DRC-2014-005081 - 0901a06880484d9d

ENERGYFUELS
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.energyfuels.com
August 29, 2014
VIA OVERNIGHT DELIVERY DRC-2014-005081
Mr. Rusty Lundberg
Director of the Utah Division of Radiation Control
State of Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144850
Salt Lake City, UT 84116-4850
Dear Mr. Lundberg:
Re: State of Utah Radioactive Material License No. UT1900479
White Mesa Mill, Blanding, Utah
Semi-Annual Effluent Monitoring Report for Period
January 1 through June 30,2014
As required by Utah Administrative Code, R 313-24-4 (incorporating by reference 10 CFR 40.65
(subpartl)), and License Condition 11.3A of State of Utah Radioactive Materials License No.
UT 1900479, enclosed is the Semi-Annual Effluent Monitoring Report for the White Mesa Mill
for the period January 1, 2014 through June 30, 2014.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
Yours very truly,
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Harold R. Roberts
David E. Turk
Frank Filas
Jaime Massey
August 29, 2014
VIA OVERNIGHT DELIVERY
Mr. Rusty Lundberg
Director of the Utah Division of Radiation Control
State of Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144850
Salt Lake City, UT 84116-4850
Dear Mr. Lundberg:
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www .energyfuels.com
Re: State of Utah Radioactive Material License No. UT1900479
White Mesa Mill, Blanding, Utah
Semi-Annual Effiuent Monitoring Report for Period
January 1 through June 30, 2014
As required by Utah Administrative Code, R 313-24-4 (incorporating by reference 10 CFR 40.65
(subpart1)), and License Condition 11.3A of State of Utah Radioactive Materials License No.
UT1900479, enclosed is the Semi-Annual Effluent Monitoring Report for the White Mesa Mill
for the period January 1, 2014 through June 30, 2014.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
Yours very truly,
{4)0ud_
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Harold R. Roberts
David E. Turk
Frank Filas
Jaime Massey
White Mesa Uranium Mill
Radioactive Materials License UT900479
Semi-Annual Effluent Monitoring Report
(January through June 2014)
Prepared For:
Utah Department of Environmental Quality
Division of Radiation Control
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
August 29, 2014
TABLE OF CONTENTS
1.0 INTRODUCTION .................................................................................................. 1
2.0 ENVIRONMENTAL AIR PARTICULATE SAMPLING ..................................... 2
2.1 Program Overview .................... , .......................................................................... 2
2.2 Sampling Protocol and Analytical Results ............................................................ 2
2.3 General Observations ............................................................................................ 3
2.4 Site Specific Sampling Data ................................................................................. 4
2.5 Radon-222 ............................................................................................................ 6
3.0 EXTERNAL RADIATION (DIRECT GAMMA) .................................................. 7
4.0 VEGETATION SAMPLES ...................................................................................... 8
5.0 STACK SAMPLING ............................................................................................... 8
6.0 SURFACE WATER MONITORING .................................................................... 11
7.0 SOIL SAMPLING ................................................................................................. 11
8.0 METEOROLOGICAL MONITORING ..................... , .................................... , ....... 11
9.0 SIGNATURE ......................................................................................................... 12
LIST OF TABLES
Table 1 NCRP Report 94-Global Pb-210 Concentration Example
Table 2 Air Monitoring Station Results U-Nat (Comparison to Limits)
Table 3 Air Monitoring Station Results Th-230 (Comparison to Limits)
Table 4 Air Monitoring Station Results Ra-226 (Comparison to Limits)
Table 5 Air Monitoring Station Results Pb-210 (Comparison to Limits)
Table 6 Environmental OSL Dosimeter Measurements (Gamma)
Table 7 Stack Sampling Requirements
Table 8 Stack Effluent Concentrations and Release Rates
l
INDEX OF TABS
A High Volume Air Monitoring Stations
B BHV Air Sampling Graphs and Data Tables
Tab 1 BHV -1 Air Sampling Graphs and Data Table
Tab 2 BHV-2 Air Sampling Graphs and Data Table
Tab 3 BHV-3 Air Sampling Graphs and Data Table
Tab 4 BHV -4 Air Sampling Graphs and Data Table
Tab 5 BHV -5 Air Sampling Graphs and Data Table
Tab 6 BHV -6 Air Sampling Graphs and Data Table
C BHV Air Sampling Laboratory Results and QA/QC
D Air Particulate Loading Graphs and Supporting Data
E Environmental Gamma (OSL) Dosimeter Graphs and Supporting Data
F Vegetation Graphs, Data Table, Laboratory Results and QA/QC
G Stack Sample Laboratory Results
H Surface Water Graphs and Field Data Sheets
I Soil Sample Graphs, Data Table, Laboratory Results and QA/QC
ii
WHITE MESA URANIUM MILL
SEMI-ANNUAL EFFLUENT REPORT, JANUARY THROUGH JUNE 2014
1.0 INTRODUCTION
The White Mesa Mill (the "Mill") has established monitoring programs to evaluate
compliance with effluent limitations and to assess the potential for release of radioactive
material into the local environment. These monitoring programs were developed and
implemented at the time of Mill constmction, operated with appropriate adaptation over
time, and are consistent with the Mill's State of Utah Radioactive Materials License No.
UT1900479 (the "License") and guidelines developed by the United States Nuclear
Regulatory Commission ("NRC") (NRC Regulatory Guide 4.14, Radiological Effluent
and Environmental Monitoring at Uranium Mills-Rev. 1, ML003739941), 1980).
Under these programs, the Mill monitors the following environmental media and
conditions:
a) Airborne particulate radionuclide concentrations obtained from the following
sampling stations:
• North, east and south of the Mill Site: BHV-1 and BHV-2 (north), BHV-5
(east), and BHV-4 (south). BHV-1 serves as a surrogate for the nearest
resident (BHV -1 is approximately 1.2 miles north of the Mill, but
approximately 0.4 miles closer to the Mill than the nearest resident);
• A background location distant to and west of the Mill (BHV-3) that was
monitored for airborne particulates up until November, 1995 (at which
time background was established), which is no longer monitored for air
particulates; and
• A station specifically requested by the White Mesa Ute Community south
of the Mill Site (BVH-6);
b) External (direct) gamma radiation measured at air monitoring stations BHV -1,
BHV-2, BHV-3, BHV-4, BHV-5 and BHV-6;
c) Vegetation at three site periphery locations, for uptake of radionuclides;
d) Stack release rates from the Mill's air emissions sources;
e) Surface water at Cottonwood Creek and, when flowing, Westwater Creek, both
located west of the Mill;
f) Soil radionuclide activity obtained near the air particulate monitoring stations,
during the third quarter of each year;
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g) Groundwater (up and down gradient) of the Mill facility; and 1
h) Seeps and springs in the vicinity of the Mill.1
This semi-annual effluent report provides the results of the specific monitoring and
sampling activities that were undertaken during the subject reporting period.
2.0 ENVIRONMENTAL AIR PARTICULATE SAMPLING
2.1 Program Overview
The environmental airborne particulate monitoring program at the Mill utilizes four air
sampling stations. Four high-volume continuous air sampling stations (BHV-1, BHV-2,
BHV -4, and BHV -5) are required by the License. These sampling stations serve as
sentinels for airborne particulate which could potentially emanate from the Mill site. In
addition to its general site monitoring function, BHV -1 also serves as a conservative
surrogate for concentrations at the nearest resident, because it is located approximately
1.2 miles north of the Mill just south of the nearest resident but between the Mill and that
resident.
With regard to background monitoring, the Mill previously operated a continuous high-
volume air sampling station (BHV-3) which was located approximately 3.5 miles west of
the Mill site. With the approval of NRC, this station (BHV-3) was removed from the
active air monitoring program in November 1995. At that time, NRC determined that a
sufficient air monitoring database had been compiled at BHV-3 to establish a
representative airborne radionuclide background for the Mill. While air sampling was
discontinued at this location, gamma measurements and soil sampling continue at BHV-
3.
In addition to the environmental air sampling locations described above, an additional
station (BHV-6) was installed at the request of the White Mesa Ute Community. This
station began operation in July of 1999 and provides airborne particulate information in
the southerly direction between the Mill and the White Mesa Ute Community.
2.2 Sampling Protocol and Analytical Results
Airborne particulate monitors are operated continuously at each of the high-volume air
sampling stations referenced above except BHV -3. Particulate sample collection filters
are gathered by site technicians weekly in accordance with the Mill's environmental air
sampling procedures and are composited on a quarterly basis for laboratory analyses.
The collected filters are analyzed for Unat activity, Th-230 activity, Ra-226 activity, and
Pb-210 activity. Fugitive dust standards for the facility are limited by the Mill's State of
Utah Air Approval Order. The specific locations of the Mill's airborne particulate
1 Groundwater sampling and seeps and springs sampling are reported separately pursuant to the Mill's State
of Utah Ground Water Discharge Permit No. UGW370004, and are not included with this report.
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monitoring stations are depicted on the figure entitled High Volume Air Monitoring
Stations included as Attachment A. Station BHV-3, which is no longer sampled for air
particulates, is located approximately 3.5 miles west of the Mill facility and is not shown
on the Figure.
The analytical results of radionuclide particulate sampling for each monitoring station
operated during this reporting period are provided in Attachment B under separate
sampling station attachment tabs (Tabs 1-6). Each tab contains graphical illustrations of
the radionuclide concentrations in log-scale presentation format. The graphs display
reported data over time since the 1981 inception of the Mill's environmental air
particulate monitoring program. The actual analytical results (and associated QA/QC
information) reported by the laboratory for the reporting period are provided under
Attachment C. In addition to the analyses for radionuclides, particulate loading is
determined for each filter and composited as a quarterly mass-loading estimate for review
purposes only. Graphs showing particulate loading at each station and the underlying data
are included as Attachment D.
The first 2 sampling periods of 2012 have been omitted from particulate loading on the
graph for BHV -6 in Attachment D. The timer on the airborne particulate monitoring
station at BHV -6 malfunctioned, and the data are considered invalid due to the inability
to measure the time sampled. The timer was replaced prior to the third sampling period in
2012 and all other measurements are valid.
For graphical jJJu tration purposes, values reported at zero, values reported at less than
the prescribed detection limit < J x J0-1G uCi/ml), and missing values were plotted as 1 x
10-16 uCi/ml concentrations. Where other "less than" values were indicated (i.e., where
detection limits for the data varied from 1 X 10'16 uCi/ml), the detection limit
concentration was utilized for plotting the data point. This graphing convention is not
utilized to formulate station average information, nor is it intended as a precedent for data
treatment. Rather, the intent is to provide a conservative viewable depiction of site
airborne radionuclide information. This is considered to be a conservative approach,
because the actual concentration below the detection limit cannot be determined and, as a
result, the plotted point will be at the same or a higher concentration than the actual
activity concentration of the collected sample.
2.3 General Observations
The results of environmental air monitoring for this semi-annual period indicate that for
all radionuclides at all monitoring stations, airborne radionuclide particulate activity
concentrations were well below regulatory Effluent Concentration Limits ("ECL's") and
the Mill's ALARA goals, which are set at 25% of the ECLs.
It is noteworthy and expected that Pb-210 concentrations are elevated when compared to
the other parent radionuclide concentrations (i.e. U-nat, Th-230 and Ra-226). This
phenomenon is due to the well-established controlling effect experienced worldwide as a
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result of the ubiquitous presence of radon in the eruth's atmosphere. Accordingly, the
elevated Pb-210 presence in disequilibrium with parent radionuchdes measured here is
not associated with uranium milling operations. Rn-222 emanates as a decay-chain
progeny of the Ra-226 contained in the soil of the earth's crust and is dispersed generally
throughout the earth's atmosphere. The electrically charged short and long-lived decay
products of Rn-222 attach to ambient dust particles found naturally in the atmosphere and
are carried with the air. Pb-210 is the longest lived of these decay products and is the
decay product of the shorter-lived radon progeny. As such, it accumulates as an electrical
attachment on the natural ambient dust in the atmosphere and is generally measured at
elevated activity when compared to local decay-chain parent radionuclide activity,
regardless of uranium milling activity. At the Mill's BHV air monitoring stations, all
dust (ambient natural and mill derived) is collected by the sample filter. Because of the
natural elevation of Pb-210 accumulated as an attachment to the naturally occurring
ambient dust particles collected by the air sampling equipment, Pb-210 is commonly
elevated and in disequilibrium when compared to parent radionuclide activity, regardless
of the Mill's presence. By way of illustration, average ground-level concentrations have
been reported for selected States (NCRP Report 94, 1992) and are summarized in Table 1
below, demonstrating that elevated Pb-210 activity is present where no uranium milling
operations are located nearby. In April 1977, prior to Mill construction and Mill
operations, air farticulate Pb-210 was measured at the Mill site to be 1.3E-14 uCi/rnl
(13.0E-3 pCi/m )2.
Table 1-NCRP Report 94-Global Pb-210 Concentration Example
·State Pb-210 Concentration
uBq/M3 uCi/ml
California 600 1.6E-14
Illinois 1500 4.1E-14
Ohio 300 8.1E-15
Massachusetts 700 1.9E-14
2.4 Site Specific Sampling Data
The results of airborne particulate monitoring for the period (without background
subtraction) are provided by sampling station and radionuclide in Tables 2 through 5
below. Along with these data, the tables present comparative ECL's and the ECL
percentage measured at each of the monitoring stations sampled during the period. A
review of these data support the conclusion that airborne particulates are well controlled
at the Mill. In all cases, the measured activity concentrations were well within the ECL,
as well as the Mill's ALARA goal (i.e. 25% of the ECL). Lower Limits of Detection
consistent with NRC Regulatory Guide 4.14 were maintained by the Mill's contract
analytical laboratory for this reporting period.
2 See the Environmental Report, White Mesa Uranium Project, San Juan County, Utah for Energy Fuels
Nuclear, Inc. prepared by Dames & Moore, January 30, 1978, Section 2.9.1.1
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The data obtained since program inception in 1981 indicates that only one individual
quarterly measurement (Th-230 at BHV-5 for the 2nd Quarter of 1996) has ever exceeded
the ECL at the Mill. While it is important to consider and evaluate an individual
measurement exceeding the ECL, it is the average annual concentration that is of primary
significance for public dose estimation purposes. In that instance, the average annual
concentration of Th-230 for BHV-5 in 1996 was well below the ECL. Data obtained
since program inception in 1981 also indicate that, with very few exceptions, the gross
(background inclusive) measurements do not exceed the site's ALARA goal (i.e. only
nine of the several thousand total gross radionuclide determinations to date exceeded the
Mill's self-imposed 25% ALARA goal).
Table 2-Air Monitoring Station Results U-Nat (Comparison to Limits) 1st and 2nd
Quarters 2014
Monitoring 1st Qtr. 2nd Qtr. Effluent Average
Station Result Result Concentration Percent
(uCilrnl) (uCilrnl) Limit (ECL) ECL
(uCilrnl)
BHV1 1.07E-15 2.24E-15 9.00E-14 1.84E+00
BHV2 4.63E-16 3.04E-16 9.00E-14 4.26E-01
BHV4 4.69E-15 4.16E-15 9.00E-14 4.92E+00
BHV5 4.74E-15 8.18E-15 9.00E-14 7.18E+00
BHV6 8.92E-15 8.29E-15 9.00E-14 9.56E+00
Table 3-Air Monitoring Station Results Th-230 (Comparison to Limits) 1st and 2nd
Quarters 2014
Monitoring 1st Qtr. 2nd Qtr. Effluent Average -"
Station Result Result Concentration Percent
(uCilrnl) (uCilrnl) Limit (ECL) ECL
(uCilrnl) I
BHV1 2.07E-16 5.14E-16 2.00E-14 1.80E+00
BHV2 4.97E-17 7.92E-17 2.00E-14 3.22E-01
BHV4 1.37E-16 6.96E-16 2.00E-14 2.08E+00
BHV5 1.42E-15 1.34E-15 2.00E-14 6.90E+00
BHV6 7.68E-16 5.35E-16 2.00E-14 3.26E+00
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Table 4-Air Monitoring Station Results Ra-226 (Comparison to Limits) 1st and 2"d
Quarters 2014
Monitoring 1st Qtr. 2nd Qtr. Effluent= Average
Station Result Result Concentration Percent
(uCilml) (uCilml) Limit (ECL) ECL
(uCi/ml)
BHVl 3.69E-16 1.09E-15 9.00E-13 8.11E-02
BHV2 1.15E-16 1.82E-16 9.00E-13 1.65E-02
BHV4 3.53E-16 1.77E-15 9.00E-13 1.18E-01
BHV5 3.48E-15 1.76E-15 9.00E-13 2.91E-Ol
BHV6 1.50E-15 6.72E-16 9.00E-13 1.21E-01
Table 5-Air Monitoring Station Results Pb-210 (Comparison to Limits) 1st and 2"d
Quarters 2014
Monitoring 1st Qtr. 2nd Qtr. Effluent Average
Station Result Result Concentration Percent
(uCi/ml) (uCi/ml) Limit (ECL) ECL
-~~ (uCilml)
BHVl 1.24E-14 1.23E-14 6.00E-13 2.06E+00
BHV2 1.49E-14 1.21E-14 6.00E-13 2.25E+00
BHV4 1.08E-14 1.06E-14 6.00E-13 1.78E+00
BHV5 1.50E-14 1.42E-14 6.00E-13 2.43E+00
BHV6 1.61E-14 1.20E-14 6.00E-13 2.34E+00
2.5 Radon-222
Due to the unavailability of monitoring equipment to detect the revised 10 CFR Part 20
standard, and with the approval of the NRC, Radon 222 monitoring at BHV stations was
discontinued in 1995. Instead, compliance with these limits and the requirements of
R313-15-301 is demonstrated by a calculation, authorized by the NRC and as
contemplated by R313-15-302(2)(a). A copy of the Technical Evaluation Report
evidencing such approval was enclosed with correspondence to the Division of Radiation
Control ("DRC") on July 28, 2008.
This calculation is performed by use of the MILDOS code for estimating environmental
radiation doses for uranium recovery operations (Strenge and Bender 1981) and more
recently in 2003 by use of the updated MILDOS AREA code (Argonne 1998). The
analysis under both the MILDOS and MILD OS AREA codes assumes the Mill to be
processing high grade Arizona Strip ores at full capacity, and calculates the
concentrations of radioactive dust and radon at individual receptor locations around the
Mill.
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The MILDOS and MILDOS AREA codes calculate the combined Total Effective Dose
Equivalent ("TEDE") from all relevant pathways, including both air particulate and
radon, at a number of locations including the nearest residence (the individual likely to
receive the highest dose from the licensed operation), approximately 1.6 miles north of
the Mill. These calculations reveal projected doses to the individual likely to receive the
highest dose from the licensed operations to be well below the 100 mrem regulatory limit
in R313-15-301(1)(a) for all pathways, including air particulate and radon, and well
below the ALARA goal of 10 mrernlyr for air emissions excluding radon as set out in
R313-15-101(4). MILDOS AREA modeling was recently conducted in support of the
Mill's 2007 License Renewal Application, utilizing the MILDOS-AREA code (Version
2.20~), to estimate the dose commitments at various receptor locations for processing of
Colorado Plateau ore (0.25% U30 8 and 1.5% V20 5) and Arizona Strip ore (0.637%
U30 8). The process rate was assumed to be at full capacity of 730,000 tons per year (an
average of 2,000 tons per day) with an average uranium recovery yield of 94%. That
modeling showed a TEDE of 2 mrem per year at the nearest resident (3 mrem per year at
the nearest potential residence, being the location of BHV -1 at the northern property
boundary of the Mill site), which included the dose from all radionuclide sources,
including radon. The modeled dose from radon itself was therefore a fraction of the
TEDE and well within the regulatory limits.
3.0 EXTERNAL RADIATION (DIRECT GAMMA)
Gamma exposure rate estimates were measured for the reporting period utilizing optically
stimulated luminescence dosimeters ("OSLs"). These dosimeters were located at each of
the Mill's high-volume air sampling stations (BHV-1, BHV-2, BHV-4, BHV-5 and
BHV-6) and at the designated background monitoring station (BHV-3). Measurements
obtained from location BHV-3 have been designated as background due to BHV-3's
remoteness from the Mill site (i.e., BHV-3 is located approximately 3.5 miles west of the
Mill site). The results of the environmental OSL measurements and semi-annual
cumulative above-background data are provided in Table 6 below. In addition,
measurement data obtained at these locations are graphically presented in Attachment E
to this report.
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Table 6-Environmental Optically Stimulated Luminescence Dosimeter
~easurements((;amma)
' Monitoring 1st Qtr 2nd Qtr 1st Qtr 2nd Qtr Cumulative
Station Result Result Result Less Result Less Semi-
(mrem) (mrem) Background Background Annual
(mrem) (mrem) Estimate
(mrem)
BHV1 32.0 37.7 3.9 4.1 8.0
BHV2 28.9 30.8 0.8 0.0 0.8
BHV3 28.1 33.6 0.0 0.0 0.0
BHV4 31.5 32.0 3.4 0.0 3.4
BHVS 32.6 37.2 4.5 3.6 8.1
BHV6 33.2 31.1 5.1 0.0 5.1
The results for this period indicate that above background measurements for stations
BHV-1, BHV-2, BHV-4, BHV-5 and BHV-6 are within regulatory limits. BHV-1 is at
the location of the nearest potential residence. The nearest actual residence is
approximately 0.4 miles north of BHV-1. The annual limit for an individual member of
the public is 100 mrem/yr for combined internal and external exposure.
4.0 VE<;ETATION SA~PLES
Vegetation samples are collected at three locations around the Mill property. The
sampling locations are: 1) northeast, 2) northwest and 3) southwest of the Mill facility.
The NRC Regulatory Guide 4.14 requires that three samples be collected during the
grazing season, without specifying exact months or times during the season. During the
2014 grazing season, two sets of samples were collected on April 16, 2014 and June 10,
2014. A third set of samples is planned for the fall season. The data from the fall season
sampling will be included in the July through December 2015 Semi-Annual Effluent
Report ("SAER") which will be submitted to the DRC on March 1, 2015. Data from the
April and June sampling events are included in this report.
Graphical log-scale presentation of the vegetation sampling results, together with the
analytical results reported by the Mill's contract laboratory (including QA/QC
information) for this sampling period, are included as Attachment F of this report. The
2014 data results are within the variation of previous sampling episodes.
5.0 STACK SA~PLIN(;
Under Section 5.0 of Tab 1.4 of the Mill's Environmental Protection Manual, Revision:
EFR-3, 12/12 (the "Environmental Protection Manual") gas stack samples are collected
at the Mill in accordance with the calendar year schedule shown below:
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Table 7 -Stack Sampling Requirements
Frequency Feed Stack (Grizzly Stack for Packaging
Baghouse) Yellowcake Dryer (Yellowcake
Baghouse)
Quarterly None If operating, U-nat If operating, U-nat
Semi-annually If operating, U-nat, If operating, U-nat, If operating, U-nat,
Th-230 Th-230, Ra-226, Pb-Th-230, Ra-226,
210 Pb-210
The analytical results of stack sampling conducted for the 1st and 2nd quarters of 2014, as
well as for the 3rd and 4th quarters of 2013, are provided in Table 8 below, indicating the
uCi/cc concentration in the stack emissions and the stack's radionuclide release rate
(uCi/sec) for U-Nat, Th-230, and Ra-226 at each of the stacks sampled. The Pb-210
results are discussed below. The actual analytical results reported by the laboratory for
the 1st and 2nd quarters of 2014 are provided in Attachment G to this report.
As shown on Table 8, the laboratory did not report the Pb-210 data for the 2nd quarter of
2014. The tracer yield for the samples was too low and insufficient for completion of the
analyses. The entire sample volume was consumed during the initial analysis and there
was no opportunity for reanalysis. EFRI was not notified of the issue by the laboratory
until August of 2014, and therefore, could not recollect the samples. EFRI is exploring
other laboratory options to prevent reoccurrence of data loss in the future.
The south yellowcake dryer, yellowcake baghouse, and grizzly baghouse operated during
the 1st and 2nd quarters of 2014. The north yellowcake dryer has not been in operation
since the 3rd quarter of 2012, and therefore, has not been sampled since it was last in
operation.
It is also important to note that stack effluent concentrations are not comparable to
environmental air sampling station ECL's for regulatory compliance purposes. The ECL
is a limit that applies to the receptor locations and is not applicable to effluents from mill
processes on the Mill site. These stack release data are more appropriately utilized for
dose modeling purposes, and dose modeling is not computed for semi-annual reporting
purposes.
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Table 8-Stack Effluent Concentrations and Release Rates
U-Nat U-Nat. Th-230 Th-230 Ra-226 Ra-226
u/Ci/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
I
3nl Qtr, 2013* '
South YC Not Not Not Not Dryer, Run 1 3.89E-10 2.50E-04 Reguired Required Rt~guired Reguired
South YC Not Not Not Not
Dryer, Run 2 4.86E-10 2.82E-04 Required Required Reg_uired R~uired
Yellowcake Not Not Not Not
Baghouse 1.04E-08 1.73E-02 Required Required Required Required
4th Qtr, 2013* c •
South YC
Dryer, Run 1 2.70E-10 1.66E-04 2.33E-14 1.43E-08 7.77E-15 4.76E-09
South YC
Dryer, Run 2 2.66E-10 1.65E-04 1.48E-13 9.13E-08 2.35E-14 1.46E-08
Yellowcake
Baghouse 8.91E-09 1.55E-02 1.67E-11 2.91E-05 4.60E-13 S.OlE-07
Grizzly Not in Not in Not in Not in Not Not
Baghouse** operation operation operation operation Rf~guired Rt~guired
1st Qtr 2014*
South YC Not Not Not Not Dryer, Run 1 2.53E-10 1.65E-04 R!<quired Re__quired" Reg_uired Rf~guired
South YC Not Not Not Not
Dryer, Run 2 2.45E-10 1.67E-04 Re_quired Required Reg_uired Rf~guired
Yellowcake Not Not Not Not
Baghouse 9.87E-10 1.83E-03 Required Required Required Required
2"d Qtr, 2014* I~
South YC
Dryer, Run 1 1.79E-09 1.04E-03 2.22E-14 1.29E-08 3.40E-14 1.97E-08
South YC
Dryer, Run 2 2.19E-12 1.25E-06 3.25E-14 1.86E-08 3.44E-14 1.97E-08
Yellowcake
Baghouse 8.48E-10 1.25E-03 2.82E-13 4.17E-07 2.11E-13 3.11E-07
Grizzly I I Not Not
Baghouse 9.10E-12 6.40E-06 2.04E-12 1.43E-06 Required Required
*The North Yellowcake Dryer was not in operation during 2013 or the first half of 2014 ..
**The Grizzly Baghouse was not in operations during the 3rd and 41h quarters of 2013.
10
N:\WMM\Required Reports\Semi Annual Effluent Reports\2014 Jan-June\Jan_June_2014_SAER_text.docx
Pb-210 Pb-210
uCi!cc uCi/sec
Not Not
Reg_uired Required
Not Not
Reg_uired Required
Not Not
Req~ired Required
2.11E-13 1.29E-07
1.65E-13 1.02E-07
1.16E-12 2.03E-06
Not Not
R~guired Required
Not Not
Rf~guired Required
Not Not
Re_guired Required
Not Not
Reqpired Required
No data reported.
See Section 5.0
above for details.
Not Not
Required Required
I
6.0 SURFACE WATER MONITORING
Under the License, Part 11.2 B surface water samples are required to be obtained
annually from Westwater Canyon and semi-annually from Cottonwood Creek. Sediment
samples from Westwater Canyon are taken in place of the Westwater Canyon surface
water sample where surface water is not available for sampling. Westwater Canyon
surface water was not sampled in the first or second quarter of 2014, because no water
was present during this reporting period. Attempts to collect a surface water sample from
Westwater Canyon will continue through the next reporting period. If no surface water is
available, a sediment sample will be collected as required.
The Mill's Environmental Protection Manual requires that samples from Cottonwood
Creek be analyzed for TDS and total suspended solids ("TSS") quarterly, and the
License, Part 11.2 B requires that samples from Cottonwood Creek be analyzed for
dissolved and suspended radionuclides including Gross Alpha, U-nat, Ra-226, and Th-
230 semi-annually. In accordance with these requirements, Cottonwood Creek was
sampled for TDS and TSS during the 1st quarter, and was sampled for TDS, TSS, and the
radionuclides during the 2nd quarter.
The field data sheets for the surface water sampling events, along with graphs showing
historic results are included as Attachment H. The results of this sampling indicate that
surface water concentrations remain low and within the range of typical background
levels.
7.0 SOIL SAMPLING
Under Tab 4.1 of the Mill's Environmental Protection Manual, surface soils are required
to be sampled at the Mill's air monitoring stations (BHV-1, BHV-2, BHV-3, BHV-4,
BHV-5 and BHV-6) once per year during August or as soon as possible thereafter, but no
later than September 30 of each year. In accordance with the Mill's Environmental
Protection Manual, surface soils will be collected during the third quarter of 2014 and
will be discussed in the July through December 2014 report.
8.0 METEOROLOGICAL MONITORING
As in prior reporting periods, an independent contractor has prepared the White Mesa
Mill Semi-annual Meteorological Monitoring Report for the period of January through
June 2014. This information is retained at the Mill site for agency review.
11
N:\WMM\Required Reports\Semi Annual Effluent Reports\2014 Jan-Juue\Jan_June_2014_SAER_text.docx
9.0 SIGNATURE
This report was prepared by Energy Fuels Resources (USA) Inc. on August 29, 2014.
Energy Fuels Resources (USA) Inc.
Frank Filas
Vice President, Permitting and Environmental Affairs
12
N:\WMM\Required Reports\Semi Annual Effluent Reports\2014 Jan-June\Jan_June_2014_SAER_text.docx
ATTACHMENT A
HIGH VOLUME AIR MONITORING STATIONS
U1 I*
I I __ ..,_ __________ ----+-----
I . ~ ~ I , ~ ,
I ; ~ ...... r . 1 *'..... ,-.J
I I .... ,,,~. ' I'Y ,' I
I ~ i . ,,1 ,~.. i -+------------~-t----:-1-1----:.----1
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I ' ' . l ._. I 1 I i
'It I I ~ • , : ,, . , ~-I ... I !
I •• • I -= --t-~-----------~'t.. 1 -t
'~ : I I "•4 ) -~ I t. : ~ ~~l \ I / ' ,. : ( I ~ ~ ) ' ; : ('-' . ... -'
.. --~ l
,,_, io / .... ~ :I .. .. .. ~
0
' I
I -------r·---
' I
' -r --------J
I 1
I
I
I N I
I I
~~ 1\ I
J i
I
I
I
I
I
I
-·-·• •• ·---2 I
" _____ ,_
/, I -
' .
I
I
' \
I
I .
I ,
0 2000 2000 , I b-CiJW
', SCAl£ II FEET
~--';f'I-1---I -
12
' • • ------f--
a I .,~ i I .,.,
• I ~ .. ,, .... J\': : ., ...... • -'. 1 ~,
~"0
( 1 '~~,-'' ... J,'_... \ I · ~...--'I -.------~,--· ----~-. ;,_.-~----E [ I
'"'· I ,_,,,, ~-''
-I ! I -! 1 't?nf"-deHv-s
0
f---~-t{_. __ ... -----i-----~~--~ . \~ . . -
''\ I ,/-,
I I ' • ,' ·1 ' '·I· .. . .. ~ .. ./ '~ , .. 't---'( ~
I ~ ' I ' I ., ..
I \ • ----.;....~-----.. ---1 t' • ••
I I ~ \ ( : , , I
' t'' I
( .. I
• ' • I : ,./ I I · ;,.
o .
