVolume(V) 4"Well:l4 1.4l 1(.653h)
3" Well: 0 (.367h) L__ ___ _.
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event),__I2J_' __ _J
Time I 6441 I Gal. Purged I ,o I Time I oct~$ I Gal. Purged I 76 I
Conductance I /137.. I pH 13.45 I Conductance I (;1 .. rz I pH I ':),'f.S I
Temp. oc I p:t qq I Temp. oc I JLM'Z I
Redox Potential Eh (m V) I ?;lg I Redox Potential Eh (m V) I bl7 I
Turbidity (NTU) I 19.Z> I Turbidity (NTU) I ,-..:; J
Time I 0'\~j I Gal. Purged I ~() I Time I 6'1.50 I Gal. Purged 110 I
Conductance I 6~ c..o I pH I 3 ,Y.L. I Conductance I<;~~ I pH I ~.Y7 I
Temp. oc I I~ I Z!::S I Temp. oc 1 14.9:> I
Redox Potential Eh (m V) I ~~~ I Redox Potential Eh (mV) I Cb I
Turbidity (NTU) I p:; I Turbidity (NTU) I 15 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 'fl) 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 g.z,g I
Number of casing volumes evacuated (if other than two) IO
If well evacuated to dryness, number of gallons evacuated lo
Name of Certified Analytical Laboratory if Other Than Energy Labs L..l.:...ft:..:.W....:./t.!...::.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 ~ D 3x40 ml D t:J HCL l) D
Nutrients !I D 100 ml D ~ H2S04 CJ D
Heavy Metals D D 250 ml D D HN03 D D
All Other Non Radiologies D D 250ml D D No Preserv. 0 D
Gross Alpha D 0 1,000 ml D 0 HN03 D 0
Other (specify) til D Sample volume 0 (I 0 ~
L'n 'or·,ae If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I 15.'!:,{) Sample Time ogoo
Comment
1 .-J See instruction
Arr-;\)e~ c?n site "'t 6 438 -J,..nl)er (}.,J C-(){'r:n rr~(J F-=F;r ?u.r~e. 'PU('~e_ be~~n ~t O'fl/]
Pu.(~e;~ \t)e)\ ~f a.. to+tA.l of q tvdnu.+es . PIAr-~c.. e11~eO. tA..J-oL\SO . l.VQ...+er w"-.s. ciGo..r. . LVhe~~ HAJI;~ t\,t; PWY1f ~~ ~ ~h.+~ s~} L;l<e p>rl;c.J~ 01') t-h~ ho~ IMJ P'"'""P· L<!P Ji~;~
Arn~J. on s1'te o-.1-0757 J;.nner ~nJ. G-o.rrln preSetl.} +o G?lled· S.~ples, Dep+h to (A,)C)..+er
w~ 5,).55 So.P1fleS bo..:\ecl a..+ OWD Le-i=}-s.lte. 0\.t ogo-z
TW4-32 07-27-2016 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 Z>'('X Qv\0-der On lo,.-;Por~ ZO).b
Location (well name): I._'T_W_4_-_3.3 _________ ____,
Field Sample ID
Sampler N arne
and initials:
, See instruction
Date and Time for Purging I &/'Yzojb and Sampling (if different) &/ Y/zo }!::, ~~~-~----~
Well Purging Equip Used: [Q]pump or [QJ bailer Well Pump (if other than Bennet) I Gr ul'l t:If'o.s
Purging Method Used: 1][]2 casings [QJ3 casings
Sampling Event I OlAt:>.rf~r b GV! JoroforrY) Prev. Well Sampled in Sampling Event ._l_-r_w_4_-_l_fo _____ ~
pH Buffer 7.0 "7,0 pH Buffer 4.0 1.\,0
Specific Conductance ._I _IO_o_o ___ ~I!J.MHOS/ em Well Depth(O.Olft): 1~....-......::£:....;...7_, Cf;_tJ __ __,
Depth to Water Before Purging j7z,q:z::; Casing Volume (V) 4" Well:' 't 75 ,(.653h)
3" Well: 0 (.367h) '---------'
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! Z_L/{} __ __,
Time l lo?k I Gal. Purged l+&.ib )3,~1 Time I I Gal. Purged I I
Conductance I q~ql I pH l 5·9lJ I Conductance I I pHI I
Temp. oc I 'j6;,30 I Temp. °C I I
Redox Potential Eh (m V) I 569 I Redox Potential Eh (m V) I I
Turbidity (NTU) I ':SD I Turbidity (NTU) I I
Time I o7.sg I Gal. Purged I 6 I Time l o75~ I Gal. Purged I 0 I
Conductance I ~S~4 I pH I s.G7o I Conductance 1qsg7 I pH Is.,, I
Temp. oc 1)6.1% I Temp. oc I \b. I:S I
Redox Potential Eh (mV) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
A-P+e.r
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 Calculalion
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 l I q.S I
I '·~
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
VOCs E) D 3x40 ml D ~ HCL ffl
Nutrients fJ D 100 ml D rJ H2S04 ~
Heavy Metals 0 0 250m! 0 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) 6 D Sample volume D rJ D
Ghlor;~e.
If preservative is used, specify
Type and Quantity of Preservative:
Final Depth IL-~=-S_,~7.5 ___ _J Sample Time ._I 0_7_5_( __ ___,
Comment
,-j. See instruction
ArriiJcd on ~rte "+-10~3_ ~(li'IU MJ. Go.rr\" p•e.sef)+ .£(' ?-'-,..5~· PIA.r~e be~M o..t }O~S
'Pv..r~e~ ~~ll .fa,. 0... te.h,l or } MtruJ·<. 20 S~Go()J~. f4r~'C'~ w~ll Jr~~ PIA.t~e ellJeal. .:t+ 10"3~
fhr w"'+er \,.)~ 0o.. 1 i+\-J~ Mw~ left s~'te ~1-IO~~
N
D
D
D
D
D
~
Au;\Je~ on ~d·e ~t 075.S ~Mer o.I"\J. &-fl..rrt11 prt:~etl-1-i-o Co} lec.f-5o.111ple..!l, Deri")., to ~J-er ~...)
72.'\.S S~Ar~~fk-::, bt~.·\eJ. ..tt 675&' L~ site IAJ o8oo
TW4-33 08-03-2016 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 '3r3 G!u.o.rfe r Gh lorl1fonl'1 ZOI(:.
See instruction
Location (well name): I._I\_W_4_-_~-~-----------J Sampler Name
and initials: I :::r;_nn~(' ADJ);Jo. .... ::VIH
Field Sample ID
Date and Time for Purging ._I _~_/z_/_z_o _lt. ____ ____, and Sampling (if different) U~/Z.O)(. .__~~~~---------~
Well Purging Equip Used: ~pump or [gJ bailer Well Pump (if other than Bennet) I Grv.."J+'os
Purging Method Used: [![12 casings IQJ3 casings
Sampling Event I Qu.o.r+e..-1~ C.\-llo'fOforrn Prev. Well Sampled in Sampling Event I IWY-~4 ~
pH Buffer 7.0 7.0 pH Buffer 4.0 4.0
Specific Conductance!._ _1;.:_0_0..;;_0 ______ __,1~-tMHOS/ em Well Depth(O.Olft): ._I _,_q1_·._z._o __ ____,
Depth to Water Before Purging I 7Z :z.rJ Casing Volume (V) 4" Well:l \()::sz 1(.653h)
3" Well:.___o ------'· (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling eventl~....IZ_D_6 __ ~
Time I OIYZ I Gal. Purged 1 ~3.~3 I Time I I Gal. Purged I I
Conductance I \4 0(,lf I pH I c.,. 45 I Conductance I I pHI I
Temp. oc I }S.zo I Temp. °C I I
Redox Potential Eh (m V) I Slj I Redox Potential Eh (m V) I I
Turbidity (NTU) I \.\ o I Turbidity (NTU) I I
Time I O&C>J I Gal. Purged I {) I Time 1 o~o~ I Gal. Purged l o I
Conductance I ·:~:/1~9 I pH lb.~ I Conductance l ~qg&f I pH I 6.'37 I
Temp. oc I 1s,n; I Temp. °C j iS, /L I
Redox Potential Eh (m V) I I Redox Potential Eh (m V) I I
Turbidity (NTU) I I Turbidity (NTU) I I
A-Fter
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 Ll ~=-=3:....:'-=3~3==-----l gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm. Time to evacuate two ca ·ing volumes (2V)
S/60 = I lO.O T=2V/Q= 13.1-b 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'----'-'\V:.LA.~...: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 Kl HCL III D
Nutrients [I D 100 ml D ~ H2S04 rB 0
Heavy Metals 0 0 250 ml D 0 HN03 0 0
All Other Non Radiologies D 0 250 ml D 0 No Preserv. 0 D
Gross Alpha D D 1,000 ml 0 0 HN03 0 0
Other (specify) IJ 0 Sample volume 0 [] D t::J
Cn loriJe If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I 9_~,__. ~;....::g __ __. Sample Time
Comment
. :J See instruction
Ar6'Ve~ on site o..t 073.1 .,.;Mer M~ &o..rrin pr-es.~t)+ -fiX ru.r~~. '?u.rt\e b~M o.t 0731
'f'u.r~~~ ~ell tor {}.. h-f"'l of 3 mirll-tfe-~ Zo S(:;GOt1J.~. fur~~~ Wt."ll Jr:J. P\..\r~e.. eY/Jed. aT
07YZ.. IAJq..fer lNA~ 'MoS.f~ c le~i-r-, t.~f.J-si+e ~+ 07'-1\.j
Af(-;\Je~ 01'1 si+e o.t o&Oi -ro.llner o..n~ G-o.rt'.-'1 pre~eflt +!) c.olled ~~rople~. Depth +b ~Uder
\N{Io.~ 72.2D, s.~mples bo.il("~ g...} oK01 Lett si-t~ ~+ 080!\
TW4-34 08-02-2016 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
DescriptionofSamplingEvent: I ?:.'(>. Gu.~rfer C~)or-ofor/YI ZOI.b
See instruction
Location (well name): l~.--r_w---'~--_;3::....H.:....R~---------~ Sampler N arne
and initials: I ::::r ~f\1'\-c:.,f' Ho ll ;J~.::1hH
Field Sample ID
Date and Time for Purging [ ~/ Z../ZO IJ.. and Sampling (if different) r.IIA
Well Purging Equip Used: OOpump or []]bailer Well Pump (if other than Bennet)
Purging Method Used: [QJ2 casings 1]]3 casings
Sampling Event I Quo.rfer I~ Gh' or oto rrYJ Prev. Well Sampled in Sampling Event ._l_'l_w_Y_-_~_) ____ ___.
pH Buffer 7.0 7.0 pH Buffer 4.0 4,0
Specific Conductance 1'---'-IO_O_D ___ ___.[!!MHOS/ em Well Depth(O.Olft): L..l _o ____ __.
Depth to Water Before Purging L..[ __ 6 __ ___, Casing Volume (V) 4" Well:lt--0----;1(.653h)
3" Well:_ Z> . (.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling eventl~.-1 ..:..:lg:::..'~~ __ ...J
Time I OlZl\ I Gal. Purged I 0 I Time I I Gal. Purged I I
Conductance I )0,0 I pH I 7 E4 I Conductance I I pH[ I
Temp. oc I "Z, '5 I 3 r.s I Temp. °C I I
Redox Potential Eh (m V) I qb'Z I Redox Potential Eh (mV) 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 pH[ 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
Pumping Rate Calcul ation
Flow Rate (Q), in gpm.
S/60= I lO.D
\~0 gallon(s)
Time to evacuate two casing volumes (2V)
T= 2V/Q= I Q I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated ._I _
0 ___ _.
N arne of Certified Analytical Laboratory if Other Than Energy Labsl '--_A~W....:.A..;..L.:;;_ ____ -....~
Sample Taken Sample Vol (indicate Filtered Preservative Added Type of Sample if other than as Preservative Type
y
VOCs rn
Nutrients rn
Heavy Metals D
All Other Non Radiologies D
Gross Alpha D
Other (specify) ~
C'n lor~ Je
Final Depth!.__ __ o ___ _,
Comment
Arf'ivea O(l s.ite ~+ 0710
R; n.sdl.te b~~(\ o.1 0 '11 \
(,,.,not\5 of D:I !A>,.tt:r.
Lef+ s;+~ (11+ Dl~l
N specified below) y
D 3x40 ml D
D 100 ml D
D 250 ml D
D 250m]. D
D 1,000 ml D
D Sample volume D
Sample Time 07ZS
N
[!]
~
D
D
D
rn
y
HCL ~
H2S04 ~
HN03 D
No Preserv. D
HN03 D
D
If preservative is used, specify
Type and Quantity of Preservative:
. .a See instruction '..l:i"'
-r.;:nMr Mel G-c:a.rr;t\ pre.Se(lt .for f";f\.s~+e
Pv.r~~p-ea .So {rq.llon..s ot ~oo.-p !No.Jer ,u,J. IOo
St1.1Ylple~ collf!ct~J o..+ 07Z5
TW4-34R 08-02-2016 Ina 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
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I 3r0t Gh ... ~rf~,... Gh lor-.,forfll) 'ZOI4
See instruction
Location (well name): l.._"T_w_~..:_\ -_35 __________ ___,
Sampler Name
and initials: ~~tlt!U Holl.'lt~trH
Field Sample ID
Date and Time for Purging LI_~_;/_"Z_/_'Z._o_IJ. _____ _J and Sampling (if different) 8/3/Zo/4 '"----------~
Well Purging Equip Used: [f[Jpump or [QJ bailer Well Pump (if other than Bennet) Ll ~_ru_,_J_t_1_.s. ____ __.
Purging Method Used: [QJ2 casings [QJ3 casings
Sampling Event I Qv-~rhrb C\'1\oroforM Prev. Well Sampled in Sampling Event ._I_I_I.J_L_I_-_3_~-------'
pH Buffer 7.0 7 ,0 pH Buffer 4.0 4.0
Specific Conductance Lj_lo_o_o ___ ___JI!!MHOS/ em Well Depth(O.Olft): I 87, .SO
Depth to Water Before Purging I 74, l~ casing Volume (V) 4" Well:r8--=-.7_1 __ -;1(.653h)
3" Well:_ o . (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event),_j -z_J• __ _.
Time I o&.o I GaL Purged I ,o I Time I I GaL Purged I I
Conductance I q~q-r; I pH I ~.~q I Conductance I I pHI I
Temp. oc 1 1~-LS I Temp. °C I I
Redox Potential Eh (m V) I 5Z~ I Redox Potential Eh (mV) I I
Turbidity (NTU) I 51 I Turbidity (NTU) I I
Time I ogJ~ I GaL Purged I 0 I Time l o~/.5 I GaL Purged I ~ I
Conductance I ~5':>n I pH I b.43 I Conductance I :\'5~t> I pHIG,yJ I
Temp. oc I 15,0~ I Temp. oc 115,0.3 I
Redox Potential Eh (m V) I I Redox Potential Eh (mV) I I
Turbidity (NTU) I I Turbidity (NTU) I I
Af+er
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 16 gallon(s)
Pumping Rat Calcu laLion
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I )O,t> T=2V/Q= I )o7li I
Number of casing volumes evacuated (if other than two) I J.l~
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs ~.-l..c/3!.!W..::..uA~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
VOCs IJ D 3x40 ml D 111 HCL 11)
Nutrients Ill D 100 ml D 1!1 H2S04 IE
Heavy Metals D D 250ml D D HN03 D
All Other Non Radiologies D D 250ml 0 0 No Preserv. D
Gross Alpha 0 D 1,000 ml 0 0 HN03 D
Other (specify) 111 D Sample volume D ~ D
c~ )ol";d(. If preservative is used, specify
Type and Quantity of Preservative:
Final Depth 1~.-~;:_'-\....:..:'-=.g...J-J __ ___J Sample Time 081Y
Comment
,.j See instruction
Ar1'i\le~
'Pv..r~~~
IA.)"hr
01" ~itG A.t 0&70 -r ... f'll\<!( Mbo {j-q..rr:() pre..S-er'\V" f'or pv.r~'(.. 'Pv.r~f 6~"-11 ~t og I'L
Well tor "' toh.l ot 1 Mir'lu.+t'. f>v.r~eJ (,jd] Jrj 1. ~~-e ertde4 of-081-:>
\,.:)cA,~ r;._ ) ~·++I~ WllA..rk~. LJ.f. sih t~.f 0}3.l.!)
Arr ;..:Jc~ ot'\ ~it~ At 0~11 '"lo."'ner a.AO. G-q..cr-•'n prt:Set'l+ +o lolled SAIVIfle~. D~fth 1-o l.;)o.ft.l'
wo..,> l4,1.S ~o.Mp1~~ bo.il~6 11,-}-O&lq Left 5i·h: ll.t 0&1~
TW4-35 08-02-2016 IDo not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
N
0
0
0
0
0
~
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 ~<do Qv:c:r:Rr ChI oro"t:6nl"l Z.O 1 G,
See instruction
Location (well name): ._I_"T\tJ __ l-l_-_3_C::. ________ __.
Sampler Name
and initials: I ::::r;.l'lllel" Ro/l r'J.o..j)tll
Field Sample ID
Date and Time for Purging ~-~ _7.:.../_Z_7_J:_ZD__.:.._l '------1 and Sampling (if different) ._17_'/_z_&_/_z_o_l_'-_____ ___,
Well Purging Equip Used: (IDpump or [QJ bailer Well Pump (if other than Bennet) ._IG_r_v._r-._OI_+:_o_~ ____ __,
Purging Method Used: ~2 casings [QJ3 casings
Sampling Event I Qv.Arf~rfu C.h lorOfor}'VI Prev. Well Sampled in Sampling Event I 'fWr.J -1:3 '-----------~
pH Buffer 7.0 7.0 pH Buffer 4.0 4.0
Specific Conductance ~-.1 ....;l_O_O_D ___ ___~I !!MHOS/ em Well Depth(O.Olft): ._I 'l_~_.o_6 __ ----'
Depth to Water Before Purging I 5C..Y'Z... Casing Volume (V) 4" WeH:I ?-7. &D 1(.653h)
3" Well:._. _o ___ _..(.367h)
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)I._3Z_6
__ _,
Time I \'Z.Ol) I Gal. Purged I 4S I Time I I Gal. Purged I I
Conductance I -z.ssq I pH I 6.~7 I Conductance I I pHI I
Temp. oc I 1c;.-zs I Temp. °C I I
Redox Potential Eh (m V) I zqz I Redox Potential Eh (m V) I I
Turbidity (NTU) I I') l I Turbidity (NTU) I I
Time I 0 g I'Z. I Gal. Purged I 0 I Time 1 ogL3 I Gal. Purged I Z> I
Conductance I 2~39 I pH I C::,g.s I Conductance I z.~l~ I pHI,.BY I
Temp. oc I 15,7'1 I Temp. °C l lS."JS 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 Calculalion
Flow Rate (Q), in gpm. Time to evacuate two casing volumes (2V)
S/60 = I 10,0 T=2V/Q= I 5,5C I
Number of casing volumes evacuated (if other than two) I.Ll
If well evacuated to dryness, number of gallons evacuated
Name of Certified Analytical Laboratory if Other Than Energy Labs 1~....:..../t_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 [I 0 3x40 ml D u HCL ~
Nutrients 'El 0 100 ml 0 ~ H2S04 Ll
Heavy Metals 0 0 250m! D D HN03 0
All Other Non Radiologies 0 D 250m! 0 0 No Preserv. D
Gross Alpha 0 0 1,000 ml 0 0 HN03 0
Other (specify) r&l 0 Sample volume 0 [] 0
G h)Dr;Je If preservative is used, specify
Type and Quantity of Preservative:
Final Depth ._I ~-"-· _9~.:.__ __ __, Sample Time
Comment
.-j See instruction
Arr \\>ej Ot\ ~·+e. <'--1-JJ 5Y """'nner ~~ G-tT-.,..;... rr~~(l+ -h>r pur~e.
PtAr~d. \,Jell -h,.. fl... ~h+~l of '1 M;n..Je~ 30 Sec.o"&t.s . R..r~c:J
Wo-.fer ltV~ mw-~ ~··th ,. bro~n hf'l+_ Left Sltt: ~~.-t IZ:D.3
A r-r j \led. 01'\ ~/1-~ ~J D801 t•nner o.nJ 6-6-rrir. pus en+ fo
~~ 57.1, S~rYif)6 b~;J.lc.\ "'-J-D&IZ \...~f} .Site
TW4-36 07-27-2016 !Do not touch this cell (SheetName)
White Mesa Mill
Field Data Worksheet for Groundwater
CA1Je.c..J.-~-(l'lp)e}. Dep-h. fo ~"\.+e,..
tAt () &/~
N
D
0
D
D
0
tJ
2 of2
Mill· Groundwat.er Oistharae Permit Groundwater'Monitorln~QuaUty Assurance Plan (QAP)
Date: 06-06-12 Re11. 7.2 -Errata
. E r ..
>-:~ ATTACHMENTJ-2
._-.-.,_.. ............... ...-..-WHITE MESA URANIUM MILL See instruction
FIELD DATA WORKSHEET FOR GROUNDWATER
Description of Sampling Event: I. ~ f'd. Q~v.o,Mer .C. hi o rOf'orm 2 D lt.
Location (well name): '-1 _:rw,.L..lC· =-9L..-..:::3;...:7 ________ __.J
Sampler Name
and initials: I ~flf!Cf" tlo} ,,a'MITH
Field Sample ID
Date and Time for Purging J, 112:.5/zou~ s and Sampling (jf different)
Well Purging Equip Used: r m I pump or I[] I bailer Well Pwnp (if other than Bennet)
Purging Method Used: I Ql· 12 casings @]3 casings
Sampling Event I Q·WA.r±er~ C.h )0.t0f0 r,..., Prev. Well Sampled in Sampling Event 1"-. _ll0 __ 4 __ -_z_z. ______ ___.
pH Buffer 7.0 1...._7;..;.·'=-D-.....:..-_ ___, pH Buffer 4.0 '-1. 0
Specific Conductance ._l....:.t.;.;oO~lJ:..__-=-----JIIlMHOS/ em Well Depth(O.Olft): I llz~QD
Depth to Water Before Purging I ~'b,.lS Casing Volume (V) 4" Well:' 3D ·t:1 ,(.653h)
3" Well: o (.367h) '-------'
Weather Cond. Ext'l Amb. Temp. oc (prior sampling event)j -;:>-:>0
Time I 1355 I Gal. Purged l o I Time I I Gal. Purged I ~ I
Conductance l·t,.jzt?l I pH I "·~o I Conductance r I pHI J
Temp. °C I 1"48 I Temp. °C I I
Redox Potential Eh (mV) 1 ~1.1 I Redox Potential Eh (mV) I I
Turbidity (NTU) I 2.. I 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 II -I pHI I
Temp. °C I ' I Temp. °C I .I
Redox Potential Eh (rnV) I r I Redox Potential Eh (mV) I I
Turbidily (NTU) I I Turbidity (NTU) ,, I
White Mesa Mill
Field Data Worksheet for Groundwater A 1 of2 CaOtUr)(' CDMPATiaLE WITH .A;~J'V--FUNCTIDNHITY
Mill-Groundwater DischarBe Permit
Gmundwater4 Monitorin';! Quality A~urance Plan (QAP)
Date: OIHl&-12 Rev. 7.2-Erriitil
Volwne of Water Purged 0 gallon(s)
Pumping Rate Calculation
Flow Rate (Q), in gpm.
S/60= I J1.0
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 '3..S'J 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 ot11er than as Preservative Type
VOCs
Nutrients
li~'1LJvletals
All Other Non Radiologies
Gross Alpha
Other (specify)
Ch lor; je
~inal Depth ._I 7.:......;.4_:t._Y~-.. _ _.....~
!
l
~omment
y
ID m
0
q
0
IJJ
t Arrive~ 61\ 6 1'+~ ~+ 1~53 .
S o-I'Vlf le.s Coli ec+eJ lA}
Lefl S (+e o.+ 13 5~
N specified below)
a 3x4Q rnl
D IOOml
0 . 250 ml
0 2~0ml
0 1,000 rill
0 Sample volume
Sample Time 13.5"
L---------__,Do not touch this cell (SheetName)
White Mesa Mill
=ield Data Worksheet for Groundwater
y N y N
0 . -·-{Xf .HGL Ill -D
0 ~ H2S04 • > Iii . []
I 0 0 HN03 D D
D rq No Prescrv. 0 -o·
0 0 NN03 D q
0 tg D tit
Jf pre:o~en'lltive is used, specify
Type and Quantity of Preservative:
See instruction
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 3 ra Qv.o.r+er Gh loro+'l)(YY) zo I b
See instruction
Location (well name): l.___-r_w_4_-_'-_0 _________ ___.
Sampler N arne
and initials: l::::r=nner-N,n:J~hlJ
Field Sample ID
Date and Time for Purging I 7/Z5/2Dib and Sampling (if different) I.__;V_/_A ________ ___.
Well Purging Equip Used: mJpump or (]]bailer Well Pump (if other than Bennet) I.__N_Y._~---------'
Purging Method Used: (]]2 casings (]]3 casings
Sampling Event I Qw;..rterl~ C'h\orofbrrt1 Prev. Well Sampled in Sampling Event Ll AJ_YA ________ __...j
pH Buffer 7.0 1.0 pH Buffer 4.0 Y.o
Specific Conductance '--1 ___,_;\O;..:CC=----...Jh..tMHOS/ em Well Depth(O.Olft): ~_I _:_O ____ __J
Depth to Water Before Purging l.___o ___ _, Casing Volume (V) 4" Well:~_o ___ --1,(.653h)
3"Well:. 0 .C.367h)
Weather Con d. Ext'l Amb. Temp. oc (prior sampling event).__lz_z_D __ __,
Time I ,"-S~ I Gal. Purged I D I Time I I Gal. Purged I I
I'Z5~
Conductance I 01Y I pH I 6.'2S I Conductance I I pHI I
Temp. °C I 'Z.S, bJ I Temp. °C I I
Redox Potential Eh (m V) I S'Z5 I Redox Potential Eh (m V) I I
Turbidity (NTU) I 0 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 (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 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 . Time to evacuate two casing volumes (2V)
S/60 = I () 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!._ _A_;__~....;.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 Ill D 3x40 ml D ffi HCL 11:! D
Nutrients m D 100 ml D rn H2S04 1!1 D
Heavy Metals D D 250 ml D 0 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) ~ D Sample volume D ~ D m
C.'nlori~
If preservative is used, specify
Type and Quantity of Preservative:
Final Depth L-1 ---=.6 ____ __..~ Sample Time 1300
Comment
! ~ See instruction
D. :C.
TW4-60 07-25-2016 ID o 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 3 ra Qv.,o-rfe(' Gh li>ro£rm zolb
See instruction
Location (well name): ._l_""i't.:....:...W_4_._--=b5=-----------'
Sampler Name
and initials: I ~t111er B6n7dlm
Field Sample ID
Date and Time for Purging I 1/z t../e.oU:. and Sampling (if different) l-t/Z7/Z0lf.
Well Purging Equip Used: OOpump or [QJ bailer Well Pump (if other than Bennet)
Purging Method Used: (![]2 casings [QJ3 casings
Sampling Event I ~M+er-b a lo roOfor m Prev. Well Sampled in Sampling Event IL--r_w_LJ_-J_z _____ ____j
pH Buffer 7.0 1.0 pH Buffer 4.0 I LJ.O
Specific Conductance ._I _ID....:OO:o.=.. __ ___.l~-tMHOS/ em Well Depth(O.Olft): I 107, () D
Depth to Water Before Purging I Y 0,3 l> Casing Volume (V) 4" Well:l Y3,55 1(.653h)
3" Well: 6 (.367h) L----_J
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event) I .:JZ"
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) 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 (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.
S/60 = I IO.D
Time to evacuate two ca ing volumes (2V)
T = 2V/Q = I ?>.7/ I
Number of casing volumes evacuated (if other than two) 0
If well evacuated to dryness, number of gallons evacuated
N arne of Certified Analytical Laboratory if Other Than Energy Labs ._I ..... A-'-'Wc.:.:...JAu.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 rll D 3x40 ml D r:J HCL ~ 0
Nutrients Ql_ D lOOml D _l!l H2S04 ~ D
Heavy Metals D D 250 ml D D HN03 0 D
All Other Non Radiologies D D 250 ml D D No Preserv. D 0
Gross Alpha 0 D 1,000 ml D D HN03 D 0
Other (specify) Ill D Sample volume D 1m D M
C}do(J'ck,
If preservative is used, specify
Type and Quantity of Preservative:
Final Depth I g 6. 50 Sample Time 062D
Comment
,..J See instruction
TW4-65 07-26-2016 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 :),..{}; Q v-c..,...f c.r c>\\oco forf'(l z.O IC:.
Location (well name): ._l_l_w_LJ_-_-,_o _________ ___,
Sampler N arne
and initials:
Field Sample ID
Date and Time for Purging I <67 Z /2..0 If:. and Sampling (if different)
Well Purging Equip Used: ~pump or [QJ bailer Well Pump (if other than Bennet)
See instruction
Purging Method Used: [![}2 casings [9]3 casings
Sampling Event I Q ku..rf u·S C..h' orof'orl"f\ Prev. Well Sampled in Sampling Event I ll.J4-3 ~
pH Buffer 7.0 7,0
Specific Conductance ._I _ro_o_o ___ __,!,.tMHOS/ em
Depth to Water Before Purging I 69. 9L)
pH Buffer 4.0 LJ.D
Well Depth(O.Olft): I IIY.oo
Casing Volume (V) 4" Well:l 'Z.~ · 75 1(.653h)
3" Well:._ __ o __ __._ (.367h)
Weather Cond. Ext'l Amb. Temp. ·c (prior sampling event)._! _z_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. 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
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 (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 qo 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 5,15 I
Number of casing volumes evacuated (if other than two) I "
If well evacuated to dryness, number of gallons evacuated 0
Name of Cettified Analytical Laboratory if Other Than Energy Labs l'tWAL.
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 Cll D 3x40 ml D ~ HCL ~ D
Nutrients [1J D 100 m1 0 rn H2S04 ~ D
Heavy Metals D D 250 ml D D HN03 0 D
All Other Non Radiologies D D 250 ml 0 0 No Preserv. 0 D
Gross Alpha D D 1,000 ml D D HN03 0 D
Other (specify) C!l D Sample volume 0 ~ D ~
L h \or:J~ If preservative is used, specify
Type and Quantity of Preservative:
Final Depth l.___g_C::_._l.\_0 _ ___, Sample Time
See instruction
Comment
TW4-70 08-02-2016 lDo 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 7/6/16 Name fn:..r-r,.,..._ Pc,lo,:V\L£1 !c..A-o"r !:1-oll•rl.e..y
System Operational (If no note
Ti me Wll e D th* ep1 c t ommen s an:!£Rro bl I . i l ems corrective act ons
D~oJ. MW-4 ~i.'-4.7 Flow L{,L{ )(e"S)No
Meter I D663 L.~.t./0 ~No
(J 7 S{, MW-26 6Y./! Flow 7.b '(e~ No
Meter CJ6Jt1D. g-o t!f__ej) No
D7o.S TW4-19 6'3.~7 Flow 1~-0 ~No
Meter 5o3'1 gt.j ~-to ((e~ No
()753 TW4-20 6 3. t(Q Flow (,?; /{if,) No
Meter _l Lt..32.. 77. UJ ~No
6810 TW4-4 (£.{,'6( Flow tD· 2-l(esj No
Meter 37l8L.l~-'i?D ~ No
6738 TWN-2 ~5.5( Flow 15S'. L{ !YeS) No
Meter 66CJ 6 3'-{. Yc:, eVe~ No -
D747 TW4-22 53'. (3 Flow \(.0 /'fes) No
Meter 33YS!i'l' ,5D .7{'W No ._
{)741./ TW4-24 t<,q ,c;--z Flow 16.o ,?(e1) No
Meter 1557'1t'f. Sh ~ No
()731..{ TW4·25 6' L.{ • <-{ '-i Flow l5.o '1(6~ No
Meter l G Y.6_D '7 o .g,o l('eSj No
CJ<l06 TW4-1 qs -zL Flow J(... .D rle'$) No
Meter I 3 I~ l 9 , 'Z.o Cf__~No
ogoo TW4-2 )!I .Z..t{ Flow //,, z_ /"i'es\ No
Meter 131\l\.~o rteSJNo
D7S7 TW4-11 0 2 _g'-l Flow J6,D ~No
Meter 3oz. 7 3 .3(') ~No
673C TW4-21 61-63 Flow I t'-,. D f{f!J~ No
Meter 5Y <6S 6( -'il !Y'eS) No --....,
TW4-37 62. I :3 Flow il,() £Yes') No
D7SO Meter Y 'JSq 8.3'L bD ~No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
Date 7/12/z.o 1-b
Time Well
03'2.1 MW-4
l)'b \~ MW-26
Oi'YJ TW4-19
0~10 TW4-20
OK3.b TW4-4
!~ TWN-2
082.'3.
0 'l,!) l TW4-22
c)15.:S TW4-24
011{'-\ TW4-25
D&3i TW4-1
~ TW4-2
OT-Ig
O~lq TW4-11
0140 TW4-21
080_5 TW4-37
Weekly Inspection Form
Name -k11ner ~oll;J~j,
System Operational (If no note
Depth* Comments anv oroblems/corrective actions)
1:,\. ·z.t{, Flow '11_3 (Yes) No
Meter lb1'2.IOI.'-I ( Ye~ No --=---..
bb-~9 Flow lab ( ~s)No
Meter l.!I5'Z.7,'l ( Yes ]No
I(~~ 1.5 Flow 1~.0 {'f_es) No
Meter 511~9/. ~ {YeS) No -~3.'l1S Flow 1~7.~ {f"es::>!_o
Meter 144 IZ9, 2. /_ Yes)No
---:::
73,'\Z Flow )0.1 ("Yes.)No
Meter 3 755 73.0 (Y'"e) No ......__
~~.b'l Flow l g,&.l r-Y_es'No
Meter · ,., ..... ~ · ( Te3/ No
."1 -~ St:zP Flow l7,0 ~No
Meter ~?:lt:;.lZ3.0 \. Yei No
(o1,.~1 Flow \~.0 CY~No
Meter LS q C:. ~Ll . .Z Z. (Ye~ No
~~.q~ Flow p;,o ~s)No
Meter[~53ZD 0 . :;{ (Yes) No -qo D5 Flow \~.0 Cles )No
Meter 1'3Z!J&z.g (YeS\ No
~ '62 ,t\Y Flow \b.~ . .!'Yes )No
Meter -.L.a. .... -s ''='T L re~ No .
Cf2.3l Flow H •. o _Q'es)No
Meter 30lf<18·g ( Yes)No
~
61 .. 7'; Flow t'-.o CY.U' No
Meter 5S~~71.Z.I {Yes.)No
(..;Z.Z\ Flow I "1· 0 (Y@U No
Meter y Cf70 K5 K {Yes) 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
Time Well Death* Comments
t.fs3 MW-4
Meter
i 3Lfl MW-26 65~_1-f_q Flow 7.7
Meter '1B137 t""
1~1.5 TW4-19
Meter Sl'lODS.'Z-D
1 3'-i_oi TW 4-20 64. bti Flow R.o
Meter ! YSU. L{ , J7
I_
1327 TW4-4 72.. £t I Flow ~ \ D .I
Meter .37<1 z:z:z ... 4 6
I 3_<;1.4 TWN-2 7:13. 4'\ Flow I £S'.6
Meter
\ 3'1 7 TW4-22 t7.o
Meter .137718 Z..D
I ~.~/) TW4-24 7o.t~ Flow
Meter
1357 TW4-25 ~s D~ Flow
Meter 166143'6.70
13Jo TW4-1 ~6 .~1.( Flow
Meter
~~~ TW4-2 g5 ,5"Z..Fiow
Meter 1 33636.so
133R TW4-11 C)3'.1Z Flow
Meter
I '-lOD TW4-21
Meter .0 Sb~bS!7_o-z.
1346 TW4-37 6 7.. _ J 7 Flow I 7. D
Meter So4 -z.o<t ,' c
Operational Problems (Please list well number):
System Operational (If no note
any problems/corrective actions)
(J'ebj No
(:e~' No
cf~sj No
(Y~ No
'(e_5> No
~No
(Yef) No
7Ye§) No
~No
/?.eS No
O'eS:> No
~No
('?eS) No
~_;No
... -lfe§\ No
~No
~No
~No
~No
(YeS) No
;fe~ No
~No -
?(es) No
~.JNO
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
Monthly Depth Check Form
Date 7}'2-z./u; Name b tJ...N'\ "'-~e.. lvtAe...!j JA.,""u-l4o/(,Jc.y
Time Well Depth* Time Well Depth*
0 ~13 MW-4 /S.tl 67~1 TWN-1 63.00
0 ~1 ~ TW4-1 g6. 1.\ l ~7~g TWN-2 'Jt.t.l3
o&t b TW4-2 S5. LtO b736 TWN-3 40. 11.{
()!ko 'I TW4-3 S7.5C6 (;)7~3 TWN-4 ss, 't (
Dg11. TW4-4 7 \.CiS C2 72.~ TWN-7 g lj{' 2-l{
D8D:t TW4-5 6~.2.?... 0736 TWN-18 6o . ?)
0 q:l_3 TW4-6 ?;r.oo D. 7'l. 7 MW-27 54. 6%'
Q ~t5 TW4-7 76.\Z. (J 750 MW-30 75,41
f'J ~I ( TW4-8 /~.5 3 b75'1 MW-31 6~. 61
(') 'lo6 TW4-9 6 J,oq
D_f<b 2... TW4-10 6. z .7C2
ogtg TW4-11 qz. 6g
07'-13 TW4-12 46.35
6. :z so TW4-13 sz.6' C> 7"i5 TW4-28 40, ::s~
675j TW4-14 7<1.66 075~ TW4-29 7Y.zo
l>~l' TW4-15 6>.so l'Y6D5 TW4-30 75.56
(
~ b7S1. TW4-16 Q:4.:f7 08D7 TW4-31 7'i.Z~
Q7S7 TW4-17 77.8D 0739 TW4-32 ~51 . .3&
87Y~ TW4-18 6.6 .l j o7L-l7 TW4-33 7 z., 15
c gl..{o TW4-19 6Li.Lj2_ ogoo TW4-34 72.2()
0.8 2.6 TW4-20 64.66 ()~03 TW4-35 7tt .ZO
67~6 TW4-21 6S.oY. (')75?.. TW4-36 56.So
D8:Z.'-t TW4-22 6_2.-34 Q5Z.L TW4-37 () Z., I <l
6 8:17 TW4-23 IO.D,('
b~"Z.'{ TW4-24 6 (6.&7
07::.}1 TW4-25 6_5. '13
0~1 t TW4-26 67.tz
0756 TW4-27 1'1.67
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Weekly Inspection Form
Date Name
System Operational (If no note
Time Well Depth* Comments anv oroblems/c.orrective actlonsJ
i 1.{ 'Z6 MW-4 <zl.t"lO Flow 1..(.'1 (Y~s ,No
Meter 1 o&" ?·z&.l<-4 ('YE!j[ No -ll{o{ MW-26 M.7o Flow 7.6 (Yes') No
Meter l i:>c -<S\ . ~o (Ye~ No
1457 TW4-19 64. t-z.. Flow 1 8'.o d_e~_No
Meter ~271'1'1. (i} /Ve~ No -:
ILtoo TW4-20 63.86 Flow b .. ( f(e?l_ No
Meter 1 ~-tbl7g. cto ffeS) No
\l-{37 TW4-4 73.5~ Flow li~D lle~ No
Meter ~S?~4~5'"' Z/") <'[~ No
1530 TWN-2 33.7o Flow 18' . .5' (Y~S)No
Meter 6702'-16.50 (Yes_} No ....
i:S4A TW4-22 58'.1~ Flow _L_&_.O ~No
Meter 3.3qb5i. u /r'"eS>) No -
( 1l_3j TW4-24 6_L.gs Flow I k.b Xe$ No
Meter i 6<30 . .53. L..j c;: /f'SS) No
ll'Z'?... TW4-25 6 'C 8-1 Flow 14.Y ;fes) No
Meter t67ol~c;. Z6 ~No
--: .........
\L/3."'"~ TW4-1 ~4. • .46 Flow lb.D fie_s )'Jo
Meter 13.5436.'2.6 TTe9) No ·-
I'-~ z.t_ TW4-2 S?rJ t) _c:; Flow 17.0 /f'es) No
Meter 1351~7. qo ?Ve~ No
lYI'-{ TW4-11 16·~ Flow L£,o Yell No qz.sz.. Meter klqs 6. 6o (VeS) No
1315 TW4-21 6 7. 75.«1 Flow lb.() .ffes')No
Meter 5 73g '17 'S' ffej No
"
1353 TW4-37 f../l.. \5 Flow (l. D /(esJ No
Meter 5 i '2 'i.e> 7 1 n ~-No ,__.
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
System Operational (If no note
Time Well Depth* Comments any problems/corrective actions)
t'l1.'3 MW-4 7q,70 Flow 4.4. \.Yes~ No
Meter loCi l 'Z. ~5 II (.~No -
tZ.3l MW-26 6 '2 .'fl.{ Flow /. ?._ rte.i) No
Meter l D 1767.56 f/eS) No
l317 TW4-19 64. rtb Flow I~.D (Y~ No
Meter -~:3E:3oq. tD ~No
1'22.~ TW4-20 ( Y .as-Flow _b,z. tY_e~ No
Meter j L.f 70_ ~ .:r. '3.0 rteS> No
IZ4h tw4-4 7g,q{., Flow I l ·D ~No
Meter J,~7b43.:?o ~No
t l.C>'t TWN-2 6Cf. YS Flow ~~-5 lf_es)No
Meter 673loo.~ ~No
l 'Z. '2.4 TW4-22 S'iS • .3.'1 Flow 11.5 lfe~ No
Meter ~ ... I'-IOS.6D ~No
1 ~'to TW4-24 t:. I.I.Z. Flow L6.D /(aS) No
Meter l/?....~7f. 5'1 .....,-ev No
t~OS TW4-25 CJo.l_3 Flow 14.0 t<ies)No
Meter i 67~7DI.6o /lf85) No
~ .....
I'Z..'-\l. TW4-1 £15 Z4 Flow J6.0 /Yej\ No
Meter 1 36737.'-lo ~No
t'Z.37 TW4-2 lll.f. 7D Flow a ll.o /'fe~ No
Meter i 368411 ~0 )'feS) No
lUI.( TW4-11 q l. ',. Flow i~.{"J reSJ No
Meter 3!?...07.oD ~No -1 z.o-z.. TW4-21 k <6. 3& Flow i6.o (Yes) No
Meter 5~3031. 33 treS\ No
I ~26 TW4-37 62.63 Flow i 6. ~ ;res :::t-J 0
I Meter .S2.o?66-t.o CIB 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 g/g/16
Svstem Ooerational tlf no note
Time Well Depth* Comments anv oroblemslcorrective action~
t7..S5 MW-4 gt.36 Flow Y. . .S )([s\No
Meter l Oli7 7 "?. CC} .~St: .~No
\!..4~ MW-26 77.Cfl.. Flow 7.0 (Y~ No
Meter 103110.70 rye~ No
...........
\ ]'2«i' TW4-19 . b 7. '-t I Flow I~.D Xes) No
Meter SYq't\6_g{) /fe§) No
\ -r 1.{ b TW4-20 6'-l.oZ. Flow b.?_ .f'f§i_ No
Meter t '-1 go '2. 'Z--~o ~ No
.::--..
l)DI TW4-4 ~7,i.f'f Flow 'i .o (Yes)No
Meter 3GI7Z..~.7o eYe~ No
_l'Z.~'i TWN-2 lS".qo Flow t ~.s /(eS) No
Meter k773"!3. 'iD .~No ..__
I L. '-f{) TW4-22 .s g, '2.5 Flow 17·6 L'(es~No
Meter 3'-1336 'Z.. YO /"'Y 6]-J No
...--.--x
r JZ-37 TW4-24 61.$'2..... Flow //;;.o (Yes,../No
r Meter l/6'17'l.Dg ,?reS')No
Jl.:3o TW4-25 72.S4 Flow Jl.\. 7...... /Y'es. No
Meter 1 b~rb_6_1' .. 13o ~No
!ZSS TW4-1 /()4, &~ Flow \6.o (Ve~ No
Meter I 3S'I71'). 7 D ~_No
)"Z-53 TW4-2 IOO."l.o Flow 1~.~ ;fes) No
Meter 13~?o ~~-so ~No
t1.5i TW4-11 qz. '3.5 Flow 16-D ~ No
Meter 3 I L-iS' '·L I r, ~No
I ?..2.7 TW4-21 f.,/~j)S Flow 1 h_O _('fa~ No
Meter 5'12:2.35. 77 779s) No
IZLl3 TW4-37 h_Z. L/7 Flow 17.0 /('e§.. No
Meter S'Z.$1( 83.. Oc.J ~No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Name UCz-rri,c,_ ~0 l,;vo..e..r, l"'-k'-X'\..-~r \\-u 1\i by
System Operational (If no note
Ti me Wll e 0 th* ec1 c t ommen s I msl . . ) anll ~robe corrective actions
l'-1'2.3 MW-4 551 34 Flow \.{,!..( /'Yes }Jo
Meter ll fl 1·L'S~ 7 ':{ S7 .zi9S)No
~.....-:::'"
l"to8 MW-26 G'i sc;-Flow /,D Xes) No
Meter lD~.iS03. 76 ?'fe"'S')No
~
1'-142 TW4-19 70, 9C, Flow I S'. l ffe$) No
Meter SS3.S¥t<~ 6_0 (reS'/ No
l'-to5 TW4-20 ~.3 . 7~ Flow 6_2. (Yes)No
Meter l '-'l qo c7 ,k'-i ffe""'$') No
\4 z.o TW4-4 '7/.,.77 Flow Lt.o /fevNo
Meter 3 '1.Slj 'Sl X'r J "7rW No
)353 TWN-2 J.3 _qg Flow 1g.s ;<?e"'S) No
Meter 68'o&~'i.l6 Cliff; No ....
135~ TW4-22 \Do.Z3 Flow \l.() ('Yes \No
Meter 3 Lj 52...5 <-1, ~0 CY_e~No
( 1356 TW4-24 6·Cj .65 Flow \6-6 ?f881 No
Meter J813lO_, 6 7 ~No
135o TW4-25 K14 ].5 Flow }I..(, 4 /'feS\ No
Meter 1Aq6'S'i3 tD ~)NO -\ Yf7 TW4-1 lt4.{.~5 Flow \ {,-. D /Ye~ No
Meter I.Y147!. 70 r=r:e§? No
ll.fl~ TW4-2 8o.96 Flow I b.() {Y,e$'-\No
Meter 13'1t.Jt..4 .7o ( YSS\ No
\ '-1' ' TW4-11 'f 1.05' Flow t {,.o r1"es) No
Meter 217 9'1.So ~No
1"34 7 TW4-21 67, &'o Flow l6.5 t/e~ No
Meter 6614 ?q_.. 7 i ~No
\ "\Ol TW4-37 6Z.. to Flow 17,6 2@§1. No
Meter S371gz f/) ?re1i 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
System Operational {If no note
T' a me Wll e D h* ept c omments anl£ (!roblems/correctlve actions}
lfZ'f MW-4 ~1.60 Flow 4.5 /(~No
Meter IIlli t:.8 . -z l ~No
::::-,_
llW MW-26 /;3.37 Flow /I /Yes) No
Meter l D59D,.:3.D ?Vesl) No -
1~'40 TW4-19 6S.z?.._ Flow t f<-0 .f'fe~No
Meter .S"AZ( 13 2;0 ~No -17.1/ TW4-20 61.{,2..5 Flow 6.'{ (Yet$) No
Meter 150D 'Z.S'. 60 ~No
~
\'L~3 TW4-4 7Z. t'-{ Flow ~q .D )(9s)No
Meter YOCOtD . "t% ~No
~
(''2-06 TWN-2 gj, 78 Flow \<6 .6 /(e~ No
Meter .( q; '-13 IS'. 4o ?fes') No
I! I L TW4-22 Si.SD Flow j g,o ;fes) No
Meter 3'-17~70 .60 /"19l0 No -
t7.oq TW4-24 61.66 Flow 15.2.. (reS) No
Meter \G553ct l'f (Ye!;> No
I H>3 TW4-25 b3.7D Flow \<.{.L.( ('?e~ No
Meter l704q6_3.3() ~No ...
IZ:S Z.. TW4-1 R6, :;o Flow l 4 .h /{S~o
Meter 140634.60 {"TT!S )No -
l 'Z. z.t. TW4-2 7tt -66 Flow l.';.o (Vei) No
Meter 140<640 .. DC ~No
I 22'1 TW4-11 C,1. '8''-{ Flow ~~-0 d'e~ No
Meter :31Cft46.60 <(e~ No
1?.-oo TW4-21 AE.SI Flow \6.0 f{es) No
Meter 61D6o9 33 ~No -
'21 L{ TW4-37 6?:.~1 Flow tl,l) ('Y'_WNo
Meter 5'45369 . 3o ct~No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
• Depth is measured to the nearest 0.01 feet.
g /'2.3(1 6
Monthly Depth Check Form
Date Name ,..A,I\1\.t!_r 1-foii~J:.y~ G"',..,..;..._ P.,J ... o:..r-
Time Well Depth* Time Well Depth*
[) ~Z.J MW-4 go 11.\ o Q92] TWN-1 Gz.qs
o rc.'-t TW4-1 ~~-10 oq'-lo TWN-2 ']." I !..j z.
C>%2'2. TW4-2 g b . qz. D'i.2~ TWN-3 L-IO. 61
Cl~3S TW4-3 57-56 oq~:s TWN-4 .s~.~~
D8U TW4-4 7""2.10 C4Y.5 TWN-7 &Sl7
0~~~ TW4-5 651'30 0'{31 TWN-18 fd).60
()S~q TW4-6 J 'l.. 86 oq4z MW-27 b4 ,~:J
o1SL\l TW4-7 7b,l.!b QGHj MW-30 75 '2--6.
()~~7 TW4-8 7'tYO Q'HI:z MW-31 ~~ .4C>
0833 TW4-9 (,3,0 ~
Og.3o TW4-10 62.66
08"'2..( TW4-11 ttl.bB
0'lD,5 TW4-12 L\6.45
D~Q3 TW4-13 S?...Sb OOfD( TW4-28 YD.L1~
QqQC> TW4-14 79. Y3. o~~g TW4-29 ]1.\.!C:.
~~L.Q TW4-15 6 L\.. 6 '2. OS53 TW4-30 15 .. ,6
OSZ.'-TW4-16 f.'i.OS 0~52. TW4-31 1~~05
oqt~ TW4-17 '77.76 0~0<1 TW4-32 S\.70
0929 TW4-18 bCc.O'J. 02lL-\3 TW4-33 ·tz.9j
D. ~DO TW4-19 65. y (') D8S~ TW4-34 72.tS
0~1~ TW4-20 6~-3£ 0~~5 TW4-35 1'(. D1S
L}CJ30 TW4-21 7~-~7 D'l'o-z.. TW4-36 S~-3:l
C28£)K TW4-22 scr .ss ~817 TW4-37 6_3,4'1.
0~:!3 TW4-23 6_'1.'15'
0 ~I b TW4-24 b I . 't6
08\5 TW4-25 63.75
0845 TW4-26 {7. 7_7
DSso TW4-27 J~. j 8
Comments: (Please note the well number for any comments)
* Depth is measured to the nearest 0.01 feet
Date ~/z./zotr-
Weekly Inspection Form
Name -r;..floer-Holi.'J&tH'
System Operational (If no note
Time Well Depth* Comments anv oroblemsk:Drrective actions)
\Oi1 MW-4 80.'15 Flow q,~ I (~No
Meter It 1.\S '\ 10 .I (Yes _...No
---.
I \Olio MW-26 G,4.Sb Flow 1.0 U..e.s No
Meter lOR 130.9 ( Yes )No
~
\D~Z-TW4-19 f,b, '3.\ Flow 1g D C 'las )No
Meter 57:5 \.f~l . g (Yes }lo
::::=::;:
lD''Z. TW4-20 (;.3.~~ Flow 6 . .5 <Y.ssANo
Meter 15\~ ~7.52 \'Yes/No
I t ..___...
\0'3"3 TW4-4 /z.~g Flow q,o (Y~ No
Meter 40~S 15. Z ~Yes -~o
:;;;:::::::::
iO~~ TWN-2 · 34, '14 Flow 1'0.0 (Y~o
Meterusq8ros (Ves \Jo
10d1:. TW4-22 sq.bo Flow \8,() (~No
Meter 34'HS33, & (Yes )No
JQO""':. TW4-24 C,...)l Flow lb,O (Y~No
Meter il1ZL_S{...rg {Yes) No
a!i5i TW4-25 (;3.82 Flow l~ • .s (Xe~No
Meter n t $lj_l5. 3 /Yes )J_o
-....~
\D~D TW4-1 B7,{;.l Flow I LJ ,_!;. ( .Y.e..s No
Meter I Ll.Zk:.C:.O .l ( TeS )No
~
\O"Z'-t TW4-2 '60 .3'3 Flow «t'c-. lb,D (Yas )No
Meter "'r~ .... h_~ • .J;. 1"!3 135,& (Yes) No
\01.1 TW4-11 qz.yj Flow~! llo.O _( )L.es ~o
Meter 3-z:::>zs. I ( Y'_es] No
-......... ./
oqE:P TW4-21 68.5~ Flow lb.O C~No
Meter f,Z'-1817,23 (Yei> No
.-<-.,
IOO't TW4-37 6Z ,S~ Flow \1.0 (~ )No
Meter t:_57'l Z""S.'l ( Yes No -
Op rational Problems (Please lis! well number):
Corrective Action(s) Taken (Please list well number): ---------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
System Operational (If no note
Time Well Deoth* Comments anv Droblemslcorrective actions}
le>o.£"" MW-4 ~-'Z..''l... Flow ~-Y ~No
Meter 1 1 -u, -z l 1 <6o ~No
.....
0'157 MW-26 6o...t.l7 Flow 7.1 ~~5) No
Meter ~ ta'll35, l~. ~No
I o '1D TW4-19 64.€& Flow I~.{) ~No
Meter SBu~. g7, lo ~No
o qs'i TW4-20 64.17 Flow 6.~ ~ No
Meter l523DO~ 70 ~ No
~
it> It TW4-4 7Lj. ~I Flow '7.o tie~ No
Meter '-to ~5""7 .3. oO ~ No .__..
0~1.{1.{ TWN-2 3J . .SD Flow ( ~.5 IY.~~ No
Meter _6_ ') Z..3 I 'l-~ msl No
~
~ qy q TW4-22 61.77 Flow I R.D ~No
Meter 35tZ.5J C)o ~ No --=--
0'147 TW4-24 65-()7_ Flow I 6.6 /fe?\ No
Meter i q.s-11q.'io ~No
()'1'-l/ TW4-25 6~ 76 Flow 14./ /(e?) No
Meter I 7_'2._Y_1...S_L.! J.iO -~_No -
ID07 TW4-1 '8~. y L( Flow I S".D ~No
Meter l43k1o g6 ~No -=
lo o:J TW4-2 M'D.ZO Flow ''·D {(.fis') No
Meter I Y4'2..52..S'O ~No
l O() U TW4-11 't'Z. t)'t Flow 1 6-o ?(es) No
Meter 3 "l-506 . ::r 0 ('YeS) No
D93S? TW4-21 6~L 70 Flow 16.S l~No
Meter {;314~~."77 (Yes} No
~
0~51 TW4-37 64.11 Flow l"l.o 0LesJNo .0
Meter 563$57. oo (y_ei§\ No
-.....__,J
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
* Depth is measured to the nearest 0.01 feet.
\
I
_)
Time Well
I:IS~ MW-4
1~47 MW-26
•.34 11 TW4-20
1'-lol TW4-4
l'tSi TWN-2
133'1 TW4-22
t337TW4-24
1 "Z.s;( TW 4-25
l3S4 TW4-1
13SDTW4~11
J 3 '-I t TW.4-37
Weekly Inspection Form
Name 6 h-f"tl\1\, P& l yVI,XC l r~ ..... "'rv L-lp '(.; J. {J-t
Depth* Comments
Slo .1 o Flow 4 _._,
Meter H ~ tlc1'"'Z. :1 o
I.S, 15 Flow '7. l
Meter t 1 ot..SSt 7()
63. 7{:. Flow t 5. o
System Operational (If no note
any problemslcorrecttve actions)
(Y~ No
<fit> No
~ No
~.No
Meter !;. ~7<;76.6~ (V"e13 No
63. gl Flow L./.. ~No
Meter JS3D 3i. lo (Ye]) No
~ No
(~No
.3t.t..lil.. Flow 1<6.5" (Yes.' No
(Vfjj No ......
58" .. ol Flow 18.0 X€S)No
Meter ~No
6'. '-\o Flow lb.()
Meter
(,6 55 Flow _..., ... ' . 1'-\.5' tres) No
Meter ~No
~o. Lb Flow JS.b l(e~ No
Meter l'f_e~ No
(Yes)No
Meter L":t . .s:·z .. ~z.3o d"eJ) No
-~z _y_s-Flow Lb. 0 ("Yes)No
Meter .21.7~_7. 60 ~No
A 7. lf.2 Flow J ~ .$ ~-~No
Meter 6:S_53_(,.<~.53 _fes) No
("'f'9S) No
tre!( No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ----------'-------
,. Depth is measured to the nearest 0.01 feet.
Date
Ti me Wll e
lZ4b MW-4
I 'l... -z..g MW-26
l ']5,<::; TW4-19
I -z..J ( TW4-20
17. 4.5 TW4-4
f z t.( TWN-2
l 'Z. ?...:J TW4-22
\ "ZZ I TW4-24
!'l..t5 TW4-25
tz.LlZ TW4-1
I Z...37 TW4-2
l 'Z-:J '-i TW4-11
l'Z.I'Z. TW4-21
lt-?...5 TW4-37
Weekly Inspection Form
D h* ept
7q, €''{
i' ...,._
_"-.;
G"J .l7
h 4.8' ~
A '·L 1. Z-
(S.U
S_f._.Sc,_
5"S. 6 'Z
6 1.51..1
I Oct, 3D
ft6,'-/'1:
1/i.,. bD
crz. "'S
E;s .ss
6Z .~o
Name Gc..rr-':A.. e<\((1(\c<Ct IAn"'-'U"" t-\c..Lt:dtty
System Operational (If no note c omments an!£ eroblems/corrective actions)
Flow Ll.5 _XSs.}No
Meter 1137,D6 '2.7 ~ No
Flow 7.Z f(es)No
Meter ,,..., ~No
\\\6.,..£". '"
Flow l€.0 lfe~ No
Meter S'16S""SLI .30 t<le~ No
Flow (, .6 tre"§\ No
Meter I .s. 4 I S( . "ZD ~ No
Flow 'LD ~No
Meter c.ttl.& 7 I Sfn ?f_e~ No
Flow J s.s-("fe~No
Meter G.'lfll./_'\1... LID {V_e~No
Flow J s-·.o ~No
Meter 2.544 '1 ~ .7~ ~ No
Flow lb.o /"'feS ""'\No
Meter Z.o '2.3 '7 c, .~l'l ~No
Flow I L\ .5 ~No
Meter 173'1/4q~J.O ~No
Flow I.S. "2.. ~)No
Meter 1 LfS"~'Hs .qo ?fe~ No -
Flow tl •. o {(9S_) No
Meter I L!6b3g. 76 ~No
Flow lb.D ;res) No
Meter 3'2-~ \0, CiO cVevNo
"'\
Flow 16.5 CY~o
Meter hi../7ZoG..f,g3 (Yes) No -Flow J7_.D Cle]) No
!Meter 577KIS ._So ('Yes) No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
* Depth is measured to the nearest 0.01 feet.
Weekly Inspection Form
Name 6o.r.-...' ....._ P ~ \ ......._~r 1 Tg, t\c"'-£C" tl-ell.'ky
( ' System Operational (If no note
T" 1me Wll e 0 h* ept c omments sf I an~ eroblem correct ve act1ons}
t.>'i Ll MW-4 @:I.:S/ Flow 4 .. 'i )(es\No
Meter II 4~11 &of Sc..f ~No
l~l,g MW-26 67·00 Flow I, l {fa§) No
Meter I 135&.-to_ '3o ~No
_li.4.S'1 TW4-19 k1.6S Flow 1 g",o nrSi. No
Meter 6f,7~q3,'-IO ~~No
\ 'J z.g TW4-20 ~4 to Flow 6.5 ~9g, No
Meter 155"tb3-9'b ~No
\ '3~ TW4-4 7Z.. '-lo Flow tt.o Xes) No
Meter 42.1~53.01"\ l[_e~ No
1314 TWN-2 35.6'-\ Flow l()"b /1e5)_ No
Meter IOZ.~l4.-C~D ~eVNo -
l :3'2S TW4-22 5ir.3'l Flow I~.{) ((es) No
Meter ~-5'~7/1.60 ~No
-
UZ'Z... TW4-24 _6_1 • ,, Fl.ow 16.{.) lYe?\ No
Meter td7515. 30 ~No
I
1316 TW4-25 65.541 Flow 14.S ~;No
Meter 1751054 ~o· l'fe?)No
I '347 TW4-1 ~g.fy Flow IS'~D ~No
Meter Jl·l 7' 1.1:3 2. I 0 ~No
13'--li TW4-2 ~~-15 Flow • t,.o ~No
Meter 11.4A~<\Gl.~ ~No
1'334 TW4-11 qz. 3n_ Flow ll; ._o_ t'TeS.J No
Meter 23Z.'Z7. \D ?Y'"e]> No
I 112_ TW4-21 6<6'.1 ~ Flow ,,,3 l(e_SJ) No
Meter b59'11.\ Ci ~0 -~No
_i:lZS' TW4-37 ~'Z.Y7 Flow 171 ~e]) No
Meter _$"g~Z.I '7. W TYe.P No
Operational Problems (Please list well number):
Corrective Action(s) Taken (Please list well number): ---------------
* Depth is measured to the nearest 0.01 feet.
TabD
Kriged Current Quarter Groundwater Contour Map, Details Map, and Depth to Water Summary
Time
1221
1400
1253
1253
1356
1409
1354
1332
1336
1238
1227
1215
711
759
1352
1440
1327
1436
1444
1437
1403
1405
1412
1416
1344
1340
1350
1348
1338
NAME: Garrin Palmer, Tanner Holliday
9/29/2016
WeU
MW-1
MW-2
MW-3
MW-3A
MW-5
MW-11
MW-12
MW-14
MW-15
MW-17
MW-18
MW-19
MW-20
MW-22
MW-23
MW-24
MW-25
MW-26
MW-27
MW-28
MW-29
MW-30
MW-31
MW-32
MW-33
MW-34
MW-35
MW-36
MW-37
Depth to
Water (ft.)
