HomeMy WebLinkAboutDRC-2012-002398 - 0901a068803251d0DRC-2012-002398
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www energyfuels com
Sent VIA Federal Express
November 21,2012
Mr Rusty Lundberg
Director
Utah Water Quality Board
Utah Department of Environmental Quality
195 North 1950 West
PO Box 144810
Salt Lake City, UT 84114-4820
Re: Transmittal of Annual Seeps and Springs Monitoring Report
Groundwater Quality Discharge Permit UGW370004 White Mesa Uranium Mill
Dear Mr. Lundberg-
Enclosed are two copies of the White Mesa Uranium Mill Annual Seeps and Springs Monitoring
Report for 2012 as required by the Groundwater Quality Discharge Permit UGW3 70004, as well as
two CDs each containing a word searchable electronic copy of the report
If you should have any questions regarding this report please contact me
Yours
ENyBcpTi^ELS RESOURCES (USA) INC.
David C. Frydenlund
Senior Vice President, Regulatory Affairs and General Counsel
CC Jo Ann Tischler
Harold R. Roberts
David E. Turk
Kathy Weinel
Sent VIA Federal Express
November 21,2012
Mr. Rusty Lundberg
Director
Utah Water Quality Board
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144810
Salt Lake City, UT 84114-4820
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
3039742140
www.energyfuels.com
Re: Transmittal of Annual Seeps and Springs Monitoring Report
Groundwater Quality Discharge Permit UGW370004 White Mesa Uranium Mill
Dear Mr. Lundberg:
Enclosed are two copies of the White Mesa Uranium Mill Annual Seeps and Springs Monitoring
Report for 2012 as required by the Groundwater Quality Discharge Permit UGW370004, as well as
two CDs each containing a word searchable electronic copy of the report.
If you should have any questions regarding this report please contact me.
EN ELS RESOURCES (USA) INC .
. Frydenlund
Senior Vice President, Regulatory Affairs and General Counsel
CC: Jo Ann Tischler
Harold R. Roberts
David E. Turk
Kathy Weinel
White Mesa Uranium Mill
2012 Annual Seeps and Springs Sampling Report
State of Utah
Groundwater Discharge Permit No. UGW370004
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Blvd., Suite 600
Lakewood, CO 80228
November 21, 2012
Contents
1.0 INTRODUCTION ................................................................................................................................... 1
1.1 Sampling Plan Revisions ..................................................................................................................... 1
2.0 SAMPLING EVENTS ............................................................................................................................ 1
2.1 June 2012 Sampling ............................................................................................................................ 1
2.3 Repeat Visits to Dry Seeps and Springs .............................................................................................. 1
2.4 Sampling Procedures ........................................................................................................................... 2
2.5 Field Data ............................................ : ............................................................................................... 3
2.6 Field QC Samples ................................................................................................................................ 3
3.0 SEEPS AND SPRINGS SURVEY AND CONTOUR MAP .................................................................. 3
4.0 QUALITY ASSURANCE AND QUALITY CONTROL ..................................................................... .4
4.1 Laboratory Results .............................................................................................................................. 4
4.2 DATA EVALUATION ....................................................................................................................... 4
4.3 Adherence to Sampling Plan and Permit Requirements ...................................................................... 5
4.4 Analyte Completeness Review ............................................................................................................ 6
4.5 Data Validation ................................................................................................................... : ............... 6
4.5.1 Field Data QAlQC Evaluation ..................................................................................................... 6
4.5.2 Holding Time Evaluation ............................................................................................................. 6
4.5.3 Laboratory Receipt Temperature Check ............................................................................... ; ...... 6
4.5.4 Analytical Method Check ............................................................................................................. 6
4.5.5 Reporting Limit Evaluation .......................................................................................................... 6
4.5.6 Trip Blank Evaluation .................................................................................................................. 7
4.5.7 QAlQC Evaluation for Sample Duplicates ................................................................................... 7
4.5.8 Radiologies Counting Error .......................................................................................................... 8
4.5.9 Laboratory Matrix QC Evaluation ................................................................................................ 8
5.0 EVALUATION OF ANALYTICAL DATA ....................................................................................... 10
5.1 Evaluation of Analytical Results ....................................................................................................... 10
5.1.1 Ruin Spring ................................................................................................................................ 10
5.1.2 Cottonwood Seep ....................................................................................................................... 11
5 .1.3 Westwater Seep .......................................................................................................................... 11
5.1.4 Entrance Spring .......................................................................................................................... 11
6.0 CORRECTIVE ACTION REPORT ............... ; ..................................................................................... 11
6.1 Assessment of Corrective Actions from Previous Period ................................................................. 11
7.0 ELECTRONIC DATA FILES AND FORMAT ................................................................................... 12
8.0 SIGNATURE AND CERTIFICATION ............................................................................................... 13
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LIST OF TABLES
Table 1 Summary of Seeps and Springs Sampling for 2012
Table 2A Detected Constituents and Comparison to Historic Values and Mill Site
Monitoring Wells -Ruin Spring
Table 2B Detected Constituents and Comparison to Historic Values and Mill Site
Monitoring Wells -Cottonwood Seep
Table 2C Detected Constituents and Comparison to Historic Values and Mill Site
Monitoring Wells -Westwater Seep
Table 2D Detected Constituents and Comparison to Historic Values and Mill Site
Monitoring Wells -Entrance Spring
INDEX OF TABS
Tab A Seeps and Springs Field Data Sheets and Photographic Documentation
Tab B Field Parameter Measurement Data
Tab C Survey Data and Contour Map
Tab D Analytical Laboratory Data
Tab E Quality Assurance and Data Validation Tables
E-1 Holding Time Evaluation
E-2 Laboratory Receipt Temperature Check
E-3 Analytical Method Check
E-4 Reporting Limit Evaluation
E-5 Trip Blank Evaluation
E-6 QAlQC Evaluation for Sample Duplicates
E-7 Radiologies Counting Error
E-8 Laboratory Matrix QC Evaluation
Tab F CSV Transmittal
Tab G DRC Correspondence Regarding Annual Seeps and Springs Reports and Data Use
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2012 ANNUAL SEEPS AND SPRINGS SAMPLING REPORT
1.0 INTRODUCTION
This is the 2012 Annual Seeps and Springs Sampling Report for the Energy Fuels Resources
(USA) Inc. (formerly Denison Mines (USA) Corp.) ("EFRI") White Mesa Mill (the "Mill"), as
required under Part I.F.7 of the Mill's State of Utah Groundwater Discharge Permit No.
UGW370004 (the "Permit") and Section 6.0 of the Mill's Sampling Plan for Seeps and Springs
in the Vicinity of the White Mesa Uranium Mill, Revision: 0, March 17, 2009 (the "Sampling
Plan") and Revision 1, June 10,2011 ("Draft Sampling Plan").
1.1 Sampling Plan Revisions
The Sampling Plan for Seeps and Springs in the Vicinity of the White Mesa Uranium Mill, was
revised during the 2011 reporting period. The revisions were completed to address corrective
actions delineated in the 2010 Annual Seeps and Springs Sampling Report for the Mill. The
Draft Sampling Plan was submitted to the Utah Division of Radiation Control ("DRC") via e-
mail for review on June 10, 2011. Per conversations with DRC personnel on June 28, 2011,
regarding the July 2011 sampling event, EFRI used the 2011 Draft Sampling Plan field forms for
the July 2011 sampling event and the June 2012 sampling event even though the 2011 Draft
Sampling Plan had not received DRC approval at the time of the sampling event. To date
comments have not been received from DRC on the 2011 Draft Sampling Plan.
2.0 SAMPLING EVENTS
Seeps and springs which were identified near the Mill in the 1978 Environmental Report (Plate
2.6-10, Dames and Moore, January 30, 1978) are to be sampled annually in accordance with the
Sampling Plan and Part I.E.6 of the Permit. The Sampling Plan specifies the following sample
locations: Corral Canyon Seep, Corral Springs, Ruin Spring, Cottonwood Seep, Westwater Seep
and Entrance Spring.
2.1 June 2012 Sampling
In accordance with the Permit and the Sampling Plan, DRC was notified of the sampling. The
DRC representative was present for this sampling event. On June 20, 2012, EFRI collected
seeps and springs samples from Cottonwood Seep, Ruin Spring, Back Spring (duplicate sample
of Cottonwood Seep), and Entrance Spring. The DRC representative collected a "split" sample
on June 20, 2012 at Cottonwood Seep from the EFRI sampling equipment, using sample
containers he provided. Corral Canyon Seep, Westwater Seep, and Corral Springs were all dry
on June 20,2012. All of the data from the June sampling event are included as Attachment D in
this report.
2.3 Repeat Visits to Dry Seeps and Springs.
During the June 20, 2012 sampling event, Westwater Seep, Corral Canyon Seep and Corral
Springs were dry, could not be sampled, and did not warrant development attempts with limited
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hand tool excavation at that time. Additional visits were made to these locations on June 27,
2012 and July 9, 2012 to determine if development attempts with hand tool excavation would
yield enough water for sampling. The additional two visits did not indicate any changes; that is
there was no indication that development attempts would be successful.
2.4 Sampling Procedures
Samples were collected and analyzed for the parameters listed in Table 2 of the Permit.
During the June sampling event, samples were collected from the locations indicated in Table 1.
Sampling procedures for each seep or spring are determined by the site location and access.
The DRC-approved sampling procedures for seeps and springs at the Mill are contained in
Sampling Plan, Revision O. Samples collected under this plan were collected either by direct
collection which involves collecting the sample directly into the sample container from the
surface water feature or from spring out-flow, or by using a stainless steel ladle to collect water
until a sufficient volume is contained in the ladle for transfer to the sample bottle.
Sampling Plan Revision 0, was revised in 2011 to provide flexibility in sampling procedures to
address differing site conditions as well as to correct several inconsistencies noted during the
2010 report preparation and review. EFRI provided detailed descriptions of the sampling
procedures used in 2010 in the 2010 Annual Seeps and Springs Sampling Report for the Mill,
which was accepted by DRC. EFRI determined a revision to Sampling Plan, Revision 0 was
necessary, because the procedures in Sampling Plan, Revision 0 do not match the site conditions
and do not include the use of a peristaltic pump for sampling or filtering samples for metals and
gross alpha analyses. EFRI submitted a Draft Sampling Plan to DRC in 2011. The procedures in
the Draft Sampling Plan are consistent with the sampling procedures employed in 2010 and
2011. Samples collected under this plan are collected by direct collection, stainless steel sample
ladle, or by use of a peristaltic pump which involves collecting the sample from the source or
out-flow using the peristaltic pump. The peristaltic pump is used to deliver the sample from the
source or out-flow to the sample bottles. Filtered parameters are pumped through a 0.45 micron
filter prior to delivery to the sample bottle.
EFRI employed the previous sampling procedures again in 2012, because the 2010 and 2011
Annual Seeps and Springs Sampling Reports for the Mill were inspected by DRC and
determined to be in compliance with the GWDP. Additionally, DRC was present during the
2010, 2011, and 2012 sampling events and did not provide comments noting that the procedures
used were unacceptable. Since DRC has not commented on the seeps and springs sampling
procedures that were used in 2010 and 2011, EFRI has continued using the procedures
implemented in 2010.
Ruin Spring
In the case of Ruin Spring, sample bottles for all analytes during the June sampling event
(except gross alpha and heavy metals) were filled directly from the spring out-flow which is a
pipe. Samples for heavy metals and gross alpha were collected by means of a peristaltic pump
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and delivered directly to the sample containers through a 0.45 micron filter. The appropriate
preservatives for the analytical technique were added to the samples.
Cottonwood Seep and Entrance Spring
For the June samples collected from Cottonwood Seep and Entrance Spring, the samples for all
analytes (except gross alpha and heavy metals) were collected by means of a peristaltic pump
and delivered directly to the sample containers. In the case of the samples for heavy metals and
gross alpha, the samples were delivered by a peristaltic pump directly to the sample containers
through a 0.45 micron filter. All samples were preserved by the addition of the appropriate
preservative for the analytical technique.
The tubing on the peristaltic pump that comes into contact with the sample water was disposed of
between each sampling. As a result, no equipment required decontamination, and no rinsate
samples were collected.
All samples were stored at 6° C or lower prior to laboratory analysis. Samples were received by
the Mill's contract laboratories, Energy Laboratories ("EL") at 2.2° C and America West
Analytical Laboratories ("A WAL") at 4.5° C.
2.5 Field Data
Attached under Tab A are copies of all of the field data sheets recorded in association with the
June seeps and springs monitoring events. Photographic documentation of the sampling sites is
also included in Tab A. Sampling dates are listed in Table 1 and field parameters collected
during the sampling program are included in Tab B.
2.6 Field QC Samples
The field Quality Control ("QC") samples generated during this sampling event included one
duplicate per sampling event and one trip blank per shipment to each laboratory which received
samples for Volatile Organic Compounds (VOCs). The duplicate samples (Back Spring) were
submitted blind to the analytical laboratory. As previously stated, no rinsate blanks were
collected during this sampling event as only disposable equipment was used for sample
collection.
3.0 SEEPS AND SPRINGS SURVEY AND CONTOUR MAP
Part I.F.7(c) of the Permit requires that a water table contour map that includes the elevations for
each well at the facility and the elevations of the phreatic surfaces observed for each of the seeps
and springs sampled be submitted with this annual report. Tab C includes two contour maps.
The contour map labeled C-l, shows the water table without the water level data associated with
the dry ridge ("DR") investigation piezometers. The contour map labeled C-2 shows the water
table with the water level data associated with the DR investigation piezometers. It is important
to note that Cottonwood Seep is not included in any of the perched water level contouring,
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because there is no evidence to establish a hydraulic connection between Cottonwood Seep and
the perched water system. Cottonwood Seep is located near the Brushy Basin
Member/Westwater Canyon Member contact, approximately 230 feet below the base of the
perched water system defined by the Burro Canyon Formation/Brushy Basin Member contact.
The stratigraphic position of Cottonwood Seep indicates that its elevation is not representative of
the perched potentiometric surface. Exclusion of the Cottonwood Seep from water level
contouring is consistent with previous submissions. The contour map includes the corrected
survey data from December 2009 as discussed below.
Part I.F. 7 (g) of the Permit requires that survey data for the seeps and springs be collected prior
to the collection of samples. DRC previously clarified that the requirement to submit survey data
applies only to the first sampling event and not on an annual basis. The December 2009 and July
2010 seeps and springs survey data shown in Tab C will be used in all reporting where seeps and
springs locations and elevations are relevant.
A full discussion of the survey data and the hydrogeology of seeps and springs at the margins of
White Mesa in the vicinity of the Mill and the relationship of these seeps and springs to the
hydrogeology of the site, in particular to the occurrence of a relatively shallow perched
groundwater zone beneath the site, is contained in Hydrogeology of the Perched Groundwater
Zone and Associated Seeps and Springs Near the White Mesa Uranium Mill Site, dated
November 12, 2010, prepared by Hydro Geo Chem, Inc. and submitted to the Director on
November 15, 2010. Additional information is also contained in the Second Revision
Hydrogeology of the Perched Groundwater Zone in the Area Southwest of the Tailings Cells
While Mesa Mill Site, dated November 7, 2012, prepared by Hydro Geo Chem, Inc. and
submitted to the Director on November 7,2012.
4.0 QUALITY ASSURANCE AND QUALITY CONTROL
4.1 Laboratory Results
All analytical results are provided by one of the Mill's two contract analytical laboratories EL or
AWAL.
The laboratories utilized during this investigation were certified under the Environmental Lab
Certification Program administered by UDEQ Bureau of Lab Improvement for the analyses they
completed.
The analytical data as well as the laboratory QAlQC summaries are included under Tab D.
4.2 DATA EVALUATION
The Permit requires that the annual seeps and springs sampling program be conducted in
compliance with the requirements specified in the Mill's approved White Mesa Uranium Mill
Groundwater Monitoring Quality Assurance Plan ("QAP"), Revision 7.2, dated June 6, 2012, the
approved Sampling Plan and the Permit itself. To meet this requirement the data validation
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completed for the seeps and springs sampling program as discussed in this section utilized the
requirements outlined in the QAP, the Permit and the approved Sampling Plan as necessary. The
2010 Annual Seeps and Springs Monitoring Report noted that in several places the requirements
in the QAP, and Sampling Plan, Revision 0, were in conflict. To address these inconsistencies,
the Sampling Plan, Revision 0 was revised and, as previously stated, submitted to DRC for
review in June 2011. For the purposes of this data review, the Permit and the QAP requirements
were used to determine compliance. The Mill QA Manager performed a QAlQC review to
confirm compliance of the monitoring program with requirements of the Permit and 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 quality control review of
laboratory data methods and data. Identification' of field QC samples collected and analyzed is
provided in Section 4.5.1. Discussion of adherence to the Sampling Plan is provided in Section
4.3. Analytical completeness review results are provided in Section 4.4. The steps and tests
applied to check laboratory data QAlQC are discussed in Sections 4.5.1 through 4.5.9 below.
The analytical laboratories have provided summary reports of the analytical QAlQC
measurements necessary to maintain conformance with National Environmental Laboratory
Accreditation Conference ("NELAC") certification ' and reporting protocol. The analytical
laboratory QAlQC 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 D. Results of review of the laboratory QAlQC information are provided under Tab E
and discussed in Section 4.5 below.
4.3 Adherence to Sampling Plan and Permit Requirements
On a review of adherence by Mill personnel to the Permit, the QA Manager observed that
QAlQC requirements established in the Permit and the QAP were being adhered to and that the
requirements were implemented as required except, as noted below.
Sampling procedures varied from those contemplated in the Revision 0, Sampling Plan as
discussed in the 2010 Annual Seeps and Springs Sampling Report for the Mill. As previously
stated, the Sampling Plan, Revision 0 was revised in June 2011 to accurately reflect the sampling
procedures used during the 2009, 2010, 2011, and 2012 sampling events. DRC has not provided
comments on the Sampling Plan to date; however, the DRC representative was present for both
the 2010, 2011, and 2012 sampling programs and observed the sampling procedures used. The
DRC representative accepted the procedures and made no comments regarding the sampling
strategies employed. No further discussions regarding the changes to the Revision 0 Sampling
Plan sampling procedures are included.
The Permit only requires the measurement of the field parameters pH, conductivity and
temperature. Field parameter measurements collected during this sampling event included pH,
conductivity, temperature, redox potential, and turbidity. The collection of additional field
parameters resulted in no effect on the usability of the data.
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4.4 Analyte Completeness Review
All analyses required by the Permit Table 2 were completed.
4.5 Data Validation
The QAP and the Permit identify the data validation steps and data quality control checks
required for the seeps and springs monitoring program. Consistent with these requirements, the
QA Manager performed the following evaluations: a field data QAlQC evaluation, a receipt
temperature check, a holding time check, an analytical method check, a reporting limit check, a
trip blank check, a QAlQC evaluation of sample duplicates, a gross alpha counting error
evaluation and a review of each laboratory's reported QAlQC information. Each evaluation is
discussed in the following sections. Data check tables indicating the results of each test are
provided under Tab E.
4.5.1 Field Data QAlQC Evaluation
The QA Manager performs a review of all field recorded parameters to assess their adherence
with QAP and Permit requirements. The assessment involved review of the Field Data sheets.
Review of the Field Data Sheets noted that all requirements for field data collection were met
except as set out below.
4.5.2 Holding Time Evaluation
QAP Table 1 identifies the method holding times for each suite of parameters. Sample holding
time checks are provided under Tab E. All samples were received and analyzed within the
required holding time.
4.5.3 Laboratory Receipt Temperature Check
Chain of Custody sheets were reviewed to confirm compliance with the sample receipt
requirements specified in the QAP. Sample receipt temperature checks are provided under Tab
E. All samples were received within the QAP required temperature limit.
4.5.4 Analytical Method Check
All analytical methods reported by both laboratories were checked against the required methods
specified in Table 1 of the QAP. Analytical method check results are provided in Tab E.
4.5.5 Reporting Limit Evaluation
Reporting limits utilized by the laboratory were required to be equal to or lower than the Ground
Water Quality Standards set out in Table 2 of the Permit. For TDS, sulfate and chloride, for
which Ground Water Quality Standards are not set out in Table 2 of the Permit, reporting limits
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specified in Part I.E.6.e).(1) were used. Those reporting limits are 10 mg/L for TDS, and 1 mg/L
for Sulfate and Chloride. All analytical method reporting limits reported by both laboratories
were checked against the reporting limits specified in the Permit. Reporting limit evaluations are
provided in Tab E. All analytes were measured and reported to the required reporting limits
except that the sulfate sample results had the reporting limit raised for samples due to sample
dilution necessary to accommodate the sulfate concentrations in the samples. In all cases the
reported value for the analyte was higher than the increased detection limit.
4.5.6 Trip Blank Evaluation
All trip blank results were reviewed to identify any blank contamination. Trip blank evaluations
are provided in Tab E. All trip blank results associated with the samples were less than reporting
limit for all V OCs.
4.5.7 QAlQC Evaluation for Sample Duplicates
Section 9.1.4 a) of the QAP states that the Relative Percent Difference ("RPD") 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 (described as activities in the QAP) 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 all duplicate pairs for all analytes regardless of whether or not the
reported concentrations are greater than 5 times the required detection limits; however, data will
be considered noncompliant only when the results are greater than 5 times the required detection
limit and the RPD is greater than 20%. RPDs are also only calculated when both the sample and
the duplicate report a detection for any given analyte. If only one of the pair reports a detection,
the RPD cannot be calculated. The additional duplicate information is provided for information
purposes.
All duplicate results were within a 20% RPD in the seeps and springs samples except chloride in
the Cottonwood Seep/Back Spring duplicate pair. The chloride duplicate RPDs greater than 20%
are most likely due to some naturally occurring interference present in the samples. Results of
the RPD test are provided under Tab E. Per QAP, Revision 7.2, and in response to requests from
UDEQ, a separate corrective action for duplicate RPDs outside of acceptance limits has been
developed and is documented in the revised QAP. The revised procedure for duplicate results
outside of acceptance limits was implemented for the chloride results in duplicate pair
Cottonwood Seep/Ruin Spring. The corrective actions that were taken in accordance with the
revised procedure are as follows: the QA Manager contacted the Analytical Laboratory and
requested a review of the raw data to assure that there were no transcription errors and the data
were accurately reported. The laboratory noted that the data were accurate and reported
correctly. Reanalysis was not completed as the samples were beyond the holding time.
Corrective actions were followed per QAP, Revision 7.2, and no formal correct action will be
provided.
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4.5.8 Radiologies Counting Error
Section 9.14 of the QAP requires that all gross alpha analysis reported with an activity equal to
or greater than the Groundwater Compliance Limits ("GWCL") set out in the Permit (for the
seeps and springs samples the Groundwater Quality Standards [" GWQS"] will be used), shall
have a counting variance that is equal to or less than 20% of the reported activity concentration.
An error term may be greater than 20% of the reported activity concentration when the sum of
the activity concentration and error term is less than or equal to the GWQS.
Section 9.4 of the QAP also requires a comparability check between the sample and field
duplicate sample results utilizing the formula provided in the text.
Results of routine radiologic sample QC are provided under Tab E. All seeps and springs
radiologic sample results that had positive detections met the QAP specified criteria for
radiological counting error. The duplicate samples were nondetect, and as such the duplicate
comparability check specified in the QAP does not apply.
4.5.9 Laboratory Matrix QC Evaluation
Section 9.2 of the QAP requires that the laboratory's QAlQC Manager check the following items
in developing data reports: (1) sample preparation information is correct and complete, (2)
analysis information is correct and complete, (3) appropriate analytical laboratory procedures are
followed, (4) analytical results are correct and complete, (5) QC samples are within established
control limits, (6) blanks are within QC limits, (7) special sample preparation and analytical
requirements have been met, and (8) documentation is complete. In addition to other laboratory
checks described above, EFRI's QA Manager rechecks QC samples and blanks (items (5) and
(6)) to confirm that the percent recovery for spikes and the relative percent difference for spike
duplicates are within the method-specific required limits, or that the case narrative sufficiently
explains any deviation from these limits. Results of this quantitative check are provided under
Tab E. All lab QAlQC results from both EL and A W AL met these requirements except as
described below.
A significant number of the seeps and springs samples had the reporting limit raised for Sulfate
due to matrix interference andlor sample dilution. In all cases where the detection limit was
increased, the concentration for the analyte was higher than the increased detection limit.
The check samples included at least the following: a method blank, a laboratory control spike
("LCS"), a matrix spike ("MS") and a matrix spike duplicate ("MSD"), or the equivalent, where
applicable. It should be noted that:
• Laboratory fortified blanks are equivalent to LCSs.
• Laboratory reagent blanks are equivalent to method blanks.
• Post digestion spikes are equivalent to MSs.
• Post digestion spike duplicates are equivalent to MSDs.
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• For method E900.1, used to determine gross alpha, a sample duplicate was used instead
ofaMSD.
All qualifiers, and the corresponding explanations reported in the QAlQC Summary Reports for
any of the check samples for any of the analytical methods, were reviewed by the QA Manager.
The QAP Section 8.1.2 requires that a MS/MSD (referred to as a Duplicate Spike [Matrix Spike]
in the QAP) 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 a MS/MSD pair with each analytical batch was met. While the QAP
does not require it, the recoveries were reviewed for compliance with each laboratory's
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 QAlQC Summary Reports indicates that the MS/MSDs
recoveries and the associated RPDs for all seeps and springs samples were within acceptable
laboratory limits except as noted in Tab E. Five MS/MSD recovery RPDs were are outside the
laboratory established acceptance limits. This result does not affect the quality or usability of the
data because the recoveries and RPDs above or below the acceptance limits are indicative of
matrix interference. Four MS/MSD recoveries were above the laboratory established acceptance
limits, indicating a high bias to the individual sample results. A high bias means that reported
results may be higher than the actual results. Two MS/MSD recoveries were below the
laboratory established acceptance limits. The recoveries do not affect the quality or usability of
the data because the recoveries outside of the acceptance limits are indicative of matrix
interference. Furthermore, the MS/MSD analyses samples for Carbon Tetrachloride,
Chloromethane, and Toluene which were spiked for analyses were not collected at the Mill, and
as such the matrix interference is not applicable to the Mill samples reported herein. The QAP
requirement 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 QAlQC Summary Reports indicates that the surrogate recoveries for all
seeps and springs samples were within acceptable laboratory limits for all surrogate compounds
except as indicated in Tab E. Sixteen surrogate recoveries were above the laboratory established
acceptance limits, indicating a high bias to the individual sample results. A high bias means that
reported results may be higher than the actual results. The surrogate compounds outside of
acceptance limits are most likely the result of laboratory spiking compound degradation. This is
apparent because the same compounds were out compliance limits in all samples analyzed within
a specific period of time. There is no effect on the quality or usability of the data, because the
low surrogate recoveries were on a laboratory matrix spike which would indicate surrogate
solution degradation at the laboratory. These recoveries do not impact other results, because
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there are multiple surrogates added to each sample and all other surrogates were within limits.