BHV· I ----.,.-··--
BIW-6
: : • • I __________ J_Lt ___ J ! ________ __\ _______________ .....
I • \ -I I I ' ., 1/ L I : ~·~ . ! -; ............ .,
I L_ __ ~ \
I . •
I . I \ .
4: ~­~r -J : -~ ...1 \
... 4 ~----l-----~-·-----. ---~i __
-'
·--------------------------~ ~,· _., ..
\i : l
I ', I ~,
I \ ' ,.... ' ' .-" ....._,
I ' I '---
• •
-•
' 1 -,
t ( f'' ~11 ,._~
,.~·
~ \ .. ,
"' i ~ I I • 1 n~Y -J t-7-L-------:,.,.... -~It,--.
-------~---_____/b_ ----
_ ........ Property Boundary
Reservation Boundary
Canyon Rim
0 Air Monitor
Stations
•· \ .. • I
-,-:I. 4 l \. \~ .,. . -\, \lt.. C:.l i _, ~.. ~ ~~ ·. I --o y,~). !S ~ ~~\,. I..(. f
"""" . l I • .., ' l -o • -. --. --~ --~~~~---_._--o---_ _. ---------~.~ I 6 -:. . .,.. ' *"' .. ~~~,,· *'f, ' ..
• "\ J ..A •..._ -I , .. , ~ , '~... ~ ll'~ ( ·l"' ' ~....... .. '!...., ..
# .... :·. ##\· ' ~. ~. . :,( ~, ~ l
• ·--·-··--·---· ·4--~ "i ---~,:~---.-­~ --... ~ .. , '~ ..... . ~ '·~ .l i ~ .
\ I ·#~,,
I , ..
~ ~, ,,
• ....., ..... ._ ... (USA) lllc. ,.... WHITE MESA MILL ...,..... ur
g,. , .. -..
WIIM -_,---.... &3-,_.. ....... ----
ATTACHMENT B
BHV AIR SAMPLING GRAPHS AND DATA TABLES
TAB 1
BHV -1 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent Concentration Limit = 9E-14 uCi/ml BHV-1U Effluent Concentration Limit = 2E-14 uCi/ml BHV-lT Effluent Concentration Limit = 9E-13 uCi/ml BHV-1R Effluent Concentration Limit= 6E-13 uCi/ml BHV-1PB
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal-·SE-13 uCi/ml ALARAGoal = 2.25E·13 uCi/ml ALARA Goal-1.5E-13 uCi/ml
Pr!!-i9!l4 MPc Umlt ~ SE-12 uCi/ml Pre 1994 MPC Limit= SE-14 uCi/ml Pre 1.9!111 MPC Umlt"' 2E-12 uCi/ml Pre 1994 MPC Limit-4E-12 uCi/ml
Pre 1994 A LARA GOAL= 1.25E-12 uCi/ml Pre 1994 ALARA GOAL= .SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone ~FC EFCA
9/28/1981 2.35E-15 5.00E-12 1.25E-12 7.82E·16 8.00E-14 2.00E·14 1.06E-15 2.00E-12 5.00E-13 2.57E-14 4.00E-12 1.00E-12
12/14/1981 1.56E-15 5.00E-12 1.25E-12 1.49E-15 8.00E-14 l.OOE-14 '1.93E-15 2.00E-12 5.00E-13 2.64E-14 4.00E-12 1.00E-12
?/29/1982 2.16E-15 S,OOE-12 1.25E-12 2,93E-15 8.00E-14 2.00E·14 1.16E-15 2.00E-12 S.OOf-13 2.09E-14 4.00E-12 l.OOE-12 j
6/30/1982 .4..69E-15 S.OOE-12 1.25E-12 3.46E-15 8.00E-14 .2.00E·14 2.38E-15 2.00E-12 $.01*13 2.14E-14 4.00E-12 l.OOE-12
9/27/1982 4.45E-15 S.OOE-12 1.25E-12 3.29E·15 8.00E-14 2.00E·14 3.23E-15 2.00E·12 5.00E-13 1.99E-14 4 OOE-12 l.OOE-12 I
1/3/1983 4.39E-15 S.OOE-12 1.25E-12 5.91E·16 8.00E-14 2.00E-14 9.14E-16 2.00E-12 5.00E-13 4.87E-14 4.00E-12 l.OOE-12
4/4/1983 7.51E-16 5.00E-12 1.25E-12 2.13E-16 8.00E-14 2.00E-14 3.20E-16 2.00E-12 5.00E-13 L88E-14 4.00E-12 l.OOE-12
9}30/1983' 2.68E-16 5.00E-12 1.25E-12 6.92E-16 S.OOE-14 2.00E·14 7.92E-16 2.00E-12 5.00E-13 2.00E-14 4.00E-12 l.OOE-12 !
10/3/1983 5.00E-12 1.25E-12 S.OOE-14 2.00E-14 O.OOE+OO 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 1
1/3/1984 2.87E-15 5.00E-12 1.25E-12 1.14E·16 8.00E-14 2.00E-14 1.79E-16 2.00E-12 5.00E-13 1.06E-14 4.00E-12 l.OOE-12
4/2/1984 1.59E-15 S.OOE-12 1.25E-12 3.40E·16 S.OOE-14 2.00E-14 3.71E-16 2.00E·12 5.00E-13 3.34E-14 4.00E-12 l.OOE-12 I
7{1;{'1!(}84 3.10E-15 S.OOE-12 1.25E-12 l.OOE-15 S.OOE-14 2.00E-14 2.09E-15 2.00E-12 S.OOE-13 l.SSE-14 4.00E-12 1.00E-12 I
10/1/1984 6.42E-16 S.OOE-12 1.25E-12 1.39E-16 8.00E-14 2.00E-14 1.94E-16 2.00E-12 5.00E-13 1.85E-14 4.00E-12 l.OOE-12
1/2/1985 5.06E-16 S.OOE-12 1.25E-12 4.56E-16 S.OOE-14 2.00E-14 3.49E-16 2.00E-12 5.00E-13 3.03E-14 4.00E·12 l.OOE-12
4}1/1985 O.OOE+OO S.OOE-12 1.25E-12 1.23E-15 8.00E-14 2.00E-14 4.88E-16 'l.OOE-12 S.OOE-13 1!.06E·15 4.00E-12 1.00E-12
7/l/1985 7.17E-16 5.00E-12 1.25E-12 8.00E-14 2.00E-14 1.05E-15 2.00E-12 5.00E-13 1.15E·14 4.00E-12 l.OOE-12
9)30/1985 6.13E-16 5.00E-12 1.25E-12 1.18E·16 8,00E-14 2.00E-14 3.71E-16 2.00E-12 S.OOE-13 3.64E-15 4.00E·12 l.OOE-12
1/2/1986 3.42E-15 5.00E-12 1,25E-12 4.74E·16 8.00E-14 2.00E-14 2.00E·12 5.00E-13 4.00E-12 1.00E-12
4/1/1986 3.98E-15 S.OOE-12 1.25E-12 9.74E-16 8.00E-14 2.00E·14 1.50E-15 2.00E-12 S.OOE-13 1.41E-14 4.00E-12 l.OOE-12
6/30/1986 5.51E-17 5.00E-12 1.25E-12 3.52E·16 8.00E-14 2.00E-14 1.37E-15 2.00E·12 5.00E-13 1.23E-14 4.00E-12 l.OOE-12
10/27/1986 1.99E-15 5.00E-12 1.25E-12 3.06E-16 8.00E-14 2.00E-14 1.25E-15 2.00E-12 S.OOE-13 1.08E-14 4.00E-12 l.OOE-12
12/15/1986 1.67E-15 5.00E-12 1.25E-12 1.16E·16 8.00E-14 LOOE-14 5.98E-16 2.00E·12 5.00E-13 1.37E-14 4.00E-12 l.OOE-12
3/16/1987 2.33E-15 5.00E-12 1.25E-12 4.30E-16 8.00E-14 2.00E-14 1.92E-16 2.00E-12 S.OOE-13 5.59E-14 4.00E-12 1.00E-12
5/11/1987 2.36E-15 5.00E-12 1.25E-12 7.69E·16 8.00E-14 2.00E-14 8 76E-16 2.00E·12 S.OOE-13 1.45E-14 4.00E-12 l.OOE-12
9/9/1987 2.27E-15 5.00E-12 1.25E-12 2.44E-15 8.00E-14 2.00E-14 8.51E-16 2.00E-12 S.OOE-13 3.14E-14 4.00E-12 l.OOE-12
ll/i/ll87 2.75E-15 S.OOE-12 1.25E-12 2.46E·15 8.00E·14 2.00E-14 1.34E-15 2.00E·12 5.00E-13 2.79E-14 4.00E-12 l.OOE-12
2/16/1988 1.07E-15 S.OOE-12 1.25E-12 1.47E·16 S.OOE-14 2.00E-14 4.44E-16 2.00E-12 5.00E-13 4.01E-14 4.00E·12 1.00E-12
5/18/1988 1.98E-15 :;,OOE-12 1.25E-12 1.25E-15 S.OOE-14 2.00E-14 6.40E-16 2.00E-12 5.00E-13 1.07E-14 4.00E-12 1.00E-12
8/15/1988 2.06E-15 S.OOE-12 1.25E·12 3.41E-15 S.OOE-14 2.00E-14 5.08E-16 2.00E-12 5,00E-13 1.62E-14 4,00E-12 1.00E-12
ll/.14/1988 3,94E-15 -5.00E-12 1.25E-12 2.12E-15 S.OOE-14 2.00E-14 1.01E-15 2.00E-12 S.OOE-13 2.47E-14 4.00E-12 1,00E-12
2/13/1989 1.99E-15 S.OOE-12 1.25E-12 5.73E·16 8.00E-14 2,00E-14 5.99E-16 2.00E·12 5.00E-13 3.23E-14 4.00E-12 l.OOE-12
5/15/1989 1.70E-15 S.OOE-12 1.25E-12 6.32E·16 8.00E-14 2.00E-14 5.86E-16 2.00E-12 5.00E-13 6.16E-15 4.00E-12 1 OOE-12
8/14/1989 2.31E-15 5.00E-12 1.25E-12 2.31E·16 S,OOE-14 2.00E-14 1.77E-16 2.00E-12 S.OOE-13 7.65E-15 4.00E-12 l.OOE-12
ll/13/1989 4.72E-15 5.00E-12 1.25E-12 1.71E-15 S.OOE-14 2.00E-14 1.52E-15 ~.OOE-12 S.OOE-13 1.89E-14 4.00E-12 1.00E-12
2/12/1990 3.44E-16 S.OOE-12 1.25E-12 8.39E-16 S.OOE-14 2.00E-14 8.31E-16 2.00E-12 S.OOE-13 2.57E-14 4.00E-12 l.OOE-12
5/14/1990 3.03E-15 S.OOE-12 1.25E-12 1.47E·15 S.OOE-14 .2 OOE-14 1.04E-15 2.00E·12 5.00E·13 1.79E-14 4.00E-12 1.00E-12
8/13/1990 1.64E-15 5.00E-12 1.25E-12 1.49E-15 8.00E-14 2.00E-14 3.34E-16 2.00E-12 5.00E-13 8.27E-15 4.00E-12 l,OOE-12
11/12/1990 1.48E-15 5.00E-12 1.25E-12 7.50E-16 S.OOE-14 2.00E-14 5.80E-16 2.00E-12 5.00E-13 2.16E-14 4.00E-12 l.OOE-12
,2/11/1991 1.90E-16 5.00E·12 1.25E-12 3.48E-17 S.OOE-14 2.00E·14 7.91E·17 2.00E-12 S.OOE-13 3.79E-14 4.00E-12 l.OOE-12
5/13/1991 3.42E-16 5.00E-12 1.25E-12 1.34E·15 8.00E-14 2.00E-14 7.39E-16 2.00E·12 5.00E·13 1.46E-14 4.00E-12 l.OOE-12
8/12/1991 2.77E-16 5.00E-12 1.25E-12 4.17E·17 8.00E-14 2.00E-14 1.45E-16 2.00E-12 S.OOE-13 1.80E·14 4.00E-12 l.OOE-12
11/11/1991 6.65E-17 5.00E-12 1.25E-12 9.13E·17 S.OOE-14 2.00E-14 2.77E-17 2.00E-12 5.00E-13 1.06E-14 4.00E-12 l.OOE-12
,2/10/1992 1.94E-16 5.00E-12 1.25E-12 4.28E·17 S.OOE-14 2.00E-14 4.08E-17 2,00E-12 S.OOE-13 3.51E-14 4.00E-12 l.OOE-12
5/11/1992 2.54E-16 5.00E-12 1.25E-12 5.49E-16 S.OOE-14 2.00E-14 6.86E-17 2.00E-12 5.00E-13 1.38E-14 4.00E-12 l.OOE-12
8/10/1992 1.73E-16 5.00E-12 1.25E-12 1.55E·16 S.OOE-14 2.00E-14 1.20E-16 2.00E·12 S.OOE-13 1.53E-14 4.00E-12 l.OOE-12
11/9/1992 1.56E-16 5.00E-12 1.25E-12 3.19E·17 B.OOE-14 2.00E-14 4.90E-18 2.DOE·12 5,00E-13 1.86E-14 4.00E-12 l.OOE-12
2/9/1993 2.10E-16 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 3.89E-17 LOOE-12 5.00E-13 2.52E-14 4.00E-12 1.00E-12
5/10/1993 1.00E-16 S.OOE-12 1.25E-12 4.11E-17 S.OOE-14 2.00E-14 6.43E-17 2.00E·12 5.00E-13 1.26E-14 4.00E-12 l.OOE-12
8f10/1993 2.30E-16 S.OOE-12 1.25E-12 6.00E-17 S.OOE-14 2.00E-14 6.43E-17 2.00E·12 S.OOE-13 1.60E-14 4.00E-12 l.OOE-12
U/8/1993 S.OOE-12 1.25E-12 S.OOE-14 2.00E-14 O.OOE+OO 2,00E-12 S.OOE-13 L.57E-14 4.00E·12 1 OOE-12
2/7/1994 1.82E-16 S.OOE-12 1.25E-12 S,OOE-18 B.OOE-14 2.00E-14 4.30E-17 2.00E-12 S.OOE-13 2.59E-14 4.00E-12 1.00E-12
5/9/1994 3.60E·16 5.00E-12 1.25E·12 2.70E-16 S.OOE-14 2.00E-14 2.87E-16 2.00E-12 ~.OOE-13 1.60E-14 4.00E-12 l.OOE-12
8/9/1994 4.04E-16 5,00E-12 1.25E-12 2.70E-16 S.OOE-14 2.00E-14 2.94E-16 2.00E-12 5.00E·13 2.00E-15 4.00E-12 l.OOE-12
11/7/1994 9.18E-17 S,OOE-12 1.25E·12 3,60E-16 S.OOE-14 l .OOE-14 2.91E·16 Z.OOE-12 5.00E-13 2.00E-15 4.00E·12 l.OOE-12 ---
Date 'Effluent Concentration Limit= 9E-14 uCi/ml BHV-1U Effluent Concentration Limit-2E-14 uCi/ml BHV-lT Effluent Concentration Limit-9E-13 uCi/ml BHV-1R Effluent Concentration Limit-6E-13 uCi/ml BHV-1PB
ALARA Goal-2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARA Goal= Z.25E-13 uCi/ml ALARAGoal = l.SE-13 uCi/ml
Pre 1994 MPC Limit= SE-12 uCijml Pre 1994 MPC Limit= SE-14 uCi/ml Pre.l994 MPC U(lllr:-2E-12 uCi/ml P~ 1994 MPC limlb 4E-12 uCi/ml
Pre 1994 ALARA GOAL= 1.25E-12 uCi/ml Pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 ALARA GOAL = lE-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC IFCA I
Z/7/1995 1.77E-16 9.00E-14 2.25E-14 9.70E-17 2.00E-14 S.OOE-15 9.70E-17 9.00E-13 2.25E-13, 8.60E-15 6.00E-13 l.50E-13
5/9/1995 9.40E-17 9.00E-14 2.25E-14 5.36E-16 2.00E-14 S.OOE-15 1.60E-15 9.00E-13 2.25E-13 3.84E-15 6.00E-13 l.50E-13 I
8/9/1995 2.70E-16 9.00E-14 2.25E-14 1.60E-16 2.00E-14 S.OOE-15 2.76E-16 'J.OOE-13 2.25E-13 3.76E-15 6.00E-13 l.50E-13
11/11/1995 4.80E-15 9.00E-14 2.25E-14 6.41E-16 2.00E-14 S.OOE-15 8.93E-16 9.00E-13 2.25E-13 5.20E-15 6.00E-13 l.50E-13 I
2/5/1996 5.34E-15 9.00E-14 2.25E-14 2.30E-15 2.00E-14 S,OOE-15 1.30E-15 9.00E-13 2.25E-13 4.20E-15 6.00E-13 1.50E-13 I
5/6/1996 5.11E-16 9.00E-14 2.25E-14 3.06E-16 2.00E-14 S.OOE-15 1,40E-16 9.00E-13 2.25E-13 7.03E-15 6.00E-13 l.50E-13
8/5/1996 5.99E-16 9,00E-14 2.25E-14 1.55E-15 2.00E-14 S.OOE-15 2.03E-16 9.00E-13 2.25E-13 5.94E-15 6.00E-13 1.50E-13
11/6/1996 3.38E-16 9.00E-14 2.25E-14 ,5.45E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.22E-14 6.00E-13 l.50E-13
216/1997 l.OOE-16 9.00E-14 2.25E-14 1.25E-16 2.00E-14 S.OOE-15 1.28E-16 9.00E-13 2.25E-13 5.68E-15 6.00E-13 1.50E-13
5/5/1997 1.09E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 4.39E-15 6.00E-13 1,50E-13
8/11/1997 2.88E-16 9.00E-14 2.25E-14 3.83E-16 2.00E-14 S.OOE-15 1.82E-16 9,00E-13 2,25E-13 5,29E-15 6.00E-13 l.50E-13
1/5/1998 3.24E-16 9.00E-14 2.25E-14 3.47E-16 2.00E-14 S.OOE-15 1.19E-16 9.00E-13 2.25E-13 4.73E-15 6,00E-13 1.50E-13
4/28/1998 4.75E-16 9.00E-14 2.25E-14 6.73E-16 2.00E-14 S.OOE-15 5.69E-16 9.00E-13 2,25E-13 5.94E-15 ,G,OOE-13 l.50E-13
7/31/1998 8.84E-16 9.00E-14 2.25E-14 l.93E-15 2.00E-14 S,OOE-15 1.43E-15 9.00E-13 2.25E-13 5.22E-15 6,00E-13 1,50E-13
.9/28/1998 2.81E-16 9.00E-14 2.25E-14 2.89E-16 2.00E-14 5.00E-15 1.80E-16 9.00E-13 2.25E-13 4.64E-15 6.00E-13 l.50E-13
12/28/1998 8.08E-16 9.00E-14 2.25E-14 4.93E-16 2.00E-14 5.00E-15 5.01E-16 9.00E-13 2.25E-13 1.06E-14 6.00E-13 1.50E-13
3)2~/1999 2.06E-16 9.00E-14 2.25E-14 2.06E-16 2.00E-14 5,00E-15 1,42E-16 9.00E-13 2.25E-13 6.69E-15 6,00E-13 l.50E-13
7/3/1999 5.31E-16 9.00E-14 2.25E-14 .2.47E-16 2.00E-14 5.00E-15 2.23E-16 9.00E-13 2.25E·13 6.44E-15 6.00E-13 1.50E-13
9/27/1999 8.98E-16 9.00E-14 2.25E-14 .3.90E-16 2.00E-14 5,00E-15 2,96E-16 9.00E-13 2.25E-13 7,29E-15 6.00E-13 1.50E-13
12/28/1999 1.48E-15 9.00E-14 2.25E-14 6.00E-16 2.00E-14 5.00E-15 5.57E-16 9.00E-13 2.25E-13 6.19E-15 6.00E-13 1.50E-13
3/27/2000 l.OOE-16 9.00E-14 2.25E·14 l.06E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.23E-15 6.00E-13 1.50E-13
6}26!2000 3.47E-16 9.00E-14 2.25E·14 3.46E-16 2.00E-14 5.00E·15 3.62E-16 9.00E-13 2.25E-13 4.50E-15 6.00E-13 1.50E-13
9/26/2000 2.51E-16 9.00E-14 Z.25E-14 1.78E-16 2.00E-14 5.00E-15 3.25E-16 9,00E-13 2,25E-13 8.55E-15 6.00E-13 150E-13
12/26/2000 l.OOE-16 9.00E-14 2.25E-14 1.42E-16 .2.00E-14 5.00E-15 1.31E-16 9.00E-13 2.25E-13 7.77E-15 6.00E-13 1.50E-13
3/26/2001 3.10E-16 ~.OOE-14 2.25E-14 l.OOE-15 .2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E-13 7.19E-15 6.00E-13 1.50E-13
7/29/2001 1.52E-16 9.00E-14 2.25E-14 1.44E-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.25E-13 7.21E-15 6.00E-13 1.50E-13
9/24/2001 1.03E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.09E-15 6.00E-13 1.50E-13
12/31}2001 1,00E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.39E-15 6.00E-13 1.50E-13
4/1/2002 2.05E-16 9.00E-14 2.25E-14 2.44E-16 2.00E-14 5,00E-15 2.29E-16 9.00E-13 2.25E-13 8.15E-15 6.00E-13 1.50E-13
7/1/2002 3.55E-16 ~.OOE-14 2.25E-14 4.85E-16 2,00E-14 5,00E-15 1.06E-16 9.00E-13 2.25E-13 7.65E-15 6.00E-13 1.50E-13
9/30/2002 1.17E-16 9.00E-14 2.25E-14 1.61E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 3.68E-15 6.00E-13 1.50E-13
12/30/2002 l.OOE-16 9.00E-14 2.25E-14 1.03E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.46E-15 6.00E-13 1.50E-13
3}31/2003 1.20E-16 ~.OOE-14 2.25E-14 1.12E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 4.68E-15 6.00E-13 1.50E-13
6/30/2003 2.18E-16 9.00E-14 2.25E-14 MOE-16 2.00E-14 5.00E-15 1.67E-16 9.00E-13 2.25E-13 5.96E-15 6.00E-13 1.50E-13
9/29/2003 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.28E-15 6.00E-13 1.50E-13
12/29/2003 l.OOE-16 9,00E-14 2.25E-14 2.54E-16 2.00E-14 5,00E-15 3.35E-16 9.00E-13 2.25E-13 6.25E-15 6.00E-13 1,50E-13
3/29/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.54E-14 6.00E-13 1.50E-13
6/27/2004 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 .2.00E-14 5.00E-15 l,OOE-16 9.00E-13 2.25E-13 3.04E-15 6.00E-13 1.50E-13
9/27/2004 l.OOE-16 9,00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.05E-14 6.00E-13 1,50E-13
12/27/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 LOOE-16 9.00E-13 2.25E-13 1.59E-14 6.00E-13 1.50E-13
3/28/2005 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 ~.OOE-13 2.25E-13 7.42E-15 6.00E-13 1.50E-13
6/29/2005 LOOE-16 9 OOE-14 2.25E-14 1.30E-16 2.00E-14 5.00E-15 1.20E-16 9.00E-13 2.25E-13 7.94E-15 6.00E-13 1.50E-13
9/26/2005 l.OOE-16 9.00E-14 2.25E-14 2,56E-16 2.00E-14 5.00E-15 2.42E-16 9.00E-13 2.25E-13 l.22E-14 6,00E-13 1.50E-13
1/3/2006 2.13E-16 9.00E-14 2.25E-14 1.04E-16 2 .. 00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 '3,73E-14 6.00E-13 1.50E-13
4/3/2006 1.62E-16 9.00E-14 2.25E-14 1.86E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.36E-15 6.00E-13 1.50E-13
7/3/2006 l.86E-16 9.00E-14 2,25E-14 l.OOE-16 ZcOOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.77E-15 6.00E-13 1.50E-13
10/2/2006 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.50E-13
1/1/2007 l.OOE-16 9.00E-14 2.25E-14 1.47E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.17E-14 6.00E-13 1.50E-13
4/2/2007 2.23E-16 9.00E-14 2.25E-14 1.63E-16 2.00E-14 5.00E-15 l.OOE-16 g.OOE-13 2.25E-13 1.65E-14 6.00E-13 1.50E-13
7/2/2007 3.35E-16 9.00E-14 2.25E-14 1.34E-16 2.00E-14 ,S.OOE-15 1.36E-16 9.00E-13 Z.25E-13 1.78E-14 6.00E-13 1.50E-13
9/30/2007 1.15E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 7.68E-15 6.00E-13 1.50E-13
12/31/2007 l.OOE-16 9,00E-14 2.25E-14 1.93E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
3/31/2008 1.14E-16 9,00E-14 2.25E-14 1.13E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 1.SOE-13
6/30/2008 7.09E-16 9,00E-14 2.25E-14 3.83E-16 2.,00E-14 S.OOE-15 2.27E-16 9.00E-13 I2.25E-13 6.52E-15 I6.00E-13 l.50E-13
Date ~ffluent Concentration Limit= 9E-14 uCi/ml BHV-1U Effluent Concentration Limit = ZE-14 uCijml BHV-lT Effluent Concentration Limit = 9E-13 uCi/ml BHV-1R Effluent Concentration Limit = pE-13 uCi/ml BHV-1PB
AlARAGoal = :Z.:ZSE-14 uCi/ml AlARA Goal= SE-13 uCi/ml AlARAGoal = 2.25E-13 uCi/ml AlARA Goal-l.SE-13 uCi/ml
Pre 1994 MPC Limit= SE-12 uCi/ml Pre 1994 MPC Limit = SE-14 uCi/ml Pre 1994 MPC Limit = :ZE-12 uCi/ml Pte 1994 MI'C.Vmit-= 4E-12 uCi/ml
Pre 1994 A lARA GOAL= 1.25E-12 uCi/ml Pre 1994 AlARA GOAL= SE-13 uCi/ml Pre 1994 AlARA GOAL = 1E-12 uCi/ml
tone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC ~FCA
9/30/2008 7.69E-16 9.00E-14 2.25E-14 2.94E-16 2.00E-14 5.00E·15 1.90E-16 9.00E-13 2.25E-13 7.64E-15 6.00E-13 1.50E-13
12/31/2008 1.21E-15 9.00E-14 2.25E-14 4.76E-16 2.00E-14 5.00E·15 3.34E-16 9.00E·13 2.25E-13 1.16E-14 6.00E-13 1.50E-13
3/15/2009 2.14E-15 9.00E-14 2.25E-14 1.02E·15 2.00E·14 S.OOE-15 1,00E-15 9.00E-13 2.25E-13 4.44E-15 6.00E·13 1.50E-13
6}15/2009 5.97E-17 9.00E-14 2.25E-14 2.35E-16 .2,00E-14 5.00E-15 2.18E-16 9.00E-13 2 25E-13 5.13E-15 G.OOE-13 1.50E-13
9/15/2009 9.55E-16 9.00E-14 2.25E-14 1.71E-16 2.00E-14 5.00E-15 9.87E-17 9.00E-13 2.25E-13 9.47E-15 6.00E·13 1.50E-13
12/15/2009 1.24E-15 9.00E-14 2.25E-14 9.25E-17 2.00E-14 5,00E-15 5.60E-17 9.00E-13 2.25E-13 5.95E-15 G.OOE-13 1.50E-13
3/31/2010 1.97E-15 t.l.OOE-14 2.25E-14 2.15E-16 2.00E-14 5.00E-15 3.27E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-13
6/30/2010 1,58E-15 9.00E-14 2.25E-14 4.71E-16 Z.OOE-14 5.00E-15 7.70E-16 9.00E-13 2.25E-13 4.07E-15 6.00E-13 1.50E-13
9}30/2010 8.42E-16 9.00E-14 2.25E-14 2.80E-16 2.00E-14 5.00E-15 1.31E-16 9.00E-13 2.25E-13 6.80E-15 G.OOE-13 1,50E-13
12/31/2010 1.27E·15 9.00E-14 2.25E-14 2.32E-16 2.00E-14 5,00E-15 2.30E-16 9.00E-13 2.25E-13 1.27E-14 6.00E-13 1.50E-13
4/4/2011 9.01E-16 ll.OOE-14 2.25E-14 1.90E-16 2.00E-14 5,00E·15 3.64E-16 9.00E-13 2.25E-13 1,09E-14 6.00E-13 1.50E-13
7/4/2011 1.59E-15 9.00E-14 2.25E-14 5.31E-16 2.00E-14 5.00E-15 4.99E-16 9,00E-13 2.25E-13 8.38E-15 6.00E-13 1.50E-13
10/3/2011 2.92E-16 S.OOE-14 2.25E·14 1.17E-16 2.00E-14 5.00E-15 li76E-17 ~.OOE-13 2.25E-13 1.14E-14 6.00E-13 1,50E-13
1/3/2012 6.73E-16 9.00E-14 2.25E-14 1.19E-16 2.00E-14 S.OOE-15 8.58E-17 9.00E-13 2.25E-13 l .73E-14 G.OOE-13 l.SOE-13
4/3/2012 7.87E-16 9.00E-14 2.25E-14 2.64E-16 2.00E-14 ·s .OOE-15 3.95E-16 9.00E-13 2.25E-13 1.25E-14 G.OOE-13 1.50E-13
7/2/2012 1.86E-15 9,00E-14 2.25E-14 8.33E-16 2.00E-14 S.OOE-15 9.85E-16 9.00E-13 2.25E-13 9.55E-15 6.00E-13 1.50E-13
10/1/2012 1.06E-15 9.00E-14 2.25E-14 2.11E-16 2.00E-14 S.OOE-15 2.34E-16 9.00E-13 2.25E-13 1.13E-14 6.00E-13 1.50E-13
12/31/2012 6.86E-16 9.00E-14 2.25E-14 1.27E-16 2,00E-14 5.00E-15 1.38E-16 S.OOE-13 2.25E-13 1.54E-14 6.00E-13 1.50E-13
3/25/2013 9.91E-16 9.00E-14 2.25E-14 1.86E-16 2,00E-14 S.OOE-15 2.04E-16 9.00E-13 2.25E-13 1.82E-14 6.00E-13 1.50E-13
7/2/2013 1.46E-16 9.00E-14 2.25E-14 3.34E-16 2.00E-14 5.00E-15 3.91E-16 9.00E-13 2.25E-13 5.78E-15 6.00E-13 l.SOE-13
9/30/2013 8.89E-16 9.00E-14 2.25E-14 9.13E-17 2.00E-14 5.00E-15 1.05E-16 9.00E-13 2.25E-13 B.OOE-15 6.00E-13 1.50E-13
12/30/2013 5.21E-16 9,00E-14 2.25E-14 4.34E-17 2.00E-14 5.00E-15 3.70E-17 9.00E-13 2.25E-13 2,59E-14 6.00E-13 1.50E-13
3/31/2014 1.07E-15 9.00E-14 2.25E-14 2.07E-16 2.00E-14 S.OOE-15 3.69E-16 9.00E-13 2.25E-13 1.24E-14 6.00E-13 1.50E-13
6/30/2014 2.24E-15 9.00E-14 2.25E-14 6.14E-16 2.00E-14 S.OOE-15 1.09E-15 9.00E-13 2.25E-13 1.23E-14 p.OOE-13 1.50E-13
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so-das
vo-das
so-das
co-das
w -das
oo-das
66-das
95-das
L6-das
96-das
95-das
v6-das
86-das
c6-das
~6-das
06-das
6s-das
ss-das
La-das
gs-das
ss-das
vs-das
ss-das
cs-das
~s-das
TAB2
BHV-2 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent Concentration Limit= 9E-14 uCi/ml BHV-ZU :effluent Concentration Limit= ZE-14 uCi/ml BHV-ZT Effluent Concentration Limit-9E-13 uCi/ml BHV-ZR ~ffluent Concentration Limit= 6E-13 uCi/ml BHV-ZPB
ALARAGoal-Z.ZSE-14 uCi/ml ALARA Goal-SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARAGoal-1.SE·13 uCi/ml_
Pre..l994 MPC Lil'l11t = , SE-12 uCi/ml Pre 1994 MPC Limit= SE-14 uCi/ml Pre J.li9,4 MpCUmlt"-2E-12 uC[/ml .Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL= 1.25E-12 uCi/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml Pre 1994 A LARA GOAL= 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA tone EFC EFCA Cone EFC EFCA
9/28/1981 1.39£-15 S.OOE-12 1.25£-12 3.69£-16 8.00£-14 2.00£-14 5.92£-16 Z.OOE-12 S.OOE-13 l.67E-14 4.00£-12 l.OOE-12
12/14/1981 4.62£-16 S.OOE-12 1.25£-12 8.03£-16 8.00£-14 2.00E-14 3.62£-16 2.00£-12 S.OOE-13 133E-14 4.00£-12 l.OOE-12
3/29/1982 7.07£-16 S.OOE-12 1.25E-12 l.lOE-15 8.00£-14 2.00E-14 '7.27E-16 2.00E-12 p.OOE-13 1.52£-14 4.00E-12 l.OOE-12
6/30/1982 8.84£-16 5.00£-12 1.25£-12 7.73£-16 8.00£-14 2.00E-14 4.78£-16 2.00£-12 S.OOE-13 1.98£-14 4.00£-12 l.OOE-12
9/27/1982 1.23£-15 5.00£-12 1.25E-12 3.60£-16 8.00£-14 2.00E-14 8.73£-16 2.00E-12 S.OOE-13 2,35£-14 4.00E-12 1,00£-12
1/3/1983 2.64E-15 S.OOE-12 1.25E-12 2.S5E-16 8.00£-14 2.00£-14 1.98£-16 Z.OOE-12 l>.OOE-13 2.85£-14 4.00E-12 l.OOE-12
4/4/1983 2.14E-16 S.OOE-12 1.25E-12 1.02£-16 8,00£-14 2.00£-14 1.57£-16 2.00E-12 S.OOE-13 2.48£-14 4.00£-12 l.OOE-12
6/30/1983 2.85£-16 5.00£-12 1.25E-12 2.06£-16 8.00E-14 2.00E-14 ,2.24£-16 Z.OOE-12 S.OOE-13 1.79£-14 4.00£-12 1.00E-12
10/3/1983 .2.70£-16 5.00£-12 1.25E-12 3.36£-16 8.00£-14 2.00E-14 4.37£-16 :Z.OOE-12 ~.OOE-13 1.78£-14 4.00£-12 1.00£-12
1/3/1984 .2.78£-15 5.00£-12 1.25E-12 1.20£-16 8,00£-14 2.00E-14 'p.64E-17 2.00£-12 S.OOE-13 9.14E-15 4,00E-12 1.00E-12
4/2/1984 4.28E-16 5.00£-12 1.25E-12 1.75E-16 8.00£-14 2.00E-14 4.57E-17 2,00£-12 ,S.OOE-13 3.55£-14 4.00E-12 1.00£-12