64.37
109.80
82.85
84.76
106.24
86.07
108.25
103.09
106.14
72.02
72.37
62.51
85.40
66.95
114.00
112.87
77.56
67.46
54.85
75.31
100.69
75.45
68.60
77.95
DRY
107.80
112.42
110.55
110.19
Time Well
1423 MW-4
1422 TW4-l
1422 TW4-2
1427 TW4-3
1421 TW4-4
1430 TW4-5
1420 TW4-6
1423 TW4-7
1425 TW4-8
1429 TW4-9
1432 TW4-IO
1433 TW4-11
1314 TW4-12
1313 TW4-13
1309 TW4-14
1436 TW4-15
1435 TW4-16
1416 TW4-17
1152 TW4-18
1459 TW4-19
901 TW4-20
1455 TW4-21
1449 TW4-22
1419 TW4-23
1448 TW4-24
1453 TW4-25
1420 TW4-26
1300 TW4-27
1316 TW4-28
1308 TW4-29
1303 TW4-30
1301 TW4-31
1317 TW4-32
1258 TW4-33
1306 TW4-34
1304 TW4-35
1311 TW4-36
902 TW4-37
Depth to
Water (ft.)
81.37
94.10
88.02
57.86
73.10
65.58
73.24
76.46
79.70
63.33
62.97
92.98
46.69
52.95
79.53
67.46
64.30
77.95
66.26
64.01
64.10
68.53
84.40
70.30
62.48
65.23
67.56
79.62
40.64
74.46
75.84
79.15
52.15
73.25
72.47
74.30
56.59
62.45
Depth to Water
Time Well (ft.) Time
1213 PIEZ-1 65.55 NA
1204 PIEZ-2 40.10 NA
1201 PIEZ-3A 50.90 717
1324 PIEZ-4 60.00 722
1322 PIEZ-5 59.66 1345
1150 TWN-1 63.14 731
1446 TWN-2 35.02 727
1231 TWN-3 40.71 724
1200 TWN-4 56.15 1246
NA TWN-5 Abandon ned 1244
1218 TWN-6 78.78 1241
1223 TWN-7 85.05 741
NA TWN-8 Abandon ned 736
NA TWN-9 Abandonned NA
NA TWN-10 Abandonned 745
NA TWN-11 Abandon ned NA
NA TWN-12 Abandon ned 748
NA TWN-13 Abandonned 803
1210 TWN-14 61.17 806
NA TWN-15 Abandonned 753
1208 TWN-16 47.70 809
NA TWN-17 Abandonned 757
1156 TWN-18 60.76 NA
838 TWN-19 53.46
Well
DR-I
DR-2
DR-5
DR-6
DR-7
DR-8
DR-9
DR-10
DR-ll
DR-12
DR-13
DR-14
DR-15
DR-16
DR-17
DR-18
DR-19
DR-20
DR-21
DR-22
DR-23
DR-24
DR-25
Depth to Water
(ft.)
Abandonned
Abandon ned
83.22
94.25
92.14
51.25
86.66
78.40
98.17
91.09
70.05
76.43
92.99
Abandon ned
65.02
Abandonned
63.15
55.80
100.77
60.61
70.24
44.39
Abandonned
@ estimated dry area
PIEZ-3A May, 2016 replacement of perched
~5587 piezometer Piez-03 showing
elevation in feet amsl
MW-5 perched monitoring well showing e 5503 elevation in feet amsl
TW4-12 heel . . II
0 5578 temporary perc mon1tonng we
showing elevation In feet amsl
TWN-7 heel . "t . A.5564 temporary perc nitrate mon1 onng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
g 5590 elevation in feet amsl
RUIN SPRING o 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11,TW4-19, TW4-20, 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 3rd QUARTER, 2016 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/nov16/WUUwl0916_rev.srf D-1
,..;;-'/:,~ ,,,,
I I I I I I I I
estimated chloroform capture zone
boundary stream tubes resulting from
pumping. (note: combined capture for
MW4,TW4-1 ,TW4-2, and TW4-11;
and for TW4-19 and TW-20 is shown)
estimated nitrate capture
zone boundary stream tubes
resulting from pumping
@ estimated dry area
PIEZ-3A May, 2016 replacement of perched
~5587 piezometer Piez-03 showing
elevation in feet amsl
M.W-5 perched monitoring well showing
5503 elevation in feet amsl
TW4·12 h d . . II 0 5578 temporary perc e monttonng we
showing elevation in feet amsl
TWN-7 h d . . . A.5564 temporary perc e nttrate momtonng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
g 5590 elevation in feet amsl
RUIN SPRING o 5380 seep or spring showing
elevation in feet amsl
HYDRO
GEO
CHEM,INC.
TW4-21 and TW4-37 are chlorofonn pumping wells; TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
KRIGED 3rd QUARTER, 2016 WATER LEVELS
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
DATE FIGURE
H:/718000/nov16/WUUwl0916cz2.srf D-2
,. ... ,,,.~ , , ,, , , ,,
I I II
estimated chloroform capture zone
boundary stream tubes resulting from
pumping. (note: combined capture for
MW-4,1W4-1 ,1W4-2, and 1W4-11 ;
and for 1W4-19 and 1W4-20 is shown)
I I II
PIEZ-3A
~5587
MW-25
• 5535
TW4-7
0 5545
PIEZ-2
I;;) 5589
estimated nitrate capture
zone boundary stream tubes
resulting from pumping
May, 2016 replacement of perched
piezometer Piez-03 showing
elevation in feet amsl
perched monitoring well showing
elevation in feet amsl
temporary perched monitoring well
showing elevation in feet amsl
perched piezometer showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11, TW4-19, TW4-20, TW4-21 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 3rd QUARTER, 2016 WA
AND ESTIMATED CAPTURE ZONES
WHITE MESA SITE
FIGURE
H:/718000/nov16/WUUwl0916cz.srf I D-3
TabE
Kriged Previous Quarter Groundwater Contour Map
@ estimated dry area
PIEZ-3A May, 2016 replacement of perched
~5588 piezometer Piez-03 showing
elevation in feet amsl
M.W-5 perched monitoring well showing
5503 elevation in feet amsl
TW4-12 0 5578 temporary perched monitoring well
showing elevation in feet amsl
TWN-7 hed o 0 0 ~5564 temporary perc mtrate mon1tonng
well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5590 elevation in feet amsl
RUIN SPRING o 5380 seep or spring showing
elevation in feet amsl
NOTES: MW-4, MW-26, TW4-1, TW4-2, TW4-4, TW4-11,TW4-19, TW4-20, TW4-21 and TW4-37 are chloroform pumping wells; TW4-22, TW4-24, TW4-25, and TWN-2 are nitrate pumping wells
TW4-11 wafer level is below the base ofthe Burro Canyon Formation
HYDRO
GEO
CHEM,INC.
KRIGED 2nd QUARTER, 2016 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H:/718000/aug16/WUUwl0616osrf 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 06117/80 94.30 92.74
5,528.03 09115/80 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 09/01184 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 09/01185 93.40 91.84
5,528.93 10/01185 93.40 91.84
5,528.93 11101185 93.40 91.84
5,528.83 12/01185 93.50 91.94
5,512.33 03/01186 110.00 108.44
5,528.91 06119/86 93.42 91.86
5,528.83 09/01186 93.50 91.94
5,529.16 12/01186 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 11120/87 93.33 91.77
5,528.75 01126/88 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 11102/88 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 11113/90 92.80 91.24
5,529.86 02/27/91 92.47 90.91
5,529.91 05/21191 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 06/11192 92.48 90.92
5,529.90 09/13/92 92.43 90.87
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5 620.77 5,622.33 1.56 123.6
5,529.92 12/09/92 92.41 90.85
5,530.25 03/24/93 92.08 90.52
5,530.20 06/08/93 92.13 90.57
5,530.19 09/22/93 92.14 90.58
5,529.75 12/14/93 92.58 91.02
5,530.98 03/24/94 91.35 89.79
5,531.35 06/15/94 90.98 89.42
5,531.62 08/18/94 90.71 89.15
5,532.58 12113/94 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 05/11/99 70.25 68.69
5,552.83 07/06/99 69.50 67.94
5,553.47 09/28/99 68.86 67.30
5,554.63 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 05115/00 66.60 65.04
5,555.98 05125/00 66.35 64.79
5,556.05 06/09/00 66.28 64.72
5,556.18 06/16/00 66.15 64.59
5,556.05 06/26/00 66.28 64.72
5,556.15 07/06/00 66.18 64.62
5,556.18 07/13/00 66.15 64.59
5,556.17 07/18/00 66.16 64.60
5,556.26 07/25/00 66.07 64.51
5,556.35 08/02/00 65.98 64.42
5,556.38 08/09/00 65.95 64.39
5,556.39 08/15/00 65.94 64.38
5,556.57 08/31/00 65.76 64.20
5,556.68 09/08/00 65.65 64.09
5,556.73 09113/00 65.60 64.04
5,556.82 09120/00 65.51 63.95
5,556.84 09/29/00 65.49 63.93
5,556.81 10/05/00 65.52 63.96
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,556.89 10/12/00 65.44 63.88
5,556.98 10/19/00 65.35 63.79
5,557.01 10/23/00 65.32 63.76
5,557.14 11/09/00 65.19 63.63
5,557.17 11/14/00 65.16 63.60
5,556.95 11/21/00 65.38 63.82
5,557.08 11/30/00 65.25 63.69
5,557.55 12/07/00 64.78 63.22
5,557.66 01/14/01 64.67 63.11
5,557.78 02/09/01 64.55 62.99
5,558.28 03/29/01 64.05 62.49
5,558.23 04/30/01 64.10 62.54
5,558.31 05/31/01 64.02 62.46
5,558.49 06/22/01 63.84 62.28
5,558.66 07/10/01 63.67 62.11
5,559.01 08/20/01 63.32 61.76
5,559.24 09/19/01 63.09 61.53
5,559.26 10/02/01 63.07 61.51
5,559.27 11/08/01 63.06 61.50
5,559.77 12/03/01 62.56 61.00
5,559.78 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 11/22/02 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 09/11103 85.23 83.67
5,539.96 10/02/03 82.37 80.81
5,535.91 11107/03 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 04112/04 61.78 60.22
5,561.06 05/13/04 61.27 59.71
5,561.48 06118/04 60.85 59.29
5,561.86 07/28/04 60.47 58.91
5,529.17 08/30/04 93.16 91.60
5,536.55 09/16/04 85.78 84.22
5,529.00 10/11104 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 07/29/05 77.17 75.61
5,544.67 09/12/05 77.66 76.10
5,541.28 09/27/05 81.05 79.49
5,536.96 12/07/05 85.37 83.81
5,546.49 03/08/06 75.84 74.28
5,546.15 06/13/06 76.18 74.62
5,545.15 07118/06 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 08/13/07 75.13 73.57
5,547.20 10110/07 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 10114/08 71.94 70.38
5,542.25 03/03/09 80.08 78.52
5,542.25 06/24/09 80.08 78.52
5,550.19 09/10/09 72.14 70.58
5,550.94 12/11/09 71.39 69.83
5,546.08 03/11110 76.25 74.69
5,550.98 05/11110 71.35 69.79
5,548.33 09/29110 74.00 72.44
5,551.01 12/21110 71.32 69.76
Water Levels and Data over Time
White Mesa Mill -Well MW 4
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,620.77 5,622.33 1.56 123.6
5,547.00 02/28/11 75 .33 73.77
5,557 .54 06/21/11 64.79 63.23
5,551.14 09/20/11 71.19 69.63
5,550.32 12/21/11 72.01 70.45
5,551.22 03/27/12 71.11 69.55
5,551.29 06/28/12 71.04 69.48
5,550.29 09/27/12 72.04 70.48
5,549.31 12/28/12 73.02 71.46
5,552.30 03/28/13 70.03 68.47
5,550.18 06/27/13 72.15 70.59
5,552.55 09/27/13 69.78 68.22
5,553.23 12/20/13 69 .10 67.54
5,551.91 03/27/14 70.42 68.86
5,552.93 06/25/14 69.40 67.84
5,552.23 09/25/14 70.10 68.54
5,552.08 12/17/14 70.25 68.69
5,551.13 03/26/15 71.20 69.64
5,556.02 06/22/15 66.31 64.75
5,543.38 09/30/15 78.95 77.39
5,551.13 12/02/15 71.20 69.64
5,542.10 03/30/16 80.23 78.67
5,542.31 06/30/16 80.02 78.46
5,540.96 09/29/16 81.37 79.81
--N 0 8
Depth Below Measuring Point (ft.)
00 0 g ~ 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 ~
01/20/92 ~
~
06/03/93 ~ 10/16/94 f"'' ~ '"1
02/28/96 t::;
~
07/12/97 "0 f"'' =--11124/98 0 <
04/07/00 ~ '"1
1-3
08/20/01 ....
9 ~
01/02/03 -.. ?
05/16/04 C"' -09/28/05 9 "0 "--'
02110/07
06/24/08
11106/09
03/21111
08/02112
12115113
04/29/15
09/10116
01123/18
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 11/09/99 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 03115/00 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 04113/00 81.40 80.38
5,537.48 04/21/00 81.10 80.08
5,537.68 04/28/00 80.90 79.88
5,537.58 05/01100 81.00 79.98
5,537.88 05111100 80.70 79.68
5,537.58 05115/00 81.00 79.98
5,537.88 05125100 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 08115/00 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 0911 3/00 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 11109/00 78.25 77.23
5,540.74 12/06/00 77.84 76.82
5,542.39 01114/01 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 03129/01 73.62 72.60
5,545.45 04/30/01 73.13 72.11
5,545 .89 05/31/01 72.69 71.67
5,546.19 06/21/01 72.39 71.37
5,546.50 07/10/01 72.08 71.06
5,547.18 08/20/01 71.40 70.38
5,547.59 09/19/01 70.99 69.97
5,547.84 10/02/01 70.74 69.72
5,548.12 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 11/22/02 66.31 65.29
5,552.48 12/03/02 66.10 65.08
5,552.74 01/09/03 65 .84 64.82
5,552.92 02/12/03 65.66 64.64
5,553.40 03/26/03 65.18 64.16
5,553.48 04/02/03 65.10 64.08
5,552.32 05/01103 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 11107/03 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 5,618.58 1.02 111.04
5,552.53 10111/04 66.05 65.03
5,552.42 11/16/04 66.16 65.14
5,552.46 12/22/04 66.12 65.10
5,552.07 01118/05 66.51 65.49
5,552.21 02/28/05 66.37 65.35
5,552.26 03/15/05 66.32 65.30
5,552.30 04/26/05 66.28 65.26
5,552.25 05/24/05 66.33 65.31
5,552.22 06/30/05 66.36 65.34
5,552.15 07/29/05 66.43 65.41
5,552.47 09/12/05 66.11 65.09
5,552.50 12/07/05 66.08 65.06
5,552.96 03/08/06 65.62 64.60
5,553.23 06/14/06 65.35 64.33
5,557.20 07/18/06 61.38 60.36
5,553.32 11/07/06 65.26 64.24
5,554.35 02/27/07 64.23 63.21
5,554.07 05/02/07 64.51 63.49
5,554.07 08/14/07 64.51 63.49
5,553.88 10/10/07 64.70 63.68
5,555.73 03/26/08 62.85 61.83
5,556.60 06/24/08 61.98 60.96
5,556.83 08/26/08 61.75 60.73
5,556.87 10/14/08 61.71 60.69
5,556.90 03/10/09 61.68 60.66
5,556.91 06/24/09 61.67 60.65
5,556.61 09/10/09 61.97 60.95
5,556.78 12111/09 61.8 60.78
5,556.75 03/1l/10 61.83 60.81
5,556.19 05/11/10 62.39 61.37
5,555.26 09/29/10 63.32 62.30
5,554.66 12/21/10 63.92 62.90
5,554.74 02/28/11 63.84 62.82
5,554.57 06/21/11 64.01 62.99
5,554.13 09/20/11 64.45 63.43
5,554.54 12/21111 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 03/28113 63.85 62.83
5,554.44 06/27/13 64.14 63.12
5,554.37 09/27/13 64.21 63.19
Water Levels and Data over Time
White Mesa Mill -Well TW 4-1
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
z 5,620.77 5,618.58 1.02 111.04
5,553.92 12/20113 64.66 63.64
5,553.20 03/27/14 65.38 64.36
5,552.20 06/25/14 66.38 65.36
5,551.13 09/25/14 67.45 66.43
5,550.72 12/17114 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 09/30115 82.73 81.71
5,529.54 12/02/15 89.04 88.02
5,527.55 03/30/16 91.03 90.01
5,525.92 06/30/16 92.66 91.64
5,524.48 09/29116 94.10 93.08
-8 1.0 Vl 1.0 0
Depth Below Measuring Point (ft.)
00 Vl 00 0 -...l Vl -...l 0 0\ Vl 0\ 0 Vl Vl Vl 0
11/08/99
04/06/00
09/03/00
01/31/01
06/30/01
11/27/01
04/26/02
09/23/02
02/20/03
07/20/03
12/17/03
05/15/04
10/12/04 ~
03/11/05 ~
08/08/05 ~ I .......
01/05/06 ~ 06/04/06
11/01106 ~ ~
""' 03/31/07 ~
08/28/07 ~ "'C
01125/08 er
06/23/08 0
11/20/08 < ~
04/19/09 ""' ~ 09/16/09 ... a 02/13/10 ~
07/13/10 ,-...
~ 12/10/10 "a'
05/09/11 -a 10/06/11 "'C .._,
03/04/12
08/01112
-12/29/12
-05/28113
10/25/13
03/24114
08/21114
01/18115
06/17/15
11/14115
04112116
09/09116
-02/06/17
07/06117
12/03117
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 11109/99 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 01124/00 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 04113/00 75.20 73.58
5,549.72 04/21100 75.00 73.38
5,549.82 04/28/00 74.90 73.28
5,549.82 05/01/00 74.90 73.28
5,550.12 05111100 74.60 72.98
5,549.82 05/15/00 74.90 73.28
5,550.12 05/25/00 74.60 72.98
5,550.12 06/09/00 74.60 72.98
5,550.22 06/16/00 74.50 72.88
5,550.07 06/26/00 74.65 73.03
5,550.17 07/06/00 74.55 72.93
5,550.17 07/13/00 74.55 72.93
5,550.18 07/18/00 74.54 72.92
5,550.33 07/27/00 74.39 72.77
5,550.38 08/02/00 74.34 72.72
5,550.40 08/09/00 74.32 72.70
5,550.42 08/15/00 74.30 72.68
5,550.54 08/31/00 74.18 72.56
5,550.87 09/08/00 73.85 72.23
5,550.97 09/13/00 73.75 72.13
5,551.04 09120100 73.68 72.06
5,545.83 10/05/00 78.89 77.27
5,546.47 11109/00 78.25 76.63
5,546.88 12/06/00 77.84 76.22
5,552.18 01/26/01 72.54 70.92
5,552.20 02/02/01 72.52 70.90
5,551.10 03/29/01 73.62 72.00
Water Levels and Data over Time
White Mesa Mill-Well TW4-2
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.10 5,624.72 1.62 121.125
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 09119/01 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 09/11102 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 05/01/03 71.01 69.39
5,548.98 06/09/03 75 .74 74.12
5,548.14 07/07/03 76.58 74.96
5,547.75 08/04/03 76.97 75.35
5,547.22 09/11/03 77.50 75.88
5,547.68 10/02/03 77.04 75.42
5,547.52 11/07/03 77.20 75.58
5,548.29 12/03/03 76.43 74.81
5,554.00 01/15/04 70.72 69.10
5,555.46 02110/04 69.26 67.64
5,556.90 03/28/04 67.82 66.20
5,557.49 04/12/04 67.23 65.61
5,558.07 05/13/04 66.65 65.03
5,558.19 06/18/04 66.53 64.91
5,559.00 07/28/04 65.72 64.10
5,554.26 08/30/04 70.46 68.84
5,551.97 09116/04 72.75 71.13
5,549.65 10111104 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 11/16/04 74.83 73.21
5,550.37 12/22/04 74.35 72.73
5,549.95 01/18/05 74.77 73.15
5,550.09 02/28/05 74.63 73.01
5,550.13 03/15/05 74.59 72.97
5,550.18 04/26/05 74.54 72.92
5,550.32 05/24/05 74.40 72.78
5,550.21 06/30/05 74.51 72.89
5,550.11 07/29/05 74.61 72.99
5,550.33 09/12/05 74.39 72.77
5,550.29 12/07/05 74.43 72.81
5,551.30 03/08/06 73.42 71.80
5,551.42 06114/06 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 08114/07 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 10114/08 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 09110/09 68.78 67.16
5,556.53 12/11109 68.19 66.57
5,557.87 03/11110 66.85 65.23
5,557.63 05111110 67.09 65.47
5,557.24 09/29/10 67.48 65.86
5,557.00 12/21/10 67.72 66.10
5,557.61 02/28111 67.11 65.49
5,557.58 06/21111 67.14 65.52
5,557.46 09/20111 67.26 65.64
5,557.84 12/21111 66.88 65.26
5,557.86 03/27112 66.86 65 .24
5,557.87 06/28112 66.85 65.23
5,557.46 09/27112 67.26 65.64
5,557.82 12/28/12 66.9 65.28
5,559.39 03/28113 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 09/25114 67.63 66.01
5,557.07 12/17114 67.65 66.03
5,549.93 03/26/15 74.79 73.17
5,551.30 06/22/15 73.42 71.80
5,547.12 09/30/15 77.60 75.98
5,538.34 12/02/15 86.38 84.76
5,542.22 03/30/16 82.50 80.88
5,538.31 06/30116 86.41 84.79
5,536.70 9/29/2016 88.02 86.40
\0 0 00 l/1 00 0
Depth Below Measuring Point (ft.)
-...1 l/1 -...1 0 0\ l/1 0\ l/1 0 l/1 l/1 0
11/08/99
04/06/00
09/03/00
01131101
06/30/01
11127/01
04/26/02
09/23/02
02/20/03
-07/20/03
12117/03
05115/04
10112/04 ~
-03/11105 ~
-08/08/05 .&;;;.
I N 01/05/06 ~ 06/04/06
11/01106 .... ~ "'1
03/31107 0
08/28/07 ~ ~
01125/08 .... t:r
06/23/08 0
11120/08 < ~
04/19/09 "'1
~ 09116/09 .....
02/13/10 e ~
07113/10 -~ 12/10/10 C"'
05/09/11 -e 10/06111 ~ '-' 03/04112
,_ 08/01112
,_ 12/29/12
05/28113
10/25113
03/24114
08/21114
-01118/15
06/17115
11114/15
04/12116
-09/09/16
-02/06/17
07/06117
12/03/17
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 11129/99 66.45 65.43
5,566.93 01102/00 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 02114/00 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 05115100 64.00 62.98
5,568.53 05/25/00 63.70 62.68
5,568.61 06/09/00 63.62 62.60
5,568.69 06/16/00 63.54 62.52
5,568.45 06/26/00 63.78 62.76
5,568.61 07/06/00 63.62 62.60
5,568.61 07/06/00 63.62 62.60
5,568.49 07113/00 63.74 62.72
5,568.55 07/18/00 63.68 62.66
5,568.65 07/27/00 63.58 62.56
5,568.73 08/02/00 63.50 62.48
5,568.77 08/09/00 63.46 62.44
5,568.76 08/16/00 63.47 62.45
5,568.95 08/31100 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 01103/01 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 07/10/01 61.21 60.19
5,571.70 08/20/01 60.53 59.51
5,572.12 09/19/01 60.11 59.09
5,572.08 10/02/01 60.15 59.13
5,572.78 11108/01 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 11/22/02 55.88 54.86
5,576.54 12/03/02 55.69 54.67
5,576.96 01/09/03 55.27 54.25
5,577.11 02/12/03 55.12 54.10
5,577.61 03/26/03 54.62 53.60
5,572.80 04/02/03 59.43 58.41
5,577.89 05/01/03 54.34 53.32
5,577.91 06/09/03 54.32 53.30
5,577.53 07/07/03 54.70 53.68
5,577.50 08/04/03 54.73 53.71
5,577.71 09/11103 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 01115/04 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 04112/04 53.08 52.06
5,579.47 05/13/04 52.76 51.74
5,579.53 06/18/04 52.70 51.68
5,580.17 07/28/04 52.06 51.04
5,580.20 08/30/04 52.03 51.01
5,580.26 09/16/04 51.97 50.95
5,580.12 10/11104 52.11 51.09
Water Levels and Data over Time
White Mesa Mill -Well TW 4-3
Total or
Measuring Measured Total
Water Land Point Depth to Depth to
Elevation Surface Elevation Length Of Date Of Water Water
(z) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 141
5,579.93 11/16/04 52.30 51.28
5,580.07 12/22/04 52.16 51.14
5,579.80 01118/05 52.43 51.41
5,580.35 02/28/05 51.88 50.86
5,580.57 03/15/05 51.66 50.64
5,580.86 04/26/05 51.37 50.35
5,581.20 05/24/05 51.03 50.01
5,581.51 06/30/05 50.72 49.70
5,581.55 07/29/05 50.68 49.66
5,581.68 09112/05 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 11107/06 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 10110/07 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 09110/09 49.33 48.31
5,583.27 12/11109 48.96 47.94
5,583.63 03/11110 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 02/28111 49.63 48.61
5,590.00 06/21111 42.23 41.21
5,582.70 09/20/11 49.53 48.51
5,583.05 12/21111 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 12/28112 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 09/27113 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) Monitor·ing (blw.MP) (bJw.LSD) Total Depth Of Well
5,631.21 5,632.23 1.02 141
5,579.62 03/27/14 52.61 51.59
5,578.52 06/25/14 53.71 52.69
5,577.59 09/25/14 54.64 53.62
5,577.40 12117114 54.83 53.81
5,576.73 03/26115 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 03/30116 56.61 55 .59
5,574.89 06/30116 57.34 56.32
5,574.37 9/29/2016 57.86 56.84
Depth Below Measuring Point (ft.)
-....! -....! 0\ 0\ Ul Ul +:-+:-Ul 0 Ul 0 Ul 0 Ul 0
11129/99
04/27/00
09/24/00
02/21/01
07/21/01
12/18/01
05/17/02
10/14/02
03/13/03
08/10/03
01/07/04
06/05/04
-11/02/04 ~
-04/01105 ~
08/29/05
,.
I ~ 01/26/06 ~ 06/25/06
11/22/06 ~ ~ "1
04/21107 ~
09/18/07 ~ "t::
02/15/08 ~ ::r
07/14/08 0
,_ 12/11108 < ~
05110109 "1
~ 10/07/09 ...
03/06/10 e ~
08/03/10 ,-..,
~ 12/31/10 er 05/30/11 -e 10/27/11 "t:: '-" 03/25/12
08/22/12
01119113
06/18/13
11115/13
04/14114
09/11114
02/08/15
07/08/15
12/05/15
05/03/16
-09/30/16
02/27/17
07/27/17
12/24/17
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 1.1 84 114.5
5,512.145 05/25/00 101.34 100.16
5,518.985 06/09/00 94.50 93.32
5,512.145 I 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 09101100 88.93 87.75
5,513.235 09/08/00 100.25 99.07
5,516.665 09113/00 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 11109/00 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 11/08/01 79.62 78.44
5,534.275 12/03/01 79.21 78.03
5,534.715 01103/02 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 01109/03 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) (bJw.LSD) Well
5,612.301 5,613.485 1.184 114.5
5,540.985 02112/03 72.50 71.32
5,541.675 03/26/03 71.81 70.63
5,541.765 04/02/03 71.72 70.54
5,541.885 05/01/03 71.60 70.42
5,542.025 06/09/03 71.46 70.28
5,541.925 07/07/03 71.56 70.38
5,541.885 08/04/03 71.60 70.42
5,541.825 09/11/03 71.66 70.48
5,541.885 10/02/03 71.60 70.42
5,541.995 11107/03 71.49 70.31
5,542.005 12/03/03 71.48 70.30
5,542.555 01115/04 70.93 69.75
5,542.705 02/10/04 70.78 69.60
5,543.225 03/28/04 70.26 69.08
5,543.555 04/12/04 69.93 68.75
5,543.865 05/13/04 69.62 68.44
5,543.915 06/18/04 69.57 68.39
5,544.655 07/28/04 68.83 67.65
5,544.795 08/30/04 68.69 67.51
5,544.845 09/16/04 68.64 67.46
5,544.705 10/11/04 68.78 67.60
5,544.525 11/16/04 68.96 67.78
5,544.625 12/22/04 68.86 67.68
5,544.305 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 1.184 114.5
5,549.305 10114/08 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 09110109 63.79 62.61
5,549.865 12/11109 63.62 62.44
5,545.60 03111/10 67.89 66.71
5,530.88 05/11110 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 06/21111 69.76 68.58
5,540.48 09/20111 73.01 71.83
5,544.36 12/21111 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 03/28113 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 12/20113 70.16 68.98
5,544.11 03/27/14 69.38 68.20
5,543.61 06/25/14 69 .88 68.70
5,543.67 09/25/14 69.82 68.64
5,543.69 12/17/14 69.80 68.62
5,541.49 03/26/15 72.00 70.82
5,539.67 06/22/15 73.82 72.64
5,541.35 09/30/15 72.14 70.96
5,541.63 12/02/15 71.86 70.68
5,540.38 03/30/16 73.11 71.93
5,539.46 06/30/16 74.03 72.85
5,540.39 09/29/16 73.10 71.92
---0 8
Depth Below Measuring Point (ft.)
\0 0 00 0 -...! 0 0'1 0
VI
0
I • J .. ! • ~ I I I ~ 8§~5g~gg
12/11/00
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
12116/03
03/25/04
07/03/04
10/11104
01119/05
04/29/05
08/07/05
11115/05
02/23/06
06/03/06
09/11106
12/20/06
03/30/07
07/08/07
10116/07
01124/08
05/03/08
08111108
11/19/08
02/27/09
06/07/09
09/15/09
12/24/09
-04/03/10
07/12/10
10/20/10
01128/11
05/08111
08/16/11
11124/11
03/03/12
06111112
09119112
-12/28/12
-04/07/13
07/16/13
-10/24113
02/01114
05/12/14
08/20/14
11128114
03/08/15
06/16115
09/24/15
01102116
-04111/16
07/20116
10/28/16
02/05117
05116117 .__ __ _____. ___ __._ ___ -L------'------'-----'-08/24117
1-3 ~ I ,&;;;..
~ ;-
"1
~ t'D "'C ;.
0 < t'D "1
1-3 ..... 9 t'D --~
C"'
§"
"'C '-"
Water Levels and Data over Time
White Mesa Mill -Well TW 4-5
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(z) (LSD) (MP) Riser (L) Monitorin~ (blw.MP) (blw.LSD) Well
5,638.75 5,640.70 1.95 121.75
5,579.30 01/02/00 61.40 59.45
5,579.60 01110/00 61.10 59.15
5,579.35 01/17/00 61.35 59.40
5,579.60 01124/00 61.10 59.15
5,579.50 02/01100 61.20 59.25
5,579.50 02/07/00 61.20 59.25
5,579.90 02114/00 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 05101100 60.20 58.25
5,580.90 05/11/00 59.80 57.85
5,580.50 05115/00 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 07113/00 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 08/31100 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 07110/01 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 01103/02 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 02/12/03 55.05 53.10
5,585.92 03/26/03 54.78 52.83
5,586.22 04/02/03 54.48 52.53
5,586.01 05/01/03 54.69 52.74
5,584.81 06/09/03 55.89 53.94
5,584.34 07/07/03 56.36 54.41
5,584.40 08/04/03 56.30 54.35
5,583.88 09/11/03 56.82 54.87
5,583.57 10/02/03 57.13 55.18
5,583.39 11/07/03 57.31 55.36
5,583.97 12/03/03 56.73 54.78
5,585.28 01/15/04 55.42 53.47
5,585.50 02/10/04 55.20 53.25
5,585.87 03/28/04 54.83 52.88
5,586.20 04/12/04 54.50 52.55
5,586.45 05/13/04 54.25 52.30
5,586.50 06/18/04 54.20 52.25
5,587.13 07/28/04 53.57 51.62
5,586.22 08/30/04 54.48 52.53
5,585.69 09116/04 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 03/15/05 55.55 53.60
5,586.25 04/26/05 54.45 52.50
5,586.79 05/24/05 53.91 51.96
5,586.52 06/30/05 54.18 52.23
5,586.03 07/29/05 54.67 52.72
5,586.05 09/12/05 54.65 52.70
5,585.80 12/07/05 54.90 52.95
5,587.06 03/08/06 53.64 51.69
5,585.90 06/13/06 54.80 52.85
5,585.32 07/18/06 55.38 53.43
5,585.35 11/07/06 55.35 53.40
5585.81 02/27/07 54.89 52.94
5,585.20 05/02/07 55.50 53.55
5,586.66 08/14/07 54.04 52.09
5,586.80 10/10/07 53.90 51.95
5,588.48 03126/08 52.22 50.27
5,586.51 06124/08 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 09110/09 56.34 54.39
5,585.02 12111109 55.68 53.73
5,585.66 03111110 55.04 53.09
5,584.86 05111110 55.84 53 .89
5,584.55 09/29/10 56.15 54.20
5,584.17 12121110 56.53 54.58
5,583.55 02/28/11 57.15 55.20
5,584.72 06/21111 55 .98 54.03
5,584.62 09/20/11 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 09127112 56.81 54.86
5,583.89 12/28/12 56.81 54.86
5,582.88 03/28/13 57.82 55.87
5,582.05 06/27/13 58.65 56.70
5,581.35 09127113 59.35 57.40
5,580.52 12/20/13 60.18 58.23
5,579.44 03/27/14 61.26 59.31
5,578.11 06/25114 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.L D) Well
5,638.75 5,640.70 1.95 121.75
5,577.15 09/25/14 63.55 61.60
5,577.44 12117/14 63.26 61.31
5,577.37 03/26/15 63.33 61.38
5,577.46 06/22/15 63.24 61.29
5,576.92 09/30/15 63.78 61.83
5,576.33 12/02/15 64.37 62.42
5,576.30 03/30/16 64.40 62.45
5,575.72 06/30/16 64.98 63.03
5,575.12 09/29/16 65.58 63.63
0\ 00 0\ 0\ 0\ .j::.
Depth Below Measuring Point (ft.)
0\ IV 0\ 0 Ul
00
Ul
0\
Ul .j::. Ul IV Ul 0
01102100
04/11100
07/20/00
10/28/00
02/05/01
05/16/01
08/24/01
12/02/01
03/12/02
06/20/02
09/28/02
01/06/03
04/16/03
07/25/03
11102/03
02/10/04
05/20/04
08/28/04 ~ 12/06/04
03/16/05 ~ 06/24/05 .,.
10/02/05 I !JI 01/10/06 ~ -04/20/06
07/29/06
11/06/06 ~ ~
02114/07 "1
05/25/07 ~
09/02/07 ~
12/11107 "C "* 03/20/08 ::r
06/28/08 0 10/06/08 < 01/14/09 ~
-04/24/09 "1
08/02/09 ~ """. 11/10/09 a 02/18110 ~
05/29110 _....
09/06/10 ~ 12115/10 r::f' 03/25111 -07/03111 a 10/11/11 "C
01/19112 '-'
04/28112
08/06112
-11/14112
-02/22113
-06/02113
09/10/13
-12/19/13
03/29114
-07/07114
10115114
01123115
-05/03115
08/11115
11/19/15
02/27116
06/06/16
09114/16
12/23/16
-04/02/17
07/11117
10/19117
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 07/13/00 86.65 85.20
5,522.17 07118/00 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 08/31100 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 05/31/01 85.89 84.44
5,522.88 06/20/01 85.90 84.45
5,522.96 07110/01 85.82 84.37
5,523.10 08/20/01 85.68 84.23
5,523.23 09/19/01 85.55 84.10
5,523.21 10/02/01 85.57 84.12
5,523.25 11/08/01 85.53 84.08
5,523.46 12/03/01 85.32 83.87
5,523.36 01/03/02 85.42 83.97
5,523.50 02/06/02 85.28 83.83
5,523.94 03/26/02 84.84 83.39
5,523.75 04/09/02 85.03 83.58
5,524.23 05/23/02 84.55 83.10
5,523.98 06/05/02 84.80 83.35
5,524.31 07/08/02 84.47 83 .02
5,524.36 08/23/02 84.42 82.97
5,524.49 09/11/02 84.29 82.84
5,524.71 10/23/02 84.07 82.62
5,524.60 11/22/02 84.18 82.73
5,524.94 12/03/02 83.84 82.39
5,525.10 01/09/03 83.68 82.23
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) Monitorin~ (blw.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 05/01103 83.04 81.59
5,525.98 06/09/03 82.80 81.35
5,526.04 07/07/03 82.74 81.29
5,526.07 08/04/03 82.71 81.26
5,526.42 09/11103 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 01115/04 81.95 80.50
5,526.81 02/10/04 81.97 80.52
5,527.14 03/28/04 81.64 80.19
5,527.39 04/12/04 81.39 79.94
5,527.64 05113/04 81.14 79.69
5,527.70 06/18/04 81.08 79.63
5,528.16 07/28/04 80.62 79.17
5,528.30 08/30/04 80.48 79.03
5,528.52 09/16/04 80.26 78.81
5,528.71 10111104 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 03115/05 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 09112/05 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 07118/06 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 05/02107 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 Elevation Length Of Date Of Water Water Well
(z) MP) Riser (L) Monitoring (blw.MP) (blw.L D) (blw.LSD
5,608.78 1.450 98.55
5,535.87 10/14/08 72.91 71.46
5,536.42 03110/09 72.36 70.91
5,536.71 06/24/09 72.07 70.62
5,536.83 09/10/09 71.95 70.50
5,537.35 12111/09 71.43 69.98
5,537.93 03/11/10 70.85 69.40
5,538.14 05111110 70.64 69.19
5,538.03 09/29/10 70.75 69.30
5,538.04 12/21/lO 70.74 69.29
5,537.98 02/28/11 70.8 69.35
5,538.46 06121111 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 03/27/12 70.05 68.60
5,538.80 06/28/12 69.98 68.53
5,539.04 09/27/12 69.74 68.29
5,538.74 12/28/12 70.04 68.59
5,539.53 03/28/13 69.25 67.80
5,539.46 06/27/13 69.32 67.87
5,539.62 09/27/13 69.16 67.71
5,539.85 12/20/13 68.93 67.48
5,539.65 03/27/14 69.13 67.68
5,538.85 06/25/14 69.93 68.48
5,538.69 09/25114 70.09 68.64
5,538.71 12/17/14 70.07 68.62
5,538.03 03/26115 70.75 69.30
5,537.78 06/22/15 71.00 69.55
5,537.40 09/30/15 71.38 69.93
5,537.44 12/02/15 71.34 69.89
5,536.76 03/30116 72.02 70.57
5,536.08 06/30/16 72.70 71.25
5,535.54 09/29/16 73.24 71.79
\0 0 00 v. 00 0
Depth Below Measuring Point (ft.)
-..J v. -..J 0 0\ v. 0\ 0 v. v. v. 0
05/25/00
09/02/00
12/11/00
03/21/01
06/29/01
10/07/01
01/15/02
04/25/02
08/03/02
11/11/02
02/19/03
05/30/03
09/07/03
12/16/03
03/25/04
07/03/04
10/11/04
01/19/05 ~ 04/29/05 ~ 08/07/05 """ 11/15/05 I
02/23/06 ~
06/03/06 ~ 09/11/06
12/20/06 ~ ~
03/30/07 "'1
07/08/07 ~
10/16/07 ~
01/24/08 "CS ~
05/03/08 ::r
08/11/08 0 11/19/08 ~
02/27/09 ~ "'1 06/07/09 ~ 09/15/09 ....
-12/24/09 a -04/03/10 ~
07/12/10 ----10/20/10 ~
01/28/11 r::r
05/08111 a 08/16111
11/24/11 "CS '-' 03/03/12
06/11/12
09/19112
12/28112
04/07113
07/16/13
10/24/13
02/01114
05/12/14
08/20114
11/28114
03/08115
06/16115
09/24/15
01/02/16
04/11116
07/20116
10/28116
02/05/17
05/16/17
08/24/17
Water Levels and Data over Time
White Mesa Mill-Well TW4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
5,552.37 11129/99 68.70 67.50
5,553.57 01102/00 67.50 66.30
5,553.87 01110/00 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 02/01/00 67.20 66.00
5,553.87 02/07/00 67.20 66.00
5,554.17 02/14/00 66.90 65.70
5,554.27 02/23/00 66.80 65.60
5,554.37 03/01/00 66.70 65.50
5,554.37 03/08/00 66.70 65.50
5,554.27 03/15/00 66.80 65.60
5,554.77 03/20/00 66.30 65.10
5,554.57 03/29/00 66.50 65.30
5,554.27 04/04/00 66.80 65.60
5,554.57 04113/00 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 05/01/00 66.20 65.00
5,555.27 05111100 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 07118/00 65 .62 64.42
5,555.59 07/27/00 65.48 64.28
5,555.65 08/02/00 65.42 64.22
5,555.70 08/09/00 65.37 64.17
5,555.74 08/16/00 65.33 64.13
5,555.96 08/31/00 65.11 63 .91
5,555.87 09/08/00 65.20 64.00
5,555.95 09/13/00 65.12 63.92
5,556.05 09/20/00 65.02 63.82
5,556.06 10/05/00 65.01 63.81
5,556.17 10/12/00 64.90 63.70
5,556.20 10/19/00 64.87 63.67
5,556.22 10/23/00 64.85 63.65
5,556.36 11/09/00 64.71 63.51
5,556.42 11114/00 64.65 63.45
5,556.45 11/30/00 64.62 63.42
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
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 07/10/01 63.09 61.89
5,558.33 08/20/01 62.74 61.54
5,558.57 09/19/01 62.50 61.30
5,558.53 10/02/01 62.54 61.34
5,558.62 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 09111103 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 01/15/04 63.90 62.70
5,558.65 02/10/04 62.42 61.22
5,559.90 03/28/04 61.17 59.97
5,560.36 04112/04 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 Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5,619.87 5,621.07 1.20 119.8
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 01118/05 74.56 73.36
5,546.66 02/28/05 74.41 73.21
5,546.81 03/15/05 74.26 73.06
5,548.19 04/26/05 72.88 71.68
5,547.11 05/24/05 73.96 72.76
5,546.98 06/30/05 74.09 72.89
5,546.92 07/29/05 74.15 72.95
5,547.26 09/12/05 73.81 72.61
5,547.26 12/07/05 73.81 72.61
5,548.86 03/08/06 72.21 71.01
5,548.62 06/13/06 72.45 71.25
5,550.04 07/18/06 71.03 69.83
5,548.32 11/07/06 72.75 71.55
5,550.44 02/27/07 70.63 69.43
5,549.69 05/02/07 71.38 70.18
5,549.97 08/14/07 71.10 69.90
5,550.30 10/10/07 70.77 69.57
5,551.92 03/26/08 69.15 67.95
5,552.94 06/24/08 68.13 66.93
5,552.34 08/26/08 68.73 67.53
5,552.61 10/14/08 68.46 67.26
5,552.81 03/10/09 68.26 67.06
5,553.11 06/24/09 67.96 66.76
5,552.55 09110109 68.52 67.32
5,553.06 12/11/09 68.01 66.81
5,554.64 03/11/10 66.43 65.23
5,554.20 05/11110 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 03/27112 67.90 66.70
5,553.21 06/28/12 67.86 66.66
5,552.90 09/27/12 68.17 66.97
5,553.15 12/28/12 67.92 66.72
Water Levels and Data over Time
White Mesa Mill -Well TW 4-7
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water Water Of Well
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) (blw.LSD)
5.619.87 5,621.07 1.20 119.8
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 09/25114 68.11 66.91
5,552.62 12117/14 68.45 67.25
5,548.57 03/26/15 72.50 71.30
5,555.88 06/22/15 65.19 63.99
5,546.22 09/30/15 74.85 73.65
5,539.47 12/02/15 81.60 80.40
5,545.08 03/30/16 75.99 74.79
5,544.62 06/30/16 76.45 75.25
5,544.61 09/29/16 76.46 75.26
00 Ul 00 0
Depth Below Measuring Point (ft.)
-...J Ul -...J 0 01 Ul ~ Ul Ul Ul 0
1-----+----1-------l____.~-+----1-----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
05/17/02
-08/25/02
12/03/02
03113/03
06/21/03
09/29/03
01107/04
04/16/04
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
04/21107
07/30/07
11107/07
02115/08
05/25/08
09/02/08
12/11/08
03/21/09
06/29/09
10/07/09
01115110
04/25110
08/03/10
11111/10
02/19111
05/30111
09/07111
12116/11
03/25112
07/03112
10111112
-01/19113
04/29/13
08/07/13
-11115113
02/23114
-06/03/14
09/11114
12/20/14
03/30/15
07/08/15
10116115
Ol/24/16
05/03/16
08/11116
11/19/16
02/27117
06/07117
~-----1-..-----'-----l'----1...-----'-----'----'--09115117
1-3 ~ I -....I
~ ;-
1'1
~ ~ ~ ;.
0 ~ 1'1
1-3 ... e ~ --?
0"' -e ~ '-'
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
5,546.40 11/29/99 75.00 70.40
5,546.20 01102/00 75.20 70.60
5,546.50 01/10/00 74.90 70.30
5,546.30 01117/00 75.10 70.50
5,546.60 01/24/00 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 02/14/00 74.50 69.90
5,546.95 02/23/00 74.45 69.85
5,547.05 03/01/00 74.35 69.75
5,547.05 03/08/00 74.35 69.75
5,547.10 03115/00 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 04113/00 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 05/11100 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 06109100 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 07118/00 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 08115/00 73.24 68 .64
5,548.40 08/31/00 73.00 68.40
5,548.50 09/08/00 72.90 68 .30
5,548.62 09/13/00 72.78 68.18
5,548.75 09120100 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 01/03/01 71.93 67.33
5,549.89 02/09/01 71 .51 66.91
5,550.37 03/27/01 71.03 66.43
5,550.50 04/30/01 70.90 66.30
Water Levels and Data over Time
White Mesa Mill -Well 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 11/08/01 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 11/22/02 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 02/12/03 66.98 62.38
5,554.71 03/26/03 66.69 62.09
5,554.83 04/02/03 66.57 61.97
5,552.21 05/01/03 69.19 64.59
5,547.93 06/09/03 73.47 68.87
5,546.97 07/07/03 74.43 69.83
5,546.58 08/04/03 74.82 70.22
5,546.24 09/11103 75.16 70.56
5,546.38 10/02/03 75.02 70.42
5,546.40 11/07/03 75.00 70.40
5,546.59 12/03/03 74.81 70.21
5,551.29 01115/04 70.11 65.51
5,552.69 02/10/04 68.71 64.11
5,554.06 03/28/04 67.34 62.74
5,554.52 04/12/04 66.88 62.28
5,555.06 05113/04 66.34 61.74
5,555.11 06/18/04 66.29 61.69
5,555.88 07/28/04 65.52 60.92
5,552.97 08/30/04 68.43 63.83
5,550.65 09/16/04 70.75 66.15
5,548.40 10/11/04 73.00 68.40
5,548.28 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 01/18/05 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 05124/05 72.55 67.95
5,548.73 06/30/05 72.67 68.07
5,548.62 07/29/05 72.78 68.18
5,548.80 09/12/05 72.60 68.00
5,548.71 12/07/05 72.69 68.09
5,549.72 03/08/06 71.68 67.08
5,549.70 06/13/06 71.70 67.10
5,549.70 07/18/06 71.70 67.10
5,549.65 11/07/06 71.75 67.15
5,551.11 02/27/07 70.29 65.69
5,550.20 05/02/07 71.20 66.60
5,550.59 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 10114/08 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 09110/09 68.28 63.68
5,553.63 12111/09 67.77 63.17
5,554.65 03111110 66.75 62.15
5,554.57 05/11/10 66.83 62.23
5,554.34 09/29/10 67.06 62.46
5,554.09 12/21/10 67.31 62.71
5,554.50 02/28/11 66.90 62.30
5,554.79 06121/11 66.61 62.01
5,554.63 09/20/11 66.77 62.17
5,555.01 12/21/11 66.39 61.79
5,554.85 03127112 66.55 61.95
5,554.90 06128112 66.50 61.90
5,554.85 09/27/12 66.55 61.95
5,554.86 12/28/12 66.54 61.94
5,556.48 03/28/13 64.92 60.32
5,556.35 06127/13 65.05 60.45
5,556.60 09/27113 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 09/30115 76.56 71.96
5,540.22 12/02115 81.18 76.58
5,542.00 03/30/16 79.40 74.80
5,542.10 06/30/16 79.30 74.70
5,541.70 09/29/16 79.70 75.10
"' 0 00 0 -..1 0
\
J
Depth Below Measuring Point (ft.)
0\ 0 VI 0 ~ 0 w 0
c [:\ ~ ....
~
~ ~
~
~ ~
~
Li l5 ~ ,
N 0 -0 0
-
-
-
-
-
.
.
--
-
-
11/29/99
03/08/00
06/16/00
09/24/00
01102/01
04112/01
07/21101
10/29/01
02/06/02
05/17/02
08/25/02
12/03/02
03/13/03
06/21103
09/29/03
01107/04
04/16/04
07/25/04
11102/04
02/10/05
05/21105
08/29/05
12/07/05
03/17/06
06/25/06
10/03/06
01111107
04/21107
07/30/07
11/07/07
02/15/08
05/25/08
09/02/08
12/11/08
03/21109
06/29/09
10/07/09
01115110
04/25/10
08/03110
11111110
02/19111
05/30111
09/07/11
12116/11
03/25112
07/03112
10/11112
01119113
04/29/13
08/07/13
11/15113
02/23114
06/03114
09/11114
12/20114
03/30115
07/08/15
10/16115
01/24116
05/03116
08/11116
11/19116
02/27/17
06/07/17
09/15117
~ ~ ~ I QC
~ ~ ~ ""'l
~ ~ "C ;.
0 < ~ ""1
~ ....
9 ~ -..
i=?
~ a "C ..._,
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
5,577.09 12/20/99 60.50 59.02
5,577.09 01102/00 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 02/01100 60.30 58.82
5,577.19 02/07/00 60.40 58.92
5,577.69 02/14/00 59.90 58.42
5,577.69 02/23/00 59.90 58.42
5,577.79 03/01100 59.80 58.32
5,577.79 03/08/00 59.80 58.32
5,577.89 03115/00 59.70 58.22
5,568.49 03/20/00 69.10 67.62
5,578.14 03/29/00 59.45 57.97
5,577.84 04/04/00 59.75 58.27
5,578.04 04/13/00 59.55 58.07
5,578.24 04/21100 59.35 57.87
5,578.39 04/28/00 59.20 57.72
5,578.39 05/01100 59.20 57.72
5,578.79 05111100 58.80 57.32
5,578.39 05115/00 59.20 57.72
5,578.79 05/25/00 58.80 57.32
5,578.81 06/09/00 58.78 57.30
5,578.89 06/16/00 58.70 57.22
5,578.74 06/26/00 58.85 57.37
5,578.86 07/06/00 58.73 57.25
5,578.87 07/13/00 58.72 57.24
5,578.84 07/18/00 58.75 57.27
5,579.03 07/27/00 58.56 57.08
5,579.03 08/02/00 58.56 57.08
5,579.05 08/09/00 58.54 57.06
5,579.04 08/15/00 58.55 57.07
5,579.25 08/31100 58.34 56.86
5,579.35 09/08/00 58.24 56.76
5,579.40 09113/00 58.19 56.71
5,579.46 09/20/00 58.13 56.65
5,579.44 10/05/00 58.15 56.67
5,579.79 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 11108/01 55.76 54.28
5,582.17 12/03/01 55.42 53.94
5,582.21 01/03/02 55.38 53.90
5,582.57 02/06/02 55.02 53.54
5,583.12 03/26/02 54.47 52.99
5,582.77 04/09/02 54.82 53.34
5,583.21 05/23/02 54.38 52.90
5,582.94 06/05/02 54.65 53.17
5,582.71 07/08/02 54.88 53.40
5,583.67 08/23/02 53.92 52.44
5,583.82 09/11102 53.77 52.29
5,584.01 10/23/02 53.58 52.10
5,583.88 11/22/02 53.71 52.23
5,583.81 12/03/02 53.78 52.30
5,584.28 01/09/03 53.31 51.83
5,584.41 02/12/03 53.18 51.70
5,584.68 03/26/03 52.91 51.43
5,584.49 04/02/03 53.10 51.62
5,584.51 05/01/03 53.08 51.60
5,583.59 06/09/03 54.00 52.52
5,582.96 07/07/03 54.63 53.15
5,582.98 08/04/03 54.61 53.13
5,582.57 09111103 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 10111104 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 01118/05 54.25 52.77
5,583.66 02/28/05 53.93 52.45
5,583.87 03115/05 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 07118/06 53.33 51 .85
5,584.21 11/07/06 53.38 51.90
5,584.67 02/27/07 52.92 51.44
5,584.06 05/02/07 53.53 52.05
5,585.33 08114/07 52.26 50.78
5,585.42 10/10/07 52.17 50.69
5,587.01 03/26/08 50.58 49.10
5,585.44 06/24/08 52.15 50.67
5,585.23 08/26/08 52.36 50.88
5,584.42 10/14/08 53.17 51.69
5,583.59 03/03/09 54.00 52.52
5,583.35 06/24/09 54.24 52.76
5,582.91 09110109 54.68 53.20
5,583.43 12/11109 54.16 52.68
5,584.00 03111/10 53.59 52.11
5,583.27 05/ll/10 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 02/28/11 54.96 53.48
5,583.62 06/21/11 53.97 52.49
5,583.52 09/20/11 54.07 52.59
5,583.91 12/21/11 53.68 52.20
5,582.84 03/27112 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 12/20113 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 12117/14 61.15 59.67
5,576.35 03/26/15 61.24 59.76
5,576.48 06/22115 61.11 59.63
5,575.98 09/30/15 61.61 60.13
5,575.41 12/02/15 62.18 60.70
5,575.38 03/30116 62.21 60.73
5,574.74 06/30/16 62.85 61.37
5,574.26 09/29116 63.33 61.85
-....J 0 0\ 00 0\ 0\
Depth Below Measuring Point (ft.)
~ 0\ N 0\ 0 U1
00
U1
0\
U1 ~ U1 N U1 0
12/20/99
03/29/00
07/07/00
10/15/00
01/23/01
05/03/01
08/11/01
11/19/01
02/27/02
06/07/02
09/15/02
12/24/02
04/03/03
07/l2/03
10/20/03
01/28/04
05/07/04
08/15/04
11/23/04 1-3 03/03/05 ~ 06111/05 ~ 09/19/05 I
12/28/05 \0
04/07/06 ~ 07116/06
10/24/06 f""'" ~ 02/01107 Joo1
05/12/07 0 08/20/07 ~
11/28/07 't:S f""'" 03/07/08 =-06/15/08 0 09/23/08 < 01/01/09 ~
04/11/09 Joo1
07/20/09 1-3
10/28/09 .....
02/05/10 a
05116/IO ~ ,-....
08/24/10 ~ 12/02/10
03/12/1 1 C" -06/20/11 a 09/28/11 't:S 01/06/12 '-"
04/15/12
07/24112
11/01112
02/09/13
05/20/13
08/28/l3
12/06/13
03/16114
06/24/14
10/02/l4
01/10/l5
04/20/l5
07/29/l5
11106/15
02/14/l6
05/24/l6
09/01/l6
12/10/l6
03/20/17
06/28/l7
10/06/17
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 01/03/02 57.49 55.24
5,576.92 02/06/02 57.32 55.07
5,577.43 03/26/02 56.81 54.56
5,577.22 04/09/02 57.02 54.77
5,577.80 05/23/02 56.44 54.19
5,577.47 06/05/02 56.77 54.52
5,577.55 07/08/02 56.69 54.44
5,578.10 08/23/02 56.14 53.89
5,578.24 09/11/02 56.00 53.75
5,578.49 10/23/02 55.75 53.50
5,578.43 11/22/02 55.81 53.56
5,578.43 12/03/02 55.81 53.56
5,578.66 01/09/03 55.58 53.33
5,578.66 02/12/03 55.58 53.33
5,578.78 03/26/03 55.46 53.21
5,578.90 04/02/03 55.34 53.09
5,578.83 05/01103 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 09/11/03 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 05113/04 55.31 53.06
5,578.99 06/18/04 55.25 53.00
5,579.18 07/28/04 55.06 52.81
5,579.06 08/30/04 55.18 52.93
5,578.78 09/16/04 55.46 53.21
5,577.80 10/11104 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 03115/05 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 Ill
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 10110/07 55.20 52.95
5,580.69 03/26/08 53.55 51.30
5,579.87 06124/08 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 09110/09 56.75 54.50
5,577.98 12/11/09 56.26 54.01
5,578.38 03/11/10 55.86 53.61
5,578.16 05111/10 56.08 53.83
5,577.85 09/29/10 56.39 54.14
5,577.28 12121110 56.96 54.71
5,577.14 02/28/11 57.10 54.85
5,578.09 06/21/11 56.15 53.90
5,578.24 09/20/11 56.00 53.75
5,578.74 12/21/11 55.50 53.25
5,577.89 03/27112 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 12128/12 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 09/27/13 57.47 55.22
5,576.22 12/20/13 58.02 55.77
5,575.36 03127114 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 12117/14 61.05 58.80
5,573.12 03/26115 61.12 58.87
5,573.33 06/22115 60.91 58.66
5,572.98 09/30/15 61.26 59.01
5,572.39 12/02/15 61.85 59.60
5,572.64 03/30/16 61.60 59.35
Water Levels and Data over Time
White Mesa Mill -Well TW 4-10
Total or
Measuring Measured
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
5,571.79 06/30/16 62.45 60.20
5,571.27 09/29/16 62.97 60.72
0\ +>-0\ N
Depth Below Measuring Point (ft.)
0\ 0 Vl
00
Vl
0\
Vl +>-Vl N
' 01/03/02
04/13/02
07/22/02
10/30/02
02/07/03
-05/18/03
08/26/03
12/04/03
03/13/04
06/21/04
09/29/04
01/07/05
04/17/05
07/26/05
11/03/05
02/11/06
05/22/06
08/30/06
12/08/06
03/18/07
06/26/07
10/04/07
01112/08
04/21/08
07/30/08
11107/08
02/15/09
05/26/09
09/03/09
12112/09
03/22/10
06/30/10
10/08/10
-01116/11
04/26111
08/04/11
11/12111
02/20112
05/30112
09/07/12
12/16112
03/26/13
07/04/13
10/12/13
01120/14
-04/30/14
08/08/14
11/16/14
02/24/15
06/04/15
09/12115
12/21/15
03/30116
07/08/16
10/16/16
01/24/17
05/04117
.._ __ ___..J. ___ ___j_ ___ _..J.._ ___ ___.__ ___ ~----L 08/12/17
~ ~ I ~
Q
~ ;-
1'1
0 .g
~
0 < ~ 1'1
~ -· ~ --?
C" ~ ._,
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 11/22/02 74.04 72.34
5,549.62 12/03/02 74.00 72.30
5,549.85 01/09/03 73.77 72.07
5,549.91 02/12/03 73.71 72.01
5,550.15 03/26/03 73.47 71.77
5,550.01 04/02/03 73.61 71.91
5,550.31 05/01103 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 06118/04 71.68 69.98
5,552.49 07/28/04 71.13 69.43
5,552.74 08/30/04 70.88 69.18
5,553.01 09/16/04 70.61 68.91
5,553.11 10/11104 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 01118/05 70.31 68.61
5,553.84 02/28/05 69.78 68.08
5,554.04 03115/05 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) Monitorin~ (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 100
5,553.86 09112/05 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 07118/06 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 09110109 59.30 57.60
5,564.70 12/11/09 58.92 57.22
5,565.14 03111110 58 .48 56.78
5,565.61 05/11110 58.01 56.31
5,565.67 09/29/10 57.95 56.25
5,565.62 12/21110 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 09/20111 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 06/28112 57.80 56.10
5,566.66 09/27112 56.96 55.26
5,565.77 12/28/12 57.85 56.15
5,566.89 03/28113 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 03/27/14 58.59 56.89
5,564.18 06/25/14 59.44 57.74
5,563.52 09/25/14 60.10 58.40
5,563.37 12/17/14 60.25 58.55
5,532.62 03/26/15 91.00 89.30
5,527.07 06/22/15 96.55 94.85
5,533.27 09/30/15 90.35 88.65
5,532.67 12/02/15 90.95 89.25
5,531.44 03/30/16 92.18 90.48
Water Levels and Data over Time
White Mesa Mill-Well TW4-11
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,621.92 5,623.62 1.70 100
5,529.85 06/30/16 93.77 92.07
5,530.64 09/29/16 92.98 91.28
-0 0 \0 Vl \0 0
Depth Below Measuring Point (ft.)
00 Vl 00 0 -.l Vl ....... 0 0\ Vl 0\ 0 Vl Vl
Vl
0
-
-
01103/02
04/13/02
07/22/02
10/30/02
02/07/03
05/18/03
08/26/03
12/04/03
03/13/04
06/21104
09/29/04
01107/05
04/17/05
07/26/05
11103/05
02111106 1-3 05/22/06 ~ 08/30/06 .&;:..
12/08/06 I ...... 03/18/07 ......
06/26/07 ~ 10/04/07
01112/08 -~
04/21108 "'1
07/30/08 0
11107/08 ~ ~ 02115/09 -05/26/09 =-
09/03/09 0
12112/09 -< ~
03/22/10 "'1
06/30/10 1-3 ....
10/08/10 a
01/16/11 ~
04/26111 ---08/04111 ~
11/12/11 0" -02/20112 a 05/30112 ~
09/07/12
,_,
12116/12
03/26/13
07/04/13
10112/13
01/20/14
04/30/14
08/08114
11116/14
02/24/15
06/04115
09112/15
12/21/15
03/30/16
07/08/16
10/16116
01/24117
05/04/17
08/12/17
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 09/11/02 42.69 40.84
5,581.33 10/23/02 42.90 41.05
5,581.47 11/22/02 42.76 40.91
5,581.55 12/03/02 42.68 40.83
5,582.58 01/09/03 41.65 39.80
5,582.47 02/12/03 41.76 39.91
5,582.71 03/26/03 41.52 39.67
5,582.11 04/02/03 42.12 40.27
5,582.92 05/01/03 41.31 39.46
5,583.13 06/09/03 41.10 39.25
5,583.21 07/07/03 41.02 39.17
5,583.31 08/04/03 40.92 39.07
5,583.55 09/11/03 40.68 38.83
5,583.72 10/02/03 40.51 38.66
5,583.77 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 10/11/04 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 09112/05 36.29 34.44
5,588.43 12/07/05 35.80 33.95
5,588.92 03/08/06 35.31 33.46
5,588.34 06/13/06 35.89 34.04
5,588.33 07/18/06 35.90 34.05
5,584.70 11/07/06 39.53 37.68
5588.85 02/27/07 35.38 33.53
Water Levels and Data over Time
White Mesa Mill -Well TW 4-12
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,622.38 5,624.23 1.85 101.5
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 12/11109 38.46 36.61
5,585.88 03/11110 38.35 36.50
5,586.35 05111110 37.88 36.03
5,585.68 09/29/10 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 09/20111 39.91 38.06
5,584.22 12/21/11 40.01 38.16
5,577.07 03/27/12 47.16 45.31
5,577.05 06/28/12 47.18 45.33
5,583.14 09/27/12 41.09 39.24
5,577.10 12/28112 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 12117114 43.90 42.05
5,579.28 03/26/15 44.95 43.10
5,579.23 06/22/15 45.00 43.15
5,578.87 09/30/15 45.36 43.51
5,578.53 12/02/15 45.70 43.85
5,578.53 03/30/16 45.70 43.85
5,578.03 06/30/16 46.20 44.35
5,577.54 09/29/16 46.69 44.84
.j::>.