Furthermore, there are no QAP requirements for surrogate recoveries.
The QAP Section 8.1.2 requires that each analytical batch shall be accompanied by a reagent
blank. Contamination detected in analysis of reagent blanks/method blanks will be used to
evaluate any analytical laboratory contamination of environmental samples. The QAP specified
process for evaluation of reagent/method blanks states that nonconformance will exist when
blanks are within an order of magnitude of the sample results. Eight analytes were reported in the
reagent/method blanks from EL. Reagent/method blank results are included in Tab E. In all
cases the reagent/method blank results were less than an order of magnitude relative to the
positive sample results or the associated sample results were nondetect. The QAP requirement to
analyze a reagent/method blank with each batch and evaluate the results has therefore been
completed as required.
5.0 EVALUATION OF ANALYTICAL DATA
Analytical Results
As previously stated, all samples were analyzed for the groundwater compliance parameters
found on Table 2 of the Permit. In addition to these laboratory parameters, the pH, temperature,
conductivity, redox potential and turbidity (although not required redox and turbidity were
collected) of each sample was measured and recorded in the field.
The samples were not analyzed for semivolatile organic compounds. Although the Sampling
Plan, Revision O,currently states that the samples will also be analyzed for semivolatile organic
compounds, the Permit was revised to eliminate the requirement for semivolatile analysis. The
requirement to analyze the seeps and springs samples for semivolatile organic compounds has
also been eliminated from the Draft Sampling Plan, Revision 1.
5.1 Evaluation of Analytical Results
The results of the June sampling event show no evidence of Mill influence in the water produced
by the seeps and springs sampled. The lack of Mill influence on seeps and springs is indicated
by the fact that the parameters detected are within the ranges of concentrations for the on-site
monitoring wells and for available historic data for the seeps and springs themselves. For those
detected analytes, concentrations are shown in Tables 2A, 2B, 2C, and 2D. The data are
compared to available historic data for each seep and spring as well as to on-site monitoring well
data. Specific discussions about each seep or spring are included below.
5.1.1 Ruin Spring
No VOCs or radiologics were detected. Metals and major ions were the only analytes detected.
The metals detections were minimal with only molybdenum, selenium and uranium having
positive detections. A comparison of the 2009, 2010, and 2011 data to the 2012 data shows that
the concentrations of most detected analytes remained approximately the same with only minor
ohanges within the limits of normal analytical deviation. The reported values for fluoride,
10
N:\WMM\Required Reports\Seeps and Springs Sampling Report\2012\2012 Annual Report -text.dOCx
magnesium, potassium, sodium, total dissolved solids ("TDS"), selenium, and uranium increased
from the 2011 sample results, but they are below the upper range of historic values for the on-site
monitoring wells. The differences are not significant and are most likely due to normal
fluctuations due to flow rates or seasonal variations due to annual precipitation. Overall, the data
reported for Ruin Spring are typical for a surface water sample with no indication of Mill
influence.
5.1.2 Cottonwood Seep
No VOCs or radiologics were detected. Metals and major ions were the only analytes detected.
The metals detections were minimal with only uranium having a positive detection. A
comparison of the 2009, 2010, and 2011 data to the 2012 data shows that the concentrations of
most detected analytes remained approximately the same with only minor changes within the
limits of normal analytical deviation. The reported values for bicarbonate, calcium, chloride,
magnesium, potassium, sodium, and TDS increased from the 2009, 2010, and 2011 sample
results. In most cases the increases were minimal and within the range of analytical deviation
(e.g. potassium increased 0.3 mg/L). In all cases the detections are significantly below the upper
range of historic values for the on-site monitoring wells. The differences are not significant and
are most likely due to the normal fluctuations due to flow rates or seasonal variations due to
annual precipitation. Overall, the data reported for Cottonwood Seep are typical for a surface
water sample with no indication of Mill influence.
5.1.3 Westwater Seep
Westwater Seep was dry and no sample was collected.
5.1.4 Entrance Spring
No VOCs were detected. Gross alpha, metals and major ions were the only analytes detected.
The metals detections were minimal with only iron, selenium, and uranium having positive
detections. A comparison of the 2009, 2010, and 2011 data to the 2012 data shows that the
concentrations of most detected analytes remained approximately the same with only minor
changes within the limits of normal analytical deviation. The reported values for calcium,
chloride, fluoride, magnesium, nitrate, sodium, TDS, selenium, and uranium increased from the
2009, 2010, and 2011 sample results. Gross alpha was reported; however, the result has
decreased compared to the 2011 results. The detected concentrations are significantly below the
upper range of historic values for the on-site monitoring wells. Overall, the data reported for
Entrance Spring are typical for a surface water sample with no indication of Mill influence.
6.0 CORRECTIVE ACTION REPORT
No corrective action reports are required for the 2012 annual sampling event.
6.1 Assessment of Corrective Actions from Previous Period
No corrective action reports were required for the 2011 annual sampling event.
11
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7.0 ELECTRONIC DATA FILES AND FORMAT
EFRI has provided to the Director electronic copies of all laboratory results as part of the annual
seeps and springs monitoring in Comma Separated Values ("CSV"), from the laboratory. A copy
of the transmittal e-mail is included under Tab F.
12
N:\WMM\Required Reports\Seeps and Springs Sampling Report\2012\2012 Annual Report -text.dOCX
8.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc. on November 21,2012.
By:
yd lund
Senior Vice President, Regulatory Affairs and General Counsel
13
N:\WMM\Required Reports\Seeps and Springs Sampling Report\2012\2012 Annual Report -text.dOCx
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 i formation submitted is, to the best of my knowledge and belief, true, accurate,
and co am aware that there are significant penalties for submitting false information,
includi ssibility of fine and imprisonment for knowing violations.
Da . Fry
Senior Vice President, Regulatory Affairs and General Counsel
Energy Fuels Resources (USA) Inc.
14
N:\WMM\Required Reports\Seeps and Springs Sampling Report\20 12\20 12 Annual Report -text.dOCX
Tables
Table 1: Summary of Seeps and Springs Sampling for 2012
'.-,
~
-, IqQcatiolt" c' , '< . SampI~ Date Work Order No~lLab SefJD Date of'Lab Report
EL = C1206931 EL = 7/27/2012
Entrance Spring 6/20/2012 AWAL = 1207214,1206379 AWAL = 7/3/2012, 7/23/2012
EL = C1206931 EL = 7/27/2012
Cottonwood Seep 6/20/2012 AWAL = 1207214, 1206379 AWAL = 7/3/2012,7/23/2012
Back Spring (Duplicate of EL = C1206931 EL = 7/27/2012
Cottonwood Seep) 6/20/2012 AWAL = 1207214, 1206379 AWAL = 7/3/2012,7/23/2012
EL = C1206931 EL = 7/27/2012
Ruin Spring 6/20/2012 AWAL = 1207214, 1206379 AWAL = 7/3/2012,7/23/2012
Westwater Seep Not Sampled -Dry Not Sampled -Dry Not Sampled -Dry
Corral Spring Not Sampled -Dry Not Sampled -Dry Not Sampled -Dry
Corral Canyon Spring Not Sampled -Dry Not Sampled -Dry Not Sampled -Dry
~
Table 2A Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
","" ~ ., ,,,,i:'~ '2~ ,~ .. ':;;'''l. l .~,;;'~~'l! "' Ruin S~Fing .j, 7q" , .Ill. 'K ri ":...;..' .~ -.,
" ';7 'rr" ':: '.,~ ". . ,:~,i' ~ Jll 7f: Range of Kverrage ,Itt,: ,7 . . 'i' I, , .:.0 I .. I ' . Historic. Values for Ave 2003-I.J "11>' IIi:/" . k' . ,iii I,
C.onstituent ;, 2009,; . 2010 I" 2011 -. May 2011 -July ' 2012· !' Monitoring Wells 1 * 2004~," " .. ~ = J' '.'
"«'cy ",. "jJ 'if !', : MaJor'lons ~mg;I~ , -"I J !;'>'; r." 'f. ",.~, ~ .:: .. : ~l.\:~~
Carbonate <1 <1 <1 1 <1 ._-.. 1~..rJ Or.
~ . (' , 7 . .,. --.~l r. _~
Bicarbonate 233 254 241 239 237 --\e, lFli 0' _::-1lJ
" Calcium 151 136 145 148 147 Ii" '" --.. ; '.'
.~:~" 'i' '~1~!
Chloride 28 23 25 44 28 ·f .. ND -213 '" 27 ~ .,
, ..
Fluoride 0.5 0.53 0.45 0.5 0.52 I:~ . ND -1.3 ',SI'/' ~. G.o 'fl{,
1.,,0'·
Magnesium 32.3 29.7 30.6 31.1 31.9 ' ~;~ "; cr ,~. 1/ -to ~:-. -~~ , ..
Ammonia 0.09 <0.05 <0.05 <0.05 . '-ND ----~:' -~ ,.
Nitrogen-Nitrate 1.4 1.7 1.7 1.6 1.6
7 -b' , "'" ,"Y.
Potassium 3.3 3.07 3.2 3.3 3.5 Ii . '" --<
, .. w __ •
.,. ," ' '" .J. "
Sodium 104 93.4 110 111 115
. c, --
'c'. 1!i ;" "
' •• W ' .
Sulfate 528 447 486 484 464 I,;c. ND -3455 5~'1 -"
pH (s.u.) 7.85 7.51 7.66 8.14 7.53 I~ 6.'7'-8.9: ,,' 0.9 .;,; ..• : ' , "" . ~
TDS 1010 903 942 905 1000
~ 1019 -5548 I, ~i 1053
.'<. I., ,,' Meta,Is·(uglI) • '1 ,CTt: . .. C" ';>
Arsenic <5 <5 <5 <5 <5 ·~ .. rIl --, ~" )! --,.,:\,:;;,
Beryllium <0.5 <0.5 <0.5 <0.5 ~ ~ '~,,'%' <0.5 --E. N -" ~!Il'
Cadmium <0.5 <0.5 <0.5 <0.5 <0.5 ;';;. Nt) :·~4.72 , 0.01 ." x ~'
Chromium <25 <25 <25 <25 <25 '" ---'iIl
I~ ~ ,,', -Ji' .", :,j, ,. -~8 "if.-
Cobalt <1 0 <10 w " <10 <10 <10 ----
'C' ,;
Copper <10 <10 <10 <10 <10 ."' --, '",ii o;::~
, ~
Iron <30 <30 <30 <30 <30 ';!i' '1 NJ? -7~4.2 "' . .;;"' 2~
Lead <1.0 <1.0 <1.0 <1.0 <1.0 --r . .,
Manganese <10 <10 <10 <10 <10 ND .. 34,550 -@:-'m .5 ',,'
Mercury <0.5 <0.5 <0.5 <0.5 <0.5 Ill' --i'" . ~1;-"'ilf~'
, I "l'.tl · 10 " '" i~ l;~
Molybdenum 17 17 16 17 16
.'!§
"
"r, --"';'
""" . ,e . <><" '" .' "'. ;,., ...
Nickel <20 <20 <20 <20 <20 ~t ;,~[,":l' ND -01 ... .c' . I·i"'· (iU)'S -" :_R
Selenium 12.2 10 ',1 ;11' ' 12.J 11.8 10.2 10.8 I~," ;i,.ND -It(')(9,5 i<'.\~ '1:,1,,--. ~ ::: ;"
Silver <10 <10 <10 <10 <10 I" $~ it .i!l __ --"'" !:! i'c," 0 ,~. ,"
Thallium <0.5 <0.5 <0.5 <0.5 <0.5 i ~' ,~ ~f .. ~. (I: :;;~:~Ii\,< ... ~. " Tin <100 <100 <100 <100 <100 «5.0)** I" .. :;:;;--~ --' .
",' . '''',w ill
,', . Jl. "'ii·, .;;
Uranium 9.11 8.47 8.63 8.68 r,;< ND .. )'~~8 i' 10 · u 9.35
"
.~ ,
Vanadium <15 <15 <15 <15 <15 '~::~ ~"!.. 'It '" ~~\0~ ;70 :' __ Ii: .~.~
'j; . .,,," """
Zinc <10 <10 <10 <10 <10 ..•. , --';';'.f "I
:"~, . " " " "i'l~f.·';;';:',· .,' /
... " -~ r~ R,2!diolbgics (pC ill) .i' ~~.'3] :~ , d' '.? ,~ . ,. <~ • ,#,. ;. .,., . . "-I~ i\1 ,. " ,"'" . ,
Gross Alpha <0.2 <0.2 <-0.3 <-0.05 <-0.09 :~~; ';"~ JffD ~~~'6 " .;f·'lt:" (}).28' '-fI('
", ·.i: ' ~~\
It'-.:rW . -'i. .~ . "'r! ..~ -c {. ., Ii ::i", .. ~ ;,~\ '" \i.}f ,yq,CS (u.g/'L) .. " , :it . Of: ii .. , ~,\ • ,,~' ::.;. ~.~,~, ',,,' .. ,,!~ JI, -",!& -',;I'
Acetone <20 <20 ND ND I?-f
. ~ _]i, . cc-;:
ND '£i;, ~.; .. ~;'" ,."-\J,l ---
Benzene <1.0 <1.0 ND ND ND ~ll~k,:!i~t:~;tr~t: _.:~ JJ,r'.' 1,7.· .• ".' . ':~ ','B
""l( '1'" "j~'iII ... ~.. !''li'.' f~
tetrachloride <1.0 <1.0 ND ND ND I~f~;~~'" ' ,~ '(; ,-Ii; ,. ':;~;;!{u ill! ,~.3"j).W.~ :.-i,., . ' . ---'~'~: IJ,'" » .. "), ,,~,~
Chloroform <1.0 <1.0
Chloromethane <1.0 <1.0 ND ND ND
MEK <20 <20 ND ND ND
Chloride <1.0 <1.0 ND ND ND
Naphthalene <1.0 <1.0 ND ND ND
Tetrahydrofuran <1.0 <1.0 ND ND ND
Toluene <1.0 <1.0 ND ND ND
Xylenes <1.0 <1.0 ND ND ND
From Figure 3, Table 10 and Appendix B of the Revised Addendum, Background Groundwater Quality Report: New Wells
for Denison Mines (USA) Corp's White Mesa Mill Site, San Juan County, Utah , April 30, 200S, prepared by INTERA, Inc.
and Table 16 and Appendix D of the Revised Background Groundwater Quality Report: Existing Wells for Denison Mines
(USA) Corp. 's White Mesa Uranium Mill Site, San Juan County, Utah , October 2007, prepared by INTERA, Inc.
2 From Figure 9 of the Revised Addendum, Evaluation of Available Pre-Operational and Regional Background Data,
Background Groundwater Quality Report: Existing Wells for Denison Mines (USA) Corp. 's White Mesa Mill Site, San Juan
Couinty, Utah , November 16,2007, prepared by INTERA, Inc.
*Range of average historic values for On-Site Monitoring Wells as reported on April 30, 200S (MW-1, MW-2, MW-3, MW-
3A, MW-4, MW-S,MW-11, MW-12,MW-14, MW-1S, MW-17, MW-1S, MW-19, MW-20, MW-22,MW-23 , MW-24,
MW-2S, MW-26, MW-27, MW-2S, MW-29, MW-30, MW-31 and MW-32) 2
**In June 2012, the samples collected were inadvertently analyzed twice for Tin only. Both results are shown, and both data
packages have been included in this report.
Table 2B Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
""~ , " , " ' n ' I,'" rlfa .. <,,, ~~~ , ,~ I~ '.-"'. ' .. ' 'ri';~, "~-, _ Ill. "', ,if~ ,O! [~ C2ttonw~o~~§~e)p '" 'I ,i. .. , ,.,' . ,~ ~ ~', ,.;il' )li'
'f': ~'!il ,~ ,"" ':1 Ii· ,'-.r ,,' ) ',. .'. ~i~, 'n; " '~/~. ': ~!'" ... '., .. ," , ,-~' I,," '-' \1 ~' '. 'r'" . ,;
1'5 I~ " Range of Average ',-
1 "
8', , Historic Val,:,es for k: A \Ie 1977 -"""
, ,',i~' ~t 2009
I!!. ~,011);; ~aYUl . 201t ;. J;uly !:< ,:" iM~nit9ring Wells1* ' Constituent I~":iii ' ,20]0 ";F' !;i& .. 2012 ,~ ',,(};_ t982 1 ~
!lI,~, ;r. ~ -~ajor Ions (mgt!) ,Ii "' ~~,~ .~ , ,', , ,~ h~ ," ,
Carbonate <1 <1 <1 6 <1 'i' --,.I Ii!! --I:il , I'~ ~. '",
Bicarbonate 316 340 " ,,;;' ,. I!~-" 330 316 326 ", ,1:, , ;'!'II! ,:~ ]Il , --"'c "'," Calcium 90.3 92.2 95.4 94.2 101 I,;:; ,,-~;;: ~ I~ --.c. ~'i .
Chloride 124 112 113 134 149 ND -21S ~ 31 ~.ij
I~ .:
Fluoride 0.4 0.38 0.34 0.38 0.38 I~'.~, NO -1:3 .~ It,-rIj'1t? 8 . 'if
.•.. ,j . " "', 'J '11;""
Magnesium 25 24.8 25.2 25.2 27.7 .. ' ... ?: ~ ii; I~; ~". --::' ! " 'c, , " ," .... "~ .. <~
Nitrogen-Ammonia <0.05 <0.05 <0.05 <0.05 <0.05 :!l ~ ~ I~ --~
" , , .... 7 '~
Nitrogen -Nitrate 0.1 <0.1 0.1 <0.1 <0.1 1,~$1 . ,~-~ ,~' "~l "I!: --'" ~ ... ,
Potassium 5.7 5.77 6 5.9 6.2 ~::-'ll~ ~' _I~: "",,--
!~ !l
.Z# '.
Sodium 205 214 229 227 247 ~ --",' ." I:' -., ':..-
Sulfate 383 389 394 389 256 ND -3455 ~,I~ .~ 230 .,; ,i,;: '" pH (s.u.) 7.73 7.47 7.55 8.04 7.53 r 6.1, j~.9 11;; ,"', ~7.6 .~
,'" ,<
TDS 1010 900 1030 978 1040 1019 -5~48 lIP 811 ,Ii
. '_' " "
-ft." ;~M~t~l~ (ug/l) !l'~ "f ~~ ''"~' "~' ",' ,"-' " 8:'~c }'i . e ~jl' ." "
",:
.'
Arsenic <5 <5 <5 <5 <5 --T'ill" ' Ii; "~, ---"'.'" t"~ 'Ill .. ~' 1", -
Beryllium <0.5 <0.5 <0.5 <0.5 <0.5 ~, u --1"\, ," , -j-q.
Cadmium <0.5 <0.5 <0.5 <0.5 <0.5 ::if " ~-~?b '", --;;, '1 ,'1,,', I~ 2. II ,~
Chromium <25 <25 <25 <25 <25 --,!,! " If ,:~i ' __ '. -·Il. ' -ti"
Cobalt <10 <10 <10 <10 <10 ---i>i, --'
Copper <10 <10 <10 <10 <10 ill; -:or --I ,-'
Iron <30 <30 53 <30 <30 NT) -7~,42 :;" '~ 150 -: ,,~ ,; i; ,
Lead <1.0 <1.0 <1.0 <1.0 <1.0 ~ ----:: --:~ -
Manganese <10 <10 <10 <10 <10 NI) -3~,5~0 F -y;c' 5*0 " ;~ lilli, I~ ,
Mercury <0.5 <0.5 <0.5 <0.5 <0.5 "'-'''.il, .,;-I~ -~~.~ ~~~~ B'. .. I .. 'L'~'
Molybdenum <10 <10 <10 <10 <10 1~ I" "',:1 ~
'" ' "
Nickel <20 <20 <20 <20 <20 " " NiD -6i " ''''.~_~ !I .'" mic'p II<
Itip
--, 'i:,~f'"
Selenium <5.0 <5.0 -y Nb -1~6.5 · . '~~" ';, <5.0 <5.0 <5.0 'II:: ---~
Silver <10 <10 <10 <10 <10 ~.'", I~ . ~ ~,; (j-'.;.""~' ", t:)) " !'it --,..;i, " ,fit,
Thallium <0.5 <0.5 <0.5 <0.5 <0.5 I'W lfii ',: ~ "'a ';-_ ',~r:Jl :", I~ ~~'!_ --:' ;1 ,~ "i
<100 h " Ji., n I;~~." rii ,""'&<J) <100 <100 I" '*i I:~ " Tin <100 <100 «5.0)** I.~' , "~ --, ..
Uranium 8.42 8.24 7.87 8.68 8.17 ND -'59.8 ',' '-':--.J ,,p rtt ' ~~
Vanadium <15 <15 <15 <15 <15 I~il". ~ ',""~ _:..' ''0; . ~::~' '. "" ';(1\1,:: ,
Zinc <10 <1 0 <10 <10 <10 '~,~f --"'I', ,. ~"
". '-' , -,,:" --". -" ' .<J~' " ~ :R3djol~g,ifS(P(]JI) .if '6 ~ -;~. --',,, ' ", ',5" . ;~ ;.;, ,: -, Il, '], ' ,," ". -" ,~' "'i , ,', "e~ \ : £;, , , ,"" ,'':# '~ Gross Alpha <0.2 <0.2 <0.1 <-0.1 <-0.2 lr ND~~' ~. ~7.2 .,; ~!fj';' ,--I,,:;;i,yc
I~ A~ ;. '~'1". ~l!.,j, fii , :" 'e' -, "'~, V()~S (ugIL) :,[ ," . ~ " "',' -:'~~ : it. ,
. \~ , "', " ' .w,. ' " J., .' , .n :::~: ~ "', ' ,1 ""ci
Acetone <20 <20 ND ND ND :~'P ii "~f,~\~i!li .:l:f ,~'~~" "~~ ..' ,~ -;:-. ,~" --, . Fow", , , .'~"
Table 2B Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
~~" 'I!'I ,~ 'Wi ' • • (J, '"'1Il . ~i' . '
" &! ~ ': r@_,:, .~ ;.i~:~ ~, q~t!0nw~od ,~eell 5: or; ".. """. '-" ,:, " . ,fO;: . ,",' ,',")1;_ ~'_i1I c..;~
.... ~, . , .... ~.~ . rJ,' ~r~i'" -'u, I:" "'-~ ,," '-Ii "iCq' I~' v ,. "."", ,N. 'if • """.' -, ·:ji ,
I' ;~ ~. Ii'll ., " ;
'; It :;, . "~1 j.) Range of Average !' I~~ ,
I, .. ·.· : ~ ,~ 1"" ~ Historic V. alues fOf<>l! A¥e 1977·;.."~ 'd ' .. R·· , I,
\~ 2011-May ~iOU -Jl,lIy " ~ ~ Constituent 2009 ,; 2010 20tZ. MO,oitoring Wells1,.. II 1982 1
10', , " ~ ,
Benzene <1.0 <1.0 ND ND ND It" ,I);v~ --1{tl
r·)Q.t. ~~, ';0 ~Jlr " "
tetrachloride <1.0 <1.0 ND ND ND ~"...., --'p.;~ --,e.;
.. .,'" "., -~
Chloroform <1.0 <1.0 ND ND ND ' ~w.~, --{~I ~.., ~" :> --,' .
-~ " ."," ~ _!. "'",
Chloromethane <1.0 <1.0 ND ND ND 1'1 ~. -~!II.' ./1 g,;~,,! . ',.,; ,j:
MEK <20 <20 ND ND ND ,,~£./, ~ -':'~ )' nLl~l ,;
. "jr~'" :. ~ "
Methylene Chloride <1.0 <1.0 ND ND ND ·"'l.,.tJi 7
, I~ " --,<f'"
I·' ; , '" . ':i> %:
Naphthalene <1.0 <1.0 ND ND ND '\.~ .,,' ~. _~ '1-\1, ,;' f ';-f':,
',d', .' 11ft" [L "<L'~ .,.. ,i' 'r"
T etrahydrofuran <1.0 <1.0 ND ND ND ,.' -" .. ',,~.h )/ , ~
I' i -;;;, . .01
Toluene <1.0 <1.0 ND ND ND :r.~
''; . __ if . . '(; ~~. ~r,. "i' "'.-''>I!' c, ",'
Xylenes <1.0 <1.0 ND ND ND 'Ii --7ft": --
'" ~, c>c
1 From FIgure 3, Table 10 and AppendIX B of the ReVIsed Addendum, Background Groundwater QualIty Report. New Wells
for Denison Mines (USA) Corp's White Mesa Mill Site, San Juan County, Utah, April 30, 2008, prepared by INTERA, Inc.
and Table 16 and Appendix D of the Revised Background Groundwater Quality Report: Existing Wellsfor Denison Mines
(USA) Corp. 's White Mesa Uranium Mill Site, San Juan County, Utah, October 2007, prepared by INTERA, Inc.
*Range of average historic values for On-Site Monitoring Wells as reported on April 30, 2008 (MW-1, MW-2, MW-3, MW-
3A, MW-4, 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 and MW-32)
**In June 2012, the samples collected were inadvertently analyzed twice for Tin only. Both results are shown, and both data
packages have been included in this report.
Table 2C Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
I~'i " ,'"'' 1l1. '" WestWater Seep~' ..... :
¥c'ff.,. .. ",' ".'" . ""4 , : orr ~ ." ,. ,-. .~.'" ~~-L:"'" r.i!i<
i~~'ii>,"""!, :rr V'.~>' 'c .,:~,~~." , ,'t ;"'i!,"i, .. • [i! . liP.' ;~~ ~, .. "= ,,:'l~ [-il, ' ,~~ ~ ,~,I ~~"" Range. of A ver~ge' I: . ~ ~. 'Historic Values for i.-, ,-~ii.f' '" . I' 'l'J' Z""O,tl -M~y 201~,,; July 2012 · M OJlJioring Wells! * .' 'Gonstituent .~ '~, ''f 2009. c.~t., fA., 2010 't"p, '~ " ..
~, . " . .t, • ,;0/ y . . Major Jons~~(mgll) ~ .. -. , "'Cl' " ~
'J' ',' '~ ~ ~ '" ~' th
Carbonate <1 <1 <1 "". " --~ . i,
,I'll.,., "-
Bicarbonate 465 450 371 ." \ J~-"ci ''''~ il
Calcium 191 179 247 -: --.i" --, -
Chloride 41 40 21 rJir~ cA, ']~JD' _ 213
.," ';~i.
Fluoride 0.7 0.6 0.54 ",:, .. ND -1.3 . ,.
Magnesium 45.9 44.7 34.7 w'" ,~i t, '" '.1, ---~~~ · "
Not Sampled -Not Sampled '~'''~ " , .:,..