7/2/1984 .2.78E-15 S.OOE-12 1.25£-12 8.12£-16 8,00£-14 2.00£-14 1.98E-16 2.00£-12 S.OOE-13 1.68£-14 4.00£-12 1.00E-12
10/1/1984 2,69E-16 '5.00£-12 1.25E-12 2.66E-17 8.00£-14 2.00E-14 O.OOE+OO 2.00£-12 S.OOE-13 1.77£-14 4.00£-12 1.00£-12
1/2/1985 2.15E-16 '5.00£-12 1.25E-12 7.55£-16 8.00£-14 2.00E-14 .2.87£-16 Z.OOE-12 S.OOE-13 H9E-14 4.00£-12 1.00E-12
4/1/1985 l.OOE-16 5.00£-12 1.25E-12 1.67£-16 8.00£-14 2.00E-14 6.75£-17 Z.OOE-12 S.OOE-13 7.56£-15 4.00£-12 1.00E-12
7/1/1985 .3.70£-17 5.00£-12 1.25E-12 9.00£-16 8.00£-14 2.00£-14 4.90£-17 2.00£-12 /).OOE-13 1.31£-14 4.00£-12 l.OOE-12
9/30/1985 9.32£-17 S.OOE-12 1.25E·12 2.18£-16 8.00£-14 2.00E-14 3.71£-16 2.00E·12 S.OOE-13 3.64£-15 4.00E-12 l.OOE-12
1]2/1986 l.OOE-16 S.OOE-12 1.25E-12 2.16E-16 8.00E-14 2.00E-14 :Z.15E·17 2.00E-12 5.00E·13 ,3,04E·16 4.00E·12 1,00£-12
4]1/1986 1.31£-15 5.00£-12 1.25£-12 1.SOE-16 8.00£-14 2.00E-14 3.71£-16 2.00E·12 5.00£-13 2.90£-15 4.00E-12 l.OOE-12
6/30/1986 2.23£-16 5.00£-12 1.25E-12 1.32£-16 8.00E-14 2.00E-14 '7.09£-17 2.00£-12 5.00E-13 2.53E·14 4.00E·12 l.OOE-12
10/27/1986 15.41E-16 S.OOE-12 1.25E-12 1.74£-16 8.00E-14 2.00E-14 3.67£-16 2.00E-12 5.00E·13 1.04£-14 4.00E·12 l.OOE-12
12/15/1986 3.56E-16 $.00£-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.05£-16 2.00£-12 5.00E-13 7.81E·15 4.00E·12 l.OOE-12
3/16/1987 5.31£-16 5.00£-12 1.25E·12 1.30E-16 8.00E-14 2.00E-14 7.74£-17 2.00£-12 5.00E·13 8.80£-14 4.00E·12 l.OOE-12
5/11/1987 4.06£-16 S.OOE-12 1.25E·12 6.63£-17 8.00£-14 2.00£-14 1.34£-16 2.00E·12 S.OOE-13 l.lOE-14 4.00£-12 l.OOE-12
9/9/1987 2.74£-16 S.OOE-12 1.25E·12 2.38E-16 8.00E-14 2.00E·14 1.38£-16 2.00E-12 5.00E·13 1.04£-14 4.00£-12 1,00£-12
11/2/1987 3.73£-16 S.OOE-12 1.25E·12 3.11E·16 8.00E·14 2.00E·14 L83E-16 2.00E·12 5.00£-13 L17E-14 4.00£-12 l.OOE-12
2/16/1988 2.78£-15 S.OOE-12 1.25E-12 2.31E-17 8.00E-14 2.00E-14 1.20£-16 2.00E-12 5.00E·13 3.55E·14 4.00E·12 l.OOE-12
5/18/1988 4.63E-16 5.00£-12 1.25E·12 1.49E-16 B.OOE-14 2.00E·14 2.30£-16 2.00E-12 5.00E·13 1.18£-14 4.00£-12 l.OOE-12
8/15/1988 8.06E·16 S.OOE-12 1.25E-12 8.69£-16 B.OOE-14 2,00E-14 1.80£-16 2.00E·12 5.00E-13 1.42E-14 4.00E-12 l.OOE-12
11/14/1988 4.34£-16 S.OOE-12 1.25E·12 6.76E·16 8.00E·14 2.00E-14 1.57£-16 2.00E-12 5.00£-13 11.25£-14 4.00E-12 l.OOE-12
2/13/1989 5.80£-16 S.OOE-12 1.25E-12 2.85£-16 8.00E-14 2.00£-14 1.55£-16 2.00E-12 5.00E-13 2.80£-14 4.00E-12 l.OOE-12
5/15/1989 5.06£-16 S.OOE-12 1.25£-12 2.28£-16 8.00E-14 2.00£-14 1.63E-16 2.00E-12 5.00E-13 6.05£-15 4.00E-12 l.OOE-12
8/14/1989 4.71£-16 5,00£-12 1.25E-12 9.60E-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 5.00E-13 6.65E-15 4.00E-12 l.OOE-12
11/13/1989 1.14£-15 S.OOE-12 1.25E-12 4.08E-16 8.00E-14 2.00£-14 4.18£-16 2.00E-12 5.00£-13 1.59E-14 4.00E-12 l.OOE-12
2}12/1990 1.09£-15 ,S.OOE-12 1.25E-12 3.25E-16 8.00E-14 2.00£-14 3.74£-16 2.00E-12 5.00£-13 1.98E-14 4.00£-12 l.OOE-12
5/14/1990 9.32£-16 5.00£-12 1.25E-12 5.27£-16 8.00£-14 2.00£-14 3.97£-16 2.00E-12 5.00£-13 1.69E-14 4.00£-12 l.OOE-12
8/13/1990 1.66£-16 5.00£-12 1.25£-12 5.49£-16 8.00£-14 2.00E-14 4.75£-17 2.00E-12 5.00E-13 1.27E-15 4.00E-12 l.OOE-12
11/12/1990 6.05£-16 S.OOE-12 1.25E-12 2.64E-16 8.00E-14 2.00£-14 1.93E-16 2.00E-12 5.00E-13 2.25E-14 4.00£-12 l.OOE-12
2/11]1991 8.72£-17 5.00£-12 1.25£-12 ?.OOE-18 8.00E-14 2.00£-14 3.33E-17 2.00£-12 5.00E-13 3.49£-14 4.00E-12 l.OOE-12
5/13/1991 1.16£-16 S.OOE-12 1.25E-12 3.86E-16 8.00E-14 2.00£-14 2.80E-16 2.00E-12 5.00E-13 1.50E-14 4,00£-12 l.OOE-12
8/12/1991 9.02E-17 p.OOE-12 1.25£-12 8.82E-17 8.00E-14 2.00£-14 7.65£-17 2.00E-12 5.00E-13 1.58E-14 4.00E-12 l.OOE-12
11/11/1991 4.81£-17 5.00£-12 1.25£-12 3.82E-17 8.00E-14 2.00£-14 2.54£-17 2.00E-12 5.00£-13 1.45E-14 4.00£-12 l.OOE-12
2/10/1992 1.54£-16 5.00£-12 1.25£-12 p.82E-17 8.00E-14 2,00£-14 1.40E-17 2.00E-12 5.00£-13 3.41E-14 4.00£-12 1.00E-12
5/11/1992 2.38£-16 5.00E-12 1.25£-12 7.63E-17 S.OOE-14 2,00£-14 3.07E-17 2.00E-12 5.00£-13 1.27E-14 4,00E-12 l.OOE-12
8/10/1992 1.01£-16 S.OOE-12 1.25£-12 7.07E-17 8.00E-14 2 OOE-14 2.80E-17 2.00E-12 5.00£-13 1.41£-14 4.00£-12 l.OOE-12
11/9/1992 5.20£-17 5.00£-12 1.25£-12 3.65E-17 8.00E-14 Z.OOE-14 1.78E-17 2.00E-12 5.00E-13 1.71E-14 4.00E-12 l.OOE-12
2/9/1993 2.39£-16 S.OOE-12 1.25£-12 2.97E-17 8.00E-14 2,00£-14 6.31E-17 2.00£-12 5.00E-13 3.41E-14 4.00E-12 l.OOE-12
5/10/1993 l.OOE-16 S.OOE-12 1.25E-12 7.11E-17 8.00E-14 2.00E-14 3.19E-17 2.00E-12 5.00E-13 1.34E-14 4.00E-12 l.OOE-12
8/10/1993 1.90E-16 S.OOE-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 5.00E-13 1.80E-14 4.00E-12 l.OOE-12
11/8/1993 l.OOE-16 S.OOE-12 1.25E-12 l.OOE-16 8.00£-14 2.00£-14 l.OOE-16 2.00E-12 5.00E-13 1.49E-14 4,00E-12 l.OOE-12
2/7/1994 2.23E-16 5.00£-12 1.25E-12 l.OOE-16 8.00£-14 2.00E-14 1.84£-16 2.00E-12 5.00£-13 2.19£-14 4.00£-12 l.OOE-12
5/9/1994 2.16E-16 5.00E-12 1.25E-12 7.20E-17 8.00E-14 2.00E-14 9.89£-17 2.00E-12 5.00E-13 1.37£-14 4.00£-12 l.OOE-12
8/9/1994 9.29£-17 S.OOE-12 1.25E-12 2.96E-16 8.00E-14 2.00E-14 3.04£-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 l.OOE-12
11/7/1994 9.21E-17 S.OOE-12 1.25E-12 2.35E-16 8.00E-14 2.00E-14 1,00£-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 1 OOE-12 -
bate Effluent Concentration Limit= 9E-14 uCi/ml BHV-ZU Effluent Concentration Limit= 2E-14 uCi/ml BHV-2T Effluent Concentration Limit = 9E-13 uCi/ml BHV-2R Effluent Concentration Limit= 6E-13 uCi/ml BHV-2PB
ALARA Goal= 2.25E-14 uCi/ml ALARAGoal = .SE-13 uCi/ml ALARA Goal= 2.25E-13 uCi/ml ALARAGoal = 1.5E-13 uCi/ml
Pre 1994 MPC Limit= SE-12 uCi/ml Pre 1994 MPC Limit = BE-14 uCi/ml Pre 1994 MPC Limit-2E-12 uCi/ml Pre 1994 MPC Limit = 4E-12 uCi/ml
Pre 1994 A LARA GOAL = 1.25E-12 uCi/ml Pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1995 1.18E-16 9.00E-14 2.25E-14 9.70E-17 .l.OOE-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 7.42E-15 6.00E-13 1.50E-13
S/9/1995 9.40E-17 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 3.50E-16 9.00E-13 2.25E-13 3.90E-15 6.00E-13 1.50E-13
'8/9/1995 8.90E-17 9.00E-14 2.25E-14 9.67E-17 l .OOE-14 5.00E-15 1.35E-16 9.00E-13 2.25E-13 2.38E-16 6.00E-13 1.50E-13
11/11/1995 2.83E-15 9.00E-14 2.25E-14 4.09E-16 2.00E-14 5.00E-15 5.23E-16 9.00E-13 2.25E-13 6.77E-15 6.00E-13 1.50E-13
.2/5/1996 1.75E-15 9.00E-14 2.25E-14 8.66E-16 .2.00E-14 5.00E-15, 4.86E-16 9.00E-13 2.25E-13 3.50E-15 6.00E-13 1.50E-13
5/6}1996 1.40E-16 9.00E-14 ~.25E-14 1.15E-16 2.00E-14 '>.OOE-15 l.OOE-16 9.00E-13 2.25E-13 6.85E-15 6.00E-13 1.50E-13
8/5}1996 1.43E-16 9.00E-14 ;1.25E-14 2.78E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 ,5.83E-15 6.00E-13 1.50E-13
11/6/1996 1.45E-16 9.00E-14 2.25E-14 1.57E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.19E-14 6.00E-13 1.50E-13
2/6/1997 1.00E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.84E-16 6.00E-13 1.50E-13
5/5/1997 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 2.00E-14 5,00E-15 l.OOE-16 9.00E-13 2.25E-13 3.89E-15 6.00E-13 1.50E-13
8/11/1997 l.OOE-16 9.00E-14 2.25E-14 1.09E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.69E-15 6.00E-13 1.50E-13
1/5/1998 2.55E-16 9.00E-14 ,2.25E-14 1.07E-16 ,2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 5.11E-15 6.00E-13 1.50E-13
4/28/1998 1.20E-16 9.00E-14 2.25E-14 1.71E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 2.25E-13 6.40E-15 6.00E-13 1.50E-13
7/31/1998 1.47E-16 9.00E-14 2,25E-14 4.24E-16 2.00E-14 5.00E-15 3.39E-16 9.00E-13 2.25E-13 4.80E-15 6.00E-13 1.50E-13
9/28/1998 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 l.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 4.26E-15 6.00E-13 1.50E-13
12/28/1998 2.54E-16 9.00E-14 2.25E-14 2.15E-16 2.00E-14 5.00E-15 1.38E-16 9.00E-13 2.25E-13 6.88E-15 6.00E-13 1.50E-13
3/29/1999 1.07E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.61E-15 6.00E-13 1.50E-13
7/3/1999 2.46E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.95E-15 6.00E-13 1.50E-13
'9/27/1999 2.81E-16 9.00E-14 2.25E-14 1.41E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2,25E-13 7.35E-15 6.00E-13 1.50E-13
12/28/1999 5.20E-16 9.00E-14 2.25.E-14 2.60E-16 2.00E-14 5,00E-15 2.01E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.50E-13
3/27/2000 l.OOE-16 9.00E-14 2,25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.12E-15 6.00E-13 1.50E-13
6/26/2000 l.lOE-16 9.00E-14 2.25E-14 l.OOE-16 l.OOE-14 5.00E-15 1.16E-16 9.00E-13 2.25E-13 5.07E-15 6.00E-13 1.50E-13
'l/26/2000 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.31E-15 6,00E-13 1.50E-13
12/26/2000 1.26E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.45E-15 6,00E-13 1.50E-13
3/26/2001 l.OOE-16 9.00E-14 ,2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.95E-15 6,00E-13 1.50E-13
7/2/2001 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 l.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.56E-15 6.00E-13 1.50E-13
9/24/2001 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9 OOE-13 2 25E-13 6.16E-15 6.00E-13 1.50E-13
12/31/2001 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 2.20E-15 6.00E-13 1.50E-13
4/1/2002 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.95E-15 6.00E-13 1.50E-13
7/1/2002 1.25E-16 9.00E-14 2.25E-14 1.43E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.25E-15 6.00E-13 1.50E-13
9/30/2002 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 3.69E-15 6.00E-13 1.50E-13
12/30/2002 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 .l.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.91E-15 6.00E-13 1.50E-13
3/31/2003 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.16E-15 6.00E-13 1.50E-13
6/30/2003 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 .l.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.27E-15 6.00E-13 1.50E-13
9/29/2003 l.OOE-16 9.00E-14 2,25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.23E-15 6.00E-13 1.50E-13
12/29/2003 l.OOE-16 9.00E-14 ,2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.80E-15 6.00E-13 1.50E-13
3/29/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 2.04E-14 6.00E-13 1.50E-13
6/27/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9 OOE-13 2.25E-13 3.09E-15 6.00E-13 1.50E-13
9/27/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5,00E-15 l.OOE-16 9.00E-13 2.25E-13 1.73E-14 6.00E-13 1.50E-13
12/27/2004 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2,25E-13 1.30E-14 6.00E-13 1.50E-13
3/28/2005 l.OOE-16 9.00E-14 2,25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9,00E-13 2.25E-13 8.88E-15 6,00E-13 1.50E-13
6/29/2005 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9,00E-13 2,25E-13 8.85E-15 6.00E-13 1.50E-13
9/26/2005 l.OOE-16 9.00E-14 ,2.25E-14 1.99E-16 .l.OOE-14 5.00E-15 1.44E-16 9,00E-13 2,25E-13 3.81E-14 6,00E-13 1,50E-13
1/3/2006 1.29E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 4.08E-16 9.00E-13 2.25E-13 6.58E-14 6.00E-13 1,50E-13
4/3/2006 1.02E-16 9.00E-14 ,2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.08E-14 6,00E-13 1.50E-13
7/3/2006 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 1.50E-13
10/2/2006 1.30E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.68E-14 6,00E-13 1.50E-13
1/1/2007 1.24E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5,00E-15 l.OOE-16 9.00E-13 2.25E-13 1.38E-14 6.00E-13 1.50E-13
4/2/2007 1.40E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.63E-14 6.00E-13 1.50E-13
7/2/2007 1.04E-16 9.00E-14 2.25E-14 l.OOE-16 7-00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.36E-14 6.00E-13 1.50E-13
9/30/2007 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 l.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.24E-15 6.00E-13 1.50E-13
12/31/2007 1.91E-16 9.00E-14 ,2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.18E-14 6.00E-13 1.50E-13
3/30/2008 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.49E-15 6.00E-13 1.50E-13
6/30/2008 1.29E-16 9.00E-14 :2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1,00E-16 9.00E-13 2.25E-13 4.82E-15 6.00E-13 1.50E-13
Date Effluent Concentration Limit = 9E-14 u(i/ml BHV-2U Effluent Concentration Limit -ZE-14 uCi/ml BHV-2T Effluent Concentration Limit-9E-13 uCi}ml BHV-2R Effluent Concentration Limit= 6E-13 uCi/ml BHV-2PB
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal-SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARAGoal = 1.5E-13 uCi/ml
Pre 1994 MPC Limit-SE-12 uCi/ml Pre 1994 MPC"timlt= BE-14 uCi/ml , Pre 1994 MPC Limit = 2E-12 uCi/ml Pre 1994 MPC Limit = 4E-12 uCi/ml
Pre 1994 ALARA GOAL= l.25E-12 uC[/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml Pre 1994 ALARA GOAL= 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/3Q/2008 2.73E-16 9.00E-14 2.25E-14 1.00E-16 2,00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 8.30E-15 6.00E-13 1.50E-13
12/31/2008 5,71E-16 9.00E-14 Z.25E-14 1.61E-16 2.00E-14 5.00E-15 1.25E-16 9.00E-13 2.25E-13 2.04E-14 6.00E-13 1.50E-13
3/15/2009 3.96E-16 9.00E-14 2.25E-14 1.38E-16 2.00E-14 5.00E-15 1.07E-16 9.00E-13 2 25E-13 4.81E-15 6.00E-13 1.50E-13
6/15/2009 1.24E-17 9.00E-14 2.25E-14 4.64E-17 2.00E-14 5.00E-15 5.11E-17 9.00E-13 2.25E-13 4.58E-15 6.00E-13 1.50E-13
9/15/2009 2.43E-16 9.00E-14 2.25E-14 5.28E-17 2.00E-14 5.00E-15 4.84E-17 9.00E-13 2.25E-13 1.19E-14 6.00E-13 1.50E-13
12/15/2009 5.72E-16 9.00E-14 2.25E-14 2.94E-17 Z.OOE-14 5,00E-15 2.57E-17 9.00E-13 2.25E-13 6.70E-15 6.00E-13 1.50E-13
3/31/2010 5.47E-16 9.00E-14 2.25E-14 1.42E-17 2.00E-14 5,00E-15 4.66E-17 9.00E-13 2.25E-13 8.24E-15 6.00E-13 1.50E-13
6/30/2010 3.58E-16 9.00E-14 2.25E-14 6.64E-17 2.00E-14 5.00E-15 9.90E-17 9.00E-13 2.25E-13 .2.01E-15 6.00E-13 l.50E-13
9/30/2010 2.91E-16 9.00E-14 2.25E-14 4.48E-17 Z.OOE-14 5.00E-15 S.72E-17 9.00E-13 2.25E-13 l.OBE-15 6.00E-13 1.50E-13
12/31/2010 5.73E-16 .9.00E-14 2.25E-14 7.24E-17 2.00E-14 5.00E-15 .6.76E-17 9.00E-13 2.25E-13 1.35E-14 6.00E-13 1.50E-13
4/4/2011 3.79E-16 9.00E-14 2.25E-14 4.01E-17 2.00E-14 5.00E-15 9.11E-17 9,00E-13 .2.25E-13 1.06E-14 6.00E-13 1.50E-13
7/4/2011 3.07E-16 9.00E-14 2.25E-14 8.54E-17 2,00E-14 5.00E-15 9.21E-17 9.00E-13 2.25E-13 7.21E-15 G.OOE-13 1.50E-13
10/3/2011 1.17E-16 9.00E-14 2.25E-14 3,04E-17 2,00E-14 5.00E-15 .2.81E-17 9.00E-13 2.25E-13 1.03E-14 6.00E-13 1.50E-13
1/3/2012 ,3,65E-16 9.00E-14 2.25E-14 2.72E-17 2.00E-14 5.00E-15 4.54E-17 9.00E-13 2.25E-13 1.58E-14 G.OOE-13 1.50E-13
4/3/2012 4.22E-16 9.00E-14 2.25E-14 1.15E-16 Z.OOE-14 5.00E-15 ;2.77E-16 9.00E-13 2.25E-13 1.58E-14 p.OOE-13 1.50E-13
7/2/2012 3.39E-16 9.00E-14 2.25E-14 1.56E-16 2.00E-14 5.00E-15 1.74E-16 9.00E-13 2.25E-13 8.60E-15 6.00E-13 1.50E-13
10/1/2012 3.13E-16 9.00E-14 2.25E-14 4.13E-17 Z.OOE-14 5.00E-15 3.04E-17 9.00E-13 2.25E-13 1.03E-14 6.00E-13 1.50E-13
12/31/2012 1.76E-16 9.00E-14 2.25E-14 5.41E-17 Z.OOE-14 5.00E-15 7.05E-17 9.00E-13 .2.25E-13 1.48E-14 6.00E-13 1.50E-13
3/25/2013 .3.38E-16 9.00E-14 2 25E-14 3.94E-17 2.00E-14 5.00E-15 8.32E-17 9.00E-13 2.25E-13 1.42E-14 6.00E-13 1.50E-13
7/2/2013 4.06E-16 9.00E-14 2.25E-14 4.89E-17 Z.OOE-14 5.00E-15 8.06E-17 9.00E-13 2.25E-13 4.93E-15 6.00E-13 1.50E-13
9/30/2013 1.76E-16 9.00E-14 2.15E-14 2.52E-17 2.00E-14 5.00E-15 6.13E-17 9.00E-13 2.25E-13 4.90E-15 6.00E-13 1.50E-13
12/30/2013 6.20E-16 9.00E-14 2.25E-14 4.19E-17 2.00E-14 5.00E-15 3.72E-17 9.00E-13 2.25E-13 r5oE-14 6.00E-13 1.50E-13
3}31/2014 4.63E-16 9.00E-14 2.25E-14 4.97E-17 2.00E-14 5.00E-15 1.15E-16 9.00E-13 2.25E-13 1.49E-14 S.OOE-13 1.50E-13
6/30/2014 3.04E-16 9.00E-14 2.25E-14 7.92E-17 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.21E-14 p.OOE-13 1.50E-13
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TAB3
BHV-3 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent Concentration Limit= 9E-14 uCi/ml .BHV-3U Effluent Concentration Limit = ZE-14 uCi/ml BHV-3T Effluent Concentration Limit= 9E-13 uCi/ml aHV-3R Effluent Concentration Limit= 6E-13 uCi/ml BHV-3PB
AlARAGoal-2.Z5E·14 uCi/ml AlARAGoal-SE-13 uCi/ml ALARAGoal = 2.Z5E-13 uCi/ml AlARAGoal= 1.5E-13 uCi/ml
Prn-1994 MPC Limit~ SE-12 uCi/ml Pre 1994 MPC Limit = SE-14 uCi/ml Pre 1994 MPC Umlr-< 2E-1Z uCi/ml Pre 1994 MPC Limit = IIE-12 uCi/ml
Pre 1994 AlARA GOAL= l.ZSE-12 uCi/ml Pre 1994 ALARA GOAL= 5E·13 uCi/ml Pre 1994 AlARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 1.74E-15 S.OOE-12 1.25E-12 9.02E-16 8.00E-14 2.00E-14 2.87E-16 2.00E·12 S.OOE-13 1.54E-14 4.00E-12 1.00E-12
12/14/1981 1.59E-15 S.OOE-12 1.25E-12 5.03E-16 8.00E-14 2.00E-14 1.30E-16 2.00E-12 S.OOE-13 2.2SE-14 4.00E·l 2 l.OOE-12
3/29/1982 3.76E-16 S.OOE-12 1.25£-12 5.25£-16 8.00£-14 2.00£-14 4.08£-16 2.00£-12 S.OOE-13 1.96£-14 4.00£-12 l.OOE-12
6/30/1982 3.83E-16 5,00£-12 1.25£-12 2.16£-16 8.00£-14 2.00£-14 1.41£-15 2.00£-12 5.00£-13 2.40£-14 4.00£-12 l.OOE-12
9/27/1982 5.95E-16 5.00E-12 1.25E-12 1.44£-15 8.00£-14 2.00£-14 5.36£-16 2 OOE-12 S.OOE-13 1.43£-14 4.00£-12 l.OOE-12
1/3/1983 2.05E-16 S.OOE-12 1.25£-12 1.23E-16 8.00E-14 2.00£-14 l.lOE-16 2.00£-12 S.OOE-13 3.01E-14 4.00£-12 1.00E-12
4/4/1983 l.OOE-16 5.00E-12 1.25E-12 6.94E-17 8.00E-14 2.00£-14 6.11£-17 2.00E-12 S.OOE-13 1.39E-14 4.00£-12 l.OOE-12
6/30/1983 3.06E-16 5.00E-12 1.25E-12 9.59E-17 8.00E-14 2.00E-14 2.08E-16 2.00E-12 5.00E-13 1.70E-14 4.00E-12 l.OOE-12
10/3/1983 1.91E-16 5.00E-12 1.25£-12 3.05E-16 8.00£-14 2.00E-14 2.79£-16 2.00£-12 5.00£-13 1.76£-14 4.00£-12 l.OOE-12
1/3/1984 3,01£-16 5.00E-12 1.25£-12 9.51E-17 8.00£-14 2.00£-14 1,00£-16 2,00E·12 5.00E-13 9.17£-15 4.00£-12 l.OOE-12
4/2/1984 8.22£-16 5.00£-12 1.25£-12 7,52£-16 8,00£-14 2.00£-14 5.20£-17 2.00E-12 5.00E-13 3,47£-14 4.00£-12 l.OOE-12
7/2/1984 5.29£-16 5.00£-12 1.25£-12 6.18£-16 8,00£-14 2.00£-14 1.40£-16 2.00E-12 5.00£-13 1.32£-14 4.00£-12 l.OOE-12
10/1/1984 1.74£-16 5.00£-12 1.25£-12 7.10£-17 8.00£-14 2,00£-14 l.OOE-16 2.00£-12 5.00£-13 1.08E-14 4.00£-12 1.00E-12
1/2/1985 1.00E-17 S.OOE-12 1.25£-12 7.10£-17 B.OOE-14 2.00E-14 7.80E-17 2.00E·12 5.00E-13 2.73E-14 4.00E-12 1.00E-12
4/1/1985 1.00E-16 S.OOE-12 1.25£-12 2.76£-16 8.00£-14 2.00E-14 4.10£-17 2.00£-12 5.00£-13 1.12£-14 4.00£-12 1.00£-12
7/1/1985 1.04E-16 5.00£-12 1.25£-12 l.OOE-16 8.00£-14 2.00£-14 l.OOE-16 2.00£-12 5.00£-13 1.64E-14 4.00£-12 1.00E-12
9/30/1985 1.00£-16 5.00£-12 1.25£-12 l.OOE-15 S.OOE-14 2.00£-14 l.OOE-16 2.00£-12 5.00£-13 1.73£-14 4.00£-12 1,00£-12
1/2/1986 1.03£-15 S.OOE-12 1.25£-12 3.17E-16 S.OOE-14 2.00£-14 1.25£-16 2.00E·12 5.00£-13 1.21E-17 4.00E-12 1.00£-12
4/1/1986 8.04£-16 S.OOE-12 1.25£-12 1.93E-17 B.OOE-14 2.00E-14 1.54£-16 2.00E-12 5,00£-13 1.69£-14 4.00£-12 1.00E-12
6/30/1.9.86 4.29E-16 5.00E-12 1.25£-12 1.77E-16 8 OOE-14 2.00£-14 2.83E-16 2.00E·12 5.00E-13 1.97E-14 4,00E-12 l.OOE-12
10/27/1!}86 6.45E-16 S.OOE-12 L2SE·12 9.89E-17 B.OOE-14 2.00E-14 4.16£-15 2.00£-12 5,00E-13 1.64£-14 4.00E-12 1.00E-12
12/15/1986 1.31£-16 S.OOE-12 1.25E-12 O.OOE+OO 8.00£-14 2.00E-14 4.16£-17 2.00E·12 5.00E-13 4.60£-15 4.00£-12 l.OOE-12
3/16/1987 2.01E-16 5.00E-12 1.25E-12 1.20£-16 8.00£-14 2.00£-14 5.73£-17 2.00E·12 5.00£-13 1.60£-14 4.00£-12 l.OOE-12
5/11/1987 :2.16£-16 5.00E-12 1.25£-12 1.96E-16 8,00£-14 2.00£-14 7.38E-17 2.00E-12 5.00£-13 1.59£-14 4.00£-12 l.OOE-12
9/9/1987 2.41E-16 5.00£-12 1.25E-12 2.18E-16 8.00£-14 2.00£-14 3.52£-17 2.00E·12 5.00E-13 1.46E-14 4.00£-12 1.00E-12
11/2/1987 2.44£-16 5.00£-12 1.25£-12 2.32E-16 8.00E-14 2.00£-14 l.37E-17 2.00E·12 S.OOE-13 2.48E-14 4.00£-12 l.OOE-12
2/16/1988 8.08E-16 5.00E-12 1.25E-12 2.55E-16 8,00£-14 2.00E-14 3.42E-16 2.00E-12 S.OOE-13 S.61E-14 4.00E-12 1,00E-12
5/18/1988 1.14E-16 5.00E-12 1.25E-12 4.14E-17 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 5.00E-13 1.20E-14 4.00E-12 l.OOE-12
8/15/1988 2.08£-16 5.00E-12 1.25E-12 3.06E-16 8.00£-14 l.OOE-14 3.65£-17 2.00£-12 ~.OOE-13 1.36£-14 4.00E-12 l.OOE-12
11/14/1988 4.21£-16 S.OOE-12 1.25E-12 2.93£-16 8.00£-14 2.00£-14 1.09£-16 2.00£-12 5.00E-13 2.48£-14 4.00£-12 l.OOE-12
2/13/1989 4.45E-16 5.00E-12 1.25E-12 4.78E·17 8.00£-14 2.00E-14 2.47E-17 l.OOE-12 S.OOE-13 3.34£-14 4.00E-12 l.OOE-12
5/15/1989 1.05£-16 5.00£-12 1.25£-12 l.OOE-16 8.00E-14 2.00E-14 2.45£-17 2.00E·12 S.OOE-13 6.56£-15 4.00£-12 l.OOE-12
8/14/1989 1.31£-16 5.00£-12 1.25£-12 5.85E-17 8.00E-14 2.00£-14 3.97£-17 2.00E·12 5.00£-13 6.75E-15 4,00E·12 l.OOE-12
1.1/.13/19&9 1.67E-16 5.00E-12 1.25£-12 3.87E-17 8.00E-14 'Z.OOE-14 8.03E-17 2.00£-12 5.00E-13 1.69E-14 4.00£-12 l.OOE-12
2/12/1990 4.43£-16 S.OOE-12 1.25E-12 l.OOE-16 8.00E·14 z.OOE-14 3.50E-17 2.00£-12 5.00£-13 2.37£-14 4.00E-12 l.OOE-12
5/14/1990 3.84£-16 S,OOE-12 1.25E-12 2.54£-16 8.00£-14 2.00E-14 1,02£-16 2.00£-12 5.00E·13 1.68£-14 4.00E-12 l.OOE-12
'M13/1990 7.27E-17 S.OOE-12 1.25E-12 2.87E-16 8.00E-14 2.00£-14 1.21E-17 2.00E-12 5.00£-13 7.86£-15 4.00£-12 l.OOE-12
11/12/1990 1.84E-16 S.OOE-12 1.25E-12 1.34E-16 8.00E-14 2.00£-14 8.53£-17 2.00E·12 5.00E-13 2.01£-14 4.00£-12 l.OOE-12