00
.j::>.
0\
Depth Below Measuring Point (ft.)
t .j::>. N .j::>.
0
w 00 w
0\
w .j::>.
1----+----+--+-,....-!---+----+-----+---+08/23/02
12/01/02
03/11/03
06119/03
09/27/03
01/05/04
04/14/04
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
01/09/07
04119/07
07/28/07
11/05/07
02/13/08
05/23/08
08/31/08
12/09/08
03119/09
06/27/09
10/05/09
01/13110
04/23/10
08/01/10
11/09110
02117111
05/28111
09/05111
-12/14/11
03/23/12
07/01112
10/09112
01/17113
04/27113
08/05/13
11/13113
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
11/17116
02/25117
06/05117
..___ __ __i_ __ ---l,... __ ____;L....._ __ ....L...-__ ---l,... ___ L....._ __ ....._09/13117
~ ~ ~ I ~ N
~ ;'
""1
~ ~ "'0 ~
0 -< ~ ""1
~ .... e ~ ,-...
~
0"' §"
"'0 '-"'
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 05/01/03 88.40 86.55
5,538.46 06/09/03 81.48 79.63
5,539.38 07/07/03 80.56 78.71
5,540.72 08/04/03 79.22 77.37
5,541.25 09/11103 78.69 76.84
5,541.34 10/02/03 78.60 76.75
5,541.69 11/07/03 78.25 76.40
5,541.91 12/03/03 78.03 76.18
5,542.44 01/15/04 77.50 75.65
5,542.47 02110/04 77.47 75.62
5,542.84 03128/04 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 10/11104 73.74 71.89
5,547.43 11116/04 72.51 70.66
5,548.96 12/22/04 70.98 69.13
5,549.02 01/18/05 70.92 69.07
5,550.66 02/28/05 69.28 67.43
5,551.26 03/15/05 68.68 66.83
5,552.23 04/26/05 67.71 65.86
5,552.87 05/24/05 67.07 65.22
5,553.42 06/30/05 66.52 64.67
5,554.00 07/29/05 65.94 64.09
5,555.21 09/12/05 64.73 62.88
5,558.13 12/07/05 61.81 59.96
5,562.93 03/08/06 57.01 55.16
5,564.39 06/13/06 55.55 53.70
5,562.09 07/18/06 57.85 56.00
5,565.49 11/07/06 54.45 52.60
5571.08 02/27/07 48.86 47.01
Water Levels and Data over Time
White Mesa Mill -Well TW 4-13
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,618.09 5,619.94 1.85 102.5
5,570.63 05/02/07 49.31 47.46
5,565.24 08/14/07 54.70 52.85
5,565.83 10110/07 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 03111110 47.93 46.08
5,572.88 05/11110 47.06 45.21
5,573.17 09/29/10 46.77 44.92
5,573.14 12/21110 46.80 44.95
5,573.10 02/28/11 46.84 44.99
5,573.75 06/21111 46.19 44.34
5,573.63 09/20/11 46.31 44.46
5,573.94 12/21111 46.00 44.15
5,572.79 03/27112 47 .15 45.30
5,572.77 06/28/12 47.17 45.32
5,573.04 09/27/12 46.90 45.05
5,572.79 12/28/12 47.15 45.30
5,573.03 03/28/13 46.91 45.06
5,572.44 06/27/13 47.50 45.65
5,573.46 09/27/13 46.48 44.63
5,573.46 12/20113 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 06/22115 50.78 48.93
5,568.66 09/30115 51.28 49.43
5,568.02 12/02/15 51.92 50.07
5,568.39 03/30/16 51.55 49.70
5,567.49 06/30/16 52.45 50.60
5,566.99 09/29116 52.95 51.10
~
8 \0 0
Depth Below Measuring Point (ft.)
00 0 -..1 0 0\ 0 VI
0
.j:>. 0
1-----...-----1-----1-----+-----+----f-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
03115/06
06/23/06
10/01106
01109/07
04/19/07
07/28/07
11105/07
02/13/08
05/23/08
08/31/08
12/09/08
03119/09
06/27/09
10/05/09
01113/10
04/23110
08/01110
11109/10
02117/11
05/28/11
09/05/11
12114/11
03/23/12
07/01/12
10/09/12
01117/13
04/27/13
08/05113
11113/13
02/21114
06/01114
09/09114
12118/14
03/28115
07/06115
10/14115
01/22/16
05/01116
08/09116
11117/16
02/25117
06/05117
' 09/13/17
1-3 ~ I ,....
~
~ -(tl
Jo'1
~ (tl
"0 ~
0 ~ Jo'1
1-3 .... ~ --~
0"' a "0 ._.,
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 11/22/02 92.45 90.60
5,520.42 12/03/02 92.35 90.50
5,520.70 01/09/03 92.07 90.22
5,520.89 02/12/03 91.88 90.03
5,521.12 03/26/03 91.65 89 .80
5,521.12 04/02/03 91.65 89 .80
5,521.24 05/01/03 91.53 89 .68
5,521.34 06/09/03 91.43 89.58
5,521.36 07/07/03 91.41 89.56
5,521.35 08/04/03 91.42 89.57
5,521.30 09/11/03 91.47 89.62
5,521.35 10/02/03 91.42 89.57
5,521.36 11/07/03 91.41 89.56
5,521.16 12/03/03 91.61 89.76
5,521.29 01/15/04 91.48 89.63
5,521.36 02110/04 91.41 89.56
5,521.46 03/28/04 91.31 89.46
5,521.54 04/12/04 91.23 89.38
5,521.59 05/13/04 91.18 89.33
5,521.69 06/18/04 91.08 89.23
5,521.71 07/28/04 91.06 89.21
5,521.76 08/30/04 91.01 89.16
5,521.77 09/16/04 91.00 89.15
5,521.79 10/11/04 90.98 89.13
5,521.80 11/16/04 90.97 89.12
5,521.82 12/22/04 90.95 89.10
5,521.82 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 11/07/06 92.60 90.75
5522.24 02/27/07 90.53 88.68
Water Levels and Data over Time
White Mesa Mill-Well TW4-14
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,610.92 5,612.77 1.85 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 12/11109 89.23 87.38
5,522.98 03/11110 89.79 87.94
5,524.01 05111110 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 02/28111 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 06/28112 86.80 84.95
5,526.32 09/27/12 86.45 84.60
5,525.88 12/28/12 86.89 85.04
5,526.91 03/28113 85.86 84.01
5,526.99 06/27/13 85.78 83.93
5,527.68 09/27/13 85.09 83.24
5,528.19 12/20/13 84.58 82.73
5,528.75 03/27/14 84 .02 82.17
5,529.21 06/25/14 83.56 81.71
5,529.78 09/25114 82.99 81.14
5,530.41 12117114 82.36 80.51
5,530.86 03/26115 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 12/02115 80.65 78.80
5,533.12 03/30116 79.65 77.80
5,533.13 06/30/16 79.64 77.79
5,533.24 09/29/16 79.53 77.68
\0 0\ ':f \0 N
Depth Below Measuring Point (ft.)
\0 0 00 00 00 0\ 00 ~ 00 N 00 0
-..,J
00
08/23/02
12/01102
03/11/03
06/19/03
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 ~
01109/07 ~
04119/07 ~ I
07/28/07 ~
11105/07 ~
02/13/08 ~ 05/23/08 """ 08/31108 ~ "1
12/09/08 '=' 03/19/09 ~
06/27/09 ~ """ 10/05/09 =-
01113/10 0
04/23/10 < ~
08/01110 "1
11109/10 ~ .....
02117/11 s
05/28/11 ~
09/05111 --~ 12114/11 .
03/23/12 f;1" -07/01/12 s
10/09/12 ~ '-"
01117/13
04/27113
08/05/13
11113/13
~ 02/21/14
06/01/14
09/09/14
12/18/14
03/28/15
07/06/15
10/14/15
01/22/16
-05/01/16
-08/09/16
-11/17/16
02/25117
06/05/17
09/13117
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 09111102 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 01109/03 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 09/11103 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 01/15/04 54.56 53.26
5,572.55 02/10/04 52.90 51.60
5,574.25 03/28/04 51.20 49.90
5,574.77 04/12/04 50.68 49.38
5,575.53 05/13/04 49.92 48.62
5,575.59 06118/04 49.86 48.56
5,576.82 07/28/04 48.63 47.33
5,527.47 09/16/04 97.98 96.68
5,553.97 11/16/04 71.48 70.18
5,562.33 12/22/04 63.12 61.82
5,550.00 01118/05 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 10114/08 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 09110109 80.84 79.54
5,549.33 12/11/09 76.12 74.82
5,543.78 03111110 81.67 80.37
5,545.61 05/11110 79.84 78.54
5,547.43 09/29110 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 06/21/11 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 03/27112 68.15 66.85
5,557.38 06/28112 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 03/28113 60.08 58.78
5,563.55 06/27/13 61.90 60.60
5,560.12 09/27113 65.33 64.03
5,559.27 12/20/13 66.18 64.88
5,556.65 03/27/14 68.80 67.50
5,552.23 06/25/14 73.22 71.92
5,554.05 09/25/14 71.40 70.10
5,550.65 12/17/14 74.80 73.50
5,557.55 03/26/15 67.90 66.60
5,558.51 06/22/15 66.94 65.64
5,560.81 09/30/15 64.64 63.34
5,560.25 12/02/15 65.20 63.90
5,561.07 03/30/16 64.38 63 .08
5,560.51 06/30116 64.94 63.64
5,557.99 09/29/16 67.46 66.16
......
0 0 \0 0
Depth Below Measuring Point (ft.)
00 0 -...l 0 ~ Ul 0
.j:::..
0
1-------+----+----t-----+--------1~------+ 08/23/02
12/01102
03/11103
06/19/03
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
03115/06
06/23/06
10/01106
01109/07
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
02/17/11
05/28111
09/05/11
12/14111
03/23/12
07/01112
-10/09/12
01117/13
~ 04/27113
08/05113
-11/13/13
02/21114
06/01114
09109114
12118/14
03/28/15
07/06115
10/14/15
01122/16
05/01/16
08/09/16
11117/16
02/25/17
06/05/17
L._ __ ___.~. ___ _.L ___ _.J.... ___ -~.... ___ ....J.._ ___ _.L 09/13/17
~ ~ N ~
~ ;-
"1
0 .g e-o < ~ "1
~ -· ~ ,-., ~
-a' s "0 '-'
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 09111102 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 05101103 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 09111103 62.29 60.46
5,561.04 10/02/03 62.98 61.15
5,560.39 11107/03 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 02110/04 62.27 60.44
5,562.98 03/28/04 61.04 59.21
5,563.29 04/12/04 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 10111104 62.23 60.40
5,560.38 11116/04 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 09112/05 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 06113/06 65.55 63.72
5,558.42 07/18/06 65.60 63.77
5,558.09 11107/06 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 10114/08 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 03111110 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 02/28/1 I 64.76 62.93
5,560.48 06/21111 63 .54 61.71
5,561.52 09/20111 62.50 60.67
5,562.95 12/21111 61.07 59.24
5,563.76 03/27112 60.26 58.43
5,563.90 06/28/12 60.12 58.29
5,564.65 09/27112 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 06/27113 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 06/25114 64.49 62.66
5,558.36 09/25/14 65.66 63.83
5,558.00 12/17114 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
5,559.95 06/30/16 64.07 62.24
5,559.72 09/29116 64.30 62.47
00 0
-.)
VI
Depth Below Measuring Point (ft.)
-.)
0 0\ VI 0\ 0 VI VI VI 0
1------+----+----!---...... ..+------+-----l--08/23/02
12/01102
03111103
06119/03
-09/27/03
01105/04
04114/04
07/23/04
10/31104
02/08/05
05/19/05
08/27/05
12/05/05
03/15/06
06/23/06
10/01/06
01/09/07
04119/07
07/28/07
11105/07
02113/08
05/23/08
08/31108
12/09/08
-03119/09
06/27/09
10/05/09
01113/10
04/23110
08/01110
11109/10
02/17/11
05/28111
09/05/11
12114/11
03/23112
07/01112
10/09/12
01117/13
04/27113
08/05113
11/13/13
02/21/14
06/01114
09/09114
12/18/14
03/28115
07/06115
10114/15
01122/16
05/01116
08/09116
11117/16
02/25117
06/05117
L-------L-----'------'--------L-----'----....1.. 09/13117
1-3 ~ I
~
0\
~ ;-
""'l
0 ~ ~ ~
0 < ~ ""'l
1-3 .... ~ -~
C"" §"
~ ._.,
Water Levels and Data over Time
White Mesa Mill -Well MW -32
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5,542.17 08/23/02 83.07 81.24
5,542.39 09/11/02 82.85 81.02
5,542.61 10/23/02 82.63 80.80
5,542.49 11/22/02 82.75 80.92
5,542.82 12/03/02 82.42 80.59
5,543.03 01/09/03 82.21 80.38
5,543.04 02/12/03 82.20 80.37
5,543.41 03/26/03 81.83 80.00
5,543.69 04/02/03 81.55 79.72
5,543.77 05/01/03 81.47 79.64
5,544.01 06/09/03 81.23 79.40
5,544.05 07/07/03 81.19 79.36
5,543.99 08/04/03 81.25 79.42
5,544.17 09/11/03 81.07 79.24
5,544.06 10/02/03 81.18 79.35
5,544.03 11/07/03 81.21 79.38
5,543.94 12/03/03 81.30 79.47
5,543.98 01/15/04 81.26 79.43
5,543.85 02/10/04 81.39 79.56
5,544.05 03/28/04 81.19 79.36
5,544.33 04/12/04 80.91 79.08
5,544.55 05/13/04 80.69 78.86
5,544.59 06/18/04 80.65 78.82
5,545.08 07/28/04 80.16 78.33
5,545.26 08/30/04 79.98 78.15
5,545.48 09/16/04 79.76 77.93
5,545.61 10/11104 79.63 77.80
5,545.46 11/16/04 79.78 77.95
5,545.66 12/22/04 79.58 77.75
5,545.33 01/18/05 79.91 78.08
5,545.51 02/28/05 79.73 77.90
5,545.57 03/15/05 79.67 77.84
5,545.46 04/26/05 79.78 77.95
5,545.45 05/24/05 79.79 77.96
5,545.33 06/30/05 79.91 78.08
5,545.16 07/29/05 80.08 78.25
5,545.54 09/12/05 79.70 77.87
5,545.77 12/07/05 79.47 77.64
5,546.09 03/08/06 79.15 77.32
5,545.94 06/13/06 79.30 77.47
5,545.94 07/18/06 79.30 77.47
5,546.24 11/07/06 79.00 77.17
5546.81 02/27/07 78.43 76.6
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) Monitorini; (blw.MP) (blw.LSD) Well
5,623.41 5,625.24 1.83 130.6
5546.56 05/02/07 78.68 76.85
5546.81 08/15/07 78.43 76.6
5546.96 10/10/07 78.28 76.45
5547.9 03/26/08 77.34 75.51
5548.08 06/25/08 77.16 75.33
5548.42 08/26/08 76.82 74.99
5548.05 10114/08 77.19 75.36
5548.29 03/03/09 76.95 75.12
5548.09 06/24/09 77.15 75.32
5547.79 09/10/09 77.45 75.62
5548.09 12/11/09 77.15 75.32
5,548.50 03/11110 76.74 74.91
5,548.89 05/11/10 76.35 74.52
5,548.83 09/29110 76.41 74.58
5,548.97 12/21/10 76.27 74.44
5,548.68 02/28/11 76.56 74.73
5,549.33 06/21/11 75.91 74.08
5,549.19 09/20/11 76.05 74.22
5,550.06 12/21111 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 03/28113 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 06/22115 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 03/30116 77.00 75.17
5,547.68 06/30/16 77.56 75.73
5,547.29 09/29116 77.95 76.12
Depth Below Measuring Point (ft.)
00 00 00 -.J -.J -.J -.J .j:>. N 0 00 0\ .j:>. N
08/23/02
12/01102
03111103
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
03115/06
06/23/06
10/01/06 ~ -01109/07 ~ 04/19/07
07/28/07 ~ N
11105/07 ~ 02/13/08
05/23/08 """ 08/31108 ('tl ....
12/09/08 ~ 03/19/09 ('tl
06/27/09 "'0 """ 10/05/09 =-
01113/10 0
04/23/10 -< ('tl
08/01110 ....
11109/10 ~ ....
02/17/11 9
05/28/11 ('tl
09/05/11 ,-.,
12/14/11 ~
03/23/12 -a' -07/01/12 9
10/09/12 "'0 '-'
01117/13
04/27/13
-08/05/13
11113/13
02/21114
06/01114
09/09/14
12/18/14
03/28/15
07/06/15
10/14/15
01/22/16
05/01116
08/09/16
11/17/16
02/25/17
06/05117
09/13117
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 11/22/02 55.88 53.73
5,585.68 12/03/02 55.60 53.45
5,585.90 01/09/03 55.38 53.23
5,590.79 02112/03 50.49 48.34
5,586.18 03/26/03 55.10 52.95
5,586.36 04/02/03 54.92 52.77
5,586.24 05/01/03 55.04 52.89
5,584.93 06/09/03 56.35 54.20
5,584.46 07/07/03 56.82 54.67
5,584.55 08/04/03 56.73 54.58
5,584.01 09/11/03 57.27 55.12
5,583.67 10/02/03 57.61 55.46
5,583.50 11107/03 57.78 55.63
5,584.08 12/03/03 57.20 55.05
5,585.45 01/15/04 55.83 53.68
5,585.66 02/10/04 55.62 53.47
5,586.13 03/28/04 55.15 53.00
5,586.39 04/12/04 54.89 52.74
5,586.66 05113/04 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 10111/04 56.06 53.91
5,584.70 11/16/04 56.58 54.43
5,584.81 12/22/04 56.47 54.32
5,584.68 01/18/05 56.60 54.45
5,585.02 02/28/05 56.26 54.11
5,585.25 03/15/05 56.03 53.88
5,586.31 04/26/05 54.97 52.82
5,586.97 05/24/05 54.31 52.16
5,586.58 06/30/05 54.70 52.55
5,586.10 07/29/05 55.18 53.03
5,586.05 09/12/05 55.23 53.08
5,585.86 12/07/05 55.42 53.27
5,587.13 03/08/06 54.15 52.00
5,585.93 06/13/06 55.35 53.20
5,585.40 07118/06 55.88 53.73
5,585.38 11107/06 55.90 53.75
5585.83 02/27/07 55.45 53.30
Water Levels and Data over Time
White Mesa Mill-Well TW4-18
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth or
(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 10114/08 56.07 53.92
5584.47 03/03/09 56.81 54.66
5584.35 06/24/09 56.93 54.78
5583.88 09110109 57.4 55.25
5584.43 12/11/09 56.85 54.70
5,585.26 03111110 56.02 53.87
5,584.17 05/11/10 57.11 54.96
5,583.61 09/29/10 57.67 55.52
5,604.29 12/21110 36.99 34.84
5,583.56 02/28/11 57.72 55.57
5,584.73 06/21111 56.55 54.40
5,584.71 09/20/11 56.57 54.42
5,585.03 12/21111 56.25 54.10
5,584.63 03/27/12 56.65 54.50
5,584.67 06/28/12 56.61 54.46
5,583.98 09/27/12 57.30 55.15
5,584.65 12/28/12 56.63 54.48
5,582.88 03/28113 58.40 56.25
5,584.63 06/27/13 56.65 54.50
5,581.38 09/27/13 59.90 57.75
5,579.71 12/20113 61.57 59.42
5,579.26 03/27/14 62.02 59.87
5,577.73 06/25/14 63.55 61.40
5,576.79 09/25/14 64.49 62.34
5,577.11 12117114 64.17 62.02
5,577.18 03/26/15 64.10 61.95
5,577.13 06/22/15 64.15 62.00
5,576.63 09/30/15 64.65 62.50
5,576.20 12/02/15 65.08 62.93
5,576.05 03/30/16 65.23 63.08
5,575.35 06/30/16 65.93 63 .78
5,575.02 09/29/16 66.26 64.11
-.J 0 0\ 0
Depth Below Measuring Point (ft.)
V1 0
.j:::.
0
(j.)
0 N 0
......
0 0
08/23/02
12/01102
03/11103
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
03/15/06
-06/23/06 ~ -10/01106
-01109/07 ~
-04/19/07 ,&;;;.
I
07/28/07 """'" 11/05/07
QC)
-02/13/08 ~ 05/23/08 """" -08/31108 ~
"'1
-12/09/08 ~
-03/19/09 ~
-06/27/09 ~
10/05/09 ~
01113/10 0
-04/23/10 -< ~
08/01110 "'1
-11/09/10 ~ ...
02117/11 e
05/28/11 ~
09/05/11 ,-.., ~ -12/14/11 .
-03/23/12 0" -07/01/12 e
10/09/12 ~ '._.1
01117/13
04/27/13
-08/05/13
-11/13113
-02/21114
-06/01/14
-09/09/14
12/18114
-03/28/15
07/06/15
10/14/15
01/22/16
05/01116
08/09/16
11117116
02/25/17
06/05117
09/13117
Water Levels and Data over Time
White Mesa Mill-Well TW4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629 .53 5,631.39 1.86 121.33
5,581.88 08/23/02 49.51 47.65
5,582.14 09111/02 49.25 47.39
5,582.06 10/23/02 49.33 47.47
5,582.07 11/22/02 49.32 47.46
5,582.16 12/03/02 49.23 47.37
5,582.28 01/09/03 49.11 47.25
5,582.29 02/21/03 49.10 47.24
5,582.74 03/26/03 48.65 46.79
5,582.82 04/02/03 48.57 46.71
5,548.47 05/01/03 82.92 81.06
5,564.76 06/09/03 66.63 64.77
5,562.53 07/07/03 68.86 67.00
5,564.10 08/04/03 67.29 65.43
5,566.01 08/30/04 65.38 63.52
5,555.16 09/16/04 76.23 74.37
5,549.80 10111/04 81.59 79.73
5,546.04 ll/16/04 85.35 83.49
5,547.34 12/22/04 84.05 82.19
5,548.77 01/18/05 82.62 80.76
5,551.18 02/28/05 80.21 78.35
5,556.81 03/15/05 74.58 72.72
5,562.63 04/26/05 68.76 66.90
5,573.42 05/24/05 57.97 56.11
5,552.94 07/29/05 78.45 76.59
5,554.00 09112/05 77.39 75.53
5,555.98 12/07/05 75.41 73.55
5,552.00 03/08/06 79.39 77.53
5,545.74 06/13/06 85.65 83.79
5,544.06 07/18/06 87.33 85.47
5,548.81 11/07/06 82.58 80.72
5543.59 02/27/07 87.80 85.94
5544.55 05/02/07 86.84 84.98
5558.97 08/15/07 72.42 70.56
5559.73 10/10/07 71.66 69.8
5569.26 03/26/08 62.13 60.27
5535.47 06/25/08 95.92 94.06
5541.41 08/26/08 89 .98 88.12
5558.45 10114/08 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 12/11/09 83.25 81.39
5,570.58 03/11110 60.81 58.95
Water Levels and Data over Time
White Mesa Mill-Well TW4-19
Total or
Measuring Measured
Water Land Point Depth to Total Depth
Elevation Surface Elevation Length Of Date Of Water to Water Total Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,629.53 5,631.39 1.86 121.33
5,561.35 05/11/10 70.04 68.18
5,535.26 09/29/10 96.13 94.27
5,568.40 12/21110 62.99 61.13
5,550.36 02/28/11 81.03 79.17
5,570.41 06/21111 60.98 59.12
5,567.84 09/20111 63.55 61.69
5,571.32 12/21111 60.07 58.21
5,572.40 03/27/12 58.99 57.13
5,572.39 06/28112 59.00 57.14
5,571.40 09/27112 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 06/27113 65.39 63.53
5,568.37 09/27113 63.02 61.16
5,564.55 12/20113 66.84 64.98
5,565.11 03/27/14 66.28 64.42
5,561.49 06/25114 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 09/30115 63.23 61.37
5,567.51 12/02/15 63.88 62.02
5,566.38 03/30/16 65.01 63.15
5,566.91 06/30/16 64.48 62.62
5,567.38 09/29/16 64.01 62.15
-0 0 \0 0
Depth Below Measuring Point (ft.)
00 0 -..J 0 0\ 0 Vl 0
.j::.
0
t------t----+----1------+----~-----+ 08/23/02
12/01102
03/11103
06/19/03
09/27/03
01105/04
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
10/01/06
01109/07
04/19/07
07/28/07
11/05/07
02/13/08
05/23/08
08/31108
12/09/08
03/19/09
06/27/09
10/05/09
01/13/10
04/23/10
-08/01110
-11109/10
02/17/11
05/28/11
09/05/11
12/14/11
03/23112
07/01112
10/09/12
01117/13
04/27113
08/05113
11113113
02/21114
06/01/14
09/09114
12/18114
03/28115
07/06115
10/14/15
01/22/16
-05/01116
08/09/16
11/17116
02/25117
06/05117
.__ __ ____!, ___ --1,. ___ _L ___ _.l__ ___ ....L,. ___ ..l._ 09/13117
~ ~ ,&;;;..
I
lo-o& ~
~ '"1
~ ~ "'C ~
0 < ~ '"1
~ .... a ~ --. ?
r::J" ! ._,
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) Monitorin~ (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 06/13/06 99.10 98.09
5,569.13 07/18/06 60.40 59.39
5,547.95 11/07/06 81.58 80.57
5,549.25 02/27/07 80.28 79.27
5,550.58 05/02/07 78.95 77.94
5,563.60 08/14/07 65.93 64.92
5,555.85 10/10/07 73.68 72.67
5,569.10 03/26/08 60.43 59.42
5,560.00 06/25/08 69.53 68.52
5,539.64 08/26/08 89.89 88.88
5,539.51 10/14/08 90.02 89.01
5,553.00 03/03/09 76.53 75.52
5,534.18 06/24/09 95.35 94.34
5,558.39 09/10/09 71.14 70.13
5,560.99 12/11/09 68.54 67.53
5,564.09 03111110 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 06/28112 61.76 60.75
5,569.58 09/27112 59.95 58.94
5,572.58 12/28/12 56.95 55.94
5,571.52 03/28/13 58.01 57.00
5,569.93 06/27113 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 06/25114 70.55 69.54
5,561.03 09/25/14 68.50 67.49
5,559.39 12/17/14 70.14 69.13
5,565.65 03/26115 63.88 62.87
5,568.25 06/22/15 61.28 60.27
Water Levels and Data over Time
White Mesa Mill-Well TW4-20
Total or
Measuring Measured
Water Land Point Depth to Total Depth Total
Elevation Surface Elevation Length Of Date Of Water to Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,628.52 5,629.53 1.01 106.0
5,566.78 09/30/15 62.75 61.74
5,565.43 12/02/15 64.10 63.09
5,565.87 03/30/16 63.66 62.65
5,564.42 06/30/16 65.11 64.10
5,565.43 09/29/16 64.10 63.09
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 11/07/06 60.88 59.73
5,579.53 02/27/07 59.82 58.67
5,578.07 05/02/07 61.28 60.13
5,583.41 08/15/07 55.94 54.79
5,583.45 10/10/07 55.90 54.75
5,586.47 03/26/08 52.88 51.73
5,579.16 06/24/08 60.19 59.04
5,579.92 08/26/08 59.43 58.28
5,577.37 10/14/08 61.98 60.83
5,578.00 03/10/09 61 .35 60.20
5,580.14 06/24/09 59.21 58.06
5,578.72 09/10/09 60.63 59.48
5,579.99 12/11109 59.36 58.21
5,582.81 03/11/10 56.54 55.39
5,582.23 05/11/10 57.12 55.97
5,576.60 09/29/10 62.75 61.60
5,581.14 12/21/10 58.21 57.06
5,579.53 02/28/11 59.82 58.67
5,584.17 06/21/11 55.18 54.03
5,584.80 09/20/11 54.55 53.40
5,585.68 12/21/11 53.67 52.52
5,585.24 03/27112 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 12/28112 54.10 52.95
5,582.84 03/28/13 56.51 55.36
5,581.79 06/27/13 57.56 56.41
5,580.89 09/27/13 58.46 57.31
5,577.45 12/20/13 61.90 60.75
5,576.01 03/27/14 63.34 62.19
5,574.08 06/25/14 65.27 64.12
5,573.20 09/25/14 66.15 65.00
5,576.13 12117114 63.22 62.07
5,578.19 03/26/15 61.16 60.01
5,574.85 06/22/15 64.50 63.35
Water Levels and Data over Time
White Mesa Mill-Well TW4-21
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,638.20 5,639.35 1.15 120.92
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
5,571.86 06/30/16 67.49 66.34
5,570.82 09/29/16 68.53 67.38
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 07118/06 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 08114/07 57.18 56.01
5,571.99 10/10/07 57.01 55.84
5,573.05 03/26/08 55.95 54.78
5,573.04 06/24/08 55.96 54.79
5,573.04 08/26/08 55.96 54.79
5,573.02 10/14/08 55.98 54.81
5,573.19 03/10/09 55 .81 54.64
5,573.32 06/24/09 55.68 54.51
5,573.17 09110/09 55.83 54.66
5,573.52 12111/09 55.48 54.31
5,573.88 03111/10 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 06/21/11 54.03 52.86
5,575.06 09/20/11 53.94 52.77
5,575.69 12/21111 53.31 52.14
5,575.61 03/27/12 53.39 52.22
5,575.62 06/28112 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 03/27114 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 12/17114 60.40 59.23
5,557.00 03/26115 72.00 70.83
5,570.93 06/22/15 58.07 56.90
Water Levels and Data over Time
White Mesa Mill-Well TW4-22
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,627.83 5,629.00 1.17 113.5
5,571.24 09/30115 57.76 56.59
5,568.23 12/02115 60.77 59.60
5,570.28 03/30/16 58.72 57.55
5,570.75 06/30/16 58.25 57.08
5,544.60 09/29/16 84.40 83.23
--
---
-
-
~
-
0 0 -
~
! ~
----...---
~
~
I
~
~
~
~
~
~
4
~
0 10
~
0 00
__.
0 0\
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 09/13/07 68.48 66.88
5,538.80 10110/07 68.57 66.97
5,539.25 11/30/07 68.12 66.52
5,539.49 12/11107 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 09110/08 66.19 64.59
5,539.57 10114/08 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 12111109 66.73 65.13
5,541.15 03/11110 66.22 64.62
5,541.61 05/11110 65.76 64.16
5,541.47 09/29/10 65.90 64.30
5,541.54 12/21110 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 12/21111 64.79 63.19
5,542.59 03/27112 64.78 63.18
5,542.61 06128/12 64.76 63.16
5,542.92 09/27/12 64.45 62.85
5,542.61 12/28112 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 09127113 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 1.60 113.5
5,542.35 03/27/14 65.02 63.42
5,541.42 06/25/14 65.95 64.35
5,540.65 09/25114 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 06/22115 68.15 66.55
5,538.82 09/30/15 68.55 66.95
5,538.28 12/02/15 69.09 67.49
5,538.29 03/30/16 69.08 67.48
5,537.60 06/30/16 69.77 68.17
5,537.07 09/29/16 70.30 68.70
-..J ...... -..) 0 0\ \0
Depth Below Measuring Point (ft.)
0\ 00 0\ -..J 0\ 0\ 0\ U1 0\ .j:::.. 0\ (j.)
09113/07
11/02/07
12/22/07
02/l0/08 03/31/08
05/20/08
07/09/08
08/28/08
10/17/08 12/06/08 01125109
03/16/09 05105109
06/24/09 08/13/09
10/02/09
11/21109 01./10/10 -03/01/10 ~ 04/20/10
-06/09/10 ~ 07/29/10 ol:;o. 09117/10 I
I J/06/10 N (.H 12/26/10 ~ -02/14/11
04/05/11
-05/25111 ..... ('tl .• 07/14/11 "'1 -09/02/11 ~ 10/22/11 ('tl 12/11111 "0 01130/12 ;. 03/20112
05/09/12 0 1-06/28112 < -08117/12 ('tl
10/06/12 "'1
J 1/25112 ~ ..... 01/14/13 a 03/05113
04/24/13 ('tl -06/1 3/13 ~ 08/02/13
09/21113 0" 11/J0/13 -12/30113 a
02/18/14 "0
04/09/14 '--"
~ 05/29114
07/18114
09/06114
10/26/J 4
12/15/14
02/03115
03/25/15
05/14/15
07/03/15
08/22/15
10/ll/15
J J/30/15
01/19116 03/09/16
04/28/16 06/17/16
08/06/16
09/25/16
11114/16
01103/17
02/22/17
04/13/17
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 09/13/07 57.22 55.09
5,570.53 10110/07 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 01108/08 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 11126/08 56.88 54.75
5,570.92 12/29/08 56.91 54.78
5,571.65 01126/09 56.18 54.05
5,571.31 02/24/09 56.52 54.39
5,571.37 03/06/09 56.46 54.33
5,571.21 04/07/09 56.62 54.49
5,571.23 05/29/09 56.60 54.47
5,571.42 06/30/09 56.41 54.28
5,571.38 07/31109 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 12/11109 56.19 54.06
5,571.86 03/11/10 55.97 53.84
5,571.91 05/11/10 55.92 53.79
5,572.18 09129110 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 03/27112 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 09/25114 64.40 62.27
5,560.97 12/17114 66.86 64.73
5,561.95 03/26115 65.88 63.75
5,565.38 06/22/15 62.45 60.32
5,562.61 09/30115 65.22 63.09
5,560.91 12/02/15 66.92 64.79
5,563.69 03/30/16 64.14 62.01
5,565.64 06/30116 62.19 60.06
5,565.35 09/29/16 62.48 60.35
00 0 0
-...J 0 0
Depth Below Measuring Point (ft.)
~ 0
~
~
•
t
t
~
~
~
"
v
( ~
t
~
U1 0 0
.j:>. o 0
(j.)
0 0
N 0 0
......
0 0 0 0
-
-
-
-
-
-
-
-
09/13/07
11/02/07
12/22/07 02/10/08
03/31/08 05/20/08
07/09/08
08/28/08 I0/17/08
12/06/08 01/25/09
03/16/09
05/05/09
06/24/09
08/13/09 10/02/09
11/21/09 01/10/10
03/01/10
04/20110
06/09110
07/29110 09117/10
11/06110
12/26/10 02/14/11
04/05/11 05/25/11
07/14/11 09/02/11
10/22/11
12111/11 01/30/12
03/20/12
05/09112 06/28/12
08/17/l2 10/06/12 11/25112
01114/13
03/05/13 04/24/13
06/13/13
08/02/13 09/21/13
I 'Ill 0/13 12/30/13
02/18/14 04/09/14
05/29/14
07/18/14 09/06/14
10/26/14 12/15114
02/03/15
03/25115 05/14115
07/03/15
?8/22/15 0111/15
11/30/15 Ol/19/16
03/09/16 04/28/16
06117/16 08/06/16
09/25/16 I 1/14/16
01103117 02/22117
04/13/17
~ ~
"'"" I N
"'"" ~ """ ~ ""1
~ ~ ~ g.
0 -< ~ ""1
~ ..... a ~ ---~
C"' -a ~ '-"'
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
5,601.86 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 12/11/07 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 07/16/08 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 10114/08 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 02/24/09 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 03111110 45.16 28.08
5,599.63 05/11110 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 06/21/11 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 12/28112 47.50 30.42
5,597.43 03/28/13 47.48 30.40
5,587.61 06/27113 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 06/25/14 62.47 45.39
5,583.95 09/25114 60.96 43.88
5,581.13 12/17/14 63.78 46.70
5,587.40 03126115 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 12/02115 66.49 49.41
5,579.42 03/30/16 65.49 48.41
5,579.25 06/30/16 65.66 48.58
5,579.68 09/29/16 65.23 48.15
\0 0 00 0 -.....1 0
Depth Below Measuring Point (ft.)
0\ 0 Ul 0
.j:>..
0 w 0 N 0 -0 0
-
--
-
09/13/07 ] IJ02/07
12/22/07
02/10/08 03/31/08
05/20/08 07/09/08
08/28/08
10/17/08 12/06/08
01/25/09 03/16/09
05105109
06/24/09 08/13/09
10/02/09
11/21/09 01110/10
03/01/10 ~ 04/20/JO
06/09/10 ~ 07/29110 ,.
09/17110 I
11/06/10 N (J) 12/26/10 ~ 02/14/11 04/05/11
05/25/11 ~ ~ 07/14/11 "'1 09/02111 ~ 10/22111 ~ 12/11/11 "CC Ol/30/12 ~ 03/20/12
05/09/12 0 06/28112 < 08/17112 ~
10/06/12 "'1
11/25112 ~ .... 01114113 a 03/05/13
04/24/13 ~ ,-..._ 06/13/13 ~ 08/02113
09/21113 0" 11/10/13 -12/30/13 a
02/18/14 "CC
04/09/14
...._,
05/29114 07/18114
09/06/14 10/26114
12/15/14
02/03/15
03/25/15
05/14/15 07/03/15
08/22115 10/11115
11130/15
01/19/16
03/09/16
04/28/16 06/17/16
08/06/16 09/25/16
11114/16
01/03/17
02/22/17
04/13/17
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 09/29110 64.73 63.03
5,537.17 12/21110 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 09/20/11 64.09 62.39
5,538.16 12/21/11 63.52 61.82
5,538.18 03/27/12 63.50 61.80
5538.23 06/28112 63.45 61.75
5,538.57 09/27/12 63.11 61.41
5,538.20 12/28/12 63.48 61.78
5,539.13 03/28/13 62.55 60.85
5,539.00 06/27113 62.68 60.98
5,538.94 09/27/13 62.74 61.04
5,538.97 12/20/13 62.71 61.01
5,538.53 03/27/14 63.15 61.45
5,537.85 06/25/14 63.83 62.13
5,537.33 09/25114 64.35 62.65
5,537.14 12117/14 64.54 62.84
5,536.43 03/26115 65.25 63.55
5,536.16 06/22/15 65.52 63.82
5,535.76 09/30/15 65.92 64.22
5,535.23 12/02115 66.45 64.75
5,535.15 03/30/16 66.53 64.83
5,534.61 06/30116 67.07 65.37
5,534.12 09/29116 67.56 65.86
L I/ZZ/60 -.--------.-------....------.------.-----.-------.
9I/OI/~O
--171/LZ/Zl ~ e -~
~ "-"
~ e .... ~
~ ~ £1/171/80 ~ 0
-5 ~ ~ ~
~ ~ .... ~
\C ZI/I0/170 -M I ~ ~ ~
OI/81/I I
60190/LO
8 ~ 8 $ 0 0 $ 0 q C'i C'i ~ V') -.5 r-00
1.0 1.0 1.0 1.0 1.0 1.0
C1J) lU!od gu!Jns~gw Mopg qldga
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 12/28112 83.08 81.33
5,526.37 03/28/13 81.57 79.82
5,526.29 06/27113 81.65 79.90
5,527.04 09/27/13 80.90 79.15
5,527.14 12/20/13 80.80 79.05
5,527.55 03/27/14 80.39 78.64
5,527.43 06/25/14 80.51 78.76
5,527.48 09/25/14 80.46 78.71
5,527.81 12/17/14 80.13 78.38
5,527.71 03/26/15 80.23 78.48
5,527.86 06/22/15 80.08 78.33
5,528.13 09/30/15 79.81 78.06
5,527.92 12/02/15 80.02 78.27
5,528.59 03/30/16 79.35 77.60
5,528.34 06/30/16 79.60 77.85
5,528.32 09/29/16 79.62 77.87
-Q.
E -..c .
~ -cu
E ·-1-
~ cu > 0
.J: ..,
Q. cu c
~ cu ..,
tO 3:
r..... N
I .qo
3: 1-
L1/90/EO
91/81/80
91/1E/T.O
S1/S1/LO
'rl1/Ll/lT.
'rl1/01/90
H/ll/H
ET./90/SO
lT./81/0T.
lT./T.O/tJO
H/'rl1/60
0 0 oci ,.....
~
~
• ~
•
'~
0 0
0 00
~
~
•
~'-.
0 C! N 00
......
0 0
o::i co
0 C!
1.0 co
0 0
co co
-~
8 0 0"1
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 06/25114 37.79 34.31
5,578.84 09/25114 38.16 34.68
5,578.72 12/17114 38.28 34.80
5,578.11 03/26115 38.89 35.41
5,577.83 06/22/15 39.17 35.69
5,577.56 09/30/15 39.44 35.96
5,577.27 12/02/15 39.73 36.25
5,577.25 03/30/16 39.75 36.27
5,576.75 06/30/16 40.25 36.77
5,576.36 09/29/16 40.64 37.16
L1190/£0
91/81180 v !
~
91/I£/IO
-.. ~ e -)
,.Q . ~ '--' ~11~11LO ~ e ...
E-t
~ ~ ~ 0 f711LZIZI -: ~ ~ Q
~ ~ ..... ~ 171101190
QO ('1
I ~ ~ E-t
£11ZZ/II
II
v
/
/
(
~
£1190/~0 /
/
Z118110I
0 0 0 0 0 0 'r: ~ 'r: ~ 'r: 0 r-00 00 0\ 0\ 0
(") (") (") (") (") """ ("U) lU!Od ~upnS'B:::lW MOJ:::lfl qld:::lQ
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) (L D) (MP) Riser (L) Monitorin~ (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 03/27114 71.72 68.24
5,533.85 06/25/14 72.19 68.71
5,533.53 09/25114 72.51 69.03
5,533.60 12/17/14 72.44 68.96
5,533.04 03/26115 73.00 69.52
5,532.93 06/22/15 73.11 69.63
5,532.79 09/30/15 73.25 69.77
5,532.34 12/02/15 73.70 70.22
5,532.54 03/30/16 73.50 70.02
5,532.01 06/30/16 74.03 70.55
5,531.58 09/29/16 74.46 70.98
9l/81/80
9lll£/10
,-.., c.. e -..c . ~ ~l/~1/LO '-"
~ e ·~ ~
~ ~ ;;;...
0 tl/LZ/Zl ..= ..... c.. ~ Q
~ ~ ..... ~ tl/Ol/90
0\ ('1
I ~ ~ ~
£1/ZZ/11
£l/90/~0
Z118l/Ol
0 0 0 0 0 0 0 0 0 ~ V"l ~ V"l ~ V"l 0 tr) ~
..--< ..--< C'l C'l Cf') Cf') ..f ..f tr) r-r-r-r-r-r-&; r-r-("lJ) lll!Od ~u!Jnsu~w Mops: ql ~a
Water Levels and Data over Time
White Mesa Mill -Well TW 4-30
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,599.33 5,602.81 3.48 105
5,524.78 03/28/13 78.03 74.55
5,524.79 06/27113 78.02 74.54
5,525.54 09/27113 77.27 73.79
5,525.81 12/20/13 77.00 73.52
5,525.98 03/27114 76.83 73.35
5,525.91 06/25/14 76.90 73.42
5,526.00 09/25114 76.81 73.33
5,526.41 12/17/14 76.40 72.92
5,526.23 03/26/15 76.58 73.10
5,526.48 06/22/15 76.33 72.85
5,526.74 09/30/15 76.07 72.59
5,526.56 12/02/15 76.25 72.77
5,527.26 03/30/16 75.55 72.07
5,527.04 06/30/16 75.77 72.29
5,526.97 09/29/16 75.84 72.36
-c.. a -,.Q . ;:::::
'-'
~ a ... ~ -~ ;...
0 .; c.. ~ Q -~ ..... ~ = ~ I ~ ~ ~
L 11901£0 -.-------.----...--------,-------,-----.-------.-------.
91181180
9111£/10 -
~11~11LO -
f711LZ/Zl -
171101190 -
£11ZZ/ll
£1190/~0
Z118110l +-----+----1-----+-----+---+-----+------1
0 lr1
00 r-
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 09/27/13 83.36 79.88
5,521.81 12/20/13 82.77 79.29
5,522.25 03/27/14 82.33 78.85
5,522.32 06/25114 82.26 78.78
5,522.64 09/25/14 81.94 78.46
5,523.27 12/17/14 81.31 77.83
5,523.33 03/26/15 81.25 77.77
5,523.82 06/22/15 80.76 77.28
5,524.34 09/30/15 80.24 76.76
5,524.29 12/02115 80.29 76.81
5,525.32 03/30116 79.26 75.78
5,525.33 06/30116 79.25 75.77
5,525.43 09/29116 79.15 75.67
00 VI
8
Depth Below Measuring Point (ft.)
00 ~
0 0
\
00 w
8
~
00 N
0 0
1\
\
~
00 .......
0 0
\
1\
00 0
0 0
' ~
-.]
10 8
~
-.]
00 0 0
.
10/18/12
05/06/13
11/22/13
06/10/14
12/27114
07/15/15
01131116
08/18/16
03/06/17
1-3 ~ ~ I ~ ~
~ ~ ~ "'1
~ ~ ~ 9'
0 -< ~ "'1
1-3 ...
9 ('D -~ •
0"' -9 ~ '-'
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 09/27113 47.41 45.77
5,563.74 12/20/13 48.10 46.46
5,563.24 03/27/14 48.60 46.96
5,562.43 06/25114 49.41 47.77
5,561.90 09/25/14 49.94 48.30
5,560.93 12117/14 50.91 49.27
5,561.35 03/26/15 50.49 48.85
5,561.15 06/22115 50.69 49.05
5,560.96 09/30/15 50.88 49.24
5,560.58 12/02115 51.26 49.62
5,560.85 03/30116 50.99 49.35
5,560.25 06/30116 51.59 49.95
5,559.69 09/29/16 52.15 50.51
-~ e -,.Q . ;::::
'-"
Q,) e ... E-t
~ Q,) ;;...
0
~ ~ Q,)
Q
~ ~ ~
N ~ I ~ E-t
L I/901£0 -,--------,.--------,-----.-----.------.----~
91/8l/80
9l/1£/10
~11~1/LO
t11LZ/Z1
tl/01190 -
£11ZZI11
£11901~0 +---~f-------+----+-----1----~f-------1
0 0
o\ "¢
0 0 0 It)
0 ~ -It)
0 0 N
It)
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 06/25/14 70.67 69.14
5,535.73 09/25/14 71.00 69.47
5,535.73 12/17/14 71.00 69.47
5,535.14 03/26/15 71.59 70.06
5,534.98 06/22/15 71.75 70.22
5,534.81 09/30115 71.92 70.39
5,534.34 12/02/15 72.39 70.86
5,534.33 03/30/16 72.40 70.87
5,533.90 06/30116 72.83 71.30
5,533.48 09/29/16 73.25 71.72
L 1190/£0
91181180
-9111£/10
Co! 8 -,.Q
i::! '-'
~ e ~11~l!LO .... E-4
J-t ~ ;;...
0 .: Co! ~ t11LZ/ZT ~
J-t ~ ~
~ ~ I tl/Ol/90 ~ ~ E-4
£1/ZZ/l I
£1190/~0
0 V)
o\ \0
8 0 r:-
/
v
/
/ ,/
v
Water Levels and Data over Time
White Mesa Mill -Well TW 4-34
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
5,601.60 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 06/25/14 70.02 68.28
5,532.94 09/25/14 70.40 68.66
5,532.99 12/17/14 70.35 68.61
5,532.37 03/26/15 70.97 69.23
5,532.24 06/22/15 71.10 69.36
5,532.08 09/30/15 71.26 69.52
5,531.79 12/02/15 71.55 69.81
5,531.80 03/30/16 71 .54 69.80
5,531.28 06/30/16 72.06 70.32
5,530.87 09/29/16 72.47 70.73
L 11901£0
91181180
9111£/10 ,-....
~ e -~ . ¢:: ,_,
QJ e ~11~11LO ..... ~
~ QJ ~ 0 ..= ...... ~ QJ v11LZIZI ~
~ QJ ...... ~
~ ~ I ~ v1I01190 ~ ~
£11ZZ/11
£1190/~0
( v
v /
8 0 r-
0 I()
0 r-
~ -r-
0 I() -r-
/
/
Water Levels and Data over Time
White Mesa Mill -Well TW 4-35
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,598.67 5,599.87 1.20 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 09/30115 74.06 72.86
5,525.57 12/02115 74.30 73.10
5,526.01 03/30116 73.86 72.66
5,525.75 06/30/16 74.12 72.92
5,525.57 09/29116 74.30 73.10
9I/8I/80
91/0I/s;'O -Q. e -~ 9I/I £/10
== '-'
~ e """" ~
~ s;'l/£Z/OI
~ ;;;.
0 ..= -Q.
~ s;'I/s;'I/ LO Q
~ ~ -~
1.11 s;'l/90/tO ~ I ~ ~ ~
tl!LZ/ZI
tl/81/60
tl/OI/90
0 0 0 0 0 0 0 00 ~ 0 ...... ~ ~ ~
C"l C"l ..,f """ """ """ """ r-r-r-r-r-r-r-
C"u) lll!Od ~upnsu;}w Mops: qld;}a
Water Levels and Data over Time
White Mesa Mill -Well TW 4-36
Total or
Measuring Measured Total
Water Land Point Depth to Depth to Total
Elevation Surface Elevation Length Of Date Of Water Water Depth Of
(WL) (LSD) (MP) Riser (L) Monitoring (blw.MP) (blw.LSD) Well
5,615.18 5,616.59 1.41 98
5,559.14 09/25/14 57.45 56.04
5,559.77 12/17114 56.82 55.41
5,559.79 03/26/15 56.80 55.39
5,560.08 06/22/15 56.51 55.10
5,560.18 09/30/15 56.41 55.00
5,559.95 12/02/15 56.64 55.23
5,560.53 03/30/16 56.06 54.65
5,560.20 06/30/16 56.39 54.98
5,560.00 09/29/16 56.59 55.18
9119Z/ll
91181180
91101/~0
,-..
Q.
= 91/1£/10 -,.Q
~ '-"
~
= .... ~l/£Z/Ol ~
~ ~ :;;...
0 ..= -Q. ~11~11LO ~ Q
~ ~ -~ ~1190tvo \C ~ I ~ ~ ~
vl!LZIZI
vl/81160
vl!Ol/90
0 00
tn tn
< v v
~ ~ ~
~
~
0 00
\0 tn
~ ~ '-.
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
5,569.07 06/30/16 62.78 61.06
5,569.40 09/29/16 62.45 60.73
9119Z/11 -.---~--~--r-----,r---,------,----,---,---,
91181/80
,.-.,
Q; = 911011~0 -,Q . it: '-'
Ql = .... ~
~ Ql ~ 0 9111£/10 -
-= -Q;
Ql ~
~ Ql -~
t--~11£Z/01 ~ I ~ ~ ~
~1/90/tO
0 8 0 0 0 0 0 0 0 8 "! tr) ~ "! 0 tr) ~ "!
0\ 0 ci ...... ...... N N M M $ tr) \0 \0 \0 \0 \0 \0 \0 \0
('lJ) lU!Od gU!JOSl!;}W MOf;}S: qldgQ
TabG
Chloroform Mass Removed and Volume Pumped in Chloroform Pumping Wells Over Time
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
MW-4 TW4-15 {formerly MW-26)
Total Pumped Total Pumped Total Total 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
Q2 2016 96540.5 1580.0 365405.8 577341152 577 1.3 22105.7 2220.0 83670.1 185747565 186 0.4
Q3 2016 79786.4 1430.0 301991.5 431847879 432 1.0 17149.5 3190.0 64910.9 207065635 207 0.5
Totals 5014353.38 89.5 2487240.8 32.1
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-19 TW4-20 -
Total Pumped Total Pumped Total Total Pumped Total Pumped Total
Quarter (gal) Cone (liters) Total (ug) Total (grams) (pounds) (gal) Cone (liters) Total (ug) Total (grams) (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
02 2016 123768.0 12600 468461.9 5.903E+09 5903 13.0 15818.3 33700 59872.3 2.018E+09 2018 4.4
03 2016 103609.0 6040 392160.1 2.369E+09 2369 5.2 12186.6 23600 46126.3 1.089E+09 1089 2.4
Totals 17631214.83 378.7 2288888.99 268.1
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 319885.1 6.4E+08 640 1.4 NA NA NA NA NA NA
Q3 2010 76916.8 2100 291130.1 6.1E+08 611 1.3 NA NA NA NA NA NA
Q4 2010 86872.1 1700 328810.9 5.6E+08 559 1.2 NA NA NA NA NA NA
Q12011 73360.0 1800 277667.6 5.0E+08 500 1.1 NA NA NA NA NA NA
Q2 2011 80334.6 1700 304066.5 5.2E+08 517 1.1 NA NA NA NA NA NA
Q3 2011 97535.0 1500 369170.0 5.5E+08 554 1.2 NA NA NA NA NA NA
Q4 2011 109043.5 1500 412729.6 6.2E+08 619 1.4 NA NA NA NA NA NA
Q12012 101616.8 1200 384619.6 4.6E+08 462 1.0 NA NA NA NA NA NA
Q2 2012 87759.1 1500 332168.2 5.0E+08 498 1.1 NA NA NA NA NA NA
Q3 2012 80006.0 1600 302822.7 4.8E+08 485 1.1 NA NA NA NA NA NA
Q4 2012 71596 1400 270990.9 3.8E+08 379 0.8 NA NA NA NA NA NA
Q12013 58716.8 1460 222243.1 3.2E+08 324 0.7 16677.4 10600 63124.0 669113965.4 669.1 1.5
Q2 2013 65603.4 1330 248308.9 3.3E+08 330 0.7 25523.2 12500 96605.3 1207566400.0 1207.6 2.7
Q3 2013 63515.4 1380 240405.8 3.3E+08 332 0.7 25592.9 9640 96869.1 933818379.5 933.8 2.1
Q4 2013 60233.6 1360 227984.2 3.1E+08 310 0.7 24952.2 13300 94444.1 1256106224.1 1256.1 2.8
Q12014 58992.9 1260 223288.1 2.8E+08 281 0.6 24532.0 12100 92853.6 1123528802.0 1123.5 2.5
Q2 2014 60235.3 1220 227990.6 2.8E+08 278 0.6 24193.9 12400 91573.9 1135516502.6 1135.5 2.5
Q3 2014 69229.4 1320 262033.3 3.5E+08 346 0.8 24610.9 12400 93152.3 1155087980.6 1155.1 2.5
Q4 2014 64422.6 1130 243839.5 2.8E+08 276 0.6 23956.9 12400 90676.9 1124393144.6 1124.4 2.5
Q12015 36941.3 1350 139822.8 1.9E+08 189 0.4 22046.9 12700 83447.5 1059783459.6 1059.8 2.3
Q2 2015 68162.8 1280 257996.2 3.3E+08 330 0.7 23191.6 8050 87780.2 706630658.3 706.6 1.6
Q3 2015 64333.0 1220 243500.4 3.0E+08 297 0.7 24619.9 7810 93186.3 727785170.9 727.8 1.6
Q4 2015 59235.1 1190 224204.9 2.7E+08 267 0.6 23657.6 7530 89544.0 674266440.5 674.3 1.5
Q12016 57274.0 1190 216782.1 2.6E+08 258 0.6 24517.8 6070 92799.9 563295229.1 563.3 1.2
Q2 2016 61378.0 1780 232315.7 4.1E+08 414 0.9 26506.3 8570 100326.3 859796780.9 859.8 1.9
Q3 2016 50104.2 1380 189644.4 2.6E+08 262 0.6 22144.1 5840 83815.4 489482044.0 489.5 1.1
Totals 1847931.6 22.7 356723.6 30.2
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)
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 144842.6 5.7 548229.2 3124906.7 3.1 0.0 99369.9 0.0 376115.1 0.0 0.0 0.0
Q2 2013 187509.3 17.4 709722.7 12349175.0 12.3 0.0 147310.4 0.0 557569.9 0.0 0.0 0.0
Q3 2013 267703.5 21.8 1013257.7 22089018.9 22.1 0.1 145840.9 0.0 552007.8 0.0 0.0 0.0
Q4 2013 260555.3 32.5 986201.8 32051558.8 32.1 0.1 126576.5 0.0 479092.1 0.0 0.0 0.0
Q12014 229063.9 78.5 867006.9 68060038.6 68.1 0.2 129979.2 0.0 491971.3 0.0 0.0 0.0
Q2 2014 216984.1 62.7 821284.8 51494558.1 51.5 0.1 124829.8 0.0 472480.8 0.0 0.0 0.0
Q3 2014 213652.5 76.3 808674.7 61701880.6 61.7 0.1 119663.9 0.0 452927.9 0.0 0.0 0.0
Q4 2014 178468.7 25.8 675504.0 17428004.0 17.4 0.04 107416.1 0.0 406569.9 0.0 0.0 0.0
Q12015 92449.3 49.2 349920.6 17216093.5 17.2 0.04 71452.4 0.0 270447.3 0.0 0.0 0.0
Q2 2015 62664.2 4.28 237184.0 1015147.5 1.0 0.002 91985.3 0.0 348164.4 0.0 0.0 0.0
Q3 2015 66313.2 46.90 250995.5 11771687.2 11.8 0.026 124137.1 0.0 469858.9 0.0 0.0 0.0
Q4 2015 107799.1 25.30 408019.6 10322895.7 10.3 0.023 116420.1 0.0 440650.1 0.0 0.0 0.0
Q12016 100063.2 22.80 378739.2 8635254.0 8.6 0.019 115483.2 0.0 437103.9 0.0 0.0 0.0 I
Q2 2016 65233.6 69.60 246909.2 17184878.6 17.2 O.D38 125606.0 0.0 475418.7 0.0 0.0 0.0
Q3 2016 51765.8 17.80 195933.6 3487617.2 3.5 0.008 104983.6 0.0 397362.9 0.0 0.0 0.0
Totals 2245068.3 0.80 1751054.4 0.0
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
-TW4-01 TW4-02 '·
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
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 NA NA NA NA NA NA NA NA NA NA NA NA
02 2013 NA NA NA NA NA NA NA NA NA NA NA NA
03 2013 NA NA NA NA NA NA NA NA NA NA NA NA
04 2013 NA NA NA NA NA NA NA NA NA NA NA NA
012014 NA NA NA NA NA NA NA NA NA NA NA NA
02 2014 NA NA NA NA NA NA NA NA NA NA NA NA
03 2014 NA NA NA NA NA NA NA NA NA NA NA NA
04 2014 NA NA NA NA NA NA NA NA NA NA NA NA
012015 24569.2 1130 92994.4 105083696.9 105.1 0.23 24156.7 1840 91433.1 168236921.5 168.2 0.37
02 2015 23989.9 1260 90801.8 114410232.1 114.4 0.25 22029.9 1650 83383.2 137582233.0 137.6 0.30
03 2015 23652.0 1060 89522.8 94894189.2 94.9 0.21 21586.9 1310 81706.4 107035405.6 107.0 0.24
04 2015 20764.3 1040 78592.9 81736590.5 81.7 0.18 21769.8 2070 82398.7 170565294.5 170.6 0.38
012016 19255.6 974 72882.4 70987502.4 71.0 0.16 20944.6 1970 79275.3 156172362.7 156.2 0.34
02 2016 19588.2 1140 74141.3 84521124.2 84.5 0.19 20624.0 2070 78061.8 161588008.8 161.6 0.36
03 2016 15613.5 1160 59097.1 68552633.1 68.6 0.15 17487.4 1780 66189.8 117817860.0 117.8 0.26
Totals 147432.7 1.37 148599.3 2.2
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-11 TW4-21
Total Total Total Total
Pumped Pumped Total Total Pumped Pumped Total Total
Quarter (gal) Cone (liters) Total (ug) (grams) (pounds) (gal) Cone (liters) Total (ug) (grams) (pounds)
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 9898.7 2450 37466.6 91793119.8 91.8 0.20 NA NA NA NA NA NA
Q2 2015 5243.3 2710 19845.9 53782363.3 53.8 0.12 30743.7 366.0 116364.9 42589555.0 42.6 0.09
Q3 2015 3584.4 1120 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 15557.5 42471935.4 42.5 0.09 134774.9 339.0 510123.0 172931695.8 172.9 0.38
Q12016 3676.2 2660 13914.4 37012349.2 37.0 0.08 125513.3 390.0 475067.8 185276457.8 185.3 0.41
Q2 2016 3760.4 3340 14233.1 47538600.8 47.5 0.10 132248.7 545.0 500561.3 272805924.6 272.8 0.60
Q3 2016 2953.8 3200 11180.1 35776425.6 35.8 0.08 110381.9 456.0 417795.5 190514744.1 190.5 0.42 ----
Totals 33227.1 0.71 658947.9 2.20
Table G-1
Quarterly Calculation of Chloroform Removed and Total Volume of Water Pumped
TW4-37
'
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
Q12013 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 110544.7 3338450242.0 3338.5 7.4 15.3 539592.9
Q3 2015 118063.9 19100 446871.9 8535252554.7 8535.3 18.8 33.4 816299.8
Q4 2015 111737.5 19500 422926.4 824 7065531.3 8247.1 18.2 32.3 847567.8
Q12016 111591.0 17500 422371.9 7391508862.5 7391.5 16.3 30.6 819302.3
Q2 2016 119241.2 16200 451327.9 7311512660.4 7311.5 16.1 39.4 832418.9
Q3 2016 98377.6 15900 372359 5920511534.4 5920.5 13.1 24.7 686543.4 -
Totals 588217.2 89.8 918.5 35198900.1
TableG-2
Chloroform Mass Removal Per Well Per Quarter
TW4-15
MW-4 (MW-26) TW4-19 TW4-20 TW4-4 TW4-22 TW4-24 TW4-25 TW4-0l TW4-02 TW4-11 TW4-21 TW4-37 Quarter
Quarter* (lbs.) (IbsJ_ (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (lbs.) (Jbs.) (lbs.) (Ibs.) (lbs.) (lbs.) Totals (!bs.)