Nitrogen-Ammonia <0.05 0.5 0.06 I 'x · ~ , Dry -Dry e "
--,,',
Nitrogen-Nitrate 0.8 <0.1 <0.1 :1F'.,: 0>' ,~;:;, ~~~.' . ,-'';' ,·"'8 . " ~
Potassium 1.19 6.57 3.9 ", " · i'
.:" ". --''!
Sodium 196 160 112 I~' .~ ".i?~;-" . ",
Sultate 646 607 354 :-" NT}-34§5 ill'
pH (s.u.) 8.01 7.38 7.2 i,i ;6.7-~.9 ,i.
TDS 1370 1270 853 ,~ tpf9i;' 55Lf8 .;
-/' il} ". , Metals (ugll) ~.~ .... -it
';\", i I 0: ll"li ~ ~ .. " .,-: I:[
Arsemc <5 <5 12.3 I,'" ", ~." -:' i":~" "f"f~ I)")"
Beryllium <0.5 <0.5 0.91 I~ '" '!l'" .. ",' --,
Cadmium <0.5 <0.5 0.9 I;', .. ,:, .~ -41."l~,/ 'Il'
-.~"
Chromium <25 <25 <25 I,: .. ~~J< . --
Cobalt <10 <10 <10 .~';'i, C,
,.IIJ',. ;;~-;~. '/ff,:
Copper <10 <10 16 Ii> --t£~ .. ~
Iron 89 56 4540 I~)~ ~ ';" · i, .~, ~'" 794g,,~ !', iC,
Lead <1.0 <1.0 41.4 I~" \" ,"" --' ~,
'C"
Manganese 37 87 268 I~ '0; ND -34,550",
Mercury <0.5 <0.5 <0.5 Not Sampled -Not Sampled ,', ,,--" --
Molybdenum
Dry -Dry 1-' ,'" " '0 29 29 <10 ~; ---'" £
Nickel <20 <20 29 ., 'S , NJD -61' I:if" "
Selenium <5.0 <5.0 <5.0 I' "P,' ' NJ? -106.5 'r:;
Silver <10 <10 <10 'iel'" . 5:1,.,--',' ''t" '"
Thallium <0.5 <0.5 <0.5 ~-. --" ,~
(c;> • .:''!!. --w cf:-'W". !r
Tin <100 <100 <100 _1i!!'1iI .... : --~"""':, -1:; ie" '.
Uranium 15.1 46.6 6.64 in !~ ~ }ID -5~.8 ... '.'" T ,~J,
Vanadium <15 <15 34 ~{:' .' "",,",1 --f~ .'!l~ }~,~: ';::"7.;' , ~ i~'ll(!l < •
Zinc <10 <10 28 ,'" ," ~~' :~ .. " '. ~ ,-, -;\, ';,
-'i','.' ~,;": .. " ~ ','; ,."" I", /. ·',i" " ";:iF~ , . ~'i' . ;Ra(J;i~loglcs (pC-iii)' "1 ,~:, '1\1; ,.;r 'i~~ 1, , '""j1f't.,' ~,¥", ", ~'\'1I!',i"~,:(~~' :'S;;;, • lj. ,Iii'
:'1: :s; '" ",,-;~ . .; "" if ,F 0.5 Not Sampled -Not Sampled ~ts', .
Gross Alpha < -0.1 <0.3 Dry -Dry No' -36 " ~ " ,,'
Table 2C Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
,Westwater. Seep
Benzene <1.0 ND
<1.0 <1.0 ND
<1.0 <1.0 ND
<1.0 <1.0 ND Not Sampled ., <20 <20 ND Not Sampled-
<1.0 <1.0 ND Dry -Dry
<1.0 <1.0 ND
<1.0 <1.0 ND
<1.0 <1.0 ND
<1.0 <1.0 ND
1 From Figure 3, Table 10 and Appendix B of the Revised Addendum, Background Groundwater Quality Report: New Wells for Denison
Mines (USA) Corp 's White Mesa Mill Site, San Juan County, Utah , April 30, 2008, prepared by INTERA, Inc. and Table 16 and Appendix
D of the Revised Background Groundwater Quality Report: Existing Wells for Denison Mines (USA) Corp. 's White Mesa Uranium Mill
Site, San Juan County, Utah , October 2007, prepared by INTERA, Inc.
*Range of average historic values for On-Site Monitoring Wells as reported on April 30, 2008 (MW-1, MW-2, MW-3, MW-3A, MW-4,
MW-5, MW-11, MW-12, MW-14, MW-15, MW-17,MW-18, MW-19, MW-20, M W-22,MW-23, MW-24, MW-25, MW-26, MW-27,
MW-28, MW-29, MW-30, MW-31 and MW-32)
Table 2D Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
;J:l ,; '''ti " . ". ~ '" ")'. }.i'. ~\ ' '!Il'>' I
",: .' J;',. ~ f~ C>-~;;>!k . "",i. ", "".~ ,-.. .'!L '.; , .... ". ,~~.p~tranee Sp~?g ~' "''4( ;i;", " .,~ A>o ,.",-t •. ",
1'<" D' iii:< "" .. , , . ~;,-~ 5~' . ." .. ,,",' " "". '"oil-> . ~l ' '" lif' ':. ""e I.: 'Range oJ Average' Ie..;> . ''j. ;~ . 'ii ,r Historic Values for ".; .~' I' '
,
Itlf.l. €,onstituent rt';~ It! 20ll-,May ,,:2011 _ July '" Monitorjng Wells! *~_ 'j Y. 2,009 ,. ,2010 "Ii) '<~ • -'" "' 2012 .F'
I'~ -",j ~ ",'. :( .y'. W,o; i'~ t! (1.,,%" '~aj or, Ions (!ll~l)-~~, ,'f':. if. " ' ,"~, 1'1" _aiO",
;. "' • '~;i .f!,., ,1\">" .. ' ,_ "'i, .~ Ii " "'ff: •. 1Ii! ," ',1, .... ,~ ,
Carbonate <1 <1 <1 7 <1 ""'I ':.-" .. ,'iJ'~" l' . ,iL
Bicarbonate 292 332 270 299 298
.. ~ --I"" ";~i . II! T " Calcium 90.8 96.5 88.8 96.6 105 ~I ,):~. --"''', . :;r.l.""~"'
Chloride 60 63 49 64 'i" 78 ND -2.13 "
Fluoride 0.7 0.73 0.58 0.58 0.64 'il ND-1,3 !~
Magnesium 26.6 28.9 26.4 28.4 32.7 ~~i: r~} --", ~' .i,~ .. ..
Nitrogen-Ammonia 0.28 <0.05 <0.05 0.32 <0.05 ~ . "" ;i ~~.~--.
Nitrogen-Nitrate 1,4 1 1.4 0.5 2.8 . "", ';
" ::ij--:1,
Potassium 2.4 2.74 2.6 2.9 2 ''1<1 "!I '" ~1!." :c~,!';l "J ,_,/'i>i.-' A" J ,~'. ~j
Sodium 61.4 62.7 62.5 68.6 77.4 .~ --."
Sulfate 178 179 166 171 171 ND -3455 ~
~ .~
pH (s.u.) 7.85 7.56 7.96 8.17 7.5 :r, ,1\1'( 6.7-8.~" ,,,,Ji
TDS 605 661 571 582 660 i 1019 -"5548 .':~;:'
~' "', Me~als (ug/l) '~ \'i " ..
i· .' m .,; ,., . ;;', -.,
Arsenic <5 <5 <5 <5 <5 ."" 'ii, ' . ,:, .~
, .,~_'.*jJ; -;" "~,, i'! 'f~ ~;J~','ii
Beryllium <0.5 <0.5 <0.5 <0.5 <0.5 I':· . ,g.~:.~ I', i~l\t'" :~ .,
Cadmium <0.5 <0.5 <0.5 <0.5 <0.5 ~ ND -4.78 -, ,
Chromium <25 <25 <25 <25 <25 I'f' 'Ii ,,":~ ',,-~ .. ,,J'; ~~.,~
Cobalt <10 <10 <10 <10 <10 :~ 2-'~:
Copper <10 <10 <10 <10 <10 -:' --<c"
'" iii 'il
Iron <30 <30 37 55 34 ~ Nq:-]942 ,
", . l¥, ":
Lead <1.0 <1.0 <1.0 <1.0 <1.0 " --
" .'"
Manganese 54 11 47 84 <10 ND -3~~550 m ;~
Mercury <0.5 <0.5 <0.5 <0.5 <0.5 I"" , -,; .,'] ,"-'!Ii~i:J~;: ., . ~
Molybdenum <10 <10 <10 <10 <10 II:: ~ c ""': '-.
I~ --If.
Nickel <20 <20 <20 <20 <20 NJi) -61 ,1:1
. -;:,; ~, ,r:t
Selenium 12.1 9.2 13.1 5.5 13.2 . ,; NDJ;!.06.5 '~r~~
Silver <10 <10 <10 <1 0 <10 .~-
"I,
Thallium <0.5 <0.5 <0.5 <0.5 <0.5 .' --'" -~"
,', ,J'j ",~
<100 <100 <100 ;h '~~;~~,,~ ~. Tin <100 <100 «5.0)** Iii: .. " ili'~'" "
Uranium 15.2 17.8 18.8 15.3 21.1 .:.. ND ~··59.8 . 'f'JI/i!
Vanadium <15 <15 <15 <15 <15 1;i;. '," < ,"," ''''~" . ;" ~'
Zinc <10 <10 <10 <10 <10 .' :;".'11' .~:-,';;·G,l;' I,r,,~;~,~ .·iiI .ni .0;, ''" \
~ .' ,. -'-. ell',' ,P .:'#fni. "', ~t ' Radiologies (PCill) .', "nf .~ I" ,.:' .~ ii!',fj! ".f\ iF ':', " .,. ~/1h '(l' \0 '?' " ~"~,, ;5 , "~
Gross Alpha 0.9 <0.5 1.5 1.6 0.5 ~ ~tI't;. 36 ,
I"" ,'} , ~":~:; ••• !,: ~:~;f~tl~/:'\' ,_t;),~., ,;~jt ,~:,i~d\i:i ;.'," .';,;' 'i',VOCS (ugfC)' ',','" "fi~;,.~;;'. ,',\"'j;.", '., ;,., , •..•. ~
~ ,;;,' " ',~r 0' ~~, ii', ",,,, <tii;'. «,' ~F ,.;,' ,'" ;,,,.1:1] "', '.," ", ,\: ',.J':;(
Acetone <20 <20 ND ND ND D!}!J~ ;.~~ ·,e
, ~,
Benzene <1.0 <1.0 ND ND ND tf"J !~~ ~-• ''& ;~~ I~ ". ':;'.: ',i; ,"'>fl,W!!. '", ,,'1li ",
Table 2D Detected Constituents and Comparison to Historic Values and Mill Site Monitoring Wells
~~~~~~~~~~~
Chloroform <1.0 <1.0 ND ND ND
Chloromethane <1.0 <1.0 ND ND ND
MEK <20 <20 ND ND ND
Methylene Chloride <1.0 <1.0 ND ND ND
Naphthalene <1.0 <1.0 ND ND ND
Tetrahydrofuran <1.0 <1.0 ND ND ND
Toluene <1.0 <1.0 ND ND ND
Xylenes <1.0 <1.0 ND ND ND
1 From Figure 3, Table 10 and Appendix B of the Revised Addendum, Background Groundwater Quality Report: New Wells
for Denison Mines (USA) Corp's White Mesa Mill Site, San Juan County, Utah, April 30, 2008, prepared by INTERA, Inc.
and Table 16 and Appendix D of the Revised Background Groundwater Quality Report: Existing Wells for Denison Mines
(USA) Corp. 's White Mesa Uranium Mill Site, San Juan County, Utah, October 2007, prepared by INTERA, Inc.
*Range of average historic values for On-Site Monitoring Wells as reported on April 30, 2008 (MW-l, MW-2, MW-3, MW-
3A, MW-4, MW-5, MW-ll, 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 and MW-32)
**In June 2012, the samples collected were inadvertently analyzed twice for Tin only. Both results are shown, and both data
packages have been included in this report.
INDEX OF TABS
Tab A Seeps and Springs Field Data Sheets and Photographic Documentation
Tab B Field Parameter Measurement Data
Tab C Survey Data and Contour Map
Tab D Analytical Laboratory Data
Tab E Quality Assurance and Data Validation Tables
E-l Holding Time Evaluation
E-2 Laboratory Receipt Temperature Check
E-3 Analytical Method Check
E-4 Reporting Limit Evaluation
E-5 Trip Blank Evaluation
E-6 QA/QC Evaluation for Sample Duplicates
E-7 Radiologies Counting Error
E-8 Laboratory Matrix QC Evaluation
Tab F CSV Transmittal
Tab G DRC Correspondence Regarding Annual Seeps and Springs Reports and Data Use
Tab A
Seeps and Springs Field Data Sheets and Photographic Documentation
Field Data Record-Seeps and Springs Sampling
Seep or Spring Location: Co±+ol\.wl200 5prl~
Date For Initial Sampling Visit:~/.2.0~ __ Time:_O_'_'"t_S _____ _
Sample Collected: Jil Yes 0 No
Date For Second Sampling Visit: ________ Time: ________ _
Sample Collected: 0 Yes 0 No
Date For Third Sampling Visit: ________ Time: _________ _
Sample Collected: 0 Yes 0 No
Sampling Personnel:
Weather Conditions at Time of Sampling:_S""""lN\;;;...;..;..:.(\-.;:.t?,:->r-' ___________ _
Estimated Seep or Spring Flow Rate: _._7.....,;;S __ 6-_· _p_~ ___________ _
Field Parameter Measurements:
-pH "'.01,
-Temperature (OC) --=.13I.'~.":::"~':"'« __ ----:-__ -_____ _
-Conductivity fjMHOC/cm _l..::.5;;....'=...;g~ _______ _
-Turbidity (NTU) (if measured).---.;~=3~."-,---______ _
-Redox Potential Eh (m V) (if measured) _'i...:.::l,;...;:;.;..' ____ _
Analytical Parameters/Sample Collection Method:
DYes oNo DYes o No 1!J
Nutrients DYes oNo DYes o No ftI
Other Non DYes o No DYes o No .,
Gross Alpha DYes o No DYes oNo 0
QC Samples Associated with this Location:
o Rinsate Blank
'fi Duplicate
Duplicate Sample Name: ~~lc. 51';tlj
0
0
0
lG
0
0
0
Notes: lwt;~«Al ____ ta _ $a~c J-b:r,JtL "'M1Mr~~~ OeM. tb;t eft $ t~. __ m = .... ~ .. d QTJS. Len: A.1ft ..,! .. ~"() . '~~~:.f"~-"'+-'!!!I;( :"""r'i~I...u.f,t!l . ---
0
0
0
Field Data Record-Seeps and Springs Sampling
Date For Initial Sampling Visit: , '~t>ll..b'~
Sample Collected: t$Yes 0 No
Date For Second Sampling Visit: ________ Time: ________ _
Sample Collected: 0 Yes 0 No
Date For Third Sampling Visit: ________ Time: _________ _
Sample Collected: 0 Yes 0 No
Sampling Personnel: :t:'M\crf ~",c;or De.n: I . P\~~ r
Weather Conditions at Time of sampling:-~~~~~".:...1+----________ _
Estimated Seep or Spring Flow Rate: --"--7z...o5 _____ , _____________ _
Field Parameter Measurements:
-pH i.O,
-Temperature (OC) __ ..... I.z:.'.:.... ::a..--.;:::8 _________ ~
-Conductivity (.tMHOC/cm _~I~,.r.tUIlPY-__ -------
-Turbidity (NTU) (if measured),==--, 2._:> ... ~OL.."'1~_. __ ~ __ ~~
-Redox Potential Eh (mV) (if measured) _S ...... ., ..",.1,...,-l~' ._,_~~~
Analytical Parameters/Sample Collection Method:
DYes oNo DYes 0 0
Nutrients DYes oNo DYes o No 0 0
Other Non DYes o No DYes oNo tt 0 0 0
Radiolo .
Gross Alpha o Yes oNo o Yes oNo 0 0 0
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name: ___________ _
Notes: ... ~ot' Cl>*t)n~ -¥~"_._ .. ~._w ____ ~
I ,
• _ ••••• ___ ::IIIW .. _ .......... '. • •• -••••
Field Data Record-Seeps and Springs Sampling
Date For Initial Sampling Visit: b /:4) I !26 12
Sample Collected: ~ Yes 0 No
Time: 1()J5
Date For Second Sampling Visit: ________ Time: ________ _
Sample Collected: 0 Yes 0 No
Date For Third Sampling Visit: _____ ~~_ Time: _________ _
Sample Collected: 0 Yes 0 No
Sampling Personnel:
Weather Conditions at Time of Sampling: SUl.(\(l~ t,;>;t~ 0 -I!Hi, ,"",j~J
Estimated Seep or Spring Flow Rate: _._iS~........::&=---· f>~M.~ ___________ _
Field Parameter Measurements:
-pH 7.57
-Temperature (OC) _..:::2..~Q~.3~'~ _________ _
-Conductivity flMHOC/cm .....I\~O~4c:():.......-________ _
-Turbidity (NTU) (if measured)_..:..:IO:::..,:,!..l..8l.--______ _
-Redox Potential Eh (mV) (if measured) --=-:J}.~q.;.;.~~ ___ _
Analytical Parameters/Sample Collection Method:
DYes DNo 0
Nutrients oNo DYes DNo 0
Other Non oNo DYes o No 0
Radiolo cs
Gross Alpha o No o Yes o No 0
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name: ___________ _
J
Field Data Record-Seeps and Springs Sampling
Date For Initial Sampling Visit:~~l~f2.,.,
Sample Collected: tc Yes 0 No
Time: 0 12.0
Date For Second Sampling Visit! __ -----Time:_~ ______ _
Sample Collected: 0 Yes 0 No
Date For Third Sampling Visit: _______ Time: _________ _
Sample Collected: 0 Yes D No
Sampling Personnel: -r;M«.JIJl;J...j • &0........ ?.ll'l<t" ,.000lkJcrs!!lt EM &oAk:.
Weather Conditions at Time of Sampling: C,lcAI"' __ w'31",u .some w;,.,4 ..... m'~_' _
Estimated Seep or Spring Flow Rate: ~I ___ 6r:...aJ>~M__=__~~====~~~~-~~
Field Parameter Measurements:
-pH ,.5'
-Temperature (Oe) ~rs~: ~ .. !..!i!"=",,,,-=_ ====='~~_~~~~ __ '
-Conductivity ~MHOC/cm 1~'7 =,~=====~~~= ~ Turbidity (NTU) (if measured)--EL ..... S~ _______ _
-Redox Potential Eh (m V) (if measured) ~I!,,;;~'::L' ~~~ _. _~ __ _
Analytical Parameters/Sample Collection Method:
So Yes DYes 0 0 0
Nutrients '" Yes DNo DYes o No ~ 0 0 D
Other Non qJ Yes oNo o Yes oNo IJ 0 0 0
Radiolo
Gross Alpha ~ Yes oNo DYes o No 0 .. 0 0
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name:
Field Data Record-Seeps and Springs Sampling
Seep or Spring Location: _--:W~~e.=..s:.....Jt~W~l&c.=' :::...:+_ec~_ ..... .5~&.c:.Je......q::p~ _______ _
-'D t F I "t" IS." V" "t-"1:l.O/2.0~ a e or nl la amp Ing lSI.. bL:. .. ' L .. n n
, ,(~:, Sample Collected: 0 Yes ttNa
Date For Second Sampling Visit: b / ~'1 / !2.,o~
Sample Collected: 0 Yes IX No
Time: 4&30
Time: l.x:sO
Date For Third Sampling Visit:~21!1.l ~ ,1.2 _~ Time: 'I 3:30~w.~_~,~~
Sample Collected: 0 Yes Ql No
Sampling Personnel:
Weather Conditions at Time of Sampling: _______________ _
Esti~ated Seep or Spring Flow Rate: ____ ~ ___________ _
l/~ . i/~' .'
Field Parameter Measurements:
-pH
-Temperature C;C) ______________ _
-Conductivity f,!MHOC/cm ___________ _
-Turbidity (NTU) (if nleasured) _________ _
-Redox Potential Eh (mV) (if nteasured) ______ _
Analytical Parameters/Sample Collection Method:
DYes DYes DNa
Nutrients DYes DNa DYes o No 0
Other Non DYes o No o Yes o No 0
Radiala
Gross Alpha DYes oNo DYes o No 0 0
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name:
0
0 0
0 0
0 0
Field Data Record-Seeps and Springs Sampling
Date For Initial Sampling Visit: '1~/f/JJ)f!L ..
Sample Collected: 0 Yes ,No
Date For Second Sampling Visit: ';/27 /~\~
Sample Collected: 0 Yes ~ No
Date For Third Sampling Visit: 71 'f I M i fJ...
Sample Collected: 0 Yes Q(No
Sampling Personnel:
Time: 1:30 0
Time: 12.00
Time: I 210
Weather Conditions at Time of Sampling: ______ ~ ________ _
Estimated Seep or Spring Flow Rate: ______________ ---
Field Parameter Measurements:
-pH
-Temperature (OC) ______________ _
-Conductivity f,tMHOC/cm ___________ _
-Turbidity (NTU) (if measured) _________ _
-Redox Potential Eh (mV) (if measured) ______ _
Analytical Parameters/Sample Collection Method:
VOCs DYes o No D Yes DNo 0 0
THF DYes DNo DYes DNo 0 0
Nutrients DYes o No D Yes oNo 0 0
Other Non DYes o No DYes DNo 0 0
Radiol s
Gross Alpha DYes oNo DYes oNo 0 0
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name:
Notes: '/flb/2.0 12 • ~ pc-l~ ~4U l ~~
b/Z7/~r2 --D.-~ "1LtjL:JbI~~ .o;¥
0 0
0 0
0 0
0 0
0 0
Field Data Record-Seeps and Springs Sampling
Seep or Spring Location:
Date For Initial Sampling Visit: b/2..ol~c, ...
Sample Collected: 0 Yes IJ No
Date For Second Sampling Visit: I;(;:rzl !2012..
Sample Collected: 0 Yes ~ No
Date For Third Sampling Visit: 7/g l • 4t
Sample Collected: 0 Yes ,r No
Sampling Personnel:
Time: !!'l"So
Time: )300
Time: , 1eo
Weather Conditions at Time of SampUng: ____ ~ __________ _
Estimated Seep or Spring Flow Rate: ________________ _
Field Parameter Measurements:
-pH
-Temperature (OC) ______________ _
-Conductivity J1MHOC/cm ___________ _
-Turbidity (NTU) (if measured) _________ _
-Redox Potential Eh (mV) (if measured) ______ _
Analytical Parameters/Sample Collection Method:
DYes oNo DYes oNo
DYes o No DYes oNo
Nutrients DYes o No o Yes oNo o o
Other Non DYes o No o Yes oNo o o
Radiolo
Gross Alpha DYes D No DYes oNo o o
QC Samples Associated with this Location:
o Rinsate Blank
o Duplicate
Duplicate Sample Name: ___________ _
Notes: &/2.0/2.01')... p SP"'~".)~ Jr~
G/a.7/(/.J!)J!:J-... D:j
o o
o o
o o
. ,~.
;;r.(,: .. "
~.. {..
·,; • r ,\l < ~~ .
.. ,
~,!t; (I
'&'~J'
TabB
Field Parameter Measurement Data
F' Id Ie parameters
Location , pH , Conductivity Turbidity' , Redox ' Temperature .
. pate June 2012 June 2012 June 2012 June 2012 June 2012
Entrance Spring 7.57 1040 10.8 292 20.36
Cottonwood Seep 7.06 1568 23.4 421 16.28
Back Spring
(Duplicate of
Cottonwood Spring) 7.06 1568 23.4 421 16.28
Ruin Spring 7.56 1367 1.3 276 15.86
Not Not
measured Not measured measured Not measured Not measured
Westwater Seep (dry) (dry) (dry) (dry) (dry)
TabC
Survey Data and Contour Map
Seeps and Springs Survey Locations
Mid-December 2009 Survey
Location Latitude (N) Longitude (W) Elevation
FROG POND 37°33'03.5358" 109°29'04.9552" 5589.56
CORRAL CANYON 37°33'07.1392" 109°29'12.3907" 5623.97
ENTRANCE SPRING 3 7°32'0 1.6487" 109°29'33.7005" 5559.71
CORRAL SPRINGS 37°29'37.9192" 109°29'35.8201 " 5383.35
RUIN SPRING 37°30'06.0448" 109°31'23.4300" 5380.03
COTTONWOOD 37°31 '21.7002" 109°32'14.7923" 5234.33
WESTWATER 37°31 '58.5020" 109°31'25.7345" 5468.23
Verification Survey July 2010
RUIN SPRING 37°30'06.0456" 109°31 '23 .4181 " 5380.01
COTTONWOOD 37°31 '21.6987" 109°32'14.7927" 5234.27
WESTWATER 37°31'58.5013" 109°31'25.7357" 5468.32
® estimated dry area (kriged Brushy Basin
surface> kriged water level surface)
M.W-S perched monitoring well showing
5503 elevation in feet amsl
TW4-12 temporary perched monitoring well
0 5583 showing elevation in feet amsl
TWN-10
0 5586 temporary perched nitrate monitoring
well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
Q 5593 elevation in feet amsl
TW4-27 temporary perched monitoring well
~ 5526 installed October, 2011 showing
elevation in feet amsl
RUIN SPRING
0 5380 seep or spring showing
elevation in feet amsl
HYDRO
GEO
CHEM, INC.
NOTE: MW-4, MW-26, TW4-4, TW4-19, and TW4-20 are pumping wells
KRIGED 3rd QUARTER, 2012 WATER LEVELS
DR-SERIES DATA NOT INCLUDED
WHITE MESA SITE
APPROVED DATE REFERENCE H:/718000/nov121
seeps_springs/UwI0912sp_nodr.srf
FIGURE
C-1
® estimated dry area (kriged Brushy Basin
surface> kriged water level surface)
M.W-5 perched monitoring well showing
5503 elevation in feet amsl
TW4-12 . . temporary perched monltonng well
0 5583 showing elevation in feet amsl
TWN-10 h d . .. A,5586 temporary perc e nitrate monltonng
V well showing elevation in feet amsl
PIEZ-1 perched piezometer showing
~ 5593 elevation in feet amsl
TW4-27 temporary perched monitoring well
~ 5526 installed October, 2011 showing
elevation in feet amsl
RUIN SPRING b 5380 seep or spring showing
elevation in feet amsl
HYDRO
GEO
CHEM, INC.