2/11/1991 4.66E-17 5.00E-12 1.25E-12 8.48£-16 B.OOE-14 2.00£-14 1.94£-17 2.00E-12 5.00E·13 3.69£-14 4.00£-12 1,00E·12
5/13/1991 5.05E-17 5.00E-12 l.25E-12 7.40E-17 B.OOE-14 2.00E-14 7.00E-18 2.00E-12 5.00E-13 1.SOE·14 4.00E-12 l.OOE-12
8/12/1991 7.14£-17 5.00E-12 1.25E-12 6.22E-17 B.OOE-14 2.00E-14 7.95E-17 l.OOE-12 5,00E-13 1.77E-14 4.00E-12 l.OOE-12
11/11/1991 1.41E-17 5,00E-12 1.25£-12 2.19£-18 B.OOE-14 2.00E-14 2.75E-17 2.00£-12 5.00£-13 1.18£-14 4.00£-12 l.OOE-12
2/10/1992 8.12£-17 o.OOE-12 1.25£-12 2.35E-17 8.00£-14 2.00E-14 2.76E-18 2.00£-12 5.00E-13 3.57£-14 4.00£-12 1,00£-12
5/11/1992 9.18E-17 S,OOE-12 1.25E-12 5.80£-17 B.OOE-14 2.00£-14 3,36E-17 2.00£-12 5.00£-13 1.28£-14 4.00£-12 l.OOE-12
8/-10/1992 2.00E-18 S.OOE-12 l.25E-12 4.19E-17 B.OOE-14 2.00£-14 2.00£-18 2.00E-12 5.00£-13 1.59E-14 4.00£-12 1,00E-12
11/9/1992 4.00E-17 S.OOE-12 1.25£-12 2.68£-17 B.OOE-14 2.00£-14 1.07£-17 2.00E-12 5.00£-13 1.81£-14 4.00E-12 1.00£-12
2/9/1993 7.94E-17 S.OOE-12 1.25E-12 l.OOE-16 B.OOE-14 2,00£-14 1.09£-16 2.00E·12 5.00£-13 2.69E-14 4.00£-12 l.OOE-12
5/10/1993 1.60£-17 5.00E-12 1.25E-12 5.07£-17 B.OOE-14 2.00£-14 7.64£-17 2.00£-12 5.00E-13 1.26E-14 4.00£-12 l.OOE-12
8/J0/19'33' 6.00£-17 S.OOE-12 1.25E-12 6.00£-18 /3.00£-14 2.00£-14 l.OOE-16 2.00E-12 5.00£-13 1.50E-14 4.00£-12 1.00£-12
11/8/1993 l.OOE-16 S.OOE-12 1.25£-12 l.OOE-16 8.00E-14 2.00£-14 l.OOE-16 2,00E·12 5.00£-13 2.10£-14 4.00£-12 l.OOE-12
2/7/1994 1,61E-16 S.OOE-12 1.25£-12 1.00E-16 8.00E-14 2.00£-14 2.22E-16 .2.00£-12 S.OOE-13 2.23£-14 4.00£-12 l.OOE-12
5/9/1994 2.77£-16 S.OOE-12 1.25£-12 2.80£-17 8,00E-14 2.00£-14 8.37E-18 2.00£-12 S.OOE-13 1.40£-14 4.00£-12 l.OOE-12
8/9/1994 7.39E-17 5.00E-12 1,25E-12 l.OOE-16 8.00E-14 2.00£-14 1.14E-16 2.00E·12 5.00E-13 l.OOE-16 4.00£-12 l.OOE-12
11/7/1994 9.05£-17 5.00£-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 l.OOE-16 2.00E·12 5.00E-13 l.OOE-16 4.00£-12 l.OOE-12
Date Ufluent Concentration Limit= 9E-14 uCi/ml BHV-3U Effluent Concentration Limit= 2E-14 uCi/ml BHV-3T Effluent Concentration Limit= 9E-13 uCi/ml BHV-3R Effluent Concentration Limit= 6E-13 uCi/ml BHV-3PB
ALARAGoal-2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml .ALARA Goal = 2.2SE-13 uCi/ml ALARAGoal = 1.5E-13 uCi/ml
Pre 1994 MPC Limit= SE-12 uCi/ml PrU9!i4 MPC Umll " SE-14 uCi/ml Pre 1994 MPC Limit= 2E-12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL= 1.25E-12 uCi/ml Pre 1994 ALARA GOAL-SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2}7/1995 7.99E-17 9.00E-14 2.25E·14 9.60E-17 2.00E-14 5.00E-15 9.60E-17 9.00E-13 2.25E-13 9 05E-15 6.00E-13 1.50E-13
5/9/1995 9.40E-17 9.00E-14 2.25E-14 9.80E-17 2.00E-14 5.00E-15 8.60E-17 9.00E-13 2.25E-13 2.88E-15 6.00E-13 1.SOE-13
8/9/1995 7.30E-17 9.00E-14 2.25E-14 9.20E-17 Z.OOE-14 5.00E-15 4.40E-17 9 OOE-13 2.25E-13 1.96E-15 6,00E-13 1.50E-13
U/U/1.9<J.S 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
2/5/1996 3.41E-16 ~.OOE-14 2.25E-14 2.26E-16 Z.OOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6,00E-13 1.50E-13
5/6/1996 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
8/5/1996 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 .3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
l.l/6/1996 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
2/6/1997 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9,00E-13 2.25E-13 2.69E-14 G.OOE-13 1.50E-13
5/5/1997 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
8/11/1997 3.00E-16 9,00E-14 2.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 G.OOE-13 1.50E-13
1/5/1998 3,16E-16 9.00E-14 2.25E-14 1.31E-16 Z.OOE-14 5.00E-15 p.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
4/28/1998 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E·15 1.18E-16 9,00E-13 2.25E-13 Z.69E-14 6.00E-13 1.50E-13
7/31/1998 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6,00E-13 1.50E-13
9/28!1998 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9,00E-13 2.25E·13 1.31E-14 6.00E-13 1.50E-13
12/28/1998 3.16E-16 9,00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/29/1999 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5,00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/3/1999 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/27}1999 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1,31E-14 6.00E-13 1.50E-13
12/28/1999 3.16E-16 9.00E-14 2.25E-14 1.31E-16 ~.OOE-14 5.00E-15 6.58E-17 9,00E-13 2.25E-13 1,91E-14 6.00E-13 1.50E·13
3/28/2000 3.41E-16 9.00E-14 2.25E-14 2.26E-16 l.OOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6,00E-13 1.50E-13
6/26/2000 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5,00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/26/2000 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
12/26/2000 3.16E-16 9.00E-14 2.25E-14 1.31E-16 Z.OOE-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/26/2001 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9,00E-13 2.25E-13 2.69E-14 6.00E-13 1,50E-13
7/2/2001 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/24/2001 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5,00E-15 3.99E-16 9,00E-13 2 25E-13 1.31E-14 6.00E-13 1.50E-13
12/31/2001. 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5,00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6,00E-13 1.50E-13
4/1/2002 3.41E-16 9.00E-14 2.25E-14 2.26E-16 Z.OOE-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/1/2002 1.31E-16 9.00E-14 2.25E-14 1.39E-16 Z.OOE-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1,50E-13
9/3Q/2002 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 !3.DOE-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
12/30/2002 3.16E-16 9.00E·14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/31/2003 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E·13 2.69E-14 6,00E·13 1.50E-13
6/30/2003 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/29/2003 a.OOE-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 1.25E-13 1.31E-14 6.00E-13 1.50E-13
12/29/2003 3.16E-16 9.00E-14 2.25E-14 1,31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/29/2004 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2,00E-14 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.SOE-13
6/27/2004 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2,00E-14 S.OOE-15 1.82E-16 9.00E-13 2 25E-13 1.53E-14 6.00E-13 1.50E-13
9j27/2004 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6,00E-13 1.50E-13
12/27/2004 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 G.OOE-13 1.50E-13
3/28/2005 3,41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
6/29/2005 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/26/2005 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9,00E-13 2.25E-13 1.31E-14 6,00E-13 L50E-13
1/3/2006 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
01/3/2006 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5,00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/3f2oo6 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
10/2/2006 3.00E-16 9.00E-14 2.25E-14 3.43E-16 Z,OOE-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1,31E-14 6.00E-13 l .SOE-13
1/1/2006 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2,25E-13 1.91E-14 6,00E-13 1.50E-13
4/2/2007 3.41E-16 ,.OOE-14 2,25E-14 2.26E-16 2,00E-14 5,00E-15 1.18E-16 9,00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/212007 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5,00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6,00E-13 1.50E-13
9/30/2007 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
12/31/2007 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2,00E-14 5.00E-15 p.58E-17 9 OOE-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/31/2008 3.41E-16 9.00E·14 2.25E-14 2.26E-16 Z.OOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
6/30/2008 1.31E-16 9.00E-14 2,25E-14 1.39E-16 2.00E-14 S,OOE-15 1.82E-16 ~.OOE-13 2.25E-13 1.53E-14 6.00E-13 l.SOE-13
Date Effluent Concentration Limit-9E-14 uCi/ml 1!HV-3U Effluent Concentration Limit-ZE-14 uCi/ml BHV-3T Effluent Concentration Limit -9E-13 uCi}ml BHV-3R Effluent Concentration Limit-6E-13 uCi/ml BHV-3PB
ALARAGoal-2.2SE-14 uCi/ml ALARAGoal-SE-13 uCi/ml ALARA Goal-2.25E-13 uCi/ml ALARA Goal -l.SE-13 uCi/ml
Pre:19!14 MPC Limit= SE-12 uCi/ml Pre 1994 MPC Limit= BE-14 uCi/ml Pre 1994 MPC Limit= 2E-12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL = 1.2SE·12 uCi/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/30/2008 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 G.OOE-13 1.50E-13
12/31/2008 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 G.OOE-13 L50E-13
3/15/2009 3.41E-16 ·9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 G.OOE-13 1.50E-13
6/15/2009 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 p.OOE-13 1.50E-13
9/15/2009 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-l3 1.31E-14 6.00E-13 1.50E-13
12/lS/2009 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 G.OOE-13 1.50E-13
3/31/2010 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 1.18E-16 9.00E-13 2,25E-13 2.69E-14 6.00E-13 1.50E-13
6/30/2010 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 G.OOE-13 1.50E-13
9/30/2010 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 S,OOE-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
12/31/2010 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
4/4/2011 3.41E-16 9.00E-14 2.25E-14 2.26E-16 Z.OOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2,69E-14 6.00E-13 1.50E-13
7/4/2011 1.31E-16 S.OOE-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
10/3/2011 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5,00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
1/3/2012 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 L91E-14 6.00E-13 l.SOE-13
4/3/2012 3.41E-16 9.00E-14 2.25E-14 2.26E-16 Z.OOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/2/2012 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 G.OOE-13 1.50E-13
10/1/2012 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5,00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 G.OOE-13 1.50E-13
12/31/2012 3.16E-16 9,00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 G.OOE-13 1.50E-13
3/25/2013 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/2/2013 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S,OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 G.OOE-13 1.50E-13
9/30/2013 3.00E-16 9.00E-14 i.25E-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 G.OOE-13 1.50E-13
12/30/2013 3.16E-16 9.00E-14 2.25E-14 1,31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 G.OOE-13 1.50E-13
3/31/2014 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 1.18E-16 9,00E-13 2.25E-13 2.69E-14 G.OOE-13 1.50E-13
6/30/2014 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 G.OOE-13 1.50E-13
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TAB4
BHV -4 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent Concentration Limit= 9E-14 uCi/ml 'BHV-4U Effluent Concentration Limit-2E-14 uCi/ml BHV-4T Effluent Concentration Limit-9E-13 uCi/ml BHV-4R Effluent Concentration Limit= 6E-13 uC[/ml BHV-4PB
ALARA Goal= 2.25E-14 uCi/ml ALARA Goal= SE-13 uCi/ml ALARA Goal= 2.25E-13 uCi/ml ALARAGoal = 1.5E-13 uCi/ml
Pre 1994 MPC Limit = SE-12 uCi/ml Pre:·1994 MK limit = BE-14 uCi/ml Pre 1994 MPC Limit = 2E·12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL= :J..25E-12 uCi/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml Pre 1994 A LARA GOAL= 1E-12 uCi/ml
Cone EFC EFCA Cone HC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 5.20E-15 S.OOE-12 1.25E-12 2,93E-15 8.00E-14 2.00E-14 2.74E-15 2.00E-12 S.OOE-13 1,84E-14 4.00E-12 1.00E-12
12/14/1981 4.53E-15 S.OOE-12 1.25E-12 1.78E-15 B.OOE-14 2,00E-14 2.29E-15 2.00E-12 S.OOE-13 2.54E-14 4.00E-12 l.OOE-12
3/29/1982 1.06E-15 S.OOE-12 1.25E-12 1.42E-14 I!.OOE-14 2.00E-14 1.07E-15 2.00E-12 5.00E-13 2.31E-14 4.00E-12 l.OOE-12
6/30/1982 6,03E-15 S,OOE-12 1.25E-12 1.57E-14 s.OOE-14 2.00E-14 2.62E-15 2.00E-12 5.00E-13 2.25E-14 4.00E-12 l.OOE-12
9/27/1982 1.26E-14 5.00E-12 1.25E-12 7.58E-16 KOOE-14 2.00E-14 5.35E-15 2.00E-12 5.00E-13 2.68E-14 4.00E-12 l.OOE-12
1/3/1983 ,4.33E-15 5.00E-12 1.25E-12 6.52E-16 8.00E-14 2.00E-14 6.04E-16 2.00E-12 5,00E-13 2.57E-14 4.00E-12 l.OOE-12
4/4/1983 1.25E-15 S.OOE-12 1.25E-12 7.17E-16 8.00E-14 2.00E-14 6.76E-16 2,00E-12 5.00E-13 2.00E-14 4.00E-12 l.OOE-12
6/30/1983 3.73E-16 S.OOE-12 1.25E-12 9.43E-16 S.OOE-14 2.00E-14 4.13E-16 2,00E-12 5.00E-13 1,20E-14 4,00E-12 l.OOE-12
10/3/1983 2.54E-16 S.OOE-12 1.25E-12 1.51E-16 S.OOE-14 2.00E-14 2.6SE-16 2.00E-12 S.OOE-13 2.SOE-14 4.00E-12 l.OOE-12
1/3/1984 2.76E-15 5.00E-12 1.25E-12 1.60E-16 S.OOE-14 2.00E-14 l.OSE-16 2.00E-12 5.00E-13 1,59E-16 4.00E-12 1,00E-12
4/2/1984 ,4.27E-16 S.OOE-12 1.25E-12 2.33E-16 8.00E-14 2.00E-14 6.28E-16 2.00E-12 5.00E-13 3.67E-14 4.00E-12 l.OOE-12
7/2/1984 2.57E-15 S,OOE-12 1.25E-12 1.36E-16 8.00E-14 2.00E-14 1.11E-16 2.00E-12 5.00E-13 1.58E-14 4.00E-12 l.OOE-12
10/1/1984 4.18E-16 S.OOE-12 1.25E-12 3.54E-16 8.00E-14 2.00E-14 1.10E-17 2.00E-12 5.00E-13 9.83E-15 4.00E-12 l.OOE-12
1/2/1985 5.30E-17 5.00E-12 1,25E-12 3.55E-17 8.00E-14 2.00E-14 7.00E-18 2.00E-12 5.00E-13 2.57E-14 4.00E-12 l.OOE-12
4/1/1985 l.OOE-16 5.00E-12 1.25E-12 6.00E-16 8.00E-14 2.00E-14 I\.35E-17 2.00E-12 5.00E-13 5.02E-15 4.00E-12 l.OOE-12
7/1/1985 9.36E-16 5.00E-12 1.25E-12 2.33E-16 8.00E-14 2.00E-14 2.36E-16 2.00E-12 .S.OOE-13 7.48E-15 4.00E-12 l.OOE-12
9/30/1985 1.46E-15 S.OOE-12 1.25E-12 7,69E-16 8.00E-14 2.00E-14 5.38E-16 2.00E-12 5.00E-13 7.86E-15 4.00E-12 l.OOE-12
1/2/1986 8.40E-15 5.00E-12 1.25E-12 7.60E-16 8.00E-14 2.00E-14 2.99E-16 2.00E-12 S.OOE-13 2.12E-14 4.00E-12 l.OOE-12
4/1/1986 5.79E-15 S.OOE-12 1.25E-12 5.80E-16 8.00E-14 2.00E-14 1.34E-15 2.00E-12 S.OOE-13 1.33E-14 4.00E-12 l.OOE-12
6/30/1986 5.19E-15 5.00E-12 1.25E-12 7.83E-16 8.00E-14 2.00E-14 2.20E-15 2.00E-12 5.00E-13 7.14E-16 4.00E-12 1.00E-12
10/27/1986 4.60E-15 5.00E-12 1.25E-12 4.67E-16 8.00E-14 2.00E-14 2.37E-15 2.00E-12 S.OOE-13 1.13E-14 4.00E-12 l.OOE-12
12/15/1986 2.75E-15 5.00E-12 1.25E-12 5.90E-16 8.00E-14 2.00E-14 9.39E-16 2.00E-12 5.00E-13 1.20E-14 4.00E-12 l.OOE-12
3/16/1987 4.64E-15 S.OOE-12 1.25E-12 1.18E-15 8.00E-14 2.00E-14 4.97E-16 2.00E-12 S.OOE-13 5,89E-14 4.00E-12 l.OOE-12
5/11/1987 4.35E-15 S.OOE-12 1.25E-12 1.23E-14 8.00E-14 2.00E-14 l.BE-15 2.00E-12 5.00E-13 l.21E-14 4.00E-12 1.00E-12
9/9/1987 6.39E-15 5.00E-12 1.25E-12 1.50E-14 8.00E-14 2.00E-14 2.26E-15 ,l.OOE-12 S.OOE-13 1.57E-14 4.00E-12 1.00E-12
11/2/1987 6.72E-15 S.OOE-12 1.25E-12 4.53E-16 8,00E-14 2.00E-14 2.20E-15 2.00E-12 S.OOE-13 .2.S5E-14 4.00E-12 l.OOE-12
2/16}1988 1.91E-15 5.00E-12 1.25E-12 1.35E-14 8.00E-14 2.00E-14 4.42E-16 2.00E-12 5.00E-13 4.44E-14 4.00E-12 1.00E-12
5/18/1988 1.78E-14 S.OOE-12 1.25E-12 4.39E-14 8.00E-14 2.00E-14 4.92E-16 2.00E-12 5.00E-13 1.38E-14 4.00E-12 l.OOE-12
8/15/1988 7.56E-15 S.OOE-12 1.25E-12 3.31E-14 S.OOE-14 2.00E-14 l .S1E-15 2.00E-12 5.00E-13 1.97E-14 4.00E-12 l.OOE-12
11/14/1988 1.47E-14 p.OOE-12 1.25E-12 1.56E-15 8.00E-14 2.00E-14 2.57E-15 2.00E-12 5.00E-13 2.12E-14 4.00E-12 l.OOE-12
2/13/1989 2.47E-15 S.OOE-12 1.25E-12 3.14E-15 S.OOE-14 2.00E-14 6.94E-16 2.00E-12 5.00E-13 2.12E-14 4,00E-12 l.OOE-12
5/15/1989 2.50E-16 s.OOE-12 1.25E-12 7.68E-15 8.00E-14 2.00E-14 9.03E-16 2.00E-12 5.00E-13 8.05E-15 4.00E-12 1.00E-12
8/14/1989 6.50E-15 S.OOE-12 1.25E-12 4.72E-15 8.00E-14 2.00E-14 2.35E-15 2.00E-12 5,00E-13 9.95E-15 4.00E-12 l.OOE-12
11/13/1989 9.63E-15 ,5.00E-12 1.25E-12 4.05E-15 8.00E-14 2.00E-14 4.03E-15 2.00E-12 S,OOE-13 1.99E-14 4.00E-12 l.OOE-12
2/12/1990 8.92E-15 S.OOE-12 1.25E-12 3.56E-15 B.OOE-14 2.00E-14 2.89E-15 2.00E-12 5.00E-13 2.69E-14 4.00E-12 l.OOE-12
5/14/1990 8.90E-15 5.00E-12 1.25E-12 3.58E-15 B.OOE-14 2.00E-14 2.33E-15 2.00E-12 5.00E-13 2,09E-14 4.00E-12 l.OOE-12
8/13/1990 1.92E-15 S.OOE-12 1.25E-12 1.87E-15 B.OOE-14 2.00E-14 5.06E-16 2.00E-12 5.00E-13 8.86E-15 4.00E-12 1,00E-12
11/12/1990 2.91E-15 5.00E-12 1.25E-12 2.25E-17 8.00E-14 2.00E-14 1.08E-15 2.00E-12 5.00E-13 2.19E-14 4.00E-12 l.OOE-12
2/11/1991 1.67E-16 5.00E-12 1.25E-12 7.89E-16 8.00E-14 2.00E-14 6.38E-17 2.00E-12 5.00E-13 4.19E-14 4.00E-12 l.OOE-12
5/13/1991 1.87E-16 5.00E-12 l.25E-12 2.61E-15 B.OOE-14 2.00E-14 3.54E-16 2.00E-12 5.00E-13 1.40E-14 !I.OOE-12 l.OOE-12
8/12/1991 4.85E-16 5.00E-12 1.25E-12 4.38E-16 B.OOE-14 2.00E-14 1.27E-16 2.00E-12 5.00E-13 2.20E-14 1\.00E-12 1.00E-12
11/11/1991 1.77E-16 S.OOE-12 1.25E-12 1.46E-16 8.00E-14 2.00E-14 3.76E-17 2,00E-12 S.OOE-13 1.15E-14 4.00E-12 l.OOE-12
2/10/1992 1.83E-16 5.00E-12 1.25E-12 1.95E-15 8,00E-14 2.00E-14 1.33E-16 2,00E-12 S.OOE-13 3.35E-14 4.00E-12 l.OOE-12
5/11/1992 4.40E-16 S.OOE-12 1.25E-12 ,2.S6E-16 S.OOE-14 2.00E-14 4.04E-16 2.00E-12 5.00E-13 1,41E-14 4.00E-12 l.OOE-12
8/10/1992 9.09E-17 5,00E-12 1.25E-12 1.15E-16 8.00E-14 2.00E-14 4.50E-17 2.00E-12 ,5.00E-13 1.57E-14 ii.OOE-12 l.OOE-12
11/9/1992 2.07E-16 5,00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 3,62E-17 2.00E-12 S.OOE-13 2.24E-14 4.00E-12 1,00E-12
2/9/1993 1.73E-16 S.OOE-12 1.25E-12 2.76E-17 8.00E-14 2.00E-14 2.89E-17 2.00E-12 S.OOE-13 3.08E-14 4.00E-12 l.OOE-12
5/10/1993 2.70E-17 5.00E-12 1.25E-12 2.50E-17 8.00E-14 2.00E-14 8.74E-17 2.00E-12 5.00E-13 l.25E-14 4.00E-12 l.OOE-12
8/10/1993 9.00E-17 5.00E-12 L25E-12 1.76E-16 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 1.50E-14 4.00E-12 l.OOE-12
11/8/1993 l.OOE-16 5.00E-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 6.00E-17 2.00E-12 5.00E-13 1.75E-14 4.00E-12 l.OOE-12
2/7/1994 l.lOE-16 5.00E-12 1,25E-12 3.38E-16 8.00E-14 2.00E-14 2.21E-16 2.00E-12 5.00E-13 3.08E-14 4.00E-12 l.OOE-12
5/9/1994 3.80E-16 5.00E-12 1.25E-12 2.82E-16 8.00E-14 2.00E-14 3.46E-16 2.00E-12 5.00E-13 1.73E-14 4.00E-12 l.OOE-12
8/9/1994 3.85E-16 5.00E·12 1,25E-12 3.53E-16 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 S.OOE-13 l.OOE-16 4.00E-12 l.OOE-12
11/7/1994 6.21E-17 5.00E-12 1.25E-12 9.70E-17 8,00E-14 2.00E-14 1.96E-16 2.00E-12 S.OOE-13 l.OOE-16 4.00E-12 l.OOE-12
Date Effluent Concentration Limit = 9E-14 uCi}ml BHV-4U Effluent Concentration Limit -2E-14 uCi/ml BHV-4T Effluent Concentration Limit= 9E-13 uCi/ml BHV-4R Effluent Concentration Limit = 6E-13 uCi/ml BHV-4PB
ALARAGoal= 2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARA Goal-2.25E-13 uCi/ml ALARAGoal-1.5E-13 uCi/ml
Pre 1994 MPC Limit = SE-12 uCi/ml Pre 1994 MPC Limit= BE-14 uCi/ml Pre 1994 MPC Limit= 2E-12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 A LARA GOAL = 1.25E-12 uCi/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml Pre 1994 A LARA GOAL= 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1995 3.70E-16 9.00E-14 2.25E-14 9.80E-17 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 8.84E-15 p.OOE-13 1.50E-13
5/9/1995 9.40E-17 9.00E-14 2.25E-14 2.86E-16 2.00E-14 S.OOE-15 1.90E-16 9.00E-13 2.25E-13 2.90E-15 6.00E-13 1.50E-13
8/9/1995 1.45E-16 9.00E-14 2.25E-14 2.31E-15 2.00E-14 S.OOE-15 7.10E-17 9.00E-13 2.25E-13 2.70E-15 p.OOE-13 l.SOE-13
11/11/1995 1.43E-14 9.00E-14 2.25E-14 5.70E-15 2,00E-14 5.00E-15 2.61E-15 9.00E-13 .2.25E-13 S.60E-15 6.00E-13 1.50E-13
2/5/1996 1.19E-14 9.00E-14 2.25E-14 3.80E-16 2.00E-14 5.00E-15 6,10E-15 9.00E-13 2.25E-13 6.48E-15 p.OOE-13 1.SOE-13
5/6/1996 4.55E-16 9.00E-14 2.25E-14 3.57E-15 2.00E-14 S.OOE-15 2.84E-16 9.00E-13 2.25E-13 7.68E-15 6.00E-13 1.50E-13
8/5/1996 7.78E-16 9.00E-14 2.25E-14 3.51E-15 2.00E-14 .5.00E-15 1.69E-16 9.00E-13 2.25E-13 4.90E-15 6.00E-13 1.50E-13
11/6/1996 1.36E-15 9.00E-14 2.25E-14 1.00E-16 Z.OOE-14 5.00E-15 4.21E-16 9.00E-13 ,2.25E-13 l.lOE-14 G.OOE-13 1.50E-13
2/6/1997 l.OOE-16 9.00E-14 2.25E-14 1.40E-16 Z.OOE-14 5.00E-15 1.03E-16 9.00E-13 .2.25E-13 6.76E-15 6.00E-13 1.50E-13
5/5/1997 l.OOE-16 9.00E-14 2.25E-14 4,00E-16 2.00E-14 5.00E-15 2.24E-16 9.00E-13 2.25E-13 4.55E-15 6.00E-13 1.SOE-13
.8/11/1997 4.74E-16 9.00E-14 2.25E-14 9.07E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.55E-15 6.00E-13 1.50E-13
1/5/199.8 8-31E-16 9.00E-14 2.25E-14 4 . .82E-16 2.00E-14 5,00E-15 1.77E-16 9.00E-13 2.25E-13 5.28E-15 6.00E-13 1.50E-13
4/2.8/199.8 3.32E-16 9.00E-14 2.25E-14 4.43E-15 Z.OOE-14 5,00E-15 1.21E-16 9.00E-13 2.25E-13 7.43E-15 6.00E-13 1.50E-13
7/31/1998 4.60E-16 9.00E-14 2.25E-14 9.02E-16 Z.OOE-14 5.00E-15 3.54E-16 9.00E-13 2,25E-13 6.91E-15 6.00E-13 1,50E-13
9/28/1998 4.08E-16 9.00E-14 2.25E-14 4,93E-16 Z.OOE-14 5.00E-15 2,53E-16 9.00E-13 2.25E-13 4.52E-15 6.00E-13 1.50E-13
12/28/1998 7.72E-16 9.00E-14 .2.25E-14 3.75E-16 2.00E-14 5.00E-15 3.43E-16 9.00E-13 2.25E-13 6.73E-15 6.00E-13 1.50E-13
3/29/1999 5.11E-16 9.00E-14 .2.25E-14 4.70E-16 ,2.00E-14 5.00E-15 3.70E-16 9.00E-13 2,25E-13 8.96E-15 6.00E-13 1.50E-13
7/3/1999 5.90E-16 9.00E-14 2.25E-14 9.89E-16 2.00E-14 S.OOE-15 1.28E-16 9.00E-13 2.25E-13 6.40E-15 6.00E-13 1.50E-13