012007 36.8 12.9 150.2 87.0 NA NA NA NA NA NA NA NA NA 286.9
02 2007 1.4 0.1 0.0 2.5 NA NA NA NA NA NA NA NA NA 4.0
03 2007 2.2 0.8 2.9 3.1 NA NA NA NA NA NA NA NA NA 9.0
04 2007 1.7 1.0 3.1 4.8 NA NA NA NA NA NA NA NA NA 10.6
01 2008 1.7 0.4 4.6 7.2 NA NA NA NA NA NA NA NA NA 13.8
02 2008 1.3 0.5 3.2 9.9 NA NA NA NA NA NA NA NA NA 14.8
03 2008 1.2 0.3 15.9 9.3 NA NA NA NA NA NA NA NA NA 26.8
04 2008 1.3 0.3 20.7 0.4 NA NA NA NA NA NA NA NA NA 22.7
01 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
03 2009 1.5 0.4 11.1 5.5 NA NA NA NA NA NA NA NA NA 18.5
Q42009 4.8 0.6 17.8 26.1 NA NA NA NA NA NA NA NA NA 49.4
012010 0.9 0.4 2.7 0.4 NA NA NA NA NA NA NA NA NA 4.5
02 2010 1.5 1.0 6.8 5.9 1.4 NA NA NA NA NA NA NA NA 16.5
03 2010 1.3 1.2 2.0 4.9 1.3 NA NA NA NA NA NA NA NA 10.6
04 2010 1.l 0.5 7.7 7.4 1.2 NA NA NA NA NA NA NA NA 17.9
01 2011 1.1 0.2 12.9 9.6 1.1 NA NA NA NA NA NA NA NA 24.9
02 2011 1.2 0.8 5.3 4.6 1.1 NA NA NA NA NA NA NA NA 13.1
03 2011 1.2 0.4 1.1 4.1 1.2 NA NA NA NA NA NA NA NA 8.1
042011 1.2 0.8 2.7 4.8 1.4 NA NA NA NA NA NA NA NA 10.8
012012 1.1 0.6 0.8 7.0 1.0 NA NA NA NA NA NA NA NA 10.6
02 2012 1.1 0.7 0.7 6.9 1.1 NA NA NA NA NA NA NA NA 10.4
03 2012 1.l 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
OJ 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
03 2013 0.9 0.6 22.3 4.4 0.7 2.1 0.1 0.0 NA NA NA NA NA 31.1
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
012014 0.8 0.3 1.5 2.8 0.6 2.5 0.2 0.0 NA NA NA NA NA 8.6
02 2014 0.8 0.4 2.0 3.4 0.6 2.5 0.1 0.0 NA NA NA NA NA 9.9 i
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
04 2014 0.8 0.4 7.1 3.2 0.6 2.5 0.04 0.0 NA NA NA NA NA 14.6 i
Q\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
02 2015 0.7 0.5 1.0 2.8 0.7 1.6 0.00 0.0 0.25 0.30 0.12 0.09 7.4 15.3
Q3 2015 1.0 0.4 7.6 2.5 0.7 1.6 0.03 0.0 0.21 0.24 O.o3 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
Q12016 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 I
Q2 2016 1.3 0.4 13.0 4.4 0.9 1.9 0.04 0.0 0.19 0.36 0.10 0.60 16.1 39.4
Q3 2016 1.0 0.5 5.2 2.4 0.6 1.1 0.01 0.0 0.15 0.26 0.08 0.42 13.1 24.7
Well Totals 89.5 32.1 378.7 268.1 22.7 30.2 0.80 0.00 1.37 2.25 0.71 2.20 89.8 918.5
* Q1 2007 represents the cumulative total prior to and including 01 2007.
Table G-3 Well Pumping Rates and Volumes
Volume of Water Pumped
Pumping Well Name During the Quarter (gals) Average Pump Rate (gQm)
MW-4 79786.4 4.4
MW-26 17149.5 7.3
TW4-19 103609.0 18.0
TW4-20 12186.6 6.7
TW4-4 50104.2 9.6
TWN-2 42329.6 18.5
TW4-22 22144.1 17.6
TW4-24 51765.8 15.9
TW4-25 104983.6 14.5
TW4-01 15613.5 15.4
TW4-02 17487.4 16.1
TW4-11 2953.8 16.0
TW4-21 110381.9 16.2
TW4-37 98377.6 17.0
350.0
300.0
250.0
200.0
Cii -g 150.0
:::J
0 a.. -""C Cl.l > ~ 100.0
Cl.l a:
E ..... 0 0 50.0 ..... .Q .s::::
()
0.0
""" 0 0 C\J ,.... a
""" 0 0 C\J
""'" a
co 0 0 C\J
C') a
0)
0 0 C\J
~
Mass of Chloroform Removed by Quarter (lbs.)
0 ,....
0 C\J ,.... a
0 ,....
0
C\J
0
,.... ,....
0 C\J
C') a
I
C\J ,....
0
C\J
C\J a
C') ,....
0 C\J
0
C') ,....
0
C\J
""'" a
Ql 2007 represents the cumulative total prior to and including Ql 2007.
""'" ,....
0 C\J
C') a
l!) ,....
0 C\J
C\J a
(!) ,....
0 C\J ,.... a
40.0
35.0
30.0
25.0
(j) 20.0
"C c: :::::l 0 c.. -"C 15.0
Q) > 0 E Q) a: 10.0
E ....
.E 0 ....
_Q 5.0 ..s:::: ()
0.0
~
1'-0 0 C\1 ..... a
........ .,....
1'-0 0 C\1
"<t a
...
co 0 0 C\1
C') a
MW-04 Mass of Chloroform Removed by Quarter (lbs.)
A
lV\~~ ....
0> 0 0 C\1
C\1 a
.
0 ..-0 C\1
,-a
0 ..-0 C\1
"<t a
.....
..-0 C\1
C') a
.....
C\1 ..-0 C\1
C\1 a
C') ..... 0 C\1
,-a
C') ..-0 C\1
0
Ql 2007 represents the cumulative total prior to and including Ql 2007.
.... . ......
"<t ..-0 C\1
C') a
...... ,..,.. .....
I!) ..-0 C\1
C\1 a
..... _..... ... . .....
<0 ..-0 C\1
,-a
...... ....
--ui ..c -....
Q) t::: ct1 :::J a
>. ..c
"'0 Q) > 0 E
Q) a:
E ....
0 -0 .... 0
..c
(.) -0
en en ct1 ~
T"""
0 I -.::t ~ I-
l{)
C\1
ci
0
C\1
ci
9~0G £0
9~0G GO
9~0G ~0
S~OG 170
S~OG £0
S~OG GO
S~OG ~0
l{) 0 l{) 0 ,.... 0 0
ci ci ci ci (spunod) paAoWal:l WJO!OJOI40
-(/)
.0 _...
~ Q) t ctl
:J
0
>. .0
"'0 Q) > 0 E Q) a:
E ~
0 -0 ~ 0
..c
(..) -0
(/)
(/)
ctl ~
C\1 0 I '<:t ~
0 C")
0
ll')
C\1 0
0 ll') 0 ll') 0 ~ ~ ~ 0 0
0 (spunogj paAOW~ WJOJd.R>ILIO 0
9~0G £0
9~0G GO
9~0G ~0
S~OG PO
S~OG £0
cri .0 :::::.. ....
Q) t cu
::J 0
>-.0
"0 Q) > 0 E Q) a:
E .... 0 -0 ....
0 ::2
()
0
en en cu :2
.q-
0 I .q-
~
co
0
CD
0
C\1
0
(spunOd) paAOW9l:l WJOJOJOILI:)
0
0
9~0G GO
S~OG 80
17~0G 170
17WG ~o
8~0G GO
G~OG 80
~ ~OG 170
-C/)
..0 ::::, ....
Q) t:: «S
::::::1 a
>. ..0
"'0 Q) > 0 E Q) a:
E .... 0 -0 .... 0
.c 0 -0
C/)
C/)
«S
:2 .,.... .,....
I v ~ 1-
LO C\J c)
0 C\J 0
LO ,....
0
0 LO ,.... 0
(spuno'd) paAOW9CJ ulioJOJOII.jQ
0 0
0
9~0G £0
9~0G GO
9~0G ~0
9~0G tO
9~0G £0
9~0G GO
CiJ "0 c ::I
0 a.. -"0 (]) > 0 E (]) a:
E ....
0 -0 ....
.Q .s::::.
()
14.0
12.0
10.0
8.0
6.0
4.0
2.0
0.0
~
1'-0 0
C\1 ....
0
MW-26 Mass of Chloroform Removed by Quarter (lbs.)
~~ ~ .... ..... .....-.........
1'-0 0
C\1
"""" 0
co 0 0
C\1
C")
0
en 0 0
C\1
C\1 0
"""~~ ~ ....
0 ....
0
C\1 ....
0
0 ....
0 C\1
"""" 0
....
0 C\1
C")
0
C\1 ....
0
C\1
C\1 0
~
C") .... 0 C\1 ....
0
..... ,.
C") ....
0 C\1
"""" 0
Ql 2007 represents the cumulative total prior to and including Ql 2007.
"""" ....
0 C\1
C")
0
..... .... ....._
LO ....
0 C\1
C\1 0
""
' <0 ....
0 C\1 ....
0
I
.....
TW4-19 Mass of Chloroform Removed by Quarter (lbs.)
160.0
140.0
120.0 -1---1-----------------------------------------i
100.0 +-~----------------------------------------------------------------------------~
80.0
(j)
"C c ::I 0 60.0 a.. -"C Q) > 0
E 40.0 Q) a:
E ....
0 -20.0 0 .... ..Q
~ ()
0.0 ,..... ,..... co 0'> 0 0 ..... C\1 C') C') """ LO co 0 0 0 0 ..... ..... ..... ..... ..... ..... ..... ..... ..... 0 0 0 0 0 0 0 0 0 0 0 0 0 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 C\1 ..... """ C') C\1 ..... """ C') C\1 ..... """ C') C\1 ..... a a a a a a a a a a a a a
Ql 2007 represents the cumulative total prior to and including Ql 2007.
TW4-20 Mass of Chloroform Removed by Quarter (lbs.)
100.0
90.0
~
80.0
70.0
60.0
-50.0 en "C c
:J 0 40.0 a_ -"C Q) > 30.0 0
E
Q) a:
E 20.0 ,_
0 -0 ,_ 10.0 0
..c ()
0.0
~
..... I .....
~ .... ~ ~ ~ ............................................ .A.. ..... .... ...... -.... ....... .... ,... ,... .... ....
,...... ,...... co C) 0 0 T"" N C') C') -.;t LO co 0 0 0 0 T"" T"" T"" T"" T"" T"" T"" T"" T"" 0 0 0 0 0 0 0 0 0 0 0 0 0 N N N N N N N N N N N N N
T"" -.;t C') N T"" -.;t C') N T"" -.;t C') N T"" 0 0 0 0 0 0 0 0 0 0 0 0 0
Ql 2007 represents the cumulative total prior to and including Ql 2007.
..-.. en .0 --....
Q)
t co :::J 0
>-.0
"'C
Q) > 0 E
Q) a:
E .... 0 -0 ....
0
..c () -0
en en co ~
T"""
C\J I -.;;1-
~ I-
0 "" 0
0 <0 0
0 ll)
0
0 .;t
0
0 C')
0
0 C\J
0
0 ..-
c)
0 0
0
(spunod) paAowal:J WJOJOJOI40
9~0G £0
9~0G cO
9~0G ~0
S~OG tO
S~OG £0
-en ..c :::::.. .... Q) t
ctl
:::J a
>. ..c
"'C Q) > 0 E
Q) a:
E .... 0 -0 ....
0
~
() -0
en en ctl ~
C\1 C\1 I v
$: I-
l!)
C\J
0
C\i ~ ~ l!) .,.... .,.... ci
(spunOd) paAOW8l:::J WJO!OJ0140
0 0
9~0G cO
v~Oc 80
8~0G vO
-(/) ..c :::::.. ......
Q) t::: eel :::J a 9WGG0
>-..c
"0 Q) > 0 E
Q) a:
E ...... 0 -0 ...... 0
~ vWG£0 (.) -0
(/)
(/)
eel ~
.q-
C\1 I .q-
~
£WG170
(spunod) paAOW9tJ WJOJOJ0140
-(/) ..c :::=... .....
Q) t:: C(j
:::::1 a
>. ..c
"'0
Q) > 0 E
Q) a:
E .....
0 -e 0 ..c: ()
())
c)
co
c)
(()
c)
L!)
c)
C\1
c)
(spunOd) paAOW9l:l WJOJOJ0140
~
~
~
~
~~
~
~
-
-
-
0
c)
v~Oc 80
8~0G 170
C/)
..0
.....
Q)
t co
:::J
0
>-..0
"'0 Q) > 0
E
Q)
0:
E .....
0 -e
0
..c () -0
C/)
C/) co ~
"" Cf)
I ~ ~ I-
'
~, ~ ~
v
~ ~ ~ ~
C! C! 0 0 0 0
C\J 0 ex) co "<t C\i
(spunOd) paAOW91:1 WJO!OJOIL!:)
-
0
c::)
9WG£0
S~OG 170
, gwz to
9Wllb
9Wl 1:0
~ swl vO
\ SWl tb
SWllb
SWl l:b
I vwz vb
vwz €'0
vWllb
vwl l:b
~ noz vb
tl:Ol tb -• €Wllb ns tl:Ol l:b aD -nolvb '-~
cv lWl tb t= lWllb ns :::s lWl l:b a nozvu
> HOltb .a
"'C HOllb
cv nol l:b a. OWl vb E OWl tb :::s
Q. OWllb r--: 0 cv OWl l:b N ...... E Gooz vb CY
bO :::s s:: -600l tb ;o
~ ::l
600llb u .5
~ 600l l:b "0 s:: «!
~ sool vb 0 ..... ....
800l tb 0 ·;::::
Q..
800llb ~ .....
~ 800l l:b .8
<!)
LOOl vb .:::; (;j
) LOOl tb ]
::l
LOOllb u
<!)
LOOl l:b
..g
.'!] s:: <!)
0 0 0 Vl 0 0 0 0 <!)
ci ci ci ci ci ci ci .... Q.. 0 0 0 0 0 0 <!)
0 0 0 0 0 8 ....
0 0 0 0 0 r-
0 0 0 0 0 0 0
0 0 0 0 0 0 0
N 0 00 \.0 '<:!" N N
rl rl ...... CY
1400000
1200000
1000000
800000
600000
400000
200000
0
I ~ MW-04 Volume Pumped by Quarter (gal.)
A
........... .... .J ~ \ ~ ...... ... .... ... ,... _... ...... ...... ..-T ~ ........ .... -..... ..... -..... ........
I I I I I I I l l
Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3 Q1 Q3
2007 2007 2008 2008 2009 2009 2010 2010 2011 2011 2012 2012 2013 2013 2014 2014 2015 2015 2016 2016
Ql 2007 represents the cumulative total prior to and including Ql 2007.
-• -ru bO -....
GJ ..., .... ru :::s a
> .c
""C
GJ c.
E :::s
Q.
GJ
E :::s -~
't""'t
0 I ~ ~ 1-
0 0 0 0 0 ('(')
0 0 8 Ll')
N
I
I
0 0 0 0 0 N
~
0 0 0 0 Ll')
.-I
0 0 0 0 0 .-I
0 0 0 0 Ll')
0 0
9lOZEb
9Wllb
9Wl l:b
SWZ17b
SlOZEb
SlOZZb
swz l:b
-• -nJ tlD ......
'-QJ .... '-nJ :::s a
> ..a
"'C QJ a.
E :::s
tl.
QJ
E :::s -~
N 0 I "" ~
0 0 0 0 0
CV')
0 0 0 0 Ll'l N
0 0 0 0 0 N
0
0 0 0 Ll'l ...-i
0
0 0 0 0 ...-i
0
0 0 0 Ll'l
0
0
9Wl £0
910ll0
910Z10
S10l170
SlOl £0
SlOllO
S10l10
1-> 1->
N .j::o. m co 0 N 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0
Q2 2010
Q3 2010
Q4 2010
Q12011
Q2 2011
~ -1
Q3 2011 I I I I ~ I ~
Q4 2011 I I I I I I > I .a::.
I
0
012012 1 I I I I 7 I .a::.
Q2 2012 1 v ~ -c: Q3 2012 3
Q4 2012 I I I I __, I I I tD
"'C
012013 I I I 4(" I I I c:
3
02 2013 I I I I ~ I I I "C
tD
03 2013 1 I I I I I I a.
C"'
04 2o13 1 I I f I I <
Q12014 I I I t I I 0 c:
Q,)
02 2014 I I I '" I I ..,
r+
tD
Q3 2014 1 I I I > I I .., ......
Q4 2014 I I I ~ I I OQ
Q,) -• Q12015 I ~ I I -
Q2 2015
Q3 2015
Q4 2015
Q12016
Q2 2016
Q3 2016
-•
ta
llO -.... cu ... .... ta
::::s a
> ..c
""C cu a.
E
::::s
~
cu
E
::::s -0 > ..... .....
I ~ ~ 1-
0 0 0 0 N .-t
0 0 0 0 0 .-t
0 0 0 0 co
C? 0 0 0 1.0
0
0 0 0 o::t
0
0 0 0 N
0 0
910l EO
910ll0
910l10
S10l170
SlOl EO
SWllO
SlOllO
tO ......
N 0 0 -..l
'"' ~ 0
"0 '"' ~ 012007 "' ~ ::I
!;,' 02 2007 g 03 2007 (") c:: ~ 04 2007
~-012008
)
I
< ~ 02 2008 ..... g
~ 03 2008
"0
~
t
:::::!. 04 2008 0 ~
'"' ..... 012009 0 ~
§ 02 2009 Q..
5' 03 2009 s c:: 9: 04 2009 ::I (JQ 012010 tO ......
N 0 02 2010
0 03 2010 :-..1
04 2010
012011
02 2011
03 2011 ~
04 2011
012012
02 2012
03 2012
04 2012 ~
012013
02 2013
03 2013
04 2013
012014
02 2014
03 2014
04 2014
012015
02 2015 •
03 2015
04 2015
012016
02 2016
03 2016 I ~
I-' 0 0 0 0 0
N 0 0 0 0 0
w 0 0 0 0 0
.j:>.
0 0 0 0 0
U'1 0 8 8
C)
0 0 0 0 0
-....! 0 0 0 0 0
~ 0 8 0
lO 0 0 0 0 0
....
I-' 0 0 0 0 0 0
s
:E I N en
~ -c:
3
tD
"tJ c:
3
"'C tD a.
C'" <
0 c:
OJ ..,
r+ tD .., -OQ OJ -• -
0 ......
N 0 0 -..J
'"' (1)
"0 0 '"' (1) en (1) Q12007 = .... en
g. Q2 2007
(1)
(") Q3 2007 c s Q4 2007 E. I" :;:t. Q12008 < ~
(1) .... Q2 2008 0 ..... e:.. Q3 2008 "0 ::::!. 0 Q4 2008 '"' ~ ..... 0 Q12009 I" = 0.. Q2 2009 s· (") Q3 2009 2' 8: Q4 2009 = (lq
0 Q12010 ......
N Q2 2010 0 ' ~
0 :-.J Q3 2010
Q4 2010
Q12011
Q2 2011
Q3 2011
Q4 2011
Q12012
Q2 2012
Q3 2012
Q4 2012
Q12013
Q2 2013
Q3 2013 ' Q4 2013 ~
Q12014
Q2 2014
Q3 2014
Q4 2014
Q12015
Q2 2015
Q3 2015
Q4 2015
Q12016
Q2 2016
Q3 2016
...... 0 0 0 0 0 0
N 0 0 0 0 0 0
w 0 0 0 0 0 0
.j:>o 0 0 0 0 0 0
V1 0 0 0 0 0 0
0"1 0 0 0 0 0 0
....
-....! 0 0 0 0 0 0
-t :e ~ I .,_.a,
U)
~ -r::::
3
tD
"'C
r::::
3
"C
tD a..
C"' <
/:)
r::::
OJ
""' ,...
tD
""' -OQ OJ -. -
00 0 0 0 0 0 0
10 -N 0 0 -.1 0 ...,
(1) "0 ..., Q12007 (1) 'fJ (1) ::s Q2 2007 .... 'fJ
So Q3 2007 (1)
(") Q4 2007 j;:;:
[ Q12008 ~. <: Q2 2008 (1) .... 0 Q3 2008 .... e:.
"0 Q4 2008 ..., c;· ..., Q12009 0
~ Q2 2009 ::s ~
0. :;· Q3 2009
(") 8" Q4 2009 0. :;· Q12010 (JQ
10 -Q2 2010 N
~
0 Q3 2010 0 :--1 ~
Q4 2010
Q12011 ~
Q2 2011
Q3 2011
Q4 2011
Q12012
Q2 2012
Q3 2012
Q4 2012
Q12013
Q2 2013
Q3 2013
Q4 2013
Q12014
Q2 2014
Q3 2014
Q4 2014
Q12015
Q2 2015
Q3 2015
Q4 2015
Q12016
Q2 2016
Q3 2016 ~
~
~
....... 0 0 0 0 0
,.... ,.,-
~
N 0 0 0 0 0
~ ~ ..
~
w 0 0 0 0 0
.j:>.
0 0 0 0 0
lJ1 0 0 0 0 0
0' 0 0 0 0 0
......
.......
0 0 0 0 0
-1 ~ ~ I N
0
~ -c:
3
tD
-a c:
3
"C tD c.
C"' < p c:
Q)
~ tD ..., -OQ
Q) -• -
910l £b
..-.. 910llb •
ns ao ._. .... cu ..., .... ns
::::s a 910l1b
> .c
"C cu c.
E
::::s S10l17b 0..
cu
E
::::s -0 >
~
N S10l £b I
-.:::1' ~
S10llb
0 q q q 0 0 0 0 0
c) 0 0 0 c) c) c) c) c)
0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0
1.0 ""' N 0 00 1.0 ""' N
.-I .-I .-I .-I
9Wlf'O
9Wllb
9Wl1b
-SWZ17b •
(U
QO -'-SWZ:Eb
C1l ~
(U S10llb ::::J a
> SWZ:lb .c
-c
C1l c. 17Wl17b E
::::J Q. 17Wl Eb C1l
E
::::J 17Wllb -~
N
N 17Wl1b
I ~ ~ HOZ17b 1-
HOZ:Eb
HOllb
HOllb
0 0 0 0 0 0 0 ci ci ci ci ci ci ci 0 0 0 0 0 0 0 0 0 0 0 0 0 Ll'l 0 Ll'l 0 Ll'l m N N .-t .-t
910'l £0
910'l 'lO
9lO'll0
-SlO'l 170 • -"' ao ._ SlO'l £0 ...
QJ
~
"' SlO'l 'lO
:::3 Cl
> SlO'llO ..c
"'C
QJ vwz vo c.
E
:::3 vlO'l £0 Q.
QJ
E vwz zo :::3 -~ 1710'll0 q-
N I q-noz vo ~ I-
noz £0
noz zo
no-z:IO
q q q q q 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0
0 1.11 0 1.11 0 1.11
("(') N N ~ ~
910l Eb
910llb
910l1b
......... • S10l17b -ta bO ....._.. .... Sl:Ol Eb cu ..... ....
ta Sl:Ollb
::::J a
> Sl:Ollb
.c
"'C 1710l17b cu c.
E 1710l Eb ::::J c.
cu 1710llb
E
::::J -1710l1b ~
Ln
N E10l17b
I --=t
3: El:Ol Eb
.....
E10llb
E10l1b
0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 1.0 """ N 0 00 1.0 """ N .-t .-t .-t .-t
9Wl£b
...... 9Wllb
• -"' b.() -.... cu ., ....
"' ::::s 9WZtb Cl
> .a
"'C cu a.
E
::::s SWlvb Q.
cu
E
::::s -~
r-...
M SWZEb I ~ ~
swzzn
0 q q 0 0 0 0 0
c:i 0 0 c:i c:i c:i c:i c:i 0 8 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 o:::t N 0 00 ~ o:::t N .-t .-t .-t
TabH
Laboratory Analytical Reports
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-013C
American West Client Sample ID: MW-04_07252016
ANALYTicAL LABORATORIEs Collection Date: 7/25/2016 1432h
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
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1543h
Units: f.lg/L
Compound
Chloroform
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor: 50
CAS Result
17060-07-0 2,680
460-00-4 2,520
1868-53-7 2,590
2037-26-5 2,510
--The reporting limits were raised due to high ana/yte concentrations.
Analyzed: 8/l/2016 1807h
Units: f.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4 17060-07-0 55.5
Surr: 4-Bromofluorobenzene 460-00-4 48.2
Surr: Dibromofluoromethane 1868-53-7 54.5
Surr: Toluene-d8 2037-26-5 50.3
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 1,430
Amount Spiked %REC Limits Qual
2,500 107 72-151
2,500 101 80-152
2,500 104 80-124
2,500 101 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
50.00 111 72-151
50.00 96.4 80-152
50.00 109 80-124
50.00 101 77-129
ReportDate: 8/9/2016 Page42of61
All ont:~l)ses applicnble to the CWA. SDWA. and RCRA rue perfomted in accordance to NELAC protocols Per1inent somplin~ inrommtion is locoted on the attnched COC Conridential Business tnronnotion: This repor1 is pro,'ided for the exclusi\e we oft he ~ddressee Pri\ ile~es or sub .. seq~ent ~~e of the ~~le of this .cot~pllllY or M) ~~:mber of its staff, or reproductio~ ~~this repo~ in .cotl~ection,.. \Vilh the ll~\ ertisef!lenl, P~?moti~n ~r sale of~;)_ ~I Odl~CI or pt.ocess, ~r in ~onn~c~ion w~th th~ r~-publication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2016
Lab Sample ID: 1607518-013
Client Sample ID: MW-04_07252016
ANALYTICAL LABoRATORIEs Collection Date: 7/25/2016 1432h
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: 7/29/2016 1600h
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
8/1/2016 1857h E300.0 10.0 42.5
8/112016 1814h E353.2 0.100 4.95
Report Date: 8/9/2016 Page 19 of61
All anal~ ses applicJble to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent snmpling information is located on the aU ached COC Confidential Business Information: This repon is pro\'ided for the exclusi\ e use of the
~ddressee Pri\ ile~es or sub ... seq~enl ~~e of the ~~e of this _col~pwly or nn~ ~mber of its staff, or reproductiOI~ ~r this repo~ in ~on~ection~ \\ilh the a~vertisement, p~omotio_n ~r ~ale of~;~.~· odl~Ct or P•.?cess, ~r in ~onn~c~ion w~Lh Lh~ r~-publica.tiOil of lhis report
American West
ANAl YTI CA I I.AB ORA TO A IE B
3440 South 700 West
'alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-012C
Client Sample ID: TW4-01_07252016
Collection Date: 7/25/2016 1437h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1443h
Units: j.!g/L
Compound
Chloroform
Dilution Factor: 50
Surrogate CAS Result
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
2,730
2,560
2,650
2,490
--The reporting limits were raised due /o high analyte concentrations.
Analyzed: 8/1/2016 1747h
Units: j.!g/L Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
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 50.0 1,160
Amount Spiked %REC Limits Qual
2,500 109 72-151
2,500 103 80-152
2,500 106 80-124
2,500 99.5 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
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 55.2 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.9 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 54.3 50.00 109 80-124
Surr: Toluene-d8 2037-26-5 51.1 50.00 102 77-129
Report Date: 8/9/2016 Page 41 of 61
All analyses applicnble to the CWA, SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the altached COC Confidential Business lnformt~lion: This report is plo\ ided for the exclush e use of the ~ddressee Pri\ ile~es o!' su~seq~ent ~~e or the ~~ne of this .cm~pany or nny r~_:mbe1· of its staff, or reproductio~ ~f this repo~ in .con~tection ... \\itb the a~vertisement, P~?moti~n ~r Sflle of~!)~~~ odl~ct or p1.ocess, ~r in 7onn~c~ion w~th lh~ n;:-publication of this report
3440 South 700 West
~a It Lake City, UT 841 19
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-012
Client Sample ID: TW4-01_07252016
Collection Date: 7/25/2016 1437h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1840h
8/1/2016 1812h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 44.7
E353.2 0.100 5.49
Report Date: 8/9/2016 Page 18 of61
All anal~ ses applicable to the CWA. SDWA. and RCRA are periOmred in accordance to NELAC protocols Pertinent sampling information is locoted on the attached COC Confidentinl Business Information: This report is prO\ ided for the exclusi' e use of the
~ddressee Pri' ile~es o.f sub .. seq~nt ~;e of the ~~e of this .c01~pany or M) ~mber of its struT, or reproducti~ ~f this repo~ in ~o~ection .. \\·ith the a~vertisement P~?moli~ ~r saJe of ?A~~ ~rodl~l or P'.?Cess, ~r in 7onn~c~ion w~th th~ r~-publica1ion or I his repor1
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-015C
Client Sample ID: TW4-02_07252016
Collection Date: 7/25/2016 1425h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1623h
Units: J.lg/L
Compound
Chloroform
Dilution Factor: 50
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
2,760
2,420
2,660
2,470
--The reporting limits were raised due to high ana/yte concentrations.
Analyzed: 8/1/2016 1847h
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 50.0 1,780
Amount Spiked %REC Limits Qual
2,500 110 72-151
2,500 96.9 80-152
2,500 107 80-124
2,500 99.0 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: 1,2-Dichloroethane-d4 17060-07-0 56.0 50.00 112 72-151
Surr: 4-Bromotluorobenzene 460-00-4 52.1 50.00 104 80-152
Surr: Dibromotluoromethane 1868-53-7 55.5 50.00 Ill 80-124
Surr: Toluene-d8 2037-26-5 51.5 50.00 103 77-129
Report Date: 8/9/2016 Page 44 of 61
All onnlyses applicable to the CWA. SDWA. and RCRA a1e performed in accordance to NELAC protocols Pertinent sampling information is located on the auached COC Confidential Business Information: This report is provided for the exclusi' c use oft he
~ddressee Pri\ ile~es o_fsub .. seq~tenl ~~~e of' the ~~e of this .cm~pany or M) ~~~ber of its stnff, or reproductio~ ~~this repo~ in ~on~eclion .. "~Lh the CJ~' er1isement, P~?molio.n o.r saJe of~~) ~rO<h~cl or pr.ocess, ~r in ~nn~c!ion w!th th~ r~·publicatioll of this 1eport
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-015
Client Sample ID: TW4-02 07252016
ANALYTICAL L ~lloRAToRtEs Collection Date: 7/25/2016
7/29/2016
1425h
1600h
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:
Analytical Results
Compound
Chloride
Nitrate/Nitrite (as N)
Date
Units Prepared
mg/L
mg/L
Contact: Garrin Palmer
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
8/1/2016 1930h E300.0 10.0 42.9
8/1/2016 1818h E353.2 0.100 4.07
Report Date: 8/9/2016 Page 21 of 61
All analyses applicable Ia the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business [nformalion: This reporl is provided for the exclusi' e use oft he
~ddressee, Pri' ile~es o_f sub~seq~ent ~~e of1he ~~e of lhts .cot~pany or an) 1~mbe1 of its staff, or reproductio~ ~fthis repo~ in .con~ection~ \\ilh the a~;ertisement, P~?moti~n ~r sale of ?J~~. ~rodL~ct or pt.?cess, ~r in 7onn~c~ion w~lh th~ r~-p~blication of !his repon
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 518-002C
American West Client Sample ID: TW4-03 07272016
ANALYTicAL LABoRATORIEs Collection Date: 7/27/2016 754h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1350h
Units: J!g/L Dilution Factor:
3440 South 700 West
;;att 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
Laboratmy Director
Jose Rocha
QA Officer
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: l ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS Result
17060-07-0 54.4
460-00-4 52.5
1868-53-7 52.9
2037-26-5 51.8
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
50.00 109 72-151
50.00 lOS 80-152
50.00 106 80-124
50.00 104 77-129
Report Date: 8/9/2016 Page 31 of 61
All anD lyses applicnble to the CWA. SDWA, and RCRA are l}erformed in accordance 10 NELAC protocols Pertinent sampling information is located on the altached COC Conlidential Business Information: This report is provided for the exclusi\e use oft he ~ddressee Pri\ile~es o.fsu~seq~enl ~~e of the ~~e of this .col~ puny or M) 1~mber ofils staff, or reproduclio~ ~fthis repo~ in ~~eel ion .. wilh the ::J~vertisement, P~?molio.n or sale of:U~Y ~rod~cl or P~?cess, ~r in ~onn:c~ion w~lh lh~ r:-publication of lhis report
3440 South 700 West
'alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-Jabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 5 18-002
Client Sample ID: TW4-03 07272016
Collection Date: 7/27/2016 754h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
8/J/2016 JSS!h
8/1/2016 175lh
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 26.5
£353.2 0.100 6.10
Report Date: 8/9/20 16 Page 8 of 61
All anal~ ses applicable to the CWA. SDWA. and RCRA rue perfom1ed in accordance 10 NELAC protocols Pertinent sampling information is located on the attached COC Confldentinl Business Information: TI1is report is pro\'ided for the exclusi' e use of the ~ddressce Pri\ ile~es o~ sub~seq~ent ~~e of the ~~1e of this .con~pany or M) ~~~be• of its stall, or reproduclio~ ~f this repo~ in ~on~ection" \\ith the ~\'er1isemenl, P~?motio.n or sale of~!). ~rod~ct or P~?'ess, ~r in <_X>•m:c~ion '''!lh lh~ r~-publicaJion of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax : (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-00IC
Client Sample ID: TW4-03R_07262016
Collection Date: 7/26/2016 1238h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1330h
Units: J.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
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
53.1
51.2
52.6
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 < 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
50.00 102 80-152
50.00 105 80-124
50.00 102 77-129
Report Date: 8/9/2016 Page 30 of61
All nnol) ses applicnble Lo the CWA. SDWA. and RCRA rue perfom1ed in accordance to NELAC protocols Pe1tinent sampling inforn1ation is located on the attached COC. Confictenti~l Business Information: This repor1 is provided for the exclusive use of the ~ddressee p.;, ile~cs o_f sub .. seq~enl ~~e of• the ~~1e or this .cm~pun~ or an~ 1~7mber of its stnff, or reproductio~ ~f I his repo~ in .con~ection .. \"ith the ~vertisement, P~?moli~ ~r sale of ~~y ~rodl~ct or P~?cess, ~r in ~onn~c~ion w~lh lh~ r~-publication of this repor1
3440 South 700 West
)alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-001
Client Sample ID: TW4-03R_07262016
Collection Date: 7/26/2016 1238h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1535h
8/1/2016 1750h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 8/9/2016 Page 7 of 61
All anol~ ses applicable to the CWA, SDWA. and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is located on the au ached COC. Confidential Business Jnfonno.lion: This reporl is provided for I he exdusi\e use oft he ~ddressee Pri' ile~es o,r su~seq~ent ~~e of the ~~1e ofthis.co•~pan) or nH) 1~mber of its staff, or reproductio~ ~[this repo~ in ~on~1ection ... "ilh the a~vertisemenl. p~~motio.n or sale of?J!) ~rod~ct or P•:?cess, ~r in ~onn~c~ion w!th th~ r~·p~IJiication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-014C
Client Sample ID: TW4-04_07252016
Collection Date: 7/25/2016 1445h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1602h
Units: J.lg/L
Compound
Chloroform
Dilution Factor: 50
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
2,760
2,470
2,640
2,490
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/1/2016 1827h
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 50.0 1,380
Amount Spiked %REC Limits Qual
2,500 110 72-151
2,500 98.9 80-152
2,500 105 80-124
2,500 99.8 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 56.2 50.00 112 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.8 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 55.8 50.00 112 80-124
Surr: Toluene-dB 2037-26-5 51.5 50.00 103 77-129
Report Date: 8/9/2016 Page 43 of61
All nnolyses applic~ble to tht! CWA. SDWA. and RCRA we perfomlt!d in accordance to NELAC protocols Pertinent sampling information is located on the auached COC Confidenlinl Business Information: This refJort is proYided for the exclusi\e use of the
~ddressee pJi, ile~es o_f sub .. seq~Jent ~~~e of the ~~1e of this .cm~pany or rul)" ~~~ber of its st(lrf, or reproductio~ ~~this repo~ in ~on~l\!:Ciion .. \\ilh the ll~vertisemenl. p~~moti~n ~r sale of~!) ~rodl~cl or p~ocess, ~r in ~onn~c.tion w~th th~ r!-publication of this r\!:port
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-014
Client Sample ID: TW4-04 07252016
ANALYTICAL LABoRAToRIEs Collection Date: 7/25/2016 1445h
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
Received Date: 7/29/2016 1600h
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
8/1/2016 1913h E300.0 10.0 40.2
8/1/2016 1817h E353.2 0.100 7.22
Report Date: 8/9/2016 Page 20 of61
All anal) ses applicable to the CWA SDWA_ and RCRA are performed in accordance to NELAC protocols. Pe1tinent sampling infonnation is located on the auached COC Confidential Business Information: This report is proyided for the exclusi\e use of the
~ddressee P1iYile~es o_[ sub~seq~enl ~·~e of the ~~1e of this .c01~pany or an) r~_:mbe•· of its staff, or reproductio~ ~r Lhis repo~ in .con~tection~ with the ~vertisemenl, P~?moti~n ~~ sale of ?J!), ~rod~cl or p~ocess, ~r in ~onn:c~ion w~th lh~ r~-publication of this report
American West ANAlYTICAl LABORATORIES
3440 South 700 West
:lalt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-009C
Client Sample ID: TW4-05 08032016
Collection Date: 8/3/2016 908h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1626h
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
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
48.5
48.5
47.8
48.6
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 10.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 97.0 72-151
50.00 97.1 80-152
50.00 95.6 80-124
50.00 97.2 77-129
Report Date: 8/17/2016 Page 33 of 52
All analyses applicnble to the CWA. SDWA and RCRA we performed in accordance to NELAC protocols Pe11inent swnpling Information is located on the attached COC Confidential Business lnformnlion: This repon is provided for lhe exdusiye use oft he
~ddressee Pri\·ile~es ofsub~seq~enl ~~e of the ~~e of this .em~ pony or M) l~mbe•·ofits slafT, or reproduclio~ ~fthis repory in ~con~1ectio~ 'vilh Lhe ll~\ ertisement, P~?motio.n ~r sa1e of~~~ ~rod~ct or P~?Cess, ~r in7onm;.c~ion w!th Lh: r:_·p~blication or Lhis report
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-009
Client Sample ID: TW4-05_08032016
Collection Date: 8/3/2016 908h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1649h E300.0 10.0 44.6
Nitrate/Nitrite (as N) mg/L 8/5/2016 1627h E353.2 0.100 8.49
Report Date: 8/17/20 16 Page 14 of 52
All anal' ses applicable lo the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infonnntion is located on Lhe attached COC Confidential Business Information: This repon is provided for the e:xclusi,·e use of the
~ddressee Pri\ ile~es o_fsub .. seq~ent ~~e of the ~~e of this ,co~pany or any ~mber of its staff, or reproductio~ ~fthis repo~ in ,co~ection .. with the ~vertisemenl. P~?motio.n or saJe of~) ~rod~cl or p~ocess, ~r in ~onn~c!ion w~lh lh~ r~·publication of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-015C
American West Client Sample ID: TW4-06_08042016
ANALYTICAL LAooRATORies Collection Date: 8/4/2016 813h
3440 South 700 West
;;aJt Lake City, UT 84119
Received Date: 8/5/2016
Analytical Results
Analyzed: 8/9/2016 1439h
Units: J.tg/L
Compound
Chloroform
1040h
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 10.0 433
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
Surrogate CAS Result Amount Spiked %REC Limits Qual
~-mail: [e-mail]
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0 546
460-00-4 506
1B6B-53-7 52B
2037-26-5 510
--The reporting limits were raised due to high ana/yte concentrations.
web: www.awal-labs.com Analyzed: 8/8/2016 1826h
Units: J.tg/L
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-dB
Dilution Factor:
CAS Result
17060-07-0 49.9
460-00-4 52.3
1B6B-53-7 50.7
2037-26-5 51.6
500.0 109 72-151
500.0 101 B0-152
500.0 106 B0-124
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.B 72-151
50.00 105 B0-152
50.00 101 B0-124
50.00 103 77-129
Report Date: B/17/20 16 Page 39 of 52
All analyses applicable to the CWA. SDWA. and RCRA rue performed in Hccordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is proYided for I he exclusire use ofthe
~ddressee Pli\ ile~es o: sub ... seq~enl ~l;"e of the ~~e of this .c01~pnny or uny 1~mbe1 of its si:Jff, or reproductio~ ~f this repo~ in ~on~eclion ... \\ith the u~' ertisemenl, P~?motio.n or sale of ~!Y ~rod~cl or p1:ocess, ~r in c;:onn:c~ion w!th th~ r~-publicntion of this repon
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-015
Client Sample ID: TW4-06_08042016
MaLvrlc AL LAaonATOIIIEs Collection Date: 8/4/2016 813h
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: 8/5/2016 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
8/10/2016 1938h E300.0 10.0 42.2
8/5/2016 1646h E353.2 0.100 3.85
Report Date: 8/17/2016 Page 20 of 52
All annl~ ses applicable to I he CW A. SDW A. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC, Confidential Business Information: This repoi1 is pro\'ided for I he exclusi \ e use of the
~ddressee. Pri\ ile~es o_fsub~seq~enl ~?e of the ~~e of this _co~pany or any ~mbe1 of its slaff, or reproductio~ ~fthis repo~ in _con~ eel ion~ with the a~vertisemenL p~omoti~n or sale of?J!~~ ~rod~cl or p~ocess, ~r in ~·m:c!ion w~Lh lh~ r;_-publict~lion of this 1eport
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-017C
American West Client Sample ID: TW4-07_08042016
ANALYTICAL LABORAToRIEs Collection Date: 8/4/2016 825h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/9/2016 1518h
Units: ~-tg/L Dilution Factor: 50
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Compound
Chloroform
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 2,760
460-00-4 2,550
1868-53-7 2,660
2037-26-5 2,510
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/8/2016 1906h
Units: J.lg/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 50.0 1,000
Amount Spiked %REC Limits Qual
2,500 110 72-151
2,500 102 80-152
2,500 106 80-124
2,500 100 77-129
Method: SW8260C
CAS Reporting Analytical Kyle F. Gross 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: I ,2-Dichloroethane-d4 17060-07-0 45.9 50.00 91.9 72-151
Surr: 4-Bromofluorobenzene 460-00-4 48.6 50.00 97.2 80-152
Surr: Dibromofluoromethane 1868-53-7 47.7 50.00 95.4 80-124
Surr: Toluene-d8 2037-26-5 47.9 50.00 95.9 77-129
Report Date: 8/17/2016 Page 41 of 52
All anol~ ses applicable lo I he CWA. SDWA. and RCRA are perJOrrned in accordance Ia NELAC protocols Pe1tinent swnpling information is locuted on the allached COC Confidential Business lnformolion: This 1eport is p1ovided for the exclusive use of the ~ddressee Pri\ ile~es o_fsub ... seq~enl .u~e of the ~~e of this .co11_1pony or M) 1~mbe1 of its staff, or reproductio~ ~f this repo~ in .co1~ection ... with the ~''ertisement, P~?rnolio.n or ~ale of?J!Y ~rod~cl or p1.ocess, ~~·in ~onn~c~ion w!lh 1h7 r~-publication or this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-017
Client Sample ID: TW4-07 08042016
Collection Date: 8/4/2016 825h
Received Date: 8/5/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/10/2016 2013h
8/5/2016 1656h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 42.3
E353.2 0.100 4.21
Report Date: 8/17/2016 Page 22 of 52
All analyses applicable to the CWA SDWA and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on t.he attached COC Confidential Business Information: This report is prm·ided for the exclusi\e use of the
~ddressee. Pri,ile~es o.fsub~seg~ent ~?e of the ~~1e of this .co~pany or any ~mbe1 of its staff, or reproductio.~ ~fthis repo~ in ~on~ection ... \\ilh the a~vertisement, P~?motio.n or sale of~~)· ~rod~cl or p1.ocess, ~r in ~mmt;c~ion ''!Lh th~ r~-publication of this report
Client:
Project:
Lab Sample ID:
ORGANIC ANALYTICAL REPORT
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-016C
Contact: Garrin Palmer
Client Sample ID: TW4-08 08042016
ANAlYTICAl lABORATo111r,e Collection Date: 8/4/2016 819h
3440 South 700 West
;;altLake 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: 8/5/2016
Analytical Results
Analyzed: 8/9/2016 1459h
Units: f.lg/L
Compound
Chloroform
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
1040h
Dilution Factor: 10
CAS Result
I7060-07-0 552
460-00-4 5I7
I868-53-7 534
2037-26-5 506
~-The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/8/2016 1846h
Units: f.lg/L Dilution Factor:
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 10.0 522
Amount Spiked %REC Limits Qual
500.0 110 72-151
500.0 I03 80-I52
500.0 I07 80-I24
500.0 IOI 77-I29
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 I7060-07-0 49.7 50.00 99.4 72-151
Surr: 4-Bromofluorobenzene 460-00-4 52.2 50.00 I04 80-I52
Surr: Dibromofluoromethane I868-53-7 51.0 50.00 102 80-I24
Surr: Toluene-d8 2037-26-5 51.2 50.00 I02 77-129
Report Date: 8/I7 /20 I6 Page 40 of 52
All analyses applicable lo lhe CWA, SDW A. and RCRA rne perl'om1ed in accordance to NELAC protocols Pertinent. sumpling infornmlion is located on t.he allached CDC Conlident.inl Business lnfm motion: This report is pro\'ided for the exclusire use of the
~ddressee Pli\ ile~es of sub .. seq~ent ~~e of the ~:u:ne of this .c01~pany or an) •~mbe• or its starr, or reproductio~ ~fthis repo~ in ,con~ectio~ \\ith the o~vertisement P~?moti~n or sa1e of ?J!~ ~rod~ct or p~ocess, ~r in ~onm~c~ion \\'!lh th~ r~-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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-016
Client Sample ID: TW4-08_08042016
Collection Date: 8/4/2016 819h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg!L 8/10/2016 1955h E300.0 10.0 56.9
Nitrate/Nitrite (as N) mg/L 8/5/2016 1655h E353.2 0.100 2.10
Report Date: 8/17/2016 Page 21 of 52
All anai)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 Jnformation: This reporl is provided for the exclusi' e use of the
~ddressee Pri' ile~es o[sub .. seq~enl ~_:;e of the ~~e of this .co~pany or ffil) 1~mbe1 of ils staff. or reproductio.~ ~fthis repo~ in .co~eclion~ with the ~\ertisement, P~?motio.n or saJe of~~y ~rod~ct or p1;ocess, ?r in ~onn~c~ion w~lh th7 r~-publica1ion of this reporl
American West
ANAI.YTICAL LABORATORIES
3440 South 700 West
;;aJt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-0llC
Client Sample ID: TW4-09 08032016
Collection Date: 8/3/2016 926h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1706h
Units: j.Lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 51.1
Surr: 4-Bromotluorobenzene 460-00-4 52.1
Surr: Dibromotluoromethane 1868-53-7 50.4
Surr: Toluene-d8 2037-26-5 51.0
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 76.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 102 72-151
50.00 104 80-152
50.00 101 80-124
50.00 102 77-129
Report Date: 8/17/2016 Page35 of 52
All analyses applicable lo the CW A. SOW A. and RCRA are performed in accordance to NELAC protocols Pertinent sampling infornmtion is located on the aUached CDC Confidential Business lnformotion: This 1eport is provided for the exclusi' e use oft he
~ddressee. Pri\ ile~es or sub .. seq~Jent ,u~e of the ~~e of this .co~pany or ffil) 1~mbe1" of its slafT, or reproductio~ ~fthis repo~ in .cOI~leclion ... \\ith the tu!' ertisement, p~~motio.n ~r ~ale of :U!Y ~rod~cl or pl:?cess, ~r in ~onn:_c~ion w!th th~ r~-p~blication 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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-011
Client Sample ID: TW4-09 _08032016
Collection Date: 8/3/2016 926h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 172311 £300.0 10.0 33.6
Nitrate/Nitrite (as N) mg/L 8/5/2016 1639h £353.2 0.100 2.11
ReportDate: 8/17/2016 Page16of52
All ann lyses applicuble to the CW A. SDW A. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the atlached COC Confidential Business Jnformalion: This report is provided for the exclush e use of the
~ddressee. Pri' ile~es o: sub~seq~enl ~~e of the ~~e of this .co~pany or an) ~mbe1 of its staff, or reproduclio~ ~f this repo~ in ~o~ection~ with the a~vertisemenl, P~?moti~n or sale of~~). ~rodl~cl or P•.ocess, ~r in ~onn<;_c~ion w!lh th~ r:-publication of lhis report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-018C
American West Client Sample ID: TW4-10_08042016
ANAl vrlcAL LABORATORies Collection Date: 8/4/2016 831h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/9/2016 1538h
Units: j.lg/L Dilution Factor: 50
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
Compound
Chloroform
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS Result
17060-07-0 2,770
460-00-4 2,360
1868-53-7 2,690
2037-26-5 2,530
--The reporting limits were raised due to high analyte concen/ra/ions.
web: www.awal-labs.com Analyzed: 8/8/2016 1926h
Units: j.lg/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 50.0 1,500
Amount Spiked %REC Limits Qual
2,500 Ill 72-151
2,500 94.6 80-152
2,500 108 80-124
2,500 101 77-129
Method: SW8260C
CAS Reporting Analytical Kyle F. Gross
Laboratory Director
Compound Number Limit Result Qual
Jose Rocha
QA Officer
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS Result
17060-07-0 48.8
460-00-4 52.8
1868-53-7 50.7
2037-26-5 51.9
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 97.7 72-151
50.00 106 80-152
50.00 101 80-124
50.00 104 77-129
Report Date: 8/17/2016 Page 42 of 52
All anal) ses applicnble to the CWA~ SDWA. and RCRA (l[e performed in accordance to NELAC protocols Peninent sampling information is locnted on the attached COC Confidential Business Information: This repor1 is prO\ ided for the exclusi\e use of the ~ddressee Pri\ ile~es o.fsub .. seq~enl .u~e oflhe ~~e of this .em~ pony or illl) ~mberofils st:1rT, or reproductio~ ~fthis repo~ in .con~ection .... with then~' er1isement, P~?motio.n ~l"sa1e of~!) ~rod~cl or p1:?cess, ~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
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chlorofonn 2016
1608133-018
Client Sample ID: TW4-10_08042016
CollectionDate: 8/4/2016 831h
Received Date: 8/5/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/10/2016 2030h
8/5/2016 1657h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 85.3
E353.2 0.100 14.9
Report Date: 8/17/2016 Page 23 of 52
All analyses applicable to I he CWA. SDWA.. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located 011the auached COC Confidenriol Business Information: This report is provided for the exclusire use oft he
~ddressee Pri\ ile~es o_f sub ... seq~tenl ~e of lhe ~?'."e of this .co"_lp:my or MY r~;mbe1 of its slaiT, or reproducti~ ~f this repo~ in ~on?ection ... with the a~vertisemelll, l'~?motio.n ~r snJe of~~) ~rodl~CI or p~ocess, ~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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-017C
Client Sample ID: TW4-11_07252016
Collection Date: 7/25/2016 1419h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1703h
Units: J.Lg/L
Compound
Chloroform
Dilution Factor: 50
Surrogate CAS Result
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1B6B-53-7
2037-26-5
2,740
2,490
2,650
2,500
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/l/2016 1927h
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
Number Limit Result Qual
67-66-3 50.0 3,200
Amount Spiked %REC Limits Qual
2,500 110 72-151
2,500 99.7 B0-152
2,500 106 B0-124
2,500 99.9 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: 1 ,2-Dichloroethane-d4 17060-07-0 55.9 50.00 112 72-151
Surr: 4-Bromofluorobenzene 460-00-4 50.5 50.00 101 B0-152
Surr: Dibromofluoromethane 1B6B-53-7 55.3 50.00 111 B0-124
Surr: Toluene-dB 2037-26-5 51.7 50.00 103 77-129
Report Date: B/9/20 16 Page 46 of 61
All analyses applicoble to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is locoted 011the attached COC Confidential Business lnformnlion: This 1eport is proYided fort he e:xclush e use oft he
~ddressee Pri\ ile~es or su~seq~Jenl ~~e oft he ~:u:ne of this .cOI~pany or M~' ~mber of its slafr, or reproducti~ .~r this repm! in ~Oit?eclion ... \\ilh the U~\ ertisement. P~?moti~ 01 s:tle of ?J!Y ~IOdl~Cl or P•,ocess, ~r in 7onn:_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:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-017
Client Sample ID: TW4-ll 07252016
Collection Date: 7/25/2016 1419h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 2004h
8/1/2016 1830h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 55.3
E353.2 0.100 8.83
Report Date: 8/9/2016 Page 23 of 61
All anolyses applicable to the C'WA. SDWA. and RCRA are perfom1ed m accordance to NELAC protocols Pertinent sampling information is located on the altached COC Conlidenlial Business lnformalion: This report is prO\ ided for the exclusi\e use of the
~ddressee Pti\ ile~es o.r sub ... seq~enl ~;e of the ~~1e of this .cot~pony or an) 1~mbe1 of its staff, or reproduclio~ ~f this repo~ in ~on~eclion~ \\il11 I he~' ertisemenl P~?moti~n ':r sale of ~y ~roch~cl or p~ocess, ~r in ~onn~c!ion w!th th~ n;-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:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-003C
Client Sample ID: TW4-12_07272016
Collection Date: 7/27/2016 813h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1410h
Units: J.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 55.1
460-00-4 51.6
1868-53-7 54.0
2037-26-5 51.4
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
50.00 110 72-151
50.00 103 80-152
50.00 108 80-124
50.00 103 77-129
Report Date: 8/9/2016 Page 32 of61
All analyses applicable to I he CWA. SDWA. and RCRA rue performed in accordance to NELAC protocols Pertinent sampling information is located on the all ached COC Confidentiul Business Information: This repon is provided for the exdusi' e use or the
~ddressee Pri\'ile~es o,C sub .. seq~ent ~~e or the ~~e or this .cm~pany or any ~mber or ils stair, or reproductio~ ~~this repo1! in .cm~leclion,.. \\·ith the a~\ ertisement, P~?moli~n ~r sale of ~~Y ~rod~ct or P~?cess, ~r in ~onn~c~ion "~th lh~ r~-p~blicntion or this 1eport
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-003
Client Sample ID: TW4-12_07272016
LABoRAToRIEs Collection Date: 7/27/2016 813h
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: 7/29/2016 1600h
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
8/1/2016 1608h E300.0 10.0 67.5
8/1/2016 1846h E353.2 0.200 37.7
Report Date: 8/9/2016 Page 9 of 61
All anal~ ses applicable to the CWA. SDWA. and RCRAwe performed in accordance to NELAC protocols. Pertinent sampling information is located on Lhe altached COC Confidential Business lnfonnalion: This report is proYided for the exclusiYe use of the
~ddressee Pri' ile~es of' su~seq~enl ~~e of the ~~e of this .cm~pany or an~ 1~mber of its stafT, or reproductio~ ~f this repo~ in ~on~eclion ... \\ilh the a~vertisement. P~?moti~n ~r sa1e of :U~~ ~rodl~ct or p~ocess, ~r in ~onn:_c.tion w!th th~ r:-publicalion or this reporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 841 1 9
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 518-006C
Client Sample ID: TW4-13 07282016
Collection Date: 7/28/2016 807h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1548h
Units: flg/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 54.5
460-00-4 50.8
1868-53-7 52.7
2037-26-5 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
50.00 109 72-151
50.00 102 80-152
50.00 105 80-124
50.00 101 77-129
Report Date: 8/9/2016 Page 3 5 of 61
All annl)·ses applicable to I he CWA, SDWA, and RCRA rue 1Jerfom1ed in accordance Lo NELAC p1olocols Pertinent sumpling information is locnted on the atlnched COC Conlidentlnl Business lnformahon: This repor1 is provided for the exclusi\'e use of the
~ddressee Pri' ile~es o_F sub ... seq~ent ~~e of Lhe ~~e of this .co11_1pany or nny 1~7mbe1· of its stnff, or reproductio~ ~f this repo~ in ~on~u~clion .. with the n~:ertisement. P~?motio.n 0_1 sale of~!) ~rod~ct or p1:ocess, ~r in ~onn~c~ion w~th 1h~ 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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-006
Client Sample ID: TW4-13_07282016
Collection Date: 7/28/2016 807h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1659h
8/1/2016 1756h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 69.3
E353.2 0.100 6.14
Report Date: 8/9/2016 Page 12 of61
All anal~ ses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinenl sampling information is locnted on the attached COC Conridential Business lnfonnation: This report is provided for the excltLsi,·e use of the
~ddressee. P1i' ile~es o,f sub_;eq~ent ~~e of the ~~1e of this .c01~pany or an~ ~mber of ils slnJT, or reproductio~ ~~this repo~ in ~on~eclion .... with the a~:ertisemenl, P~?molio.n or sale of~~. ~rod~cl or pl.ocess, ~r in ;o•m:_c!ion w!th th~ r:_·p~blication of this 1eport
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-006C
Client Sample ID: TW4-14_08032016
Collection Date: 8/3/2016 840h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1527h
Units: J.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 48.4
Surr: 4-Bromofluorobenzene 460-00-4 50.5
Surr: Dibromofluoromethane 1868-53-7 47.5
Surr: Toluene-d8 2037-26-5 48.6
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 5.00
74-87-3 1.00 < 1.00
75-09-2 1.00 1.80
Amount Spiked %REC Limits Qual
50.00 96.9 72-151
50.00 101 80-152
50.00 95.0 80-124
50.00 97.3 77-129
Report Date: 8/17/2016 Page 30 of 52
All anal) ses applicable to the CWA. SDWA. and RCRA nre perforn~d in accordance to NELAC protocols Pertinent swnpling informntio11 is locnted on the altached COC Confidential Business lnformntion: This report is pro\'ided for I he c.\dUSi\e use of the
~ddressee. Pri' ile~es o.r sub ... seq~nl ~·;e or the ~~e of this .cor1_1pnny or M) ·~:mbet' of its staff, or reproductio~ ~f I his repo~ in ~on~1eclion .. nith the a~:ertisemenl, P~?motio.n o.r sale of~~~. ~rod~ct or p1:?Cess, ~r in ~onn~c~ion w~th lh~ r:·publicntion of lhis report
3440 South 700 West
;;a]t 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. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-006
Client Sample ID: TW4-14_08032016
Collection Date: 8/3/2016 840h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1559h E300.0 10.0 42.4
Nitrate/Nitrite (as N) mg/L 8/5/2016 1623h E353.2 0.100 2.88
Report Date: 8/17/2016 Page 11 of 52
All anol~ ses applicJble to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinent sampling informfl.lion is located on the attached COC Confidenlial Business lnfo1mation: This report is provided for the exclusi' e use of the
~ddressee Pri' ile~es o.r sub~seq~enl ~~e of the ~:u;ne of this .cm~pan~ or rul) 1!:~mbe1 of its staff, or reproductio~ ~f lhis repo~ in ~on~ection ... with the a~vertisemenL p~~molio.n 01 sale of~!) ~rod~cl or P~?Cess, ~r in ~rm~c~ion w!th th~ r~·publication of rhis •eport
3440 South 700 West
~alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-016C
Client Sample ID: MW-26_07252016
Collection Date: 7/25/2016 1412h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1643h
Units: J.Lg/L
Compound
Chloroform
Dilution Factor: 50
Surrogate CAS Result
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1868-53-7
2037-26-5
2,800
2,490
2,710
2,560
--The reporting limits were raised due to high analyle concentrations.