NOTE: MW-4, MW-26, TW4-4, TW4-19, and TW4-20 are pumping wells
KRIGED 3rd QUARTER, 2012 WATER LEVELS
WHITE MESA SITE
APPROVED DATE REFERENCE H :/718000/nov121
seeps _ springs/Uwl0912sp.srf
FIGURE
C-2
TabD
Analytical Laboratory Data
EN:RGY
LABORATORiES
www.energylab.com
Analytical ExCSJISfICB Sines 1952
Heli!na, MT 877-472 .. 0711 • Billings, MT 800-135-4489 • Gasper, WV 888-235-0515
~i"efte, WY ,866~686-7175 • Rapid Gfty, SI} 888-672-1225 • College Station, TX 888-690-2218
ANALYTICAL SUMMARY REPORT
July 27, 2012
Denison Mines USA Corp
6425 S Hwy 191
Blanding, UT 84511
Workorder No.: C12060931 Quote ID: C1640 -POC Wells
Project Name: Seeps and Springs 2012
Energy Laboratories, Inc. Casper WY received the following 6 samples for Denison Mines USA Corp on 6/22/2012 for analysis.
Sample ID Client Sample ID Collect Date Receive Date Matrix Test
C12060931-001 Entrance Seep 06/20/12 10:15 06/22/12 Aqueous Alkalinity
QA Calculations
Chloride
Fluoride
Metals by ICP, Dissolved
Metals by ICP-MS, Dissolved
Nitrogen, Ammonia
Nitrogen, Nitrate + Nitrite
pH
Gross Alpha minus Rn222 and
Uranium
Solids, Total Dissolved
Solids, Total Dissolved -Calculated
Sulfate
SW8260B VOCs, Standard List
C 12060931-002 Ruin Spring 06/20/12 9:20 06/22/12 Aqueous Same As Above
C12060931-003 Cottonwood Spring 06/20/127:45 06/22/12 Aqueous Same As Above
C12060931-004 Back Spring 06/20/127:45 06/22/12 Aqueous Same As Above
C 1 2060931-005 Trip Blank 6746 06/20/120:00 06/22/12 Aqueous SW8260B VOCs, Standard List
---------------~*---------------
C 12060931-006 Temp Blank 06/21/120:00 06/22/12 Aqueous Temperature
The results as reported relate only to the item(s) submitted for testing. The analyses presented in this report were
performed at Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601, unless otherwise noted.
Radiochemistry analyses were performed at Energy Laboratories, Inc., 2325 Kerzell Lane, Casper, WY 82601,
unless otherwise noted. Any exceptions or problems with the analyses are noted in the Laboratory Analytical
Report, the QA/QC Summary Report, or the Case Narrative.
If you have any questions regarding these test results, please call.
Report Approved By:
C3¥~ £l uJtJl~
Reporting Supervisor
Digitally signed by
Stephanie Waldrop
Date: 2012.07.27 15:42:16 ·06:00
Page 1 of 33
www.energylab.com
Analytical ExcsllsncB SiIlCB 1952
Heiena, MT 877·412-071 t • Billings, MT 800-735-4489 • Casper, WV 888-235-0515
-Gillette, WY :866-686-7175 • Rapid City, SO 888-672-1225 • College Station, IX 888-690-2218
CLIENT: Denison Mines USA Corp
Project: Seeps and Springs 2012 Report Date: 07/27/12
Sample Delivery Group: C12060931 CASE NARRATIVE
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 40C (±2OC)
Temperature of samples received may not be considered properly preserved by accepted standards. Samples that are
hand delivered immediately after collection shall be considered acceptable if there is evidence that the chilling process has
begun.
GROSS ALPHA ANALYSIS
Method 900.0 for gross alpha and gross beta is intended as a drinking water method for low TDS waters. Data provided by
this method for non potable waters should be viewed as inconsistent.
RADON IN AIR ANALYSIS
The desired exposure time is 48 hours (2 days). The time delay in returning the canister to the laboratory for processing
should be as short as possible to avoid excessive decay. Maximum recommended delay between end of exposure to
beginning of counting should not exceed 8 days.
SOIL/SOLID SAMPLES
All samples reported on an as received basis unless otherwise indicated.
ATRAZINE, SIMAZINE AND PCB ANALYSIS
Data for PCBs, Atrazine and Simazine are reported from EPA 525.2. PCB data reported by ELI reflects the results for seven
individual Aroclors. When the results for all seven are NO (not detected), the sample meets EPA compliance criteria for
PCB monitoring.
SUBCONTRACTING ANALYSIS
Subcontracting of sample analyses to an outside laboratory may be required. If so, ENERGY LABORATORIES will utilize its
branch laboratories or qualified contract laboratories for this service. Any such laboratories will be indicated within the
Laboratory Analytical Report.
BRANCH LABORATORY LOCATIONS
eli-b -Energy Laboratories, Inc. -Billings, MT
eli-g -Energy Laboratories, Inc. -Gillette, WY
eli-h -Energy Laboratories, Inc. -Helena, MT
eli-r -Energy Laboratories, Inc. -Rapid City, SO
eli-t -Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
USEPA: WY00002, Radiochemical WY00937; FL-DOH NELAC: E87641 , Radiochemical E871 017; California: 02118CA;
Oregon: WY200001 , Radiochemical WY200002; Utah: WY00002; Virginia: 00057; Washington: C836
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER,WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELI's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical ExcsHBflCB Sines '952
Helena, MT 877-472-0711 • Billings. MT 800-735-4489 • Casper, WY 888-235-0515
:GiII~fte, WY 8~_& .. 6B6-7115 • Rapid City, SD 888-672-1225 • College Station, IX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client:
Project:
Lab 10 :
Denison Mines USA Corp
Seeps and Springs 2012
C12060931-001
Client Sample 10: Entrance Seep
Analyses
MAJOR IONS
Carbonate as C03
Bicarbonate as HC03
Calcium
Chloride
Fluoride
Magnesium
Nitrogen, Ammonia as N
Nitrogen, Nitrate+Nitrite as N
Potassium
Sodium
Sulfate
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS @ 180 C
METALS -DISSOL VEO
Arsenic
Beryllium
Cadmium
Chromium
Cobalt
Copper
Iron
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Uranium
Vanadium
Zinc
RADIONUCLIDES -DISSOLVED
Gross Alpha minus Rn & U
Gross Alpha minus Rn & U Precision (±)
Gross Alpha minus Rn & U MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
ND
298
105
78
0.64
32.7
ND
2.8
2.0
77.4
171
660
ND
ND
ND
ND
ND
ND
34
ND
ND
ND
ND
ND
13.2
ND
ND
21 .1
ND
ND
0.5
0.4
0.5
Units
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
pCi/L
pCi/L
pC ilL
MDC - Minimum detectable concentration
Report Date: 07/27/12
Collection Date: 06/20/12 10:15
OateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date / By
D
A2320 B 06/22/12 17:29 / jba
1 A2320 B 06/22/12 17:291 jba
0.5 E200.7 07/06/1220:15 /sf
A4500-CI B 06/27/12 14:191 wc
0.10 A4500-F C 06/25/12 10:09 1 jba
0.5 E200.7 07/06/12 20:151 sf
0.05 A4500-NH3 G 06/29/12 17:351 Ijl
0.1 E353.2 06/27/12 15:10 /lr
0.5 E200.7 07/06/12 20:151 sf
0.5 E200.7 07/06/1220:151 sf
5 A4500-S04 E 06/26/12 11 :23 1 Ir
10 A2540 C 06/25/12 13 :57 1 ab
5.0 E200.8 07/11/12 19:25 1 cp
0.50 E200.8 07/11/1219:25/cp
0.50 E200.8 07/11/1219:25 1 cp
25 E200.8 07/11/1219:25/cp
10 E200.8 07/11/1219:25/cp
10 E200.8 07/11 /1219:25 /cp
30 E200.7 07/06/1220:15 1 sf
1.0 E200.8 07/11/1219:25/cp
10 E200.8 07/11/1219:25/cp
0.50 E200.8 07/11/1219:25 /cp
10 E200.8 07/11 /1219:25 /cp
20 E200.8 07/11/1219:25/cp
5.0 E200.8 07/11/1219:25 /cp
10 E200.8 07/11/1219:25 /cp
0.50 E200.8 07/11/1219:25/cp
0.30 E200.8 07/11/1219:25/cp
15 E200.8 07/11/1219:25/cp
10 E200.8 07/11/1219:25 /cp
E900.1 07/04/12 10:04 /lbb
E900.1 07/04/12 10:041 Ibb
E900.1 07/04/12 10:04 /lbb
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 3 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical UeslJBflCB Sines '952
Helena, MT 877-412-071 f • Billings, MT 800-735-4489 " Casper, WY 888-235-0515
_~ille~~, WY 866-~86-7115 • Rapid City, S[) 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
LablD: C12060931-001
Client Sample ID: Entrance Seep
Analyses
DATA QUALITY
AlC Balance (± 5)
Anions
Cations
Solids, Total Dissolved Calculated
TDS Balance (O.BO -1.20)
VOLATILE ORGANIC COMPOUNDS
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
Methyl ethyl ketone
Methylene chloride
Naphthalene
Toluene
Xylenes, Total
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
2.11
10.9
11.3
650
1.02
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
126
112
146
114
Units
0/0
meq/L
meq/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 07/27/12
Collection Date: 06/20/12 10:15
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date 1 By
A1030 E 07/27/12 10:361 kbh
A1030 E 07127/12 10:361 kbh
A1030 E 07127/12 10:361 kbh
A1030 E 07/27/12 10:361 kbh
A1030 E 07/27/1210:361 kbh
20 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:32 1 jlr
20 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16:321 jlr
1.0 SWB260B 06/29/12 16 :32 1 jlr
S ' BO-120 SWB260B 06/29/12 16:321 jlr
70-130 SWB260B 06/29/12 16 :32 1 jlr
S BO-120 SWB260B 06/29/12 16:321 jlr
BO-120 SWB260B 06/29/12 16:321 jlr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 33
EN:RGY
LABORATORIES
www.energylab.com
AnalytIcal ExcsHBflCB Sines 7952
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
~iUette, 'Iff nS .. 686-1175 • Rapid Cfty, SD 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Collection Date: 06/20/1209:20
Lab lD: C 12060931-002 DateReceived: 06/22/12
Client Sample ID: Ruin Spring Matrix: Aqueous
MCL!
Analyses Result Units Qualifier Rl QCl Method Analysis Date I By
MAJOR IONS
Carbonate as C03 ND mg/l A2320 B 06/22/12 17:37 1 jba
Bicarbonate as HC03 237 mg/L A2320 B 06/22/12 17:37 1 jba
Calcium 147 mg/L 0.5 E200.7 07106/1218:54/sf
Chloride 28 mg/L 1 A4500-CI B 06/27/12 13:08 1 wc
Fluoride 0.52 mg/L 0.10 A4500-F C 06/25/12 10:121 jba
Magnesium 31 .9 mg/L 0.5 E200.7 07106/1218:54/sf
Nitrogen, Ammonia as N ND mg/L 0.05 A4500-NH3 G 06/29/12 16:431 Ijl
Nitrogen, Nitrate+Nitrite as N 1.6 mg/L 0.1 E353.2 06/27/12 15:131 Ir
Potassium 3.5 mg/L 0.5 E200.7 07106/1218:54/sf
Sodium 115 mg/L 0.5 E200.7 07106/1218:54/sf
Sulfate 464 mg/L D 10 A4500-S04 E 06/26/12 11 :26 I Ir
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS @ 180 C 1000 mg/L 10 A2540 C 06/25/12 13 :58 1 ab
METALS -DISSOLVED
Arsenic ND ug/L 5.0 E200.8 07/11 /1219:29/cp
Beryllium ND ug/L 0.50 E200.8 07/11/1219:29/cp
Cadmium ND ug/L 0.50 E200.8 07/11 /1219:29/cp
Chromium ND ug/L 25 E200.8 07/11/1219:29/cp
Cobalt ND ug/L 10 E200.8 07/11/1219:29/cp
Copper ND ug/L 10 E200.8 07/1 1/1219:29/cp
Iron ND ug/L 30 E200.7 07106/12 20 :27 1 sf
Lead ND ug/L 1.0 E200.8 07/11/1219:291 cp
Manganese ND ug/L 10 E200.8 07/11/1219:29/cp
Mercury ND ug/L 0.50 E200.8 07/11/1219:29/cp
Molybdenum 16 ug/L 10 E200.8 07/11/1219:29/cp
Nickel ND ug/L 20 E200.8 07/11/1219:29/cp
Selenium 10.8 ug/L 5.0 E200.8 07/11 /1219:29/cp
Silver ND ug/L 10 E200.8 07/11/12 19:291 cp
Thallium ND ug/L 0.50 E200.8 07/11 /12 19:291 cp
Uranium 8.68 ug/L 0.30 E200.8 07/11/1219:29/cp
Vanadium ND ug/L 15 E200.8 07/11/12 19:291 cp
Zinc ND ug/L 10 E200.8 07/11/12 19:291 cp
RADIONUCLIDES -DISSOLVED
Gross Alpha minus Rn & U -0.09 pC ilL U E900.1 07104/12 10:041 Ibb
Gross Alpha minus Rn & U Precision (±) 0.3 pC ilL E900.1 07104/12 10:041 Ibb
Gross Alpha minus Rn & U MDC 0.5 pC ilL E900.1 07104/12 10:04 /lbb
-----------------------------------------------------_.
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 5 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical ExesllBflCB Sines 1952
Hel~na, MT 877-472-:-071 t • Billings, MT 800-735-4489 -Casper, WY 888-235-0515
,.mil~~Ei, Wy .&.6.;&86-7n~ • Rapid City, SO 888-&12-1225 • College Station, lX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client:
Project:
Lab 10:
Denison Mines USA Corp
Seeps and Springs 2012
C 12060931-002
Client Sample 10: Ruin Spring
Analyses
DATA QUALITY
AlC Balance (± 5)
Anions
Cations
Solids, Total Dissolved Calculated
TOS Balance (0.80 -1.20)
VOLATILE ORGANIC COMPOUNDS
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
Methyl ethyl ketone
Methylene chloride
Naphthalene
Toluene
Xylenes, Total
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
2.03
14.5
15.1
930
1.07
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
122
115
140
110
Units
%
meq/l
meq/l
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 07/27/12
Collection Date: 06/20/1209:20
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date 1 By
A1030 E 07/27/12 10:381 kbh
A1030 E 07/27/1210:381 kbh
A1030 E 07/27/1210:38/kbh
A1030 E 07/27/1210:381 kbh
A1030 E 07/27/12 10:381 kbh
20 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
20 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
1.0 SW8260B 06/29/12 17:07 1 jlr
S 80-120 SW8260B 06/29/12 17:07 1 jlr
70-130 SW8260B 06/29/12 17 :07 1 jlr
S 80-120 SW8260B 06/29/12 17:07 1 jlr
80-120 SW8260B 06/29/12 17:07 1 jlr
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 6 of 33
EI\ERGY
LABORATORIES
www.energylab.com
Analytical ExCSU8I1CB Sines 7952
Helena, MT 877-472-071 f • Billings. MT 800-735-4489 • Casper, WY 888-235-0515
~illefte, WY 866 .. 686-7175 • Rapid City, SO 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Lab 10: C 12060931-003
Client Sample 10: Cottonwood Spring
Analyses
MAJOR IONS
Carbonate as C03
Bicarbonate as HC03
Calcium
Chloride
Fluoride
Magnesium
Nitrogen, Ammonia as N
Nitrogen, Nitrate+Nitrite as N
Potassium
Sodium
Sulfate
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS @ 180 C
METALS -DISSOLVED
Arsenic
Beryllium
Cadmium
Chromium
Cobalt
Copper
Iron
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Uranium
Vanadium
Zinc
RADIONUCLIDES -DISSOLVED
Gross Alpha minus Rn & U
Gross Alpha minus Rn & U Precision (±)
Gross Alpha minus Rn & U MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
ND
326
101
149
0.38
27.7
ND
ND
6.2
247
356
1040
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
8.17
ND
ND
-0.2
0.2
0.5
Units
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
pCi/L
pCi/L
pCi/L
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Report Date: 07/27/12
Collection Date: 06/20/12 07:45
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date 1 By
D
U
A2320 B 06/22/12 17:441 jba
1 A2320 B 06/22/12 17:441 jba
0.5 E200.7 07106/1220:31 1 sf
A4500-CI B 06/27/1213:18/wc
0.10 A4500-F C 06/25/12 10:161 jba
0.5 E200.7 07106/1220:31 1 sf
0.05 A4500-NH3 G 06/29/12 16:491 Ijl
0.1 E353.2 06/27/1215:15/1r
0.5 E200.7 07106/1220:31 1 sf
0.5 E200.7 07106/12 20:31 1 sf
10 A4500-S04 E 06/26/12 11 :27 1 Ir
10 A2540 C 06/25/12 13:581 ab
5.0 E200.8 07/11/1219:52/cp
0.50 E200.8 07/13/12 07:20 1 cp
0.50 E200.8 07/11/1219:521 cp
25 E200.8 07/11/1219:52/cp
10 E200.8 07/11/1219:521 cp
10 E200.8 07/11/1219:521 cp
30 E200.7 07106/12 20:31 1 sf
1.0 E200.8 07/11/1219:521 cp
10 E200.8 07/11/12 19:521 cp
0.50 E200.8 07/11/1219:52/cp
10 E200.8 07/11/12 19:521 cp
20 E200.8 07/11/1219:52/cp
5.0 E200.8 07/11/1219:52/cp
10 E200.8 07/11/12 19:521 cp
0.50 E200.8 07/11/1219:52/cp
0.30 E200.8 07/11/1219:52/cp
15 E200.8 07/11/12 19:521 cp
10 E200.8 07/11/12 19:521 cp
E900.1 07104/12 10:041 Ibb
E900.1 07104/12 10:041 Ibb
E900.1 07104/12 10:041 Ibb
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 7 of 33
EN:RGY
LABORATORiES
www.energylab.com
Analytical ExcsHBflCB Sines 7952
Helena, MT 877~472-071 t -Billings, MT 808-735-4489 • Casper, WV 888-235-0515
'~iII~fl:e, WY86l'G86-7175 • Rapid City, SD 888-672-1225 • College Station, lX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Lab 10: C 12060931-003
Client Sample 10: Cottonwood Spring
Analyses
OAT A QUALITY
AlC Balance (± 5)
Anions
Cations
Solids, Total Dissolved Calculated
TOS Balance (0.80 -1.20)
VOLATILE ORGANIC COMPOUNDS
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
Methyl ethyl ketone
Methylene chloride
Naphthalene
Toluene
Xylenes, Total
Surr: 1 ,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
3.60
17.0
18.2
1100
0.960
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
122
105
138
113
Units
%
meq/L
meq/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 07/27/12
Collection Date: 06/20/12 07:45
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date / By
A1030 E 07/27/1210:38/ kbh
A1030 E 07127/12 10:381 kbh
A1030 E 07/27/1210:381 kbh
A1030 E 07/27/1210:38 / kbh
A1030 E 07/27/1210:381 kbh
20 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 / jlr
20 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
1.0 SW8260B 06/29/12 20:01 1 jlr
S 80-120 SW8260B 06/29/1220:01 1 jlr
70-130 SW8260B 06/29/12 20:01 1 jlr
S 80-120 SW8260B 06/29/12 20:01 1 jlr
80-120 SW8260B 06/29/12 20:01 1 jlr
--------------------
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 8 of 33
EN:RGY
LABORAT ORIES
www.energylab.com
Analytical Excs.IJBllCB SiIlCB 1952
Helena, MT 877-412-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, 'NY 866-686-7115 • Rapid City, Sf} 888-672-1225 • College Station, IX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Lab 10: C 1 2060931-004
Client Sample 10: Back Spring
Analyses
MAJOR IONS
Carbonate as C03
Bicarbonate as HC03
Calcium
Chloride
Fluoride
Magnesium
Nitrogen, Ammonia as N
Nitrogen, Nitrate+Nitrite as N
Potassium
Sodium
Sulfate
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS @ 180 C
METALS -DISSOLVED
Arsenic
Beryllium
Cadmium
Chromium
Cobalt
Copper
Iron
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Uranium
Vanadium
Zinc
RADIONUCLIDES -DISSOLVED
Gross Alpha minus Rn & U
Gross Alpha minus Rn & U Precision (±)
Gross Alpha minus Rn & U MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
ND
326
93.8
121
0.38
25.5
ND
ND
6.2
223
366
1040
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
8.56
ND
ND
0.07
0.3
0.5
Units
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
pCi/L
pC ilL
pC ilL
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Report Date: 07/27/12
Collection Date: 06/20/12 07:45
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier RL QCL Method Analysis Date 1 By
D
U
A2320 B 06/22/12 17:531 jba
1 A2320 B 06/22/1217:531 jba
0.5 E200.7 07/06/1219:021 sf
A4500-CI B 06/27/1213:25/wc
0.10 A4500-F C 06/25/12 10:191 jba
0.5 E200.7 07/06/1219:021 sf
0.05 A4500-NH3 G 06/29/12 16:51 1 Ijl
0.1 E353.2 06/27/12 15:181 Ir
0.5 E200.7 07/06/1220:351 sf
0.5 E200.7 07/06/12 19:02 1 sf
10 A4500-S04 E 06/26/12 11 :35 1 Ir
10 A2540 C 06/25/12 13:58 1 ab
5.0 E200.8 07/11/12 19:571 cp
0.50 E200.8 07/13/1207:251 cp
0.50 E200.8 07/11/1219:57/cp
25 E200.8 07/11/12 19:571 cp
10 E200.8 07/11/1219:571 cp
10 E200.8 07/11/1219:571 cp
30 E200.7 07/06/1220:351 sf
1.0 E200.8 07/11/1219:571 cp
10 E200.8 07/11/12 19:571 cp
0.50 E200.8 07/11/1219:57/cp
10 E200.8 07/11/1219:571 cp
20 E200.8 07/11/1219:571 cp
5.0 E200.8 07/11/12 19:571 cp
10 E200.8 07/11/1219:571 cp
0.50 E200.8 07/11/1219:571 cp
0.30 E200.8 07/11/1219:571 cp
15 E200.8 07/11/1219:571 cp
10 E200.8 07/11/1219:571 cp
E900.1 07/04/12 10:041 Ibb
E900.1 07/04/1210:04/1bb
E900.1 07/04/1210:04/1bb
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 9 of 33
EI\ERGY
LABORATORIES
www.energyiab.com
Analytical ExCSUBflCB Sines 1952
Helena, MT 877 ·472-0711 -Billings. MT 800-735-4489 • Casper, WY 888-235-0515
Jli11efte, WY~6&:"686-7175 • Rapid City, SD 888-672-1225 • College Station, IX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Lab 10: C 12060931-004
Client Sample 10 : Back Spring
Analyses
DATA QUALITY
NC Balance (± 5)
Anions
Cations
Solids, Total Dissolved Calculated
TDS Balance (O.BO -1.20)
VOLATILE ORGANIC COMPOUNDS
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
Methyl ethyl ketone
Methylene chloride
Naphthalene
Toluene
Xylenes, Total
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-dB
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result
0.740
16.4
16.6
1000
1.01
ND
ND
ND
ND
ND
ND
ND
ND
ND
ND
120
112
133
105
Units
%
meq/L
meq/L
mg/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 07/27/12
Collection Date: 06/20/12 07:45
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date 1 By
A1030 E 07/27/1214:491 sdw
A1030 E 07/27/1214:491 sdw
A1030 E 07/27/1214:491 sdw
A1030 E 07/27/1214:491 sdw
A1030 E 07/27/1214:491 sdw
20 SWB260B 07102/12 16:051 jlr
1.0 SWB260B 07102/1216:051 jlr
1.0 SWB260B 07102/12 16:051 jlr
1.0 SWB260B 07102/12 16:051 jlr
1.0 SWB260B 07102/12 16:051 jlr
20 SWB260B 07102/12 16:051 jlr
1.0 SWB260B 07102/1216:051 jlr
1.0 SWB260B 07102/12 16:051 jlr
1.0 SWB260B 07102/1216:051 jlr
1.0 SWB260B 07102/12 16:05 1 jlr
BO-120 SWB260B 07102/12 16:051 jlr
70-130 SWB260B 07102/1216:051 jlr
S BO-120 SWB260B 07102/1216:051 jlr
BO-120 SWB260B 07102/12 16:051 jlr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 33
EN:RGY
LABORATORIES
www.energylab.com (
Analytical ExcsDBflCB Sines 1852 J.' Helena, PM B77~472~0711 • Billings, MT 800-735-4489 • Casper, WV 888~235-0515
.§illett.~, WY 866 .. 686-7175 • Rapid City, SO 888-672-1225 • College Station, IX 888-690-2218
LABORATORY ANAL VTICAL REPORT
Prepared by Casper, WY Branch
Client:
Project:
Lab 10:
Denison Mines USA Corp
Seeps and Springs 2012
C 12060931-005
Client Sample 10: Trip Blank 6746
Analyses Result
VOLATILE ORGANIC COMPOUNDS
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
Methyl ethyl ketone
Methylene chloride
Naphthalene
Toluene
Xylenes, Total
Surr: 1,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
NO
NO
NO
NO
NO
NO
NO
NO
NO
NO
121
113
138
117
Units
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
ug/L
%REC
%REC
%REC
%REC
S -Spike recovery outside of advisory limits.
Report Date: 07/27/12
Collection Date: 06/20/12
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
Qualifier Rl QCl Method Analysis Date 1 By
20 SW8260B 06/29/1218:161 jlr
1.0 SW8260B 06/29/12 18:161 jlr
1.0 SW8260B 06/29/1218:161 jlr
1.0 SW8260B 06/29/1218:161 jlr
1.0 SW8260B 06/29/1218:16/jlr
20 SW8260B 06/29/12 18: 16 1 jlr
1.0 SW8260B 06/29/1218:161 jlr
1.0 SW8260B 06/29/1218:16/jlr
1.0 SW8260B 06/29/1218:16/jlr
1.0 SW8260B 06/29/1218:16/jlr
S 80-120 SW8260B 06/29/1218:16/jlr
70-130 SW8260B 06/29/1218:16/jlr
S 80-120 SW8260B 06/29/12 18:161 jlr
80-120 SW8260B 06/29/1218:161 jlr
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 11 of 33
EI\ERGY
LABORATORIES
www.energylab.com
Analytical ExCBDBllCB SiIlCB ,g52
Helena, MT 871-472-071 t • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
. 9illef.!:e, 'NY 866 .. 686-7175 • Rapid City, SI} 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client:
Project:
LablD:
Denison Mines USA Corp
Seeps and Springs 2012
C 12060931-006
Client Sample ID: Temp Blank
Analyses Result Units
PHYSICAL PROPERTIES
Temperature
Report
Definitions:
Rl -Analyte reporting limit.
QCl -Quality control limit.