9/27/1999 1.70E-15 9.00E-14 2.25E-14 7.50E-16 .Z.OOE-14 S.OOE-15 4.61E-16 9.00E-13 2.25E-13 7.86E-15 6.00E-13 1.50E-13
12/28/1999 1.03E-15 9.00E-14 2.25E-14 7.50E-16 2.00E-14 5.00E-15 2.43E-16 9.00E-13 2.25E-13 6.42E-15 6.00E-13 l.SOE-13
3/27/2000 LOOE-16 9.00E-14 2.25E-14 2.13E-16 2.00E-14 5.00E-15 2.20E-16 9.00E-13 2.25E-13 5.61E-15 6,00E-13 1.50E-13
6/26/2000 1.75E-16 9.00E-14 2.25E-14 3.08E-16 2.00E-14 S.OOE-15 l.llE-16 9.00E-13 2.25E-13 3.92E-15 6.00E-13 1.50E-13
9/26/2000 3.65E-16 9.00E-14 2.25E-14 2.01E-16 2.00E-14 S.OOE-15 2.24E-16 ~.OOE-13 2.25E-13 7.79E-15 6.00E-13 1.50E-13
12/26/2000 2.27E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 S.OOE-15 4.35E-16 ~.OOE-13 Z.25E-13 8.45E-15 6.00E-13 1.SOE-13
3/26/2001 1.45E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 p.37E-15 6.00E-13 1.50E-13
7/2/2001 l.OOE-16 9.00E-14 2.25E-14 1.05E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.99E-15 6.00E-13 1.50E-13
9/24/2001 1.91E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 2.01E-16 9.00E-13 Z.25E-13 B.04E-15 6.00E-13 1.50E-13
12/31/2001 1.38E-16 9.00E-14 2.25E-14 2.05E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.83E-15 6.00E-13 1.50E-13
4/1/2002 2.20E-16 9.00E-14 2.25E-14 3.38E-16 2100E-14 5.00E-15 1.26E-16 9.00E-13 2.25E-13 7.48E-15 6.00E-13 1.50E-13
7/1/2002 1.97E-16 9.00E-14 2.25E-14 4,10E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.40E-15 6.00E-13 1.50E-13
9/30/2002 230E-16 9.00E-14 2.25E-14 2.42E-16 2.00E-14 5.00E-15 1.56E-16 9,00E-13 2.25E-13 4.21E-15 6.00E-13 1.50E-13
12/30/2002 l.OOE-16 9.00E-14 z.25E-14 1.92E-16 Z.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.42E-15 6.00E-13 1.SOE-13
3/31/2003 2.SOE-16 ~.OOE-14 .2.25E-14 1,69E-16 Z.OOE-14 5.00E-15 1.29E-16 9.00E-13 Z.25E-13 4.55E-15 6.00E-13 1.50E-13
6/30/2003 l.OOE-16 9.00E-14 2.25E-14 2.87E-16 z.OOE-14 5.00E-15 1,00E-16 9.00E-13 2.25E-13 4.20E-15 6.00E-13 1.50E·13
9/29}2003 1.00E-16 9.00E-14 2.25E-14 B.53E-16 2.00E-14 5.00E-15 3.32E-16 9.00E-13 2.25E-13 8.69E-15 6,00E-13 1.50E-13
12/29/2003 1.02E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.49E-15 9,00E-13 2.25E-13 9.45E-15 6.00E-13 1.50E-13
3/29/2004 1.00E-16 9.00E-14 2.25E-14 1.26E-16 Z,OOE-14 5.00E-15 1.00E-16 9.00E-13 2.Z5E-13 2,00E-15 6.00E-13 L50E·13
6/27/2004 1.00E·16 9.00E-14 2.25E-14 .2.53E·16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E·13 3.23E-15 p.OOE-13 1.50E-13
9/27/2004 1,00E-16 9,00E-14 2.25E-14 1.15E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.68E-15 6.00E-13 1.50E-13
12/27/2004 l.OOE-16 9.00E-14 2.25E-14 2.30E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.Z5E-13 1.37E-14 6.00E-13 1.50E·13
3/28/2005 1.00E-16 9.00E-14 Z.25E-14 2.66E-16 2,00E-14 5.00E-15 3.15E-16 9.00E-13 Z.Z5E-13 9.22E-15 6.00E-13 1.50E·13
6/29/2005 1.47E·16 9.00E-14 2.25E-14 1.45E·15 2.00E-14 5.00E·15 1.42E-16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 1.SOE·13
9/26/2005 2.01E-16 9.00E-14 2.25E-14 2,06E-16 2.00E-14 S.OOE-15 4,80E-16 9.00E-13 2.25E-13 2.12E-14 6.00E-13 1.50E·13
1/3/2006 4.54E-16 9.00E-14 2.25E-14 1.24E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E·13 3.60E-14 ~.OOE-13 1.50E-13
4/3/2006 1.99E-16 9.00E-14 2 25E-14 1.32E·16 2.00E-14 .S.OOE-15 l.OOE-16 9.00E-13 2.Z5E-13 8.36E-15 6.00E-13 1.50E-13
7/3/2006 2.76E-16 9.00E-14 2.25E-14 2.63E-16 2.00E-14 5.00E-15 l.OOE-16 ll.OOE-13 Z.25E·13 1.03E-14 6.00E-13 l.SOE-13
10/2/2006 4.97E-16 9.00E-14 2.25E-14 2.37E·16 2-00E-14 5.00E·15 l.OOE-16 9.00E-13 2.25E-13 1,60E,14 6.00E-13 1.50E-13
1/1/2007 6.46E-16 9.00E-14 2.25E-14 2.81E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 2.10E-14 6.00E-13 1.50E-13
4/2/2007 7.08E-16 '9.00E-14 2.25E-14 3.20E'-16 2.00E-14 5.00E·15 l.OOE-16 9.00E-13 2.25E-13 1.54E-14 6.00E-13 1.50E-13
7/2/2007 9.41E-16 9.00E-14 2.25E-14 1.46E-16 2.00E-14 5.00E-15 1.99E-16 9.00E-13 2.25E-13 2.56E-14 6.00E-13 1.SOE-13
9/30/2007 3.30E-16 9.00E-14 2.25E-14 5.50E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.57E-15 6.00E-13 1.50E-13
12/31/2007 1.42 E-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9,00E-13 2 25E-13 9.93E-15 6.00E-13 1.50E-13
3/31/2008 1.25E·16 9.00E-14 2 25E-14 1.72E-16 2.00E-14 5.00E·15 l.OOE-16 9.00E-13 2.25E-13 4"09E-15 6.00E-13 1.50E-13
6/30/2008 1.28E-15 9.00E-14 Z.25E-14 l.OOE-16 2.00E-14 S.OOE-15 3,61E-16 9,00E-13 2.Z5E-13 1.18E-14 6.00E-13 1.50E-13 -
Date ~ffluent Concentration Limit= 9E-14 uCi/ml BHV-4U Effluent Concentration Limit= 2E-14 uCi/ml BHV-4T Effluent Concentration Limit= 9E-13 uCi/ml 1!HV-4R Effluent Concentration Limit = ,GE-13 uCi/ml BHV-4PB I
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal= SE-13 uCi/ml ALARA Goal-2.25E-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml I
pre 1994 MPC Limit= SE-12 uCi/ml Pre 1994 MPC Limit= BE-14 uCi/ml P.rl! 1994 MP<! Umlt-" 2E-12 uCi/ml Pr~ 1994 M PC _If mit~ 4E-12 uCi/ml
Pre 1994 ALARA GOAL-1.25E-12 uCi/ml pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
f=onc EFC EFCA Cone EFC EFCA Cone EFC EFCA tone EFC EFCA
9/30/2008 2.72E-15 9.00E-14 2.25E-14 1.27E-15 2.00E-14 5.00E-15 '7.66E-16 9.00E-13 2.25E-13 1,10E-14 G.OOE-13 1.SOE-13
12/31/2008 2.88E-15 9.00E-14 2.25E-14 1.10E-15 2.00E-14 5.00E-15 6.56E-16 9.00E-13 2.25E-13 1.38E-14 G.OOE-13 1.50E-13
3/15/2009 1.56E-15 9.00E-14 2.25E-14 4.57E-16 2.00E-14 5.00E-15 2.99E-16 9.00E·13 2,25E-13 4.97E-15 G,OOE-13 1.50E-13
6/15/2009 5.67E-17 9.00E-14 2.25E-14 2.17E-16 z.OOE-14 5.00E-15 1.51E-16 9.00E-13 2.25E-13 4.47E-15 G.OOE-13 1.50E-13
9/15/2009 4.05E-15 9.00E-14 2.25E-14 1.45E-15 2.00E-14 5.00E-15 2.52E-16 9.00E-13 2.25E-13 1.24E-14 G.OOE-13 1.50E-13 I
12/15/2009 6.50E-15 9.00E-14 2.25E-14 3.48E-16 Z.OOE-14 5.00E-15 1,33E·16 9.00E·13 2.25E-13 7.60E-15 G.OOE-13 1.50E-13
3/31/2010 6.01E-15 9.00E-14 2.25E-14 1.26E-16 l.OOE-14 5.00E-15 1.34E-16 9.00E-13 2.25E·13 1.19E·14 G.OOE-13 1.50E-13
6/30/2010 2.33E-15 9.00E-14 ,2.25E-14 7.29E-16 l.OOE-14 5.00E-15 2.66E-16 9.00E-13 2.25E-13 3.27E-15 6.00E-13 1.50E-13
9/30/2010 4.77E-15 9.00E-14 2.25E-14 1.80E-15 2.00E-14 5.00E-15 8.23E-16 9.00E-13 2.25E-13 5.11E-15 G.OOE-13 1.50E-13
12/31/2010 3.93E-15 9.00E-14 2.25E-14 3,90E-16 Z.OOE-14 5.00E-15 2.56E-16 9.00E-13 2.25E-13 1,13E-14 G.OOE-13 1.50E-13
4/4/2011 1.29E-15 9.00E-14 2.25E-14 1.40E·16 2.00E-14 S.OOE-15 1,58E-16 ~.OOE-13 2.25E-13 1.11E-14 6.00E-13 1.50E-13
7/4/2011 3,30E-15 9.00E-14 2.25E-14 5.44E-16 2.00E-14 S.OOE-15 4.18E-16 S.OOE-13 2.25E-13 8.26E-15 6.00E·13 1.50E-13
10/3/2011 1.32E-15 9.00E-14 2.25E-14 7.89E-16 2.00E-14 5.00E-15 1.28E-16 S.OOE-13 2.25E-13 1.18E-14 G.OOE-13 1.50E-13
1/3/2012 1.04E-15 9.00E-14 2.25E-14 3.25E-16 2,00E-14 S.OOE-15 .2.28E-16 9.00E-13 2.25E-13 1.14E-14 G.OOE-13 1.50E-13
4/3/2012 ,2,51E-15 9.00E-14 2.25E-14 5.02E-16 2.00E-14 5.00E·15 2.27E-16 S.OOE-13 .2.25E-13 1.03E-14 G.OOE-13 1.50E·13
7/2/2012 2.62E-15 9.00E-14 2.25E-14 1.23E-15 2.00E-14 5.00E-15 2.97E-16 9.00E·13 2.25E-13 9.27E-15 6.00E-13 1.50E-13
10/1/2012 4.05E-15 9.00E-14 2.25E-14 8,33E-16 2.00E-14 5.00E-15 5.43E-16 9.00E-13 2.25E-13 l.21E-14 6.00E-13 1.50E·13
12/31/2012 2.32E-15 9.00E-14 2.25E-14 5.89E-16 2.00E-14 5.00E-15 3.75E-16 9.00E-13 2.25E-13 1.56E-14 6.00E-13 1.50E-13
3/25/2013 3.04E-15 9.00E-14 2.25E-14 4.99E·16 2.00E-14 5.00E-15 2.79E-16 9.00E-13 2.25E-13 2.13E-14 G.OOE-13 1.50E-13
7/2/2013 2.50E-15 9.00E-14 2.25E-14 3.62E·16 2.00E-14 5.00E-15 2.40E-16 9.00E-13 2.25E·l3 4.93E-15 G.OOE-13 1.50E-13
9/30/2013 2.98E-15 9.00E-14 2.25E-14 4.49E·16 Z.OOE-14 S.OOE-15 154E-16 9.00E·13 2.25E-13 7.49E·15 6.00E·13 1.50E·13
12/30/2013 3.88E-15 ll.OOE-14 2.25E-14 1.03E-16 Z.OOE-14 5.00E-15 4.47E-17 9.00E-13 2.25E-13 2.93E-14 6.00E-13 1.50E-13
3/31/2014 4,69E-15 9.00E-14 .2.25E-14 1.37E-16 2.00E-14 S.OOE-15 3.53E-16 9.00E-13 2.25E-13 l.OBE-14 6.00E-13 1.50E·13
6/30/2014 4.16E-15 9.00E-14 2.25E-14 6.96E-16 .Z.OOE-14 S.OOE-15 1.77E-15 9.00E-13 2.25E-13 LOGE-14 6.00E-13 1.50E-13
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TABS
BHV-5 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent Concentration Limit= 9E-14 uCi/ml BHV-SU Effluent Concentration Limit= 2E-14 uCi/ml BHV-ST Effluent Concentration limit= 9E-13 uCijml BHV-SR Effluent Concentration Limit = 6E-13 uCi/ml BHV-SPB
AlARAGoal = 2.25£-14 uCi/ml AlARA Goal= SE-13 uCi/ml AlARAGoal = 2.25£-13 uCi/ml AlARAGoal = 1.5£-13 uCi/ml
Pre 1994 MPC Limit-SE-UuCi/ml Prel994 MPC.Limfl; BE-14 uCi/ml Pre 1994 MPC Limit -2E-12 uCi/ml Pre 1994 MPC Limit-4E-12 uCi/ml
Pre 1994 A lARA GOAL = l.25E-12 uCi/ml Pre 1994 A lARA GOAL = SE-13 uCi/ml Pre 1994 A lARA GOAL= 1E-12 uCi/ml
Cone EFC eFCA Cone eFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 2.44E-15 S,OOE-12 1.25E·12 1.53E-15 8.00E-14 2.00E-14 7.54E-16 2.00E-12 5.00E-13 1.69E-14 4.00E-12 1.00E-12
12/14/1981 4,84E-15 S.OOE-12 1.25E-12 2.78E-15 8.00E-14 2.00E-14 1.84E-15 2.00E-12 5.00E-13 1.53E-14 4.00E-12 l.OOE-12
3/29/1982 1.04E-15 5.00E-12 1.25E-12 2.62E-15 8.00E-14 Z.OOE-14 1.11E-15 2.00E-12 5.00E-13 2.98E-14 4.00E-12 l.OOE-12
6/30/1982 3.61E-15 5.00E-12 1.25E-12 7.61E-15 S.OOE-14 2.00E-14 1.39E-15 2.00E-12 5.00E-13 1.80E-15 4.00E-12 l.OOE-12
9/27/1982 1.71E-14 5.00E-12 l.25E-12 9.46E-15 B.OOE-14 2.00E-14 3.80E-15 2.00E-12 5.00E-13 2.35E-14 4.00E-12 l.OOE-12
1/3/1983 1.90E-14 5.00E-12 125E-12 5.77E-15 S.OOE-14 2.00E-14 9.34E-17 2.00E-12 5,00E-13 4.32E-14 4.00E-12 l.OOE-12
4/4/1983 5.00E-12 1.25E-12 2.33E-15 B.OOE-14 2.00E-14 5.93E-16 2.00E-12 5.00E-13 3.01E-14 4.00E-12 l.OOE-12
6/30/1983 7.62E-16 5.00E-12 1.25E-12 3.25E-15 8.00E-14 Z.OOE-14 6.28E-15 2.00E-12 5.00E-13 2.69E-14 4.00E-12 l.OOE-12
10/3/1983 4.86E-16 5.00E-12 1.25E-12 L10E-15 S.OOE-14 2.00E-14 3.63E-16 2.00E-12 5.00E-13 2.08E-14 4.00E-12 l .OOE-12
1/3/1984 6.96E-15 5.00E-12 1.25E-12 9.69E-16 B.OOE-14 2.00E-14 9.60E-16 2.00E-12 5.00E-13 1.83E-14 4.00E-12 l.OOE-12
4/2/1984 1.64E-15 5.00E-12 1.25E-12 1.34E-15 8.00E-14 2.00E-14 3.88E-15 2.00E-12 5.00E-13 4.67E·14 4.00E-12 1.00E-12
7/2/1984 1.12E·15 5.00E·12 1.25E-12 1.92E-15 8.00E-14 2.00E-14 3.31E-15 2.00E-12 5.00E-13 2.21E·14 ·4.00E-12 l.OOE-12
10/1/1984 1.11E-15 5.00E-12 1.25E-12 3.13E-16 8.00E-14 2.00E-14 4.21E-16 Z.OOE-12 5.00E-13 1.57E-14 4.00E-12 l.OOE-12
1/2/1985 7.32E-16 5.00E-12 1.25E·12 6.71E-16 8.00E·14 2.00E-14 4..94E-16 2.00E-12 5.00E-13 2.42E-14 4.00E-12 l.OOE-12
4/1/1985 2.36E·16 5.00E-12 1.25E-12 5.43E-16 8.00E·14 2.00E-14 2.71E-16 2.00E-12 5.00E-13 1.25E-14 4.00E-12 1.00E-12
7/1/1985 7.58E-16 5.00E-12 1.25E-12 4.00E-16 8.00E-14 2.00E-14 6.90E-16 2.00E-12 5.00E-13 2.15E-14 4.00E-12 l.OOE-12
9/30/1985 7.47E·15 5 OOE-12 1.25E-12 1.16E-15 8.00E·14 Z.OOE-14 2.19E-15 Z.OOE-12 5.00E-13 9.20E-15 4.00E-12 l.OOE-12
1/2/1986 1.75E-14 5.00E-12 1.25E-12 7.24E-15 8.00E-14 2.00E-14 3.83E-15 2.00E-12 S.OOE-13 1.13E-16 4.00E-12 l.OOE-12
4/1/1986 2.99E·14 5.00E-12 1.25E-12 7.64E-15 8.00E-14 2.00E-14 1.51E-14 Z.OOE-12 S.OOE-13 2.22E-14 4.00E-12 l.OOE-12
6/30/1986 2.23E·14 5.00E-12 1,25E-12 5.19E-15 8.00E-14 2.00E-14 1.05E-14 2.00£-12 S.OOE-13 2.16E·14 4.00E-12 l.OOE-12
10/27/1986 2.33E-14 5.00E-12 1.25E-12 7.78E-15 8.00E-14 Z.OOE-14 1.60E-14 2 OOE-12 S.OOE-13 2.02E·14 4.00E-12 l .OOE-12
12/15/1986 3.40E·14 5.00E-12 1.25E-12 5.35E-15 8,00E-14 2.00E-14 1.47E-14 Z.OOE-12 o.OOE-13 2.82E-14 4.00E-12 l.OOE-12
3/16/1987 2.06E·14 5.00E-12 1.25E·12 4.SOE-15 8.00E-14 2.00E-14 6.74E-15 2.00E-12 S.OOE-13 7,29E·14 4.00E-12 1.00E-12
5/11/1987 2.50E-14 5.00E-12 1.25E-12 8.54E-15 8.00E-14 z.OOE-14 8.15E-15 Z.OOE-12 S.OOE-13 3.28E-14 4.00E-12 1.00E·12
9/9/1987 2.65E-14 5.00E-12 1.25E-12 6,62E-15 8,00E-14 2.00E-14 9.34E-15 2.00£-12 5.00E-13 2.77E·14 4.00E-12 l.OOE-12
11/2/1987 1.80E·14 5,00E-12 1.25E-12 7.09E-15 8.00E·14 2.00E-14 7.20E-15 ~.OOE-12 S.OOE-13 1.77E-14 4.00E-12 l.OOE-12
2/16/1988 1.01E-14 5.00E-12 1.25E-12 2.98E-15 B.OOE-14 2.00E-14 3,93E-15 2.00E-12 S.OOE-13 3.36E-14 4.00E-12 1.00E·12
5/18/1988 1.78E-14 5.00E-12 1.25E-12 8.14E-15 8.00E-14 Z.OOE-14 7.43E-15 Z.OOE-12 S.OOE-13 2.12E-14 4.00E-12 1.00E-12
8/15/1988 1.79E-14 5.00E-12 1.25E-12 1.49E-14 B.OOE-14 2.00E-14 5.34E-15 2.00E-12 ,S,OOE-13 2.45E-14 4.00E-12 1.00E-12
11/14/1988 4.46E·14 S.OOE-12 1.25E-12 1.39E-14 B.OOE-14 ~.OOE-14 1.17E-14 ,Z.OOE-12 5.00E-13 3.43E-14 4.00E-12 1.00E-12
2/13/1989 1.67E-14 S.OOE-12 1.25E-12 5.54E-15 B.OOE-14 2.00E-14 7.20E-15 Z,OOE-12 5.00E-13 5.02E-14 4.00E-12 1.00E-12
5/15/1989 2.03E-14 S.OOE-12 1.25E-12 7.05E-15 8.00E-14 2.00E-14 9.56E-16 .Z.OOE-12 S.OOE-13 l.43E-14 4.00E-12 1,00E-12
8/14/1989 2.81E-15 S.OOE-12 1.25E-12 3.78E-15 8.00E-14 2.00E-14 9.26E-15 l .OOE-12 G.OOE-13 1.50E-14 4.00E-12 l,OOE-12
11/13/1989 5.38E-14 5.00E-12 1.25E-12 8.01E·15 8.00E·14 2.00E-14 1.81E-14 2.00E·12 5.00E-13 4,09E·14 4.00E-12 1,00E-12
2/12/1990 4.48E·14 S.OOE-12 1.25E-12 1.48E·14 8.00E·14 2.00E-14 1.28E-14 2.00E-12 ·s.OOE-13 3.88E·14 4.00E-12 1.00E-12
5/14/1990 2.18E·14 5.00E-12 1.25E-12 1.70E-14 8.00E·14 2.00E-14 L59E-14 2.00E-12 S.OOE-13 3.49E·14 4.00E-12 1.00E-12
8/13/1990 9.53E·15 5.00E-12 1.25E-12 1,70E-14 8,00E-14 2.00E-14 3.27E-15 2.00E-12 S.OOE-13 1,27E·14 4.00E-12 1.00E·12
11/12/1990 1.11E-14 5.00E-12 1.25E-12 5.27E-15 8.00E-14 2.00E-14 5.38E-15 Z,OOE-12 5.00E-13 1.56E-14 4.00E-12 l.OOE-12
2/11/1991 6.35E-16 S.OOE-12 1.25E-12 3.13E-16 8.00E-14 2.00E-14 2.31E-16 2.00E-12 5.00E-13 3.89E-14 4.00E-12 1.00E·12
5/13/1991 1.22E·15 5.00E-12 1.25E-12 6.14E-15 8.00E-14 2.00E-14 4.41E-15 2.00E-12 5.00E-13 2.50E-14 4.00E-12 l.OOE-12
8/12/1991 7.84E·16 5.00E-12 1.25E-12 1.43E-15 B.OOE-14 2.00E-14 4.47E-16 2.00E-12 5.00E-13 1.84E-14 4.00E-12 l.OOE-12
11/11/1991 5.37E-16 5.00E-12 1.25E-12 4.20E-16 B.OOE-14 2.00E-14 1.37E-16 2.00E-12 5.00E-13 1.27E·14 4.00E-12 l.OOE-12
2/10/1992 3.54E·16 5.00E-12 1.25E·12 1.18E-16 B.OOE-14 2.00E-14 4.08E-17 2.00E-12 5.00E-13 3.69E·14 4.00E-12 l.OOE-12
5/11/1992 4.71E·16 5.00E-12 1.25E·12 9.58E-16 B.OOE-14 2,00E-14 8.31E-17 2.00E-12 5.00E-13 1.43E-14 4.00E-12 l.OOE-12
8/10/1992 5.32E·15 S.OOE-12 1.25E·12 3.36E-16 B.OOE-14 2.00E-14 1.65E-16 2.00E-12 5.00E-13 1.59E-14 4.00E-12 l.OOE-12
11/9/1992 3.66E-16 S.OOE-12 1.25E-12 2.25E-16 8.00E-14 2.00E-14 1.08E-16 2.00E-12 5.00E-13 2.24E·14 4.00E-12 l.OOE-12
2/9/1993 2.05E-16 S.OOE-12 1.25E-12 9.14E·17 8.00E-14 2.00E-14 6.31E-17 2.00E-12 5.00E-13 3.41E-14 4.00E-12 l.OOE-12
5/10/1993 4.80E·16 5.00E-12 1.25E-12 8.25E·16 8.00E·14 2,00E-14 1.26E-15 2.00E-12 5.00E-13 1.83E-14 4.00E-12 l.OOE-12
8/10/1993 8.30E-16 S.OOE-12 1.25E-12 1.90E-16 S.OOE-14 2.00E·14 2.10E-16 2.00E-12 5.00E-13 1.70E-14 4,00E-12 1.00E·12
11/8/1993 2.70E·16 5.00E-12 1.25E-12 8.00E-17 B.OOE-14 2,00E-14 7.00E-17 2.00E-12 S.OOE-13 2.34E-14 4.00E-12 '1.00E·12
2/7/1994 3.18E-16 S.OOE-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 5.18E-16 2,00E-12 5.00E·13 3.64E·14 4.00E-12 1.00E·12
5/9/1994 1.80E-15 5.00E-12 1.25E-12 9.78E-16 B.OOE-14 2.00E-14 l.lOE-15 2.00E·12 S.OOE-13 8.30E-15 4,00E-12 l.OOE-12
8/9/1994 2.67E-15 S.OOE-12 1.25E-12 l.11E-15 S,OOE-14 2.00E-14 4.95E-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 l.OOE-12
11/7/1994 9.21E-17 5.00E-12 l.25E-12 1.59E-15 B.OOE-14 2.00E-14 1.66E-15 2.00E-12 S,OOE-13 l.OOE-16 4.00E-12 l.OOE-12
Date Effluent Concentration Limit = 9E-14 uCi/ml BHV-SU ~ffluent Concentration Limit = ZE-14 uCi/ml BHV-ST Effluent Concentration Limit = 9E-13 uCi/ml BHV-SR Effluent Concentration Limit= 6E-13 uCi/ml BHV-SPB
ALARA Goal= Z.ZSE-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARA Goal= Z.ZSE-13 uCi/ml ALARA Goal= 1.5E-13 uCi/ml
Pre 1994 MPC Limit= SE-12 uCi/ml pre 1994 MPC Limit = BE-14 uCi/ml Pre 1994 MPC Limit-ZE-12 uCi/ml Pre 1994 MPC Limit -4E-12 uCi/ml
Pre 1994 ALARA GOAL= l.ZSE-12 uCi/ml Pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 A LARA GOAL -1E-12 uCi/ml
Cone EFC EFCA tone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1995 1.51E-15 9.00E-14 2.25E-14 il.SOE-16 2.00E-14 S.OOE-15 9.70E-17 9.00E-13 2.25E-13 9.35E-15 6 OOE-13 1.50E-13
5/9/1995 2.21E-16 9.00E-14 2.25E-14 S.56E-16 2.00E-14 S.OOE-15 3.06E-15 9.00E-13 2.25E-13 4.34E-15 6.00E-13 150E-13
8/9/1995 1.66E-16 9.00E-14 2.25E-14 1.67E-15 2.00E-14 S.OOE-15 3.90E-15 9.00E-13 2,25E-13 5,60E-15 6.00E-13 1.50E-13
11/11/1995 2.04E-14 9.00E-14 2.25E-14 6.70E-15 2.00E-14 S.OOE-15 7.65E-15 9.00E-13 2,25E-13 4.47E-15 6.00E-13 1.50E-13
U5/1996 4.50E-14 9.00E-14 2.25E-14 3.58E-14 2.00E-14 S.OOE-15 2,39E-14 9.00E-13 2.25E-13 7.30E-15 6.00E-13 1,50E-13
5/6/1996 1.76E-15 9.00E-14 2.25E-14 3.57E-15 2"00E-14 S.OOE-15 9.55E-16 9.00E-13 2.25E-13 7,54E-15 G.OOE-13 1.50E-13
8/5/1996 2.37E-15 9.00E-14 2.25E-14 8,18E-15 2.00E-14 S.OOE-15 7.46E-16 9.00E-13 2.25E-13 5.75E-15 6.00E-13 1.50E-13
11/6/1996 3.53E-15 9.00E-14 2.25E-14 6.31E-15 2.00E-14 S.OOE-15 9.39E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 L50E-13
2/6/1997 1.84E-16 9.00E-14 2.25E-14 2.01E-16 2.00E-14 S.OOE-15 1.87E-16 9.00E-13 2.25E-13 6.14E-15 6.00E-13 l.50E-13
5/5/1997 5.75E-16 9.00E-14 2.25E-14 7.24E-16 2.00E-14 S.OOE-15 6.07E-16 9.00E-13 2.25E-13 4.75E-15 6.00E-13 1.50E-13
8/11/1997 1.21E-15 9.00E-14 2.25E-14 7.39E-16 2.00E-14 S.OOE-15 5.05E-16 9.00E-13 2.25E-13 4.92E-15 G.OOE-13 l.SOE-13
1/5/1998 9.89E-16 9.00E-14 2.25E-14 1.92E-15 2.00E-14 S.OOE-15 6,21E-16 9.00E-13 2.25E-13 4.68E·15 6.00E-13 1.50E-13
4/28/1998 2,84E-15 9.00E-14 2.25E-14 2.38E-15 Z.OOE-14 5.00E-15 1.72E-15 9.00E-13 2.25E-13 7.35E·l5 6.00E-13 1.50E-13
7/31/1998 7.49E·l6 9.00E-14 2.25E-14 1.49E-15 2.00E-14 S.OOE-15 8.34E-16 9.00E-13 2.25E-13 7.01E-15 6.00E-13 1.50E-13
9/28/1998 1.07E-15 9.00E-14 2.25E·14 9.20E-16 2.00E-14 S.OOE-15 6.32E-16 9.00E-13 2.25E-13 3.95E-15 6.00E-13 1.50E-13
12/28/1998 8.51E-15 9.00E-14 2.25E-14 4.58E-15 2.00E-14 S,OOE-15 4.58E-15 9.00E-13 2.25E-13 1.43E-14 6.00E-13 1.50E-13
8/29/1999 3.75E-15 9.00E-14 2.25E-14 2.45E-15 Z.OOE-14 S,OOE-15 2.39E-15 9.00E-13 2.25E-13 8.46E-15 G.OOE-13 1.50E-13
7/3/1999 1.53E-15 9.00E-14 2.25E-14 8.65E-16 2.00E-14 S,OOE-15 6.52E-16 '9.00E-13 2.25E-13 7.20E-15 6.00E-13 1.50E-13
9/27/1999 5.83E-15 9.00E-14 2.25E-14 3.52E-15 2.00E-14 .S.OOE-15 2.55E-15 9.00E-13 2.25E-13 8.22E-15 6.00E-13 1.50E-13
12/28/1999 9.48E-15 9.00E-14 2.25E-14 6.20E-15 2.00E-14 S.OOE-15 3.96E-15 9,00E-13 2.25E-13 7.56E-15 6.00E-13 1.50E-13
3/27/2000 2.06E-15 9.00E-14 2.25E-14 1.27E-15 2.00E-14 S.OOE-15 1.09E-15 9~00E-13 2.25E-13 7.72E-15 6.00E-13 1.50E-13
6/26/2000 1.SOE-15 9.00E-14 2.25E-14 1.24E-15 2.00E-14 S,OOE-15 1.01E-15 9.00E-13 2.25E-13 4.36E-15 6~00E-13 1.50E-13
'J/26/2000 1.04E-15 9.00E-14 2.25E-14 5.45E-16 2.00E-14 S.OOE-15 6.01E-16 9.00E-13 2.25E-13 7.67E-15 6.00E-13 1.50E-13
12/26/2000 1.48E-15 9.00E-14 2.25E-14 7.56E-16 2.00E-14 S.OOE-15 6.84E-16 9,00E-13 2.25E-13 7.00E-15 6.00E-13 1.50E-13
3/26/2001 4.27E-16 9.00E-14 2.25E-14 2.19E-16 2.00E-14 S.OOE-15 1.89E-16 9.00E-13 2.25E-13 6.13E-15 G.OOE-13 1.50E-13
7/2/2001 4.52E-16 9.00E-14 2.25E-14 4,02E-16 2.00E-14 S.OOE-15 LOOE-16 9.DOE-13 2.25E-13 7.48E·15 G.OOE-13 1.50E-13
9/24/2001 4.65E-16 9.00E-14 2.25E-14 2.06E-16 2.00E-14 S.OOE-15 2.02E-16 9.00E-13 2.25E-13 6.98E-15 6.00E-13 1.SOE-13
12/31/2001 7.40E-16 9.00E-14 2.25E-14 3.51E-16 2.00E-14 S.OOE-15 3.64E-16 9.00E-13 2.25E-13 4.72E-15 6.00E-13 1.50E-13
4/1/2002 L26E-15 9.00E-14 2.25E-14 7.53E-16 2.00E-14 S.OOE-15 7.19E-16 g.OOE-13 2.25E-13 ~.65E-15 6.00E-13 1.50E-13
7/1/2002 1.02E-15 9.00E-14 2.25E-14 1.03E-15 2.00E-14 !i.OOE-15 3.39E-16 9.00E-13 2.25E-13 7.20E-15 6.00E-13 1.50E-13
9/30/2002 ;;.82E-16 9.00E-14 2.25E-14 9.28E-16 2.00E-14 :S.OOE-15 a.14E-16 '9.00E-13 2.25E-13 4.48E-15 6.00E-13 1.50E-13
12/30/2002 l.OOE-16 9.00E-14 2.25E-14 7.67E-16 2.00E-14 S,OOE-15 3.48E-16 fl.OOE-13 2.25E-13 9.56E-15 IJ.OOE-13 1.50E-13
3/31/2003 1.13E-15 9.00E-14 2.25E-14 7.41E-16 2.00E-14 S.OOE-15 4.41E-16 9.00E-13 2.25E-13 6.68E-15 p.OOE-13 1.50E-13
6/30/2003 4.35E-16 9.00E-14 2.25E-14 5.08E-16 2.00E-14 S.OOE-15 2.51E-16 S.OOE-13 2.25E-13 1.34E-15 6.00E-13 1.50E-13
9/29/2003 1.51E-16 9.00E-14 2.25E-14 1.02E-16 2.00E-14 !;,OOE-15 l.OOE-16 IJ.OOE-13 2.25E-13 7.28E-15 p.OOE-13 1.50E-13
12/29/2003 1.52E-16 9.00E-14 2.25E-14 1.54E-16 2.00E-14 S.OOE-15 1.51E-16 il.OOE-13 2.25E-13 7.02E-15 6.00E-13 1.50E-13
3/29/2004 1.00E-16 9.00E-14 2.25E-14 1.12E-16 2.00E-14 !>.OOE-15 l.OOE-16 IJ.OOE-13 2.25E-13 8.82E-15 p,OOE-13 1.SOE-13
6/27/2004 1.18E-16 ·9.00E-14 2.25E-14 3.11E-16 2.00E-14 5.00E-15 1.25E-16 9.00E-13 2.25E-13 2.47E-15 G.OOE-13 l.SOE-13
9/27/2004 1.16E-16 9.00E-14 2.25E-14 1.72E-16 2.00E-14 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 l.lOE-14 IJ.OOE-13 l.SOE-13
12/27/2004 1.14E-16 9.00E-14 2.25E-14 l.OGE-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.59E·14 6.00E-13 1.SOE-13
3/28}2005 l.OOE-16 9.00E-14 2.25E-14 2.04E-16 2.00E-14 6.00E-15 1.83E-16 9.00E-13 2.25E-13 8.57E-15 G.OOE-13 1.50E-13
6/29/2005 1.83E-16 9.00E-14 2.25E-14 3.81E-16 2.00E-14 S.OOE-15 3.09E-16 9.00E-13 ,2.25E-13 1.06E-14 G.OOE-13 1.50E-13