Analyzed: 8/1/2016 1907h
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 50.0 3,190
Amount Spiked %REC Limits Qual
2,500 112 72-151
2,500 99.6 80-152
2,500 108 80-124
2,500 103 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 7.81
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: 1 ,2-Dichloroethane-d4 17060-07-0 55.5 50.00 111 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.8 50.00 104 80-152
Surr: Dibromofluoromethane 1868-53-7 54.7 50.00 109 80-124
Surr: Toluene-dB 2037-26-5 51.4 50.00 103 77-129
Report Date: 8/9/2016 Page45 of61
All anol) ses applicnble 10 the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinenl samplin£ informal ion is localed on Lhe attached COC. Conridenlial Business Information: This report is provided for lhe exdusi,·e use of the
~ddressee p.;, ile~es o.f sub .. seq~ent ~1;e of the ~~e of this .c01~pany or M~ ~'!lber of its staff, or reproducti"!! ~!this repo~ in ~01~1ection .. \\~Lh the ll~' ertisemenL, P~?motio.n or sale of ?J!~ ~rodL~ct or p~ocess, ~r in 7onn~c~ion w~th 1h~ r~·publication of this 1epor1
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:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chlorofonn 2016
1607518-016
Client Sample ID: MW-26_07252016
Collection Date: 7/25/2016 1412h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/112016 1947h
8/1/2016 1829h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
£300.0 10.0 66.4
£353.2 0.100 1.57
Report Date: 8/9/2016 Page 22 of61
All anal)ses applicable to the CWA. SDWA. and RCRA rue ~erlOrmed in accordance to NELAC protocols Pe1tinent sampling iuformation is located on Lhe atlached COC Confidential Business lnform<liJOn: This report is prorided for the exdusi\e use of the
~ddressee Pri' ile~es o.f sub~seq~1ent ~~e of the ~~e of this .co1~pru1y or rul) 1~mbe1 of its staff, or reproducti~ ~fthis repo~ in ,cmJ~lection .. \\·ith I he a~"enisemenl, p~omoti~n ~r saJe of~!) ~rodt~ct or P~?cess, ~r in ~onn:c~ion w!th th~ r~-publica.Lion of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-012C
American West Client Sample ID: TW4-16_08032016
AIIALYTi ct.L I.Ao oRATORI Es Collection Date: 8/3/2016 932h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1726h
Units: f.!g/L Dilution Factor:
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
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 48.0
460-00-4 48.2
1868-53-7 47.9
2037-26-5 48.3
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 49.0
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 96.3 80-152
50.00 95.7 80-124
50.00 96.6 77-129
ReportDate: 8/17/2016 Page36of52
All analyses applicuble to the CW A. SDWA. and RCRA nre perfom1ed in accordance to NELAC protocols Pertinent su.mpling information is located on the attached COC Confidentiul Business Jnformalion: This report is pro,•ided for the exclush e use of the
~ddressee Pri\ ile~es o_Fsub .. seq~enl ~;e of the ~~e of this _c01~pnny or M) ~7mber of its st::~ff, or reproductio~ ~~this repo~ in ~on~ection ... \\·ith the a~venisement, P~?moti~n or sale of ~;y ~rodl~«:l or p•;ocess, ~r in 7onm;c~ion \\'~lh 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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-012
Client Sample ID: TW4-16_08032016
Collection Date: 8/3/2016 932h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1740h E300.0 10.0 60.0
Nitrate/Nitrite (as N) mg/L 8/5/2016 1643h E353.2 0.100 2.20
Report Date: 8/17/2016 Page 17 of 52
All anal) ses applicable lo I he CWA. SDW A. and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Conlldentlnl Business Jnformntion: This report is pro\'ided for !he exclusi\ e use oflhe
~ddressee. Pri,·ile~es orsub .. seq~enl ~~e of lhe ~~e of this .co~pany or M) L~mber of its staff, or reproductio~ ~fthis repo~ in .con~eclion~ \\·ilh the a~vertisemenl, P~?moli~n or saJe of?J!). ~rOdl~CI or PL.ocess, ~r in ~onn~c~ion "'!'h th~ r~-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608399-00lC
Client Sample ID: MW-32_08172016
Collection Date: 8/17/2016 1235h
Received Date: 8/19/2016 1 040h
Analytical Results
Analyzed: 8/22/2016 914h
Units: llg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4 17060-07-0 50.0
Surr: 4-Bromofluorobenzene 460-00-4 47.7
Surr: Dibromofluoromethane 1868-53-7 49.8
Surr: Toluene-d8 2037-26-5 48.5
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
50.00 100 72-151
50.00 95.3 80-152
50.00 99.5 80-124
50.00 97.0 77-129
Report Date: 8/26/2016 Page 6 of 15
All anal~ses applicnble to the CWA, SDWA, and RCRA rue perfom1ed in accordance to NELAC protocols Pertment sampling information is located on the attached CDC. Confidential Business lnfonmt1ion: This repor1 is provided fort he exclusi\e use of the
~ddressee pn_, ilel:?es or sub ... seq~enl ~~~e or the ~~le of this .COI~pruly or an) ·~mber of its staff, or reproduclim~ ~fthis repo~ in .con?ection ... wilh I he D~' eltisemenl. p~omolio.n or saJe of ?A!). ~rodL~CI or PI,OCess, ~r in ~rm:c~ion \\ ~lh th~ r:-publication of I his repon
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-1abs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608399-001
Client Sample ID: MW-32_08172016
CollectionDate: 8/17/2016 1235h
Received Date: 8/19/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
8122/2016 1338h
8/19/2016 2017h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
EJOO.O 10.0 37.5
E353.2 0.100 < 0.100
Report Date: 8/26/2016 Page 5 of 15
All an;,lyses applicoble to the CWA. SOW A. and RCRA are perfom1ed in accordance lo NELAC protocols Peninenl sampling information is located on the aUnched COC Confidential Business Information: This 1epon is pro\'ided for the e..xclusi\ e use of the
~ddressee Pri' ile~es o.f su~seq~enl ~e of the ~~eo( this .c01~pany or M) ~mbe1 of its slaff, or reproducti~ ~f this repo~ in ~on~tection~ \\ith the n~\er1isement. P~?moti~n 01 sale of ?'!Y ~todL~cl or p~ocess, ~r in ~~m~~ion w~th th~ r~-publicn1ion of !his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-010C
Client Sample ID: TW4-18 08032016
Collection Date: 8/3/2016 917h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1646h
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-dB
CAS
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
49.6
51.3
49.6
49.8
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 56.3
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 99.3 72-151
50.00 103 80-152
50.00 99.2 80-124
50.00 99.6 77-129
Report Date: 8/17/2016 Page 34 of 52
All onnlyses applicable lo the CWA. SDWA. and RCRA nre perfonned in accordance to NELAC protocols, Pertinent sampling information is located on the allached COC Conlidentinl Business lnformo.lion: This report is pro\•ided for the exdusi\ e use oft he
~ddressee Pri' ile~es o.f sub .. seq~en1 ~~~e of the ~:u,ne of this ~c01~pnny or rut)" 1~mbe1 of its staff, or reproductio~ ~fthis repo~ in ~OI~echon,.. with then~' ertisemenl, p~omotio.n ~r sale of~!~. ~rod~ct or p1.ocess, ~r in 7onn:_c~ion \\'!th lh~ r~-public!.l\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. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-010
Client Sample ID: TW4-18_08032016
Collection Date: 8/3/2016 917h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 170611 E300.0 10.0 40.7
Nitrate/Nitrite (as N) mg!L 8/5/2016 1635h E353.2 0.100 5.79
Report Date: 8/17/2016 Page 15 of 52
All analyses applicable to the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the allached COC Confidential Business lnformation: This report is provided for1he exclusi\e use of the
~ddressee. Pri\ ile~es o.r sub~seq~enl ~~e of the ~?-'."e of this .co~pnny or an~' ~mber of its staff, or reproductio~ ~f this repo~ in ~o~eclion_ with the a~ertise~enl, P~?molio.n ~r sale of :U!) ~rod~cl or pl.?cess, ~r in ~onn:c~ion w~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: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-019C
Client Sample ID: TW4-19 _07252016
Collection Date: 7/25/2016 1500h
Received Date: 7/29/2016 1600h
Analytical Results
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Analyzed: 8/2/2016 1742h
Units: 1-1g/L Dilution Factor: 100 Method: SW8260C
Compound
Chloroform
Surrogate
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 5,520
460-00-4 5,040
1868-53-7 5,370
2037-26-5 5,090
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/1/2016 2006h
Units: 1-1g/L Dilution Factor:
CAS Reporting Analytical
Number Limit Result Qual
67-66-3 100 6,040
Amount Spiked %REC Limits Qual
5,000 110 72-151
5,000 101 80-152
5,000 107 80-124
5,000 102 77-129
Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Carbon tetrachloride 56-23-5 1.00 9.89
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: 1,2-Dichloroethane-d4 17060-07-0 55.2 50.00 110 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.1 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 54.8 50.00 110 80-124
Surr: Toluene-d8 2037-26-5 50.4 50.00 101 77-129
Report Date: 8/9/2016 Page 48 of 61
All analyses applicable to the CWA, SDWA_ and RCRA are performed in accordance to NELAC protocols, Pertinent sampling information is located on the aunched COC. Confidentinl Business Information: This repor1 is provided for the exclusi\ e use of the
~ddressee Pri' ile~es of'sub .... seq~ent ~~e of the ~~e of this .cm~pany or M) J~mbel of its staff, or reproductio~ ?.~this repo~ in ~01~1ection~ \\ilh the o~vertisemenl, p~~motio.n m'sale of~!' ~rodl~l or P~?cess, ~r in ~onn:c~ion \\ ~th th~ r~-publication of this repon
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;;alt Lake City, UT 841 I 9
Phone: [phone]
Toll Free: [phone]
Fax:[phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-019
Client Sample ID: TW4-19 _07252016
Collection Date: 7/25/2016 1500h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 2253h
8/1/2016 1833h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 214
E353.2 0.100 10.5
Report Date: 8/9/2016 Page 25 of 61
All anal) ses applicable to lhe CWA_ SDWA, and RCRA are performed in accordMce to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Busin~ss Information: This repon is provided for the e:xclusi\ e use oft he ~ddressee Pli \ ile~es or su~seq~enl ~?e or the ~~e of this .cOI~pany or anr ~mber of ils staff, or reproducti~ ~f lhis repo~ in ~on~ection~ \\ilh the !1~\'ertisement, P~?motio.n or sale of ?J!~ ~rodL~CI or pl:ocess, ~r in ~onn:c.lion \\'~lh th~ r:-publication or I his report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-021C
Client Sample ID: TW4-20_07252016
Collection Date: 7/25/2016 1404h
Received Date: 7/29/2016 1600h
Analytical Results
Test Code: 8260-W-DEN100
VOAs by GC/MS Method 8260C/5030C
Analyzed: 8/3/2016 2033h
Units: J.lg/L
Compound
Chloroform
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Dilution Factor: 1000 Method:
CAS Reporting
Number Limit
67-66-3 1,000
CAS Result Amount Spiked %REC
17060-07-0 49,600 50,000 99.2
460-00-4 50,600 50,000 101
1868-53-7 50,200 50,000 100
2037-26-5 50,600 50,000 101
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/2/2016 1842h
Units: J.lg/L Dilution Factor: Method:
CAS Reporting
Compound Number Limit
Carbon tetrachloride 56-23-5 1.00
Chloromethane 74-87-3 1.00
Methylene chloride 75-09-2 1.00
Surrogate CAS Result Amount Spiked %REC
Surr: I ,2-Dichloroethane-d4 17060-07-0 54.2 50.00 108
Surr: 4-Bromofluorobenzene 460-00-4 49.1 50.00 98.1
Surr: Dibromofluoromethane 1868-53-7 53.8 50.00 108
Surr: Toluene-d8 2037-26-5 50.6 50.00 101
SW8260C
Analytical
Result Qual
23,600
Limits Qual
72-151
80-152
80-124
77-129
SW8260C
Analytical
Result Qual
26.6
< 1.00
< 1.00
Limits Qual
72-J51
80-152
80-124
77-129
Report Date: 8/9/2016 Page 50 of61
All anal) ses applicable to !he CWA. SDWA. and RCRA are performed in accordance to NELAC p1otocols. Pe11inent sampling information is located on the attached COC Confidential Business lnformalion: This repor1 is provided fort he exclusi\e use oft he
~ddressee P•i,·iJe~es o_fsub .. seq~enl ~~~e of the ~~ne or I his .co1~pany or nny 1~mber or its starr, or reproductio~ ~r this repo~ in ~on~ection ... with the a~venise~enL, P~?motio.n ~r sale or~~~~ ~rodl~CL or p~~ss, ~r in ~nn:c~ion w~th th~ r~-p~blicalion of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: [phone]
!-mail: [e-mail]
web: www.awal-1abs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-021
Client Sample ID: TW4-20_07252016
Collection Date: 7/25/2016 1404h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 2326h
8/1/2016 1835h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 307
E353.2 0.100 11.3
Report Date: 8/9/2016 Page 27 of61
All an~ lyses applicable to the CWA. SOW A, and RCRA are perfomted in accordance to NELAC protocols Pertinent sampling information is locoted on the aU.:u.:hed COC Confidential Business Information: This 1eport is prO\'ided for the e.~clusi' e use of the
~ddressee Pri\ ile~es o~ sub~seq~nt ~~e oflhe ~~1e of this .co1~pany or an) 1~mber of its stnff, or reproductio~ ~f this repo~ in ~o~ection~ with the !1~\ ertise~ent, p~~motio.n ~~ sale of~~) ~IOd\~cl or p1.ocess, ~r in ~onn~~ion w~lh th~ r:_-publication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-011C
Client Sample ID: TW4-21_07252016
Collection Date: 7/25/2016 1320h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1423h
Units: ~giL Dilution Factor: 10
Compound
Chloroform
Surrogate
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
CAS Result
17060-07-0 529
460-00-4 483
1868-53-7 524
2037-26-5 496
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/1/2016 1728h
Units: ~giL 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 10.0 456
Amount Spiked %REC Limits Qual
500.0 106 72-151
500.0 96.6 80-152
500.0 105 80-124
500.0 99.3 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: 1,2-Dichloroethane-d4 17060-07-0 55.6 50.00 Ill 72-151
Surr: 4-Bromofluorobenzene 460-00-4 51.0 50.00 102 80-152
Surr: Dibromofluoromethane 1868-53-7 54.8 50.00 110 80-124
Surr: Toluene-d8 2037-26-5 50.9 50.00 102 77-129
Report Date: 8/9/20 16 Page 40 of 61
All annl~ ses applicable to the CWA. SDWA_ and RCRA are performed in accordance 10 NELAC protocols Pe1tinent sampling mformation is located on the attached COC Conlldentinl Business Information: This repon is provided for the excl~1sh·e use oft he
~ddressee Pri,·ile~es o.r su~seq~enl ~~e of the ~~e of this .coJ~pany or rnl) ~~~';lbe1 of its staff, or reproduclio~ ~f this repo~ in .con~1ection .. with the n~~ eHisement, P~?moti~n ~r ~ale of~!) .~rodl~cl or p1:?cess, ~tin ~onn:c~ion \\ !th th~ r~-p~blication of this 1eport
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
LabSampleiD: 1607518-011
Client Sample ID: TW4-21_07252016
Collection Date: 7/25/2016 1320h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
8/1/2016 1410h
8/1/2016 18llh
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 457
E353.2 0.100 16.5
Report Date: 8/9/2016 Page 17 of61
All anal~ ses applicable to the CWA. SDWA. and RCRA we perfonned in accordance to NELAC protocols, Pertinent sampling informa..Lion is located on the allached COC Confidential Business Information: l11is 1eport is pro\ ided for the exclusi\ e use of1he ~ddressee Pri\ ile~es o.r sub .. seq~enl ~~~e of the ~~e of this .cm~pany or nn~· J~mbet of its stniT, or reproductio~ ~r this repo~ in ~on~ecl!on .. \\ilh lhe a~\'eJtisemenL p~omotio,n ~r saJe of~!~ ~1odt~cl or P':?cess, ?r in ~onn:,c~ion w!lh th~ r~-p~blicalion of this 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
Laboratmy Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-018C
Client Sample ID: TW4-22_07252016
Collection Date: 7/25/2016 1350h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1722h
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Units: J.lg/L Dilution Factor: 100 Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 100 5,840
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4 17060-07-0 5,620 5,000 112 72-151
Surr: 4-Bromofluorobenzene 460-00-4 5,110 5,000 102 80-152
Surr: Dibromofluoromethane 1868-53-7 5,470 5,000 109 80-124
Surr: Toluene-d8 2037-26-5 5,120 5,000 102 77-129
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/1/2016 1947h
Units: J.lg/L Dilution Factor: 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 51.8 50.00 104 72-151
Surr: 4-Bromofluorobenzene 460-00-4 46.1 50.00 92.2 80-152
Surr: Dibromofluoromethane 1868-53-7 51.0 50.00 102 80-124
Surr: Toluene-d8 2037-26-5 47.9 50.00 95.9 77-129
Report Date: 8/9/2016 Page 47 of61
All analyses applicable to the CWA_ SDWA_ and RCRA are perfonned in accordance to NELAC protocols. Pertinent samplin,g information is located on the attached COC Conlidentiul Business lnfonnnhon: This report is proYided for the e:xclush e use oft he
~ddressee P1i' ile~es oF sub~seq~ent ~~e of the ~~1e or this .cot~pruly or nnr t~mbet of its starr, or reproductio~ ~r this repo~ in ~01~1ectionr "ith the a~~ ertisement, P~?motio.n ~~·sale of ~!Y ~rodl~ct or pt.ocess, ?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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-018
Client Sample ID: TW4-22_07252016
Collection Date: 7/25/2016 1350h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 2202h
8/1/2016 1849h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 619
E353.2 0.500 61.3
Report Date: 8/9/2016 Page 24 of 61
All anal) 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 Infonnotion: This report is provided for1he exclusire use of the
~ddressee P1i\ ile~es or sub,..seq~ent ~~~e of the ~~e of this .cm~pany or anr ~mbe1 of its staff, or reproductio~ ~f this repo~ in ~~ection~ "il11 the a~\ ertisemenl, P~?motio.n ~r sale of ?J!Y ~rodl~CL or p~ocess, ~r in ~onn:c~ion w~th 1h7 r~-publicalion of I his report
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-004C
Client Sample ID: TW4-23_08032016
Collection Date: 8/3/2016 823h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1447h
Units: IJ.g/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 49.3
460-00-4 48.2
1868-53-7 47.2
2037-26-5 48.6
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 98.6 72-151
50.00 96.4 80-152
50.00 94.3 80-124
50.00 97.3 77-129
Report Date: 8/17/2016 Page 28 of 52
All anal~ ses applicoble to the CW A. SDWA. and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is Jocnted on the auached COC Confidentinl Business lnfonnution: This 1epor1 is provided for the exclusi\ e use of1he
~ddressee. Pri,~ite~es o.r sub .. seq~ent ~~~e of the ~~e of this .cm~pany or M) 1~1?ber of its stall, or reproduclio~ ~f this repo~ in ~OI~ection ... \\·ith the o~''ertisel~ent, P~?molio.n ~r ~ale of ~l} ~rodl~CI or p1.ocess, ~r in ~nn~c!ion 1\'~lh 1h~ r~·publicDJiOil of I his report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-004
Client Sample ID: TW4-23_08032016
LABORAToRIEs Collection Date: 8/3/2016 823h
3440 South 700 West
'alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 l) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Received Date: 8/5/2016 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
8/10/2016 1418h E300.0 10.0 49.6
8/5/2016 162lh E353.2 0.100 < 0.100
Report Date: 8/17/2016 Page 9 of 52
All analyses applicnble to the CWA. SDWAc and RCRA are perfom1ed m accordance to NELAC protocols Peninent sampling information is Jocuted on the attached COC Confidential Business lnformulion: This repor1 is provided for the exclusi\e use of the
~ddressee Pri\ ile~es o:sub__seq~nl ~~e of the ~~e ofthis.cOI~pany or M) ~~ber of its stiliT, or reproduclio.~ ~fthis repo~ in ~o~ec1i01~ with the u~vertisement, P~?motio.n or sale or~!~ ~rodl~CI or P•.ocess, ~r in ~nn:c~ion w~th th~ r~·publicaJ.ion 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-0lOC
Client Sample ID: TW4-24_07252016
Collection Date: 7/25/2016 134lh
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/112016 1708h
Units: flg/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 55.3
460-00-4 50.6
1868-53-7 53.6
2037-26-5 51.5
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 17.8
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 111 72-151
50.00 101 80-152
50.00 107 80-124
50.00 103 77-129
Report Date: 8/9/2016 Page 39 of61
All anolyses applicable to the CWA. SDWA. and RCRA are perfonned in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidentlnl Business Information: This report is prm•ided for the exclusi,·e use of the ~ddressee P1i' ile~es o.r sub ... seq~ent ~~e of the ~~1e of this.cOI~pany or an) ~mber of its stotff. or reproductio~ ~f this repo~ in ~ot~lection ... with the n~vertisemenl, P~?motio.n or sale of :U~) ~~ odl~cl or P':?cess, ~r in ~onn~c~ion w!th th: r~-publication of this 1-eport
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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chlorofonn 2016
Lab Sample ID: 1607518-010
Client Sample ID: TW4-24_07252016
Collection Date: 7/25/2016 1341h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1320h
8/1/2016 1848h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 1,180
E353.2 0.500 34.4
Report Date: 8/9/2016 Page 16 of61
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 Confidential Business lnfonnation: This repon is pro,ided for 1he exclusi' e use of the
~ddressee Pri\ ile~es o_f sub~seg~enl ~~e of the ~~e of this _co1~pany or any 1~mbe1 of its slniT, or reproductio~ ~fthis repo~ in _con~lection .. \\ilh the a~vertisemenL P~?motio_n ~r sale of~~~. ~rodL~I or P~?<=ess, ~r in ~onn:_c~i011 w~lh 1h: r~-p~blicalion of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: l607518-009C
Client Sample ID: TW4-25_07252016
Collection Date: 7/25/2016 1326h
Received Date: 7/29/2016 l600h
Analytical Results
Analyzed: 8/l/2016 1648h
Units: flg/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
54.6
49.1
52.8
49.7
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
50.00 109 72-151
50.00 98.2 80-152
50.00 106 80-124
50.00 99.4 77-129
Report Date: 8/9/2016 Page 38 of61
All analyses applicable to the CWA, SDWA. and RCRA n1e performed in accordam;:e to NELAC protocols Peninent samplins information is located on the attached COC Confidential Business Information: This repon is provided for the exch1si\ e use oft he
~ddressee Pri\ ile~es o_fsu~seq~ent ~~~e of the ~~e of this .coi~PilllY or M) ·~mber of its st~rr. or reproducti~ ~r this repo~ in ~Oll~lection, \Vi th the~~ ertisemenl, P~?motio.n ~r sale of ?J!) rrod~t or PJ.ocess, ~r in ~onm;c~iOJ\ w~th th~ r;_-publication or this report
ANAlYTICAl lABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607 518-009
Client Sample ID: TW4-25 07252016
Collection Date: 7/25/2016 1326h
Received Date: 7/29/2016 1600h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/1/2016 174911 E300.0 10.0 74.1
Nitrate/Nitrite (as N) mg/L 8/1/2016 175911 E353.2 0.100 1.78 '@
@-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.
Report Date: 8/9/2016 Page 15 of61
All anal~ ses applicable to the CWA. SDWA. and RCRA me performed in accordance to NELAC protocols Per1inenl sampling infommtion is located on Lhe attached COC Confidential Business Information: This report is provided for the exchL'ihe use of the
~ddressee Pli\ ile~es or sub.seq~ent .u~e of the ~~e or this .col~prnl~ or anr ~mbel of its stall, or reproductio~~ ~~this repo~ in .con~leclion~ with the a~vertisemenl, p~omotio.n ~r saJe of ?J!_)_ ~rodt~CI or P:_?Cess, ~r in ~onn;.c!ion w!th 1h~ r:-publicalioll 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
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-008C
Client Sample ID: TW4-26_08032016
Collection Date: 8/3/2016 900h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1606h
Units: ~-tg/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
49.7
49.1
48.2
49.3
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 4.42
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 99.3 72-151
50.00 98.2 80-152
50.00 96.4 80-124
50.00 98.5 77-129
Report Date: 8/17/2016 Page 32 of 52
All an31) ses applicoble to the CW A. SDWA. and RCRA are perfonned in accordance to NELAC protocols. Perlinent sampling information is located on Lhe aU ached COC Conlidentlul Business lnformu1ion: This repon is provided for the exclush·e use of the
~ddressee p.;, ile¥es or sub .. seq~ent ~·~e of the ~?'."e of this .col~ pony or nny r~:mbel of its stnff, or reproductio~ ~f this repo~ in .con~ection_ \\ith the u~vertisement, p~omotio.n or sale of ?J-2_) ~ rrod~cl or p!:_ocess, ~r in ~onn:.c!ion \\'!th th~ r:_·publicntion of this repor1
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-008
Client Sample ID: TW4-26 08032016
Collection Date: 8/3/2016 900h
Received Date: 8/5/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/16/2016 1921h
8/5/2016 1626h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 13.9
E353.2 0.100 17.9
Report Date: 8/17/2016 Page 13 of 52
All analyses applicable to the CW A. SDWA. and RCRA are perfo1111ed in accordance to NELAC protocols, Pertinent sampling information is located on the at1e~ched COC Conlidential Business Jnformalion: This report is provided for the exclusi' e use oft he
~ddressee Pri\ile~es ofsub ... seq~ent ~~e of the ~~e of this .con;pany or any ~mbe1 of its staff, or reproductio~~ ~fthis repo~ in .con~ection ... with the a~vertiset~enl, p~omotio,n ~r sale of?J_!) ~rod~cl or pt:?cess, ~r in :onn:_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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-005C
Client Sample ID: TW4-27 _08032016
Collection Date: 8/3/2016 834h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1507h
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 Result
17060-07-0 48.2
460-00-4 49.2
1868-53-7 46.9
2037-26-5 47.6
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 2.78
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 98.3 80-152
50.00 93.8 80-124
50.00 95.2 77-129
Report Date: 8/17/2016 Page 29 of 52
All annl) ses applicable lo the CW A. SDWA. and RCRA are perfom1ed 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_f sub ... seq~ent ~;-e of the ~:u,ne of this .co~pnny or M) ~~~her of its si31T, or reproductio~ ~~this repo~ in ,con~ection~ with the n~: er1isemenl, P~?moti~n o_r sale of :U!) ~rodt~cl or p1.ocess, ~r in ~onn: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. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-005
Client Sample ID: TW4-27_08032016
Collection Date: 8/3/2016 834h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1435h E300.0 10.0 27.1
Nitrate/Nitrite (as N) mg/L 8/5/2016 1659h E353.2 0.200 21.8
Report Date: 8/17/2016 Page I 0 of 52
All analyses applicable 10 the CWA. SDWA. and RCRA are perfom1ed in ~ccordwn:e to NELAC protocols Pertinent smnpling information is locnled on tJ1e au ached COC Conf1denlinl Business Information: This report is pro,•ided for the exclusi' e use of the
~ddressee Pri\ ile~es o.r su~seq~Jenl ~~~e of the ~~e of this .co1~prmy or M) ~mber of ils slaff, or reproductio!~ ~fthis repo~ in ~01~1ection ... "~lh the a~~er1isemenL P~?molio.n ~r sale of ?JlY ~rod1~cl or PI,?Cess, ~r i11 ~onn~~ion \\'~lh lh~ r~-p~blicotion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;a It Lake City, UT 841 19
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 518-004C
Client Sample ID: TW4-28 07272016
Collection Date: 7/27/2016 820h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1509h
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 54.2
460-00-4 51.6
1868-53-7 52.3
2037-26-5 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
50.00 108 72-151
50.00 103 80-152
50.00 105 80-124
50.00 103 77-129
Report Date: 8/9/2016 Page 33 of 61
All annl)ses applicnble to the C'W A. SOW A. and RCRA are performed in accordance to NELAC protocols, Per1inent sampling information is located on the attr~ched COC Confidential Business lnfonnulion: This 1eport is provided for the exclusi\ e use oft he
~ddressee p.;, ile~es o.r sub .. seq~ent ~~e of the ~~e of this .c01~pany or any ~mber of its staff, or reproductio~ ~~this repo~ in ~OJ~lection~ \\~lh the ll~' ertiser~enl, P~?motio.n ~r sale of :U!~ ~· odl~cl or P~?cess, ?r in ~nn~c~ion w!th th~ r:_-publication of this reporl
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 518-004
Client Sample ID: TW4-28 07272016
Collection Date: 7/27/2016 820h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1625h
811/2016 1847h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 70.1
E353.2 0.200 31.3
Report Date: 8/9/2016 Page 10 of61
All anal) ses applicable to the CWA. SDW A. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COC Conflden11al Business Information: This reporl is provided for the exclusi\"e use of the
~ddressee Pri\ ile~es o: sub~seq~tent ~~e of the ~:u:'1e ofth1s .cot~pany or any J~mber of its staff, or reproductio.~ ~!this repo~ in .con~ectio~ \\ilh the at!' ertisemenL p:omotio.n ~r saJe of~~ ~rodl~cl or pt.ocess, ~r in 7onn:c!ion w~lh th~ n;-publication of this report
ORGANIC ANALYTICAL REPORT
3440 South 700 West
;a!t Lake City, UT 84119
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-014C
Client Sample ID: TW4-29 _08042016
Collection Date: 8/4/2016 805h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/9/2016 1339h
Units: J.lg/L
Compound
Chloroform
Dilution Factor: 10
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 10.0 401
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
Surrogate CAS Result Amount Spiked %REC Limits Qual
~-mail: [e-mail]
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
17060-07-0
460-00-4
1B6B-53-7
2037-26-5
54B
496
536
509
--The reporting limits were raised due to high ana/yte concentrations.
web: www.awal-labs.com Analyzed: 8/8/2016 1806h
U nits: J.lg/L
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Dilution Factor:
CAS Result
17060-07-0 46.0
460-00-4 46.9
1B6B-53-7 47.1
2037-26-5 47.1
500.0 110 72-151
500.0 99.3 B0-152
500.0 107 B0-124
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 92.0 72-151
50.00 93.9 B0-152
50.00 94.1 B0-124
50.00 94.2 77-129
Report Date: B/17/2016 Page3B of 52
All analyses applicoble to the CWA. SDWA, and RCRA !lfe perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the all ached COC Confidentiul Business Information: This report is provided for the exdusi\ e use of the
~ddressee Pri\ ile~es o.fsub ... seq~tenl ~~~e of the ~:u:ne of this .cot~pnny or nn~ J~'!lber of its staff, or reproductio.~ ~~this repo~ in ~on~lection .. \\·ith the a~; ertise"?enl, P~?motio.n ~~ ~aJe of~!). ~1od~ct or p1:?cess, ~r in c;onn;c~ion w!th th~ r~-publicnlion of this report
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-014
Client Sample ID: TW4-29 _08042016
Collection Date: 8/4/2016 805h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1921h E300.0 10.0 40.6
Nitrate/Nitrite (as N) mg/L 8/5/2016 1645h E353.2 0.100 2.44
Report Date: 8/17/2016 Page 19 of 52
All analyses applicable to the CWA. SDWA. and RCRA rue perfom1ed in accordance to NELAC protocols Pertinent sampling information is Jocuted on the all ached COC Confidential Business [nfornmtion: This report is provided for the cxclusi\e use of the
~ddressee Prh i\e~es of sub,.seq~•enl ~1?e of the ~~e of this .cm~pany or nn) r~;mbe1 of its staff, or reproductio~ ~f this repm; in .con~ection ... \\ilh the a~vertisement, P~?motio.n or saJe of ~!Y ~rod~t::L or p~ocess, ~r in ~nn:c~ion \\'~lh 1h~ n~-publication of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-007C
American West Client Sample ID: TW4-30_08032016
ANALYTICAl LABoRAToRIEs Collection Date: 8/3/2016 850h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1546h
Units: ~g/L Dilution Factor:
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
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
CAS Result
17060-07-0 49.6
460-00-4 51.5
1868-53-7 48.0
2037-26-5 49.1
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 6.79
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 99.2 72-151
50.00 103 80-152
50.00 96.1 80-124
50.00 98.3 77-129
Report Date: 8117/2016 Page 31 of 52
All :mnlyses applicnble to the CWA. SOW A. and RCRA are perfom..ed in ru:cordance to NELAC protocols Pertinent sampling information is located on lhe aU ached CDC Confidential Business Jnformalion: This 1eport is provided for the exclusiYe use of the
~ddressee Pri.\ ile~es o,f sub ... seq~Jenl ~~~e or the ~~e or this .c011.lpany or M)' t~'!lbe1 of its staff, or reproductio~ ~fthis repo~ in .con~ection,. '"ith the ~vertisemenl, P~?nlolio.n or sale of~~) ~· odl~CI or pl.ocess, ~r in ~nnc:_c~ion w~lh lh~ 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. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-007
Client Sample ID: TW4-30_08032016
Collection Date: 8/3/2016 850h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1616h E300.0 10.0 38.6
Nitrate/Nitrite (as N) mg/L 8/5/2016 1625h E353.2 0.100 2.32
Report Date: 8/17/2016 Page 12 of 52
All analyses 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 Information: This report is pro\'ided for the exclusive use of the
~ddressee Pri' ile~es o! sub,_seq!tenl ~~~e of the ~~1e o[ this ,con;pany or any ~~~mber of its staJT, or reproductim~ ~f this repo~ in ~on~ eel ion_ with the a~\'ertisement, p~omotio.n ~r sale of~~). ~rod~cl or p~ocess, ~r in ~onn:_c!ion w!1h th~ n~-publicalion of this report
3440 South 700 West
:lalt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 20 I 6
Lab Sample ID: 1607518-008C
Client Sample ID: TW4-31_07282016
Collection Date: 7/28/2016 819h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 811/2016 1628h
Units: J.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 55.6
460-00-4 50.6
1868-53-7 53.4
2037-26-5 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 Ill 72-151
50.00 101 80-152
50.00 107 80-124
50.00 100 77-129
Report Date: 8/9/2016 Page 37 of61
All nnulyses applicnble to the CWA. SDWA. and RCRA are perfomu~d in accordance to NELAC protocols Pertinent sampling infornuuion is located on the al1ached COC Confidential Business lnfonnation: This 1eport is provided for the exclusi\ e use of the
~ddressee Pri' ile~es o_fsub .. seq~enl .u~e of' the ~~1e of this _cm~pntly or nny ~~~bet ofils stnff, or reproductio~ ~fthis repo~ in ~n~ection .. \\ilh lhe a~vertisement, P~?motio.n or sale of~~ ~rodL~cl or p1.ocess, ~r in ~nm;_c~ion '''~lh lh~ 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: 3rd Quarter Chlorofonn 2016
Lab Sample ID: 1607518-008
Client Sample ID: TW4-31_07282016
Collection Date: 7/28/2016 819h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/112016 1732h
8/1/2016 1758h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 30.6
E353.2 0.100 1.41
Report Date: 8/9/2016 Page 14 of 61
All anolyses applico.ble to the CW A. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling i11formntion is located 011 the au ached COC Conlidential Business Information: This report is prO\ ided for the e:\:clusiYe use of the
~ddressee Pli\ ile~es or sub ... seq~enl ~~e of the ~~e of this .co!~pn.ny or any ~mber of its stnlT, or reproducti~ ~f this repo~ in ~on~1ection~ with the ~vertisemenl. P~?motio_n or saJe of~;) ~~ odi~l or Pl.ocess, ~r in ~nn~c~ion w~lh lh~ n;_-publicnlion of this 1eport
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
Laborat01y Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-005C
Client Sample ID: TW4-32 07282016
Collection Date: 7/28/2016 800h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1529h
Units: f.lg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate
Surr: 1 ,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
55.7
51.8
53.5
51.6
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
50.00 111 72-151
50.00 104 80-152
50.00 107 80-124
50.00 103 77-129
Report Date: 8/9/2016 Page 34 of61
All anolyses applicable to the CWA. SDWA. and RCRA rue performed in accordance to NELAC protocols. Pe1tinent sampling information is located on the attached COC. Confidential Business lnfonnalion: This repon is prm ided for the exclusi'e use oft he
~ddressee Pri' ile~es of sub,..seq~ent ~~~e of the ~~e of this .co1~pany or an) •~mber of its staff, or reproductio~ ~fthis repo~ in .con~tection ... "ith the u~\ erlisement. P~?motio.n ~r sale of ~!Y. ~·odl~cl or P•;ocess, ~r in 7onn~c~ion w!th th~ r:-publication of this repor1
American West
ANALYTICAL LADORATORIE6
3440 South 700 West
;;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-005
Client Sample ID: TW4-32_07282016
Collection Date: 7/28/2016 800h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) rng/L
Date
Analyzed
8/1/2016 1642h
8/1/2016 1754h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 64.4
E353.2 0.100 3.44
Report Date: 8/9/20 16 Page II of 61
All annlyses applicoble to the CWA, SDWA. and RCRA me perfOm1ed in accordance to NELAC protocols Pertinent sampling inromuu..ion is located on the nltnched COC Confidential Business Information: This reporl is prm ided for1he e:xclusi\ e use of the
~ddressee Pri\ ile~es a: su~seq~enl ~~~e or the ~~ne of this .cot~pany or any ~~~her of its stnlT, or reproductio~ ~~this repo~ in ~~eclion~ \Vilh the a~' ertisemenl, P~?motio.n ~r sale of~~), ~rod~cl or p~ocess, ~r in ~onn:c!ion \\'~lh th~ n~:-publicaJion of this reporl
American West ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-013C
Client Sample ID: TW4-33_08042016
Collection Date: 8/4/2016 758h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1746h
Units: J.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
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
51.1
51.2
50.8
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 1.00 121
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 102 72-151
50.00 102 80-152
50.00 102 80-124
50.00 103 77-129
Report Date: 8/17/2016 Page 37 of 52
All ann!~ ses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the aU ached CDC Confidential Business Information: This report is pro\'ided for1he exclusi' e use of the
~ddressee Prh ile~es o_fsub .. seq~Jenl ~·?e of lhe ~~e of this .cot~pany or nn) 1~7mbel of its stall, or reproductio~ ~fthis repm; in ~on~1ection,.. with 1he ~' ertisement. P~?rnotio.n or sale of :U!) ~rod~cl or p1:ocess, ~r in ~onn:c~ion w!th lh~ r~-p~blication of this report
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-013
Client Sample ID: TW4-33_08042016
~~~A LVTIC A L LAaonATon H& Collection Date: 8/4/2016 758h
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: 8/5/2016 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
8/10/2016 1757h £300.0 10.0 48.5
8/5/2016 1644h E353.2 0.100 2.32
Report Date: 8/17/2016 Page 18 of 52
All anal~ ses applicoble to I he CW A. SDWA. and RCRA rue perfom1ed in accordance to NELAC protocols Pertinent sDmpling information is located on the attached COC Confidential Business Information: This repor1 is proyided for lhe exclusi\ e use of the
~ddressee Pri' ile~es or sub~seq~ent ~~~e of the ~~1e of this .cm~pany or M) 1~mber of its stafT. or reproduclio!~ ~f this repo~ in .con~eclion~ with the a~;·ertisemenl, P~?molio.n o.r sale of ~!Y ~rod~cl or p1.ocess, ~r in ~onn~c~io11 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: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-002C
Client Sample ID: TW4-34_08032016
Collection Date: 8/3/2016 807h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1327h
Units: J.tg/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 51.4
460-00-4 50.0
1868-53-7 49.8
2037-26-5 50.8
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
50.00 100 80-152
50.00 99.5 80-124
50.00 102 77-129
Report Date: 8/17/2016 Page 26 of 52
All ann lyses applicable to the CWA. SDWA, and RCRA are performed in accordance 1o NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business lnfonnalion: l11is report is provided for the exclusi\ e use oft he
~ddressee P1i' ile~es o.r sub ... seq~enl ~~e of the ~~e of this .co1~pany or illl) J~'!lbe1' of its slaff, or reproduclio~ ~f this repo~ in ~on~eclion_. with the n~''ertisemenl, p~~motio.n or sale of~~~ ~rod~ct or pl.ocess, ?r in ~nn~c~ion w!lh lh~ n;-publication of lhis report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;aJt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-002
Client Sample ID: TW4-34_08032016
Collection Date: 8/3/2016 807h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1344h E300.0 10.0 17.2
Nitrate/Nitrite (as N) mg/L 8/5/2016 1616h E353.2 0.100 0.726
Report Date: 8/17/2016 Page 7 of 52
All analyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Pertinenl sampling information is located on the altached COC Confidenliul Business lnfmmalion: This report is provided for the excll.L'>i\ e use oft he
~ddressee. Pri' ile~es a: sub,..seq~enl ~~e oflhe ~~e of lhis .con;pany or nil) 1~mbe1 of its staff, or reproduclio~ ~fthis repo~ in .co~eclion,.. \Vith the a~:enisement. P~?moli~n ':r sale of~~): ~rod~cl or P~?cess, ~r in ~01m~c~ion w!lh th~ n;_-p~blicatlon of this report
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-001C
American West Client Sample ID: TW4-34R_08022016
ANALYTICAL LABoRATORIEs Collection Date: 8/2/2016 725h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1308h
Units: Jlg/L Dilution Factor:
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
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 51.4
460-00-4 52.6
1868-53-7 48.9
2037-26-5 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 < 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
50.00 105 80-152
50.00 97.8 80-124
50.00 102 77-129
Report Date: 8/17/2016 Page 25 of 52
All analyses appliCDble to the CWA, SDW A.. and RCRA are perfom1ed in accordance to NELAC protocols, Per1inenl sampling information is located on the attached COC Conlidential Business Jnformalion: This report is provided for the e'<clnsi\·e use of the
~ddressee P1i\ ile~es o_fsub ... seq~enl ~?e of the ~~e of lhis .co",lpany or nn~ 1~mber ofils slnrf, or reproductio.~ ~fthis repo~ in ;o~eclion. with the ll~''ertisement. p~omolio.n o.r sale of~;) ~rod~ct or p~ocess, ?r in ~onn:c!ion w!th th: r~-publication of this report
3440 South 700 West
:lalt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-001
Client Sample ID: TW4-34R_08022016
Collection Date: 8/2/2016 725h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg!L 8/11/2016 736h E300.0 1.00 < 1.00
Nitrate/Nitrite (as N) mg!L 8/5/2016 1608h E353.2 0.100 <0.100
Report Date: 8/17/2016 Page 6 of 52
All analyses applict~ble to the CWA, SDWA_ and RCRA are performed in accordance to NELAC protocols Per1inent sampling information is located on the allached COC Confidential Business lnfonnntion: This report is provided for the exdusi'e use of the
~ddressee Pri' ile~es o;sub .. seq~ent ~~e of the ~~e of this .co1~1pnuy or an) ~~~mbe1 of its staff, or reproductio~ ~[this repo~ in ~n~tecliOJ~ \\ilh the n~vertisemenl, P~?motio.n '!r sale of~~ ~rod~t or P~?Cess, ~r in ~nn~~io11 w~lh th~ r~-p~blication of this repor1
American West
ANALYTICAL LABORATORIES
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: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-003C
Client Sample ID: TW4-35_08032016
Collection Date: 8/3/2016 814h
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1347h
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 48.3
460-00-4 49.0
1868-53-7 46.0
2037-26-5 47.4
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 < 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 98.1 80-152
50.00 92.1 80-124
50.00 94.7 77-129
Report Date: 8/17/2016 Page27 of 52
All anol) ses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the atlached COC Conlidentinl Business lnformnlion: This report is prm·ided for the exclusi\e use of the
~ddressee Pri,·ile~es or su~seq~ent ~~:e of the ~?':'e of this .co1~pany or anr 1~mbe1 of its stnff, or reproductio~ ~fthis repo~ in ;o~eclion~ \\ilh I he u~:er1ise1~ent, P~?molio.n ':r ~ale of :U!Y. ~rod~cl or P~?cess, ?I in ~nn~c~ion \\'!Lh lh~ r~-p~blicalion of Lhis reporl
American West
ANALYTICAL LABORATORIES
3440 South 700 West
)alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1608133-003
Client Sample ID: TW4-35_08032016
Collection Date: 8/3/2016 814h
Received Date: 8/5/2016 1040h
Analytical Results
Date Date Method Reporting Analytical
Compound Units Prepared Analyzed Used Limit Result Qual
Chloride mg/L 8/10/2016 1401h E300.0 10.0 34.8
Nitrate/Nitrite (as N) mg/L 8/5/2016 1620h E353.2 0.100 0.723
ReportDate: 8/17/2016 Page8of52
All analyses applicnble to the CW A. SDW A, and RCRA are performed in accordance to NELAC protocols Pertinent sampling infommlion is locnted on the nl1ached COC Confidentiul Business rnformation: This report is pro,•ided for the e;o.;clusi\ e use of the
~ddressee. Pri\ ile~es o.fsub .. seq~enl ~~e of the ~:u_ne of this .co~pany or any ~mbe1 or its staff, or reproduclio~ ~fthis repo~ in .con~ection ... wi1J11he «<.!''ertisemenl, P~?motio.n ~r sale of~~). ~1od~cl or pt:ocess, ~r in ;onn~c~ion w!lh th7 r:_-publication or I his report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratmy Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-007C
Client Sample ID: TW4-36_07282016
Collection Date: 7/28/2016 812h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/1/2016 1608h
Units: Jlg/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
54.9 50.00
49.9 50.00
52.8 50.00
51.4 50.00
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
1.00 < 1.00
%REC Limits Qual
110 72-151
99.8 80-152
106 80-124
103 77-129
Report Date: 8/9/2016 Page 36 of61
All anolyses applicnble to the CWA. SDWA. and RCRA we perfomled in ac~ordance to NELAC protocols Pertinent sampling information is located on the ati:Jched COC Confidential Business Jnfornrotion: This repon is pro,,ided for the exclusi\ e use of1he
~ddressee PriYile~es o,C sub .. seq~1ent ~~~e of the ~~1e of this .co•~pcm~ or an) J~mberof its st:liT, or reproduclio~ ~f this repo~ in ~n~1ecfion .. \\ith the"'!'.. el1ise'?ent, P~?moti~n or sale or~!) ~rodl~ct or p~ocess, ~r in ~nn~c~ion w~th th~ r~-publica1ion or 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.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-007
Client Sample ID: TW4-36_07282016
Collection Date: 7/28/2016 812h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 1716h
8/1/2016 1757h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
£300.0 10.0 69.4
£353.2 0.100 < 0.100
Report Date: 8/9/2016 Page 13 of61
All analyses applicoble to the CWA. SDWA. Rnd RCRA me perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached CDC Confidential Business Information: This report is prm ided for the excl11sh e use of the
~ddressee Pri\·ile~es o_f sub .. seq~enl ~~~e of the ~~e of I his .cm~pnny or nny ~mber of its staff, or reproduclio~ ~f this repo~ in .co1~1ection .. \\ilh the a~vertisemenl, P~?motio.n or sale of ~!Y ~rodl~Cl or p~ocess, ~r in ~onn:_c~ion w~lh th~ r~·publication of this report
3440 South 700 West
~alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: l607518-020C
Client Sample ID: TW4-37_07252016
Collection Date: 7/25/2016 1356h
Received Date: 7/29/2016 1600h
Analytical Results
Contact: Garrin Palmer
Test Code: 8260-W-DENIOO
VOAs by GC/MS Method 8260C/5030C
Analyzed: 8/2/2016 1802h
Units: ~giL Dilution Factor: 100 Method: SW8260C
CAS Reporting Analytical
Compound Number Limit Result Qual
Chloroform 67-66-3 100 15,900
Surrogate CAS Result Amount Spiked %REC Limits Qual
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
17060-07-0
460-00-4
1868-53-7
2037-26-5
5,550
5,080
5,440
5,110
--The reporting limits were raised due to high analyte concentrations.
Analyzed: 8/1/2016 2026h
Units: ~giL Dilution Factor:
Compound
Carbon tetrachloride
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: 1,2-Dichloroethane-d4 17060-07-0 55.8
Surr: 4-Bromofluorobenzene 460-00-4 49.5
Surr: Dibromofluoromethane 1868-53-7 54.7
Surr: Toluene-d8 2037-26-5 50.6
5,000 Ill 72-151
5,000 102 80-152
5,000 109 80-124
5,000 102 77-129
Method: SW8260C
CAS Reporting Analytical
Number Limit Result Qual
56-23-5 1.00 16.7
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 112 72-151
50.00 99.0 80-152
50.00 109 80-124
50.00 101 77-129
Report Date: 8/9/2016 Page 49 of61
All anal) ses applicable to the CWA. SDWA. and RCRA are perfom..ed in accordance to NELAC protocols Peninent sampling inCormation is located on the altached COC Confidential Business lnfonnalion: This reporl is provided for the exclusi,·e use oft he
~ddressee Pri \ ile~es or su~seq~enl ~~~e of the ~~e of this .col~pilny or all) ~~:mber of its stniT, or reproduclio~ ~fthis repo~ in ~on~u~ction ... \Vilh the ~' er1isement, P~?moti~n or sale of~!~ ~rodl~cl or P•,ocess, ~r in :-onn~c~ion \\ !th th7 n;-publicaiion of this repoT1
American West
ANALYTICAL LABORATORIES
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
!-mai l: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-020
Client Sample ID: TW4-37 _07252016
Collection Date: 7/25/2016 1356h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/112016 2309h
8/1/2016 185Jh
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 100 294
E353.2 0.200 33.4
Report Date: 8/9/2016 Page 26 of 61
All an3lyses applicable to the CWA. SDWA. and RCRA are performed in accordance to NELAC protocols Per1inenl sampling information is located on the attached COC Confidential Business Information: This 1epor1 is pro\'ided for the exdusi\ e use of the
~ddressee, Pri' ile~es o.f sub .. seq~ent ~~e of the ~~le of this .co1~pany or nny ~~~ber of its Sl:lff, or reproductio~ ~f this repo~ in .con~eclion .. \\lith the n~~ertisement P~?motio.n ~r :ale of ?J!) ~todl~CI or P•.oc:ess, ~r in ~nn~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
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607 518-022C
Client Sample ID: TW4-60 07252016
Collection Date: 7/25/2016 1300h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/3/2016 1416h
Units: fJg/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
57.4
49.6
54.8
50.1
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 < 1.00
74-87-3 1.00 < 1.00
75-09-2 1.00 < 1.00
Amount Spiked %REC Limits Qual
50.00 115 72-151
50.00 99.3 80-152
50.00 110 80-124
50.00 100 77-129
Report Date: 8/9/2016 Page 51 of 61
All analyses applicoble to the CWA, SDWA. and RCRA are performed in accordance to NELAC protocols Perlinenl sampling information is located on the altnched COC Confidential Business rnformution: This repor1 is proYided for the excllJSh·e use of the
~ddressee Pri\ ile¥es or su~seq~enl ~~e of the ~~e of this _con:pany or nfl) J~mber of its stnfT, or reproductio~ ~~this repo~ in ~~~eel ion ... wilh I he a~vertisemenl, P~?molio.n ~· ~ale of~~)-~IOdl~Cl or P•,?cess, ~r in ~onm:c~ion \\'!lh lh~ n;:_-p~blicalion of lhis report
3440 South 700 West
;;alt Lake City, UT 84119
Phone: (80 I) 263-8686
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-022
Client Sample ID: TW4-60_07252016
Collection Date: 7/25/2016 1300h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg!L
Nitrate/Nitrite (as N) mg!L
Date
Analyzed
8/1/2016 2021h
8/1/2016 1836h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 1.00 < 1.00
E353.2 0.100 < 0.100
Report Date: 8/9/2016 Page 28 of 61
All .analyses applicable to the CWA~ SDWA,. and RCRA are performed in accordance to NELAC protocols_ Penineot samplin£ infonnnlion is loculed on lhe attached COC Conflchmtiul Business lnformution: This report is pro\'ided for the exclusi\·e use of the
~ddressee Pri,·ile~es o,r sub ... seq~nt ~~~e of the ~~1e of this .co•~pany or an} r~_:~1ber of its staff, or reproducli~ ~~litis repo~ in ~~eclion .. "·ith tJte ~' ertise~nt, p~omotio,n or sale of ~!Y_ ~rod~ct or p~ocess, ~r in :onnt;=~ian w~lh th~ r~·p~blication of this report
American West ANALYTICAl LAGORATORIES
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518-023C
Client Sample ID: TW4-65 07272016
Collection Date: 7/27/2016 820h
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/3/2016 1336h
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
17060-07-0
460-00-4
1868-53-7
2037-26-5
Result
57.1
51.7
56.1
50.0
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
50.00 114 72-151
50.00 103 80-152
50.00 112 80-124
50.00 100 77-129
Report Date: 8/9/2016 Page 52 of 61
All anal) ses applicable to the CWA. SDWA. and RCRA are performed in accordance lo NELAC protocols Pertinent sampling information is located on the atlachecl COC. Confidential Business Inrormation: This report is provided fort he exclush e use of the
~ddressee Pri\ ile~es o! sub .. seq~enl ~~e of the ~~e of this .cot~pllll) or an) J~mber of its staJT. or reproduclio~ ~f lhis repo~ in ~on~1eclion~ with the a~vertisement. p~omotio.n or sa1e of :U~Y ~rodl~ct or Pl.?cess, ~r in ~onn:,c!ion \\ ~th th~ r:-publication of this repor1
American West
ANALVTICAl 1-ADOAATOAIES
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
INORGANIC ANALYTICAL REPORT
Client: Energy Fuels Resources, Inc.
Project: 3rd Quarter Chloroform 2016
Lab Sample ID: 1607518-023
Client Sample ID: TW4-65_07272016
Collection Date: 7/27/2016 820h
Received Date: 7/29/2016 1600h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/1/2016 2038h
8/1/2016 1852h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 70.9
E353.2 0.200 35.6
Report Date: 8/9/2016 Page 29 of 61
All annl)ses applicable to the CWA. SOW A. and RCRA rue ped'om1ed in accordance to NELAC protocols. Pertinent sampling information is located on the aU ached COC Confidential Business Jnfonnalion: This report is prm'ided for1he e.xclusi\e use of the
~ddressee Pri' ile~es o.r sub ... seq~enl ~~~e of the ~~r:ne of this .cm~pnny or onr ~~~~be1 of its staff, or reproductio.~ ~~-this repo~ In ~on~1ection ... with the n~vertisemenl. P~?motio.n or saJe of :U!)~ ~rod~ct or p~ocess, ~r in ~onn~c.tion w!th th~ r~-p~blication of this report
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-0 19C
Client Sample ID: TW4-70 08032016 American West
ANALYTICAL LABoRAToRIEs Collection Date: 8/3/2016 823h
Received Date: 8/5/2016
Analytical Results
Analyzed: 8/8/2016 1945h
Units: J..lg/L
1040h
Dilution Factor:
Contact: Garrin Palmer
Test Code: 8260-W-DENlOO
VOAs by GC/MS Method 8260C/5030C
Method: SW8260C
CAS Reporting Analytical
3440 South 700 West
~alt Lake City, UT 84119 Compound Number Limit Result Qual
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
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 48.4
460-00-4 52.2
1868-53-7 49.3
2037-26-5 50.9
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 96.8 72-151
50.00 104 80-152
50.00 98.7 80-124
50.00 102 77-129
Report Date: 8/17/2016 Page 43 of 52
All anol) ses applicable to the CW A. SDWA. and RCRA ure perfom1ed in accordance to NELAC p10tocols, Pertinent swnplin£ information is located on the attached COC Confidentlc:tl Business Information: This report is provided for the exclush e use oft he
~ddressee Pri\ ile~es of' sub .. seq~enl _u;;e oflhe ~~e of this .cot~ pony or My t~mbet of its starr, or reproductio~ ~f this repo~ in ~on~eclion ... \\~lh the n~:ertisemenl, P~?moli~n ~r saJe of~!~. ~rodL~Cl or P~?cess, ~r in ~onm~.c~ion w~th th~ r~-publication of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;a!t Lake City, UT 841 1 9
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-019
Client Sample ID: TW4-70 08032016
Collection Date: 8/3/2016 823h
Received Date: 8/5/2016 1040h
Analytical Results
Date
Compound Units Prepared
Chloride mg/L
Nitrate/Nitrite (as N) mg/L
Date
Analyzed
8/10/2016 2047h
8/5/2016 1658h
Contact: Garrin Palmer
Method Reporting Analytical
Used Limit Result Qual
E300.0 10.0 48.3
E353.2 0.100 < 0.100
Report Date: 8/17/2016 Page 24 of 52
All anal) ses applicable to the CWA SDWA. and RCRA are perl'om1ed in accordance to NELAC protocols Pertinent sampling Ill formation is located on the attached COC Confidential Business Jnformation: This report is provided for the exclusi\e use of the
~ddressee. Pri\ ile~es or sub,:;eq~enl ~l;e of the ~~e of this .cm~pany or anr 1~7mber of its starr. or reproductio~ ~f this repo~ in .cOJ~ection~ \Vilh the a~vertise~enl. P~?moti~n ~r saJe of~!). ~rodl~CI or plrocess, ~r in ;onn;c!ion w~th lh? r:_-publication of this report
American West
ANAI.VTICAL 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
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608133-020A
Client Sample ID: Trip Blank
Collection Date: 8/2/2016
Received Date: 8/5/2016 1040h
Analytical Results
Analyzed: 8/8/2016 1248h
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
51.5
52.3
49.3
50.9
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 < 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
50.00 105 80-152
50.00 98.6 80-124
50.00 102 77-129
Report Date: 8/17/2016 Page 44 of 52
All anolyses applicnble to the CW A. SDWA and RCRA are performed in accordance Lo NELAC protocols Pertinent sampling information is locuted on the attached COC Confidential Business Information: This 1eport is pro"ided for the e:-.:clusi\·e use of the
~ddressee. Pri,·ile~es o.r sub .. seq~enl ~~~e ol' the ~~e of this .cm~pnny or nny ~~~mbe1 of its stnfr, or reproduclio~ ~f this repo~ in .con~teclion ... wilh the a~Yertisement~ P~?motio.n or sa.le of~~) ~rodL~CI or P•.ocess, ~r in ~onn: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.awa1-1abs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chlorofonn 2016
1607518-024A
Client Sample ID: Trip Blank
Collection Date: 7/25/2016
Received Date: 7/29/2016 1600h
Analytical Results
Analyzed: 8/2/2016 1822h
Units: ~giL Dilution Factor:
Compound
Carbon tetrachloride
Chlorofonn
Chloromethane
Methylene chloride
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
54.5
47.1
52.7
49.4
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
50.00 109 72-151
50.00 94.2 80-152
50.00 105 80-124
50.00 98.7 77-129
Report Date: 8/9/2016 Page 53 of61
All analyses applicoble to the CWA_ SDWA and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located 011 the attached COC Confidential Business Information: This report is pro\'ided for the e:xclusire use of the
~ddressee Pri' ile~es o_f sub .. seq~enl ~~e of the ~~e of this .coJ~pal\Y or an~ •~mbeJ of its stall, or reproductio~ ~f this rep01; in ~OI~tection,. \\·ilh the 11~\ ertisemenL, P~?motio.n or sale of ?J!) ~rodl~Ll or p1.ocess, ~r in ~nn:c~ion w~lh lh~ r~-publica1ion or this reporl
3440 South 700 West
)alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608399-002A
Client Sample ID: Trip Blank
Collection Date: 8/17/2016
Received Date: 8/19/2016 1040h
Analytical Results
Analyzed: 8/22/2016 934h
Units: jlg/L Dilution Factor:
Compound
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surrogate CAS Result
Surr: I ,2-Dichloroethane-d4 17060-07-0 48.9
Surr: 4-Bromofluorobenzene 460-00-4 46.0
Surr: Dibromofluoromethane 1868-53-7 48.9
Surr: Toluene-d8 2037-26-5 48.4
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 97.8 72-151
50.00 92.1 80-152
50.00 97.9 80-124
50.00 96.7 77-129
Report Date: 8/26/2016 Page 7 of 15
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 CDC Conridentlnl Business Information: This repor1 is prm 1ded for the exclusive use of the
:ddressee Pri' ile~es o!sub.seg~ent ~1;e o[ the ~~e of this .cot~pany or all) 1~mbe1 of its slafL or reproduclio~ ~fthis repo~ in ~on~eclion ... '\ilh the a~ver1isemenl. P~?molio.n or sale of?J2?. ~rodl~cl or P• .. ocess, ~r in ~onn:_c~ion w!lh 1h~ r~publicalion of this report
American West
ANALYTICAl LABORATORIES
3440 South 700 West
~alt Lake City, UT 84119
Garrin Palmer
Energy Fuels Resources, Inc.
6425 S. Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 3rd Quarter Chloroform 2016
Dear Garrin Palmer: Lab Set ID: 1607518
American West Analytical Laboratories received sample(s) on 7/29/2016 for the analyses
presented in the following report.
American West Analytical Laboratories (AW AL) is accredited by The National
Phone: [phone] Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
Toll Free: [phone] state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
Fax: [phone]
!-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
Thank You,
Approved by:
K I F Digitally signed y e . by Kyle F. Gross
Date:
Gross 2016.08.09
09:40:51 -06'00'
Laboratory Director or designee
Report Date: 8/9/2016 Page I of 61
All anal) ses applicable to the CWA, SDWA. and RCRA are perfom1ed in accordance to NELAC p1otocols. Pertinent sampling informnlion is locnled on the attached COC. Confidential Business Information: This report is provided for the exclusi\e use of1he
~ddressee Pri\ ile~es or sub .. seq~ent ~~e of the ?.?'?e of this .co!~pany or M) t~mber of its starr, or reproduclio.~ ~r this repOI~ in .con~lection .. \\ilh the a~verlisemenl, ll~?molio,n ~1' sale of :U!). ~rodl~Cl or p~ocess, ~r in 7onn~c~ion "!lh th~ r~-publication of this report
SAMPLE SUMMARY
American West Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
ANALYTICAL LABORATORIES Project: 3rd Quarter Chloroform 2016
Lab Set ID: 1607518
Date Received: 7/29/2016 1600h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West 1607518-001A TW4-03R 07262016 7/26/2016 1238h Aqueous Anions, E300.0
;;alt Lake City, UT 84119 1607518-00 lB TW4-03R 07262016 7/26/2016 1238h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-001C TW4-03R 07262016 7/26/2016 1238h Aqueous VOA by GC/MS Method
8260C/5030C
Phone: [phone] 518-002A TW4-03 07272016 7/27/2016 754h Aqueous Anions, E300.0
1607 518-0028 TW4-03 07272016 7/27/2016 754h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1607 518-002C TW4-03_07272016 7/27/2016 754h Aqueous VOA by GC/MS Method
Fax: [phone]C/5030C
~-mail: [e-mail] 1607518-003A TW4-12 07272016 7/27/2016 813h Aqueous Anions, E300.0
1607518-0038 TW4-12 07272016 7/27/2016 813h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1607518-003C TW4-12_07272016 7/27/2016 813h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-004A TW4-28 07272016 7/27/2016 820h Aqueous Anions, E300.0
Kyle F. Gross 1607518-0048 TW4-28 07272016 7/27/2016 820h Aqueous Nitrite/Nitrate (as N), E353.2
1607 518-004C TW4-28_07272016 7/27/2016 820h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1607518-005A TW4-32 07282016 7/28/2016 800h Aqueous Anions, E300.0
Jose Rocha 1607518-0058 TW4-32_07282016 7/28/2016 800h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1607518-005C TW4-32_07282016 7/28/2016 800h Aqueous VOA by GC/MS Method
8260C/5030C
1607 518-006A TW4-13 07282016 7/28/2016 807h Aqueous Anions, E300.0
1607 518-0068 TW4-13 07282016 7/28/2016 807h Aqueous Nitrite/Nitrate (as N), E353.2
1607 518-006C TW4-13 07282016 7/28/2016 807h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-007A TW4-36 07282016 7/28/2016 812h Aqueous Anions, E300.0
1607 518-0078 TW 4-36 07282016 7/28/2016 812h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-007C TW4-36 07282016 7/28/2016 812h Aqueous VOA by GC/MS Method
8260C/5030C
1607 518-008A TW4-31_07282016 7/28/2016 819h Aqueous Anions, E300.0
1607 518-0088 TW4-31 07282016 7/28/2016 819h Aqueous Nitrite/Nitrate (as N), E353.2
1607 518-008C TW4-31_07282016 7/28/2016 819h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-009A TW4-25 07252016 7/25/2016 1326h Aqueous Anions, E300.0
1607 518-0098 TW4-25 07252016 7/25/2016 1326h Aqueous Nitrite/Nitrate (as N), E353.2
1607 518-009C TW4-25 07252016 7/25/2016 1326h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-010A TW4-24 07252016 7/25/2016 1341h Aqueous Anions, E300.0
1607518-0108 TW4-24_07252016 7/25/2016 1341h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 8/9/2016 Page2 of61
All ann!) ses applicnble to the CWA. SDWA. and RCRA me performed in accordance to NELAC p•otocols. Pe1tinent sampling information is located on the attached COC. Confidential Business rnformation: This report is provided for the exclusiw use of the
~ddressee Pli,•ile~es o(" sub,..seq~ent ~~~e of the ~~le of this .c01~pnny or on~· ~~~mbe•· of its sir~ IT, or reproductio~ ~f this repo~ in .con~ection .. 'dth the ~vertisement, P:?motio.n ~r sale of :U!): ~rodl~ct or p•:ocess, ~r in ~nm;:c~ion \\'!lh th~ r~-publication or this reporl
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
American West Lab Set ID: 1607518
ANALYTICAL LABORATORIES Date Received: 7/29/2016 1600h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
1607518-01 oc TW4-24 07252016 7/25/2016 1341h Aqueous VOA by GC/MS Method
3440 South 700 West 8260C/5030C
1607518-0 11A TW4-21 07252016 7/25/2016 1320h Aqueous Anions, E300.0
;alt Lake City, UT 84119 1607518-011B TW4-21 07252016 7/25/2016 1320h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-011C TW4-21 07252016 7/25/2016 1320h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-012A TW4-01 07252016 7/25/2016 1437h Aqueous Anions, E300.0 Phone: [phone] 1607518-0128 TW 4-0 1_ 07252016 7/25/2016 1437h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1607518-012C TW4-01 07252016 7/25/2016 1437h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260C/5030C
!-mail: [e-mail] 1607518-013A MW -04 _ 07252016 7/25/2016 1432h Aqueous Anions, E300.0
1607518-0138 MW-04 07252016 7/25/2016 1432h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1607518-013C MW-04 07252016 7/25/2016 1432h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-014A TW4-04 07252016 7/25/2016 1445h Aqueous Anions, E300.0
1607518-0148 TW4-04 07252016 7/25/2016 1445h Aqueous Nitrite/Nitrate (as N), E353.2 Kyle F. Gross 1607518-0 14C TW4-04 07252016 7/25/2016 1445h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1607518-015A TW4-02 07252016 7/25/2016 1425h Aqueous Anions, E300.0
Jose Rocha 1607518-0158 TW4-02 07252016 7/25/2016 1425h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1607518-0 15C TW4-02 07252016 7/25/2016 1425h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-016A MW-26_07252016 7/25/2016 1412h Aqueous Anions, E300.0
1607518-0168 MW-26 07252016 7/25/2016 1412h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-016C MW-26 07252016 7/25/2016 1412h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-017A TW4-11_07252016 7/25/2016 1419h Aqueous Anions, E300.0
1607518-0178 TW4-11 07252016 7/25/2016 1419h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-017C TW4-11_07252016 7/25/2016 1419h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-018A TW4-22 07252016 7/25/2016 1350h Aqueous Anions, E300.0
1607518-0188 TW4-22 07252016 7/25/2016 1350h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-018C TW4-22 07252016 7/25/2016 1350h Aqueous VOA by GC/MS Method
8260C/5030C
1607518-019A TW4-19_07252016 7/25/2016 1500h Aqueous Anions, E300.0
1607518-0198 TW4-19 07252016 7/25/2016 1500h Aqueous Nitrite/Nitrate (as N), E353.2
1607518-019C TW4-19 07252016 7/25/2016 1500h Aqueous VOA by GC/MS Method
8260C/5030C
1607 518-020A TW4-37_07252016 7/25/2016 1356h Aqueous Anions, E300.0
1607518-0208 TW4-37_07252016 7/25/2016 1356h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 8/9/2016 Page 3 of61
All Mnl) ses applicable to the CWA~ SDWA. and RCRA nre pert'ormed in accordance to NELAC protocols. Pertinent sampling information is located on lhe auached COC. Confidential Business Information: This report is provided for the exclusi\ e use of the
~ddressee Prh·iJe~es o,r sub .. seq~enl ~~~e of the ~~1e of this .em~ pan~ or anr ~~~mbe1· of its staff, or reproductio~ ~f this repo~ in ~on~tection .. \Vith the ~vertisement, P~?moti~n or sale of ~!Y ~rodl~ct or p~ocess, ~r in ~onm;c~ion w~Lh th7 n~-p~blication 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
Client:
Project:
Lab Set ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1607518
Date Received: 7/29/2016 1600h
Lab Sample ID Client Sample ID
1607 518-020C TW4-37 07252016
1607518-021A TW4-20 07252016
1607518-0218 TW4-20_07252016
1607518-021C TW4-20 07252016
1607 518-022A TW4-60 07252016
1607 518-022B TW4-60 07252016
1607518-022C TW4-60 07252016
1607518-023A TW4-65_07272016
1607518-0238 TW4-65 07272016
1607518-023C TW4-65_07272016
1607518-024A Trip Blank
Contact: Garrin Palmer
Date Collected Matrix Analysis
7/25/2016 1356h Aqueous VOA by GC/MS Method
8260C/5030C
7/25/2016 1404h Aqueous Anions, E300.0
7/25/2016 1404h Aqueous Nitrite/Nitrate (as N), E353.2
7/25/2016 1404h Aqueous VOA by GC/MS Method
8260C/5030C
7/25/2016 1300h Aqueous Anions, E300.0
7/25/2016 1300h Aqueous Nitrite/Nitrate (as N), E353.2
7/25/2016 1300h Aqueous VOA by GC/MS Method
8260C/5030C
7/27/2016 820h Aqueous Anions, E300.0
7/27/2016 820h Aqueous Nitrite/Nitrate (as N), E353.2
7/27/2016 820h Aqueous VOA by GC/MS Method
8260C/5030C
7/25/2016 Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 8/9/2016 Page 4 of 61
All analyses applicable to the C'WA. SDWA, and RCRA me performed in accordance to NELAC protocols_ Pertinmt sampling information is located on the altached COC Confidentinl Business lnfonnahon: This reporl is pro\ ided for the exclusi\ e use oft he
~ddressee Pri' ile~es o,r sub .. seq~ent ~~~e of the ~~1e of this .col~pnn~ or M) 1~7mber of its stnff, or reproduclio~ ~f this repo~ in .cm~ection .. with the ~venisemenl, P~?molio.n 01 saJe of :U~~. ~rodL~ct or P•.ocess, ~r in ~onn~c.tion w~th th~ r~-publication of 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
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:
3rd Quarter Chloroform 2016
1607518
7/29/2016
7/25-7/25/2016
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 exception: the MSD percent recovery and RPD for Nitrate/Nitrite (as N)
on sample 1607518-009B were outside of the control limits due to matrix
interference or sample non-homogeneity.