2.2
Qualifier Rl
Report Date: 07/27/12
Collection Date: 06/21/12
DateReceived: 06/22/12
Matrix: Aqueous
MCL!
QCl Method Analysis Date / By
E170.1 06/22/1209:501 kbh
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 12 of 33
EI\ERGY
LABORATORIES
www.energylab.com
Analytical ExcsJlencB Sines "52
Hel~na, MT 871·472-0111 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
~iII~tte, WV86&-686-7175 • Rapid City, 51} 888-672-1225 • College Station, IX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client:
Project:
Denison Mines USA Corp
Seeps and Springs 2012
Lab 10: C12060931-001
Client Sample 10: Entrance Seep
Analyses
PHYSICAL PROPERTIES
pH
Lab 10: C 1 2060931-002
Client Sample 10: Ruin Spring
Analyses
PHYSICAL PROPERTIES
pH
Lab 10: C 12060931-003
Client Sample 10: Cottonwood Spring
Analyses
PHYSICAL PROPERTIES
pH
Lab 10: C 12060931-004
Client Sample 10: Back Spring
Analyses
PHYSICAL PROPERTIES
pH
Report Rl -Analyte reporting limit.
Definitions: QCl -Quality control limit.
Result Units
7.50 s.U.
Result Units
7.53 s.U.
Result Units
7.53 s.U.
Result Units
7.58 s.U.
H -Analysis performed past recommended holding time.
Qualifiers Rl
H 0.01
Qualifiers Rl
H 0.01
Qualifiers Rl
H 0.01
Qualifiers Rl
H 0.01
MeL!
Report Date: 07/27/12
Collection Date: 06/20/12 10:15
DateReceived: 06/22/12
Matrix: Aqueous
Qel Method Analysis Date / By
MeL!
A4500-H B 06/22/12 13:04/ ab
Collection Date: 06/20/1209:20
DateReceived: 06/22/12
Matrix: Aqueous
Qel Method Analysis Date / By
MeL!
A4500-H B 06/22/12 13:06/ ab
Collection Date: 06/20/1207:45
DateReceived: 06/22/12
Matrix: Aqueous
Qel Method Analysis Date / By
MeL!
A4500-H B 06/22/12 13 :09 / ab
Collection Date: 06/20/1207:45
DateReceived: 06/22/12
Matrix: Aqueous
Qel Method Analysis Date / By
A4500-H B 06/22/12 13:12/ ab
MCl -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 13 of 33
EN:RGY
LABORATORIES
www.energylab.com
Ana/ylil;al Exesll8flcfI Sines 1152
Hele~af MTB7l·472-0711 • Billings, MT 800-735-4489 . Casper, WY 888-235-0515
jill~tie, WY e~6-686-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: A2320 B
Sample 10: MBLK
Alkalinity, Total as CaC03
Carbonate as C03
Bicarbonate as HC03
3 Method Blank
ND mg/L
ND mg/L
1.62 mg/L
Sample 10: LCS-6677 Laboratory Control Sample
Alkalinity, Total as CaC03 201 mg/L
Sample 10: C12060935-003AOUP 3 Sample Duplicate
Alkalinity, Total as CaC03 329 mg/L
Carbonate as C03 ND mg/L
Bicarbonate as HC03
Sample 10: C12060935-005AMS
Alkalinity, Total as CaC03
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
401 mg/L
Sample Matrix Spike
299 mg/L
RL
5.0
1.0
1.0
5.0
5.0
5.0
5.0
5.0
Report Date: 07/27/12
Work Order: C12060931
%REC Low Limit High Limit RPO RPOLimit Qual
Batch: R1611 03
Run: MANTECH_120622A 06/22/12 14:55
Run: MANTECH_120622A 06/22/1215:11
101 90 110
Run: MANTECH 120622A 06/22/12 20:05 -
0.7 10
10
0.7 10
Run: MANTECH_120622A 06/22/12 20:29
103 80 120
ND -Not detected at the reporting limit.
Page 14 of 33
EN:RGY
LABORATORIES
www.energyJab.com
Analytical ExC8UsnCB Sines '952
Helena, MT 877-472-071 t • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
_~,'~iJle~e, WY 86& .. 686-7175 · Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client : Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result
Method: A2540 C
Sample 10: MB-1_120625A
Solids, Total Dissolved TDS @ 180 C
Method Blank
ND
Units
mg/L
Sample 10: LCS-2_120625A Laboratory Control Sample
Solids, Total Dissolved TDS @ 180 C 1100 mg/L
Sample 10: C12060946-002A MS Sample Matrix Spike
Solids, Total Dissolved TDS @ 180 C 1690 mg/L
Sample 10: C12060983-001 A OUP Sample Duplicate
Solids, Total Dissolved TDS @ 180 C 450 mg/L
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Report Date:
Work Order:
RL %REC Low Limit High Limit RPO
Run: BAL-1_120625A
10
Run: BAL-1_120625A
10 99 90 110
Run: BAL-1 120625A
10 105 90 110
Run: BAL-1 120625A
10 0.4
ND -Not detected at the reporting limit.
07/27/12
C12060931
RPOLimit Qual
Batch: TDS120625A
06/25/12 12:04
06/25/12 12:04
06/25/12 14:00
06/25/12 14:03
5
Page 15 of 33
EN:RGY www.energylab.com Helena, MTB71-472-0111 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
. _9.iII~fta! VjY 866 .. 6B6~ 7115 • Rapid City, SO 888-672-1225 • College Station, TX 888-690-2218 LABORATORIES Analytical ExC8/Jsnc, Sines 1952
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: A4500-CI B
Sample 10: MBLK9-120627
Chloride
Sample 10: LCS35-120627
Chloride
Sample 10: C12060931-001AMS
Chloride
Sample 10: C12060931 -001AMSO
Chloride
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Method Blank
NO mg/L
Laboratory Control Sample
3690 mg/L
Sample Matrix Spike
248 mg/L
Sample Matrix Spike Duplicate
248 mg/L
Report Date: 07/27/12
Work Order: C 12060931
RL %REC Low Limit High Limit RPO RPOLimit Qual
Batch: 120627-CL-TTR-W
Run: TITRATION_120627A 06/27/1211:19
1.0
Run: TITRATION_120627A 06/27/1213:57
1.0 104 90 110
Run: TITRATION 120627A 06/27/1214:34 -
1.0 96 90 110
Run: TITRATION 120627A 06/27/12 14:35 -
1.0 96 90 110 0.0 10
NO -Not detected at the reporting limit.
Page 16 of 33
EI'I:RGY www.energylab.com Helen,a, Mt 877-472-0711 • Billings, MT 800-735-4489 • Casper, W'f 888-235-0515
, _ l ille,tte, WY866-.86-7175 • Rapid Cfty, SD 888-672-1225 • College Station, TX 888-690-2218 LABORATORIES Anatylical ExcslJsnCB Sines 1952
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: A4S00-F C
Sample 10: MBLK
Fluoride
Sample 10: LCS-6892
Fluoride
Sample 10: C12060917-00SAMS
Fluoride
Sample 10: C12060917-00SAMSO
Fluoride
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Method Blank
ND mg/L
Laboratory Control Sample
2.00 mg/L
Sample Matrix Spike
2.20 mg/L
Sample Matrix Spike Duplicate
2.20 mg/L
Report Date:
Work Order:
RL %REC Low Limit High Limit RPO
Run: MANTECH_120625A
0.10
Run: MANTECH_120625A
0.10 100 90 110
Run: MANTECH_120625A
0.10 101 80 120
Run: MANTECH_120625A
0.10 101 80 120 0.0
ND -Not detected at the reporting limit.
07/27/12
C12060931
RPOLimit Qual
Batch: R161131
06/25/1209:31
06/25/12 09:34
06/25/1209:42
06/25/12 09:45
10
Page 17 of 33
I
EN:RGY www.energylab.com Helena, MT 877-472-011 t . Billings, MT 800-735-4489 • Casper, WY 888-235-0515
~_~~iil~t;te, WY 866-586-7175 • Rapid Cfty, SD 888-672-1225 • Col/ege Station, TX 888-690-2218 LABORATORIES Analytical ExCSUIlflCB Sines '952
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte
Method: A4S00-H B
Sample 10: pH 6.86
pH
Sample 10: pH 6.86
pH
Method: A4S00-H B
Count
QA/QC Summary Report
Prepared by Casper, WY Branch
Report Date: 07/27/12
Work Order: C12060931
Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Initial Calibration Verification Standard
6.84 s.u. 0.010 100
Initial Calibration Verification Standard
6.84 s.u. 0.010 100
98
98
Analytical Run: PHSC_101-C_120622A
06/22/1208:56
102
06/22/12 11 :41
102
Sample 10: C12060894-00SAOUP
pH
Sample Duplicate
Batch: R161 051
06/22/1209:44
3 8.54 s.u. 0.010 0.0
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 18 of 33
EN:RGY www.energylab.com Helena, MT877 .. 472-D711 • Billings, MT 800-735-4489 . Casper, WV 888-235-0515
< :~il!~tte, Wy8G.S-GB6-7l75 • Rapid Cfty, SD 888-672-1225 • College Station, lX 888-690-2218 LABORATORIES Analytical ExcsDsncB Sinc8 1152
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Work Order: C12060931
Analyte Count Result Units RL O/OREC Low Limit High Limit RPO RPOLimit Qual
Method: A4S00-NH3 G Batch: R161381
Sample 10: MBLK-1 Method Blank Run: TECHNICON~120629A 06/29/12 15:11
Nitrogen, Ammonia as N NO mg/L 0.050
Sample 10: LCS-2 Laboratory Control Sample Run: TECHNICON_120629A 06/29/12 15:13
Nitrogen, Ammonia as N 1.98 mg/L 0.050 99 90 110
Sample 10: LFB-3 Laboratory Fortified Blank Run: TECHNICON_120629A 06/29/12 15: 15
Nitrogen, Ammonia as N 1.87 mg/L 0.050 95 80 120
Sample 10: C12060931-002CMS Sample Matrix Spike Run: TECHNICON_120629A 06/29/12 16:45
Nitrogen, Ammonia as N 1.96 mg/L 0.050 100 90 110
Sample 10: C12060931 -002CMSO Sample Matrix Spike Duplicate Run: TECHNICON_120629A 06/29/12 16:47
Nitrogen, Ammonia as N 2.07 mg/L 0.050 106 90 110 5.5 10
-------_._--------------------------------------------------.. ---------------_._---
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 19 of 33
EN:RGY www.energylab.com Helena, MTB77-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888 .. 235-0515
~iII~tte, WY 88&·&86-7175 • Rapid City, SO 888-672-1225 • College Station, lX 888-690-2218 LABORATORIES Analytical ExCSJlsn&B Sines 1152
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: A4S00·S04 E
Sample 10: LCS·1_120626
Sulfate
Sample 10: MBLK-1_1 20626
Sulfate
Sample 10: C12060931·003AMS
Sulfate
Sample 10: C12060931·003AMSO
Sulfate
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Laboratory Control Sample
4740 mg/L
Method Blank
ND mg/L
Sample Matrix Spike
548 mg/L
Sample Matrix Spike Duplicate
551 mg/L
Report Date: 07/27/12
Work Order: C12060931
RL %REC Low Limit High Limit RPO RPOLimit Qual
Batch: 120626_1_S04-TURB-W
Run: TURB-2_120626A 06/26/12 10:05
100 99 90 110
Run: TURB-2_120626A 06/26/12 10:07
10
Run: TURB-2_120626A 06/26/12 11 :29
10 100 90 110
Run: TURB-2_1 20626A 06/26/12 11 :32
10 101 90 110 0.5 10
ND -Not detected at the reporting limit.
Page 20 of 33
EI'ERGY www.energyJab.com Helena, MTB77-472-071 t • Billings,. MT BOO-735-4489 • Casper, WY 888-235-0515
)iII~ti:e, Vf1866-6B6-7175 • Rapid City, SO 888-672-1225 • College Station, lX 888-690-2218 LABORATORIES Analytical Excs/lsncB Sines 1952
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Work Order: C12060931
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E200.7 Analytical Run: ICP2-C_120706A
Sample 10: ICV 5 Initial Calibration Verification Standard 07/06/12 11 :33
Calcium 49.7 mg/L 0.50 100 95 105
Iron 5.08 mg/L 0.030 102 95 105
Magnesium 52.2 mg/L 0.50 104 95 105
Potassium 49.7 mg/L 2.7 99 95 105
Sodium 50.7 mg/L 0.50 101 95 105
Sample 10: ICSA 5 Interference Check Sample A 07/06/12 12:14
Calcium 506 mg/L 0.50 101 80 120
Iron 189 mg/L 0.030 94 80 120
Magnesium 539 mg/L 0.50 108 80 120
Potassium -0.0145 mg/L 0.50
Sodium -0.0425 mg/L 0.50
Sample 10: ICSAB 5 Interference Check Sample AB 07/06/1212:18
Calcium 516 mg/L 0.50 103 80 120
Iron 190 mg/L 0.030 95 80 120
Magnesium 564 mg/L 0.50 113 80 120
Potassium -0.0163 mg/L 0.50
Sodium -0.0961 mg/L 0.50
Method: E200.7 Batch: R161622
Sample 10: MB-120706A 5 Method Blank Run: ICP2-C_120706A 07/06/12 12:38
Calcium NO mg/L 0.50
Iron NO mg/L 0.030
Magnesium NO mg/L 0.50
Potassium NO mg/L 0.50
Sodium NO mg/L 0.50
Sample 10: LFB-120706A 5 Laboratory Fortified Blank Run: ICP2-C_120706A 07/06/12 12:42
Calcium 50.0 mg/L 0.50 100 85 115
Iron 0.983 mg/L 0.030 98 85 115
Magnesium 50.5 mg/L 0.50 101 85 115
Potassium 45.8 mg/L 0.50 92 85 115
Sodium 49.9 mg/L 0.50 100 85 115
Sample 10: C12060931-0010MS2 5 Sample Matrix Spike Run: ICP2-C -120706A 07/06/1220:19
Calcium 150 mg/L 0.50 89 70 130
Iron 0.976 mg/L 0.030 92 70 130
Magnesium 81.7 mg/L 0.50 96 70 130
Potassium 46.7 mg/L 0.50 88 70 130
Sodium 130 mg/L 0.50 102 70 130
Sample 10: C12060931-0010MSO 5 Sample Matrix Spike Duplicate Run: ICP2-C -120706A 07/06/1220:23
Calcium 148 mg/L 0.50 85 70 130 1.2 20
Iron 0.972 mg/L 0.030 92 70 130 0.4 20
Magnesium 81.9 mg/L 0.50 96 70 130 0.2 20
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 21 of 33
EN:RGY www.energylab.com ijelen~, MT877-472-D711 • Billings. MT 800-735-4489 • Casper, WY 888-235-0515
9}llettEi', Vir 86.6 .. ,86-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218 LABORATORIES Analytical ExCS/JBnCB Sines 1952
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Work Order: C12060931
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E200.7 Batch: R161622
Sample 10: C12060931-0010MSO 5 Sample Matrix Spike Duplicate Run: ICP2-C_120706A 07/06/1220:23
Potassium 47.1 mg/L 0.50 88 70 130 0.9 20
Sodium 129 mg/L 0.50 101 70 130 0.4 20
Method: E200.7 Analytical Run: ICP4-C_120706A
Sample 10: ICV 3 Initial Calibration Verification Standard 07/06/12 12:39
Calcium 50.5 mg/L 0.50 101 95 105
Magnesium 50.8 mg/L 0.50 102 95 105
Sodium 52.7 mg/L 0.50 105 95 105
Sample 10: ICSA 3 Interference Check Sample A 07/06/12 12:53
Calcium 453 mg/L 0.50 91 80 120
Magnesium 515 mg/L 0.50 103 80 120
Sodium 0.367 mg/L 0.50
Sample 10: ICSAB 3 Interference Check Sample AB 07/06/12 12:58
Calcium 450 mg/L 0.50 90 80 120
Magnesium 515 mg/L 0.50 103 80 120
Sodium 0.481 mg/L 0.50
Method: E200.7 Batch: R161661
Sample 10 : MB·120706A 3 Method Blank Run: ICP4-C_120706A 07/06/12 13:02
Calcium NO mg/L 0.50
Magnesium NO mg/L 0.50
Sodium NO mg/L 0.50
Sample 10: LFB-120706A 3 Laboratory Fortified Blank Run: ICP4-C -120706A 07/06/12 13:05
Calcium 49.7 mg/L 0.50 99 85 115
Magnesium 49.6 mg/L 0.50 99 85 115
Sodium 48.9 mg/L 0.50 98 85 115
Sample 10: C12060931·0010MS2 3 Sample Matrix Spike Run: ICP4-C -120706A 07/06/12 18:47
Calcium 144 mg/L 0.50 88 70 130
Magnesium 79.3 mg/L 0.50 97 70 130
Sodium 125 mg/L 0.50 94 70 130
Sample 10: C1 2060931-0010MSO 3 Sample Matrix Spike Duplicate Run: ICP4-C_120706A 07/06/12 18:51
Calcium 142 mg/L 0.50 85 70 130 1.0 20
Magnesium 79.0 mg/L 0.50 96 70 130 0.4 20
Sodium 125 mg/L 0.50 95 70 130 0.3 20
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 22 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical ExullBncs Sines 1952
Helena,MT 871-472-0111 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
_~ill~tf:e, Y!'f 86.6~&86-7115 • Rapid City, SD 888-672-1225 • College Station, lX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Work Order: C12060931
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E200.8 Analytical Run: ICPMS4-C _120711 A
Sample 10: ICV 17 Initial Calibration Verification Standard 07/11/1213:43
Arsenic 0.0498 mg/L 0.0010 100 90 110
Beryllium 0.0508 mg/L 0.0010 102 90 110
Cadmium 0.0501 mg/L 0.0010 100 90 110
Chromium 0.0500 mg/L 0.0010 100 90 110
Cobalt 0.0478 mg/L 0.0010 96 90 110
Copper 0.0508 mg/L 0.0010 102 90 110
Lead 0.0483 mg/L 0.0010 97 90 110
Manganese 0.0505 mg/L 0.0010 101 90 110
Mercury 0.00508 mg/L 0.0010 102 90 110
Molybdenum 0.0496 mg/L 0.0010 99 90 110
Nickel 0.0507 mg/L 0.0010 101 90 110
Selenium 0.0504 mg/L 0.0010 101 90 110
Silver 0.0216 mg/L 0.0010 108 90 110
Thallium 0.0493 mg/L 0.0010 99 90 110
Uranium 0.0505 mg/L 0.00030 101 90 110
Vanadium 0.0500 mg/L 0.0010 100 90 110
Zinc 0.0514 mg/L 0.0010 103 90 110
Method: E200.8 Batch: R161811
Sample 10: LRB 17 Method Blank Run: ICPMS4-C_120711A 07/11/1214:35
Arsenic NO mg/L 0.0050
Beryllium NO mg/L 0.00050
Cadmium NO mg/L 0.00050
Chromium NO mg/L 0.020
Cobalt NO mg/L 0.010
Copper NO mg/L 0.010
Lead NO mg/L 0.0010
Manganese NO mg/L 0.010
Mercury NO mg/L 0.00050
Molybdenum NO mg/L 0.010
Nickel NO mg/L 0.020
Selenium NO mg/L 0.0050
Silver NO mg/L 0.010
Thallium NO mg/L 0.00050
Uranium NO mg/L 0.00030
Vanadium NO mg/L 0.010
Zinc NO mg/L 0.010
Sample 10: LFB 17 Laboratory Fortified Blank Run: ICPMS4-C_120711 A 07/11/1214:39
Arsenic 0.0519 mg/L 0.0010 104 85 115
Beryllium 0.0507 mg/L 0.0010 101 85 115
Cadmium 0.0505 mg/L 0.0010 101 85 115
Chromium 0.0513 mg/L 0.0010 103 85 115
Cobalt 0.0474 mg/L 0.0010 95 85 115
------------------------------------------
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MOC -Minimum detectable concentration
Page 23 of 33
EI\ERGY
LABORATORIES
www.energylab.com
Analytical ExCSUsnCB Sines 1852
Helena, MT 877-472-0711 -Billings, MT 800-735-4489 -Casper, WY 888-235-0515
'.= _~iI,l~tte! wy86t;:"',~86-7175 • Rapid City, SD 888-612-1225 • College Station, IX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count
Method: E200.8
Result Units
Sample 10: LFB
Copper
17 Laboratory Fortified Blank
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Uranium
Vanadium
Zinc
0.0515 mg/L
0.0491 mg/L
0.0516 mg/L
0.00476 mg/L
0.0497 mg/L
0.0519 mg/L
0.0527 mg/L
0.0186 mg/L
0.0500 mg/L
0.0508 mg/L
0.0512 mg/L
0.0522 mg/L
Sample 10: C12070165-003CMS4 17 Sample Matrix Spike
Arsenic 0.0549 mg/L
Beryllium 0.0470 mg/L
Cadmium
Chromium
Cobalt
Copper
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Uranium
Vanadium
Zinc
0.0512 mg/L
0.0514 mg/L
0.0518 mg/L
0.0506 mg/L
0.0500 mg/L
0.0527 mg/L
0.00493 mg/L
0.0517 mg/L
0.0507 mg/L
0.0640 mg/L
0.0189 mg/L
0.0528 mg/L
0.0773 mg/L
0.0529 mg/L
0.0537 mg/L
Sample 10: C12070165-003CMSO 17 Sample Matrix Spike Duplicate
Arsenic 0.0540 mg/L
Beryllium 0.0472 mg/L
Cadmium
Chromium
Cobalt
Copper
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Qualifiers:
RL -Analyte reporting limit.
MDC - Minimum detectable concentration
0.0512 mg/L
0.0504 mg/L
0.0515 mg/L
0.0497 mg/L
0.0499 mg/L
0.0522 mg/L
0.00499 mg/L
0.0512 mg/L
0.0499 mg/L
0.0627 mg/L
Report Date: 07/27/12
Work Order: C12060931
RL %REC Low Limit High Limit
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.0010
0.00030
0.0010
0.0010
0.0010
0.0010
0.0010
0.0050
0.0050
0.0050
0.0010
0.0010
0.00010
0.0010
0.0050
0.0010
0.0010
0.00050
0.00030
0.010
0.010
0.0010
0.0010
0.0010
0.0050
0.0050
0.0050
0.0010
0.0010
0.00010
0.0010
0.0050
0.0010
103
98
103
95
99
104
105
93
100
102
102
104
Run: ICPMS4-C_120711A
85 115
85 115
85 115
85 115
85 115
85
85
85
85
85
85
85
115
115
115
115
115
115
115
Run: ICPMS4-C_120711 A
109 70 130
94 70 130
102
102
103
100
100
105
99
97
101
102
94
106
112
101
105
107
94
102
101
103
98
100
104
100
96
99
100
70
70
70
70
70
70
70
70
70
70
70
70
70
70
70
130
130
130
130
130
130
130
130
130
130
130
130
130
130
130
Run: ICPMS4-C_120711A
70 130
70 130
70 130
70
70
70
70
70
70
70
70
70
130
130
130
130
130
130
130
130
130
ND -Not detected at the reporting limit.
RPO RPOLimit Qual
1.6
0.4
0.0
1.9
0.6
1.7
0.2
0.9
1.3
1.0
1.6
1.9
Batch: R161811
07/11/1214:39
07/12/12 01 :06
07/12/12 01 :10
20
20
20
20
20
20
20
20
20
20
20
20
Page 24 of 33
EN:RGY www.energylab.com Helena, MlB77-472-0711 • Billings. MT 800-735-4489 • Casper, WY 888-235-0515
_,~illette, 'NY 8&6"',686-7175 • Rapid City, SO 888-672-1225 • College Station, IX 888-6&0-2218 LABORATORIES Analytical ExCBUBllCB Sines 1852
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
QA/QC Summary Report
Prepared by Casper, WY Branch
Report Date: 07/27/12
Work Order: C12060931
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: E200.8
Sample 10: C12070165-003CMSO
Silver
Thallium
Uranium
Vanadium
Zinc
Method: E200.8
Sample 10 : ICV
Beryllium
Method: E200.8
Sample 10: LRB
Beryllium
Sample 10: LFB
Beryllium
Sample 10: C12060931-0040MS
Beryllium
Sample 10: C12060931-0040MSO
Beryllium
Qualifiers:
17 Sample Matrix Spike Duplicate
0.0191 mg/L 0.0010
0.0518 mg/L 0.00050
0.0762 mg/L 0.00030
0.0520 mg/L 0.010
0.0519 mg/L 0.010
Initial Calibration Verification Standard
0.0486 mg/L 0.0010
Method Blank
ND mg/L 0.00050
Laboratory Fortified Blank
0.0505 mg/L 0.0010
Sample Matrix Spike
0.0450 mg/L 0.0010
Sample Matrix Spike Duplicate
0.0459 mg/L 0.0010
Batch: R161811
Run: ICPMS4-C_120711A 07/12/1201:10
95 70 130 0.9 20
104 70 130 1.9 20
110 70 130 1.4 20
100 70 130 1.7 20
102 70 130 3.4 20
Analytical Run: ICPMS4-C_120712A
97 90 110
Run: ICPMS4-C _120712A
Run: ICPMS4-C_120712A
101 85 115
Run: ICPMS4-C_120712A
90 70 130
Run: ICPMS4-C _120712A
92 70 130 2.0
07/12/12 13:01
Batch: R161901
07/12/12 13:37
07/12/12 13:41
07/13/12 07:29
07/13/1207:34
20
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 25 of 33
EN::RGY www.energylab.com .. Helena, MT87l .. 472-0711 • Billings, MT 800-735-4489 . Casper, WY 888-235-0515
,,~i!'e,.ti:e, WV 86& ... &86-7175 • Rapid City, SD 888-&72-1225 • College Station, lX 888-690-2218 L ABORATORIES Analytical ExcslJBfI&B Sines 1952
QA/QC Summary Report
Prepared by Casper, WY Branch
Client : Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: E353.2
Sample 10: MBLK-1
Nitrogen, Nitrate+Nitrite as N
Sample 10: LCS-2
Nitrogen, Nitrate+Nitrite as N
Sample 10: LFB-3
Nitrogen, Nitrate+Nitrite as N
Sample 10: C12060198-001BMS
Nitrogen, Nitrate+Nitrite as N
Sample 10: C12060198-001 BMSO
Nitrogen, Nitrate+Nitrite as N
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Method Blank
NO mg/L
Laboratory Control Sample
2.53 mg/L
Laboratory Fortified Blank
1.94 mg/L
Sample Matrix Spike
4.93 mg/L
Sample Matrix Spike Duplicate
4.98 mg/L
Report Date:
Work Order:
RL %REC Low Limit High Limit RPO
Run: TECHNICON_120627B
0.10
Run: TECHNICON_120627B
0.10 101 90 110
Run: TECHNICON_120627B
0.10 99 90 110
Run: TECHNICON_120627B
0.10 92 90 110
Run: TECHNICON_120627B
0.10 95 90 110 1.0
NO -Not detected at the reporting limit.