9/26/2005 2.87E-16 9.00E-14 2.25E-14 8.21E-16 2,00E-14 5.00E-15 3.71E-14 9.00E-13 2.25E-13 6.28E-14 6.00E-13 1.50E-13
1/3/2006 8.74E-16 9.00E-14 2.25E-14 3.79E-16 2.00E-14 5.00E-15 1.31E-16 !:J.OOE-13 2.25E-13 4.32E-14 ~.OOE-13 1.50E-13
4/3/2006 5.22E-16 9.00E-14 2,25E-14 6.66E-16 2.00E-14 5.00E-15 1.11E-16 9.00E-13 1.25E-13 9.34E-15 6.00E-13 1.50E-13
7/3/2006 3.08E-16 9.00E-14 2.25E-14 1.10E-16 2.00E-14 5.00E-15 l.OOE-16 !l.OOE-13 2.25E-13 1.25E-14 6.00E-13 1.50E-13
10/2/2006 9.14E-16 9.00E-14 2.25E-14 4.95E-16 2.00E-14 5.00E-15 1.86E-16 9.00E-13 2.25E-13 L67E-14 6.00E-13 1.50E-13
1/1/2007 9.49E-16 9.00E-14 2.25E-14 6.81E-16 2.00E-14 5.00E-15 2.02E-16 l.l.OOE-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
4/2/2007 1.08E-15 9.00E-14 2.25E-14 8.22E-16 2.00E-14 5.00E-15 2.26E-16 9.00E-13 2.25E-13 1.64E-14 6.00E-13 1,50E-13
7/2/2007 1.54E·15 B.OOE-14 2.25E-14 8.16E-16 2.00E-14 S.OOE-15 4.76E-16 9.00E-13 2.15E-13 2.12E·14 6.00E-13 1.50E-13
9/30/2007 4.90E-16 9.00E-14 2.25E-14 2.37E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 .Z.lSE-13 6.65E-15 6.00E-13 1.50E-13
12/31/2007 1.46E-15 B.OOE-14 2.2SE-14 5.67E-16 2.00E-14 S.OOE-15 l.OOE-16 9,00E-13 2.15E-13 1.02E-14 6 OOE-13 1.50E-13
3/31/2008 3.16E-16 9.00E-14 2.25E-14 6,17E-16 2,00E-14 5.00E-15 3.71E-16 9.00E-13 2.25E-13 4.82E-15 ~.OOE-13 1.50E-13
6/30/2008 3.13E-15 9.00E-14 2.25E-14 1.55E-15 2.00E-14 5.00E-15 9.27E-16 9,00E-13 2.25E-13 7.40E-15 fi.OOE-13 1.SOE-13 -----
Date Effluent Concentration Limit= 9E-14 uCi/ml BHV-SU Effluent Concentration Limit = 2E-14 uCi/ml l!HV-ST Effluent Concentration Limit= 9E-13 uCi/ml BHV-SR Effluent Concentration Limit = 6E-13 uCi/ml :sHV-SPB
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal-SE-13 uCi/ml ALARAGoal = 2.25E-13 uCifml ALARA Goal-1.5E-13 uCi/ml
Pre 1994 MPC Limit-SE-12 uCI/ml Pre 1994 MPC Limit= SE-14 uCi/ml Pre 1994 MPC Limit= 2E-12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL-1.25E-12 uCi/ml Pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/30/2008 7.08E-15 9.00E-14 2.25E-14 3.41E-15 2 OOE-14 S.OOE-15 2.52E-15 9.00E-13 2.25E-13 1.15E-14 6.00E-13 l.SOE-13
12/31/2008 7.22E-15 9.00E-14 2.25E-14 2.82E-15 2.00E-14 6.00E-15 3.03E-15 9.00E-13 2.25E-13 1.59E-14 6.00E-13 1.50E-13
3/15/2009 4.13E-15 9.00E-14 2.25E-14 l.39E-15 2.00E-14 S.OOE-15 1.41E-15 9.00E-13 2.25E-13 4.66E-15 6.00E-13 l.SOE-13
6/15/2009 2.31E-16 9,00E-14 2.25E-14 7.79E-16 2.00E-14 S.OOE-15 6.37E-16 B.OOE-13 2.25E-13 4.18E-15 6.00E-13 l.50E-13
9/15/2009 3.10E-15 9.00E-14 2.25E-14 9.20E-16 2.00E-14 S.OOE-15 6.36E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 1.50E-13
12/15/2009 S.77E-15 9.00E-14 2.25E-14 3.13E-16 2.00E-14 6.00E-15 1.92E-16 S.OOE-13 2.25E-13 2.48E-15 6.00E-13 1.50E-13
3/31/2010 4.78E-15 9.00E-14 2.25E-14 3.73E-16 2.00E-14 5.00E-15 4.19E-16 9.00E-13 2.25E-13 1.30E-14 6.00E-13 1.50E-13
6/30/2010 4.35E-15 9.00E-14 2.25E-14 7.84E-16 2.00E-14 S.OOE-15 1.05E-15 9.00E-13 2.25E-13 4.40E-15 6.00E-13 1.50E-13
9/30/2010 d.57E-15 9.00E-14 2.25E-14 1.14E-15 2.00E-14 6.00E-15 7.97E-16 !l.OOE-13 2.25E-13 .3.78E-15 p.OOE-13 1.50E-13
12/31/2010 8.52E-15 9.00E-14 2,25E-14 1.45E-15 2.00E-14 S.OOE-15 1.29E-15 9.00E-13 2.25E-13 1.33E-14 6.00E-13 1.50E-13
4/4/2011 3.20E-15 B.OOE-14 2.25E-14 8.89E-16 2.00E-14 S.OOE-15 l.lOE-15 f.l.OOE-13 2.25E-13 1.48E-14 6.00E-13 1.50E-13
7/4/2011 6.98E-15 9.00E-14 2.25E-14 2.03E-15 2.00E-14 S.OOE-15 2.52E-15 9.00E-13 2.25E-13 l.OBE-14 6.00E-13 1.50E-13
10/3/2011 3.11E-15 9.00E-14 2.25E-14 1.14E-15 2.00E-14 5.00E-15 5.75E-16 9.00E-13 2.25E-13 1.41E-14 6.00E-13 1.50E-13
1/3/2012 4.44E-15 9.00E-14 2.25E-14 2.14E-15 2.00E-14 S.OOE-15 1.53E-15 9.00E-13 2.25E-13 2.05E-14 6.00E-13 1.50E-13
4/3/2012 S.52E-15 9.00E-14 2.25E-14 3,24E-15 2.00E-14 S.OOE-15 1.79E-15 9.00E-13 2.25E-13 1.55E-14 6.00E-13 1.50E-13
7/2/2012 5.87E-15 l:l.OOE-14 2.25E-14 3.06E-15 2.00E-14 S.OOE-15 1.21E-15 9.00E-13 2.25E-13 1.11E-14 6.00E-13 1.50E-13
10/1/2012 6.73E-15 9.00E-14 2.25E-14 2.59E-15 2.00E-14 S.OOE-15 2.43E-15 9.00E-13 2.25E-13 1.30E-14 6,00E-13 1.50E-13
12/31/2012 4.50E-15 f.l.OOE-14 2.25E-14 1.62E-15 2.00E-14 S.OOE-15 1.79E-15 9.00E-13 2.25E-13 1.74E-14 6,00E-13 1.50E-13
3/25/2013 6.66E-15 9.00E-14 2.25E-14 1.48E-15 2.00E-14 S.OOE-15 1.12E-15 9.00E-13 2.25E-13 l.SOE-14 6.00E-13 1.50E-13
7/2/2013 7.35E-15 B.OOE-14 2.25E-14 1.72E-15 2.00E-14 S.OOE-15 2.02E-15 9.00E-13 2.25E-13 6,67E-15 6.00E-13 1.50E-13
9/30/2013 2.78E-15 9.00E-14 2.25E-14 6.92E-16 2.00E-14 5.00E-15 3.29E-16 9.00E-13 2.25E-13 6.62E-15 6.00E-13 1.50E-13
12/30/2013 6.70E-15 9.00E-14 '2.25E-14 3,93E-16 2.00E-14 5.00E-15 2.53E-16 9.00E-13 2.25E-13 2.78E-14 6.00E-13 1.SOE-13
3/31/2014 4.74E-15 9.00E-14 2.25E-14 1.42E-15 2.00E-14 S.OOE-15 3.48E-15 9.00E-13 2.25E-13 1.50E-14 6.00E-13 1.50E-13
6/30/2014 8,18E-15 IJ.OOE-14 2.25E-14 1.34E-15 2.00E-14 5.00E-15 1.76E-15 9.00E-13 2.25E-13 1.42E-14 6.00E-13 1.50E-13
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66-das
95-das
L6-das
95-das
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86-das
<::6-das
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LS·das
gg-das
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<::s-das
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TAB6
BHV-6 AIR SAMPLING GRAPHS AND DATA TABLE
Date Ufluent Concentration Limit = 9E-14 uCi/ml BHV-6U Effluent Concentration Limit = ZE-14 uCi/ml ~HV-6T Effluent Concentration Limit= 9E-13 uCi/ml 1!HV-6R Effluent Concentration Limit = ~E-13 uCi/ml BHV-6PB
ALARA Goal= Z.ZSE-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARA Goal= 2.25E-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml
Prl! 1994 MPC Limit= 5E-1ZuCi/ml Pre 1994 MPC Limit = BE-14 uCi/ml Pte 1994 l'y1PC Limit " 2E-1Z uCi/ml Pre 1994 MPC Urnlt" 4E-1Z uCi/ml
Pre 1994 A LARA GOAL= l.ZSE-12 uCi/ml Pre 1994 ALARA GOAL= 5E-13 uCi/ml Pre 1994 ALARA GOAL -1E-1Z uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC ~FCA Cone ~FC EFCA
9/28/1981 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
12/14/1981 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 .2.00E-12 S.OOE-13 4.00E-12 l.OOE-12
3/29/1982 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 .2.00E-12 S.OOE-13 4 OOE-12 l.OOE-12
6/30/1982 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 .Z.OOE-12 5,00E-13 4.00E-12 1.00E-12
9/27/1982 S.OOE-12 1.25E-12 g.OOE-14 2.00E-14 l ,OOE-12 ·s.OOE-13 4.00E-12 1.00E-12
1/3/1983 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
4/4/1983 S.OOE-12 1.25E-12 S.OOE-14 2.00E-14 l.OOE-12 S.OOE-13 4.00E-12 1.00E-12
6/30/1983 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 :Z,OOE-12 5 OOE-13 4.00E-12 1,00E-12
10/3/1983 S.OOE-12 1.25E-12 s.OOE-14 2.00E-14 l.OOE-12 S.OOE-13 4.00E-12 1.00E-12
1/3/1984 S.OOE-12 1.25E-12 s.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
4/2/1984 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E·12 5.00E-13 4.00E-12 l.OOE-12
7/2/1984 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 LOOE-12
10/1/1984 S,OOE-12 1.25E-12 8.00E-14 2.00E·14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
1/2/1985 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4-00E-12 l.OOE-12
4/1/1985 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1,00E-12
7/1/1985 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
9/30/1985 S.OOE-12 USE-12 S.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
1/2/1986 '5.00E-12 1.25E-12 8.00E-14 2,00E-14 2.00E-12 5,00E-13 4.00E-12 l.OOE-12
4/1/1986 S.OOE-12 1.25E-12 S.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
6/30/1986 S.OOE-12 1.2SE-12 8.00E·14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
10/27/1986 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
12/15}1986 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2,00E-12 5.00E-13 4.00E-12 1.00E-12
3/16/1987 S.OOE-12 1.2SE-12 . S.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
5/11/1987 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
9/9/1987 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE·12
11/2/1987 .S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
2/16/1988 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E·12
5/18/1988 o.OOE-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1 OOE-12
8/15/1988 :S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
11/14/1988 S.OOE-12 1.2SE-12 8.00E-14 2,00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
2/13/1989 S.OOE-12 1.25E-12 S.OOE-14 2,00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
5/15/1989 5.00E-12 1.25E-12 B.OOE-14 MOE-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12
.8/14/1989 S.OOE-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
11/13/1989 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12
2/12/1990 5.00E-12 1.25E-12 8.00E-14 2,00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
5/14/1990 5.00E-12 1.25E-12 8.00E-14 2.00E-14 MOE-12 S.OOE-13 4.00E-12 l.OOE-12
8/13/1990 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
11/12/1990 5.00E-12 1.2SE-12 e.ooe-14 2.00E-14 2,00E-12 S.OOE-13 4.00E-12 l.OOE-12
2/11/1991 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12
5/13/1991 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5,00E-13 4.00E-12 l.OOE-12
8/12/1991 5.00E-12 1.2SE-12 S.OOE-14 2.00E-14 2,00E-12 5.00E-13 4,00E-12 1.00E-12
11}11/1991 5.00E-12 1.25E-12 g.OOE-14 2.00E-14 2,00E-12 S.OOE-13 4.00E-12 l.OOE-12
2/10/1992 5,00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE·12
S/11/1992 5,00E-12 1.25E-12 S.OOE-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE·12
8/10/1992 5.00E-12 1.25E-12 B.OOE-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE·12
11/9/1992 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12
2/9/1993 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4,00E-12 l.OOE-12
5/10/1993 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12
8/10/1993 S,OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5,00E-13 4.00E-12 1.00E-12
11/8/1993 S .. OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E·12 l.OOE-12
2/7/1994 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l,OOE-12
5/9/1994 S,OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
8/9/1994 S,OOE-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12
11/7/1994 S,OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 ------
Date Effluent Concentration Limit= 9E-14 uCi/ml BHV-6U Effluent Concentration Limit= :ZE-14 uCi/ml-BHV-6T Effluent Concentration Limit= 9E-13 uCi/ml BHV-6R Effluent Concentration Limit = 6E-13 uCi/ml BHV-6PB
ALARAGoal = 2.25E-14 uCi}ml ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARAGoal = l.SE-13 uCi/ml
P«! 1994 MPC limit " 5E-12 uCi/ml Pre 1994 MPC Omll "' BE-14 uCi/ml Pre 1994 MPC Limit = 2E-12 uCi/ml Pre 1994 MPC Limit= 4E-12 uCi/ml
Pre 1994 ALARA GOAL = .1.25E-12 uCi/ml Pre 1994 ALARA GOAL = SE-13 uCi/ml Pre 1994 ALARA GOAL= 1E-12 uCi/ml
Cone EFC .EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
5)9/1995 9.00E-14 2.25E-14 ,2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
8/9/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2,25E-13 6.00E-13 1.50E-13
11/11/1995 9.00E-14 :2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
2/5/1996 i:J.OOE-14 .2.25E-14 .2.00E-14 5.00E-15 9.00E-13 2,25E-13 6.00E-13 1.50E-13
5/6/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
&/5/1996 .i:J,OOE-14 .2.25E-14 .2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1,50E-13
11/6/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2..25E-13 6,00E-13 1.50E-13
2/6/1997 9.00E-14 .2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
5/5/1997 9.00E-14 ,2.25E-14 .2.00E-14 5.00E-15 9,00E-13 2.25E-13 6.00E-13 1.50E-13
8/11/1997 9.00E-14 .2.25E-14 .2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
1/5/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
4/28/1998 9.00E-14 :2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
7/31/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2,25E-13 6.00E-13 1.50E-13
9/28/1998 9.00E-14 :2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
12/28/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
3/29/1999 9.00E-14 .2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
7/3/1999 9,00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13
9/27/1999 3,03E-15 9.00E-14 .2.25E-14 1.37E-15 .2.00E-14 5,00E-15 8.72E-16 9.00E-13 2.25E-13 7.55E-15 6.00E-13 1.50E-13
12/28/1999 5.01E-15 9.00E-14 2.25E-14 2.89E-15 2.00E-14 5.00E-15 1.31E-15 9.00E-13 2.25E-13 8.10E-15 6.00E-13 1,50E-13
3)30/2000 7.46E-16 9.00E-14 :2.25E-14 5.25E-16 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 7.83E-15 6.00E-13 1.50E-13
6/26/2000 5.40E-16 !J.OOE-14 .2.25E-14 3.53E-16 2.00E-14 5.00E-15 6.11E-16 9.00E-13 2.25E-13 4.83E-15 6.00E-13 1.50E-13
9/25/2000 3,75E-16 9.00E-14 :2.25E-14 2.23E-16 2.00E-14 5.00E-15 1.91E-16 9.00E-13 2.25E-13 6.41E-15 6.00E-13 1.50E-13
12/26/2000 5.21E-16 9.00E-14 2.25E-14 3.39E-16 l.OOE-14 5.00E-15 3.28E-17 9.00E-13 2.25E-13 8.57E-15 6.00E-13 1.50E-13
3/26/2001 1.42E-16 9.00E-14 ,2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1,00E-16 9.00E-13 2.25E-13 6.15E-15 6.00E-13 1.50E-13
7/2/2001 1.81E-16 9.00E-14 :2.25E-14 1.66E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.95E-15 6.00E-13 1.50E-13
9/24/2001 3.08E-16 9.00E-14 ,2.25E-14 1.01E-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.25E-13 8.59E-15 6.00E-13 1.50E-13
12/31/2001 3.31E-16 9.00E-14 .2.25E-14 1.25E-16 .2.00E-14 5.00E-15 1.09E-16 9.00E-13 2.25E-13 3.14E-15 6.00E-13 1.50E-13
4/1/2002 4.77E-16 !J.OOE-14 .2.25E-14 2.94E-16 .2.00E-14 5.00E-15 1.96E-16 9.00E-13 2.25E-13 8.61E-15 6.00E-13 1.50E-13
7/1/2002 3.68E-16 9.00E-14 2.25E-14 4.41E-16 .2.00E-14 5,00E-15 1.76E-16 9.00E-13 2.25E-13 8.20E-15 6.00E-13 1.50E-13
9/30/2002 3.67E-16 9.00E-14 ,2.25E-14 5.60E-16 2.00E-14 5.00E-15 1.80E-16 9.00E-13 2.25E-13 5.55E-15 6,00E-13 1.50E-13
12/30/2002 1.00E-16 9.00E-14 .2.25E-14 3.43E-16 2.00E-14 5.00E-15 1.67E-16 9.00E-13 2.25E-13 1.35E-14 6.00E-13 1.50E-13
3/31/2003 1.98E-16 9.00E-14 ,2.25E-14 1.68E-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.77E-15 6.00E-13 1.50E-13
6/30/2003 1,18E-16 g,OOE-14 ,2.25E-14 1.15E-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.92E-15 6,00E-13 1.50E-13
9/29/2003 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.30E-15 6.00E-13 1.50E-13
12/29/2003 1,00E-16 !).OOE-14 .2.25E-14 1.36E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.66E-15 6.00E-13 1.50E-13
3/29/2004 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 .2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.17E-15 G.OOE-13 1.50E-13
6/27/2004 l.OOE-16 9.00E-14 .2.25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 3.55E-15 G.OOE-13 1.50E-13
9/27/2004 l.OOE-16 9.00E-14 2.25E-14 1.38E-16 :Z.OOE-14 5.00E-15 l.OOE-16 9.00E-13 2,25E-13 1.22E-14 6.00E-13 1.50E-13
12/27/2004 1.05E-16 9.00E-14 .2.25E-14 1.72E-16 .2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.52E-14 6.00E-13 1.50E-13
3/28/2005 l.OOE-16 9.00E-14 ,2,25E-14 l.OOE-16 ,2.00E-14 5.00E-15 l.OOE-16 9,00E-13 2.25E-13 9.34E-15 6.00E-13 1.50E-13
6/29/2005 1.28E-16 9.00E-14 .2.25E-14 1.01E-16 ,2.00E-14 5,00E-15 l.OOE-16 9.00E-13 2.25E-13 9.85E-15 6.00E-13 1.50E-13
9/26/2005 1.98E-16 9.00E-14 .2.25E-14 5.98E-16 ,2.00E-14 5.00E-15 3.55E-16 9.00E-13 2,25E-13 1.71E-14 6,00E-13 1.50E-13
1/3/2006 7.67E-16 9.00E-14 2.25E-14 2.88E-16 .2.00E-14 5.00E-15 3.60E-15 9.00E-13 2.25E-13 4.85E-14 6.00E-13 1.50E-13
4/3/2006 2.92E-16 9.00E-14 ;2.25E-14 2.00E-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2,25E-13 1.11E-14 6.00E-13 1.50E-13
7/3/2006 3.25E-16 9.00E-14 "2.25E-14 U6E-16 :2.00E-14 5.00E-15 1.08E-16 9.00E-13 2,25E-13 l.lOE-14 6.00E-13 1.50E-13
10/2/2006 5 03E-16 9.00E-14 ,2.25E-14 1.49E-16 2.00E-14 5.00E-15 1.19E-16 9.00E-13 2.25E-13 2.13E-15 6.00E-13 1.50E-13
1/1/2007 8.31E-16 9.00E-14 .2.25E-14 2.49E-16 .2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.50E-13
4/2/2007 5.36E-16 9.00E-14 .2.25E-14 3.15E-16 ,2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.43E-14 6.00E-13 1.50E-13
7/2/2007 1.08E-15 9.00E-14 ,2.25E-14 2.18E-16 2.00E-14 5.00E-15 1.54E-16 9.00E-13 2.25E-13 2.04E-14 6.00E-13 1.50E-13
9/30/2007 3.92E-16 9.00E-14 ,2.25E-14 1.02E-16 .2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.38E-15 6.00E-13 1.50E-13
12/31/2007 2.92E-15 9.00E-14 .2,25E-14 1.55E-15 2.00E-14 5,00E-15 3,16E-16 9.00E-13 2.25E-13 9.19E-15 6.00E-13 1.50E-13
3)31/2008 4.34E-16 9.00E-14 2.25E-14 ~.51E-16 .2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.99E-15 6.00E-13 1,50E-13
6/3102008 1.88E-15 9.00E-14 ,2.25E-14 9.00E-16 2.00E-14 5.00E-15 4.04E-16 9.00E-13 2.25E-13 7.41E-15 6.00E-13 1.SOE-13
Date Effluent Concentration Limit= 9E-14 uCi/ml BHV-6U Effluent Concentration Limit= 2E-14 uCi/ml BHV-6T Effluent Concentration Limit= 9E-13 uCi/ml BHV-6R Effluent Concentration Limit= 6E-13 uCi/ml BHV-6PB
ALARAGoal = 2.25E-14 uCi/ml ,<I.LARAGoal = SE-13 uCi/ml ALARA Goal= 2.25E-13 uCi/ml ALARAGoal = 1.5E-13 uCi/ml
Pre 1994 MPC Limit = 5E-12 uCi{ml Pre 1994 MPC Limit = BE-14 uCi/ml ~re 1994 MPC Limit= 2E-12 uCi/ml Pre 1994 MPC Limit = 4E-12 uCi}ml
Pre 1994 ALARA GOAL = l.ZSE-12 uCi/ml Pre 1994 ALARA GOAL= SE-13 uCi/ml Pre 1994 ALARA GOAL = 1E-12 uCi/ml
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/30/2008 4.82E-15 ~.OOE-14 '~.25E-14 2.10E-15 2.00E-14 S.OOE-15 1.27E-15 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 1.50E-13
12/31/2008 4.80E-15 9.00E-14 2.25E-14 1.70E-15 .2.00E-14 5.00E-15 1.25E-15 9.00E-13 2.25E-13 1.49E-14 6.00E-13 1.50E-13
3/15/2009 2.77E-15 9.00E-14 2.25E-14 1.01E-15 .2.00E-14 5.00E-15 7.82E-16 9.00E-13 2.25E-13 6.46E-15 6.00E-13 1.50E-13
6/15/2009 1.41E-16 9.00E-14 .2.25E-14 2.67E-16 .Z.OOE-14 5.00E-15 1.81E-16 9.00E·13 2.25E-13 5.76E-15 6.00E-13 1.50E-13
9/15/2009 4.87E-15 9.00E-14 2.25E-14 4.32E-16 2.00E-14 5,00E-15 2.23E-16 9.00E-13 2.25E-13 8.98E-15 6.00E-13 1.50E-13
12/15/2009 9.24E-15 9.00E-14 .2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.15E-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 1.50E-13
3/31/2010 9.63E-15 9.00E-14 2.25E-14 1.82E-16 2.00E-14 5.00E-15 2.06E-16 9.00E-13 2.25E-13 1.37E-14 6.00E-13 1.50E-13
6/30/2010 3.62E-15 9.00E-14 2.25E-14 3.94E-16 2.00E-14 5.00E-15 4.89E-16 9.00E-13 2.25E·13 4.30E-15 6.00E-13 1.50E-13
9/30/2010 5.42E-15 ~.OOE-14 2.25E-14 1.08E-15 2.00E-14 5.00E-15 5.68E-16 9.00E-13 2.25E-13 3.98E-15 6.00E-13 1.50E-13
12/31/2010 1.24E-14 9.00E-14 .2.25E-14 1.21E-15 2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
4/4/2011 2.70E-15 9.00E-14 .2.25E-14 4.62E-16 2.00E-14 5.00E-15 6.51E-16 9.00E-13 2.25E-13 1.29E-14 6.00E-13 1.50E-13
7/4/2011 3.01E-15 9.00E-14 .2.25E-14 7.07E-16 2.00E-14 5.00E-15 5.75E-16 9.00E-13 2.25E-13 7.97E-15 6.00E-13 1.50E-13
10/3/2011 2.05E-15 9.00E-14 2.25E-14 6.12E-16 2.00E-14 5.00E-15 1.88E-16 9.00E-13 2.25E-13 9.93E-15 6.00E-13 1.50E-13
1/3/2012 3.14E-15 9.00E-14 ·2.25E-14 1.09E-15 2.00E-14 5.00E-15 7.65E-16 9.00E-13 2.25E-13 1.89E-14 6.00E-13 1.50E-13
4/3/2012 4.41E-15 9.00E-14 ,2.25E-14 1.82E-15 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 l.SOE-14 6.00E-13 1.50E-13
7/2/2012 6.42E-15 9.00E-14 2.25E-14 2.25E-15 2.00E-14 5.00E-15 5.11E-16 9.00E-13 2.25E-13 9.54E-15 6.00E-13 1.50E-13
10/1/2012 6.63E-15 9.00E-14 2.25E-14 1.31E-15 2.00E-14 5.00E-15 1.22E-15 9.00E-13 2.25E-13 1.34E-14 6.00E-13 1,50E-13
12/31/2012 3.83E-15 ~.OOE-14 2.25E-14 1.18E-15 2.00E-14 5.00E-15 9.30E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 1.50E-13
3/25/2013 4.52E-15 9.00E-14 2.25E-14 7.93E-16 2.00E-14 5.00E-15 4.91E-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.50E-13
7/2/2013 5.91E-15 9.00E-14 2.25E-14 6.74E-16 2.00E-14 5.00E-15 7.85E-16 9.00E-13 2.25E-13 5.18E-15 6.00E-13 1.50E-13
9/30/2013 2.68E-15 9.00E-14 2.25E-14 3.97E-16 2.00E-14 5.00E-15 1.04E-16 9.00E-13 2.25E-13 6.13E-15 6.00E-13 1.50E-13
12/30/2013 1.60E-14 9.00E-14 2.25E-14 2.48E-16 2.00E-14 . 5.00E-15 1.05E-16 9.00E-13 2.25E-13 2.67E-14 6.00E-13 1.50E-13
3/31/2014 8.92E-15 9.00E-14 .2.25E-14 7.68E-16 2.00E-14 5.00E-15 1.50E-15 9.00E-13 2.25E-13 1.61E-14 6.00E-13 1.50E-13
6/30/2014 8.29E-15 9.00E-14 2.25E-14 5.35E-16 2.00E-14 5.00E-15 6.72E-16 9.00E-13 2.25E-13 l.ZOE-14 6.00E-13 1.50E-13
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ATTACHMENT C
BHV AIR SAMPLING LABORATORY RESULTS AND QAJQC
EI\ERGY
L '1• t ,,,;.I :_d.JI '
www.energylab.com
,.,_ En:ellwlclstw. IIU
Helena, MT 877-472-G711 • Billings, MT 101·735-440 • Casper, WV 811·235·1515
Gillett&, WY 11&-188· 7175 • Rapid Ctty, SD 118-872·1225 • College Station, TX 881-BUD-2211
May 20, 2014
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C14040336
Project Name: 1st Quarter Air 2014
ANALYTICAL SUMMARY REPORT
Energy Laboratories, Inc. Casper WY received the following 6 samples for Energy Fuels Resources (USA) Inc on 4/9/2014 for
analysis.