Corrective Action: None required.
Report Date: 8/9/2016 Page 5 of 61
All analyses applicable 10 the CWA. SDWA. and RCRA are perfom1ed in accordance to NELAC prolocols. Per1inenl sampling information is located on the attached COC Confidential Business Information: This report is prm'ided for the exclusi\e use oft he
~ddressee P1i' ile~es of sub_seq~ent .. u~e of the ~~1e of this ,cm~pany or acJY ~mber of its staff. or reproductio~ ~f this repo~ in ~01~1ection~ \\ilh the a~vertisement, p~~motio_n ~r sale of~!). ~10dl~Cl or p1:ocess, ~r in 7onn~c~ion w!th 1h~ r:·publication 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
Volatile Case Narrative
Contact:
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
Method:
Analysis:
Energy Fuels Resources, Inc.
Garrin Palmer
3rd Quarter Chloroform 2016
1607518
7/29/2016
7/25-7/25/2016
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: 8/9/2016 Page 6 of61
All analyses applicable to the CWA. SDWA. and RCRA <:~re perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attr~ched COC Conlidentiul Business lnformalion: This report is pro"ided for the exclusi\ e use of the
~ddressee Pri, ile~es o.fsub ... seq~ent ~~e of the ~~e of this .co1~pany or illl)' ~~~ber of its staff, or reproductio~ ~fthis repo~ in ~on~1ection ... \\ilh the a~;ertiseJ~enl. P~?motio.n ~r sale of~!). ~rod~ct or p1:?cess, ~r in ~onn~c~ion w!lh lh~ r~-publica1ion of this 1epor1
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1607518
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: LCS-R92383 Date Analyzed:
Test Code: 300.0-W
Chloride 5.04
Lab Sample ID: LCS-R92385 Date Analyzed:
Test Code: 300.0-W
Chloride 5.01
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: LCS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
08/0112016 1303h
mg/L E300.0 0.00516 0.100 5.000 0 101
08/0112016 2145h
mg/L E300,0 0.00516 0.100 5.000 0 100
Lab Sample ID: LCS N03-R92372 Date Analyzed: 08/0112016 1732h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.960 mg/L E353.2 0.00833 0.0100 1.000 0 96.0
Lab Sample ID: LCS N03-R92373 Date Analyzed: 08/01/2016 1816h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.952 mg!L E353.2 0.00833 0.0100 1.000 0 95.2
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: 8/9/2016 Page 54 of 61
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC, Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use 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
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1607518
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R92383 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R92385 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
08/01/2016 1246h
mg/L E300.0 0.00516 0.100
08/01/2016 2128h
mg/L E300.0 0.00516 0.100 -Lab Sample ID: MB-R92372 Date Analyzed: 08/0 l/20 16 1729h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100 mg/L E353.2 0.00833 0.0100
Lab Sample ID: MB-R92373 Date Analyzed: 08/01/2016 1815h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100 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: 8/9/2016 Page 55 of61
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 lnfom1ation: 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 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-publication of this report tbr any purpose other than for the addressee will be granted only on contact This
ANALYTICAL LABORATORIES
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_QC SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Dept: we Lab Set ID: 1607518
Project: 3rd Quarter Chloroform 2016
Analyte Result Units Method
Lab Sample ID: 1607518-010AMS Date Analyzed: 08/01/2016 1337h
Test Code: 300.0-W
Chloride 2,250 mg!L E300.0
Lab Sample ID: 1607518-0llAMS Date Analyzed: 08/01/2016 1427h
Test Code: 300.0-W
Chloride 1,510 mg!L E300.0
Lab Sample ID: 1607518-018AMS Date Analyzed: 08/01/2016 2219h
Test Code: 300.0-W
Chloride 1,680 mg/L E300.0
Lab Sample ID: 1607518-009BMS NOJ Date Analyzed: 08/0112016 1808h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 12.1 mg/L E353.2
Lab Sample ID: 1607518-015BMS Date Analyzed: 08/01/2016 1827h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 13.8 mg/L E353.2
MDL
1.03
1.03
1.03
0.0833
0.0833
Reporting
Limit
20.0
20.0
20.0
0.100
0.100
QC Type: MS
Amount
Spiked
1,000
1,000
1,000
10.00
10.00
Spike Ref.
Amount
1180
457
619
1.78
4.07
%REC
107
106
106
103
97.4
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: 8/9/2016 Page 56 of61
analyses applicable to the CWA. SDWA, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact. This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone], Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
American West _QC SUMMARY REPORT ANAlYTICAL lABORATORIES
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1607518 Dept: we
Project: 3rd Quarter Chloroform 2016 QC Type: MSD
--
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1607518-010AMSD Date Analyzed: 08/01/2016 1353h
Test Code: 300.0-W
Chloride 2,250 mg/L E300.0 1.03 20.0 1,000 1180 107 90-110 2250 0.173 20
Lab Sample ID: 1607518-0llAMSD Date Analyzed: 08/0112016 1444h
Test Code: 300.0-W
Chloride 1,520 mg/L E300.0 1.03 20.0 1,000 457 106 90-110 1510 0.473 20
Lab Sample ID: 1607518-018AMSD Date Analyzed: 08/01/2016 2236h
Test Code: 300.0-W
Chloride 1,690 mg!L E300.0 1.03 20.0 1,000 619 107 90-110 1680 0.940 20
Lab Sample ID: 1607518-0098MSD N03 Date Analyzed: 08/01/2016 1809h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 13.4 mg/L E353.2 0.0833 0.100 10.00 1.78 117 90-110 12.1 10.7 10 I@
Lab Sample ID: 1607518-015BMSD Date Analyzed: 08/01120 16 1828h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 14.5 mg!L E353.2 0.0833 0.100 10.00 4.07 104 90-110 13.8 4.81 10
@-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.
Report Date: 8/9/2016 Page 57 of61
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 lnforrnation: 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 _b'Tanted only on contact. This
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1607518
Project: 3rd 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-Iabs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-1 080ll6A Date Analyzed: 08/01/2016 1228h
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-1 080316A
Test Code: 8260-W-DEN100
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
21.5 J.lg/L SW8260C
20.6 llg/L SW8260C
52.2 J.lg/L SW8260C
50.2 llg/L SW8260C
51.4 J.lg/L SW8260C
50.9 llg/L SW8260C
Date Analyzed: 08/03/2016 1209h
23.9 llg/L SW8260C
25.3 llg/L SW8260C
53.9 llg/L SW8260C
44.4 J.lg/L SW8260C
53.5 llg/L SW8260C
49.0 J.lg/L SW8260C
0.153 1.00 20.00 0 108
0.172 1.00 20.00 0 103
50.00 104
50.00 100
50.00 103
50.00 102
0.153 1.00 20.00 0 119
0.172 1.00 20.00 0 127
50.00 108
50.00 88.8
50.00 107
50.00 98.0
Limits
85. 124
81. 135
80. 122
85. 121
80. 116
81. 123
85. 124
71-135
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: 8/9/2016 Page 58 of61
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: 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: 1607518
Project: 3rd 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
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QC Type: MBLK
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: MB VOC-1 080116A Date Analyzed: 08/01/2016 1307h
Test Code: 8260-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: MB VOC-1 080316A
Test Code: 8260-W-DENIOO
Carbon tetrachloride
Chloroform
Chloromethane
Methylene chloride
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
52.8
51.3
51.4
50.5
Date Analyzed:
< 1.00
< 1.00
< 1.00
< 1.00
56.6
48.2
54.6
50.5
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
l!g/L SW8260C 50.00 106
llg!L SW8260C 50.00 103
llg!L SW8260C 50.00 103
l!g/L SW8260C 50.00 101
08/03/2016 1249h
l!g/L SW8260C 0.504 1.00
l!g/L SW8260C 0.153 1.00
llg!L SW8260C 0.163 1.00
l!g/L SW8260C 0.172 1.00
l!g/L SW8260C 50.00 113
llg!L SW8260C 50.00 96.4
llg!L SW8260C 50.00 109
l!g/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
ReportDate: 8/9/2016 Page59of61
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 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
ANALYTI CAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1607518
Project: 3rd 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
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: MS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1607518-001CMS Date Analyzed: 08/01/2016 1429h
Test Code: 8260-W-DENlOO
Chloroform
Methylene chloride
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 1608032-001AMS
Test Code: 8260-W-DENlOO
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
21.6
20.8
53.3
49.9
52.4
49.5
Date Analyzed:
452
476
1,020
992
1,020
1,030
llg/L SW8260C 0.153 1.00 20.00 0 108
llg/L SW8260C 0.172 1.00 20.00 0 104
llg/L SW8260C 50.00 107
llg/L SW8260C 50.00 99.9
llg/L SW8260C 50.00 105
llg/L SW8260C 50.00 99.1
08/03/2016 1635h
llg/L SW8260C 3.06 20.0 400.0 0 113
llg/L SW8260C 3.44 20.0 400.0 0 119
llg/L SW8260C 1,000 102
llg/L SW8260C 1,000 99.2
llg/L SW8260C 1,000 102
llg/L SW8260C 1,000 103
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: 8/9/2016 Page 60 of 61
analyses applicable to the CW A. SDW A, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC ConfidentiaJ Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use 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], Fmc [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
ANALYTICAL LABORATORIES QC SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1607518 Dept: MSVOA
Project: 3rd 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: 1607518-001CMSD Date Analyzed: 08/01/2016 1449h
Test Code: 8260-W-DEN100
Chloroform 21.2 f.lg/L SW8260C 0.153 1.00 20.00 0 106 50 -146 21.6 2.06 25
Methylene chloride 22.0 f.lg/L SW8260C 0.172 1.00 20.00 0 110 30-192 20.8 5.94 25
Surr: 1 ,2-Dichloroethane-d4 53.4 f.lg/L SW8260C 50.00 107 72 -151
Surr: 4-Bromofluorobenzene 47.6 f.lg/L SW8260C 50.00 95.2 80-152
Surr: Dibromofluoromethane 52.6 f.lg/L SW8260C 50.00 105 80 -124
Surr: Toluene-d8 49.1 f.lg/L SW8260C 50.00 98.2 77 -129 -Lab Sample ID: 1608032-001AMSD Date Analyzed: 08/0312016 1655h
Test Code: 8260-W-DENIOO
Chloroform 431 f.lg/L SW8260C 3.06 20.0 400.0 0 108 50-146 452 4.80 25
Methylene chloride 422 f.lg/L SW8260C 3.44 20.0 400.0 0 106 30-192 476 12.0 25
Surr: 1,2-Dichloroethane-d4 1,020 f.lg/L SW8260C 1,000 102 72-151
Surr: 4-Bromofluorobenzene 937 f.lg/L SW8260C 1,000 93.7 80-152
Surr: Dibromotluoromethane 1,000 f.lg/L SW8260C 1,000 100 80-124
Surr: Toluene-d8 992 f.lg/L SW8260C 1,000 99.2 77-129
Report Date: 8/9/2016 Page 61 of61
analyses applicable to the CWA. SOW A, and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use 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
ill.
Denison American West Analytical Laboratories
WORK ORDER Summary Work Order: 1607518
Due Date: 8/9/2016
Page 1 of4
Client:
Client ID:
Project:
Comments:
SampleiD
1607518-001A
1607518-001B
1607518-001C
1607518-002A
1607518-002B
1607518-002C
1607518-003A
1607518-003B
1607518-003C
1607518-004A
1607518-004B
1607518-004C
1607518-00SA
1607518-005B
1607518-005C
Printed: 7/29/2016
Energy Fuels Resources, Inc.
DENlOO Contact: Garrin Palmer
3rd Quarter Chloroform 2016 QC Level: III WO Type: Project
PARush. QC 3 (Summary/No chromatograms). RL ofl ppm for Chloride and VOC and 0.1 ppm forN02/N03-RunN02/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.; ;,£__
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
TW4-03R_07262016 7/26/2016 1238h 7/2912016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Arwlytes: N03N02N
8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJOO; #of Arwlytes: 4 I # ofSurr: 4
TW4-03_07272016 7/27/2016 0754h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4 I# of Surr: 4
TW4-12_07272016 7/27/2016 0813h 7/29/2016 1600h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Arwlytes: N03N02N
8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENI 00; #of Ana/ytes: 4 I # of Surr: 4
TW4-28_07272016 7/27/2016 0820h 7/29/2016 1600h 300.0-W Aqueous df-wc
I SEL Arwlytes: CL
N021N03-W-353.2 df -no2/no3
I SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Arwlytes: 4 I # of Surr: 4
1W4-32_07282016 7/28/2016 0800h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Arwlytes: CL
N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJOO; #of Arwlytes: 4 I # of Surr: 4
FORLABORATORYUSEONLY[filloutonpage1): %M ,/i!f R0"-c~ TAJ,.e('" ~ HOK~ HOK __ _ HOK___ COC Emailed. ____ ~
WORK ORDER Summary Work Order: 1607518 -· Page2 of4
Client: Energy Fuels Resources, Inc. Due Date: 8/9/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1607518-006A TW4-l3_07282016 7/28/2016 0807h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0068 N02/N03-W-353.2 df -no2/no3
I SEL Analytes: N03N02N
1607518-006C 8260-W-DENlOO VOCFridge 3
Test Graup: 8260-W-DENIOO; #of Analytes: 4 1 # ofSurr: 4
1607518-007A TW4-36_07282016 7/28/2016 0812h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0078 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
1607518-007C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 / #of Surr: 4
1607518-008A 1W4-31_07282016 7/28/2016 0819h 7/29/2016 1600h 300.0-W Aqueous df-wc
I SEL Analytes: CL
1607518-00SB N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-008C 8260-W-DENlOO VOCFridge 3
Test Graup: 8260-W-DEN100; #of Analytes: 41 # ofSurr: 4
1607518-009A 1W4-25_07252016 7/25/2016 1326h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0098 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-009C 8260-W-DENIOO VOCFridge 3
Test Graup: 8260-W-DEN1 00; #of Analytes: 41 #of Surr: 4
1607518-010A TW4-24_07252016 7/25/2016 1341h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0108 N02/N03-W-353.2 df -no2/no3
1 SEL Analytes: N03N02N
1607518-010C 8260-W-DENIOO VOCFridge
Test Graup: 8260-W-DEN100; #of Analytes: 4 /# ofSurr: 4
1607518-0llA TW4-21_07252016 7/25/2016 1320h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0118 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-011C 8260-W-DENIOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 41 #of Surr: 4
1607518-012A 1W4-01_07252016 7/25/2016 1437h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
IJjnted: 7/29/20~6 FOR LABORATORY USE ONLY [fill out on page 1]: %M D RT D C.N D TAT 0 QCD HOK~ HOK __ H!)K __ COC Ema,i!ed
'\,·.:a:•
WORK ORDER Summary Work Order: 1607518 Page3 of4
Client: Energy Fuels Resources, Inc. Due Date: 8/9/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Set Storage
1607518-012B TW4-01_07252016 7/25/2016 1437h 7/29/2016 1600h N02/N03-W-353.2 Aqueous df-no2/no3
I SEL Analytes: N03N02N
1607518-012C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 41 #of Surr: 4
1607518-0BA ~-04_07252016 7/25/2016 1432h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0BB N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-0BC 8260-W-DEN100 VOCFridge 3
Test Group: 8260-~-DENIOO; #of Analytes: 4/# ofSurr: 4
1607518-014A TW4-04_07252016 7/25/2016 1445h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1607518-014B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-014C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 4/ #of Surr: 4
1607518-015A TW4-02_07252016 7/25/2016 1425h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SELAnalytes: CL
1607518-015B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-015C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENJ 00; #of Anolytes: 4/ # of Surr: 4
1607518-016A ~-26_07252016 7/25/2016 1412h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-016B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-016C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 41 #of Surr: 4
1607518-017A TW4-11_07252016 7/25/2016 1419h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-017B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-017C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 41 #of Surr: 4
1607518-0lSA TW4-22_07252016 7/25/2016 1350h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL A11alytes: CL
1607518-018B N02/N03-W-353.2 df-no2/no3
1 SELAnalytes: N03N02N
Printed: 7/29/2016 FOR lABORATORY USE ONLY [fill out on page 1): %M D RT 0 . CN 0 TAT 0 QCO HOK __ HOK __ ,, HOK __ COC Emailed
WORK ORDER Summary Work Order: 1607518 Page4 of4
Client: Energy Fuels Resources, Inc. Due Date: 8/9/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1607518-018C ~4-22_07252016 7/25/2016 1350h 7/29/2016 1600h 8260-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 4 I # ofSurr: 4
1607518-019A ~4-19_07252016 7/25/2016 1500h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0198 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-019C 8260-W-DEN100 VOCFridge
Test Group: 8260-W-DEN100; #of Analytes: 4 I # ofSurr: 4
1607518-020A ~4-37 _07252016 7/25/2016 1356h 7/29/2016 1600h 300.0-W Aqueous df·wc
1 SEL Analytes: CL
1607518-0208 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-020C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DEN 1 00; # of Analytes: 4 I # of Surr: 4
1607518-021A ~4-20_07252016 7/25/2016 1404h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0218 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-021C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DEN100; # ofAnalytes: 41# ofSurr: 4
1607518-022A ~4-60_07252016 7/25/2016 1300h 7/29/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0228 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-022C 8260-W-DEN100 VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # ofSurr: 4
1607518-023A TW4-65_07272016 7127/2016 0820h 7129/2016 1600h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1607518-0238 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1607518-023C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Surr: 4
1607518-024A TripB1ank 7/25/2016 712912016 1600h 8260-W-DEN100 Aqueous VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 4 I # ofSurr: 4
.Printed: 8/112016 FORLABORATORYUSEONLY[filloutonpage1]: %M 0 RT 0 CN 0 TAT 0 QCO HOK __ _ HOK __ HOK___ COC Emailed. ____ _
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# {801) 263-8686 Toll Free# {888) 263-8686
L~~ Fax# {801) 263-a687 Email [e-mail]
www.awal-labs.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] Cell#:
[e-mail] KWetnel®energyfu.cls.com;
Email: dtw:k@encr~cls.com
Project Name: 3RD QUARTER CHLOROFORM 2016
Project#:
PO#:
Sampler Name: TANNER HOLLIDAY
,,
r
4
r s
i 7
(a
~
TW4-04_07252016
TW4-02_07252016
MW-26_07252016
TW4·11_07252016
TW4-22_07252016
TW4-19_07252016
TW4-37 _07252016
TW4-20_07252016
TW4-60_07252016
{. 1 TW4-65_07272016
TRIP BLANK
I TEMP BLANK
1
Rollnq\Jf6!ledl>y: {.~ SIQIIOiuro
Sample ID:
..__ p~
PrlrdNamo: OARRIN PALMER
lloUnqo.Wshod by:
Slgnat<ro
P~mNnmo:
AallnqWho<ll>y:
Sl~n1111ro
PrintN.,..:
RolirqW;IIod l>y:
Sl!!natum
Print Name:
Date
Sampled
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/25/2016
7/27/2016
7/25/2016
7/29/2016
QalD~
7na'201E
Tlmo; 1600
ro•to:
Tlmo:
DDLo:
Tlmv:
Dlllo:
11111<1:
CHAIN OF CUSTODY
All analysis will be conducted using NELAP accredited methods and all data will be reported using AWAL1s standard analyte lists and reporting
limits (POL) unless specifically requested otherwise on this Chain of Custody and/or attached documentallon.
I QC Level: I Turn Around Time: Unless other arrangements have been made,
signed reports wiU 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
0 ELAPIA2LA
0 0 NLLAP
c;j' 0 Non-Compliance
M c:i 0 Other: 0 "' 0:. 0 £!! ~ <2 ... 0 " (I) 0 (0 c: <ii 0 "' ~ :;; 0 0 ~ Known Hazards 1!: "' 0 (I) ..... ~ "' Time 0 15. C'1 t.J & 0 E g 0 0 Sampled "' Sample Comments .. [J) ~
1445 5 w X X X
1425 5 w X X X
1412 5 w X X X
1419 5 w X X X
1350 5 w X X X
1500 5 w X X X
1356 5 w X X X
1404 5 w X X X
1300 5 w X X X
820 5 w X X X
3 w X
I w
r v t7 / \
A"'*'ed~ ~d -Oalo;l I 1-t:t /1 u . Special Instructions: s~/ ~ ~m<r. 1 h-1 ~~ ~~---lfv--nme: L~ ~ vtJ
Page of
Due Date: g!~/J~'
-
Laboratory usa· on~
Samplj!sWIIIO:
1 Shipped a<~
Ambio~ 2
Temperal~ -..!/.;2__ "C 3
~ R<alivedBro!<"""'-">Jf1119
e~s...,-o
5 tt-'Y'P•...,ovedN
·Chotkad "' bench ~ -N
6 IJOoelvod Wlfhtn
~Times N
CDC Tape Was:
I Pro;;ent on.OuiOr Paclm~
y ~
2 Unbroken on OUt« Pac~
y N
3 .Present on Sample 6 y N
4 UribrOken on Sample
y N @)
ploaeponcleo BoiiWIHI S>mp!o
labo!< ond coc fl.,.,.,Q?.
y ~
Received by: u Date: See the Analytical Scope of Work for Reporting Limits and VO<
Signature anaJyte llst.
Time:
PdniName:
Aecelved by: Date:
Sigr:tature rnm•:
Print Name:
Received by: I Dale:
SlgnaiYre
nme:
Print Name:
American West
Analytical Laboratories
463 W. 3600 S. Sail Lake City, UT 64 i i 5
Phone# (80i) 263-8686 Toll Free# [phone]
~ Fax# (BOi) 263-8687 Emall awal C 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#:
gpalme<@energyfuela.com; [e-mail]:
Email: dtmk@enUI!Yfnela.com
Project Name: 3RD QUARTER CHLOROFORM 2016
Project#:
PO#:
Sampler Name: TANNER HOLLIDAY
Date
Samole 10: Samoled
I TW4-03R_07262016 7/26/2016
· TW4-03_07272016 7/27/2016
I TW4-12_07272016 7/27/2016
I TW4-28_07272016 7/27/2016
• TW4-32_07282016 7/28/2016
i TW4-13_07282016 7/28/2016
' TW4-36_07282016 7/28/2016
I TW4-31_07282016 7/28/2016
I TW4-25_07252016 7/25/2016
o TW4-24_07252016 7/25/2016
: TW4-21_07252016 7/25/2016
2 TW4-01_07252016 7/25/2016
~ MW-04_07252016 7/25/2016
Refinquished by: h~~ (\)~-Date:
Signature 7t291201e
Print Name: GARRIN PALMER Time:,, ~DeS
Relinquished by: Dete:
Signature
1m a:
Print Name:
Relinquished by: Date:
Signature
nne:
Print Name:
Relinquished by: Date:
Signatu-e
Time:
Prtnt Noma:
CHAIN OF CUSTODY
All analysis ..,;11 be conducted using NELAP a=ed~ed methods and all data wil be reported using AWAL's standard anatyte lists and roporting
imlls (POL) unless speciflcaly requested otherwise on this Chain of Custocly and/or attached documentation.
I OC Level: I Tum Around Time: u~ other arrangements have baen made,
signed reports w111 be emalled by 5:00 pm on
3 Standard lhe day !hey are duo.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAPIA2LA
0' 0 NLLAP
c;j' 0 0 Non-Compliance
M 0 0 Other. on (") D' ~ ~ !2 .... 0 ., "' c "" " ~ 1ii 0 0 "" ::E 0 ~ Known Hazards " ;l: ltl 0 ., ..... ~ .. Time 0 "i'i C'l (J & 0 E 0 0 g Samoled "' Sample Comments .. CJ) ;l:
1238 5 w X X X
754 5 w X X X
813 5 w X X X
820 5 w X X X
800 5 w X X X
807 5 w X X X
812 5 w X X X
819 5 w X X X
1326 5 w X X X
1341 5 w X X X
1320 5 w X X X
1437 5 w X X X
1432 5 ~ X )>--~ ....,.
Aecei~f~ £ ---Data: "1J 7.dJJ /C, Special Instructions: llgpal 7~ -~-Print Nama: ~e fJJ?\..,? ~ .... lfiliiO' ll.t;t?O
J<oo fJ:Sl %'
j (po1§tztl11V"~h~·
AWAJ.. Lab Sample Set#
Page i of 2
rue0a~71l~ I
La~ratory Use Onty
Snmplos-W,.o:
1~or~
2 Ambient "' led
3· Tempe<a~~ ~ •c
4_ :Received Brok~ng
(lfT1l"opel1y Seei(S:> . y . N
SG:rrfY Preserved . .. N
Checked al benCh
y N .
6 RocalvddWHhlo c:;:J"ngT'imos
N
COCTnpoWas:
1 P,_,lon OUter-~ Y N N
2 Unb!ok.,.onO..O<P~ y N
3 Pr....,. •• 5arrtple . (5) y N No\
4 Urbni<on on Samplo {;;) y N No\
Disci-""""*" a. ...... Samp(o
l..al:ieloand COC R*B I y N
Received by: "-\_) Date: See the Analytical Scope of Work for Reporting Limits and VOC
Sl.gnature analyte list.
T!me:
Print Name:
fleceiVedby: Oat a:
Slanature
I me:
Prln(N_ame:
Received by: Date:
Slonature
nne:
Print Name:
Analysis
Ammonia
COD
Cyanide
Metals
N02&NDJ
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s le Set Ext,
Preservative I ;2. 3 y -s-~
pH<2H2S04
pH<2H2S04
pH>12
NaOH
oH<2HN03
DH<2H2S04 'J/<:1.. \]pq,_ ve<s. ~1"~ -..J.1'.t.. m
oH<2HCL I ( , I I I
t>H<2H2S04
pH>9NaOH,
ZnAcetate
pH<2H2S04
oH<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
7
'l.f A
I
--doH
() 9
"~ vt£
I I
l 0 l/
\..Jet 1.-..J(J,P,.
I 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.
Lab Set ID: /"'0 7S78 1 P -11500~
(_;} /c t'/ { ~~ -~~ /7 If
I
I"'--'<.> \lei ~t'~ '-/-a ~..If VP9.. \.!d.
I I I { I I/ 1/
Analysis
Ammonia
COD
Cyanide
Metals
N02&N03
O&G
Phenols
Sulfide
TKN
TP04
Procedure:
Frequency:
Preservation Check Sheet
s SetE
Preservative II 2o .,:2( c2cfl dJ-3 :-;;rrr, -;:::71 tfll1
pH<2 H2S04
oH<2H2S04
pH>12
NaOH
pH<2HN03
pH<2 H2S04 'll~ \.1 1'_9:. '\Jf:l'j-, ...._ ri'Y-.. '-lt'_b.
oH<2HCL I { I I
pH<2H2S04
pH>9NaOH,
ZnAcetate
pH<2H2S04
oH<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 ---
~-
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 Set ID: l{o 0 7c;;1 8
{~ P -:1:1-5/Jua
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
Garrin Palmer
Energy Fuels Resources, Inc.
6425 S. Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 3rd Quarter Chloroform 2016
Dear Garrin Palmer: Lab Set ID: 1608133
American West Analytical Laboratories received sample(s) on 8/5/2016 for the analyses
presented in the following report.
American West Analytical Laboratories (AW AL) is accredited by The National
Environmental Laboratory Accreditation Program (NELAP) in Utah and Texas; and is
state accredited in Colorado, Idaho, New Mexico, Wyoming, and Missouri.
All analyses were performed in accordance to the NELAP protocols unless noted
otherwise. Accreditation scope documents are available upon request. If you have any
questions or concerns regarding this report please feel free to call.
The abbreviation "Surr" found in organic reports indicates a surrogate compound that is
intentionally added by the laboratory to determine sample injection, extraction, and/or
purging efficiency. The "Reporting Limit" found on the report is equivalent to the
practical quantitation limit (PQL). This is the minimum concentration that can be
reported by the method referenced and the sample matrix. The reporting limit must not be
confused with any regulatory limit. Analytical results are reported to three significant
figures for quality control and calculation purposes.
Thank You,
Approved by:
K I F Digitally signed y e . by Kyle F. Gross
Date:
Gross 2016.08.18
08:18:25 -06'00'
Laboratory Director or designee
Report Date: 8/17/2016 Page I of 52
All analyses applicable to the CWA. SDWA, and RCRA rue perfOrmed in accordance to NELAC protocols Pertinent sampling information is locoled on the utlached COC Conl1dentiol Business lnrormution: This report is provided for the exclusi\ e use oft he
~ddressee Pri\ ile~es o,F sub,.seq~Jent ~1;e of the ~~e of this .cm~pnny or nny 1~mbe1 of its starr, or reproduclio~ ~fthis repo~ in .con~1ection ... with the"'!' ertisement. P~?motio.n ~I' sale of:U~) ~rod~cl or Pl.ocess, ~~·in ~onn~c~ion w!th lh~ r~·publication of this 1epor1
SAMPLE SUMMARY
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
Lab Set ID: 1608133
Date Received: 8/5/2016 1040h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
3440 South 700 West
1608133-001A TW4-34R 08022016 8/2/2016 725h Aqueous Anions, E300.0
~alt Lake City, UT 84119 1608133-00lB TW4-34R 08022016 8/2/2016 725h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-001C TW4-34R_08022016 8/2/2016 725h Aqueous VOA by GC/MS Method
8260C/5030C
Phone: [phone] 1608133-002A TW4-34_08032016 8/3/2016 807h Aqueous Anions, E300.0
1608133-002B TW4-34 08032016 8/3/2016 807h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1608133-002C TW4-34 08032016 8/3/2016 807h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260C/5030C
~-mail: [e-mail] 1608133-003A TW4-35_08032016 8/3/2016 814h Aqueous Anions, E300.0
1608133-003B TW4-35_08032016 8/3/2016 814h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1608133-003C TW4-35 08032016 8/3/2016 814h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-004A TW4-23_08032016 8/3/2016 823h Aqueous Anions, E300.0
Kyle F. Gross 1608133-004B TW4-23_08032016 8/3/2016 823h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-004C TW4-23_08032016 8/3/2016 823h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1608133-00SA TW4-27_08032016 8/3/2016 834h Aqueous Anions, E300.0
Jose Rocha 1608133-00SB TW4-27 08032016 8/3/2016 834h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1608133-00SC TW4-27 08032016 8/3/2016 834h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-006A TW4-14 08032016 8/3/2016 840h Aqueous Anions, E300.0
1608133-006B TW4-14_08032016 8/3/2016 840h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-006C TW4-14 08032016 8/3/2016 840h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-007A TW4-30_08032016 8/3/2016 850h Aqueous Anions, E300.0
1608133-007B TW4-30_08032016 8/3/2016 850h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-007C TW4-30 08032016 8/3/2016 850h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-008A TW4-26 08032016 8/3/2016 900h Aqueous Anions, E300.0
1608133-008B TW4-26 08032016 8/3/2016 900h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-008C TW4-26 08032016 8/3/2016 900h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-009A TW4-05 08032016 8/3/2016 908h Aqueous Anions, E300.0
1608133-009B TW4-05 08032016 8/3/2016 908h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-009C TW4-05_08032016 8/3/2016 908h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-010A TW4-18 08032016 8/3/2016 917h Aqueous Anions, E300.0
1608133-010B TW4-18 08032016 8/3/2016 917h Aqueous Nitrite/Nitrate (as N), E353.2
Report Date: 8/17/2016 Page 2 of 52
A \Ianni) ses applicable to the CWA SDWA. and RCRA ore perfom1ed in accordance to NELAC protocols Pertinent sampling information is locoted on the attached COC. Conlidentinl Business lnformDlion: This repon is provided fort he exclusi\·e use oft he
~ddressee Prh ile~es o~sub .. seq~enl ~~~e of the ~~1e of this .cm~pun~ or nil) ~~~berofils starr, or reproductio~ ~fthis repo~ in ~on~ection ... with the Cl~\er1isement, P~?moti~n OJ" sale of ?J!) ~rod~cl or P~?cess, ~r in ~onn:c.tion w!th th~ r~-publica1ion of lhis 1eport
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Project: 3rd Quarter Chloroform 2016
American West Lab Set ID: 1608133
ANALYTICAL LABORATORIES Date Received: 8/5/2016 1040h
Lab Sample ID Client Sample ID Date Collected Matrix Analysis
1608133-0IOC TVV4-18 08032016 8/3/2016 917h Aqueous VOA by GC/MS Method
3440 South 700 West 8260C/5030C
1608133-011A TVV4-09_08032016 8/3/2016 926h Aqueous Anions, E300.0
~alt Lake City, UT 84119 1608133-011B TVV4-09 08032016 8/3/2016 926h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-011C TVV4-09_08032016 8/3/2016 926h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-012A TVV4-16 08032016 8/3/2016 932h Aqueous Anions, E300.0 Phone: [phone] 1608133-0128 TVV4-16 08032016 8/3/2016 932h Aqueous Nitrite/Nitrate (as N), E353.2
Toll Free: [phone] 1608133-012C TVV4-16 08032016 8/3/2016 932h Aqueous VOA by GC/MS Method
Fax: (80 I) 263-8687 8260C/5030C
~-mail: [e-mail] 1608133-013A TVV4-33 _08042016 8/4/2016 758h Aqueous Anions, E300.0
1608133-0138 TVV4-33 08042016 8/4/2016 758h Aqueous Nitrite/Nitrate (as N), E353.2
web: www.awal-labs.com 1608133-013C TVV4-33 08042016 8/4/2016 758h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-014A TVV4-29_08042016 8/4/2016 805h Aqueous Anions, E300.0
1608133-0148 TVV4-29_08042016 8/4/2016 805h Aqueous Nitrite/Nitrate (as N), E353.2 Kyle F. Gross 1608133-014C TVV4-29 08042016 8/4/2016 805h Aqueous VOA by GC/MS Method
Laboratory Director 8260C/5030C
1608133-015A TVV4-06_08042016 8/4/2016 813h Aqueous Anions, E300.0
Jose Rocha 1608133-0158 TVV4-06_08042016 8/4/2016 813h Aqueous Nitrite/Nitrate (as N), E353.2
QA Officer 1608133-015C TVV4-06 08042016 8/4/2016 813h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-016A TVV4-08_08042016 8/4/2016 819h Aqueous Anions, E300.0
1608133-0168 TVV4-08 08042016 8/4/2016 819h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-016C TVV4-08_08042016 8/4/2016 819h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-017A TVV4-07 08042016 8/4/2016 825h Aqueous Anions, E300.0
1608133-0178 TVV4-07 08042016 8/4/2016 825h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-017C TVV4-07_08042016 8/4/2016 825h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-018A TVV4-10_08042016 8/4/2016 831h Aqueous Anions, E300.0
1608133-0188 TVV4-10 08042016 8/4/2016 831h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-018C TVV4-10_08042016 8/4/2016 831h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-019A TVV 4-70 08032016 8/3/2016 823h Aqueous Anions, E300.0
1608133-0198 TVV4-70_08032016 8/3/2016 823h Aqueous Nitrite/Nitrate (as N), E353.2
1608133-019C TVV4-70_08032016 8/3/2016 823h Aqueous VOA by GC/MS Method
8260C/5030C
1608133-020A Trip Blank 8/2/2016 Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 8/17/2016 Page 3 of 52
All nnnlyses applicnble to the CWA. SDWA. and RCRA ate performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COC Con!idential Business Information: This report is provided for the exdusi'e use of the
~ddressee Plirile~es o.fsu~seq~tent ~~e or the ~~e of this .cOI'l_lPllll) or nn) ~mber of ils staff, or reproductio_~ ~f this repory in ~on~ection .. "ith the o.~' ertisement. P~?molio.n ~r ~ale of~~).~· odl~cl or pr.?cess, ~r in ~onn~c~ion "'!lh 1h~ n~-publica1ion 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 Case Narrative
Client:
Contact:
Energy Fuels Resources, Inc.
Garrin Palmer
Project:
Lab SetiD:
Sample Receipt Information:
Date of Receipt:
Date(s) of Collection:
Sample Condition:
C-0-C Discrepancies:
3rd Quarter Chloroform 2016
1608133
8/5/2016
8/2-8/4/2016
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, indicating no
apparent matrix interferences.
Corrective Action: None required.
Report Date: 8/17/2016 Page 4 of 52
All onal)·ses applicnble to tht! CW A. SDWA. and RCRA are perfomted in accordance to NELAC protocols. Pe1tinent sampling information is located on the attached COC Confidential Business Information: This repor1 is provided for the exclush e use of the
~ddressee Pri\ ile~es o_fsub .. seq~lent ~~~e of the ~~1e of this .cm~po.ny or ony 1~7mbe1 of its st~ff, or reproductio~ ~f this repo~ in .con~tection .. \\ilh the a~\ er1ise~ent, P~?motio,n ~r saJe of ?J~Y ~Jodl~cl or PJ,?cess, ?I in 7onn~c~ion w!th th~ n;:·publicnlion of lhis report
3440 South 700 West
'alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (801 ) 263-8687
!-mail: [e-mail]
web: www.awal-Iabs.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:
3rd Quarter Chloroform 2016
1608133
8/5/2016
8/2-8/4/20 16
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: 8/17/2016 Page 5 of 52
All analyses a[J!Jiicoble to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the au ached COC Conlidentinl Business lnfonnalion: This report is provided for the e.xdusi,·e use of1he
~ddressee Pri' ile~es o,r sub~seq~ent ~~e of the ~~e of this .co",lpany or M) ~~~mber of its staff, or reproductio~ ~f this repo~ in ~011~1ection .. "~th the ~~er1ise1'?ent, P~?motio,n ~~ sale of~!). ~rod~ct or P•.ocess, ~r· in ~nn~c~ion w!th th~ r~-publicntion of this repon
ANAlYTICAl lABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608133
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone]. Fax: [phone]
e-mail: [e-mail], web: www.awal-Jabs.com
_QC SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
Project: 3rd Quarter Chloroform 2016 QC Type: LCS
Analyte Result Units Method
Lab Sample ID: LCS-R92697 Date Analyzed: 08/10/2016 1139h
Test Code: 300.0-W
Chloride 5.09 mg!L E300.0
Lab Sample ID: LCS-R92926 Date Analyzed: 08/16/2016 1830h
Test Code: 300.0-W
Chloride 5.24 mg!L E300.0
Lab Sample ID: LCS N02-R92553 Date Analyzed: 08/05/2016 1558h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 1.03 mg!L E353.2
Lab Sample ID: LCS N03-R92553 Date Analyzed: 08/05/2016 1600h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.961 mg!L E353.2
Lab Sample ID: LCS-R92554 Date Analyzed: 08/05/2016 1638h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.944 mg!L E353.2
MDL
0.00516
0.00516
0.00833
0.00833
0.00833
Reporting
Limit
0.100
0.100
0.0100
0.0100
0.0100
Amount
Spiked
5.000
5.000
1.000
1.000
1.000
Spike Ref.
Amount %REC
0 102
0 105
0 103
0 96.1
0 94.4
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
ReportDate: 8/17/2016 Page45of52
analyses apphcable to the CW A. SDWA, and RCR.A are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC ConfidentiaJ Business Information: This report is provided for the exclusive use of the addressee. Privileges of subsequent use oftt
ne of this company or any member of its staff. or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection wlth the re-publication of this report for any purpose other than for the addressee will be granted only on conlact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608133
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R92697 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R92926 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R92553 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
Lab Sample ID: MB-R92554 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
08/10/2016 ll22h
mg!L E300.0 0.00516 0.100
08/16/2016 1813h
mg!L E300.0 0.00516 0.100
08/05/2016 1557h
mg/L E353.2 0.00833 0.0100
08/05/2016 1637h
mg/L E353.2 0.00833 0.0100
Limits
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
ReportDate: 8/17/2016 Page46of52
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 [nformation: This report is provided for the exclusive use of the addressee. Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process, or in connection with the re-publication of this report for any purpose other than for the addressee will be granted on]y on contact This
American West
ANAlYTICAl LABORATORIES
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
we Lab Set ID: 1608133
Project: 3rd Quarter Chloroform 2016
Analyte Result Units Method
Lab Sample ID: 1608133-00SAMS Date Analyzed: 08/10/2016 1452h
Test Code: 300.0-W
Chloride 132 mg/L E300.0
Lab Sample ID: 1608133-013AMS Date Analyzed: 08/10/2016 1814h
Test Code: 300.0-W
Chloride 155 mg/L E300.0
Lab Sample ID: 1608133-008AMS Date Analyzed: 08/16/2016 1940h
Test Code: 300.0-W
Chloride 40.9 mg/L E300.0
Lab Sample ID: 1608133-002BMS Date Analyzed: 08/05/2016 1617b
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.3 mg!L E353.2
Lab Sample ID: 1608133-0llBMS Date Analyzed: 08/05/2016 1640h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 12.5 mg!L E353.2
MDL
0.103
0.103
0.0258
0.0833
0.0833
Reporting
Limit
2.00
2.00
0.500
0.100
0.100
Dept:
QC Type:
Amount
Spiked
100.0
100.0
25.00
10.00
10.00
MS
Spike Ref.
Amount %REC
27.1 lOS
48.5 106
13.9 108
0.726 106
2.11 103
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
ReportDate: 8/17/2016 Page47of52
anaJyses 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 fnformation: This report is provided for the exclusive use of the addressee Privileges of subsequent use oft}-
ne of this company or any member of il..s 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
_Q_C SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1608133 Dept: we
Project: 3rd Quarter Chloroform 2016 QCType: MSD ----
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample 10: 1608133-00SAMSD Date Analyzed: 08/10/2016 1508h
Test Code: 300.0-W
Chloride 133 mg/L E300.0 0.103 2.00 100.0 27.1 106 90-110 132 0.562 20
Lab Sample 10: 1608133-013AMSD Date Analyzed: 08/10/2016 1831h
Test Code: 300.0-W
Chloride 154 mg/L E300.0 0.103 2.00 100.0 48.5 106 90-110 155 0.274 20
Lab Sample 10: 1608l33-008AMSD Date Analyzed: 08/16/2016 1957h
Test Code: 300.0-W
Chloride 40.6 mg!L E300.0 0.0258 0.500 25.00 13.9 107 90-110 40.9 0.889 20 -Lab Sample 10: 1608133-002BMSD Date Analyzed: 08/05/2016 1619h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 11.6 mg!L E353.2 0.0833 0.100 10.00 0.726 109 90-110 11.3 2.35 10
Lab Sample 10: 1608133-0llBMSD Date Analyzed: 08/05/2016 1641h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 12.6 mg!L E353.2 0.0833 0.100 10.00 2.11 105 90-110 12.5 1.36 10
Report Date: 8117/2016 Page 48 of 52
ana1yses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC Confidential Business Information: This report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of thjs 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 f01 any purpose other than for the addressee will be granted only on contact. This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608133
Project: 3rd 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.awai-Iabs.com
_QC SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS VOC-2 080816A Date Analyzed: 08/08/2016 1148h
Test Code: 8260-W-DEN100
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromotluorobenzene
Surr: Dibromotluoromethane
Surr: Toluene-d8
Lab Sample ID: LCS VOC-1 080916A
Test Code: 8260-W-DENIOO
Chloroform
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.4
19.4
48.3
49.4
48.7
48.6
Date Analyzed:
22.5
52.5
48.8
52.3
49.8
J.Lg/L SW8260C 0.153 1.00 20.00 0 97.0
J.Lg/L SW8260C 0.172 1.00 20.00 0 97.0
J.Lg/L SW8260C 50.00 96.5
J.Lg/L SW8260C 50.00 98.8
J.Lg/L SW8260C 50.00 97.5
J.Lg/L SW8260C 50.00 97.1
08/09/2016 1141h
J.Lg/L SW8260C 0.153 1.00 20.00 0 113
J.Lg/L SW8260C 50.00 105
J.Lg/L SW8260C 50.00 97.7
J.Lg/L SW8260C 50.00 105
J.Lg/L SW8260C 50.00 99.5
Limits
85-124
71 -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: 8/17/2016 Page 49 of 52
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 Information: This report is provided for the exc1usive use of the addressee. Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be ,b'fanted only on contact. This
Client: Energy Fuels Resources, Inc.
LabSetiD: 1608133
Project: 3rd 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
_Q_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 080816A Date Analyzed: 08/08/2016 1228h
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 080916A
Test Code: 8260-W-DENIOO
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
< 1.00
< 1.00
< 1.00
< 1.00
50.4
51.4
49.0
50.0
Date Analyzed:
< 1.00
54.8
51.2
52.5
50.8
Jlg/L SW8260C 0.504
Jlg/L SW8260C 0.153
Jlg/L SW8260C 0.163
Jlg/L SW8260C 0.172
Jlg/L SW8260C
Jlg/L SW8260C
Jlg/L SW8260C
Jlg/L SW8260C
08/09/2016 1220h
Jlg/L SW8260C 0.153
Jlg/L SW8260C
Jlg/L SW8260C
Jlg/L SW8260C
Jlg/L SW8260C
1.00
1.00
1.00
1.00
1.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
50.00
101
103
97.9
99.9
110
103
105
102
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 o;. RPD Limit Qual
Report Date: 8/17/2016 Page 50 of 52
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·publicatlon of this repon for any purpose other than for the addressee w;n be granted only on contact. This
ANALYTICAL
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608133
Project: 3rd 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.awa1-labs.com
_QC SUMMARY REPORT
Contact: Garrin Palmer
Metbod MDL
Reporting
Limit
Dept: MSVOA
QCType: MS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1608133-00ICMS Date Analyzed: OB/OB/2016 1407h
Test Code: B260-W-DENIOO
Chlorofonn
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Lab Sample ID: 1608166-00JGMS
Test Code: B260-W-DENIOO
Chlorofonn
Surr: I ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
IB.7 Jlg/L SW8260C
19.0 Jlg/L SW8260C
4B.5 Jlg/L SW8260C
4B.5 Jlg/L SW8260C
4B.9 Jlg/L SW8260C
47.4 Jlg/L SW8260C
Date Analyzed: OB/09/2016 1359h
33.B Jlg/L SW8260C
53.B Jlg/L SW8260C
49.2 Jlg/L SW8260C
53.4 Jlg/L SW8260C
52.0 J,lg/L SW8260C
0.153 1.00
0.172 1.00
0.153 1.00
20.00
20.00
50.00
50.00
50.00
50.00
20.00
50.00
50.00
50.00
50.00
0
0
12.6
93.5
95.0
97.1
97.1
97.7
94.B
106
lOB
9B.3
107
104
Limits
50-146
30-192
72-151
BO-!52
BO-124
77-129
50-146
72-151
BO-152
BO-124
77-129
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: B/17/2016 Page 51 of 52
analyses applicable to the CWA. SDWA, and RCRA are perfonned in accordance to NElAC protocols Peninent sampling information is located on the attached COC Confidential Business Infonnation; This report is provided for the e.xclusive use of the addressee. Privileges of subsequent use of ti-
ne of this company or any member of its staff. or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or ln connection wlth the re·publ icatlon 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: 1608133
Project: 3rd 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-Jabs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: MSD
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1608133-001CMSD Date Analyzed: 08/08/2016 1427h
Test Code: 8260-W-DEN100
Chloroform
Methylene chloride
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-dB
Lab Sample ID: 1608166-00JGMSD
Test Code: 8260-W-DENIOO
Chloroform
Surr: 1,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
19.2
19.5
48.9
48.6
49.1
48.0
Date Analyzed:
33.9
53.6
48.3
52.3
50.9
J.lg/L SW8260C 0.153
J.lg/L SW8260C 0.172
J.lg/L SW8260C
J.lg/L SW8260C
J.lg/L SW8260C
J.lg/L SW8260C -08/0912016 1419h
J.lg/L SW8260C 0.153
J.lg/L SW8260C
J.lg/L SW8260C
J.lg/L SW8260C
J.lg/L SW8260C
1.00
1.00
1.00
20.00
20.00
50.00
50.00
50.00
50.00
20.00
50.00
50.00
50.00
50.00
0
0
12.6
96.0
97.6
97.8
97.2
98.3
96.1
106
107
96.6
105
102
Limits
50-146
30-192
72-lSI
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 "'o RPD Limit Qual
18.7 2.59 25
19 2.70 25
33.8 0.236 25
Report Date: 8/17/2016 Page 52 of 52
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 oftJ-
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 on]y on contact This
.. _
American West Analytical Laboratories· .UL
Denison
WORK ORDER Summary WorkOrder: 1608133
Due Date: 8/16/2016
Page 1 of4
Client:
Client ID:
Project:
Comments:
SampleiD
1608133-001A
1608133-001B
1608133-001 c
1608133-002A
1608133-002B
1608133-002C
1608133-003A
1608133-003B
1608133-003C
1608133-004A
1608133-004B
1608133-004C
1608133-00SA
1608133-00SB
1608133-00SC
,. ' P.rinted: 8~51?,Q16
Energy Fuels Resources, Inc.
DENlOO Contact: Garrin Palmer
3rd 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 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.;
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
~4-34ll_08022016 812/2016 0725h 8/5/2016 1040h 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; #of Analytes: 4/ #of Surr: 4
~4-34_08032016 8/3/2016 0807h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL A11alytes: N03N02N
8260-W-DEN100 VOCFridge
Test Group: 8260-W-DEN100; #of Analytes: 41 # ofSurr: 4
~4-35_08032016 8/3/2016 0814h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260-W-DEN100 VOCFridge
Test Group: 8260-W-DEN100; #of Analytes: 4 / # ojSurr: 4
~4-23_08032016 813/2016 0823h 8/S/2016 1040h 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-DEN100; #of Analytes: 41 # ofSurr: 4
~4-27_08032016 8/3/2016 0834h 8/S/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
8260-W-DEN100 VOCFridgc
Test Group: 8260-W-DENJOO; #of Analytes: 41 # of Surr: 4
3
3
3
FORLABORAT9.f3)'USEONLY[fiii01J.Ipnpage,1]:.,. ~M ,D RT 0 .. CN [;;:;;), ~'· T~I)~ OC.Q . , .. '-=-1.....,1_.,.. ~,~0~-.;:;--.-:---coc Ernailed r!rrn I
,. -.'\ .... ~( --"'· __ ., ...-... (<> C"" •• # ... ~ ••
WORK ORDER Summary WorkOrder: 1608133 Page2 of4
Client: Energy Fuels Resources, Inc. Due Date: 8/16/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1608l33-006A ~4-14_08032016 8/3/2016 0840h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608 133-006B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1608133-006C 8260-W-DEN100 VOCFridge
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Su": 4
1608133-007A ~4-30_08032016 8/3/2016 0850h 8/5/2016 1 040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-0078 N02/N03-W-353.2 df -no2/no3
1 SEL Analyzes: N03N02N
1608133-007C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4/ #of Surr: 4
1608133-008A ~4-26_08032016 8/3/2016 0900h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-0088 N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1608133-00SC 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4 / #of Su": 4
1608133-009A ~4-05_08032016 8/3/2016 0908h 8/5/2016 1040h 300.0-W Aqueous df-wc
I SEL Ana lyles: CL
1608133-0098 N02/N03-W-353.2 df -no2/no3
1 SEL Analytes: N03N02N
1608133-009C 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Surr: 4
1608133-010A ~4-18_08032016 8/3/2016 0917h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-010B N02/N03-W-353.2 df·no2/no3
1 SEL Analytes: N03N02N
1608133-010C 8260-W -DEN100 VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4 I # of Su": 4
1608133-011A ~4-09 _08032016 8/3/2016 0926h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-0118 N02/N03-W-353.2 df-no2/no3
I SEL Analytes: N03N02N
1608133-0llC 8260-W-DEN100 VOCFridge 3
Test Group: 8260-W-DENI 00; #of Analytes: 4 I # ofSurr: 4
1608133-012A ~4-16_08032016 8/3/2016 0932h 8/5/2016 1040h 300.0-W Aqueous df·wc
I SEL Analytes: CL
Printed: 8/5/2016 FOR LABORATORY USE ONLY [fill out on page 1]:. %MD RTO CN 0 TAT 0 QCO HOK __ HOK __ HOK~ COCEmailed
:':"·.-....... ·'.
WORK ORDER Summary· Work Order: 1608133 Page3 of4
Client: Energy Fuels Resources, Inc. Due Date: 8/16/2016
SampleiD Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
1608133-012B 1W4-16_08032016 8/3/2016 0932h 8/5/2016 I 040h N02/N03-W-353.2 Aqueous df-oo2/no3
1 SEL Analytes: N03N02N
1608133-012C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Surr: 4
1608133-0BA 1W4-33_08042016 8/4/2016 0758h 8/512016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-0 13B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1608133-013C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN100; #of Analytes: 4 l #ofSurr: 4
1608133-0I4A 1W4-29 _08042016 8/4/2016 0805h 8/5/20I6 I 040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-0I4B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1608133-014C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DENJOO; #of Analytes: 4 I # of Surr: 4
I608133-015A 1W4-06_08042016 8/4/20I6 0813h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608 133-0 I 5B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
I608133-0ISC 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I# of Surr: 4
I608133-016A 1W4-08_08042016 8/4/20I6 08I9h 8/5/20I6 I040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
I608133-016B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
1608133-0I6C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; #of Analytes: 4 I # of Surr: 4
1608133-0I?A 1W4-07_08042016 8/412016 0825h 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
1608133-017B N02/N03-W-353.2 df-no2/no3
1 SELAna/ytes: N03N02N
1608133-017C 8260-W-DENlOO VOCFridge 3
Test Group: 8260-W-DEN1 00; # of Analytes: 4 I # of Surr: 4
1608133-018A 1W4-10_08042016 8/412016 083Ih 8/5/2016 1040h 300.0-W Aqueous df-wc
1 SEL Ana/ytes: CL
I608133-018B N02/N03-W-353.2 df-no2/no3
1 SEL Analytes: N03N02N
Printed: 8/5/2016 ,FOR LABORATORY USE ONLY [fill out on page 1]: 'YoM 0 RTO .. CNO TAT.O . QCO H,OK __ HOK __ HOK __ COC,Emailed
WORK ORDER Summary
Client: Energy Fuels Resources, Inc.
SampleiD Client Sample ID
1608133-018C 1W4-10_08042016
1608133-019A 1W4-70_08032016
1608133-019B
1608133-0 19C
1608133-020A Trip Blank
WorkOrder: 1608133
Due Date: 8/16/2016
Collected Date Received Date Test Code Matrix Sel Storage
8/412016 0831h 8/S/20 16 1 040h 8260-W-DENlOO Aqueous VOCFridge
Test Group: 8260-W-DENIOO; #of Analytes: 4/ # ofSu": 4
8/3/2016 0823h 8/S/2016 1040h 300.0-W Aqueous df-wc
I SEL Analytes: CL
N02/N03-W-3S3.2 df-oo2/oo3
I SELAnalytes: N03N02N
8260-W-DENlOO VOCFridge
Test Group: 8260-W-DENI 00; #of Analytes: 4/ #of Surr: 4
8/2/2016 8/512016 1040h 8260-W-DENlOO Aqueous VOCFridge
Test Group: 8260-W-DENJOO; #ofAnalytes: 4/#o/Surr: 4
Page4 of4
3
3
3
Printed: 8/5/2016 FORLABORATORYUSEONLY[filloutonpage1]: .%M 0 RT 0 CN 0 TAT 0 QCO HOK __ HOK __ HOK __ , _ COC Emailed,___ ___ _
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake Clly, UT 84115
Phone# [phone] Toll Free# [phone]
Fax# [phone] Email [e-mail]
www.awal-labs.com
Client Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact Garrin Palmer
Phone#: [phone] Cell #: 435 459 9463
[e-mail]; [e-mail].c" ....... i
Email: dturk@~.com
Project Name: 3rd Quarter Chloroform 2016
CHAIN OF CUSTODY
All analysis will be conducted using NELAP accredfted methods and all dala will ba reported using AWAL's standard analyte lists and reporting
limits (POL) unless specifically requested otherwise on this Chain of Custody and/or attached documentation.
I~ o &--r 33
AWAL Lab Sample Set#
Page 1 of 2 I ac Level: 1-Tum Around Time: Unlessa4hor ...._.,..,us have been made, I
signed rvpo1t1 will be emalled by 5:00 pm on
3 Standard 1t>o day !hay oto due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For:
Laboratory .Use Only
1 Shipped hilnd detivered
S.m?aW .. ·\A 15
For Compliance With: 2 ~ l I/J
0 NELAP ~~ ~ ..._IY 0 RCRA 3 Tlll1)p0r.IIUIO • _ 0 CWA ___ c
0 SDWA ~ Rl><-lllYedBrol<!!!Vl .. klng ..{ "U
0 ELAP I A2LA (lrtllltD!'cd)l Soalpdi'\
0 NLLAP Y \!:_)
Project#: -----------------------------cq ,..;
0
c:i 0 Non-Compliance
0 other.
5 Propol1y Pr...,.,od ~odalbencll N PO#:
SampLer Name: Tanner Holliday
Sample 10:
Date
Sampled
1 ITW4-34R_08022016 I 8/2/2016
I~TW4-16_08032016 I 8/3/2016
3ITW4-33_08042016 I 8/4/2016
Aellnq<.ishad by: r
Signature U " ~A.
Print Name:
Rellnqulihodby: I signature
Print Name;
RelinqWhed by:
SI!JNI!ur•
P~nl Name:
ROllnqUiGIIOd by:
iSIIlflblure
Print Name:
Gc.rr-1"'-
?talA A-Date: 'a l"th~
?A.\~ lllme: l23o
Da1e:
'Tima:
Oa1e:
nme:
Dale:
Time:
"' I!! -~ '2 " t') " iii :rg :::; 0 c: !;!:; 0 CD ..... Time l) 15. C'il 0 E 0 Sampled "' .. U) !;!:;
7~ 5 w X
807 5 w X
814 5 w X
823 5 w X
834 5 w X
840 5 w X
850 5 w X
900 5 w X
908 5 w X
917 5 w
926 5 w X
932 6 w X
758 6 w X
Received by:
Signature
Print Name: 1\
Rooeiv~. j SlgfiDiun> \,_A J/t-.....
Print Name: 1:.--( h-..5-
Received by:
Signature
frlnt Name:
Received by:
Signature
Print Name:
0 ~ G ... 0 0 <o 0 "l 0 ~ "' .:! .,
tJ 0 0 :>
X X
X X
X X
X X
X X
X X
X X
X X
X X
X X
X X
/
~
~~
l
Dale:
(Time:
A"'"'~/! A-~
/(JL/~ 7
-.J'
Tti-ne:
Date:
fT"ne:
Date:
lime:
Known Hazards
&
Sample Comments
Special Instructions:
y N
6 Recc~Vt<! Within ~~m~ N
See the Analytical Scope of Work for Reporting Limits and VOC
analyte list.
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone# (801) 263-l!686 Totl Free # [phone]
L-~ Fax# [phone] Email [e-mail]
www.awal-lab~.com
Client: Energy Fuels Resources, Inc.
Address: 6425 S. Hwy. 191
Blanding, UT 84511
Contact: Garrln Palmer
Phone#: [phone] Cell#: 435 459 9463
gpalmeriienergyfuels.com: [e-mail]:
Em all: dturk@ener&'l!!e1s.colll
Project Name: Srd Quarter Chloroform 2016
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Sampled
~ TW4-29_08042016 8/4/2016
r TW4-0G_o8o420l6 8/4/2016
~ TW4-08_08042016 8/4/2016
t TW4·07 _08042016 8/4/2016
r TW4-10_o8042016 8/4/2016
~ TWof!-70_08032016 8/3/2016
C Trip Blank 8/2/2016
I Temp Blank
I
0
1
2
3
IW!nquisllod""' (: -Sklnaiure ''7 (! ..o p~ DaiO: 9' I r.t lit..
PrtriNilmll: b6K't-lA PcJ~ ITTrM= I 'l2:o
Rollnq1d!Nd by. D•to: k;r~natt.lft
l'lme:
Prtnl Noma:
Aellnqo.i.shodl:rf.
isTgnal'-1"0
O..lo:
•mo:
Pl!niNomm
ReTJnqt.iolleclby. Dato:
SlQnaturo
llmo:
Print Nomo:
I
Time
Sampled
805
813
819
825
831
823
Received by:
Signature
PrlniNnmo·
CHAIN OF CUSTODY
All analysis will be condl.cted using NELAP accredlted methods and all data will be reported using AWAL's standard analytelisls end reporting
limits (Pal) unii!S6 speclllcaly r~ed otha<Wise on this Chain of Custody and/or attaohed documenlation.
QC Level: I Turn Around Time: Unless other anangemenls have been made,
signed reports will be emailed by 5:00 pm on
3 Standard the day they are due,
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Filtered For.
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAP/A2LA
s 0 NLLAP
~ 0 D Non-Compliance
M 0 D Other. ll') {") u ~ )( !2 .... 0 a> 0 " '0: "' 'D ... 1ii 0 0 "l
" :::;; 0 IQ Known Hazards 0 " 1!: ll') ..... ~ ., () a C'il 0 & 0 E 0 0 0 .. Sample Comments .. CJ) 1!: :>
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
5 w X X X
3 w X
1 w
Date: Special instructions:
I ;/ llmo:
/~ ()~ '~3
AWAL Lab Sample Set#
Page 2 of 2
r ue Da1e: I
Labora!ory. Use 0nly 7;1;5
1 Shipped or deliveied
2 ,._om~
3 Temperature ~ •c
4 Allcelvod Broi<ar>'t.oolclng
(lmpropertySeol([)
V N
~~oct y N
Cl>oc .. bench
N
G Reeltved Wlfh\n
c5~ N
GOC Tapo Was.