07/27/12
C12060931
RPOLimit Qual
Batch: R161256
06/27/12 14:53
06/27/12 14:55
06/27/12 14:58
06/27/12 15:03
06/27/12 15:05
10
Page 26 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical ExCSUsnCB Sines 1952
Helena, Mt877-472-D711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
;.,:Gl!i~tte, Wy 866-686-7175 • Rap,irl City, SO 888-672-1225 • College Station, IX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: E900.1
Sample 10: LCS-GA-OS42
Gross Alpha minus Rn & U
Sample 10: MB-GA-OS42
Gross Alpha minus Rn & U
Laboratory Control Sample
23.0 pC ilL
3 Method Blank
-0.249
Gross Alpha minus Rn & U Precision (±) 0.207
pC ilL
pC ilL
pC ilL Gross Alpha minus Rn & U MDC 0.483
Sample 10: C12061068-003CMS
Gross Alpha minus Rn & U
Sample 10: C12061068-003CMSO
Gross Alpha minus Rn & U
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Sample Matrix Spike
51.5 pC ilL
Sample Matrix Spike Duplicate
50.0 pC ilL
Report Date: 07/27/12
Work Order: C12060931
RL %REC Low Limit High Limit RPO RPOLimit -.Qual
Run: BERTHOLD 770-1_120629A
113 70 130
Run: BERTHOLD 770-1 120629A
Run: BERTHOLD 770-1_120629A
121 70 130
Run: BERTHOLD 770-1 120629A
118 70 130 3.0
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: GA-0542
07/04/12 10:04
07/04/12 10:04
U
07/04/12 11 :44
07/04/12 11 :44
24.2
Page 27 of 33
EI'I:RGY
LABORATORIES
www.energylab.com
Analytical ExCSUsnCB Sines 1852
Helena, MT 877-472-071 t • Billings, MT 800-735-4489 • Casper, W'f 888-235-0515
, .. ~i!le.ttl!, WY .866-686-7175 • Rapid City, SD 888-672-1225 • College Station, lX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date: 07/27/12
Project: Seeps and Springs 2012 Work Order: C12060931
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPOLimit Qual
Method: SW8260B Batch: R161404
Sample 10: 29-Jun-12_LCS_ 4 16 Laboratory Control Sample Run: GCMS2_120629A 06/29/12 12:33
Acetone 100 ug/L 20 101 70 130
Benzene 9.7 ug/L 1.0 97 70 130
Carbon tetrachloride 9.4 ug/L 1.0 94 70 130
Chloroform 9.6 ug/L 1.0 96 70 130
Chlorom ethane 9.1 ug/L 1.0 91 70 130
m+p-Xylenes 19 ug/L 1.0 96 70 130
Methyl ethyl ketone 100 ug/L 20 102 70 130
Methylene chloride 9.9 ug/L 1.0 99 70 130
Naphthalene 8.8 ug/L 1.0 88 70 130
o-Xylene 9.2 ug/L 1.0 92 70 130
Toluene 10 ug/L 1.0 104 70 130
Xylenes, Total 28 ug/L 1.0 94 70 130
Surr: 1,2-0ichlorobenzene-d4 1.0 103 80 120
Surr: Oibromofluoromethane 1.0 110 70 130
Surr: p-Bromofluorobenzene 1.0 105 80 130
Surr: Toluene-d8 1.0 120 80 120
Sample 10: 29-Jun-12_MBLK_6 16 Method Blank Run: GCMS2 -120629A 06/29/12 13:43
Acetone NO ug/L 20
Benzene NO ug/L 1.0
Carbon tetrachloride NO ug/L 1.0
Chloroform NO ug/L 1.0
Chloromethane NO ug/L 1.0
m+p-Xylenes NO ug/L 1.0
Methyl ethyl ketone NO ug/L 20
Methylene chloride NO ug/L 1.0
Naphthalene NO ug/L 1.0
o-Xylene NO ug/L 1.0
Toluene NO ug/L 1.0
Xylenes, Total NO ug/L 1.0
Surr: 1,2-0ichlorobenzene-d4 1.0 121 80 120 S
Surr: Oibromofluoromethane 1.0 111 70 130
Surr: p-Bromofluorobenzene 1.0 136 80 120 S
Surr: Toluene-d8 1.0 116 80 120
Sample 10: C12060931-003EMS 16 Sample Matrix Spike Run: GCMS2 120629A 06/29/1220:35 -
Acetone 2100 ug/L 200 107 70 130
Benzene 290 ug/L 10 144 70 130 S
Carbon tetrachloride 170 ug/L 10 87 70 130
Chloroform 180 ug/L 10 88 70 130
Chloromethane 150 ug/L 10 74 70 130
m+p-Xylenes 380 ug/L 10 96 70 130
Methyl ethyl ketone 2200 ug/L 200 108 70 130
Methylene chloride 170 ug/L 10 84 70 130
Naphthalene 150 ug/L 10 74 70 130
------------------------------------------------
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MOC -Minimum detectable concentration S -Spike recovery outside of advisory limits.
Page 28 of 33
EN:RGY
LABORATORIES
www.energylab.com
Analytical Exesllsnell Sines 1952
Helena, MT877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
" "9,~II~tte, WY866 .. ~86-717~ • Rapid City, SI} 888-672-1225 • College Station, lX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: SW8260B
Sample 10: C12060931-003EMS 16 Sample Matrix Spike
o-Xylene 180 ug/L
Toluene 290 ug/L
Xylenes, Total 570 ug/L
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: T oluene-d8
Sample 10: C12060931-003EMSO 16 Sample Matrix Spike Duplicate
Acetone 2400 ug/L
Benzene 190 ug/L
Carbon tetrachloride 180 ug/L
Chloroform 200 ug/L
Chloromethane 190 ug/L
m+p-Xylenes 380 ug/L
Methyl ethyl ketone 2300 ug/L
Methylene chloride 190 ug/L
Naphthalene 170 ug/L
o-Xylene 190 ug/L
Toluene 220 ug/L
Xylenes, Total 570 ug/L
Surr: 1,2-Dichlorobenzene-d4
Surr: Dibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
S -Spike recovery outside of advisory limits.
Report Date:
Work Order:
RL %REC Low Limit High Limit
Run: GCMS2_120629A
10 92 70 130
10 146 70 130
10 95 70 130
1.0 100 80 120
1.0 108 70 130
1.0 103 80 120
1.0 171 80 120
Run: GCMS2 120629A -
200 119 70 130
10 95 70 130
10 90 70 130
10 98 70 130
10 94 70 130
10 96 70 130
200 116 70 130
10 96 70 130
10 84 70 130
10 93 70 130
10 108 70 130
10 95 70 130
1.0 102 80 120
1.0 116 70 130
1.0 103 80 120
1.0 123 80 120
ND -Not detected at the reporting limit.
R -RPD exceeds advisory limit.
RPO
11
41
3.2
10
23
0.4
7.1
14
13
1.3
30
0.7
0.0
0.0
0.0
0.0
07/27/12
C12060931
RPOLimit Qual
Batch: R161404
06/29/12 20:35
S
S
06/29/1221 :10
20
20 R
20
20
20 R
20
20
20
20
20
20 R
20
10
10
10
10 S
Page 29 of 33
EI\ERGY
LABORATO RIES
www.energylab.com
Analytical ExcsllsnCB Sines '852
Helena,MT 877-472-071 t • Billings, MT 800-735-4489 • Casper, WV 888-235-0515
. _~illet±li, WY 866,,688-7175 • Rapid City, SI} 888-&72-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp
Project: Seeps and Springs 2012
Analyte Count Result Units
Method: SW8260B
Sample 10: 02-Jul-12_LCS_ 4 16 Laboratory Control Sample
Acetone 100 ug/L
Benzene 12 ug/L
Carbon tetrachloride 12 ug/L
Chloroform 13 ug/L
Chlorom ethane 13 ug/L
m+p-Xylenes 25 ug/L
Methyl ethyl ketone 100 ug/L
Methylene chloride 12 ug/L
Naphthalene 9.6 ug/L
o-Xylene 12 ug/L
Toluene 13 ug/L
Xylenes, Total 37 ug/L
Surr: 1 ,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Sample 10: 02-Jul-12_MBLK_6 16 Method Blank
Acetone NO ug/L
Benzene NO ug/L
Carbon tetrachloride NO ug/L
Chloroform NO ug/L
Chloromethane NO ug/L
m+p-Xylenes NO ug/L
Methyl ethyl ketone NO ug/L
Methylene chloride NO ug/L
Naphthalene NO ug/L
o-Xylene NO ug/L
Toluene NO ug/L
Xylenes, Total NO ug/L
Surr: 1 ,2-0ichlorobenzene-d4
Surr: Oibromofluoromethane
Surr: p-Bromofluorobenzene
Surr: Toluene-d8
Sample 10: C12060949-001 BMS 16 Sample Matrix Spike
Acetone 2600000 ug/L
Benzene 210000 ug/L
Carbon tetrachloride 190000 ug/L
Chloroform 210000 ug/L
Chloromethane 260000 ug/L
m+p-Xylenes 400000 ug/L
Methyl ethyl ketone 2600000 ug/L
Methylene chloride 210000 ug/L
Naphthalene 160000 ug/L
RL
20
1.0
1.0
1.0
1.0
1.0
20
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
20
1.0
1.0
1.0
1.0
1.0
20
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
1.0
200000
10000
10000
10000
10000
10000
200000
10000
10000
Report Date: 07/27/12
Work Order: C12060931
%REC Low Limit High Limit RPO RPOLimit Qual
Batch: R161460
Run: GCMS2_120702A 07/02/1212:40
103 70 130
122 70 130
120 70 130
126 70 130
129 70 130
124 70 130
104 70 130
124 70 130
96 70 130
117 70 130
130 70 130
122 70 130
95 80 120
115 70 130
92 80 130
114 80 120
Run: GCMS2 120702A 07/02/12 13:50 -
121 80 120 S
107 70 130
132 80 120 S
111 80 120
Run: GCMS2_120702A 07/02/1220:43
130 70 130
98 70 130
96 70 130
104 70 130
130 70 130
97 70 130
128 70 130
103 70 130
78 70 130
___________ • ____________________ w _______________________________________ • ___________________________________ • __________________ " ____________________ • ______ • ____________________________________________ "_
Qualifiers:
RL -Analyte reporting limit. NO -Not detected at the reporting limit.
MOC -Minimum detectable concentration S -Spike recovery outside of advisory limits.
Page 30 of 33
EI\ERGY
LABORATORIES
www.energylab.com
Analytical ExCSUBf/CB Sinc8 1952
.Helena, MTB77-472-071 t • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
_,J!l!I~fte, WY866-686-7t 75 • Rapid CIty, SD 888-672-1225 • College Station, IX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Denison Mines USA Corp Report Date:
Project: Seeps and Springs 2012 Work Order:
Analyte Count Result Units RL %REC Low Limit High Limit RPO
Method: SW8260B
Sample 10: C12060949-001 BMS 16 Sample Matrix Spike Run: GCMS2_120702A
a-Xylene 190000 ug/L 10000 96 70 130
Toluene 250000 ug/L 10000 109 70 130
Xylenes, Total 590000 ug/L 10000 97 70 130
Surr: 1 ,2-Dichlorobenzene-d4 1.0 101 BO 120
Surr: Dibromofluoromethane 1.0 122 70 130
Surr: p-Bromofluorobenzene 1.0 97 BO 120
Surr: Toluene-dB 1.0 11B BO 120
Sample 10: C12060949-001 BMSO 16 Sample Matrix Spike Duplicate Run: GCMS2 -120702A
Acetone 2600000 ug/L 200000 129 70 130 0.6
Benzene 250000 ug/L 10000 120 70 130 19
Carbon tetrachloride 97000 ug/L 10000 4B 70 130 66
Chloroform 210000 ug/L 10000 105 70 130 0.4
Chloromethane 290000 ug/L 10000 145 70 130 10
m+p-Xylenes 400000 ug/L 10000 97 70 130 0.6
Methyl ethyl ketone 2400000 ug/L 200000 122 70 130 4.5
Methylene chloride 220000 ug/L 10000 112 70 130 B.2
Naphthalene 160000 ug/L 10000 7B 70 130 1.0
a-Xylene 190000 ug/L 10000 96 70 130 0.4
Toluene 500000 ug/L 10000 232 70 130 66
Xylenes, Total 590000 ug/L 10000 97 70 130 0.3
Surr: 1 ,2-Dichlorobenzene-d4 1.0 102 BO 120 0.0
Surr: Dibromofluoromethane 1.0 122 70 130 0.0
Surr: p-Bromofluorobenzene 1.0 101 BO 120 0.0
Surr: Toluene-dB 1.0 233 BO 120 0.0
-----------------------
Qualifiers:
RL -Analyte reporting limit.
MDe -Minimum detectable concentration
S -Spike recovery outside of advisory limits.
ND -Not detected at the reporting limit.
R -RPD exceeds advisory limit.
07/27/12
C12060931
RPOLimit Qual
Batch: R161460
07/02/1220:43
07/02/1221 :1B
20
20
20 SR
20
20 S
20
20
20
20
20
20 SR
20
10
10
10
10 S
Page 31 of 33
EN:RGY
LABORATORIES
~J'" www.energylab.com ~ Analytical ExcsUsnc, Sines 1952
Helena, MT 877-472 .... 0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
. ,~ille{te, WY 86&-~86-7115 • Rapid City, SD 888-672-1225 • College Station, IX 888-690-2218
Standard Reporting Procedures
Lab measurement of analytes considered field parameters that require analysis within 15 minutes of sampling such as pH, Dissolved Oxygen and Residual
Chlorine, are qualified as being analyzed outside of recommended holding time.
Solid/soil samples are reported on a wet weight basis (as received) unless specifically indicated. If moisture corrected, data units are typically noted as -dry.
For agricultural and mining soil parameters/characteristics, all samples are dried and ground prior to sample analysis.
Workorder Receipt Checklist
Denison Mines USA Corp
Login completed by: Timothy I.. Houghteling
Reviewed by: BL2000\kschroeder
Reviewed Date: 6/27/2012
Shipping container/cooler in good condition?
Custody seals intact on shipping container/cooler?
Custody seals intact on sample bottles?
Chain of custody present?
Chain of custody signed when relinquished and received?
Chain of custody agrees with sample labels?
Samples in proper container/bottle?
Sample containers intact?
Sufficient sample volume for indicated test?
All samples received within holding time?
(Exclude analyses that are considered field parameters
such as pH, DO, Res CI, Sulfite, Ferrous Iron, etc.)
ContaineriTemp Blank temperature:
Water -VOA vials have zero headspace?
Water -pH acceptable upon receipt?
Contact and Corrective Action Comments:
None
Yes 0
Yes 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
2.2'C On Ice
Yes 0
Yes 0
C12060931
Date Received: 6/22/2012
Received by: kg
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
Carrier Next Day Air
name:
Not Present D
Not Present D
Not Present 0
No VOA vials submitted D
Not Applicable D
Page 32 of 33
""'0 Q) co CD
c.v c.v
o -c.v c.v
EN:RGY aa" Chain of Custody and Analytical Request Record Page ~ of --1-
-----~ - ----~ -.. , .. - -~ -........ ----~ ----_ •••••• -•••• -~.-•• -----.P. .............. .., ..... ,
Company Name: Project Name, PWS, Permit, Etc. Sample Origin EPA/State Compliance: D~t\\·.son M\\ne~ See..ps ~~ S~t";tt~ 2.0\~ State: U'T' Yes ~ No 0
Report Mail Address: f6 130 )( 80~ Contact Name: Phone/Fax: Email: Sampler: (Please Print)
~ )C\Y\a; flDt ~ 0--('(' \ '" 'P ().. \ yV\ t: (" L\~S b7g ~\ ~r\~r Ao 1\: AAd \J\\ gY:;JI
Invoice Address: V Invoice Contact & Phone: Purchase Order: Quote/Bottle Order: S,,~ D~\)\~ -):r\:. Ll~S G.78 ~,
Special Report/Formats: ~ W@D@ lK1§®GDrn®LrrnW • Contact ELI prior to 5~ppedby: 3: f r .,.#f)t4 0 ..... RUSH sample submittal ~o U)~ ~ R for charges and Co~er 10(5): ~CQ;gOI ('fi Q ~ scheduling ~ See C,l41f ._> 0 >-1ij
DDW D EDD/EDT(Electronic Data) ~en~m~ W Instruction Page
03:= ~ C) 0 :::r: "C Receipt Temp o POTWIWWTP Format: u 0 0 1:: ::r t) c Comments: ::;, U .... « CJ)ICOI32 ~ .:: 0 ;>. ? o State: o LEVEL IV o L-. I:: '-°c •• <I) c:'-:3 «l '-~1U.Q Ci l-e:: o Other: o NELAC ~~IE~ .... On Ice: Q)N « ::;, t-~~«I~O ~ W "E 5 Custody Seal Z c. Q) ~ >1 W CU On Bottle V. ~ en "'0 ~N en e:: On Cooler
0 ~ H Intact ~: 1 C/)
SAMPLE IDENTIFICATION Collection Collection MATRIX ~ Signature {Name, Location, Interval, etc.} Date Time Match
1 -er'lfdo..t'lC~ ~ee.p 'i: ,/;J..O/l?.. lO'~ b-W ~
2 ~ , \Mn ~Pf"\r'\" '/~O/I'J.. O'1;l.O , .... W )C I~
3 ""-oJ ~/:;.c/~ 074.5 6-W y: ~ Co+-\-on\J.l()od ~1:>{';"<lt. Innn
4B~ • I ~ '/';)..6/12-O,t..t5 b-W X ~ SPl"rlll
5-(;;0 R)~l< c1t./ (, '/!lO/)~ ~
6 -r l'.~~ K I~,.~ ~c. l'')...b(,/2 b <1'3.1
7 , . ~
8 ~.
9
OOJ I~
10 .td]
Custody ;a~~~Y#:;\IJA~ ~~t/;\b..o\Q.. .1100 ~ s~:n=~ it IJ-L. -l
Received by (print): DatefTime: Signature:
Record Relinquished by (print): "" DatefTime: Signature: • V Received by (print): DatefTime: Signature:
MUST be Kecelveo Dy LaDOra1Ory: C. uaIa/llme: k.J ~,gnature: Signed Sample Disposal: Return to Client: Lab Disposal: .. ;)7·ld er:s-o 1:"'> C:.:s"
In certain circumstances. samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analysis requested.
This serves as notice of this possibility. All sub·contract data will be clearly notated on your analytical report.
\ 1:_:. -•.•••• ~&... _i+~ ~~ .. n ..... " ... "r,..." ... h ............... fnr .:"irlifi,.. ... .",' inftVI'YH::atinn rtrnAJnln:::art ::ahl"" f""p C:f'h""rtlll"" fnrm<: ::::ann linlce:
ANALYTICAL LAaOJ~AT<>R IE-S
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Jo Ann Tischler
Denison Mines
1050 17th Street, # 950
Denver, CO 80265
TEL: (303) 389-4132
RE: Seeps and Springs 2012
Dear JoAnn Tischler: Lab Set ill: 1206379
American West Analytical Laboratories received 5 sample(s) on 6/22/2012 for the
analyses presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Association Conference (NELAC) Institute in Utah and Texas;
and is state accredited in Colorado, Idaho, New Mexico, and Missouri. In addition,
A W AL is also accredited by the American Analytical Laboratory Association (A2LA) on
ISO IEC 17025:2005, Department of Defense (DOD), UST for the State of Wyoming, and
the National Lead Laboratory Accreditation Program (NLLAP). All analyses were
performed in accordance to The NELAC Institute and/or A2LA protocols unless noted
otherwise. Accreditation 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, Ky I e F·, Digitally signed by Kyle F. Gross
ON: cn=Kyle F. Gross, o=AWAL,
ou=AWAL, email=kyle@awal-
G laos.com, c=US r 0 S ~Date: 2012.0:0313:38:23 -06'00'
Approved by: L...-__ -il-~..:::;...~ ______ ---I
Laboratory Director or designee
Report Date: 7/3/2012 Page 1 of 26
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of t~e name of this company or any. member of its start: or reproduction of this report in. c?nnection \\lith the adverti~ement, promotion or sale .of any product or process, or in connection with the re_-publication of this report for any
Client:
Project:
Lab Set ID:
Date Received:
Lab Sample ID
463 West 3600 South
1206379-001A
;alt Lake City, UT 84115
1206379-001B
1206379-002A
Phone: (801) 263-8686 1206379-002B
Toll Free: (888) 263-8686 1206379-003A
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com 1206379-003B
1206379-004A
web: www.awal-labs.com 1206379-004B
1206379-005A
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
SAMPLE SUMMARY
Denison Mines
Seeps and Springs 2012
1206379
6/22/2012 1030h
Client Sample ID
Entrance Seep
Entrance Seep
Ruin Spring
Ruin Spring
Cottonwood Spring
Cottonwood Spring
Back Spring
Back Spring
Trip Blank
Date Collected
6/20/2012 1015h
6120/2012 1015h
6/20/2012 920h
6120/2012 920h
6120/2012 745h
6/2012012 745h
6/20/2012 745h
6/2012012 745h
6/2012012
Contact: JoAnn Tischler
Matrix Analysis
Aqueous VOA by GCIMS Method
8260C/5030C
Aqueous ICPMS Metals, Dissolved
Aqueous VOA by GCIMS Method
8260C/5030C
Aqueous ICPMS Metals, Dissolved
Aqueous VOA by GCIMS Method
8260C/5030C
Aqueous ICPMS Metals, Dissolved
Aqueous VOA by GCIMS Method
8260C/5030C
Aqueous ICPMS Metals, Dissolved
Aqueous VOA by GC/MS Method
8260C/5030C
Report Date: 713/2012 Page 2 of26
All analyses applicable to. the CWA, SDWA, and RCRA are perfonned in accordance to NELAC pro.tocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use o.fthe addressee. Privileges of
subsequent use of the name of this company or any member of its staff, or repro.duction of this report in. c~nnection ~ith the adverti~ement, pro.motion or sale .of any product or process, or in connection with the re.-publication of t~is report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
;:-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-O-C Discrepancies:
Denison Mines
Jo Ann Tischler
Seeps and Springs 2012
1206379
6/22/2012
6/20/2012
Intact
None
Holding Time and Preservation Requirements: The analysis of the sample was
performed within the method holding times. The sample was properly preserved.
Preparation and Analysis Requirements: The sample was analyzed following the
methods stated on the analytical reports. The sample was not digested pursuant to the client
request.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Corrective Action: None required.
Report Date: 7/3/2012 Page 3 of 26
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use of t~e name ?~ this company or any member of its staff, or reproduction of this report in. c?nnection v:ith the adverti~ement, promotion or sale of any product or pro.cess, or in connection with the re.-publication of t~is. report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Volatile Case Narrative
Client:
Contact:
Denison Mines
JoAnn Tischler
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-O-C Discrepancies:
Method:
Analysis:
Seeps and Springs 2012
1206379
6/22/2012
6/20/2012
Intact
None
SW -846 8260C/5030C
Tetrahydrofuran
General Set Comments: Tetrahydrofuran was not 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 1 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: 7/3/2012 Page 4 of26
All analyses applicable to' the CWA, SDWA, and RCRA are perfo.nned in acco.rdance to. NELAC pro.toco.ls. Pertinent sampling info.nnatio.n is lo.cated o.n the attached COc. This repo.rt is provided fo.r the exclusive use ofthe addressee. Privileges o.f
subsequent use o.fthe name o.f this co.mpany o.r any member o.f its staff; o.r reproductio.n o.fthis repo.rt in c~nnectio.n v:ith the advertisement, pro.mo.tio.n o.r sale .o.f any pro.duct o.r process, o.rin co.nnectio.n with the re.-publicatio.n o.ft~is repo.rt fo.r any
INORGANIC ANALYTICAL REPORT
463 West 3600 South
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-001
Client Sample ID: Entrance Seep
Collection Date: 6/20/2012 1015h
Received Date:
Analytical Results
Compound
6/22/2012 1030h
Units
Date
Prepared
;alt Lake City, UT 84115 Tin mglL
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
This sample was not digested pursuant to the client request.
Date
Analyzed
6/27/2012 1l06h
Contact: JoAnn Tischler
DISSOLVED METALS
Method
Used
E200.8
Reporting
Limit
0.100
Analytical
Result
< 0.100
Qual
Report Date: 7/3/2012 Page 5 of 26
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent useofthe name of this company or any member of its staff, or reproduction ofthis report in. c~nnection \\lith the advertisement, pro.motion or sale of any product or process, or in connection with the re.-publication of this report for any
INORGANIC ANALYTICAL REPORT
463 West 3600 South
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-002
Client Sample ID: Ruin Spring
Collection Date: 6/20/2012 920h
Received Date:
Analytical Results
Compound
6122/2012 1030h
Units
Date
Prepared
;alt Lake City, UT 84115 Tin mg/L
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
This sample was not digested pursuant to the client request.
Date
Analyzed
6/27/2012 1l10h
Contact: JoAnn Tischler
DISSOLVED METALS
Method
Used
E200.8
Reporting
Limit
0.100
Analytical
Result
< 0.100
Qual
Report Date: 7/3/2012 Page 6 of 26
All analyses applicable to the CWA, SDW A, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COe. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of t~e name of this comp'any or any member of its start: or reproduction of this report in. c~nnection \\lith the adverti~ement, pro.motion or sale .of any product or pro.cess, orin connection with the re.-publication of t~is report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-003
Client Sample ID: Cottonwood Spring
Collection Date: 6/20/2012 745h
Received Date: 6/2212012 1030h
Analytical Results
Date
Compound Units Prepared
Tin mg/L
This sample was not digested pursuant to the client request.
Contact: JoAnn Tischler
DISSOLVED METALS
Date Method Reporting Analytical
Analyzed Used Limit Result Qual
6127/2012 1114h E200.8 0.100 < 0.100
Report Date: 7/3/2012 Page 7 of26
All analyses applicable to the CW A, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infom1ation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of the name of this company or any member of its staff, or reproduction of this report in. c~nnection \\lith the adverti~ement, pro.motion or sale .of any product or pro?ess, or in connection with the re.-publication oft~isreport for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-004
Client Sample ID: Back Spring
Collection Date: 6/20/2012 745h
Received Date: 6/22/2012 1030h
Analytical Results
Date
Compound Units Prepared
Tin mg/L
This sample was not digested pursuant to the client request.