LabiD Client Sample ID Collect Date Receive Date Matrix Test
c 14040336-001 BHV-1 03/31 /14 00:00 04/09/14 Filter Composite of two or more samples
Field Parameters
Metals, Total
Digestion, Total Metals
RAD Alternate Unit Reporting Air
Filters
Lead 210
Radium 226
Thorium, Isotopic
c 14040336-002 BHV-2 03/31/14 00:00 04/09/14 Filter Same As Above
C14040336-003 BHV-4 03/31 /14 00:00 04/09/14 Filter Same As Above
C14040336-004 BHV-5 03/31/14 00:00 04/09/14 Filter Same As Above
c 14040336-005 BHV-6 03/31/14 00:00 04/09/14 Filter Same As Above
c 14040336-006 Blank 03/31/14 00:00 04/09/14 Filter Same As Above
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 OA/QC Summary Report, or the Case Narrative.
If you have any questions regarding these test results, please call.
Report Appmved By' ~ z kh,__-
Acling Branch Manager ·
Digitally signed by
Steve Carlston
Date: 2014.05.20 11:51:25 -06:00
Page 1 of22
·~·~· ... ~--·-··-....... --...... ~ ..................... --,.
Gilletta, WY 818-688-117! • Rapid City, SD 888-&72·1225 • Collage station, TX 181-610-2218
CLIENT: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Sample Delivery Group: C14040336
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4"C (±2"C)
Report Date: 05/20/14
CASE NARRATIVE
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.
SOIUSOLID 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 Ell 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-cs -Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
USEPA: WY00002, Radiochemical WY00937; FL-DOH NELAC: E87641, Radiochemical E871017; California: 02118CA;
Oregon: WY200001, Radiochemical WY200002; Utah: WY00002; 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 Ell's certification coverage by visiting www.energylab.com
Ell 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 22
EI\ERGY
f', :-II-1,•, 1 ';.o .. JII •o
www.energylab.com
Mlfyt/AI ,..,. Sit/c. llfl
Helena, MT 871·412·0711 • Billings, MT 800-735·4489 • Casper, WY 881·235·0515
Gillette, WY 866·686-7175 • Rapid City, SD 118·672-1225 • Collage station, TX 888·690·2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20, 2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: BHV-1
Quarter/Date Sampled Concentration Radio nuclide Air Volume J1CilmL
C14040336-001 ""'u 1.07E-15
First Quarter 2014 23oTh 2.07E-16
Air Volume in mLs 226Ra 3.69E-16
1.36E+11 2IOPb 1.24E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
J1CilmL
N/A
3E-17
3E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B-Table 2
Yearfor Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC J1CilmL
N/A
1E-17
IE-17
9E-17
L.L.D.+ Effluent Cone.* %Effluent
11CilmL J1CilmL Concentration
1E-16 9E-14 1.19E+00
1E-16 3E-14 6.91E-01
1E-16 9E-13 4.11E-02
2E-15 6E-13 2.07E+00
Page 3 of 22
EN:RGY
f .1\ t<-:-. >I '..)UII ~
www.energylab.com
IMifl/alm.r.-Siia ,.
Helena, MT 817-412-0111 • Billings, MT BOD-735-4489 • Casper, WY 888-235-0515
Gillette, W'f 8&6-&8&-7175 • Rapid City, SD 818-172-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
LabiD: c 14040336-001
Client Sample ID: BHV-1
Analyses Result Units
TRACE METALS -IN AIR
Uranium 1.6E-09 mgiL
Uranium, Activity 1.1 E-15 uCilmL
RADIONUCLIDES-IN AIR
Lead 210 1.2E-14 uCilmL
Lead 210 precision (±) 2.3E-16 uCilmL
Lead 210 MDC 9.4E-17 uCilmL
Radium 226 3.7E-16 uCilmL
Radium 226 precision (±) 2.7E-17 uCilmL
Radium 226 MDC 1.0E-17 uCilmL
Thorium 230 2.1E-16 uCilmL
Thorium 230 precision (±) 3.3E-17 uCilmL
Thorium 230 MDC 1.2E-17 uCilmL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210
Lead 21 0 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Anaiyte reporting limit.
QCL-Quality control limit.
1700 pCiiFiiter
31.1 pCi!Fiiter
12.8 pCiiFilter
50.4 pCiiFilter
3.7 pCiiFiiter
1.4 pCiiFilter
28.3 pCiiFilter
4.5 pCi/Filter
1.6 pCiiFilter
146 pCiiFilter
136421082 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 05/20/14
Collection Date: 03/31/14
Date Received: 04/09/14
Matrix: Filter
Method Analysis Date I By
SW6020 04118114 12:08 I elm
SW6020 04118114 12:08 I elm
E909.0 05106114 18:051 eli-cs
E909.0 05106114 18:05 I eli-cs
E909.0 05106114 18:05 I eli-cs
E903.0 04123114 06:38 lime
E903.0 04123114 06:381imc
E903.0 04123114 06:38 lime
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05/15114 17:58 I sec
RADCALC 05/15114 17:58 I sec
RADCALC 05/15/14 17:58 I sec
RADCALC 05115/14 17:58 I sec
RADCALC 05/15/1417:58 I sec
RADCALC 05115/14 17:58 I sec
RADCALC 05/15114 17:58 I sec
FIELD 03/31114 00:00 I***
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 4 of22
www.energylab.com
INIIflai~SIIa 111n
Helena, MT 177-472-0711 • BillinRs, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 866-616-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20, 2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: BHV-2
Quarter/Date Sampled Concentration Radionuclide Air Volume ~CilmL
C14040336-002 ""'U 4.63E-16
First Quarter 2014 23oTh 4.97E-17
Air Volume in mLs 226Ra 1.15E-16
1.36E+11 210Pb 1.49E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
~CilmL
N/A
1E-17
9E-18
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC~Ci/mL
N/A
6E-18
3E-18
9E-17
L.L.D.+ Effluent Cone.* o/o Effluent
~Ci/mL ~CilmL Concentration
1E-16 9E-14 5.15E-01
1E-16 3E-14 1.66E-01
IE-16 9E-13 1.28E-02
2E-15 6E-13 2.48E+00
Page 5 of22
www.energylab.com EN:RGY
I #\1 I ( )I • I'• I (_,;,t• ', MMtbl En:ellwa Slll:l 11!1
Helena, MT 817-412-11111 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY IB&-&8&-7175 • Rapid City, SD 818-872-1225 • Collage Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
LabiD: c 14040336-002
Client Sample ID: BHV-2
Analyses Result Units
TRACE METALS • IN AIR
Uranium 6.8E-10 mgiL
Uranium, Activity 4.6E-16 uCilmL
RADIONUCLIDES • IN AIR
Lead 210 1.5E-14 uCilmL
Lead 21 0 precision (±) 2.4E-16 uCilmL
Lead 210 MDC 9.1E-17 uCilmL
Radium 226 1.2E-16 uCilmL
Radium 226 precision (±) 8.6E-18 uCilmL
Radium 226 MDC 3.2E-18 uCilmL
Thorium 230 5.0E-17 uCilmL
Thorium 230 precision (±) 1.0E-17 uCilmL
Thorium 230 MDC 5.6E-18 uCi/mL
RADIONUCLIDES • IN AIR -PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
2030 pCi/Filter
33.4 pCiiFilter
12.4 pCiiFilter
15.7 pCiiFilter
1.2 pCiiFilter
0.44 pCiiFilter
6.8 pCiiFilter
1.4 pCiiFilter
0.76 pCiiFilter
63.2 pCiiFilter
136430085 L
MDC -Minimum detectable concentration
Qualifiers
MCL!
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 05/20/14
Collection Date: 03/31/14
DateReceived: 04/09/14
Matrix: Filter
Method Analysis Date I By
SW6020 0411811412:11 I elm
SW6020 04118114 12:11 I elm
E909.0 05106114 22:40 I eli-cs
E909.0 05106114 22:40 I eli-cs
E909.0 05106114 22:40 I eli-cs
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E908.0 04123114 13:37 I dmt
E908.0 04123114 13:37 I dmt
E908.0 04123114 13:37 I dmt
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
FIELD 03131114 00:00 I***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 22
EI\ERGY
,~ I '' '' ~ ·, Jo J, I
www.energylab.com
IM/yl/al £JI:IIItlcl ~ IIJZ
Helene, MT 877-472-0711 • Billings, MT BOD· 735-4489 • Casper, WY 888-235-0515
Gillette, WYB&&-&8&-7175 • Rapid City, SD 888-&72-1225 • College Station,lX 888-&90-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20,2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: BHV -4
Quarterillate Sampled Concentration Radionuclide Air Volume J!CilmL
C14040336-003 "''U 4.69E-15
First Quarter 2014 230Th 1.37E-16
Air Volume in mLs 226Ra 3.53E-16
1.35E+I I 210pb_ 1.08E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
J!CilmL
N/A
2E-17
2E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDCJJCilmL
N/A
1E-17
SE-18
9E-17
L.L.D.+ Effluent Cone.* %Effluent
JJCilmL J!CilmL Concentration
1E-16 9E-14 5.21E+00
1E-16 3E-14 4.58E-01
IE-16 9E-13 3.93E-02
2E-15 6E-13 1.81E+00
Page 7 of22
www.energylab.com EN:RGY
I •'~•:lU I •J\l(_:IJ I _•_. IMiyllal Elcelltla Sllu II!Z
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillatts, WY 866-&86·7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
LabiD: c 14040336-003
Client Sample ID: BHV-4
Analyses Result Units
TRACE METALS -IN AIR
Uranium 6.9E-09 mgiL
Uranium, Activity 4.7E-15 uCilmL
RADIONUCLIDES • IN AIR
Lead 210 1.1E-14 uCilmL
Lead 210 precision (±) 2.1 E-16 uCilmL
Lead 210 MDC 9.4E-17 uCilmL
Radium 226 3.5E-16 uCilmL
Radium 226 precision (±) 1.9E-17 uCilmL
Radium 226 MDC 5.2E-18 uCilmL
Thorium 230 1.4E-16 uCilmL
Thorium 230 precision (±) 2.4E-17 uCilmL
Thorium 230 MDC 1.0E-17 uCi/mL
RADIONUCLIDES • IN AIR • PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
1470 pCiiFilter
28.9 pCi/Filter
12.7 pCi/Filter
47.8 pCi/Filter
2.6 pCiiFilter
0.71 pCiiFilter
18.6 pCi/Filter
3.2 pCiiFilter
1.4 pCiiFilter
634 pCiiFilter
135285983 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-1 0
1.0E-16
0.20
Report Date: 05/20/14
Collection Date: 03/31/14
Date Received: 04/09/14
Matrix: Filter
Method Analysis Date I By
SW6020 04118114 12:14 I elm
SW6020 04118114 12:14 I elm
E909.0 05107114 00:12 I eli-cs
E909.0 05107114 00:12 I eli-cs
E909.0 05107114 00:12 I eli-cs
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
FIELD 03131114 00:00 I •••
MCL -Maximum contaminant level.
ND-Not detected at the reporting limit.
Page 8 of22
www.energylab.com
ANI1flal ~stm:e 1m
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
GilleHe, WY 866·686-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20,2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: BHV-5
Quarter/Date Sampled Concentration Radio nuclide Air Volume f.ICilmL
C14040336-004 nalu 4.74E-15
First Quarter 2014 230Th 1.42E-15
Air Volume in mLs 226Ra 3.48E-15
1.35E+ll 210Pb l.SOE-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
f.ICilmL
N/A
IE-16
8E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDCf.ICilmL
N/A
2E-17
IE-17
9E-17
L.L.D.+ Effluent Cone.* %Effluent
f.ICilmL f.ICilmL Concentration
IE-16 9E-14 5.27E+00
IE-16 3E-14 4.73E+00
IE-16 9E-13 3.86E-Ol
2E-15 6E-13 2.51E+00
Page 9 of22
www.energylab.com EI\ERGY
l •• -,1_11 c. i l.:OI t il ~ Au11tJa1 EmiMct S.C. IIBI
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 888-686-7175 • Rapid City, SD 888-672-1225 • Collage Station, 1X 888-&90-221 8
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Lab ID: c 14040336-004
Client Sample ID: BHV-5
Analyses Result Units
TRACE METALS -IN AIR
Uranium 7.0E-09 mgl l
Uranium, Activity 4.7E-15 uCilml
RADIONUCLIDES-IN AIR
Lead 210 1.5E-14 uCilmL
Lead 21 0 precision (±) 2.5E-16 uCilmL
Lead 210 MDC 9.3E-17 uCilmL
Radium 226 3.5E-15 uCilmL
Radium 226 precision (±) 8.2E-17 uCilml
Radium 226 MDC 1.0E-17 uCi/mL
Thorium 230 1.4E-15 uCi/mL
Thorium 230 precision (±) 1.5E-16 uCilmL
Thorium 230 MDC 2.4E-17 uCilmL
RADIONUCLIDES-IN AIR • PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
2040 pCiiFilter
33.6 pCi/Filter
12.6 pCi/Filter
470 pCi/Filter
11 .1 pCiiFilter
1.4 pCi/Filter
192 pCi/Filter
20.1 pCiiFilter
3.2 pCiiFilter
641 pCiiFilter
135287479 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL OCL
1.5E-10
1.0E-16
0.20
Report Date: 05/20/14
Collection Date: 03/31/14
Date Received: 04/09/1 4
Matrix: Filter
Method Analysis Date I By
SW6020 0411811412:17 I elm
SW6020 04118114 12:17 I elm
E909.0 05107114 01 :43 I eli-cs
E909.0 05/07114 01:43 I eli-cs
E909.0 05/07114 01:43 I eli-cs
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 /lmc
E908.0 04123/14 13:37 I dmf
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
RADCALC 05115114 17:58 I sec
RADCALC 05115/14 17:58 I sec
RADCALC 05115/14 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05/15114 17:58 I sec
RADCALC 05/15114 17:58 I sec
RADCALC 05/15/14 17:58 I sec
RADCALC 05/15114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
FIELD 03131114 00:00 I***
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 10 of 22
EI\ERGY
! I • I ( • ~ .~ I t 'I <It 1
www.energylab.com
Alllllf/UI EmiiMce Sltlct II$%
Helena, MT 877-472-0711 • Billings, MT BOD-735·4489 • Casper, WY 188-235-0515
Gillette, WY 866-686-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20,2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: BHV-6
Quarter/Date Sampled Concentration Radionuclide Air Volume JJCilmL
C14040336-005 ""U 8.92E-15
First Quarter 2014 23oTh 7.68E-16
Air Volume in mLs 226Ra l.SOE-15
1.35E+ll zwPb 1.61E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
,..cilmL
N/A
lE-16
4E-17
3E-16
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDCJ!CilmL
N/A
2E-17
6E-18
9E-17
L.L.D.+ Effluent Cone.* %Effluent
J.!CilmL J!CilmL Concentration
lE-16 9E-14 9.91E+00
lE-16 3E-14 2.56E+00
IE-16 9E-13 1.67E-OI
2E-15 6E-13 2.69E+00
Page 11 of 22
EN:RGY
t .-,-l ..... , ._11 ... 1• .:
www.energytab.com
AM/fbi~SIIu 1/I!Z
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 818-686-7175 • Rapid City, SD 118-672-1225 • College Station, 1X 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
LabiD: c 14040336-005
Client Sample ID: BHV-6
Analyses Result Units
TRACE METALS-IN AIR
Uranium 1.3E-08 mgiL
Uranium, Activity 8.9E-15 uCilmL
RADIONUCLIDES -IN AIR
Lead 210 1.6E-14 uCilmL
Lead 21 0 precision (±) 2.6E-16 uCi/mL
Lead 210 MDC 9.2E-17 uCil mL
Radium 226 1.5E-15 uCil mL
Radium 226 precision (±) 4.0E-17 uCil mL
Radium 226 MDC 5.7E-18 uCil mL
Thorium 230 7.7E-16 uCi/mL
Thorium 230 precision (±) 9.7E-17 uCilmL
Thorium 230 MDC 1.7E-17 uCilmL
RADIONUCLIDES-IN AIR-PER Fll TER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
2180 pCiiFilter
34.6 pCiiFilter
12.5 pCiiFilter
203 pCiiFilter
5.5 pCiiFilter
0.77 pCiiFilter
104 pCiiFilter
13.1 pCiiFilter
2.3 pCii Filter
1210 pCiiFilter
135283468 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL OCL
1.5E-10
1.0E-16
0.20
Report Date: 05/20/14
Collection Date: 03/31 /14
DateReceived: 04/09/14
Matrix: Filter
Method Analysis Date I By
SW6020 04118114 12:23 I elm
SW6020 04118114 12:23 1 elm
E909.0 05107114 03:151 eli-cs
E909.0 05107114 03:151 eli-cs
E909.0 05107114 03:15 I eli-cs
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 l ime
E903.0 04123114 06:38 l ime
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 1 dmf
E908.0 04123114 13:37 I dmf
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 0511511417:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
FIELD 03131114 00:00 I***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 12 of22
www.energylab.com
A/llfrt/UI ~S/Jtef IISI
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WV 888-235-0515
Gillette, WY 866-686-7175 • Rapid City, SO BBB-612-1225 • College Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: May 20,2014
PROJECT: 1st Quarter Air 2014
SAMPLE ID: Blank
Quarter/Date Sampled Concentration Radionuclide Air Volume J!CilmL
C14040336-006 natu 1.46E-17
First Quarter 2014 230Th 1.98E-18
Air Volume in mLs 226Ra 2.79E-18
1.36E+II 210Pb -1.20E-17
Counting
Precision
J!CilmL
N/A
lE-18
2E-18
4E-17
Note: Th1s sample uses 136,000,000 L of air volume for companson purposes.
+LLD's are from NRC Reg. Guide 4.14
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-21 0
MDC J!CilmL
N/A
2E-18
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
J!Ci/mL J!CilmL Concentration
1E-16 9E-14 1.62E-02
1E-16 3E-14 6.60E-03
IE-16 9E-13 3.10E-04
2E-15 6E-13 -2.0JE-03
Page 13 of22
EN:RGY
I /\• I~,,-, l· 1 ' Ill! '.l
www.energylab.com
AMiybl E'Balleta Slllu 11152
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-8515
Gillette, WY 866-686-7115 • Rapid Crty, SD 888-612-1225 • College Station, TX 888-690-2218
LABORATORY ANAL VTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Lab ID: c 14040336-006
Client Sample ID: Blank
Analyses
TRACE METALS -IN AIR
Uranium
Uranium, Activity
RADIONUCLIDES -IN AIR
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
RADIONUCLIDES-IN AIR-PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
Result Units
0.0029 mgll
2.0E-09 uCilmL
-1.6E-09 uCilmL
5.3E-09 uCilmL
9.0E-09 uCilmL
3.8E-10 uCilmL
2.2E-10 uCilmL
2.8E-10 uCilmL
2.7E-10 uCilmL
1.6E-10 uCilmL
2.1E-10 uCilmL
-1.6 pCi!Filter
5.3 pCi/Filter
9.0 pCiiFilter
0.38 pCiiFilter
0.22 pCiiFilter
0.28 pCiiFilter
0.27 pCiiFilter
0.16 pCiiFilter
0.21 pCiiFilter
2.0 pCiiFilter
1 L
MDC -Minimum detectable concentration
Qualifiers
D
D
u
u
U -Not detected at minimum detectable concentration
MCL/
RL QCL
0.000043
2.9E-11
0.20
Report Date: 05/20/14
Collection Date: 03/31/14
Date Received: 04/09/14
Matrix: Filter
Method Analysis Date I By
SW6020 04118114 12:36 I elm
SW6020 04118114 12:36 I elm
E909.0 05107114 04:46 I eli-cs
E909.0 05107114 04:46 I eli-cs
E909.0 05107114 04:46 I eli-cs
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E903.0 04123114 06:38 I lmc
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
E908.0 04123114 13:37 I dmf
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
RADCALC 05115114 17:58 I sec
FIELD 03131114 00:00 I ***
MCL -Maximum contaminant level.
ND-Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 14 of22
EN:RGY
l .~. ~ l 1• ) J. ~A· I _j( "I. -'
www.energylab.com
AM/yfii:M Eml/wJu SIRu ISU
Helena, MT 811-412·0711 • Billings, MT 800-735·4489 • Casper, WV 888-235-1515
Gillatta, WY 8&&-&86-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-&90-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Analyte
Method: E903.0
Lab ID: C 14040336-004AD UP
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C14040336-005AMS
Radium 226
Lab ID: LCS-41112
Radium 226
Lab ID: MB-41112
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte reporting limit.
Count Result Units
3 Sample Duplicate
3.50E·06 pCi/L
8.30E-08 pCi/L
1.03E-08 pCi/L
Sample Matrix Spike
2.82E-06 pCi/L
Laboratory Control Sample
23.6 pCi/L
3 Method Blank
·0.05 pCi/L
0.1 pCi/L
0.2 pCi/L
MDC · Minimum detectable concentration
Report Date: 05/20/14
Work Order: C14040336
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: BERTHOLD 770·2_140417A
0.5
Run: BERTHOLD 770·2_140417A
116 70 130
Run: BERTHOLD 770·2 140417A
110 80 120
Run: BERTHOLD 770·2_140417 A
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 41112
04/23/14 06:38
14.7
04/23/14 06:38
04/23/14 06:38
04/23/14 09:43
u
Page 15 of 22
EN:RGY
l ·~~,,p,q tJI: ~
www.energylab.com
Allll/ffiDM En:tlltwl&l Slla 1152
Helena, MT 817-472-0711 • Billings, MT 800-735·4489 • Casper, WV 888-235-1515
Gillatta, WV 8&&-&8&-7175 • Rapid City, SD 888-&72-1225 • College Station, 1X 888-690-!218
QAJQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Analyte Count Result Units
Method: E908.0
Lab ID: C14040336-002AMS
Thorium 230
Lab ID: C14040336-002AMSD
Thorium 230
Lab ID: LCS-41112
Thorium 230
Lab ID: MB-41112
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Qualifiers:
RL -Analyte reporting limit.
3
MDC - Minimum detectable concentration
Sample Matrix Spike
1.18E-06 pCi/L
Sample Matrix Spike Duplicate
1.21 E-06 pCi/L
Laboratory Control Sample
27.6 pCi/L
Method Blank
0.4 pCi/L
0.2 pCi/L
0.3 pCi/L
Report Date: 05/20/14
Work Order: C14040336
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run:ALPHANALYST_140421A
98 70 130
Run: ALPHANAL YST _140421 A
101 70 130 3.1
Run:ALPHANALYST_140421A
104 80 120
Run:ALPHANALYST_140421A
NO -Not detected at the reporting limit.
Batch: 41112
04/23/14 13:37
04/23/14 13:37
29.5
04/23/14 13:37
04/23/1413:37
Page 16 of 22
EI\ERGY
l 1\ • It ! I ,• '• I 1_; I~· I· '-•
www.energylab.com
IM/fllai~S'-JJU
Helena, MT 817-472-0711 • Billings, MT 800-735-4489 • Casper, WY BBB-235-1515
Gillette, WY 866-686-7115 • Rapid City, Sll 888-672-1225 • College Station, TX 888-690-2218
QAJQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014
Analyte Count Result Units
Method: E909.0
Lab ID: LCS-21048
Lead 210
Lab ID: MB-21048
Lead 210
Lead 21 0 precision (±)
Lead 210 MDC
Lab ID: C14040336-001AMS
Lead 210
Lab ID: C14040336-001AMSD
Lead 210
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Laboratory Control Sample
103 pCi/L
Method Blank
-3 pCi/L
5 pCi/L
9 pCi/L
Sample Matrix Spike
1.78E-05 pCi/L
Sample Matrix Spike Duplicate
1.74E-05 pCi/L
Report Date: 05/20/14
Work Order: C14040336
RL %REC Low Limit High Limit
Run: SUB-T56720
81 80 120
Run: SUB-T56720
Run: SUB-T56720
125 70 130
Run: SUB-T56720
115 70 130
NO-Not detected at the reporting limit.
RPD RPDLimit Qual
2.7
Batch: T~21 048
05/06/14 15:02
05/06/14 16:34
u
05/06/14 19:37
05/06/14 21 :08
15.8
U -Not detected at minimum detectable concentration
Page 17 of 22
·-El\ERGY www.energylab.com Helena, MT 877-472-011 t • Billings, MT 801·735-4489 • Casper, WY 888-235·1515
Gillatts, WY 866-68&-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690·2218 I 1\ • ~ l I ·.,I · .!i 'I· • AM/ftk:M Etwlltlta Sl1lr:l IIIU
QAJQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2014 I Analyte Count Result
Method: SW6020
Units
Report Date: 05/20/14
Work Order: C14040336
RL %REC Low Limit High Limit RPD RPDLimit Qual
Lab ID: ICV Initial Calibration Verification Standard
Analytical Run: ICPMS2-C_140417A
04/18/14 10:35
Uranium
Lab ID: ICSA
Uranium
LabiD: ICSAB
Uranium
Method: SW6020
Lab 10: MB-41112
Uranium
Lab ID: LCS2-41112
Uranium
Lab 10: C14040336·004ADIL
Uranium
Lab 10: C14040336-006AMS
Uranium
LabiD: C14040336·006AMSD
Uranium
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
0.0499 mg/L 0.00030 100 90 110
Interference Check Sample A
0.000634 mg/L 0.00030
Interference Check Sample AB
-0.000259 mg/L 0.00030
Method Blank Run: ICPMS2-C_140417A
ND mg/L 4E-05
Laboratory Control Sample Run: ICPMS2-C_140417A
0.0974 mg/L 4.3E-05 97 85 115
Serial Dilution Run : ICPMS2-C_140417A
6.38E-09 mg/L 1.5E-10
Sample Matrix Spike Run : ICPMS2-C_140417A
0.256 mg/L 4.3E-05 101 75 125
Sample Matrix Spike Duplicate Run: ICPMS2-C_140417A
0.262 mg/L 4.3E-05 104 75 125
ND -Not detected at the reporting limit.
9.3
2.3
04/18/14 10:38
04/18/14 10:41
Batch: 41112
04/18/14 11 :58
04/18/14 12:01
04/18/14 12:20
20
04/18/14 12:39
04/18/14 12:42
20
Page 18 of 22
EI\ERGY
: 1\ !' r •· I' Jt-'1
www.energylab.com
AMI1flal ElrfiiMa .. 1152
Helena, MT 877-472-0711 • Billings, MT 800-73!1-4489 • Casper, WY 888-235-0!115
Gillette, WY 866-686-7175 • Rapid City, SO 888-172-122!1 • College Station, TX 888-&90-2211
Workorder Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Corinne Wagner
Reviewed by:
Reviewed Date:
BL2000\khelm
4/11/2014
Shipping container/cooler in good condition?
Custody seals intact on all shipping container(s)/cooler(s)?
Custody seals intact on all 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 Cl, Sulfite, Ferrous Iron, etc.)
Temp Blank received in all shipping container(s)/cooler(s)?
Container/Temp Blank temperature:
Water-VOA vials have zero headspace?
Water-pH acceptable upon receipt?
Yes 0
Yes 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
N/A'C
Yes D
Yes D
C14040336
Date Received: 4/9/2014
Received by: dcq
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
Carrier Next Day Air
name:
Not Present D
Not Present D
Not Present 0
Not Applicable 0
NoVOA vials submitted 0
Not Applicable 0
---------------------------------------------------------------------------------~
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.
Contact and Corrective Action Comments:
None
Page 19 of 22
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: Energy Laboratories Contact: Garrin Palmer -=2:..;.;39.,;;.;3~Sf-a.:,;.lt;;;.;;C~r.;..;ee;;.;,.k~H,;.;;.wy-=--------Ph: 435 678 4115
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samplers Name Samplers Signature
1st Quarter Air 2014 Garrin Palmer I
Time
SampleiD Date Collected Collected Laboratory Anal~sis Requested
BHV-1 12/30/14-3/31/14 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-2 12/30/14-3/31/14 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-4 12/30/14-3/31114 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-5 12130/14-3/31/14 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-6 12/30/14-3/31/14 NA U-NAT. TH-230, Ra-226, Pb-21 0
Blank 12/30/14-3/31/14 NA U-NAT, TH-230, Ra-226, Pb-21 0
Comments:
Relinquished By:(Signature) DateTTime Received By:(Signature) Datemme
Garrin Palmer 4/7/2014
1230
ReliGI~ig~ Date/Time Received By:(Signature) DatefTime
~~~~ 4lq}14 q, ~I b
www.energylab.com EI\ERGY
I I' •• ' 'I~ I • , I! Alfll1l/rll blllltla lila 1111
Halana, MT 877-472-0711 • Billings, MT 800·738·4488 • Caspar, WY 888·235·8515
Gillette, WY 888-888-7171 • Rapid City, SD 111·872·1221 • Collage station, TX 888·81D-Z211
ANALYTICAL SUMMARY REPORT
July 29, 2014
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C 14070123
Project Name: 2nd Quarter Air 2014
Energy Laboratories, Inc. Casper WY received the following 6 samples for Energy Fuels Resources (USA) Inc on 7/2/2014 for
analysis.