1 "'-"!on O<Jier Package C) N NA
2 ~a!< on on Outer Pi!CI<D~o
, V N NA
3 ; Present oo Sampla ~
Y N NA
Unbroken on ~a(Jiph! 4 eJ y N
Olscr.pard .. Botlwlen Sample
V N LobolsandCOCIIV
R_ocllv~~~ m. / oat'8-,?r~ See the Analytical Scope of Work for Reporting Umits and VOC
Sognatwo analyte list. ....... £(tiL ... '\) iZ.J _;'__{ Time: //') r-{0 Print Nome:
Received by: ( Date:
Signature
Time:
Print Name:
Received by: Date:
Signature
Time:
Print Name:
Preservation Check Sheet
s le Set Ext' --doH
Analysis Preservative J 2 3 l( S" G 7 ~ 4' /<I Jl
Ammonia pH<2H2S04
COD pH<2HzS04
Cyanide pH>12
NaOH
Metals oH<2HN03
NOz&N03 pH<2H2S04 ~ Ye'5 ~') ~ ikS Xe'> IJ/c; ~~ }4~ Yer yfo~
O&G pH<2HCL ~~· I" '
Phenols oH<2H2S04
Sulfide pH>9NaOH,
ZnAcetate
TKN pH<2H2S04
TP04 _ _ _pH <2 H2S04
Procedure:
Frequency:
1)
2)
3)
4)
5)
6)
7)
Pour a small amount of sample in the sample lid
Pour sample from Lid gently over wide range pH paper
Do Not dip the pH paper in the sample bottle or lid
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 Set ID: / <i 0~ /3 J
p f4 k f ,..cr<rJ
12 1:!; 1'/ j$ /~ f) IY' )"'{
!~1 ~ ~ -~ ~ ~~ 1 ~-~ v
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 S. Hwy 191
Blanding, UT 84511
TEL: [phone]
RE: 3rd Quarter Chloroform 2016
Dear Garrin Palmer: Lab Set ID: 1608399
American West Analytical Laboratories received sample(s) on 8/19/2016 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 5 e G ~~~~~=Jose G. Rocha,
• o=American West Analytical
Laboratories, ou, R 0 c h a ~:~[e-mail].
Date: 2016_08.26 09:42:42
-06'00'
Laboratory Director or designee
Report Date: 8/26/2016 Page I of 15
All anal~ ses applicable to the CW A. SDWA. and RCRA are perfom1ed in accordance to NELAC protocols. Pertinent sampling information is located on the altached COC. Confidential Business Jnformation: This repor1 is prO\•lded for the exclusi\e use of the
~ddressee Pri' ile~es o.r sub~seg~ent ~~~e of the ~:u.ne of this .c01~pany or an)" ~~~mbe1· of its staff, or reproductio.~ ~~this repo~ in .con~leclion ... "·ith the a~Yertisemenl. P~?motio.n or sale of ?J~) ~rodL~cl or P~?cess. ~r in ';Onn~c~ion w~lh 1h~ r~-publicalion of this report
American West
ANALYTICAL LABORATORIES
3440 South 700 West
;alt Lake City, UT 84119
Phone: [phone]
Toll Free: [phone]
Fax: [phone]
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
SAMPLE SUMMARY
Client:
Project:
Lab Set ID:
Energy Fuels Resources, Inc.
3rd Quarter Chloroform 2016
1608399
Date Received: 8/19/2016 1040h
Lab Sample ID Client Sample ID
1608399-001A MW-32 08172016
1608399-0018 MW-32 08172016
1608399-001C MW-32 08172016
1608399-002A Trip Blank
Date Collected
8/17/2016 1235h
8/17/2016 1235h
8/17/2016 1235h
8/17/2016
Contact: Garrin Palmer
Matrix Analysis
Aqueous Anions, E300.0
Aqueous Nitrite/Nitrate (as N), E353.2
Aqueous VOA by GC/MS Method
8260C/5030C
Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 8/26/2016 Page 2 of 15
All anol~ ses applicoble to the CWA. SDWA. and RCRA me performed in accordance to NELAC protocols_ Pertinent sampling informalion is located on lhe aU ached COC Conlidential Business Information: This report is prm ided for the exclusi\ e use of the
~ddressee Pli \ ile~es o.r sub~seq~enl ~·~e of the ~~e of this .em~ pan~ or an~ ~mbet of its stnff, or reproductio~ ~r this repo~ in ;o~leclion_ \Vith the a~\ enisemenl, p~omoti~n or ~ale of~) rrodt!cl or p~ocess, ~r in ~nn~c~ion ''!'h the r:_-publication of this reporl
3440 South 700 West
;alt Lake City, UT 84119
Phone:[phone]
Toll Free: [phone]
Fax: (80 I) 263-8687
~-mail: [e-mail]
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
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:
3rd Quarter Chloroform 2016
1608399
8/19/2016
8117/2016
Intact
None
SW-846 8260C/5030C
Volatile Organic Compounds
General Set Comments: No 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: 8/26/2016 Page 4 of 15
All anal) ses applicDble to the CWA_ SDWA and RCRA are perfom1ed in accordance to NELAC protocols Pertinent sampling information is located on Lhe altached COC Confidenlinl Business lnformotion: This report is p•o,•ided for the exclusi\ e use oft he
~ddressee Pri \ ile¥es o; su~seq~ent ~?e of the ~?-'.ne of this .co1~pm1~ or any '!!:mber of its slaJT, or reproductio~ ~f this repo~ in ,con!lection. \\~lh the a~' e1tisemenL P~?molio.n or sale of~~) ~1odL~ct or p1.ocess, ~r in ~onn~c~ion \\'~lh lh~ r~-publication of this repon
ANAL YTICH LAOO RATOR I[Ii
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 SetiD:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-0-C Discrepancies:
3rd Quarter Chloroform 2016
1608399
8/19/2016
8117/2016
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, indicating no
apparent matrix interferences.
Duplicate (DUP): The parameters that required a duplicate analysis had RPDs
within the control limits.
Corrective Action: None required.
Report Date: 8/26/2016 Page 3 of 15
All anal) ses applic11ble to the CWA. SDWA. and RCRA are perl'omted in accordance to NELAC protocols Pertinent sampling informaLion is located on lhe attached COC Confidential Business 1nformation: This report is provided for the exclusi\ e use of the
~ddressee Pri \ ile~es o.f sub ... seq~enl ~~~e of the ~~1e of this .cm~pan~ or nn) ~~~mber of its slaff, or reproductio~ ~r this repo~ in ;on~techon ... \\ilh the at!vertisement. P~?motio.n or ~aJe of~) ~rodt~cl or p~ocess, ~r in ~onn:c~ion \\ !lh th~ r:-publicalion of lhis repon
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd 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
Contact: Garrin Palmer
Dept: we
Method MDL
Reporting
Limit
QC Type: LCS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: LCS-R93109 Date Analyzed: 08/22/2016 1321h
Test Code: 300.0-W
Chloride 5.33 mg/L E300.0 0.00516 0.100 5.000 0 107
Lab Sample ID: LCS-R93046 Date Analyzed: 08/19/2016 1940h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 0.970 mg/L E353.2 0.00833 0.0100 1.000 0 97.0
Limits
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt % RPD Limit Qual
Report Date: 8/26/2016 Page 8 of 15
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 [nformation· Th1s report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West
ANALYTICAL LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB-R93109 Date Analyzed:
Test Code: 300.0-W
Chloride < 0.100
Lab Sample ID: MB-R93046 Date Analyzed:
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) < 0.0100
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fa"X: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Dept: we
QC Type: MBLK
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
08/22/2016 1304h
mg!L E300.0 0.00516 0.100
08/19/2016 1937h
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: 8/26/2016 Page 9 of 15
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: Th1s report is provided for the exclusive use of the addressee. Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement, promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1608399-001AMS Date Analyzed:
Test Code: 300.0-W
Chloride 145
Lab Sample ID: 1608400-007AMS Date Analyzed:
Test Code: 300.0-W
Chloride 1,230
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
Reporting
Units Method MDL Limit
08/22/2016 1355h
mg!L E300.0 0.103 2.00 -08/22/2016 1445h
mg!L E300,0 1.03 20.0
Contact: Garrin Palmer
Dept: we
QCType: MS
Amount Spike Ref.
Spiked Amount %REC
100.0 37.5 108
1,000 150 108
Lab Sample ID: 1608399-001BMS Date Analyzed: 08/19/2016 2018h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 10.2 mg!L E353.2 0.0833 0.100 10.00 0 102
Limits
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit Qual
Report Date: 8/26/2016 Page 10 ofl5
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: This report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of thi.s company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West
ANALYTICAl lABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: 1608399-001AMSD Date Analyzed:
Test Code: 300.0-W
Chloride 144
Lab Sample ID: 1608400-007AMSD Date Analyzed:
Test Code: 300.0-W
Chloride 1,220
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
QCType: MSD
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
08/22/2016 1412h
mg/L E300.0 0.103 2.00 100.0 37.5 107
08/22/2016 1502h
mg/L E300.0 1.03 20.0 1,000 !50 107
Lab Sample ID: 1608399-001BMSD Date Analyzed: 08/19/2016 2019h
Test Code: N02/N03-W-353.2
Nitrate/Nitrite (as N) 10.3 mg/L E353,2 0.0833 0.100 10.00 0 103
Limits
90-110
90-110
90-110
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
RPDRef. RPD
Amt %RPD Limit
145 0.634 20
1230 0.606 20
10.2 0.682 10
Qual
Report Date: 8/26/2016 Page 11 of 15
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC ConfidentiaJ Business Information This report is provided for the exclusive use of the addressee Privileges of subsequent use of ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
ANALYTICAL
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: LCS VOC-1 082216A Date Analyzed:
Test Code: 8260-W-DENlOO
Chloroform 19.2
Methylene chloride 21.7
Surr: 1 ,2-Dichloroethane-d4 49.7
Surr: 4-Bromofluorobenzene 46.1
Surr: Dibromofluoromethane 51.0
Surr: Toluene-d8 48.2
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Dept: MSVOA
QC Type: LCS
Reporting Amount Spike Ref.
Units Method MDL Limit Spiked Amount %REC
08/22/2016 7llh
j!g/L SW8260C 0.153 1.00 20.00 0 95.8
j!g/L SW8260C: 0.172 1.00 20.00 0 109
j!g/L SW8260C: 50.00 99.4
j!g/L SW8260C: 50.00 92.2
j!g/L SW8260C 50.00 102
j!g/L SW8260C 50.00 96.4
Limits
85 -124
71 -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: 8/26/2016 Page 12 of 15
analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sarnpllng information is located on the attached COC Confidential Business [nfonnation: This report is provided for the exclusive use of the addressee Privileges of subsequent use of tl·
ne of this company or any member of its statT, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or ln connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result
Lab Sample ID: MB VOC-1 082216A Date Analyzed:
Test Code: 8260-W-DENlOO
Carbon tetrachloride < LOO
Chloroform < LOO
Chloromethane < LOO
Methylene chloride < LOO
Surr: 1 ,2-Dichloroethane-d4 49.8
Surr: 4-Bromofluorobenzene 47.8
Surr: Dibromofluoromethane 49.7
Surr: Toluene-d8 49.5
Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: (80 I) 263-8686, Toll Free: [phone], Fax: [phone]
e-mail: [e-mail], web: www.awal-labs.com
_ _Q{: SUMMARY REPORT
Contact:
Dept:
QC Type:
Reporting Amount
Method MDL Limit Spiked
Garrin Palmer
MSVOA
MBLK
Spike Ref.
Amount %REC
08/22/2016 75lh
~tg/L SW8260C 0.504 LOO
~tg/L SW8260C 0.153 LOO
llg!L SW8260C 0.163 LOO
llg!L SW8260C 0.172 LOO
~tg/L SW8260C 50.00 99.6
~tg/L SW8260C 50.00 95.6
llg!L SW8260C 50.00 99.5
~tg/L SW8260C 50.00 98.9
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: 8/26/2016 Page 13 of 15
analyses applicable to the CWA. SDWA, and RC'RA are performed in accordance to NELAC protocols Pertinent sampling infonnation 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 ti-
ne of this company or any member of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
American West
ANALYTICAl LABORATORIES
Client: Energy Fuels Resources, Inc.
Lab Set ID: 1608399
Project: 3rd Quarter Chloroform 2016
Analyte Result Units
3440 South 700 West
Salt Lake City, UT 84119
Phone: [phone], Toll Free: [phone], F1L'C [phone]
e-mail: [e-mail], web: www.awal-labs.com
QC SUMMARY REPORT
Contact: Garrin Palmer
Method MDL
Reporting
Limit
Dept: MSVOA
QCType: MS
Amount
Spiked
Spike Ref.
Amount %REC
Lab Sample ID: 1608399-00ICMS Date Analyzed: 08/22/2016 1219h
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
Lab Sample ID: 1608400-006EMS
Test Code: 8260-W-DENIOO
Chloroform
Methylene chloride
Surr: 1 ,2-Dichloroethane-d4
Surr: 4-Bromofluorobenzene
Surr: Dibromofluoromethane
Surr: Toluene-d8
18.9 J.lg/L SW8260C
21.4 J.lg/L SW8260C
50.1 J.lg/L SW8260C
46.4 J.lg/L SW8260C
50.5 J.lg/L SW8260C
47.9 J.lg/L SW8260C
Date Analyzed: 08/22/2016 1017h
3,790 J.lg/L SW8260C
1,110 J.lg/L SW8260C
2,540 J.lg/L SW8260C
2,240 J.lg/L SW8260C
2,560 J.lg/L SW8260C
2,410 J.lg/L SW8260C
0.153 1.00 20.00 0 94.4
0.172 1.00 20.00 0 107
50.00 100
50.00 92.8
50.00 101
50.00 95.9
7.65 50.0 1,000 2950 84.0
8.60 50.0 1,000 0 Ill
2,500 102
2,500 89.6
2,500 103
2,500 96.5
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: 8/26/2016 Page 14 ofl5
analyses applicable to the CWA. SDWA, and RCRA are performed in accordance to NELAC protocols Pertinent sampling information is located on the attached COC. ConfidentiaJ Business Information: This report is prov1ded for the exclusive use of the addressee Privileges of subsequent use of tr
ne of this company or any membeT" of its staff, or reproduction of this report in connection with the advertisement. promotion or sale of any product or process. or in connection with the re-publication of this report for any purpose other than for the addressee will be granted only on contact This
3440 South 700 West
Salt Lake City, UT 84119 Kyle F. Gross
Phone: [phone], Toll Free: [phone]. Fax: [phone] Laboratory Director
e-mail: [e-mail], web: www.awal-labs.com
Jose Rocha
QA Officer
ANAlYTICAL lABORATORIES _QC SUMMARY REPORT
Client: Energy Fuels Resources, Inc. Contact: Garrin Palmer
Lab Set ID: 1608399 Dept: MSVOA
Project: 3rd Quarter Chloroform 2016 QC Type: MSD
-------
Reporting Amount Spike Ref. RPDRef. RPD
Analyte Result Units Method MDL Limit Spiked Amount %REC Limits Amt %RPD Limit Qual
Lab Sample ID: 1608399-00ICMSD Date Analyzed: 08/22/2016 1239h
Test Code: 8260-W-DENIOO
Chloroform 19.8 J.lg/L SW8260C 0.153 1.00 20.00 0 99.0 50-146 18.9 4.71 25
Methylene chloride 19.6 J.lg/L SW8260C 0.172 1.00 20.00 0 98.2 30-192 21.4 8.29 25
Surr: 1,2-Dichloroethane-d4 51.2 J.lg/L SW8260C 50.00 102 72-151
Surr: 4-Bromofluorobenzene 45.6 J.lg/L SW8260C 50.00 91.2 80-152
Surr: Dibromofluoromethane 51.7 J.lg/L SW8260C 50.00 103 80-124
Surr: Toluene-d8 47.7 J.lg/L SW8260C 50.00 95.5 77-129
Lab Sample ID: 1608400-006EMSD Date Analyzed: 08/22/2016 1037h
Test Code: 8260-W-DENIOO
Chloroform 3,650 J.lg/L SW8260C 7.65 50.0 1,000 2950 69.8 50-146 3790 3.82 25
Methylene chloride 1,080 J.lg/L SW8260C 8.60 50.0 1,000 0 108 30-192 ll10 2.74 25
Surr: 1,2-Dichloroethane-<14 2,560 J.lg/L SW8260C 2,500 102 72-151
Surr: 4-Bromofluorobenzene 2,290 J.lg/L SW8260C 2,500 91.4 80-152
Surr: Dibromofluoromethane 2,580 J.lg/L SW8260C 2,500 103 80-124
Surr: Toluene-d8 2,440 J.lg/L SW8260C 2,500 97.5 77-129
Report Date: 8/26/2016 Page 15 of 15
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: 1608399
Due Date: 8/30/2016
Page 1 ofl
Client:
Client ID:
Project:
Comments:
SampleiD
1608399-00 1A
1608399-00 lB
1608399-001C
1608399-002A
Printed: 8/19/2016
Energy Fuels Resources, Inc.
DENlOO Contact: Garrin Palmer
3rd Quarter Chloroform 2016 QC Level: III WO Type: Project
PARush. QC 3 (Summary/No chromatograms). RL ofl ppm for Chloride and VOC and 0.1 ppm forN02/N03-RunN02/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.;
Client Sample ID Collected Date Received Date Test Code Matrix Sel Storage
MW-32_08172016 8/17/2016 1235h 8/19/2016 1040h 300.0-W Aqueous df-wc
1 SEL Analytes: CL
N02/N03-W-353.2 df-no2/no3
I SELAnalytes: N03N02N
8260-W-DEN100 VOCFridge
Test Group: 8260-W-DENJOO; #ofAnalytes: 4/#ofSu": 4
Trip Blank 8/17/2016 8/19/2016 1040h 8260-W-DEN100 Aqueous VOCFridge
Test Group: 8260-W-DENJ 00; #of Analytes: 4 I# of Su": 4
FORLABORATORYUSEONLY[filloutonpage1]: %M 0 RT 0 CN 0 TAT 0 QCO HOK __ _ HOK __ _ HOK___ COC Emailed e 1 , , "' ,
3
3
American West
Analytical Laboratories
463 W. 3600 S. Salt Lake City, UT 84115
Phone II [phone] Toll Free II [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: Garrin Palmer
Phone#: (435} 678-2221 Cell#: 435 459 9463
gpalmer®eacrafuels.com; [e-mail];
Email: [e-mail]&.eom
Project Name: 3rd Quarter Chloroform 2016
Project#:
PO#:
Sampler Name: Tanner Holliday
Date
Sample ID: Sampled
MW-32_08172016 8/17/2016
-r;; ·? '5lcM\ k ~117/lb
:
'
I
0
t
~
Rotinqliohodby: ~~ 'P ~ S'!gtlOluro ,.,~ ..A.A.-ruto: sl, ~~~~~.
Prit~ Name: br:.r-ri .... p c..l ""'-~r-l1mo: I 'Z3o.
RelinqWhod by: !lain;
Slgnalure
n"la:
PnntNomo:
f!oinquiohod by: Date:
SlQMiure nmo:
Pttnt Name:
RotlnQUishll<l by: pato;
Slgnoturo
Tlmo:
Print Nam«
I
Time
Sampled
1235
Received by:
Signature
Prlni Nama:
CHAIN OF CUSTODY
An analysis win b9 COf1ducled using NELAP accredited methods and all data will be reported using AWAL's standard analyle lists and reporting
limits (POL} unless specifically requested otherwise on this Chain of Custody andfor aHached documentation.
ac Level: I Tum Around Time: Un~ other arrangements have been made,
signed reports win b9 emalled by 5:00 pm on
3 Standard the day they are due.
X Include EDD:
LOCUS UPLOAD
EXCEL
Field Fltered For.
For Compliance With:
0 NELAP
0 RCRA
0 CWA
0 SDWA
0 ELAP/A2LA
0 NLLAP
~ 0' 0 Non-Compliance c:i M Cl 0 Other: "' C<) G e ~ !2 ,_ 0 Q) C') 0 <o c: ., Cl C'l ]i ::;; 0 Cl !!!. Known Hazards c: z "' 0 Q) ..... ::t "' ll a. eo! (.J & ·0 E 0 0 0 ., Sample Comments .. rn z >
5 X X X X
3 x X
Oate: Special Instructions:
l1mo:
l&a'i31CJ
AWAL Lab Sample Set ll
Page 1 or 1 rile Date: I
Laboratory Use Only
~mplos WOio: \A t''J ~enddolfivered
2:Am@
3 Tempernwo $~'jf-•c
4 Recei'<ed B-eoldrlg
~~lySeal79
6 P!!>P"'IyPr......,..; ~ . N
kodill bonc:ll
y N
6 RO<ol\rod Within
y {Srm ... N
..
CDC Tape Was:
I 6nl on Outer Pack'!g.e
Y . N NA
2 ~roken on outer PackaQ&
· .. . N .. NA :
:i Present on Sample · 6 Y N· . NA·.
4 Y,-..non ~~ .~ 1 Y N .NA
Ois<:"""""' .. BotW40n S.mpto fo!:-a tf._,c.,
tr,
Received~ j J!L "--lk. ___,/ 0.10! v--/~ !/~ See the Analytical Scope of Work for Reporting Limits and VOC
SlgnatiKO ~ analyte list.
"!.-(~ 1-fv. ./ fllmo: tatfo PrtntNamll:
Received by:
Signature I I Oato:
l1me:·
Print Name:
Received by: Dale:
Signature
rnme:
Prlnl Name: --
.....
AWAL-Analytical Scope ofWork
White Mesa Mill Blanding Utah
Page 11 of 13
Contaminant Analytical
Methods
to be Used
~l Ihorganics
Chloride--....._____... A4500-Cl
B or
~
or E300.0
Sulfate ~ r ~ E300.0
Carbon~03 A2320 B
~bonate as HC03 A2320 B
Reporting
Limit
1 mg/L
~
--tllig/L
1 mg/L
1 mg/L
Volatile Organic Compounds -Chloroform Program
Carbon Tetrachloride SW8260B l.Of.!g/L
or
SW8260C
Chloroform SW8260B 1.0 f.lg/L
or
SW8260C
Dichloromethane SW8260B 1.0 f.lg/L
(Methylene Chloride) or
SW8260C
Chloromethane SW8260B 1.0 f.!g/L
or
SW8260C
~OCs-Tailing~ Impoundment Sample~ Only
1,2,~chlorobenzene SW8270D <10 ug/L
1,2-Dichl~enzene SW8270D <10 ug/L
1 ,3-Dichlorob~ne SW8270D <10 ug/L
1,4-Dichlorobenzen~ SW8270D <10 ug/L
1-Methv lnaphthalene ~ SW8270D <10 ug/L
2,4,5-Trichlorophenol ~8270D <10 ug/L
2,4,6-Trichlorophenol SW8"NQD <10 ug/L
2,4-Dichlorophenol SW8270I)---<10 ug/L
2,4-Dimethylphenol SW8270D <~g/L
2,4-Dinitrophenol SW8270D <20u~
2,4-Dinitrotoluene SW8270D <).e"ug/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 · -Oktllorobenzidine 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 ::; 6°C
~
14 days None ~
14 days None -..............
14 days HCI to pH<2 ::; 6°C
14 days HCl topH<2 ::; 6°C
14 days HCl to pH<2 ::; 6°C
14 days HCl to pH<2 ::; 6°C
/
7/40 days None <])9-C
7/40 days None A6°C
7/40 days None / v ::; 6°C
7/40 days Non_V <6°C
7/40 days _N6"ne <6°C
7/40 days / None <6°C
7/40da~ None ::; 6°C
7/~ys None <6°C
f/1140 days None <6°C
7/40 days None <6°C
~40 days None ::; 6°C
7/4lhleys 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
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 1
pH<2 H2S04
pH<2H2S04
pH>l2
NaOH
pH<2HN03
pH<2H2S04 Yd.
pH<2HCL (
pH<2H2S04
pH>9NaOH,
ZnAcetate
pH<2H2S04
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
--doH
1)
2)
3)
4)
5)
6)
7)
If sample is not preserved, properly list its extension and receiving pH in the appropriate colunm above
Flag COC, notify client if requested
Place client conversation on COC
Samples may be adjusted
All samples requiring preservation
*
+ ...
#
•
The sample required additional preservative upon receipt.
The sample was received unpreserved.
The sample was received unpreserved and therefore preserved upon receipt.
The sample pH was unadjustable to a pH < 2 due to the sample matrix.
The sample pH was unadjustable to a pH > __ due to the sample matrix interference.
Lab Set ID: (~ Q '? J '11 r II hf 5" co~
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 --1895 N/A 6.57 NIA 16.01 N/A 326
TW4-01 NA Continuously pumped well --2481 N/A 6.59 NIA 16.14 N/A 346
TW4-02 NA Continuously pumped well --3422 N/A 6.40 N/A 15.43 N/A 329
TW4-03 54.59 100.00 109 Pumped Dry 1715 1724 0.52 6.25 6.27 0.32 16.50 16.43 0.43 NM
TW4-04 NA Continuously pumped well -2400 N/A 6.63 N/A 16.34 N/A 363
TW4-05 35.85 90.00 72 OK 1528 1518 0.66 6.36 6.38 0.31 15.62 15.60 0.13 500 500
TW4-06 16.11 30.00 32 Pumped Dry 3878 3891 0.33 6.46 6.45 0.15 14.86 14.84 0.13 NM
TW4-07 28.53 80.00 57 OK 1656 1698 2.50 6.55 6.57 0.30 15.25 15.23 0.13 504 504
TW4-08 29.80 80.00 80 OK 5031 5025 0.12 6.18 6.19 0.16 15.22 15.21 0.07 543 543
TW4-09 43.76 100.00 88 OK 2498 2494 0.16 6.23 6.24 0.16 15.29 15.29 0.00 486 486
TW4-10 31.63 60.75 63 Pumped Dry 3025 3025 0.00 6.33 6.29 0.63 15.05 15.00 0.33 NM
TW4-11 NA Continuously pumped well --3778 N/A 6.35 N/A 18.17 N/A 293
TW4-12 36.04 70.00 72 Pumped Dry 1548 1549 0.06 6.57 6.59 0.30 15.45 15.43 0.13 NM
TW4-13 26.11 60.00 52 Pumped Dry 2141 2152 0.51 6.61 6.61 0.00 15.30 15.27 0.20 355 356
TW4-14 8.78 15.00 18 Pumped Dry 5344 5348 0.07 6.37 6.38 0.16 15.10 15.09 0.07 NM
MW-26 NA Continuously pumped well -3512 N/A 6.26 N/A 16.49 N/A 251
TW4-16 50.87 110.00 102 OK 3930 3934 0.10 6.19 6.20 0.16 15.15 15.14 0.07 497 496
MW-32 35 .77 71.61 72 OK 3921 3920 0.03 6.30 6.29 0.16 15.27 15.16 0.72 483 475
TW4-18 46.68 110.00 93 OK 1970 1964 0.31 5.96 5.96 0.00 15.72 15.72 0.00 469 468
TW4-19 NA Continuously pumped well --2902 N/A 6.28 N/A 17.15 N/A 408
TW4-20 NA Continuously pumped well -4736 N/A 6.31 N/A 17.20 N/A 384
TW4-21 NA Continuously pumped well --4628 N/A 5.99 N/A 17.15 N/A 541
TW4-22 NA Continuously pumped well --5712 N/A 6.36 N/A 16.21 N/A 422
TW4-23 28.75 90.00 58 OK 3747 3747 0.00 6.25 6.24 0.16 14.46 14.48 0.14 470 467
TW4-24 NA Continuously pumped well -8841 N/A 6.19 N/A 16.22 N/A 453
TW4-25 NA Continuously pumped well --2820 N/A 6.42 N/A 16.54 N/A 479
TW4-26 12.25 20.00 25 Pumped Dry 6547 6527 0.31 4.11 4.08 0.73 15.53 15.50 0.19 NM
TW4-27 10.72 15.00 21 Pumped Dry 5285 5296 0.21 6.26 6.27 0.16 15.27 15.25 0.13 NM
TW4-28 43.55 90.00 87 OK 1457 1457 0.00 6.53 6.57 0.61 15.09 15.07 0.13 437 436
TW4-29 12.64 20.00 25 Pumped Dry 4353 4368 0.34 6.33 6.34 0.16 15.20 15.10 0.66 NM
TW4-30 10.93 20.00 22 Pumped Dry 4437 4449 0.27 5.20 5.19 0.19 15.48 15.31 1.10 NM
TW4-31 17.53 27.50 35 Pumped Dry 4879 4868 0.23 6.64 6.66 0.30 15.34 15.30 0.26 NM
TW4-32 41.41 90.00 83 OK 6960 6978 0.26 3.46 3.47 0.29 14.93 14.93 0.00 616 615
TW4-33 9.75 13.33 20 Pumped Dry 4594 4587 0.15 5.60 5.66 1.07 16.18 16.15 0.19 NM
TW4-34 16.32 33.33 33 Pumped Dry 3934 3989 1.39 6.35 6.37 0.31 15.76 15.72 0.25 NM
TW4-35 8.71 10.00 17 Pumped Dry 4530 4540 0.22 6.43 6.41 0.31 15.09 15.03 0.40 NM
TW4-36 27.80 45.00 56 Pumped Dry 2439 2473 1.38 6.85 6.84 0.15 15.79 15.75 0.25 NM
TW4-37 NA Continuously pumped well --4201 N/A 6.60 N/A 16.48 N/A 411
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, TW4-12, 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
0.00 14
NC
0.00 53
0.00 11.2
0.00 30
NC
N/A
NC
NC 16
NC
N/A
0.20 121
1.67 13.0
0.21 37
NIA
N/A
N/A
N/A
0.64 42
N/A
N/A
NC
NC
0.23 38
NC
NC
NC
0.16 14
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.
5.3
0.0
8.5
NM
8.0
14
NM
53
11.3
30
NM
0.0
NM
17
NM
7.10
123
13.0
37
0.0
1.8
8.3
3.7
40
25
5.3
NM
NM
36
NM
NM
NM
15
NM
NM
NM
NM
2.1
RPD
N/A
N/A
N/A
NC
N/A
0.00
NC
0.00
0.89
0.00
NC
NIA
NC
NC
NC
N/A
1.64
0.00
0.00
N/A
N/A
N/A
N/A
4.88
N/A
N/A
NC
NC
5.41
NC
NC
NC
6.90
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 7/25/2016 8/2/2016 8 14 OK
Trip Blank Chloroform 7/25/2016 8/2/2016 8 14 OK
Trip Blank Chloromethane 7/25/2016 8/2/2016 8 14 OK
Trip Blank Methylene chloride 7/25/2016 8/2/2016 8 14 OK
Trip Blank Carbon tetrachloride 8/2/2016 8/8/2016 6 14 OK
Trip Blank Chloroform 8/2/2016 8/8/2016 6 14 OK
Trip Blank Chloromethane 8/2/2016 8/8/2016 6 14 OK
Trip Blank Methylene chloride 8/2/2016 8/8/2016 6 14 OK
Trip Blank Carbon tetrachloride 8/17/2016 8/22/2016 5 14 OK
Trip Blank Chloroform 8117/2016 8/22/2016 5 14 OK
Trip Blank Chloromethane 8117/2016 8/22/2016 5 14 OK
Trip Blank Methylene chloride 8117/2016 8/22/2016 5 14 OK
MW-04 Chloride 7/25/2016 8/1/2016 7 28 OK
MW-04 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
MW-04 Chloroform 7/25/2016 8/2/2016 8 14 OK
MW-04 Chloromethane 7/25/2016 811/2016 7 14 OK
MW-04 Methvlene chloride 7/25/2016 8/1/2016 7 14 OK
MW-04 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
MW-26 Chloride 7/25/2016 8/1/2016 7 28 OK
MW-26 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
MW-26 Chloroform 7/25/2016 8/2/2016 8 14 OK
MW-26 Chloromethane 7/25/2016 8/1/2016 7 14 OK
MW-26 Methylene chloride 7/25/2016 8/1/2016 7 14 OK
MW-26 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
MW-32 Chloride 8117/2016 8/22/2016 5 28 OK
MW-32 Carbon tetrachloride 8117/2016 8/22/2016 5 14 OK
MW-32 Chloroform 8/17/2016 8/22/2016 5 14 OK
MW-32 Chloromethane 8117/2016 8/22/2016 5 14 OK
MW-32 Methylene chloride 8117/2016 8/22/2016 5 14 OK
MW-32 Nitrate/Nitrite (as N) 8117/2016 8/19/2016 2 28 OK
TW4-01 Chloride 7/25/2016 811/2016 7 28 OK
TW4-01 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
TW4-01 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-01 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-01 Methylene chloride 7/25/2016 8/1/2016 7 14 OK
TW4-01 Nitrate/Nitrite (as N) 7/25/2016 811/2016 7 28 OK
TW4-02 Chloride 7/25/2016 811/2016 7 28 OK
TW4-02 Carbon tetrachloride 7/25/2016 8/1/2016 7 14 OK
TW4-02 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-02 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-02 Methylene chloride 7/25/2016 811/2016 7 14 OK
TW4-02 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
TW4-03 Chloride 7/27/2016 8/1/2016 5 28 OK
TW4-03 Carbon tetrachloride 7/27/2016 8/1/2016 5 14 OK
TW4-03 Chloroform 7/27/2016 811/2016 5 14 OK
TW4-03 Chloromethane 7/27/2016 811/2016 5 14 OK
TW4-03 Methylene chloride 7/27/2016 811/2016 5 14 OK
TW4-03 Nitrate/Nitrite (as N) 7/27/2016 8/1/2016 5 28 OK
TW4-03R Chloride 7/26/2016 8/1/2016 6 28 OK
TW4-03R Carbon tetrachloride 7/26/2016 8/1/2016 6 14 OK
TW4-03R Chloroform 7/26/2016 811/2016 6 14 OK
TW4-03R Chloromethane 7/26/2016 811/2016 6 14 OK
TW4-03R Methylene chloride 7/26/2016 811/2016 6 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-03R Nitrate/Nitrite (as N) 7/26/2016 8/1/2016 6 28 OK
TW4-04 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-04 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
TW4-04 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-04 Chloromethane 7/25/2016 811/2016 7 14 OK
TW4-04 Methylene chloride 7/25/2016 811/2016 7 14 OK
TW4-04 Nitrate/Nitrite (as N) 7/25/2016 811/2016 7 28 OK
TW4-05 Chloride 8/3/2016 8/10/2016 7 28 OK
TW4-05 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-05 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-05 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-05 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-05 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-06 Chloride 8/4/2016 8/10/2016 6 28 OK
TW4-06 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-06 Chloroform 8/4/2016 8/9/2016 5 14 OK
TW4-06 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-06 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-06 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 1 28 OK
TW4-07 Chloride 8/4/2016 8/10/2016 6 28 OK
TW4-07 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-07 Chloroform 8/4/2016 8/9/2016 5 14 OK
TW4-07 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-07 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-07 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 1 28 OK
TW4-08 Chloride 8/4/2016 8/10/2016 6 28 OK
TW4-08 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-08 Chloroform 8/4/2016 8/9/2016 5 14 OK
TW4-08 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-08 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-08 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 I 28 OK
TW4-09 Chloride 8/3/2016 8/10/2016 7 28 OK
TW4-09 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-09 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-09 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-09 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-09 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-10 Chloride 8/4/2016 8/10/2016 6 28 OK
TW4-10 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-10 Chloroform 8/4/2016 8/9/2016 5 14 OK
TW4-10 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-10 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-10 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 1 28 OK
TW4-11 Chloride 7/25/2016 811/2016 7 28 OK
TW4-11 Carbon tetrachloride 7/25/2016 8/1/2016 7 14 OK
TW4-11 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-11 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-11 Methyjene chloride 7/25/2016 8/1/2016 7 14 OK
TW4-11 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
TW4-12 Chloride 7/27/2016 8/1/2016 5 28 OK
TW4-12 Carbon tetrachloride 7/27/2016 8/1/2016 5 14 OK
TW4-12 Chloroform 7/27/2016 8/1/2016 5 14 OK
TW4-12 Chloromethane 7/27/2016 8/1/2016 5 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-12 Methylene chloride 7/27/2016 8/1/2016 5 14 OK
TW4-12 Nitrate/Nitrite (as N) 7/27/2016 8/1/2016 5 28 OK
TW4-13 Chloride 7/28/2016 8/1/2016 4 28 OK
TW4-13 Carbon tetrachloride 7/28/2016 8/1/2016 4 14 OK
TW4-13 Chloroform 7/28/2016 811/2016 4 14 OK
TW4-13 Chloromethane 7/28/2016 811/2016 4 14 OK
TW4-13 Methylene chloride 7/28/2016 811/2016 4 14 OK
TW4-13 Nitrate/Nitrite (as N) 7/28/2016 8/1/2016 4 28 OK
TW4-14 Chloride 8/3/2016 8110/2016 7 28 OK
TW4-14 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-14 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-14 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-14 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-14 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-16 Chloride 8/3/2016 8110/2016 7 28 OK
TW4-16 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-16 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-16 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-16 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-16 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-18 Chloride 8/3/2016 8110/2016 7 28 OK
TW4-18 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-18 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-18 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-18 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-18 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-19 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-19 Carbon tetrachloride 7/25/2016 8/1/2016 7 14 OK
TW4-19 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-19 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-19 Methylene chloride 7/25/2016 8/1/2016 7 14 OK
TW4-19 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
TW4-20 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-20 Carbon tetrachloride 7/25/2016 8/2/2016 8 14 OK
TW4-20 Chloroform 7/25/2016 8/3/2016 9 14 OK
TW4-20 Chloromethane 7/25/2016 8/2/2016 8 14 OK
TW4-20 Methylene chloride 7/25/2016 8/2/2016 8 14 OK
TW4-20 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
TW4-21 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-21 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
TW4-21 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-21 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-21 Methylene chloride 7/25/2016 8/1/2016 7 14 OK
TW4-21 Nitrate/Nitrite (as N) 7/25/2016 8/1/2016 7 28 OK
TW4-22 Chloride 7/25/2016 811/2016 7 28 OK
TW4-22 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
TW4-22 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-22 Chloromethane 7/25/2016 811/2016 7 14 OK
TW4-22 Methylene chloride 7/25/2016 811/2016 7 14 OK
TW4-22 Nitrate/Nitrite (as N) 7/25/2016 811/2016 7 28 OK
TW4-23 Chloride 8/3/2016 8110/2016 7 28 OK
TW4-23 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-23 Chloroform 8/3/2016 8/8/2016 5 14 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
TW4-23 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-23 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-23 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-24 Chloride 7/25/2016 811/2016 7 28 OK
TW4-24 Carbon tetrachloride 7/25/2016 8/l/2016 7 14 OK
TW4-24 Chloroform 7/25/2016 8/l/2016 7 14 OK
TW4-24 Chloromethane 7/25/2016 811/2016 7 14 OK
TW4-24 Methylene chloride 7/25/2016 8/l/2016 7 14 OK
TW4-24 Nitrate/Nitrite (as N) 7/25/2016 8/112016 7 28 OK
TW4-25 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-25 Carbon tetrachloride 7/25/2016 811/2016 7 14 OK
TW4-25 Chloroform 7/25/2016 8/1/2016 7 14 OK
TW4-25 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-25 Methylene chloride 7/25/2016 811/2016 7 14 OK
TW4-25 Nitrate/Nitrite (as N) 7/25/2016 811/2016 7 28 OK
TW4-26 Chloride 8/3/2016 8/16/2016 13 28 OK
TW4-26 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-26 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-26 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-26 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-26 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-27 Chloride 8/3/2016 8110/2016 7 28 OK
TW4-27 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-27 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-27 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-27 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-27 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-28 Chloride 7127/2016 8/1/2016 5 28 OK
TW4-28 Carbon tetrachloride 7/27/2016 8/1/2016 5 14 OK
TW4-28 Chloroform 7/27/2016 8/l/2016 5 14 OK
TW4-28 Chloromethane 7/27/2016 8/l/2016 5 14 OK
TW4-28 Methylene chloride 7/27/2016 811/2016 5 14 OK
TW4-28 Nitrate/Nitrite (as N) 7/27/2016 811/2016 5 28 OK
TW4-29 Chloride 8/4/2016 8110/2016 6 28 OK
TW4-29 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-29 Chloroform 8/4/2016 8/9/2016 5 14 OK
TW4-29 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-29 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-29 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 I 28 OK
TW4-30 Chloride 8/3/2016 8/10/2016 7 28 OK
TW4-30 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-30 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-30 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-30 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-30 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-31 Chloride 7/28/2016 8/1/2016 4 28 OK
TW4-31 Carbon tetrachloride 7/28/2016 811/2016 4 14 OK
TW4-31 Chloroform 7128/2016 811/2016 4 14 OK
TW4-31 Chloromethane 7128/2016 811/2016 4 14 OK
TW4-31 Methylene chloride 7/2812016 8/1/2016 4 14 OK
TW4-31 Nitrate/Nitrite (as N) 7/28/2016 8/1/2016 4 28 OK
TW4-32 Chloride 7/28/2016 811/2016 4 28 OK
TW4-32 Carbon tetrachloride 7/28/2016 811/2016 4 14 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
Location ID Parameter Name Sample Date Analysis Date (Davs) Time (Davs) Check
TW4-32 Chloroform 7/28/2016 811/2016 4 14 OK
TW4-32 Chloromethane 7/28/2016 811/2016 4 14 OK
TW4-32 Methylene chloride 7/28/2016 811/2016 4 14 OK
TW4-32 Nitrate/Nitrite (as N) 7/28/2016 8/112016 4 28 OK
TW4-33 Chloride 8/4/2016 8/10/2016 6 28 OK
TW4-33 Carbon tetrachloride 8/4/2016 8/8/2016 4 14 OK
TW4-33 Chloroform 8/4/2016 8/8/2016 4 14 OK
TW4-33 Chloromethane 8/4/2016 8/8/2016 4 14 OK
TW4-33 Methylene chloride 8/4/2016 8/8/2016 4 14 OK
TW4-33 Nitrate/Nitrite (as N) 8/4/2016 8/5/2016 1 28 OK
TW4-34 Chloride 8/3/2016 8/10/2016 7 28 OK
TW4-34 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-34 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-34 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-34 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-34 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-34R Chloride 8/2/2016 8111/2016 9 28 OK
TW4-34R Carbon tetrachloride 8/2/2016 8/8/2016 6 14 OK
TW4-34R Chloroform 8/2/2016 8/8/2016 6 14 OK
TW4-34R Chloromethane 8/2/2016 8/8/2016 6 14 OK
TW4-34R Methylene chloride 8/2/2016 8/8/2016 6 14 OK
TW4-34R Nitrate/Nitrite (as N) 8/2/2016 8/5/2016 3 28 OK
TW4-35 Chloride 8/3/2016 8/10/2016 7 28 OK
TW4-35 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-35 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-35 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-35 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-35 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
TW4-36 Chloride 7/28/2016 8/1/2016 4 28 OK
TW4-36 Carbon tetrachloride 7/28/2016 8/1/2016 4 14 OK
TW4-36 Chloroform 7/28/2016 811/2016 4 14 OK
TW4-36 Chloromethane 7/28/2016 811/2016 4 14 OK
TW4-36 Methylene chloride 7/28/2016 8/112016 4 14 OK
TW4-36 Nitrate/Nitrite (as N) 7/28/2016 8/1/2016 4 28 OK
TW4-37 Chloride 7/25/2016 8/1/2016 7 28 OK
TW4-37 Carbon tetrachloride 7/25/2016 8/112016 7 14 OK
TW4-37 Chloroform 7/25/2016 8/2/2016 8 14 OK
TW4-37 Chloromethane 7/25/2016 8/1/2016 7 14 OK
TW4-37 Methylene chloride 7/25/2016 811/2016 7 14 OK
TW4-37 Nitrate/Nitrite (as N) 7/25/2016 8/112016 7 28 OK
TW4-60 Chloride 7/25/2016 8/112016 7 28 OK
TW4-60 Carbon tetrachloride 7/25/2016 8/3/2016 9 14 OK
TW4-60 Chloroform 7/25/2016 8/3/2016 9 14 OK
TW4-60 Chloromethane 7/25/2016 8/3/2016 9 14 OK
TW4-60 Methylene chloride 7/25/2016 8/3/2016 9 14 OK
TW4-60 Nitrate/Nitrite (as N) 7/25/2016 8/112016 7 28 OK
TW4-65 Chloride 7/27/2016 811/2016 5 28 OK
TW4-65 Carbon tetrachloride 7/27/2016 8/3/2016 7 14 OK
TW4-65 Chloroform 7/27/2016 8/3/2016 7 14 OK
TW4-65 Chloromethane 7/27/2016 8/3/2016 7 14 OK
TW4-65 Methylene chloride 7/27/2016 8/3/2016 7 14 OK
TW4-65 Nitrate/Nitrite (as N) 7/27/2016 811/2016 5 28 OK
TW4-70 Chloride 8/3/2016 8110/2016 7 28 OK
1-2: Holding Time Evaluation
Hold Time Allowed Hold Hold Time
LoeationlD Paramete; Name Sample Date Analysis Date (Days) Time (Days) Check
TW4-70 Carbon tetrachloride 8/3/2016 8/8/2016 5 14 OK
TW4-70 Chloroform 8/3/2016 8/8/2016 5 14 OK
TW4-70 Chloromethane 8/3/2016 8/8/2016 5 14 OK
TW4-70 Methylene chloride 8/3/2016 8/8/2016 5 14 OK
TW4-70 Nitrate/Nitrite (as N) 8/3/2016 8/5/2016 2 28 OK
Table 1-3 Recipt Temperature Check
Sample Batch Wells in Batch Temperature
1607518 MW-04, MW-26, TW4-0l, TW4-02, TW4-03, TW4-03R, 4.3 oc
TW4-04, TW4-ll, TW4-12, TW4-13, TW4-19, TW4-20,
TW4-21, TW4-22, TW4-24, TW4-25, TW4-28, TW4-31,
TW4-32, TW4-36, TW4-37, TW4-60, TW4-65, Trip Blank
1608133 TW4-05, TW4-06, TW4-07, TW4-08, TW4-09, TW4-IO, 2.6 oc
TW4-14, TW4-16, TW4=18, TW4-23, TW4-26, TW4-27,
TW4-29, TW4-30, TW4-33, TW4-34, TW4-34R, TW4-35,
TW4-70 and Trip Blank
1608399 MW-32 and Trip Blank 3.8 oc
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
1-5 Reporting Limit Check
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 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
Trip Blank Carbon tetrachloride 1 ug!L u 1 1 OK
TriQBiank 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 50 ug!L 50 1 OK
MW-04 Chloromethane 1 ug/L u 1 1 OK
MW-04 Methylene chloride 1 ug!L u 1 1 OK
MW-04 Nitrate/Nitrite (as N) 0.1 mg_IL 10 0.1 OK
MW-26 Chloride 10 mg!L 10 1 OK
MW-26 Carbon tetrachloride 1 ug!L u 1 1 OK
MW-26 Chloroform 50 ug!L 50 1 OK
MW-26 Chloromethane 1 ug!L u 1 1 OK
MW-26 Methylene chloride 1 ug!L 1 1 OK
MW-26 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
MW-32 Chloride 10 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 1 1 OK
MW-32 Methylene chloride 1 ug!L u 1 1 OK
MW-32 Nitrate/Nitrite (as N) 0.1 mg!L u 10 0.1 OK
TW4-0l Chloride 10 mg!L 10 1 OK
TW4-0J Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-01 Chloroform 50 ug/L 50 1 OK
TW4-01 Chloromethane 1 ug!L u 1 1 OK
TW4-01 Methylene chloride 1 ug!L u 1 1 OK
TW4-01 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-02 Chloride 10 mg!L 10 1 OK
TW4-02 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-02 Chloroform 50 ug!L 50 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 10 0.1 OK
1-5 Reponing Limit Check
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-04 Chloride 10 mg/L 10 1 OK
TW4-04 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-04 Chloroform 50 ug!L 50 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
TW4-05 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-05 Chloroform 1 ug/L 1 I OK
TW4-05 Chloromethane 1 ug!L u I I OK
TW4-05 Methylene chloride I ug/L u I I OK
TW4-05 Nitrate/Nitrite (as N) O.I mg!L 10 0.1 OK
TW4-06 Chloride 10 mg/L 10 I OK
TW4-06 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-06 Chloroform 10 ug/L 10 I OK
TW4-06 Chloromethane I ug!L u I 1 OK
TW4-06 Methylene chloride I ug/L u 1 1 OK
TW4-06 Nitrate/Nitrite (as N) 0.1 mg/L 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 50 ug!L 50 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 1 OK
TW4-08 Chloromethane 1 ug/L u 1 1 OK
TW4-08 Methylene chloride 1 ug!L u 1 1 OK
TW4-08 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-09 Chloride 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 1 OK
TW4-09 Methylene chloride 1 ug/L u 1 1 OK
TW4-09 Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-10 Chloride 10 mg/L 10 1 OK
TW4-10 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-10 Chloroform 50 ug!L 50 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 I ug!L u I 1 OK
TW4-11 Chloroform 50 ug/L 50 1 OK
TW4-11 Chloromethane 1 ug!L u 1 1 OK
TW4-Il Methylene chloride 1 ug/L u 1 1 OK
TW4-ll 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 I I OK
TW4-12 Chloroform I ug!L u I 1 OK
TW4-12 Chloromethane 1 ug/L u 1 1 OK
TW4-12 Methylene chloride 1 ug!L u 1 1 OK
TW4-12 Nitrate/Nitrite (as N) 0.2 mg/L 20 0.1 OK
1-5 Reporting Limit Check
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-13 Chloride 10 mg/L 10 l OK
TW4-13 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-13 Chloroform 1 ug!L u 1 1 OK
TW4-13 Chloromethane I ug/L u 1 1 OK
TW4-13 Methylene chloride 1 ug/L u 1 1 OK
TW4-13 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-14 Chloride 10 mg!L 10 1 OK
TW4-14 Carbon tetrachloride 1 ug!L u 1 I OK
TW4-14 Chloroform 1 ug!L 1 1 OK
TW4-14 Chloromethane 1 ug!L u 1 1 OK
TW4-14 Methylene chloride 1 ug!L 1 1 OK
TW4-14 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-16 Chloride 10 mg!L 10 1 OK
TW4-16 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-16 Chloroform 1 ug!L 1 1 OK
TW4-16 Chloromethane 1 ug!L u 1 1 OK
TW4-16 Methylene chloride 1 ug!L u 1 1 OK
TW4-16 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-18 Chloride 10 mg!L 10 1 OK
TW4-18 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-18 Chloroform 1 ug!L 1 1 OK
TW4-18 Chloromethane 1 ug/L u 1 1 OK
TW4-18 Methylene chloride 1 ug!L u 1 1 OK
TW4-18 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-19 Chloride 100 mg!L 100 1 OK
TW4-19 Carbon tetrachloride 1 ug!L 1 1 OK
TW4-19 Chloroform 100 ug!L 100 1 OK
TW4-19 Chloromethane 1 ug!L u 1 1 OK
TW4-19 Methylene chloride 1 ug!L u 1 1 OK
TW4-19 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-20 Chloride 100 mg/L 100 1 OK
TW4-20 Carbon tetrachloride 1 ug!L 1 1 OK
TW4-20 Chloroform 1000 ug!L 1000 1 OK
TW4-20 Chloromethane 1 ug!L u 1 1 OK
TW4-20 Methylene chloride 1 ug!L u 1 1 OK
TW4-20 Nitrate/Nitrite (as N) 0.1 mg/L 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 ug/L u 1 1 OK
TW4-2l 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 100 ug!L 100 1 OK
TW4-22 Chloromethane 1 ug!L u 1 1 OK
TW4-22 Methylene chloride 1 ug!L u 1 1 OK
TW4-22 Nitrate/Nitrite (as N) 0.5 mg!L 50 0.1 OK
TW4-23 Chloride 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 10 0.1 OK
1-5 Reporting Limit Check
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-24 Chloride 100 mg/L IOO I OK
TW4-24 Carbon tetrachloride I ug/L u I I OK
TW4-24 Chloroform I ug/L I I OK
TW4-24 Chloromethane I ug/L u I I OK
TW4-24 Methylene chloride I ug/L u I 1 OK
TW4-24 Nitrate/Nitrite (as N) 0.5 mg/L 50 O.I OK
TW4-25 Chloride IO mg/L IO I OK
TW4-25 Carbon tetrachloride 1 ug/L u I I OK
TW4-25 Chloroform I ug/L u I I OK
TW4-25 Chloromethane I ug/L u I 1 OK
TW4-25 Methylene chloride 1 ug/L u I I OK
TW4-25 Nitrate/Nitrite (as N) O.I mg/L IO O.I OK
TW4-26 Chloride I mg/L I 1 OK
TW4-26 Carbon tetrachloride 1 ug/L u I I OK
TW4-26 Chloroform 1 ug/L I 1 OK
TW4-26 Chloromethane I ug/L u 1 I OK
TW4-26 Methylene chloride I ug/L u 1 I OK
TW4-26 Nitrate/Nitrite (as N) 0.1 mg/L 10 O.I OK
TW4-27 Chloride 10 mg/L 10 I OK
TW4-27 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-27 Chloroform 1 ug/L I I OK
TW4-27 Chloromethane 1 ug/L u 1 I OK
TW4-27 Methylene chloride 1 ug/L u 1 1 OK
TW4-27 Nitrate/Nitrite (as N) 0.2 mg/L 20 O.I OK
TW4-28 Chloride 10 mg/L 10 I OK
TW4-28 Carbon tetrachloride 1 ug/L u 1 I OK
TW4-28 Chloroform 1 ug/L u 1 1 OK
TW4-28 Chloromethane 1 ug/L u I 1 OK
TW4-28 Methylene chloride 1 ug/L u I 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 I 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 I I OK
TW4-30 Nitrate/Nitrite (as N) O.I mg/L IO O.I OK
TW4-3I Chloride 10 mg/L 10 1 OK
TW4-31 Carbon tetrachloride 1 ug/L u I 1 OK
TW4-31 Chloroform 1 ug/L u 1 I OK
TW4-31 Chloromethane 1 ug/L u 1 1 OK
TW4-31 Methylene chloride I ug/L u I 1 OK
TW4-3I Nitrate/Nitrite (as N) 0.1 mg/L 10 0.1 OK
TW4-32 Chloride 10 mg/L 10 1 OK
TW4-32 Carbon tetrachloride 1 ug/L u 1 1 OK
TW4-32 Chloroform 1 ug/L u 1 1 OK
TW4-32 Chloromethane I ug/L u 1 1 OK
TW4-32 Methylene chloride I ug/L u I 1 OK
TW4-32 Nitrate/Nitrite (as N) O.I mg/L 10 0.1 OK
1-5 Reporting Limit Check
Lab Required
Reporting Dilution Reporting
Location Analyte Limit Units Qualifier Factor Limit RLCheck
TW4-33 Chloride 10 mg!L 10 1 OK
TW4-33 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-33 Chloroform 1 ug!L 1 1 OK
TW4-33 Chloromethane 1 ug!L u 1 I OK
TW4-33 Methylene chloride 1 ug!L u 1 1 OK
TW4-33 Nitrate/Nitrite (as N) 0.1 mg/L 10 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 10 0.1 OK
TW4-34R Chloride 1 mg/L u 1 1 OK
TW4-34R Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-34R Chloroform 1 ug!L u 1 1 OK
TW4-34R Chloromethane I ug!L u I I OK
TW4-34R Methylene chloride I ug/L u I I OK
TW4-34R Nitrate/Nitrite (as N) O.I mg/L u 10 0.1 OK
TW4-35 Chloride IO 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 I 1 OK
TW4-35 Methylene chloride 1 ug!L u I 1 OK
TW4-35 Nitrate/Nitrite (as N) 0.1 mg!L 10 0.1 OK
TW4-36 Chloride 10 mg!L IO 1 OK
TW4-36 Carbon tetrachloride I ug!L u I 1 OK
TW4-36 Chloroform I ug/L u I 1 OK
TW4-36 Chloromethane I ug/L u 1 1 OK
TW4-36 Methylene chloride I ug!L u 1 1 OK
TW4-36 Nitrate/Nitrite (as N) 0.1 mg/L u 10 0.1 OK
TW4-37 Chloride 100 mg/L 100 1 OK
TW4-37 Carbon tetrachloride I ug!L I 1 OK
TW4-37 Chloroform 100 ug!L 100 1 OK
TW4-37 Chloromethane 1 ug!L u 1 1 OK
TW4-37 Methylene chloride 1 ug!L u I I OK
TW4-37 Nitrate/Nitrite (as N) 0.2 mg!L 20 0.1 OK
TW4-60 Chloride 1 mg!L u I I OK
TW4-60 Carbon tetrachloride 1 ug!L u 1 I OK
TW4-60 Chloroform I ug!L u I 1 OK
TW4-60 Chloromethane 1 ug!L u I 1 OK
TW4-60 Methylene chloride 1 ug/L u I 1 OK
TW4-60 Nitrate/Nitrite (as N) 0.1 mg!L u 10 0.1 OK
TW4-65 Chloride 10 mg!L 10 1 OK
TW4-65 Carbon tetrachloride I ug!L u 1 1 OK
TW4-65 Chloroform I ug!L u 1 1 OK
TW4-65 Chloromethane 1 ug!L u I 1 OK
TW4-65 Methylene chloride 1 ug/L u I 1 OK
TW4-65 Nitrate/Nitrite (as N) 0.2 mg!L 20 0.1 OK
TW4-70 Chloride IO mg!L 10 1 OK
TW4-70 Carbon tetrachloride 1 ug!L u 1 1 OK
TW4-70 Chloroform I ug!L u 1 1 OK
TW4-70 Chloromethane I ug!L u I 1 OK
TW4-70 Methylene chloride 1 ug!L u I 1 OK
TW4-70 Nitrate/Nitrite (as N) 0.1 mg!L u 10 0.1 OK
I-6 Trip Blank Evaluation
Lab Report Constituent Result
1607518 Carbon tetrachloride ND ug/L
Chloroform ND ug/L
Chloromethane ND ug/L
Methylene chloride ND ug!L
1608133 Carbon tetrachloride ND ug!L
Chloroform ND ug!L
Chloromethane ND ug!L
Methylene chloride ND ug!L
1608399 Carbon tetrachloride ND ug!L
Chloroform ND ug!L
Chloromethane ND ug!L
Methylene chloride ND ug!L
1-7 QNQC Evaluation for Sample Duplicates
Ci.Qnstl"'tll::ld
Chloride (mg/L)
Nitrate+ Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
Constituent
Chloride (mg/L)
Nitrate+ Nitrite (as N)
Carbon Tetrachloride
Chloroform
Chloromethane
Dichloromethane (Methylene Chloride)
RPD = Relative Percent Difference
ND = The analyte was not detected
TW4~'
70.1
31.3
ND
ND
ND
ND
TW4-23
49.6
ND
ND
ND
ND
ND
n\~4-65 %RiPD
70.9 1.1
35.6 12.9
ND NC
ND NC
ND NC
ND NC
· 'YW4-'m ~D
48.3 2.7
ND NC
ND NC
ND NC
ND NC
NO NC
1-8 QC Control Limits for Analysis and Blanks
Method Blank Detections
All Method Blanks for the quarter were non-detect.
Matrix Spike % Recovery Comparison
MS MSD REC
Lab Report Lab Sample ID Well Analyte %REC o/oREC 'Q.ange RPD
1607518 1607 518-009BMSD TW4-25 Nitrate 103 117 90-110 __ 10.1__ --
Laboratory Control Sample
All Laboratory Control Sample recoveries 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; ND =not detected;
ND 02 =not detected in second quarter
......_70
PIEZ·3A
~NS
MW-32
e ND
kriged chloroform isocon and label
May, 2016 replacement of perched
piezometer Piez-03 showing
concentration in 11g/L
perched monitoring well showing
concentration in 11g/L
1W4-7 temporary perched monitoring well 0 1 000 showing concentration in llg/L
1WN·1 ()Ns
PIEZ-1
<iil NS
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 3rd QUARTER, 2016 CHLOROFORM (J.tg/L)
WHITE MESA SITE
APPROVED DATE REFERENCE FIGURE
H fl18000/Nov16/chloroform/Uchl0916.srf J-1
....._70
NS = not sampled; ND = not detected;
ND 02 =not detected in second quarter
kriged chloroform isocon and label
PIEZ-3A May, 2016 replacement of perched ~NS piezometer Piez-o3 (not sampled)
MW·32
e ND perched monitoring well showing
concentration (~giL)
TW4-7 temporary perched monitoring well 0 1 000 showing concentration (~g/L)
PIEZ-2 perched piezometer showing ~ NS concentration (~giL)
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 3rd QUARTER, 2016 CHLOROFORM (J,~g/L)
WHITE MESA SITE
1\l'PROIIED DATE
(detail map)
REFERENCE H:/718000/
nov16/chloroform/Uchl0916det.srf
FIGURE
J-2
NS c not sampled; NO= not detected;
NO 02 = not detected in second quarter
......_70 kriged chloroform isocon and label
PIEZ-3A May, 2016 replacement of perched ~NS piezometer Piez-03 (not sampled)
MW-32 e No
TW4-7
0 1000
PIEZ-2
Q NS
perched monitoring well showing
concentration (j.ig/L)
temporary perched monitoring well
showing concentration (j.ig/L)
perched piezometer showing
concentration (IJg/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.
3rd QUARTER, 2016 CHLOROFORM
GREATER THAN OR EQUAL TO 70 ~gL GRID
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/
nov16/chloroform/Uchl0916ge70.srf
FIGURE
J-3
TabK
Analyte Concentration Data and Chloroform Concentration Trend Graphs Over Time
Cblorof~um Carboa Chlo efltane Metb Nitrate Chloride MW-4 'rebr mdc e
(ugll) (uJrln (qj) Cldori (ugll) (mg/J) (mg4)
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 <I <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
Cld'~eform Carbon Chloro~Mthaue Met!\~ Nitrate Chloride MW-4 Tetra:,~Jiid~
' gf<l) (u ~ ~) Chlmide (ug/ll) (mglt) ~mg/1}
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
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
23-May-16 1580 1.44 ND ND 4.54 43.7
25-Jul-16 1430 ND ND ND 4.95 42.5
(ug/L}
~ 0 0 0
1\)
0 0 0
O'l 0 0 0
.j:>.