Date
Analyzed
6127/2012 1118h
Contact: Jo Ann Tischler
DISSOLVED METALS
Method Reporting Analytical
Used Limit Result Qual
E200.8 0.100 < 0.100
Report Date: 7/3/2012 Page 8 of26
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on the attached COe. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use of t~e name of this company or any member of its staff, or reproduction of this report in. c~nnection v:ith the adverti~ement, pro.motion or sale .of any product or pro.cess, or in connection with the re.-publication of t~is. report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-001A
Client Sample ID: Entrance Seep
Collection Date: 6/20/2012 1015h
Received Date: 6/22/2012 1030h
Contact: Jo Ann Tischler
Analytical Results VOAs by GC/MS Method 8260CIS030C
Analyzed: 6/26/2012 829h
Units: ~g/L
Compound
Tetrahydrofuran
Surrogate
Surr: Toluene-d8
Surr: Dibromofluoromethane
Surr: 4-Bromofluorobenzene
Surr: 1,2-Dichloroethane-d4
Dilution Factor: Method:
CAS Reporting
Number Limit
109-99-9 1.00
CAS Result Amount Spiked %REC
2037-26-5 44.9 50.00 89.8
1868-53-7 49.2 50.00 98.3
460-00-4 42.2 50.00 84.4
17060-07-0 49.0 50.00 98.0
SW8260C
Analytical
Result Qual
< 1.00
Limits Qual
77-129
80-124
80-128
72-151
Report Date: 7/3/2012 Page 9 of 26
All 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 CDC. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use oft~e name of this company or any member of its staff, or reproduction of this report in. c~nnection v:ith the adverti~ement, promotion or sale .of any product or pro.cess, orin connection with the re.'publication of this report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-002A
Client Sample ID: Ruin Spring
Collection Date: 6/20/2012 920h
Received Date: 6/22/2012 1030h
Contact: Jo Ann Tischler
Analytical Results VOAs by GC/MS Method 8260CIS030C
Analyzed: 6/2612012920h
Units: Jlg/L
Compound
Tetrahydrofuran
Surrogate
SUIT: Toluene-d8
SUIT: Dibromofluoromethane
SUIT: 4-Bromofluorobenzene
SUIT: 1,2-Dichloroethane-d4
Dilution Factor: Method:
CAS Reporting
Number Limit
109-99-9 1.00
CAS Result Amount Spiked %REC
2037-26-5 45.3 50.00 90.5
1868-53-7 50.6 50.00 101
460-00-4 42.1 50.00 84.2
17060-07-0 50.9 50.00 102
SW8260C
Analytical
Result Qual
< 1.00
Limits Qual
77-129
80-124
80-128
72-151
Report Date: 7/3/2012 Page 10 of26
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling information is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use of the name o~ this company or any member of its staff, or reproduction of this report in. c~nnection v:ith the adverti~ement, pro.motion or sale of any product or pro. cess, or in connection with the re.-publication of t?isreport for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
3-mail: awal@awal-Iabs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-003A
Client Sample ID: Cottonwood Spring
Collection Date: 6/20/2012 745h
Received Date: 6/22/2012 1030h
Contact: Jo Ann Tischler
Analytical Results VOAs by GC/MS Method 8260C/5030C
Analyzed: 6126/2012 1036h
Units: IlglL
Compound
Tetrahydrofuran
Surrogate
SUIT: Toluene-d8
Surr: Dibromofluoromethane
SUIT: 4-Bromofluorobenzene
SUIT: 1,2-Dichloroethane-d4
Dilution Factor: Method:
CAS Reporting
Number Limit
109-99-9 1.00
CAS Result Amount Spiked %REC
2037-26-5 45.8 . 50.00 91.5
1868-53-7 49.5 50.00 99.0
460-00-4 42.8 50.00 85.7
17060-07-0 49.6 50.00 99.2
SW8260C
Analytical
Result Qual
< 1.00
Limits Qual
77-129
80-124
80-128
72-151
Report Date: 7/3/2012 Page 11 of 26
All 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. This report is provided for the exclusive use ofthe addressee. Privileges of
subsequent use of the name of this company or any member of its staff; or reproduction of this report in. c(mnection ""ith the adverti~ement, pro.motion or sale .of any product or process, or in connection with the re.-publication of t?is report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mai1: awal@awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-004A
Client Sample ID: Back Spring
Collection Date: 6/2012012 745h
Received Date: 6/22/2012 1030h
Contact: JoAnn Tischler
Analytical Results VOAs by GC/MS Method 8260CIS030C
Analyzed: 6/2612012 1101h
Units: Jlg/L
Compound
Tetrahydrofuran
Surrogate
Surr: Toluene-d8
Surr: Dibromofluoromethane
Surr: 4-Bromofluorobenzene
Surr: 1,2-Dichloroethane-d4
Dilution Factor: Method:
CAS Reporting
Number Limit
109-99-9 1.00
CAS Result Amount Spiked %REC
2037-26-5 44.8 50.00 89.6
1868-53-7 49.6 50.00 99.3
460-00-4 41.3 50.00 82.6
17060-07-0 49.4 50.00 98.9
SW8260C
Analytical
Result Qual
< 1.00
Limits Qual
77-129
80-124
80-128
72-151
Report Date: 7/3/2012 Page 12 of26
All analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of t~e name of this company or any member of its staff, or reproduction of this report in. c~nnection ""ith the adverti~ement, pro. motion or sale .of any product or process, or in connection with the re.-publication of t~is report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
ORGANIC ANALYTICAL REPORT
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1206379-005A
Client Sample ID: Trip Blank
Collection Date: 6/20/2012
Received Date: 6/22/2012 1030h
Contact: Jo Ann Tischler
Analytical Results VOAs by GC/MS Method 8260CIS030C
Analyzed: 6/2612012 1127h
Units: /-lg/L
Compound
Tetrahydrofuran
Surrogate
Surr: Toluene-d8
Surr: Dibromofluoromethane
Surr: 4-Bromofluorobenzene
Surr: 1,2-Dichloroethane-d4
Dilution Factor: Method:
CAS Reporting
Number Limit
109-99-9 1.00
CAS Result Amount Spiked %REC
2037-26-5 45.2 50.00 90.4
1868-53-7 51.3 50.00 103
460-00-4 42.3 50.00 84.5
17060-07-0 51.8 50.00 104
SW8260C
Analytical
Result Qual
< 1.00
Limits Qual
77-129
80-124
80-128
72-151
Report Date: 7/3/2012 Page 13 of26
All analyses applicable to the CW A, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COC. This report is provided for the exclusive use ofthe addressee. Privileges of
subsequent use of the name of this company or any member of its staft; or reproduction of this report in. c?nnection v:ith the adverti~ement, pro.motion or sale .of any product or pro.cess, or in connection with the re.-publication of t~is report for any
Client: Denison Mines
Lab Set ID: 1206379
Project: Seeps and Springs 2012
SampleID Analyte
LCS VOC 062612A Tetrahydrofuran
LCS VOC 062612A SUIT: 1,2-Dichloroethane-d4
LCS VOC 062612A SUIT: 4-Bromofluorobenzene
LCS VOC 062612A SUIT: Dibromofluoromethane
LCS VOC 062612A SUIT: Toluene-d8
463 West 3600 South
Salt Lake City, UT 84115
Phone: (801) 263-8686, Toll Free: (888) 263-8686, Fax: (801) 263-8687
e-mail: awal@awal-labs.com, web: www.awal-labs.com
_QC_SJJMMARX_RE_fQl~~I_
Contact: JoAnn Tischler
Dept: MSVOA
QC Type: LCS
Amount Original
Units Method Result Spiked Amount %REC Limits
IlglL SW8260C 16.0 20.00 0 80.1 43-146
%REC SW8260C 48.3 50.00 96.5 76-138
%REC SW8260C 42.2 50.00 84.5 77-121
%REC SW8260C 51.2 50.00 102 67-128
%REC SW8260C 45.2 50.00 90.5 81-135
%RPD
RPD
Limit
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Qual Date Analyzed
6/26/2012 713h
6/26/2012 713h
6/26/2012 713 h
6/26/2012 713h
6/2612012 713h
Report Date: 7/312012 Page 14 of26
I analyses applicable to the CWA, SDW A, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the name of this company or any
mber 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 company accepts no responsibility
Client: Denison Mines
Lab Set ID: 1206379
Project: Seeps and Springs 2012
Sample ID Analyte
MB VOC 062612A Tetrahydrofuran
MB VOC 062612A SUIT: 1,2-Dichloroethane-d4
MB VOC 062612A SUIT: 4-Bromofluorobenzene
MB VOC 062612A SUIT: Dibromofluoromethane
MB VOC 062612A SUIT: Toluene-d8
463 West 3600 South
Salt Lake City, UT 84115
Phone: (80l) 263-8686, Toll Free: (888) 263-8686, Fax: (80l) 263-8687
e-mail: awal@awal-Iabs.com, web: www.awal-Iabs.com
QC ___ SILM_MARY __ RE_PQRI __ _
Contact: JoAnn Tischler
Dept: MSVOA
QC Type: MBLK
Amount Original
Units Method Result Spiked Amount %REC Limits
/lglL SW8260C < 1.00
%REC SW8260C 49.6 50.00 99.2 76-l38
%REC SW8260C 42.7 50.00 85.3 77-121
%REC SW8260C 49.8 50.00 99.7 67-128
%REC SW8260C 45.2 50.00 90.5 81-135
%RPD
RPD
Limit
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Qual Date Analyzed
6/26/2012 804h
6/26/2012 804h
6/26/2012 804h
6/26/2012 804h
6/26/2012 804h
Report Date: 7/3/2012 Page 15 of 26
I 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 COCo This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the name of this company or any
mber 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 company accepts no responsibility
Client: Denison Mines
Lab Set ID: 1206379
Project: Seeps and Springs 2012
SampleID Analyte
1206379-001AMS Tetrahydrofiuan
1206379-001AMS Surr: 1,2-Dichloroethane-d4
1206379-001AMS Surr: 4-Bromofluorobenzene
1206379-001 AMS Surr: Dibromofluoromethane
1206379-001 AMS Surr: Toluene-d8
463 West 3600 South
Salt Lake City, UT 84115
Phone: (801) 263-8686, Toll Free: (888) 263-8686, Fax: (801) 263-8687
e-mail: awal@awal-labs.com, web: www.awal-labs.com
~£_BJIM_MARY ~POJ~~~I_
Contact: Jo Ann Tischler
Dept: MSVOA
QC Type: MS
Amount Original
Units Method Result Spiked Amount %REC Limits
/lglL SW8260C 14.4 20.00 0 72.0 43-146
%REC SW8260C 51.5 50.00 103 72-151
%REC SW8260C 41.5 50.00 83.0 80-128
%REC SW8260C 52.0 50.00 104 80-124
%REC SW8260C 45.0 50.00 90.1 77-129
%RPD
RPD
Limit
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Qual Date Analyzed
6/26/2012 945h
6/26/2012 945h
6/2612012 945h
6/2612012 945h
6126/2012 945h
Report Date: 7/3/2012 Page 16 of 26
I analyses applicable to the CWA, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the name of this company or any
mber 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 company accepts no responsibility
~.
Client: Denison Mines
Lab Set ID: 1206379
Project: Seeps and Springs 2012
Sample ID Analyte
1206379-001AMSD Tetrahydrofuran
1206379-001AMSD Surr: 1,2-Dichloroethane-d4
1206379-001 AMSD Surr: 4-Bromofluorobenzene
1206379-001 AMSD Surr: Dibromofluoromethane
1206379-001 AMSD Surr: Toluene-d8
463 West 3600 South
Salt Lake City, Dr 84115
Phone: (801) 263-8686, Toll Free: (888) 263-8686, Fax: (801) 263-8687
e-mail: awal@awal-labs.com, web: www.awal-Iabs.com
__ Q_C _S_UMMARY __ REl~QRI _
Contact: JoAnn Tischler
Dept: MSVOA
QC Type: MSD
Amount Original
Units Method Result Spiked Amount %REC Limits
IlgiL SW8260C 13.3 20.00 0 66.3 43-146
%REC SW8260C 49.9 50.00 99.8 72-151
%REC SW8260C 42.4 50.00 84.9 80-128
%REC SW8260C 51.9 50.00 104 80-124
%REC SW8260C 45.1 50.00 90.2 77-129
%RPD
8.24
RPD
Limit
25
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Qual Date Analyzed
6/26/2012 10 11 h
6/2612012 1011h
6/26/2012 1011h
6/26/2012 1011h
6/26/2012 1011h
Report Date: 7/3/2012 Page 17 of 26
I analyses applicable to the CWA, SDWA, and RCRA are performed in accordance to NELAC protocols. Pertinent sampling information is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of subsequent use of the name of this company or any
mber 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 company accepts no responsibility
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F10L3791.D
26 Jun 2012 8:29 am
AH
1206379-001A
SAMP 5.0ML 10F3 SB
6 Sample Multiplier: 1
Jun 26 08:42:14 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
!Abundance TIC: F10L3791.D\data.ms
I 28000001 I
1
2700000j
I
26000001.
2500000
2400000
2300000j I :~:::::I
I
20000001
19000001
1800000J
I 1700000j I I
16000001
I
15000001
1400000 1 I
13000001
i 1200000j
11000001
1
1000000j
900000.J
1
800000
I
7000001
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6000001
5000001
I
400000j
DFULLW_01.M Tue Jun 26 11:48:25 2012
CI) aj
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Page: 4
Report Date: 7/3/2012 Page 18 of26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F12L3792.D
26 Jun 2012 9:20 am
AH
1206379-002A
SAMP 5.0ML 10F3 SB
8 Sample Multiplier: 1
Quant Time: Jun 26 09:32:10 2012
Quant Method C:\MSDCHEM\1\METHODS\DFULLW_01.M
Quant Title VOA Calibration
QLast Update Fri May 18 13:38:02 2012
Response via Initial Calibration
(QT Reviewed)
Abundance , I TIC: F12L3792.D\data.ms
2700000j i
; 26000001
25000001
24000001
23000001
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22000001
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2100000i
I 20000001 i
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I ~ il'l 1300000j I
I g II 12000001 ~ I
I ~ I'
1100000j I
10000001 Ii
1 00
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7000001 j ! II
6000001 ~ ~ II
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_ L~,_~~illL _ ?~Q _~·OQ, __ ~~~JL'tQ9 __ 4_.,§O ~:Qg _ §~§Q ___ §._Q_Q~_.,§'Q_ Z.~QQ.. __ Z~§Q ____ ~.OQ §-!_§Q ~~QQ __ ~:§9_,lQJ)9 1QJ)g Uj)Jl l L§Q_
DFULLW_01.M Tue Jun 26 11:50:50 2012 Page: 4
Report Date: 7/3/2012 Page 19 of26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F15L3793.D
26 Jun 2012 10:36 am
AH
1206379-003A
SAMP 5.0ML 10F3 SB
11 Sample Multiplier: 1
Jun 26 10:48:25 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
Abundance-----------_. --------------------------------------TTc:-F15L3793~b\aata:ms -------------------------------------------------------
i
28000001
1 i
2700000j
26000001
2500000j
1 2400000j i
23000001
1
2200000j
I 2100000i
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20000001
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19000001
i 1800000j
1700000j
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16000001
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900000j
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DFULLW_01.M Tue Jun 26 11:55:40 2012
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Page: 4
Report Date: 7/3/2012 Page 20 of 26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F16L3794.D
26 Jun 2012 11:01 am
AH
1206379-004A
SAMP 5.0ML 10F3 SB
12 Sample Multiplier: 1
Jun 26 11:13:46 2012
C:\MSDCHEM\l\METHODS\DFULLW_Ol.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
Abundance
2800000j
TIC: F16L3794.D\data.ms
2700000j
26000001
25000001
i j
2400000 1
23000001
2200000 i 1
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2000000j
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DFULLW_Ol.M Tue Jun 26 11:56:34 2012 Page: 4
Report Date: 7/3/2012 Page 21 of 26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F17L3795.D
26 Jun 2012 11 :27 am
AH
1206379-005A
SAMP 5.0ML 10F3 SB
13 Sample Multiplier: 1
Jun 26 11:39:15 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
Abundance TIC: F17L3795.D\data.ms
,
2800000j
I
27000001
i 26000001
I
25000001
I
24000001 I I
2300000i
!
2200000i
j
21000001
20000001 i I 1900000i
I 18000001
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1500000j
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11000001 I
10000001
!
900000j
I
8000001
I
7000001 I
6000001
I
500000j
I
400000j I
1 300000j
en cD t: .:g a; E e g
15 E e .c is ::: :::> en
en g
11 a; e 0 :c .9 0 N.
:; en
200000j II
l,rl" i
...; "9 Q) t: ~ Q) J:J f J2 "fi
t.ri' ~
"'0
m Q, t: Q) N (I) t: en t:I5 Q) ..Q cD "'0 e Q, t: 0 Q) t: :c ~ Q) :::> () Q) (5 0 ..Q I--I--e
:; !l1 0 :::> en 15 E e III
:::> en
1000001 II II ii,
01. , 1 ' , , , ; , -TT-rrrrr..,.L\-·r·, )~~~--l--r!-n'-rT!.L~+TrT· ,~, T --.. ~:\... l--T',-i·~~i-T""F1"=fT=f"'''T'T::f::-F::;:'~rrl:=T'-l.:.:r=;:::l::::n::nl:::r::::;:';::::-;::f=:"-::~ ! [nr:DE:l-~._J~~Q ___ ?~Q.<L_,g:?_Q. _ ~9_9 __ .~~~ __ .~hQ9_._4.~Q._.§~gQ ___ ?~~g .'§:..QQ, .Sl...:.[Q_._2:QQ __ l .5Q _,_?~QQ .... ~.~,[Q_., ~. 00_. __ ~§'Q. __ 1Q~QJQ.:.?.Q __ l1&Q.. JL§Q._i
DFULLW_01.M Tue Jun 26 11:57:35 2012 Page: 4
Report Date: 7/3/2012 Page 22 of26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F07LCS20.D
26 Jun 2012 7:13 am
AH
LCS VOC 062612A
(QT Reviewed)
LCS SEE COVERSHEET FOR ID AND AMOUNTS JO
3 Sample Multiplier: 1
Jun 26 07:43:18 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
Abundance
4400000
---------------------------TIC:-F07LCS20.D\data~ms--------------------------------------------------------,
4200000
4000000
3800000
3600000
3400000
3200000
3000000
2800000
2600000
2400000
2200000
2000000
1800000
1600000
1400000
1200000 '
1000000 ,
800000 ,
i
600000 1
400000 ,
I
200000!
i I,
0:: ~-~ I ~ C$
i ~ III ~ E e 0
Q) .a ~ ~Q)§ ,-IQ) Q)~:C: ~ ~fij 5-E·g E~I-~ ,..:~ 0'-£ g ~O Cll::E () UJ -c .2
01;, I
Q) I:: Q)I/) -<:1:: ~ ~I o --
0-<: -<:0 I i~
-B ~~ ~ t:~ <[I 2<
0::_
iii
I -£ fr
!I
i
I' f ~ "I £!. .. I Jl. ,-
'I I 'I I
[lrrr~:? __ L~Q __ ~~QQ _ _?_~~Q _~Q9__~~§_Q __ 1~QJL ___ 'L~Q ____ §~QQ _____ §~§Q __ J~&Q ___ ~§Q __ L9~_.L~Q __ ~OO _Jh~ ___ 9.00 ___ ~~50 __ JQ~~L1Q~~Q .J _1.0(L 1 L§Q._
DFULLW_01.M Tue Jun 26 07:43:42 2012 Page: 4
Report Date: 7/3/2012 Page 23 of 26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Abundance
2800000 1
I 2700000 !
I
26000001 :
2500000 j
i
2400000 j
2300000 j
j
2200000 1
1 2100000 1
1
20000001
19000001
18000001
1700000i
1600000i
1500000j
1400000i
i 1300000i I I
1200000i
1
11000001
10000001
!
900000\
8000001
700000 !
6000001
500000 )
J
400000 1
300000 ]
200000\
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F09LMBLK.D
26 Jun 2012 8:04 am
AH
MB VOC 062612A
MBLK 5.0ML JO
5 Sample Multiplier: 1
Jun 26 08:15:54 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
TIC: F09LMBLK.D\data.ms
CIl ai a: c ~ "0 I-::: ::l en
en ~ nI .s::: en a; E cD c E nI g .s::: a; '5 E E 0
E :c: ,!.! .c Cl is ~. ::: ::l en 15 en
o.ri' "0 d> c Q) ~ Q) ..c E .2 .s::: 0
Cl I-!:Q
!I
Ii
!I !I
en cD c Ql N C Ql ..c E 0 ::l '5 E E In
::l en
..r -0 d> c re c Q) ..c ~ ~ qi
'1.
m
I I
'I
1000001 I
] 0.1 i ' I ~-. -, -, -'~T,~~,)L!L, 'rr,J,LCT~~,A-r~~-'-'-'''''''T".:r''-l='F"i'''i'T"=]=l=T'l':.r~:::;=;C::T'::;=~':::]':~:'::;=~:::;::T:;::'~:::-~:':';-:::;::;:::;: i [l~~:-~~_.t2.Q ___ .?~Qg __ .~~~L ... ;1:00 ._~_.:§Q ... _~LQQ __ . ..t§Q,-.§.:Q.Q ,-?~2.Q. __ .§..QQ. __ §.:.5J2...l.:.QJL .. l~9 ._~:9Q __ -,J3_&Q_ . ~~QQ ____ ~50_J O:OQ. _J9~5.Q~1~Q_ 1:L~Q_i
DFULLW_01.M Tue Jun 26 11:47:03 2012 Page: 4
Report Date: 7/3/2012 Page 24 of26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F13S3791.D
26 Jun 2012 9:45 am
AH
1206379-001AMS
MS 5.0ML 10F3 SB
9 Sample Multiplier: 1
Quant Time: Jun 26 11:52:10 2012
Quant Method C:\MSDCHEM\1\METHODS\DFULLW_01.M
Quant Title VOA Calibration
QLast Update Fri May 18 13:38:02 2012
Response via Initial Calibration
(QT Reviewed)
Abundance TIC: F13S3791.D\data.ms
4000000
3800000
3600000,
3400000!
3200000!
!
3000000:
i
I 2800000 :
i
I
2600000
2400000
2200000
2000000
1400000
1200000
1000000
8000001
600000
400000
20
a) c: ~ Q) ..0 e o ::l u::
Cl ~
en
fI) ~ cxi "C CD N cD c: c: CD CD ..0 ::l e 15 0 r-::l
::l '5 E en e al
~ en
I 1'1 L§Q __ ~Q~ ___ ?~_§Q ___ ;tQ_Q __ ~~~_Q ___ 4JlQ ___ 4J5.Q __ §~QQ ___ 5.50 ___ '§~QQ __ §.:_~!L L 9_Q ___ I 5Q ___ !!.gQ_
DFULLW_Ol.M Tue Jun 26 11:52:39 2012 Page: 4
Report Date: 7/3/2012 Page 25 of 26
Data Path
Data File
Aeq On
Operator
Sample
Mise
ALS Vial
Quant Time:
Quant Method
Quant Title
QLast Update
Response via
Abundance
3800000
3
2800000
1800000
II: aD 6()O()()()iS< ~
I 4Q!OOIJOifi [i
Quantitation Report
C:\msdehem\1\data\JUN12-D\26JUN12\
F14D3792.D
26 Jun 2012 10:11 am
AH
1206379-001AMSD
MSD 5.0ML 10F3 SB
10 Sample Multiplier: 1
Jun 26 11:53:41 2012
C:\MSDCHEM\1\METHODS\DFULLW_01.M
VOA Calibration
Fri May 18 13:38:02 2012
Initial Calibration
(QT Reviewed)
TIC: F14D3792.D\data.ms
'" (J) cO <D "9 <:
Q) :!l <: <: Q) Q) ::J .0 '0 E f-0 ::J
::J '5 (J) E E m t: ::> (J)
I I iIlr:D~_~-~ ___ L~!L.1~QQ ____ g_&~ __ ~JlJL ~~~Q ___ ~QQ___ 1_~§_Q ____ 5.0~ __ ~~§~ ____ §~QQ __ 6.5<l ___ L~ __ 7 .5Q_J3~QQ ___ ~~~_Q __ ~~QQ ___ 9.50 __ JQ_~QQ __ 1Q!?~ J1JlQ __ l 1&9_!
DFULLW_01.M Tue Jun 26 11:54:04 2012 Page: 4
Report Date: 7/3/2012 Page 26 of 26
American West Analytical Laboratories
WORK ORDER Summary
Client:
Client ID:
Project:
Denison Mines
DEN 1 00
Seeps and Springs 2012
Contact: JoAnn Tischler
QC Level: LEVEL III
UL
Denison
Work Order: 1206379
Page 1 of 1 6/22/2012
WOType: Project
Comments: PA Rush. QC 3 & Summary. EDD-EIM into Locus Database. Report THF to 1 /lglL. Samples for metals are field filtered.; l)f>
Sample ID
1206379-001A
1206379-001B
1206379~002A
1206379-002B
1206379~003A
1206379-003B
1206379-004A
1206379-004B
1206379-00SA
Client Sample ID
Entrance Seep
SEL Analytes: SN
Ruin Spring
SEL Analytes: SN
Cottonwood Spring
SEL Analytes: SN
Back Spring
SEL Analytes: SN
Trip Blank
Collected Date
6/20/2012 10 15h
6120/20120920h
6/20120120745h
6/20/2012
FOR LABORATORY USE ONLY [fill out on page 1]: %M ~ RT l!f eN
Received Date Date Due
6122/20121030h 7/3/2012
---
Matrix Test Code Sel Storage
Aqueous 8260-W ~ VOCFridge 3
200.8~DIS ~ df ~ dis met
8260~W ~ VOCFridge 3
200.8-DIS ~ df ~ dis met
8260-W ~ VOCFridge 3
200.8-DIS ~ df ~ dis met
8260-W ~ VOCFridge 3
200.8-DIS ~ df ~ dis met
8260-W ~ VOCFridge 3
HOK __ HOK __ _
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: American West Analytical Lab
463 West 3600 South
Contact: Garrin Palmer or David Turk
Ph: 4356782221
p . t rOJec
Seeps and Springs
2012
Sample 10
Enterance Seep
Ruin Spring
Cottonwood Spring
Back Spring
Trip Blank
Salt Lake City, Ut 84115 goalmer@denisonmines.com
dturk@denisonmines.com
thol! iday@denisonmines.com
Chain of Custody/Sampling Analysis Request
S amp ers N arne s amp ers Ignature
Tanner Holliday 0~)fJJk
'-./
Date Time
Collected Collected Laboratory Analysis Requested
6/20/2012 1015 THF, TIN
6/20/2012 920 THF, TIN
6/20/2012 745 THF, TIN
6/20/2012 745 THF, TIN
6/20/2012
0~~~c\ Ti\\ rD L-Ltl:tl '~
r D--L~ i()~ ~rvcicl.d ~ u ;iY(2-, ~h,I2-'2.J l~
'/
~t\Q~ ~ -\-~l ~~ \,~ \d ..