0 0 0
(]1
0 0 0 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
-...I 0 0 0
~~~~~~! I ! 1: 7 L Sep-04 t • • _ ~ Dec-04 Mar-05
Jun-05
Sep-05 Dec-05
Mar-06
Jun-06 Sep-06
Dec-06 Mar-07
Jun-07
Sep-07 Dec-07
Mar-08
Jun-08 Sep-08
Dec-08 Mar-09
Jun-09
Sep-09 Dec-09
Mar-10 Jun-10
Sep-10
Dec-10 Mar-11
Jun-11
Sep-11 Dec-11
Mar-12 Jun-12
Sep-12
Dec-12 Mar-13
Jun-13
Sep-13 Dec-13
Mar-14 Jun-14
Sep-14 Dec-14
Mar-15
Jun-15 Sep-15
Dec-15 Mar-16
Jun-16 1 1
~ ~ ~ I ()
::J'"
0 a -0 ..... 3
~
c:
CD C/)
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
10-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 I 2.4
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 <1 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
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-1 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ugll) (ug/1)
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
29-Dec-09 1400 <I <1 <1 6.8 41
3-Mar-10 1300 <I <1 <1 7.1 35
15-Jun-10 1600 1.2 <1 <1 6.8 40
24-Aug-10 1500 <I <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-1 I 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 NO 7.1 42
13-Sep-12 1000 ND NO ND 5 39
4-0ct-12 1100 NO 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 NO 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 NO NO 7.06 38.3
8-Jun-15 1260 ND ND NO 6.07 40.3
31-Aug-15 1060 ND ND ND 6.28 45.9
19-0ct-15 1040 ND ND ND 1.55 38.5
9-Mar-16 974 ND ND ND 0.148 41.7
23-May-16 1140 ND ND ND 0.138 44.4
25-Jul-16 1160 ND ND ND 5.49 44.7
w CD :::l "iii >
E ...
0 -0 ...
.2 .c
0 ...-
I
'11:1' 3!: ~
0 0 0 r--
0 0 0 <D
0 0 0 lt)
0 0 0 "=t
0 0 0 ('I)
(1fl5n)
0 0 0 C\1
0 0 0
v~-oaa-a
5o-1nr-9
go-•oo-o~
vo-uer-v~
0
Cbl retromn Cafb&D Chloromethane M«ilt}JJ Nitrate Chloride TW4·! 1'ew Itt&ride ~ ('uffij (~ ~ gAl~ ~} (mgM) rJl}
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 2S <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
Chloroform Carb~ Cld A·-Methylene Nitrate Chloride T:W4·2 T*HIW»i<le Ch~Gride (ugll) (u,gfl} ~uglt) {~~ (mgll) (mg/1)
3-Mar-10 2600 2 <1 <1 6.8 42
15-Jun-10 3300 2.6 <1 <1 6.7 43
16-Aug-10 3300 2.5 <1 <1 6.6 43
14-0ct-10 3000 2.1 <1 <1 6.5 41
24-Feb-11 3100 2.4 ND ND 7 46
2-Jun-11 3000 2.2 ND ND 6.8 42
17-Aug-11 2400 1.6 ND ND 6 48
29-Nov-11 3900 2.8 ND ND 7 49
24-Jan-12 2500 2 ND ND 7.1 49
14-Jun-12 2500 2.1 ND ND 7.7 52
13-Sep-12 2900 1.8 ND ND 4 76
4-0ct-12 3100 2 ND ND 7.6 49
13-Feb-13 3580 5.17 ND ND 8.1 46
19-Jun-13 3110 2.65 ND ND 7.51 46.9
12-Sep-13 3480 2.41 ND ND 9.3 44.9
14-Nov-13 3740 3.15 ND ND 8.39 43.9
6-Feb-14 3180 7.1 ND ND 7.87 45.9
23-May-14 2930 6.05 ND ND 9.11 45.4
27-Aug-14 3170 1.4 3.6 ND 6.2 45
30-0ct-14 3580 2.6 ND ND 8.45 45.5
9-Mar-15 1840 1.44 ND ND 5.32 44.9
8-Jun-15 1650 ND ND ND 4.3 48.1
31-Aug-15 1310 ND ND ND 3.76 50.0
19-0ct-15 2070 ND ND ND 5.18 41.9
9-Mar-16 1970 1.20 ND ND 5.30 43.4
23-May-16 2070 1.49 ND ND 5.67 43.8
25-Jul-16 1780 ND ND ND 4.07 42.9
TW4-2 Chloroform Values
7000 ~-------------------------------------------------------------------------------------------------------------------------------------------------------------------------,
6000 +-------------------------_. ____________________________________________________________________________________________________________ _,
5000 \ I 'J "{I
4000 --...I a,
::II -3000 I -.:.1 ..;, • ~ I I T """ V \ I
2000 +---------------------------------------~H---------+r---------------------+~~~----;
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.
0 ' ' co 0> I '3 ""')
I
""' C\J
.....
9 ,_
0.. <( c,
""' 0 c ca
""') I
""'
CD 9 t5 0 6
0> 0 I '3 ""')
I CD
C\J .....
I ,_
0.. <( I
""' I'-..... .....
I I (.) 0.. Q) Q)
0 (/)
I I I'-C\J C\J C\J
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-3 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (D.211J (u2lJ)
28-Jun-99 3500 7.6
29-Nov-99 702
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
Cblol'oloml Carbo: Oblorom Meihflene Nitrrate Ckla<l'e TW4·3 Tetraehl0riide e Cldo.ride ugl) •tl1dl (ugM) f,~ (mg/1~ (~)
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
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 ND ND ND ND 4.4 23
17-Jan-12 ND ND ND ND 4.3 21
31-May-12 ND ND ND ND 4.4 24
29-Aug-12 ND ND ND ND 4.9 25
3-0ct-12 ND ND ND ND 4.8 25
7-Feb-13 ND ND ND ND 5.05 23.7
29-May-13 ND ND ND ND 5.83 23.8
29-Aug-13 ND ND ND ND 6.26 24.0
6-Nov-13 ND ND ND ND 5.89 24.1
22-Jan-14 ND ND ND ND 6.66 24.9
19-May-14 ND ND ND ND 6.01 24.4
13-Aug-14 ND ND ND ND 5.3 26
23-0ct-14 ND ND ND ND 6.07 26.7
11-Mar-15 ND ND ND ND 6.64 26.2
10-Jun-15 ND ND ND ND 5.71 27.5
2-Sep-15 ND ND ND ND 3.88 27.4
21-0ct-15 ND ND ND ND 5.37 25.6
15-Mar-16 ND ND ND ND 5.83 32.8
25-May-16 ND ND ND ND 5.65 27.9
27-Jul-16 ND ND ND ND 6.10 26.5
(ug/L)
1\:) 1\:) (,) (,)
"""" CJ'1 0 CJ'1 0 CJ'1 0 CJ'1 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
Jun-99 I
Nov-99
Apr-00
Sep-00
Feb-01 ~
Jul-01
Dec-01
May-02
Oct-02 a.-
Mar-03 t'D ~ ,...
Aug-03 t'D ~ n I
Jan-04
,... \I. -· 0 :::::J
Jun-04 :::::J DJ
Nov-04 -"' 3" c Apr-05 -· t'D -4 ,... t'D ::E Sep-05 "' :::::J ol:lo -· I
Feb-06 :::::J (,)
n (") Jul-06 t'D :::r
Dec-06 s 0 ...
May-07 DJ 0 -.., 0 Oct-07 n ... ::::r 3 Mar-08 NtD < Aug-08 co D) ..
Jan-09 N c
CD 0 0 Jun-09 0
Nov-09 w
Apr-10
Sep-10
Feb-11
Jul-11
Dec-11
May-12
Oct-12
Mar-13
Aug-13 1
Jan-14 :
Jun-14
Nov-14
Apr-15
' Sep-15 1
Feb-16
Jul-16
Chlorofo[!JD c b&D Oblur..eJRe.t.IUmc ~ itrate ebb-ide TW'I-it 11ekaehl&ria ekf•lide i~ (~} {ug{j) -~· (mgAl) (mg/J)
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
Chloroform Carl» Cldorometha Metflt,'le ·e Nitrate Chloride TW4-4 (ug/1) Tetraehlol"jtle (~) Otloride (mg/1) (mg/1) .(uWJ) .(~·
17-Feb-10 1700 1 <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
23-Feb-11 1800 1.4 ND ND 7 41
1-Jun-11 1700 1.2 ND ND 7 35
17-Aug-11 1500 NO ND NO 6.6 40
16-Nov-11 1500 1 ND ND 7 39
23-Jan-12 1200 ND NO ND 7.1 38
6-Jun-12 1500 NO NO ND 7.1 43
4-Sep-12 1600 1.2 NO NO 7.1 39
3-0ct-12 1400 1 NO ND 7 38
11-Feb-13 1460 1.12 ND NO 7.36 39
5-Jun-13 1330 ND NO NO 6.3 39.6
3-Sep-13 1380 ND ND NO 7.22 38.8
29-0ct-13 1360 5.3 ND ND 7.84 43.9
27-Jan-14 1260 3.88 ND NO 7.28 37.4
19-May-14 1220 5 NO ND 5.91 47.5
11-Aug-14 1320 NO 7 ND 5.30 40.0
21-0ct-14 1130 NO NO ND 7.02 40.0
9-Mar-15 1350 1 ND NO 7.70 37.6
8-Jun-15 1280 NO NO NO 6.33 41.3
31-Aug-15 1220 ND NO NO 6.45 45.8
19-0ct-15 1190 ND NO NO 6.27 38.5
9-Mar-16 1190 NO NO NO 6.71 39.7
23-May-16 1780 1 NO NO 6.56 41.9
26-Jul-16 1380 ND ND ND 7.22 40.2
tn Cl)
:I ca >
E "-0 -0 "-.2 .c 0
~ I ~ 3: t-
0 0 L!)
""'"
0 0 0
""'"
0 0 L!)
C')
0 0 0 C')
0 0 L!)
C\J
0 0 0 C\J
0 0 L!)
0 0 0
0 0 L!)
v~-oaa-a
6o-1nr-g
90-~00-0~
vo-uer-v~
0
0Motr&f6RR Cari.JGD Chbwemethone Mea,l~•e Nitrate Cllloride TW4-5 ~~ Twae ~ 6agft) C)d's (mgll) (mg/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
·ell•refR'BI Carb&a cw.-~ MetitJlene Nitrate Chloride TWii•S 'levacl!Jmde ~ide (u~ '(ad (~ 'Uf).lt} (1ngll) (mgtl!)
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 <1 7.1 28
11-Aug-10 12.0 <1 <1 <1 7 38
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
26-May-16 13.6 ND ND ND 8.98 45.9
25-Jul-16 10.8 ND ND ND 8.49 44.6
U)
Cl) ::s
ca >
E II.. 0 -0 II..
.2 .t:. 0
It)
I ~ 3: 1-
.-------.------.------r-----,-----.------r-------.-H-das-~~
v~-oaa-a
5o-1nr-9
-90-PO-O~
vo-uer-v~
1-----+----+----+-----1----+----t-----+ B6-1nr-v~
0 L{)
C')
0 0 C')
0 L{)
C\J
0 0 C\J
0 L{)
(1t6n)
0 0 0 L{) 0
Chlorofo.rm Cat· Ito C.bloromethtme r.letb)4 Nitrate Chi 1ide TWU 'fetraebJ' ide Cblerble (u~) ~0,~ ugm .(u,WJ) ~gil) ~mtrm
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 I 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
Ohl~l'Qform Camo ~tihaBe Methylene 'Nitr-ate CblWide TW4·6 Tetrulllorifle CMerid'e (u-) (~' (iugti~ , .. ~mgll) (~
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
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
8-Jun-16 486.0 ND ND ND 3.19 44.1
4-Aug-16 433.0 ND ND ND 3.85 42.2
U)
Cl)
::I a; >
E ...
0 -0 ...
.2
J:
0
CD I ~ 1-
0 0
"""
0 0 C\1
0 0 0
0 0 CX)
0 0 <0
0 0
"""
0 0 C\1
0
c~/~0/170
60/90/LO
90/0~/0~
vO/v~HO
W/6~/170
1dloMfQn:n 61'&.u ftileQJD ~ •• ChiDll'itle ne 'I'W4-7 (~ Tdr.ad:d&Thle '~ ~ .,m €DT§G) ~), f!lld
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 3.7 35
24-Jun-09 1400 <1 <1 <1 3.8 37
15-Sep-09 1500 1.0 <1 <1 4.1 37
Cla:f .Mfcwm C.&n tCMerct~tfiane Mie~ Nitrtlle ~ TW4-'7 , .. ) 'l':etiradil~id'e (Uglj) Qlomte, Ctng4) (..-€~} ~· 29-Dec-09 1300 <I <1 <1 4.2 37
3-Mar-10 1200 <1 <1 <1 3.8 36
10-Jun-10 1100 <1 <1 <1 3.9 31
18-Aug-10 1500 1.1 <1 <1 3.9 36
13-0ct-10 1100 1.1 <1 <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 NO 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
8-Jun-16 909 ND ND ND 3.75 44.1
4-Aug-16 1000 ND ND ND 4.21 42.3
rn Cl)
::l
ca >
E Jo.. 0 -0 Jo.. .2 .c
(.)
.....
I o:::t ~ t-
0 0 0 <0
0 0 0 I[)
0 0 0
"""
0 0 0 ('I)
0 0 0 C\J
0 0 0
0
v~-oaa-a
6o-1nr-g
90-lOQ-O~
vo-uer-v~
~O-Jd'v'-6 ~
·Chh:rufenRJ Car~J,eu c !FUme :ne Me-le :e ~ 011~ 'I'WU ~ etdmu 7Qd&l't8
~· ('!_IM) t~ {~ ~mgf~J
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
Cklorohnn Cawea Clduo tbane Methyl Nit:mte Chl0ft ,e TW4-8 1'etra:dtlodde Chi i · e higH~!) :(~ (Dglll~ {~ ( g~) ~
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
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 NO ND ND 47
7-Feb-13 ND ND NO NO 0.411 46.6
30-May-13 ND ND ND ND NO 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 NO 0.914 46.7
12-Mar-15 961 ND NO 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
8-Jun-16 595 ND ND ND 2.14 58.7
4-Aug-16 522 ND ND ND 2.1 56.9
rn Cl,)
::l
ca >
E ...
0 ~ ..2 .c
0
co I ~
0 0 C\1
I~
0 0 0
~ ...---.
0 0 CX)
0 0 <D
(1f6n)
'
~
~
~
~
~
r ,-A
Cl .... ~ ..,::.::
~~
'\j
0 0
"""
0 0 C\1
0
L~-das-cc
vkoaa-a
5o-1nr-g
90-lOQ-O~
vo-uer-v~
~O-JdV-6 ~
~hnn Carhpn ~~ ~ NiB e Oht~ TWM <( .. ) 11 Maritle ~~ .rib w g«) ~ :~ .~
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 <1 <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
~eftOi11ID•· C•tntn ~ ejftmte Mdh,.teu Nitrate CWeriiie TW4-f 1.?eW eh1wiile ~ ~ry .(~0, €uP0 .(~ (lng/1) fntgll}
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
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
8-Jun-16 76.2 ND ND ND 2.16 35.1
3-Aug-16 76.8 ND ND ND 2.11 33.6
(/)
Cl)
:J ca >
E Jo. 0 -e
.2 .c (.)
0)
I ~
0 C\J 0 0 0 fX)
..... ____ , -
-.........,
/ 'II ~
~ ~ c
5
~
0 co
(1J6n)
IJ
.....
0 C\J
~
0
L~-das-cc:
vkoaa-a
6o-1nr-g
90-PO-O~
vo-uer-v~
CMo,m1ta1'1tm C.)O. Olf:aa ...... Mr~ Jlitrate Clll.nle TW4-8 'lletradd, t"i !Oilkri«e ~) l'UWIJ ~-(q/4~ <~ (mgt!~)
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
Chl1t.POfttMl Cari!)on Ol:ll~tbmle Mefhyl~-e *rate ~·e TW~·19 ~} ietFa~C!Ie .(oWl) auo· (tngfl) ~~ ·!nd~ {llSI!>'
17-Aug-11 180 ND ND ND 1.9 41
16-Nov-11 110 ND ND ND 1.1 45
19-Jan-12 76 ND ND ND 0.9 40
13-Jun-12 79 ND ND ND 0.8 46
12-Sep-12 130 ND ND ND 1.0 44
3-0ct-12 140 ND ND ND 1.6 45
13-Feb-13 154 ND ND ND 1.2 49.1
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
8-Jun-16 1510 ND ND ND 14.9 89.5
4-Aug-16 1500 ND ND ND 14.9 85.3
rn Cl)
:::l
cu >
E ...
0 -0 ...
.2 .c
0
0 ,...
I "=t
== 1-
0 0 (()
0 0
"""
0 0 C\J
0 0 0
0 0 00
0 0 (()
0 0
"""
0 0 C\J
0
v~-oaa-a
60-lnr-g
90-PO-O~
vo-uer-v~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-11 Tetrachloride I (ug/1) (uWJ) (ug/1) Chloride (ug/1) (mg/1) (mg/1)
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 9.01
22-Jun-04 5700 8.74
17-Sep-04 4800 8.75
17-Nov-04 5800 9.1
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 <1 6.8 44
15-Sep-09 1000 <1 <1 <1 7 49
29-Dec-09 860 <1 <1 <1 6.6 46
3-Mar-10 820 <1 <1 <1 6.8 42
10-Jun-10 820 <1 <1 <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 ND ND 6.5 46
1-Jun-11 930 ND ND ND 7.3 49
VMB~ Carlton .CdcmDmetlliume Mtetlbyt :e Nikate Chloride TW4-U TetmdOri.tte
~ ~~ ·~uWI) tu,g!j) i61oY.Iide (~ ~ (.ll)g/1}
17-Aug-11 820 ND ND ND 7.1 48
16-Nov-11 1500 ND ND ND 7.1 46
24-Jan-12 610 ND ND ND 6.8 43
13-Jun-12 660 ND ND ND 6.7 52
13-Sep-12 740 ND ND ND 3 49
4-0ct-12 730 ND ND ND 7 50
13-Feb-13 867 3.23 ND ND 6.83 47.3
18-Jun-13 788 ND ND ND 7.42 49.7
12-Sep-13 865 ND ND ND 7.8 46.6
13-Nov-13 874 ND ND ND 8.01 46.7
5-Feb-14 785 5.19 ND ND 8.47 48.5
23-May-14 751 ND ND ND 6.92 51.6
27-Aug-14 719 ND 1.2 ND 5.4 48
29-0ct-14 803 ND ND ND 7.33 56.4
9-Mar-15 2450 1.24 ND ND 8.72 49.8
8-Jun-15 2710 ND ND ND 8.48 62.2
31-Aug-15 1120 ND 1.62 ND 9.61 73.1
19-0ct-15 2730 ND ND ND 7.5 55.3
9-Mar-16 2660 1.2 ND ND 7.13 55.5
23-May-16 3340 2.19 ND ND 7.81 56.4
25-Jul-16 3200 ND ND ND 8.83 55.3
U)
CD :l m >
E ...
0 -0 ...
.2 .c
0 ,.... ,....
I o::t
== 1-
0 0 0 1'-
0 0 0 tO
0 0 0 Ll)
0 0 0
""'"
0 0 g
(1J6n)
0 0 0 C\1
0 0 0
v~-oaa-a
60-lnr-9
90-JOQ-O~
vo-uer-v~
0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-12 (ugll) Tetrachloride (ugll) Chloride (mgll) (mg/1) (uWJ) (uWJ)
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 <1 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 <I <1 1.4 16
26-Mar-08 <1 <1 <I <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
&l'ofOPIIl Cadwn Cb0r :ethmle Metbylene Nitrate ehkt:ride TW4-Il Cug~Ml) Tet.radllo.r~ e (ag.t) Chlo ·de (mg/1) {mfil? ~lt~, (:UI/'t)
31-May-12 ND ND ND ND 10 34
29-Aug-12 ND ND ND ND 13 39
3-0ct-12 ND ND ND ND 13 39
7-Feb-13 ND ND ND ND 12.6 36.7
29-May-13 ND ND ND ND 14.2 38.6
29-Aug-13 ND ND ND ND 17.4 41.7
6-Nov-13 ND ND ND ND 16.4 41.4
22-Jan-14 ND ND ND ND 18.4 41.6
21-May-14 ND ND ND ND 17 40.2
27-Aug-14 ND ND ND ND 13 47
23-0ct-14 ND ND ND ND 16.1 50.2
11-Mar-15 ND ND ND ND 19.2 50.6
10-Jun-15 ND ND ND ND 18.8 56
2-Sep-15 ND ND ND ND 16.4 60.2
21-0ct-15 ND ND ND ND 18 51.0
15-Mar-16 ND ND ND ND 34.8 56.2
25-May-16 ND ND ND ND 30.7 66.4
27-Jul-16 ND ND ND ND 37.7 67.5
U)
Q) :::s c; >
E ... 0 -0 ...
..2 .c 0
N ,....
I ;
1-
I()
0
~
:
~
-
~
~
0 0
L~-daS-GG
v~-oaa-a
5o-1nr-g
90-PO-O~
vo-uer-v~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-13 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (ul!ll) (ul!ll)
12-Sep-02 ND ND
24-Nov-02 ND ~D
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 <l <l 3.1 <1 4.6 ~A
1-Dec-05 <1 <1 <I <l 4.3 NA
9-Mar-06 <I <I 1.7 <I 4.2 67
14-Jun-06 <1 <1 1.4 <1 4.9 66
20-Jul-06 <1 <l <1 <1 4.3 65
8-Nov-06 <1 <1 <1 <1 0.8 33
28-Feb-07 <1 <1 <1 <I 4 59
27-Jun-07 <1 <1 <1 <l 4.6 59
15-Aug-07 <1 <l <1 <1 4.4 58
10-0ct-07 <1 <l <1 <I 4.1 58
26-Mar-08 <1 <1 <I <1 3.8 54
25-Jun-08 <I <1 <1 <1 4.24 58
10-Sep-08 <1 <1 <l <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 <l 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 <1 <1 <1 5.2 52
10-Aug-10 <1 <l <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-11 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
eblJ&roferm Carbao Cbl&rometlitaue Medl:yleae Nitrate ()h101ide TW'4·1S ~Ug/t~ Jfetr$hlw.id.e (~ CM'M'icte ~In gil) (mg{l) "'gfl,) (U£1t)
29-May-13 ND ND ND ND 6.84 56
29-Aug-13 ND ND ND ND 7.16 63.5
6-Nov-13 ND ND ND ND 6.48 58.5
22-Jan-14 ND ND ND ND 7.09 63.1
21-May-14 ND ND ND ND 5.99 56.1
13-Aug-14 ND ND ND ND 4.8 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
25-May-16 ND ND ND ND 5.87 71.8
28-Jul-16 ND ND ND ND 6.14 69.3
Sep-02
Dec-02
Mar-03
Jun-03
Sep-03
Dec-03
Mar-04
Jun-04
Sep-04
Dec-04
Mar-05
Jun-05
Sep-05
Dec-05
Mar-06
Jun-06
Sep-06
Dec-06
Mar-07
Jun-07
Sep-07
Dec-07
Mar-08
Jun-08
Sep-08
Dec-08
Mar-09
Jun-09
Sep-09
Dec-09
Mar-10
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
0
~
j
j
~
9 0
i\l 9 c.u
0 ~
(ug/L)
9 ()1
0
:::J"'
0 ~ 0 ........ 0
~
3
:::J"'
Sl> en
:::J
0 .....o+
0'"
CD
CD :::J
a.
CD .....o+
CD ()
.....o+ CD a.
:::J
-I ~ ~
I .......
U)
0
0,
0 ~ 0
Co 9
CD
-t ~ I ...... w
0 :::r 0 "'I 9. 0 "'I 3
~
c CD 0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-14 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (u,Wl) (uWI)
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
26-May-16 6.15 ND ND 3.18 2.45 43.6
28-Jul-16 5.00 ND ND 1.80 2.88 42.4
tn Q)
:::J
ca >
E ...
0 ~ ..2 .c
0
"':t ,....
I ;
1-
0 0 r-..:
..
0 0 <Ci
-_..
0 0 u;
-r--
0 0 ...t
(1J6n)
0 0
cY:i
0 0
C\i
L
0 0
~
t
•
•
•
~
0 0
0
L~-das-cc
g~-keV\1-0~
vkoaa-a
£ ~ -onv-v ~
0 ~-/\ON-8 ~
60-lnr-g
so-qa.:J-cc
90-PO-O~
C&dJtm M~e 1l
MW.i16 I ·€ltl&l~ID 1leb:adrl i ~efiban Qbmi fe Glduid
(11,-~lld!(j;) ~ ,&ld}. {--~)
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
Od-.cl onn CaF'hon Chloromethane Metl\ylene ~r te Cldme MW-26 (ug/1) 1'etra · &rid! (qg/1) Ckle ~) ~ 'i f·ue/1~ (iu-1/
31-May-11 1800 ND ND 1.3 0.4 88
17-Aug-11 720 ND ND 7.2 0.9 58
5-Dec-11 1800 ND ND 2.9 2 69
7-Feb-12 2400 ND ND 16 1.7 98
6-Jun-12 3000 ND ND 21 2.5 73
4-Sep-12 3100 ND ND 31 2.6 73
4-0ct-12 1200 ND ND 4 1.8 68
11-Feb-13 2120 ND ND 9.34 2.27 81.9
5-Jun-13 4030 ND ND 52.4 2.11 77.9
3-Sep-13 2940 ND ND 33.2 1.18 60.5
29-0ct-13 1410 ND ND 4.03 1.38 72.3
27-Jan-14 1400 ND ND 13.8 0.549 59.4
19-May-14 1960 ND ND 15.4 0.928 53.4
11-Aug-14 2120 ND 8.7 26 0.7 59
21-0ct-14 2090 ND ND 23.2 0.934 60.1
9-Mar-15 1980 ND ND 27.4 0.732 56.5
8-Jun-15 1980 ND ND 11.2 0.419 62
31-Aug-15 2350 ND 4.05 11.6 0.684 69.6
19-0ct-15 2680 ND 1.32 8.28 0.991 62.6
9-Mar-16 2650 ND 1.32 4.66 1.45 68.3
23-May-16 2220 ND ND 4.57 1.12 66.2
25-Jul-16 3190 ND ND 7.81 1.57 66.4
0 Q)
::::5
"i >
E
""" 0 -0
""" .2 .c 0
co N I
== :E
0 0 I!)
"""
0 0 0
"""
0 0 I!)
C')
0 0 0 C')
0 0 I!) C\1
(1J6n)
0 0 0 C\1
0 0 I!)
0 0 0
0 0 I!)
0
9 ~ -ABVIJ-0 ~
17~-oaa-a
E~-5nv-v~
c~-Jdv-~
0~-AON-8~
6o-1nr-9
so-qa.:J-cc
90-PO-O~
90-ABVIJ-SG
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-16 Tetrachloride Chloride (og/1) (oWl) (og/1) (oWl) (mgll) (mgll)
12-Sep-02 140 ND
24-Nov-02 200 ND
28-Mar-03 260 ND
23-Jun-03 370 ND
12-Sep-03 350 ND
8-Nov-03 400 ND
29-Mar-04 430 ND
22-Jun-04 530 ND
17-Sep-04 400 ND
17-Nov-04 350 ND
16-Mar-05 240 ND
25-May-05 212 NA NA NA <0.1 NA
31-Aug-05 85 <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 <I <1 1.8 9.9 75
15-Aug-07 7.1 <I <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 <1 <1 1.46 58
10-Sep-08 10 <1 <1 14 10.5 71
15-0ct-08 3.9 <1 <1 6.6 9.82 89
4-Mar-09 <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
.CJdoti<dtmll €~ Cldn.eme:llatm M~ae Mitmle a•~ TW4-l6 ;fetl'a -tc!fe .. nga) (~ ~gr4), {o,gi'J) ~) €fi£)
31-May-12 ND ND NO NO ND 53
30-Aug-12 ND NO NO NO ND 59
3-0ct-12 NO ND NO 3 ND 53
7-Feb-13 NO NO NO 3 NO 58-.1
30-May-13 NO NO NO 4.21 NO 49.8
5-Sep-13 NO NO NO NO NO 54.4
7-Nov-13 13.4 NO NO NO 1.37 56.6
29-Jan-14 6.9 NO NO NO 3.16 66.8
22-May-14 14.6 NO NO NO 4.94 80.7
14-Aug-14 229.0 ND ND NO 5.1 80
24-Sep-14 371.0 ND ND ND N/A N/A
29-0ct-14 387.0 ND NO NO 8.40 92.1
12-Mar-15 153.0 ND NO NO 4.30 65.3
11-Jun-15 65.3 NO NO NO 1.06 61
3-Sep-15 82.0 NO NO NO 1.18 65.8
28-0ct-15 112.0 NO NO NO 1.69 58.3
17-Mar-16 45.9 NO NO NO 1.63 56.5
26-May-16 93.4 ND NO ND 1.89 61.3
3-Aug-16 49.0 ND NO ND 2.20 60.0
rn Q)
:::J a; >
E .... 0 -0 ....
.2 .c 0
U) .....
I -.::1' 3: 1-
0 0 co
0 0 It)
0 0
""'"
0 0 C')
(1J6n)
0 0 C\1
0 0
T""
0
v~-oaa-a
6o-1nr-g
90-PO-O~
vo-uer-v~
Bl'etlam CadJ ,g ~ MetllJfeae Nilnlte 1~~1l'ide .MW-32 Ycett; ·~i· •JI (~ :::00.. H :{ud~ (uqtd} (~
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-May-11 ND ND ND ND ND 31
16-Aug-11 ND ND ND ND ND 33
6-Dec-11 ND ND ND ND ND 32
Chloroform Carbon Chloromethane Methylene Nitrate Chloride MW-32 Tetrachloride Chloride ~ug/1) (ug/1) (ug/1) (ug/1) (mg/1) (mg/1)
18-Jan-12 ND ND ND ND ND 21
4-Jun-12 ND ND ND ND ND 32
5-Sep-12 ND ND ND ND ND 33
10-0ct-12 ND ND ND ND ND 35
13-Feb-13 ND ND ND ND ND 34.3
18-Jun-13 ND ND ND ND ND 34.9
4-Sep-13 ND ND ND ND ND 33
29-0ct-13 ND ND ND ND ND 35.7
29-Jan-14 ND ND ND ND ND 34
23-May-14 ND ND ND ND ND 39.7
26-Aug-14 ND ND ND ND ND 34
29-0ct-14 ND ND ND ND ND 34.9
17-Mar-15 ND ND ND ND ND 36.3
11-Jun-15 ND ND ND ND ND 35.8
9-Sep-15 ND ND ND ND ND 37.7
28-0ct-15 ND ND ND ND ND 34.7
22-Mar-16 ND ND ND ND ND 36.7
8-Jun-16 ND ND ND ND ND 37.2
17-Aug-16 ND ND ND ND ND 37.5
(1f6n)
co ci <D ci C\1 ci
~
~
~
~
~
~
~.
~
~~
~~
0
L~-das-cc
v~-oaa-a
5o-1nr-9
90-lOQ-0~
vo-uer-v~
~Q-JdV-6 ~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4·18 Tetrachloride Chloride (ug/1) (ugll) (ug/1) (uWJ) (mg/1) (mg/1)
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-Dec-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 <1 <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 <1 <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 <1 <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 <1 <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 <1 <I 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 ND 9 36
17-Aug-11 29.0 ND ND ND 4.6 23
7-Dec-11 28.0 ND ND NO 6.3 23
19-Jan-12 25.0 ND ND ND 4.4 18
Ckm1!'o1Gnn Ca~ Ctiltl~ ·~lene Nitrate Cblmicle TW4-JJS (t9b) 'fe.traclJJICUidt (1J-) ~ (Jng(l~ ~mgJI~ ~~~~1) •{'~Jg)')ll}
13-Jun-12 24.0 ND ND ND 6.6 30
11-Sep-12 38.0 ND ND ND 6.6 26
3-0ct-12 30.0 ND ND ND 6 27
13-Feb-13 34.9 ND ND ND 5.58 23.1
13-Jun-13 37.9 ND ND ND 8.86 22.9
5-Sep-13 41.0 ND ND ND 12.1 36.2
13-Nov-13 44.3 ND ND ND 14.2 37.1
30-Jan-14 38.9 ND ND ND 12.8 40.9
22-May-14 34.8 ND ND ND 12.2 47
14-Aug-14 32.8 ND ND ND 9.8 49
28-0ct-14 33.0 ND ND ND 11.1 40.8
12-Mar-15 32.0 ND ND ND 11.7 41.6
11-Jun-15 30.5 ND ND ND 9.69 43.5
3-Sep-15 28.7 ND ND ND 15.7 47.6
28-0ct-15 52.9 ND ND ND 6.24 39.4
17-Mar-16 56.6 ND ND ND 5.96 40.7
8-Jun-16 60.0 ND ND ND 5.43 43.8
3-Aug-16 56.3 ND ND ND 5.79 40.7
0 C1)
::::J
CiS >
E ... 0 0 ...
.2 .c
0
00 ,...
I ~
0 0 1.0
...
0 1.0 v
0 0 v
0 1.0 (I')
0 0 (I')
, I
~ •
1\
·r
II~
~ .,::::.: ~
~
~
~..---~-....,j ..,
f....-!).
I ~
l---+" j.....!).
l---+" ~
0 1.0 C\1
0 0 C\1
(1J6n)
0 1.0 0 0 ......
j
0 1.0 0
L~-das-cc
v~-oaa-a
6o-1nr-g
90-PO-O~
vo-uer-v~
CMoMfQ:il'm Cub.cm Clill .~ Medl,teue NJ~,-ate lrcbWMe TW'4•8 'lJJ1 _,u, ride Olaloricle (~ ~~), (ugfrl~ :{us'~ (mgll:) (
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-Ju1-03 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 llOO <50 <50 <50 5.2 ll6
20-Jul-06 ll20 <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 llOO 1.9 <1 <1 4.1 129
10-0ct-07 llOO 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 ll3
15-0ct-08 4200 12 <1 <1 47.8 124
4-Mar-09 llOO 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
~01'01 Ow boa Chlotrometlum.e 1\Whylelre Nitrate Qtl~ TW4-t9 Tetra ti'Ori:cle' Cbliol!'ide ~ugl'~) fugt.t:) (tlg/j) (~) (mJ¥1) {mglt)
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
5-Dec-11 2200 5.4 ND ND 5 148
23-Jan-12 650 1.5 ND ND 0.6 138
6-Jun-12 460 1.1 ND ND 2.4 149
5-Sep-12 950 3.5 ND ND 2.5 149
3-0ct-12 1500 4 ND ND 4.1 150
11-Feb-13 4210 5.15 ND ND 7.99 164
5-Jun-13 2070 5.15 ND ND 2.95 148
3-Sep-13 8100 20.7 ND ND 17.6 179
29-0ct-13 942 6.42 ND ND 4.7 134
27-Jan-14 586 4.05 ND ND 1.62 134
19-May-14 810 5.51 ND ND 1.34 152
11-Aug-14 1410 1.9 8.3 ND 1.6 140
21-0ct-14 4310 4.8 ND ND 4.72 130
9-Mar-15 4660 8.92 ND ND 8.56 238
8-Jun-15 1570 2.62 ND ND 0.916 180
4-Sep-15 7860 7.78 ND ND 11.6 326
19-0ct-15 7840 12.2 5.46 ND 10.6 252
9-Mar-16 . 7780 13.5 1.40 ND 15.7 276
23-May-16 12600 23.1 ND ND 1.27 204
25-Jul-16 6040 9.89 ND ND 10.5 214
(ug/L)
....... .......
1\) """ 0) CXl 0 1\) """ 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0
1-Sep-02
14-Jan-04
28-May-05
10-0ct-06
-t
22-Feb-08 I '\..I\ I I I I I I :e ol::lo I ......
<D
0 J
6-Jul-09 I • I \ I I I I I I 0
""'' 0 -0 ""'' 3
<
18-Nov-10 I ~\ I I I I I I !. c CD rn
I .::sl: \ I I I I I I 1-Apr-12
14-Aug-13
27-Dec-14
10-May-16
22-Sep-17 ~,_ __ _.~, ___ ___.J.... ___ __._ ___ _,__ ___ ......__ ___ ..__ __ ___,
Call4ml 1l
Cti 0 nn ·PI& etfk. I'! --"~ . _.;_
TWA .. Tetlr~!...~.t'de '!f'11r"'; ·-{'··
, __ ,..
<uglj) ~~ (ugQ) ·'-~ ~ gft) (DWJ[)
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 9.4 235
20-Jul-06 5300 <1000 <1000 <1000 2.9 134
8-Nov-06 11000 7.1 1.9 2.2 3.5 124
28-Feb-07 4400 3.1 <1 1.1 4.2 124
27-Jun-07 1800 2.2 <1 <1 2.3 112
15-Aug-07 5200 3.5 <1 1.8 2.1 117
10-0ct-07 9000 6.8 <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
Chloroform Cub on Chloromethane Methylene Nitrate Chloride 1'W4-20 (uWt~ 'l'e~acllloride (ug/1) Chloride (mgll) (mg:/1) (lllgt)) (ugti)
9-Mar-15 19900 20.8 4.85 1.38 9.8 290
8-Jun-15 17600 16.2 13.4 1.73 5.76 296
31-Aug-15 17000 15.1 12.3 ND 9.27 365
19-0ct-15 17000 14.5 10.8 1 6.23 293
9-Mar-16 21600 20.2 4.09 1.16 10.3 293
23-May-16 33700 40.6 ND ND 11.2 318
25-Jul-16 23600 26.6 ND ND 11.3 307
.--------.-----.----....------.------,-----.------.-L ~-das-cc
-9 ~ -ABVIJ-0 ~
-v~-oaa-LG
8 ~ -onv-v ~
G ~ -Jd'v'-~
tn Cl) :;:,
(ij >
E 0~-AON-8~ ... 0 0 ... 0
:2 0 6o-1nr-9 0 N I 'lit 3: 1-
so-qa.:J-cc
-90-PO-O~
vo-uer-v~
0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 0 ....... <D I!) ...;t C') C\1
(1fl5n)
(]tla:rol rm C mfa . Bblowme h Methylene "'~· de 41-U ,. dtforitll Chloride ·~--ll ~ {tel) (ugA) (uWl) ( ~
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
IO-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-1 2 420 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
~JtlorofoJ'Ill Carbon Chlo~tomethane Metbyle~e Nitrate Chloride 'fW4;:21 Tetrachloride Chloride (ng(l? ~ ... 211~ (Ug/1) (oWl) (mgtl) ~mgll)
12-Mar-15 292 1.75 ND ND 10.9 255
8-Jun-15 366 1.92 ND ND 13.1 494
31-Aug-15 281 ND ND ND 14.7 499
19-0ct-15 339 ND ND ND 14.3 413
9-Mar-16 390 ND ND ND 14.6 452
23-May-16 545 ND ND ND 13.1 425
25-Jul-16 456 ND ND ND 16.5 457
t/)
Cl)
::::s c; >
E ... 0 -0 ... ..2 .c 0 .,..
N I "1:1' 3: 1-
0 0 co
0 0 L!)
0 0 ~
0 0 C')
(1f6n)
0 0 C\1
0 0 0
9 ~ -ABV\1-0 ~
v~-oaa-a
8 ~ -Bnv-v ~
G ~ -Jd'v'-~
0~-AON-8~
6o-1nr-9
so-qa.:J-cc
90-PO-O~
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-22 Tetrachloride Chloride (ug/1) (uWJ.) (ug/1) (uWJ.) (mg/1) (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 <I <1 <1 15 130
13-0ct-10 340 <I <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
CW&r&IM'm Carban ~ll&JDShall! Metillylene Nitrate ehloride TW4-22 (ugl£) Te:tnelltol'1We (agti) Cld i. ~mg/1) (mg"L) €·~ '~)
9-Mar-15 12700 3.77 4.31 ND 69.2 675
8-Jun-15 8050 2.42 3.42 ND 47.1 390
31-Aug-15 7810 ND 5.47 ND 64.7 557
19-0ct-15 7530 ND 5.1 ND 56.1 567
9-Mar-16 6070 ND ND ND 31.1 583
23-May-16 8570 2.64 ND ND 58.4 598
25-Jul-16 5840 ND ND ND 61.3 619
U)
C1)
::::s
'i >
E ...
0 -0 ...
.2 .c
(.)
N N I "':t 3: .....
.--------.-----,...-------r------.----.,.----.-------.-L ~ -das-cc
9 ~ -keVIJ-0 ~
v~-oaa-a
£~-Bnv-v~
c~-JdV-~
• 0~-AON-B~
6o-1nr-9
so-qa.:J-cc
90-PO-O~
1----~~----~---~-----+------1------1-----+ vo-uer-v~
0 0 0 -.:!"
0 0 0 C\J
0 0 0 0
0 0 0 co
0 0 0 co
(1f6n)
0 0 0 -.:!"
0 0 0 C\J
0
Chlorofonn Carbon Chloromethane Methylene Nitrate Chloride TW4-23 Tetrachloride Chloride (ug/1) (uWJ) (ug/1) (uWJ) (mg/1) (mg/1)
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 ND ND ND 41
15-Nov-11 ND ND ND ND ND 43
17-Jan-12 ND ND ND ND ND 40
31-May-12 ND ND ND ND ND 44
29-Aug-12 ND ND ND ND ND 46
3-0ct-12 ND ND ND ND ND 45
7-Feb-13 ND ND ND ND ND 43.6
30-May-13 ND ND ND ND 0.116 44.7
5-Sep-13 ND ND ND ND ND 48.0
7-Nov-13 ND ND ND ND ND 43.0
23-Jan-14 ND ND ND ND ND 44.6
21-May-14 ND ND ND ND ND 42.3
13-Aug-14 ND ND ND ND ND 46.0
28-0ct-14 ND ND ND ND ND 46.8
12-Mar-15 ND ND ND ND ND 47.3
10-Jun-15 ND ND ND ND ND 48.4
3-Sep-15 ND ND ND ND ND 54.1
28-0ct-15 ND ND ND ND ND 46.4
16-Mar-16 ND ND ND ND ND 49.1
26-May-16 ND ND ND ND ND 50.4
3-Aug-16 ND ND ND ND ND 49.6
Jun-07
Sep-07
Dec-07
Mar-08
Jun-08
Sep-08
Dec-08
Mar-09
Jun-09
Sep-09
Dec-09
Mar-10
Jun-10
Sep-10
Dec-10
Mar-11
Jun-11
Sep-11
Dec-11
Mar-12
Jun-12
Sep-12
Dec-12
Mar-13
Jun-13
Sep-13
Dec-13
Mar-14
Jun-14
Sep-14
Dec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
0 0 0
(ug/L)
0 0 _.
()
:::J"'
0
"""': 0 ........
0
"""': 3
:::J"'
PJ
(/)
:::J
0 -C"' CD
CD
:::J
a.
CD -CD (") -CD a.
:::J
-1 :E ~ I
1\)
VJ
_.
-4 ~ I N w
0
J 0 ... s. 0 ... 3
< Cl.)
c CD 0
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-24 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (uWl) (oWl)
27-Jun-07 2.6 <1 <1 <1 26.1 770
15-Aug-07 2.2 <1 <1 <1 29 791
10-0ct-07 1.5 <1 <1 <1 24.7 692
26-Mar-08 1.5 <1 <) <1 24.4 740
25-Jun-08 1.4 <l <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 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 NO ND 37 373
6-Jun-12 NO NO NO ND 37 355
30-Aug-12 1.1 ND NO NO 37 489
3-0ct-12 1.0 ND NO NO 38 405
11-Feb-13 5.7 ND ND ND 35.9 1260
5-Jun-13 17.4 ND ND NO 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 NO ND 1.18 31.6 809
19-May-14 62.7 NO 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
23-May-16 69.6 ND ND ND 24.2 771
25-Jul-16 17.8 ND ND ND 34.4 1180
Ill IV ::J
IV >
E ...
.E 0 ... ..2 .s: u
qo
N I qo
~
0
c:i en
---~ ~
0
c:i 00
0 c:i r--
0 c:i 1.0
~
0 c:i U")
(1/Bn)
~
\ I
' \
~ ~
'"""
0 c:i m
..
~ ~
0 c:i N
0 c:i .-l
~
~
~
~
~
l
~
~
~
~
:
~
0 c:i
n-das-n:
9"[-AeLAJ-01:
n-3nv-v1
0"[-1\0N-81
60-1nr-9
so-qa:J-ll
90-P0-01
Chloroform Carbon Chloromethane Methylene Nitrate Chloride TW4-25 (ug/1) Tetrachloride (ug/1) Chloride (mg/1) (mg/1) (owl) (l!g{l)_
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 ND ND ND ND 16 321
16-Aug-11 ND ND ND ND 16 276
15-Nov-11 ND ND ND ND 16 294
18-Jan-12 ND ND ND ND 16 304
31-May-12 ND ND ND ND 16 287
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 ND ND 0.837 62.7
23-May-16 ND ND ND ND 0.959 75.5
25-Jul-16 ND ND ND ND 1.78 74.1
Jun-07
Sep-07
Dec-07
Mar-08
Jun-08
Sep-08
Dec-08
Mar-09
Jun-09
Sep-09
Oec-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
Oec-14
Mar-15
Jun-15
Sep-15
Dec-15
Mar-16
Jun-16
0 0
~
~
~
~
~
~
~
~
-
-
(ug/L)
0 0 0 .....
0
:::J"'
0 --,:
0 ........ 0 --,:
3
:::J"'
0> en
:::J
0 -C"'
(1)
(1)
:::J
a.
(1) -(1)
(") -(1) a.
:::J
-I ~ ~ I 1\)
CJ1
.....
~ I N
U1
0 :::T
0 a -0
""'' 3
< !. c CD UJ
CldnPe c b-eD C'-"' ..... '»ethY.lme Nitntte ~ 'fW'4..2S 1"eb-add0~ ---' ~ toridl ~~ €c.. ~uw') -~g'li_ ~J ~
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
26-May-16 8.23 ND ND ND 15.2 13.9
3-Aug-16 4.42 ND ND ND 17.9 13.9
(ug/1)
0 N .j:>. en 00
...... 0 ...... N ...... .j:>.
~~=18 i I I J I I 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
Apr-16
May-16 Jun-16
Jul-16
Aug-16 •
~ ~ N
0\
n :::T
0 ... 0 0' ... 3
< Ql
s::::: CD Ill
Chloroform Carbon Cblorom~thane Nitrate Chle ·de TW4-l7 Tetr chloride e eue
(ug/.1) _iu;gtj) (ug/1) ~itorlde (ugli) (mglt) (mgil)
24-Jan-12 9 ND ND ND 24 11
13-Jun-12 ND ND ND ND 41 17
30-Aug-12 ND ND ND ND 37 21
3-0ct-12 ND ND ND ND 36 18
7-Feb-13 ND ND ND ND 31.2 18.8
30-May-13 ND ND ND ND 29.4 20.3
29-Aug-13 ND ND ND ND 27.2 19
6-Nov-13 ND ND ND ND 29.8 21.8
23-Jan-14 ND ND ND ND 31.3 21.8
21-May-14 ND ND ND ND 31.1 20.6
13-Aug-14 ND ND ND ND 27.0 23
23-0ct-14 ND ND ND ND 28.2 24.4
11-Mar-15 ND ND ND ND 26.5 26.2
10-Jun-15 ND ND ND ND 24.0 26.8
2-Sep-15 1.30 ND ND ND 20.9 26.8
28-0ct-15 1.60 ND ND ND 23.5 26.2
16-Mar-16 2.11 ND ND ND 25.0 28.0
26-May-16 3.16 ND ND ND 21.2 28.7
3-Aug-16 2.78 ND ND ND 21.8 27.1
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
Apr-16
May-16
Jun-16
Jul-16
Aug-16
0 1-' N UJ
,.....
~
~
~
~
~
~
~
~" ~
' ,
'
(ug/1) .,. V1 0'1 -..1 00 1.0
~
1-' 0
~ .l:=o I N ...... n :::r
0 ..,
0 0' ..,
3
< t:l.l
c I'D Ill
Chlorofo11m CBI'~O Clduem-eQJaue Meth~ Ni~ Qllo1'We TWI4'-l8: T'etr ld.oride Cldo·. (ugtl) [eg!ll) t•g7•) ~· {~gil) ~)
19-Jun-13 ND ND ND ND 14.9 44.6
29-Aug-13 ND ND ND ND 17.3 45.3
6-Nov-13 ND ND ND ND 16.2 45.2
22-Jan-14 ND ND ND ND 16.9 47.8
21-May-14 ND ND ND ND 16.5 45.7
13-Aug-14 ND ND ND ND 14.2 50
23-0ct-14 ND ND ND ND 16.5 52.1
11-Mar-15 ND ND ND ND 19 52.2
10-Jun-15 ND ND ND ND 19 56.4
2-Sep-15 ND ND ND ND 17.8 61.4
21-0ct-15 ND ND ND ND 18.7 52.7
15-Mar-16 ND ND ND ND 34.0 61.6
25-May-16 ND ND ND ND 29.0 67.1
27-Jul-16 ND ND ND ND 31.3 70.1
UJ
Cl) ::::.
CIS >
E ... 0 0 ...
.2 .c
0
co C\1 I ~ .....
co
C\1
I -q-
$
I-
c ·-
"'C
(])
+-' ()
(])
+-' (])
"'C
c
(])
(]) ..c
+-' 0 c
en ctS ..c
E '-0 ........
0 '-0 -..c
0
9~-unr
9 ~ -JBV\1
s~-oaa
s~-das
s~-unr
9 ~ -JBV\1
v~-oaa
v~-das
v~-unr
•
£~-oaa
£~-des
£~-unr
0 0 0 0 0
(1J6n)
ChlorofQrm Catho Cl'dol'emethane ~thylen Nitrate Ohloride TW~Z9 Te rilcl'dGride Chlori e (ugll) (nell} ~ug/1) {uef.l) (mffl) (mg/1)
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
8-Jun-16 366 ND ND ND 2.51 42.9
4-Aug-16 401 ND ND ND 2.44 40.6
0
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
Apr-16
May-16
Jun-16
Jul-16
Aug-16
1-' 0 0
N 0 0
UJ 0 0
(ug/1)
""" 0 0
U'1 0 0
en 0 0
-...1 0 0
~ ~ I N U)
n ::r
0 ... 0 0' ... 3
< I»
c tD Ill
Ch'l:orofor 1 C81"[wn Chloronretha 1\te1h~<le.ue Nitrate Chlmme 1'W4-l9 (ug/1) 'f.elir •Mol'ld:e (ug/1) Chloride (mgll) (mgt~) ·(uWIJ f~
19-Jun-13 ND ND ND ND 0.948 36
29-Aug-13 ND ND ND ND 0.952 36.3
7-Nov-13 ND ND ND ND 1.24 35.9
23-Jan-14 ND ND ND ND 1.36 36
21-May-14 ND ND ND ND 1.44 31.99
13-Aug-14 ND ND ND ND 1.5 38
23-0ct-14 ND ND ND ND 1.84 37.1
11-Mar-15 1.65 ND ND ND 2.15 38.3
10-Jun-15 2.25 ND ND ND 1.75 40.3
3-Sep-15 3.27 ND ND ND 1.75 44.2
28-0ct-15 3.48 ND ND ND 1.86 37.8
17-Mar-16 5.16 ND ND ND 2.74 39.6
26-May-16 7.38 ND ND ND 2.04 40.2
3-Aug-16 6.79 ND ND ND 2.32 38.6
9 0 0
-1-
Jun-13
Aug-13
Oct-13
Dec-13
Feb-14
Apr-14
Jun-14
Aug-14
Oct-14
Dec-14
Feb-15
Apr-15
Jun-15
Aug-15
Oct-15
Dec-15
Feb-16
Apr-16
Jun-16
Aug-16
1\)
0
{ug/L)
~
0
!>-
0
!J1
0
9'
0
:--1
0
!X>
0
..... =E ~ I w 0
0 :::r
0 ""' 9. 0 ""' 3
< !. c CD 0
Chloroform Cftm&;a ~ethane M!ethyJeae Nitrate ~e TW4..31 tetradd«ick Olaloride (ugtf) _"fgtt)_ (ugtl) (uWJ) (,.M) {mgll)
19-Jun-13 ND ND ND ND 1.26 28.4
5-Sep-13 ND ND ND ND 1.1 29.4
7-Nov-13 ND ND ND ND 1.33 28
23-Jan-14 ND ND ND ND 1.32 28.5
21-May-14 ND ND ND ND 1.22 26.3
13-Aug-14 ND ND ND ND 1.1 30
28-0ct-14 ND ND ND ND 1.23 30
11-Mar-15 ND ND ND ND 1.33 30.6
10-Jun-15 ND ND ND ND 1.19 31.1
2-Sep-15 ND ND ND ND 0.916 30.4
21-0ct-15 ND ND ND ND 0.953 29.1
16-Mar-16 ND ND ND ND 1.84 31.5
25-May-16 ND ND ND ND 1.36 32.5
28-Jul-16 ND ND ND ND 1.41 30.6
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
Apr-16
May-16
Jun-16
Jul-16
0
-
-
(ug/L)
0 0 0 0 _..
() ::::r
0
"""'' 0 .......
0
"""'' 3
::::r
0> en
:::J
0 ......
0"'
CD
CD
:::J
a.
CD ......
CD (") ......
CD a.
:::J
-t :E ~ I
U) ........
-4 ~ I
(,.) ......
0 :r 0 ~ a 0 ...
3
~ 2" CD 0
c=hlo:rofol!m C.b.en Cltloromethae M~ Nitrate Chh}rid.e TW4·3! Tetnehlemcte (uglt} (~·) (u~) OBwide ~ug/1) (mgM.) ~mg/1)
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
25-May-16 ND ND ND ND 3.16 71.8
28-Jul-16 ND ND ND ND 3.44 64.4
Nov-1
Dec-1
Jan-1
Feb-1
Mar-1
Apr-1
May-1
Jun-1
Jul-1
Aug-1
Sep-1
Oct-1
Nov-1
Dec-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
Apr-16
May-16
Jun-16
Jul-16
0 0 0 0
'
-
-
-
-
-
-
~ -
~
~
(ug/L)
0 _.
0
:::J"'
0
""""' 0 ........ 0
""""' 3
:::J"'
Sl> en
:::J
0 -0"'
CD
CD
:::J
a.
CD -CD (') -CD a.
:::J
-;
:E ~ I c.u 1\)
_.
-4 :E ~ I w N
(")
':r
0 ""' a 0 ""' 3
< D)
2" C1)
0
Cli oro(o.flm em-u Chhtromdb ~Q Nitrate Chloride TW4~33 T~de (ugll?, .t~Udll (ugM} eb~Gdde (ugll) (ing/1) (mgll)
14-Nov-13 126 ND ND ND 1.82 47.2
30-Jan-14 124 ND NO ND 2.56 43.5
22-May-14 121 ND NO NO 1.63 46.8
27-Aug-14 104 ND ND NO 1.5 43
29-0ct-14 124 ND ND ND 2.22 44.2
12-Mar-15 134 NO ND NO 1.91 44.2
11-Jun-15 127 NO NO NO 1.62 46.4
3-Sep-15 123 NO NO NO 1.64 53.4
29-0ct-15 129 ND NO ND 1.92 44.5
17-Mar-16 122 ND NO ND 2.13 46.2
8-Jun-16 96 ND NO NO 2.06 49.7
4-Aug-16 121 NO NO NO 2.32 48.5
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
Apr-16
May-16
Jun-16
Jul-16
Aug-16
0 1\) 0 .j:>. 0 C1l 0
(ug/L)
CXl 0 0 0 1\) 0 .j:>. 0 C1l 0
-1
== ~ I (,)
(,)
0 ::r 0 ..,
9. 0 ..,
3
~
c CD 0
Cbloroform Ca~b6a ~rom ethane Methyt~e Nitrate Cillo ride TW4·3'4 Te11'acldorW Cblwhle (ug/1) .(u~} (ugtl} _(QB) (mg!l) (mgll~
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
26-May-16 ND ND ND ND 0.605 18
26-May-16 ND ND ND ND 0.605 18
3-Aug-16 ND ND ND ND 0.726 17.2
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
Apr-16
May-16
Jun-16
Jul-16
Aug-16
0
-
-
-
(ug/L)
0 0 0 0 _.
() ::::r
0
""""' 0 -h
0
""""' 3
::::r
Ill CJ)
::J
0 -0"
CD
CD
::J
c.
CD -CD (') -CD c.
::J
-I ~ ~
I
VJ ~
_.
-t ~ I w
ol::lo
0 J 0 ""' ~ ""' 3
< I»
2" CD 0
Chlorofomn Ca:rb()n Cblvomabane Mefllyhm Nitra1e ChteJ-ide TW4·35 TetJracblo:rhle {ug/1) ~!· ( ga) <ldtiide (uglt) {rng1l) tmg}J'
27-Aug-14 ND ND ND ND 0.2 34
28-0ct-14 ND ND ND ND 0.351 34.1
11-Mar-15 ND ND ND ND 0.436 34.9
10-Jun-15 ND ND ND ND 0.452 35.2
3-Sep-15 ND ND ND ND 0.304 35.9
28-0ct-15 ND ND ND ND 0.419 33.4
16-Mar-16 ND ND ND ND 0.521 35.4
26-May-16 ND ND ND ND 0.631 35.4
3-Aug-16 NO ND ND ND 0.723 34.8
Aug-
Sep-
Oct-
Nov-1
Dec-1
Jan-1
Feb-1
Mar-1
Apr-1
May-1
Jun-1
Jul-1
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
Apr-16
May-16
Jun-16
Jul-16
Aug-16
0 0 0
~
~
-
(ug/L)
0 0
()
:::J"'
0
"""': 0 ........ 0
"""': 3
:::J"'
Ill CJ)
:::J
0 -0"
CD
CD
:::J
a.
CD -CD
(') -CD a.
:::J
-1 ~ ~ I w
01
-1 ~ I w (JI
0 :::r
0 ... 9. 0 ...
3
~
c CD 0
Chlorofol'lll Cm.:bon ChloMmethaae Methylene Nitrate Chloride TW4-36 Tetrachloride (ug/1~ (QW1) (ugJI) Chloride ( ug/1) (mg/1) (mg/l)
27-Aug-14 ND ND ND ND ND 65
23-0ct-14 ND ND ND ND ND 67.3
11-Mar-15 ND ND ND ND ND 67.2
10-Jun-15 ND ND ND ND ND 69.3
3-Sep-15 ND ND ND ND ND 76.4
21-0ct-15 ND ND ND ND ND 64.5
16-Mar-16 ND ND ND ND ND 67.1
25-May-16 ND ND ND ND ND 72.3
27-Jul-16 ND ND ND ND ND 69.4
Aug-
Sap-
Oct-
Nov-
Dec-1
Jan-1
Feb-1
Mar-1
Apr-1
May-1
Jun-1
Jul-1
Aug-1
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
Apr-16
May-16
Jun-16
Jul-16
0 0 0 0
~
-
~
~
-
-
(ug/L)
0 _..
0
::J"'
0
"""' 0 ........ 0
"""' 3
::J"'
Q)
(/)
:::J
0 -C"'
CD
CD :::J
a.
CD -CD
(') -CD a.
:::J _,
~ ,J:::.
I VJ
0)
_..
-t ~ (,)
0)
0 J 0 ""'' ~
""'' 3
< Sl)
2" C1)
0
Chlo.roform Carbon Chlorome~;,me Methylene it!ra~ 1'Cbloride TW4•37 Tetrachloride Chloride (ugfl) (U2ffl (ugtl (lu~/l) (mgfl' (m~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
23-May-16 16200 14 ND 1.17 27.9 389
25-Jul-16 15900 17 ND ND 33.4 294
0 0 0 LO C')
. v
0 0 0 0 C')
0 0 0 LO C\1
• I
~
~
.......
0 0 0 0 0 0 ~ (1J6n) ~
0 0 0 0
0 0 0 LO
-
0
9~-unr
9 ~-ABV\1
9kJBV\I
9~-qa.:1
9~-uer
g~-oao
g~-AON
9kdas
g ~ -6nv
g~-unr
TabL
Contour Map Based Chloroform Plume Mass Calculations and Data Over Time
:c -QJ .... IQ
E :;::;
"' 1.1.1
"' "' IQ ::E
E ... 0 -0 ...
0
::£: u
iii :::J .,
"iii QJ a:
2400
2200
2000
1800
1600
1400
1200
1000
800
600
400
200
0
._..-~ ,_..._ ~
.....
Y-40.4x + 1780
1-r::::;\<,.
())
~mass estimate
--Linear (mass estimate)
..,r;::,\.<,
o.t>."
~ ~
~ --------------~-
1-r;::,\.((, o.\.
HYDRO
GEO
CHEM,INC.
1-r;::,\.((,
01-
"-
1-r;::,\.((,
())
TIME SERIES OF RESIDUAL CHLOROFORM MASS
ESTIMATES
M:\718000\nov16\chloroform\residual mass\MassEstTimeSeries: FL.1 Resid CHL Mass
TABLE L.1
Chloroform Plume Residual Mass
Since Third Quarter 2015
Residual
Plume Mass
Quarter (lbs)
0315 1712
0415 1869
0116 1946
0216 2261
0316 1718
Notes:
lbs =pounds
H:\718000\nov16\chloroform\residual mass\MassEstTimeSeries.xls: Table L.l
CHLOROFORM RESIDUAL MASS ESTIMATE DETAILS:
Chloroform Data File: CHL_Surferlnput_Q3_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) Q2, 2015 (previous quarter) data used at wells: MW-1, MW-2, 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):
Ucm3Q16wl.grd: third quarter, 2016 Water Level Grid (ft amsl)
Ucm3Q16bb.grd: third quarter, 2016 Aquifer Base Grid (ft amsl)
Ucm3Q16sat.grd: third quarter, 2016 Saturated Thickness Grid (ft)
Ucm3Q16logchl.grd: third quarter, 2016log of chloroform grid (log of ug/L)
Ucm3Q16chl.grd: third quarter, 2016 Chloroform Concentration Grid (ug/L)
Ucm3Q16ge70.grd: third quarter, 2016 Chloroform Concentration GE 70 Grid (ug/L)
Ucm3Q16volm3.grd: third quarter, 2016 Groundwater Volume Grid (m3)
Ucm3Q16masslb.grd: third quarter, 2016 Chloroform Plume Mass Grid (lb)
Chloroform residual mass estimate kriged grid XYZ files (ascii fot"mat):
Ucm3Q16wl.dat: third quarter, 2016 Water Level Grid XYZ file (ft amsl)
Ucm3Q16bb.dat: third quarter, 2016 top of Aquifer Base Grid XYZ file (ft amsl)
Ucm3Q16sat.dat: third quarter, 2016 Saturated Thickness Grid XYZ file (ft)
Ucm3Q16logchl.dat: third quarter, 2016log of chloroform grid XYZ file (log of ug/L)
Ucm3Q16chl.dat: third quarter, 2016 Chloroform Concentration Grid XYZ file (ug/L)
Ucm3Q16ge70.dat: third quarter, 2016 Chloroform Concentration GE 70 Grid (ug/L)
XYZ file
Ucm3Q16volm3.dat: third quarter, 2016 Groundwater Volume Grid XYZ file (m3)
Ucm3Q16masslb.dat: third quarter, 2016 Chloroform Plume Mass Grid XYZ file (lb)
Chloroform plume mass estimate flle: Ucm3Q16result.xls
TabM
CSV Transmittal Letter
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Dear Mr. Goble,
Kathy Weinel
Thursday, November 17, 2016 1:06 PM
'Phillip Goble'
'Dean Henderson'; Harold Roberts; David Frydenlund; David Turk; Scott Bakken; Logan
Shumway
Transmittal of CSV Files White Mesa Mill 2016 Q3 Chloroform Monitoring
1607518-EDD.csv; 1608133-EDD.csv; 1608399-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 third 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
1
TabN
Exceedance Notices for the Reporting Period
This attachment has been deliberately left blank.