+=t \~ N"€d oL\\ ~~ *-l'\._t \ l .. t~e 1 \l\e.'\ .-DlS t:. 11-21/ 12.
I J I
Please notify Garrin Palmer or Tanner Holliday of Reciept tempature on these samples Immediately!
Thank you.
Relinquished By:(Signature)
.::J dflN/L-J/.,r I ~/n"UflA/,"
DatelTime Received By:(Sig
6/21/2012
1100
DatelTime
Lab Set ID t2tXo~l9
SallJ.ples Were: coe Tape Was: Container Type:
l!J"Shipped By: Re\ ~"L prezon Outer Package D A W AL Supplied Plastic /
D Hand Delivered I !D es DNa D NI A D A W AL Supplied Clear Glass /
D Al]).biel'lt Unb~ on Outer package D A WAL Supplied Amber Glass / ~lilled ~Yes DNo DN/A
Temperature ti.1S DC presen~ Sample
o A WAL Supplied VOA/=X Vials
D Amber D Clear D Head ace DNo Headspace
Rec. Broken/Leaking DYes B1'fo DN/A D Yes No DN/A D N on A W AL SUjJpl»x(Contailler
Notes:
Properly Preserved
Notes:
Rec. Within Hold
Notes:
Bottle Type
Ammonia
COD
Cyanide
Metals
N02 &N03
Nutrients
O&G
Phenols
Sulfide
TKN
TOC
TP04
TPH
Procedure: 1)
2)
3)
4)
5)
6)
7)
/'
unbroken~ Sample
DYes rn 0 ON/A
~es DNo DN/A Notes:
/ ~es DNo
Preservative All pHs OK '""CD\ -002-
pH <2 I-hS04
pH <2 H2SO4
PH>12 NaOH
pH<2HN03 \/P.e, ~~
pH <2 H2SO4 I -,
pH <2 H2SO4
pH<2HCL
pH <2 H2SO4
pH> 9NaOH, ZnAC
pH <2 H2SO4
pH <2 H3P04
pH <2 H2SO4
pH <2HCL
~
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
-oo? --00-\
l"\l~ \t?b , r
/
Discrepancies Between Labels and COC
Notes:
If sample is not preserved properly list its extension and receiving pH in the appropriate column above
Flag eoe and notify client for further instructions
Place client conversation on coe
Samples may be adjusted at client request
tL
;.Mo. Rec. II
I
DYes [)..MD·
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Jo Ann Tischler
Denison Mines
1050 17th Street, # 950
Denver, CO 80265
TEL: (303) 389-4132
RE: Seeps and Springs 2012
Dear JoAnn Tischler: Lab Set ill: 1207214
American West Analytical Laboratories received 4 sample(s) on 7/16/2012 for the
analyses presented in the following report.
American West Analytical Laboratories (AWAL) is accredited by The National
Environmental Laboratory Association Conference (NELAC) Institute in Utah and Texas;
and is state accredited in Colorado, Idaho, New Mexico, and Missouri. In addition,
A W AL is also accredited by the American Analytical Laboratory Association (A2LA) on
ISO IEC 17025:2005, Department of Defense (DOD), UST for the State of Wyoming, and
the National Lead Laboratory Accreditation Program (NLLAP). All analyses were
performed in accordance to The NELAC Institute andlor A2LA protocols unless noted
otherwise. Accreditation 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, andlor
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, f'i Kyl e F '~ D;g""y,;g",dbyK"".G,~,
\DN: cn=Kyle F. Gross, o=AWAL,
9.u=AWAL, email=kyle@awal-
G l labs.com, c=us r 0 S S />_"Daie: 2(jj~23 14:09:42 -06'00'
ZI Approved by:
Laboratory Director or designee
Report Date: 7/23/2012 Page 1 of7
All analyses applicable to the CWA, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infom1ation is located on the attached COc. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use oft~e name of this company or any member of its staff, or reproduction of this report in. connection with the adverti~ement, pro.motion or sale of any product or process, orin connection with the re.-publication ofthis report for any
American West
ANALYTICAL LABORATOR IES
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
SAMPLE SUMMARY
Client:
Project:
Lab Set ID:
Denison Mines
Seeps and Springs 2012
1207214
Date Received: 7/16/2012945h
Lab Sample ID Client Sample ID
1207214-001A Enterance Seep
1207214-002A Ruin Spring
1207214-003A Cottonwood Spring
1207214-004A Back Spring
Contact: JoAnn Tischler
Date Collected Matrix Analysis
6/2012012 1015h Aqueous-ICPMS Metals, Dissolved
612012012 920h Aqueous-ICPMS Metals, Dissolved
6/20/2012 745h Aqueous-ICPMS Metals, Dissolved
612012012 745h Aqueous-ICPMS Metals, Dissolved
Report Date: 7/23/2012 Page 2 of 7
All analyses applicable to. the CWA, SDW A, and RCRA are perfo.nned in acco.rdance to. NELAC pro.to.co.ls. Pertinent sampling info.nnatio.n is Io.cated o.n the attached CDC. This repo.rt is provided fo.r the exclusive use o.fthe addressee. Privileges o.f
subsequent use o.f the name o.fthis co.m)Jany o.r any member o.f its staff, o.r repro.ductio.n o.f this repo.rt in. c~nnectio.n ,,:,ith the adverti~ement, pro.mo.tio.n o.r sale of any product or process, o.r in co.nnectio.n with the re.-publicatio.n o.f t~is repo.rt fo.r any
American West ANA LYTI CA L LAB ORATORIES
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801)263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
Inorganic Case Narrative
Client:
Contact:
Project:
Lab Set ID:
Sample Receipt Information:
Date of Receipt:
Date of Collection:
Sample Condition:
C-O-C Discrepancies:
Denison Mines
Jo Ann Tischler
Seeps and Springs 2012
1207214
7116/2012
6/20/2012
Intact
None
Holding Time and Preservation Requirements: The analysis of all samples was
performed within the method holding times. All samples were properly preserved.
Preparation and Analysis Requirements: The samples were analyzed following the
methods stated on the analytical reports. The samples were not digested pursuant to the
client request.
Analytical QC Requirements: All instrument calibration and calibration check
requirements were met. All internal standard recoveries met method criterion.
Corrective Action: None required.
Report Date: 7/23/2012 Page 3 on
All analyses applicable to the CWA, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COc. This report is provided for the exclusive use of the addressee. Privileges of
subsequent useoft~e name of this company or any member of its staff? or reproduction ofthis report in c?nnection with the adverti~ement, pro.motion or sale.of any product or process, orin connection with the re.-publication of this report for any
INORGANIC ANALYTICAL REPORT
American West ANALYT ICAL LABORATORIES
463 West 3600 South
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1207214-001
Client Sample ID: Enterance Seep
Collection Date: 6/2012012 1015h
Received Date: 711612012 .945h
Analytical Results
Compound Units
Date
Prepared
~alt Lake City, UT 84115 Tin mgIL
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
This sample was not digested pursuant to the client request.
Date
Analyzed
7/2112012 1844h
Contact: Jo Ann Tischler
Method
Used
E200.8
DISSOLVED METALS
Reporting
Limit
0.p0500
Analytical
Result
< 0.00500
Qual
Report Date: 7/23/2012 Page 4 of7
All analyses applicable to the CWA, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infoffilation is located on the attached COc. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use oft~e name of this comjlany or any member of its staff, or reproduction of this report in. c?nnection v:ith the advertisement, pro.motion or sale .of any product or process, or in connection with the re.-publication oft?is report for any
INORGANIC ANALYTICAL REPORT
American West
ANALYTI CAL LABOR ATO RIES
463 West 3600 South
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1207214-002
Client Sample ID: Ruin Spring
Collection Date: 6120/2012 920h
Received Date:
Analytical Results
Compound
7116/2012 945h
Units
Date
Prepared
;alt Lake City, UT 84115 Tin mg/L
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha.
QA Officer
This sample was not digested pursuant to the client request.
Date
Analyzed
712112012 1849h
Contact: Jo Ann Tischler
Method
Used
E200.8
DISSOLVED METALS
Reporting
Limit
0.00500
Analytical
Result
< 0.00500
Qual
Report Date: 7/23/2012 Page 5 of 7
All analyses applicable to the CW A, SDW A, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COCo This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of the name of this company or any member of its staff, or reproduction of this report in. c?nnection with the adverti~ement, pro.motion or sale .of any product or process, orin connection with the re.-publication ofthis report for any
INORGANIC ANALYTICAL REPORT
American West ANALYTICAL I.ABORATORt ES
463 West 3600 South
Client:
Project:
Lab Sample ID:
Denison Mines
Seeps and Springs 2012
1207214-003
Client Sample ID: Cottonwood Spring
Collection Date: 6/20/2012 745h
Received Date:
Analytical Results
Compound
7/16/2012 945h
Units
Date
Prepared
;alt Lake City, UT 84115 Tin mg/L
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-rnail: awal@awal-labs.com
web: www.awal-labs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
This sample was not digested pursuant to the client request.
Date
Analyzed
7/2112012 U~53h
Contact: Jo Ann Tischler
Method
Used
E200.8
DISSOLVED METALS
Reporting
Limit
0.00500
Analytical
Result
< 0.00500
Qual
Report Date: 7/23/2012 Page 6 of7
All analyses applicable to the CWA, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COe. This report is provided for the exclusive use of the addressee. Privileges of
subsequent use. of the name of this com~any or any member of its staff, or reproduction of this report in. c?nnection with the adverti~ement, pro.motion or sale of any product or process, or in connection with the re.-publication of t~is report for any
463 West 3600 South
;alt Lake City, UT 84115
Phone: (801) 263-8686
Toll Free: (888) 263-8686
Fax: (801) 263-8687
~-mail: awal@awal-Iabs.com
web: www.awal-Iabs.com
Kyle F. Gross
Laboratory Director
Jose Rocha
QA Officer
INORGANIC ANALYTICAL REPORT
Client: Denison Mines
Project:
Lab Sample ID:
Seeps and Springs 2012
1207214-004
Client Sample ID: Back Spring
Collection Date: 6/20/2012 745h
Received Date: 7/16/2012 945h
Analytical Results
Compound Units
Tin mglL
Date
Prepared
This sample was not digested pursuant to the client request.
Date
Analyzed
712112012 1858h
Contact: JoAnn Tischler
DISSOLVED METALS
Method Reporting Analytical
Used Limit Result Qual
E200.8 0.00500 < 0.00500
Report Date: 7/23/2012 Page 7 of 7
All analyses applicable to the CW A, SDWA, and RCRA are perfonned in accordance to NELAC protocols. Pertinent sampling infonnation is located on the attached COe. This report is provided for the exclusive use of the addressee. Privileges of
subsequent useofthe name of this company or any member of its staff, or reproduction of this report in. c?nnection v:ith the advertisement, pro.motion or sakof any product or pro~ess, orin connection with the re.-publication of this report for any
American West Analytical Laboratories
WORK ORDER Summary
Client:
Client ID:
Denison Mines
DEN100 Contact: Jo Ann Tischler
Project: Seeps and Springs 2012 QC Level: LEVEL III
UL
Denison
Work Order: 1207214
Page 1 of 1 7/19/2012
WOType: Project
Comments: PA Rush. QC 3 & Summary. EDD-EIM into Locus Database. Metals Split. Samples are were field filtered.; ~
Sample JD Client Sample ID
1207214-001A Enterance Seep
SEL Analytes: SN
1207214-002A Ruin Spring
SEL Analytes: S~ __________ _
1207214-003A Cottonwood Spring
SEL Analytes: SN
1207214-004A Back Spring
SE!: Analytes: SN
FOR LABORATORY USE ONLY [fill out on page 1]: %M [IJ" /' RT 0
Collected Date Received Date Date Due Matrix Test Code Sel Storage
6/20/20121015h 7/16/20120945h 7/26/2012 Aqueous-Dissolved 200.8-DIS ~ df -metals
6/20/20120920h 200.8-DTS ~ df -metals
6120120120745h 200.8-DTS ~ df -metaJ~------
200.8-DTS ~ df-metals
CN 0"" T AT ~/ QC [!1~ . HOK_~ HOK_~ HOK ___ _
! 2 0 jlllj till Chain of Custody and Analytical Request Record
PLEASE PRINT Provide as much information as r-C-o-m-p-an-y'7"':N-am-e-; -----~---------,-=-;P~ro~je=-=c';=;t N:7':a~m~e~, PWS. Permit, Etc.
'ii3'3fR
D~n\'.sDn M\'ne~ Se ;2,.0\2. U'i
Report Mail Address: Contact Name: Phone/Fax: Email:
B )"I',}, ; 110. 'PO 1$\ B t>~ 4 J i'1. (n·.(" " ? "'\ M c ( '-\llS (" 7 t ;l:2;J.. \
Invoice Address: ::::oJ I Invoice Contact & Phone: S~~ D~~~~ ~rv.. L\~S G,18 ~!
Purchase Order:
Page --L-of ~
EPA/State Compliance:
Yes b(J No 0
Sampler: (Please Print)
~l\~r ~oll:JA ~
Quote/Bottle Order:
~ Special Report/Formats: .1 Contact ELI prior to -SllIj:ij)ecll:ly:
RUSH sample submittal f£;)/f)~
DDW o EDD/EDT(Electronic Data) o POTWNVWTP o State: ----o Other: ----
Format: ___ _ o LEVEL IV o NELAC
a '-~Otl)~ ~ro;:g 012 ._> 0 >-co aCf)~ rn:::-C !:!!. tI» 0S:'O ro O'l U .-<I.lI.Q .S ~ ....... ,,-COI1§
0'0(1) c;::.-
R I for charges and
scheduling -See
Instruction Page
U I Comments:
~ ... &~.QQ ~!t6 I
(l) .... 1i)s: ~ . -.
Cooler 10(s):
G J\4n f
Receipt Temp
~. ? °C
On lee: 0 N L :i11«I~o ~ I WI" ;) ICus_SeaI
I SAMPLE IDENTIFICATION I Collection I ColI~tion MATRIX <8 I I I , IM':t~h'u,,, ~ N
I (Name, Location, Interval, etc.) Date TIme --+ . . .. -.------1
1 "C",t~MCe.. S-ee.p b/:;"O/r;)... )D\~ b~W 'i I~
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~~~~':::::::::-""~~~~~~.¥,~---;f---+~~~~~~:!:"~~~!LJ-I~~--,-q.....:.-....L' '{5 ~9L J3r LAlA~V'\~---I R eco rd Signature: -----
MUSTb~~~~~~~~~~~~--~
S i 9 ned Return to Client: Lab Disposal: ~'''==*'=-_ .... _________ ... ""'"' .... _____ .-.:~
In certain circumstances. samples submitted to Energy Laboratories, Inc. may be subcontracted to other certified laboratories in order to complete the analysis requested.
This serves as notice of this possibility. All sub~contract data will be clearly notated on your analytical report.
Visit our web site at wwW.energylab.com for additionallnformatiorl, downloadable fee schedule, forms. and links.
Lab Set ID' \ 2012.\L\
Samples Were: COC Tape Was: Container Type:
rn--shipped B y: 'Fe.c~r >f.. Present on Outer Package D A W AL Supplied Plastic
D Band Delivered , DYes ffNo DN/A D A W AL Supplied Clear Glass /
llVAmbient Unbroken on Outer package D A W AL Supplied Amber Glass /
D Chilled DYes D No G1f/A
Temperature 111 2~ °C / Present on$ample
DYes ~o DN/A
o A WAL Supplied VOA~=iaIS
D Amber D Clear D Heads e DNo Headspace
Rec. Broken/Leaking DYes ~o DN/A D Non A W AL Supplie~'Ontainer
Notes:
Properly Preserved
Notes:
Rec. Within Hold
Notes:
Bottle Type
Ammonia
COD
Cyanide
Metals
N02 &N03
Nutrients
O&G
Phenols
Sulfide
TKN
TOC
TP04
TPH
Procedure: 1)
2)
3)
4)
5)
6)
7)
Unbroken on sa~le
DYes DNo . N/A / ~Yes DNo DN/A Notes:
/
If Yes . DNo
Preservative All pHs OK
pH <2 H2SO4
pH <2 H2SO4
PH >12 NaOH
pH <2HN03
pH <2 H2SO4
pH <2 H2SO4
pH <2HCL
pH <2 H2SO4
pH> 9NaOH, ZnAC
pH <2 H2SO4
pH <2 H3P04
pH <2 H2SO4
pH <2HCL /V
/
//
/'
.... V
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
//
/'
//
/
/ .
Discrepancies Between Labels and COC
Notes:
I •
~ -,Il\ill V2-
/ I 1\
/
/
/
/
/ / LV
/
If sample is not preserved properly list its extension and receiving pH in the appropriate column above
Flag eoe and notify client for further instructions
Place client conversation on eoe
Samples may be adjusted at client request
~7n~l~
No%c. I ,
V
DYes ~o
TabE
Quality Assurance and Data Validation Tables
Table E-l Holding Time Evaluation
Back Spring
.Required Holding Time Entrance Westwater Cottonwood Ruin Spring (duplicate Of
Seep Seep Seep Cottonwood
Seep)
Major Ions
Carbonate 14 days OK OK OK OK
Bicarbonate 14 days OK OK OK OK
Calcium 6 months OK OK OK OK
Chloride 28 days OK OK OK OK
Fluoride 28 days OK OK OK OK
Magnesium 6 months OK OK OK OK
Nitrogen-Ammonia 28 days OK OK OK OK
Nitrogen-Nitrate 28 days OK OK OK OK
Potassium 6 months OK Not Sampled OK OK OK
Sodium 6 months OK -Dry OK OK OK
Sulfate 28 days OK OK OK OK
pH (s.u.) N/A OK OK OK OK
TDS 7 days OK OK OK OK
6 months (except
mercury which is 28
Metals days) OK OK OK OK
Radiologies 6 months OK OK OK OK
VOCS (including THF) 14 days OK OK OK OK
E-2 Laboratory Receipt Temperature Check
Work Order' Number/Lab Set ill
Receipt Temp
EL -C12060931 2.2°C
A WAL -1206379 (THF and Tin) 4.5°C
AWAL -1207214 (Tin) N/A
N/ A = These shipments contained samples for the analysis of tin only.
Per Table 1 in all revisions of the approved QAPs that were in effect
during this sampling period, (Revisions 6, 7.1 and 7.2),samples
submitted for tin analyses do not have a sample temperature
requirement.
E-3: Analytical Method Check -Routine Samples
Parameter QAP/Permit . Method Method Used by Lab
Ammonia (as N) A4500-NH3 G or E350.1 A4500-NH3 G
Nitrate + Nitrite (as N) E353.1 or E353.2 E353.2
Metals except Iron E 200.7 or E200.8 E200.8
Iron E 200.7 or E200.8 E200.7
Gross Alpha E900.0 or E900.1 E900.1
VOCs except Tetrahydrofuran SW8260B or SW8260C SW8260B
Tetrahydrofuran SW8260B or SW8260C SW8260C
Chloride ~4500-CI B, A4500-CI E, or E300.0 A4500-CI B
Fluoride A4500-F C or E300.0 A4500-F C
Sulfate A4500-S04 E or E300.0 A4500-S04 E
TDS , A2540 C A2540 C
Carbonate as C03, Bicarbonate as HC03 A2320 B A2320 B
Calcium, Magnesium, Potassium, Sodium E200.7 E200.7
E-4 Reporting Limit Evaluation
Parameter
Ammonia (as N)
Nitrate + Nitrite (as N)
Metals uglL
Arsenic
Beryllium
Cadmium
Chromium
Cobalt
Copper
Iron
Lead
Manganese
Mercury
Molybdenum
Nickel
Selenium
Silver
Thallium
Tin
Uranium
Vanadium
Zinc
Gross Alpha
VOCs uglL
Acetone
Benzene
Carbon tetrachloride
Chloroform
Chloromethane
MEK
Methylene Chloride
Naphthalene
T etrahydrofuran
Toluene
Xylenes
Major Ions mglL
Chloride
Fluoride
Sulfate
TDS
Carbonate as C03, Bicarbonate as RC03
Calcium, Magnesium, Potassium, Sodium
All analyses were reported to the required
RLs unless noted in the text.
Permit-Specified
25 mg/L
10 mg/L
50
4
5
100
730
1300
11000
15
800
2
40
100
50
100
2
17000
30
60
5000
15
700
5
5
70
30
4000
5
100
46
1000
10000
1
4
1
10
Not Specified
Not Specified
RL
E-5: Trip Blank Evaluation
All trip blanks for the 2012 sampling program were nondetect.
,.
Blank Sample Date Laboratory
1 6/20/2012 AWAL
2 6/20/2012 EL
E-6 Duplicate Sample Relative Percent Difference
, Back Spring
Major Ions (mg/l) Cottonwood Spring (Duplicate of RPD%
Cottonwood Spring)
Carbonate <1 <1 N/C
Bicarbonate 326 326 0.0
Calcium 101 93.8 7.4
Chloride 149 121 20.7
Fluoride 0.38 0.38 0.0
Magnesium 27.7 25.5 8.3
Nitrogen-Ammonia <0.05 <0.05 N/C
Nitrogen-Nitrate <0.1 <0.1 N/C
Potassium 6.2 6.2 0.0
Sodium 247 223 10.2
Sulfate 356 366 2.8
pH (s.u.) 7.06 7.06 0.0
TDS 1040 1040 0.0
Metals, (ug/l)
Arsenic <5 <5 N/C
Beryllium <0.5 < 0.5 N/C
Cadmium <0.5 <0.5 N/C
Chromium <25 <25 N/C
Cobalt <10 <10 N/C
Copper <10 <10 N/C
Iron <30 <30 N/C
Lead <1.0 <1.0 N/C
Manganese <10 <10 N/C
Mercury <0.5 <0.5 N/C
Molybdenum <10 <10 N/C
Nickel <20 <20 N/C
Selenium <5 <5 N/C
Silver <10 <10 N/C
Thallium <0.5 <0.5 N/C
Tin <100 <100 N/C
Uranium 8.17 8.56 4.7
Vanadium <15 <15 N/C
Zinc <10 <10 N/C
Radiologies (pC ill)
Gross Alpha <-0.2 <0.07 N/C
.'. VOCS (ug/L)
Acetone ND ND N/C
Benzene ND ND N/C
Carbon tetrachloride ND ND N/C
Chloroform ND ND N/C
E-6 Duplicate Sample Relative Percent Difference
Back Spring
Major Ions (mg/l) Cottonwood Spring (Duplicate of RPD%
Cottonwood Spring)
Chloromethane ND ND N/C
MEK ND ND N/C
Methylene Chloride ND ND N/C
Naphthalene ND ND N/C
Tetrahydrofuran ND ND N/C
Toluene ND ND N/C
Xylenes ND ND N/C
E-7 Radiologies Counting Error
Gross Alpha
Sample,ID minus Rn & U
Entrance Seep 0.5
Westwater Seep NS
, Cottonwood Seep <-0.2
Ruin Spring <-0.09
Ii. Back Spring
, (duplicate of
Cottonwood Seep) <0.07
NS -Westwater Seep was dry and not
sampled 2012
'Gross Alpha " COl!nting,
rri,inus Rn &U Error ~
Precision (±) 20%
0.4 NA
NS NA
0.2 NA
0.3 NA
0.3 NA
,
Within
'GWQS GWQS
15 NA
15 NA
15 NA
15 NA
15 NA
E-8: Laboratory Matrix QC
Matrix Spike % Recovery Comparison
MSD REC
Lab Report Well . Analyte MS %REC %REC Range RPD
Cottonwood
C12060931 Spring Benzene 144 95 70-130 41
Cottonwood
C12060931 Spring Chloromethane 74 94 70-130 23
Cottonwood
C12060931 Spring Toluene 146 108 70-130 30
C12060931 N/A Carbon Tetrachloride 96 48 70-130 66
C12060931 N/A Chloromethane 130 145 70-130 10
C12060931 N/A Toluene 109 232 70-130 66
NA = MS samples were not Denison samples.
Surrogate % Recovery
Lab QAP
Surrogate Specified Required
Lab Report Well/Sample Analyte %REC REC Range Range
C12060931 Entrance Spring 1,2-Dichlorobenzene 126 80 -120 None
C12060931 Entrance Spring p-Bromofluorobenzene 146 80 -120 None
C12060931 Ruin Spring 1,2-Dichlorobenzene 122 80 -120 None
C12060931 Ruin Spring p-Bromofluorobenzene 140 80 -120 None
C12060931 Cottonwood Spring 1,2-Dichlorobenzene 122 80 -120 None
C12060931 Cottonwood Spring p-Bromofluorobenzene 138 80 -120 1 None
C12060931 Back Spring p-Bromofluorobenzene 133 80 -120 None
C12060931 Trip Blank 1,2-Dichlorobenzene 121 80 -120 None
C12060931 Trip Blank p-Bromofluorobenzene 138 80 -120 None
C12060931 Method Blank 1,2-Dichlorobenzene 121 80 -120 None
C12060931 Method Blank p-Bromofluorobenzene 136 80 -120 None
Cottonwood Spring
C12060931 (Matrix Spike) Toluene-d8 171 80 -120 None
Cottonwood Spring
(Matrix Spike
C12060931 Duplicate) Toluene-d8 123 80 -120 None
C12060931 Method Blank 1,2-Dichlorobenzene 121 80 -120 None
C12060931 Method Blank p-Bromofluorobenzene 132 80 -120 None
N/A (Matrix Spike
C12060931 Duplicate) Toluene-d8 233 80 -120 None
NA = MS samples were not Denison samples.
Method/Laboratory Reagent Blank detections
Reported
Lab Report Well/Sa·mple . Analyte Concentration
C12060931 MB Bicarbonate 1.62 mglL
Kathy Weinel
From:
Sent:
To:
Cc:
Subject:
Attachments:
Mr. Lundberg,
Kathy Weinel
Wednesday, November 21 , 2012 8:52 AM
'rlundberg @ utah.gov'
Dean Henderson; 'Phillip Goble'; Harold Roberts; David Frydenlund; Jo Ann Tischler; Jaime
Massey; David Turk; N. Tanner Holliday; Garrin Palmer
Transmittal of CSV Files White Mesa Mill 2012 Seeps and Springs Monitoring
C12060931.csv; 1207214-EDD.csv; 1206379-EDD.csv
Attached to this e-mail are electronic copies of laboratory results for annual seeps and springs monitoring conducted at
the White Mesa Mill during 2012, in Comma Separated Value (CSV) format.
Please contact me at 303-389-4134 if you have any questions on this transmittal.
Yours Truly
Kathy Weinel
1
TabG
DRC Correspondence Regarding Annual Seeps and Springs Reports and Data Use
This attachment has been intentionally left blank.
2