LabiD Client Sample ID Collect Date Receive Date Matrix Test
C14070123-001 BHV-1 06/30/14 00:00 07/02/14 Filter Composite of two or more samples
Field Parameters
Metals, Total
Digestion, Total Metals
RAD Alternate Unit Reporting Air
Filters
Lead 21 o
Radium 226
Thorium, Isotopic
c 14070123-002 BHV-2 06/30/14 00:00 07/02/14 Filter Same As Above
c 14070123-003 BHV-4 06/30/14 00:00 07/02/14 Filter Same As Above
c 14070123-004 BHV-5 06/30/14 00:00 07/02/14 Filter Same As Above
C14070123-005 BHV-6 06/30/14 00:00 07/02/14 Filter Same As Above
c 14070123-006 Blank 06/30/14 00:00 07/02/14 Filter Same As Above
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:
Digitally signed by
Steve Carlston
Date: 2014.07.29 16:49:21 -06:00
Page 1 of 22
........ -... , .......... -·--·--.......... -........ ...... ·-·--... ...-.. -· ....... ..
Glllattl, WY 888-8811-7175 • Rapid City, SD 888-&72-1225 • Collage Station, IX 888-680-2218
CLIENT: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Sample Delivery Group: C14070123
ANALYTICAL COMMENTS
Report Date: 07/29/14
CASE NARRATIVE
Tests associated with analyst identified as ELI-CS were subcontracted to Energy Laboratories, 415 Graham Rd., College
Station, TX, EPA Number TX01520.
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4'C (±2'C)
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.
SOIUSOLID 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 Ell 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-cs -Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
US EPA: WY00002, Radiochemical WY00937; FL-DOH NELAC: E87641, Radiochemical E871 017; California: 02118CA;
Oregon: WY200001, Radiochemical WY200002; Utah: WY00002; 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 Ell's certification coverage by visiting www.energylab.com
Ell appreciates the opportunity to provide you with this analytical service. For additional information and services visit our web
page www.energylab.com.
Page 2 of22
www.energylab.com
AnlfYIIul &ullwlu Slnr:. IIU
Halana, MT 877-412-0711 • Billings, MT BDD-735-4481 • Casper, W'/888-235-0515
Gillette, WY B&B-&8&-7175 • Rapid City, SD 888-812-1225 • College Station, 1X 888·690·2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29,2014
PROJECT: 2nd Quarter Air 2014
SAMPLEID: BHV-1
Quarterillate Sampled Concentration
Air Volume Radionuclide JiCilmL
C14040336-001 ""U 1.07E-15
First Quarter 2014 23uTh 2.07E-16
Air Volume in mLs 226Ra 3.69E-16
1.36E+l1 2\0J>b 1.24E-14
Quarterillate Sampled Concentration Radionuclide Air Volume 11CilmL
C14070123-001 ""U 2.24E-15
Second Quarter 2014 230Th 5.14E-16
Air Volume in mLs 226Ra 1.09E-15
1.36E+11 210Pb 1.23E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
JiCilmL
N/A
3E-17
3E-17
2E-16
Counting
Precision
JiCi/mL
N/A
6E-17
IE-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B-Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC JiCilmL
N/A
1E-17
1E-17
9E-17
MDC 11CilmL
N/A
1E-17
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
11CilmL JiCilmL Concentration
lE-16 9E-14 1.19E+00
IE-16 3E-14 6.91E-Ol
1E-16 9E-13 4.11E-02
2E-15 6E-13 2.07E+00
L.L.D.+ Effluent Cone.* % Eftluent
11CilmL JiCilmL Concentration
IE-16 9E-14 2.49E+00
lE-16 3E-14 1.71E+00
lE-16 9E-13 1.22E-01
2E-15 6E-13 2.06E+OO
Page 3 of22
EN:RGY
I l\ ~ , ~ I • ._ I • • f .Jit ~
www.energylab.com
~ Elr:tlllwa Slllclll!l
Helena, MT 817-472-0711 • Billings, MT 800-735-4489 • Caspar, WY 888-235-0515
Gillette, WY 118-681-7115 • Rapid City, SD 118-172-1225 • Collage Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Lab ID: c 14070123-001
Client Sample ID: BHV-1
Analyses Result Units
TRACE METALS -IN AIR
Uranium 3.3E-09 mgiL
RADIONUCLIDES • IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 21 0 precision (±) 2.0E-16 uCilmL
Lead 210 MDC 7.0E-17 uCilmL
Radium 226 1.1 E-15 uCilmL
Radium 226 precision (±) 1.3E-17 uCilmL
Radium 226 MDC 1.9E-18 uCilmL
Thorium 230 5.1E-16 uCilmL
Thorium 230 precision (±) 6.0E-17 uCi/mL
Thorium 230 MDC 9.8E-18 uCilmL
Uranium, Activity 2.2E-15 uCilmL
RADIONUCLIDES · IN AIR-PER FILTER
Lead 210
Lead 21 0 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
1680 pCi/Filter
27.3 pCi!Filter
9.5 pCi!Filter
149 pCi/Filter
1.7 pCiiFilter
0.26 pCiiFilter
69.8 pCiiFilter
8.2 pCiiFilter
1.3 pCi/Filter
305 pCiiFilter
135988725 L
MDC -Minimum detectable concentration
Qualifiers
MCL!
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
DateReceived: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 07110114 23:44 1 elm
E909.0 07127114 04:241 eli-cs
E909.0 07127114 04:241 eli-cs
E909.0 07127114 04:241 eli-cs
E903.0 07115114 19:131 dmf
E903.0 07115114 19:131 dmf
E903.0 07115114 19:13 1 dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 I dmf
SW6020 07/1 0/14 23:44 I elm
RADCALC 07129/14 14:261 smm
RADCALC 07/29/14 14:261 smm
RADCALC 07/29/14 14:261 smm
RADCALC 07/29/14 14:261 smm
RADCALC 07/29/14 14:26 1 smm
RADCALC 07129114 14:26 I smm
RADCALC 07/2911414:26/ smm
RADCALC 07/29114 14:26/ smm
RADCALC 07/29114 14:26 / smm
RADCALC 07/29114 14:26/ smm
FIELD 06130/14 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 22
www.energylab.com
Anl/1llal ~ SIIHIIIIIZ
Helena, MT 871·412-0711 • Billings, 11fT 800·735·4481 • Casper, WY 888·235·0515
Gillette, WY 866·686-7175 • Rapid City, SD 888·612·1225 • College Station, TX 888-690·2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29, 2014
PROJECT: 2nd Quarter Air 2014
SAMPLE ID: BHV-2
Quarter/Date Sampled Concentration Radionuclide Air Volume flCilmL
C14040336-002 natu 4.63E-16
First Quarter 2014 23oTh 4.97E-17
Air Volume in mLs 226Ra 1.15E-16
1.36E+I1 2JUPb 1.49E-14
Quarter/Date Sampled Concentration Radionuclide Air Volume flCilmL
c 14070123-002 oatu 3.04E-16
Second Quarter 2014 23oTh 7.92E-17
Air Volume in mLs 226Ra 1.82E-16
1.38E+ 11 210Ph 1.21E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
flCilmL
N/A
1E-17
9E-18
2E-16
Counting
Precision
flCilmL
N/A
1E-17
5E-18
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B-Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-21 0
MDC flCilmL
N/A
6E-18
3E-18
9E-17
MDC flCilmL
N/A
6E-18
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
flCi/mL flCilmL Concentration
1E-16 9E-14 5.15E-01
1E-16 3E-14 1.66E-01
1E-16 9E-13 1.28E-02
2E-15 6E-13 2.48E+00
L.L.D.+ Effluent Cone.* %Effluent
flCilmL flCi/mL Concentration
IE-16 9E-14 3.38E-OI
1E-16 3E-14 2.64E-01
1E-16 9E-13 2.02E-02
2E-15 6E-13 2.01E+00
Page 5 of22
E~RGY
1 1\•.L.!h I '..JHI. ·
www.energyleb.com
Mllytlal br:llllluf ., 11!1
Helena, MT 877-472-0711 • Blllin1s. MT BGD-735-4419 • Caspar, WY 888-235-0515
Gillette, W/888-888-7115 • Rapid City, SD 818-872-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
LabiD: c 14070123-002
Client Sample ID: BHV-2
Analyses Result Units
TRACE METALS -IN AIR
Uranium 4.5E-10 mgiL
RADIONUCLIDES-IN AIR
Lead 210 1.2E-14 uCilmL
Lead 210 precision(±) 2.0E-16 uCilmL
Lead 210 MDC 6.9E-17 uCilmL
Radium 226 1.8E-16 uCilmL
Radium 226 precision (±) 5.1E-18 uCilmL
Radium 226 MDC 1.8E-18 uCilmL
Thorium 230 7.9E-17 uCilmL
Thorium 230 precision (±) 1.4E-17 uCilmL
Thorium 230 MDC 5.7E-18 uCilmL
Uranium, Activity 3.0E-16 uCilmL
RADIONUCLIDES-IN AIR -PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
1660 pCi/Filter
27.1 pCiiFilter
9.5 pCiiFilter
25.0 pCi!Filter
0.70 pCii Filter
0.25 pCiiFilter
10.9 pCiiFilter
1.9 pCiiFilter
0.79 pCiiFilter
41.8 pCiiFilter
137536199 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
DateReceived: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 07110114 23:47 I elm
E909.0 07127114 08:25 I eli-cs
E909.0 07127114 08:25 I eli-cs
E909.0 07127114 08:25 I eli-cs
E903.0 0711511419:13ldmf
E903.0 07115114 19:13 I dmf
E903.0 07115114 19:13 I dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 / dmf
E908.0 07/15/14 09:06 I dmf
SW6020 07110114 23:47 I elm
RADCALC 07129114 14:26 I smm
RADCALC 07129/1414:26/ smm
RADCALC 07129/1414:26/ smm
RADCALC 07/29/14 14:26/ smm
RADCALC 07/29/14 14:26 I smm
RADCALC 07/29114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
FIELD 06130114 00:00 I***
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 6 of22
www.energylab.com
Ataf1tlul&u"-$/Mt fW
Helena, MT 877-412-0711 • Billinas, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 866-686-7175 • Rapid City, SD 888-&72-1225 • Golleae Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29,2014
PROJECT: 2nd Quarter Air 2014
SAMPLE ID: BHV-4
Quarter/Date Sampled Concentration Radionuclide Air Volume ,..cilmL
c 14040336-003 nalu 4.69E-15
First Quarter 2014 23oTh 1.37E-16
Air Volume in mLs 226Ra 3.53E-16
1.35E+ll 210Eb 1.08E-14
Quarter/Date Sampled Concentration Radionuclide Air Volume flCi/mL
C14070123-003 nalu 4.16E-15
Second Quarter 2014 23oTh 6.96E-16
Air Volume in mLs 226Ra 1.77E-15
1.37E+ll 210Ph 1.06E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
flCi/mL
N/A
2E-17
2E-17
2E-16
Counting
Precision
flCi/mL
N/A
8E-17
2E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B-Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC flCi/mL
N/A
IE-17
SE-18
9E-17
MDC flCi/mL
N/A
8E-18
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
,..ci/mL ,..ci/mL Concentration
IE-16 9E-14 5.21E+00
IE-16 3E-14 4.58E-Ol
IE-16 9E-13 3.93E-02
2E-15 6E-13 1.81E+00
L.L.D.+ Effluent Cone.* %Effluent
,..cilmL flCi/mL Concentration
IE-16 9E-14 4.63E+00
IE-16 3E-14 2.32E+00
IE-16 9E-13 1.97E-Ol
2E-15 6E-13 1.77E+00
Page 7 of 22
EN:RGY
I .~ t._ , , 1• \ {_.1~ I ;
www.energytab.com
~Em/i~Mt Sllre.IJ!I
Helena, MT 877-472-0711 • Billings, MT 800·735-4489 • Casper, WY 888-235-0515
Gillette, WY 816-886·7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
LabiD: c 14070123-003
Client Sample ID: BHV-4
Analyses Result Units
TRACE METALS · IN AIR
Uranium 6.2E-09 mgiL
RADIONUCLIDES · IN AIR
Lead 210 1.1 E-14 uCilmL
Lead 210 precision (±) 1.9E-16 uCi/mL
Lead 210 MDC 6.9E-17 uCilmL
Radium 226 1.8E-15 uCilmL
Radium 226 precision (±) 1.6E-17 uCilmL
Radium 226 MDC 1.8E-18 uCilmL
Thorium 230 7.0E-16 uCilmL
Thorium 230 precision (±) 7.5E-17 uCil mL
Thorium 230 MDC 8.5E-18 uCilml
Uranium, Activity 4.2E-15 uCil mL
RADIONUCLIDES · IN AIR-PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
1460 pCiiFilter
25.5 pCiiFilter
9.5 pCiiFilter
244 pCiiFilter
2.1 pCiiFilter
0.25 pCiiFilter
95.7 pCi!Filter
10.3 pCiiFilter
1.2 pCiiFilter
572 pCiiFilter
137449163 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
DateReceived: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 0711 0114 23:50 I elm
E909.0 07127114 09:451 eli-cs
E909.0 07127114 09:451 eli-cs
E909.0 07127114 09:451 eli-cs
E903.0 0711511419:131 dmf
E903.0 07115114 19:13 1 dmf
E903.0 07115114 19:13 1 dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:061 dmf
SW6020 07110114 23:50 I elm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:26 1 smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 07129114 14:26 1 smm
FIELD 06130114 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 8 of22
www.eneJiYiab.com
Allll1b/ ~ Sillt:t I liZ
Helena, r.rr 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 868-686-7115 • Rapid City, SD 888-872-1225 • College Station, TX 888-&90-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29,2014
PROJECT: 2nd Quarter Air 2014
SAMPLE ID: BHV-5
Quarter/Date Sampled Concentration Radionuclide Air Volume J1Ci/mL
C14040336-004 ""'U 4.74E-15
First Quarter 2014 23oTh 1.42E-15
Air Volume in mLs 226Ra 3.48E-15
1.35E+11 210Pb l.SOE-14
Quarter/Date Sampled Concentration Radionuclide Air Volume J1CilmL
C14070123-004 nalu 8.18E-15
Second Quarter 2014 23oTh 1.34E-15
Air Volume in mLs 226Ra 1.76E-15
1.30E+ll 210Pb 1.42E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
J1CilmL
N/A
1E-16
8E-17
2E-16
Counting
Precision
J1CilmL
N/A
2E-16
2E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC J1CilmL
N/A
2E-17
IE-17
9E-17
MDC J1CilmL
N/A
2E-17
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
J1CilmL J1CilmL Concentration
1E-16 9E-14 5.27E+00
1E-16 3E-14 4.73E+00
1E-16 9E-13 3.86E-01
2E-15 6E-13 2.51E+00
L.L.D.+ Effluent Cone.* %Effluent
J1CilmL J1CilmL Concentration
IE-16 9E-14 9.09E+00
1E-16 3E-14 4.47E+00
1E-16 9E-13 1.96E-Ol
2E-15 6E-13 2.37E+OO
Page 9 of22
www.en&fRYiab.com EI\ERGY
L J\ • ~ .._ 1-1 •• I ~I ~It ...... AMI/bl Elr»>iila SJnc. IIU
Helena, MT 877-472-0711 • Billings, MT 800·735·4489 • Casper, WY 888-235-0515
Glllatta, WY 88&-688-7175 • Rapid C~, SD 888-672-1225 • College Station, TX 888-680-2218
LABORATORY ANAL VTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Lab ID: C14070123-004
Client Sample ID: BHV-5
Analyses Result Units
TRACE METALS-IN AIR
Uranium 1.2E-08 mgll
RADIONUCLIDES -IN AIR
Lead 210 1.4E-14 uCilmL
Lead 210 precision (±) 2.1E-16 uCilmL
Lead 210 MDC 6.9E-17 uCilmL
Radium 226 1.8E-15 uCilmL
Radium 226 precision (±) 1.5E-17 uCilmL
Radium 226 MDC 1.7E-18 uCi/mL
Thorium 230 1.3E-15 uCilmL
Thorium 230 precision (±) 1.5E-16 uCilmL
Thorium 230 MDC 2.0E-17 uCilmL
Uranium, Activity 8.2E-15 uCilmL
RADIONUCLIDES-IN AIR -PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
1840 pCiiFilter
27.8 pCiiFilter
9.0 pCiiFilter
229 pCiiFilter
2.0 pCiiFilter
0.23 pCiiFilter
174 pCiiFilter
19.6 pCiiFilter
2.7 pCi!Filter
1060 pCiiFilter
129804469 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
Date Received: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 07110114 23:531 elm
E909.0 07127114 11:061 eli-cs
E909.0 07127114 11 :06 I eli-cs
E909.0 07127114 11 :06 I eli-cs
E903.0 07116114 07:191 dmf
E903.0 07116114 07:191 dmf
E903.0 07116114 07:19 I dmf
E908.0 07115114 09:061 dmf
E908.0 07115114 09:061 dmf
E908.0 07115114 09:061 dmf
SW6020 07110114 23:531 elm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 07129114 14:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:26 I smm
FIELD 06130114 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 22
EI\ERGY
..... j ,,,•,'t••·l'
www.energylab.com
Allll1flal ~Sinn lim
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 86&-686-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-&90-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29, 2014
PROJECT: 2nd Quarter Air 2014
SAMPLE ID: BHV-6
Quarter/Date Sampled Concentration Radionuclide Air Volume ,..cilmL
C14040336-005 ""u 8.92E-15
First Quarter 2014 z3oTh 7.68E-16
Air Volume in mLs 226Ra l.SOE-15
1.35E+ll 210Pb 1.61E-14
Quarter/Date Sampled Concentration Radionuclide Air Volume ,..cilmL
C14070123-005 "''U 8.29E-15
Second Quarter 2014 230Th 5.35E-16
Air Volume in mLs 226Ra 6.72E-16
1.37E+11 zwPb 1.20E-14
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
11ci!mL
N/A
1E-16
4E-17
3E-16
Counting
Precision
,..cilmL
N/A
SE-17
1E-17
2E-16
*Effluent Concentration from the NEW 10 CFR Part 20-Appendix B-Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDC 11CilmL
N/A
2E-17
6E-18
9E-17
MDC 11CilmL
N/A
2E-17
2E-18
7E-17
L.L.D.+ Effluent Cone.* %Effluent
,..cilmL ,..cilmL Concentration
1E-16 9E-14 9.91E+00
1E-16 3E-14 2.56E+00
1E-16 9E-13 1.67E-01
2E-15 6E-13 2.69E+00
L.L.D.+ Effluent Cone.* %Effluent
,..cilmL ,..cilmL Concentration
1E-16 9E-14 9.21E+00
1E-16 3E-14 1.78E+00
1E-16 9E-13 7.47E-02
2E-15 6E-13 2.01E+00
Page 11 of 22
www.energylab.com EI\ERGY
'\ I• j ... )( :n ANJytJrM ElwiiHct Sllcl II!Z
Helena, MT 817·472-0111 • Billings, MT 800·735-4489 • Casper, WY 888-235·0515
Glllatta, WY 88&-686·7115 • Rapid City, SD 888-672·1225 • College Station, TX 888·690·2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
LabiD: c 14070123-005
Client Sample ID: BHV-6
Analyses Result Units
TRACE METALS ·IN AIR
Uranium 1.2E-08 mg/L
RADIONUCLIDES ·IN AIR
Lead 210 1.2E-14 uCilmL
Lead 210 precision (±) 2.0E-16 uCilmL
Lead 210 MDC 6.9E-17 uCilmL
Radium 226 6.7E-16 uCilmL
Radium 226 precision (±) 9.5E-18 uCilmL
Radium 226 MDC 1.8E-18 uCilmL
Thorium 230 5.3E-16 uCilmL
Thorium 230 precision (±) 7.6E-17 uCilmL
Thorium 230 MDC 1.7E-17 uCilmL
Uranium, Activity 8.3E-15 uCilmL
RADIONUCLIDES-IN AIR -PER FIL TEA
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
1650 pCiiFilter
27.1 pCi/Filter
9.5 pCiiFilter
92.4 pCiiFilter
1.3 pCiiFilter
0.25 pCiiFilter
73.5 pCiiFilter
10.4 pCiiFilter
2.4 pCiiFilter
1140 pCiiFilter
137419844 L
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
DateReceived: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 07/1 0114 23:56 I elm
E909.0 07127114 12:261 eli-cs
E909.0 07127114 12:261 eli-cs
E909.0 0712711412:261 eli-cs
E903.0 07116114 07:191 dmf
E903.0 07116114 07:191 dmf
E903.0 07116114 07:191 dmf
E908.0 07115114 09:061 dmf
E908.0 07115114 09:061 dmf
E908.0 07115114 09:061 dmf
SW6020 07110114 23:561 elm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
RADCALC 0712911414:261 smm
FIELD 06130114 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 12 of 22
EI\ERGY
•• " ,-(,.' >~ H -
www.energylab.com
AHI1flal Elallllla Slm:t 1/ISZ
Helena, MT 877-472-0711 • Billings, MT 800-735-4489 • Casper, WY 888-235-0515
Gillette, WY 8&6-&8&· 7175 • Rapid City, SD 888-612-1225 • Collage Station, TX 888-690-2218
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
REPORT DATE: July 29,2014
PROJECT: 2nd Quarter Air 2014
SAMPLE ID: Blank
Quarterffiate Sampled Concentration I Radionuclide Air Volume J.lCilmL
C14040336-006 ""u 1.46E-17
First Quarter 2014 230Th 1.98E-18
Air Volume in mLs 226Ra 2.79E-18
1.36E+ll 2lDPb -1.20E-17
Counting
Precision
J.lCi/mL
N/A
IE-18
2E-18
4E-17
Note: This ~'1lmplc uses 136,000,000 L of air volume for comparison purpo~Cis.
Quarterffiate Sampled Concentration Counting
Radionuclide Precision Air Volume 11CilmL J.lCilmL
C14070123-006 natu 1.90E-17 N/A
Second Quarter 2014 23oTh 6.03E-18 2E-18
Air Volume in mLs 226Ra 5.02E-18 IE-18
1.36E+ll zwPb 6.18E-18 3E-17
Note: This sample uses 136,000,000 L of air volume for comparison purposes.
+LLD's are from NRC Reg. Guide 4.14
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230
Week for Radium-226
Day for Lead-210
MDCJ.1CilmL
N/A
2E-18
2E-18
7E-17
MDCfJCilmL
N/A
2E-18
IE-18
SE-17
L.L.D.+ Effluent Cone.* %Effluent
J.1CilmL J.lCi/mL Concentration
IE-16 9E-14 1.62E-02
IE-16 3E-14 6.60E-03
IE-16 9E-13 3.10E-04
2E-15 6E-13 -2.01E-03
L.L.D.+ Effluent Cone.* %Effluent
J.lCi/mL J.1CilmL Concentration
IE-16 9E-14 2.11E-02
IE-16 3E-14 2.01E-02
IE-16 9E-13 5.58E-04
2E-15 6E-13 1.03E-03
Page 13 of22
EI\ERGY
I '\.LH •i .. l•i( I"IL
www.energylab.com
.,_,~sac. 1151
Helena, MT 877-472-0711 • Billings, MT 800-735·4488 • Caspar, WY 888-235·0515
Gillette, WY Bl&-&86-7175 • Rapid City, SD 888·872-1225 • College Station, 1X 888-690·2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Lab ID: C14070123-006
Client Sample ID: Blank
Analyses
TRACE METALS -IN AIR
Uranium
RADIONUCLIDES · IN AIR
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
RADIONUCLIDES · IN AIR -PER FILTER
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Uranium, Activity
FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.0038 mgiL
8.4E-10 uCilmL
4.0E-09 uCilmL
6.6E-09 uCilmL
6.8E-1 0 uCilmL
1.4E-10 uCilmL
1.7E-1 0 uCilmL
8.2E-10 uCilmL
2.9E-10 uCilmL
2.4E-10 uCilmL
2.6E-09 uCilmL
0.84 pCiiFilter
4.0 pCi/Filter
6.6 pCi/Filter
0.68 pCii Filter
0.14 pCii Filter
0.17 pCiiFilter
0.82 pCiiFilter
0.29 pCiiFilter
0.24 pCiiFilter
2.6 pCiiFilter
1.0 L
MDC -Minimum detectable concentration
Qualifiers
D
u
D
u
U -Not detected at minimum detectable concentration
MCL/
RL CCL
0.000043
2.9E-11
0.20
Report Date: 07/29/14
Collection Date: 06/30/14
Date Received: 07/02/14
Matrix: Filter
Method Analysis Date I By
SW6020 07111114 00:17 I elm
E909.0 07127114 13:46 I eli-cs
E909.0 07127114 13:46 I eli-cs
E909.0 07127114 13:46 I eli-cs
E903.0 07116114 07:19 I dmf
E903.0 07116114 07:19 I dmf
E903.0 07116114 07:19 I dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 I dmf
E908.0 07115114 09:06 I dmf
SW6020 07111114 00:17 I elm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:261 smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 07129114 14:26 I smm
RADCALC 0712911414:26 I smm
FIELD 06130114 00:00 I***
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 14 of22
EN:RGY
t ·, lt.•t··"•l •'i"l' •
www.energylab.com
AM/yfJrll Elf:INIIIct Slllu 11!1
Helena, MT 871·412·0711 • Billings, MT 800·735·4489 • Casper, WY 888·235·0515
Gillette, WY 861·688-71711 • Rapid City, SD 818-672-12211 • College Station,TX 881-690-2218
QAIQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Analyte Count Result Units
Method: E903.0
Lab ID: C14070120-001AMS
Radium 226
LabiD: C14070120·001AMSD
Radium 226
Lab ID: LCS-41872
Radium 226
Lab ID: MB-41872
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab 10: MB-41884
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte reporting limit.
3
3
MDC -Minimum detectable concentration
Sample Matrix Spike
8.33E-07 pCi/L
Sample Matrix Spike Duplicate
9.18E-07 pCi/L
Laboratory Control Sample
21.2 pCi/L
Method Blank
0.2 pCi!L
0.08 pCi!L
0.1 pCi/L
Method Blank
0.05 pCi!L
0.07 pCi/L
0.1 pCi/L
Report Date: 07/29/14
Work Order: C14070123
RL %REC Low Limit High Limit
Run:G5000VV_140709B
90 70 130
Run:G5000VV_140709B
101 70 130
Run:G5000VV_140709B
97 80 120
Run: G5000VV_140709B
Run:G5000VV_140709B
NO -Not detected at the reporting limit.
RPD RPDLimit Qual
9.6
Batch: R188757
07/15/1419:13
07/15/1419:13
13.7
07/15/1419:13
07/15/1419:13
07/16/14 07:19
u
U -Not detected at minimum detectable concentration
Page 15 of 22
EN:RGY
1 lt,,_,j ,•I :_::•IL'•
www.energylab.com
AllllyiJr:M Elwllrlla Slllc. IBU
Helena, MT 877·472·0711 • Billings, MT 800-735-4489 • Casper, WV 888·235-0515
Gillette, WV 866-686-7175 • Rapid City, SO 888-672-1225 • Collage Station, TX 888-690-2218
QAJQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Analyte Count Result Units
Method: E908.0
LabiD: C14070191-003AMS
Thorium 230
Lab ID: C14070191-003AMSD
Thorium 230
Lab ID: LCS-41884
Thorium 230
Lab ID: MB-41884
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Qualifiers:
RL -Analyte reporting limit.
3
MDC - Minimum detectable concentration
Sample Matrix Spike
1 .22E-05 pCi/L
Sample Matrix Spike Duplicate
1.20E-05 pCi/L
Laboratory Control Sample
16.4 pCi/L
Method Blank
0.2 pCi/L
0.1 pCi/L
0.2 pCi!L
Report Date: 07/29/14
Work Order: C14070123
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: ALPHANAL YST_140709B
100 70 130
Run: ALPHANAL YST_140709B
98 70 130 1.7
Run: ALPHANAL YST_140709B
97 80 120
Run: ALPHANAL YST_140709B
ND -Not detected at the reporting limit.
Batch: 41884
07/15/14 09:06
07/15/14 09:06
30.8
07/15/14 09:06
07/15/14 09:06
Page 16 of22
EI\ERGY
I ·,. l 1 •~,. I , )ill l ~-
www.energylab.com
AMiyflal~ .. 11111
Helena, MT 877·472·0711 • Billings, MT 800-735·4489 • Caspar, WY 888·235·0515
Gillette, WY 8&&-68&-7175 • Rapid City, SD 888-672-1225 • College Station, 1X 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Analyte Count Result Units
Method: E909.0
Lab ID: MB-21598
Lead 210
Lead 21 0 precision (±)
Lead 210 MDC
Lab ID: LCS-21598
Lead 210
Lab ID: C14070123-001AMS
Lead 210
Lab ID: C14070123-001AMSD
Lead 210
Qualifiers:
RL-Analyte reporting limit.
3
MDC -Minimum detectable concentration
Method Blank
-1 pCi/L
4 pCi/L
7 pCi/L
Laboratory Control Sample
138 pCi/L
Sample Matrix Spike
1.78E-05 pCi/L
Sample Matrix Spike Duplicate
1.78E-05 pCi/L
Report Date: 07/29/14
Work Order: C14070123
RL %REC Low Limit High Limit
Run: SUB-T58010
Run: SUB-T58010
108 80 120
Run: SUB-T58010
121 70 130
Run: SUB-T5801 0
119 70 130
NO -Not detected at the reporting limit.
RPD RPDLimit Qual
0.0
Batch: T_21598
07/27/14 01 :44
u
07/27/14 03:04
07/27/14 05:45
07/27/14 07:05
15.2
U -Not detected at minimum detectable concentration
Page 17 of22
www.energylab.com
..,.,_,~Sin. IIU
Helena, MT 877-472-0711 • Billings, MT 800-735·4489 • Casper, WV 888-235-0515
Gillette, WV 8&&-&8&-7175 • Rapid City, SD 818-&72-1225 • College Station, TX 888-680-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2014
Report Date: 07/29/14
Work Order: C14070123
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: SW6020 Analytical Run: ICPMS2-C_14071 OA
Lab ID: ICV Initial Calibration Verification Standard 07/10/14 13:24
Uranium 0.0505 mg/L
LabiD: ICSA Interference Check Sample A
Uranium 2.79E-05 mg/L
Lab ID: ICSAB Interference Check Sample AB
Uranium 7.10E-06 mg/L
Method: SW6020
Lab ID: MB-41884 Method Blank
Uranium 6E-05 mg/L
Lab ID: LCS2-41884 Laboratory Control Sample
Uranium 0.105 mg/L
Lab ID: C14070123-005AMS Sample Matrix Spike
Uranium 1.51 E-08 mg/L
Lab ID: C14070123-005AMSD Sample Matrix Spike Duplicate
Uranium 1.55E-08 mg/L
Lab ID: C14070171-001 ADI L Serial Dilution
Uranium 1.06E-10 mg/L
Qualifiers:
RL -Analyte reporting limit.
ND -Not detected at the reporting limit.
0.00030 101 90 110
07/10/14 13:27
0.00030
07/10/14 13:30
0.00030
Batch: 41884
Run: ICPMS2-C_14071 OA 07/10/14 23:34
4E-05
Run: ICPMS2-C_14071 OA 07/10/14 23:38
4.3E-05 105 85 115
Run: ICPMS2-C_140710A 07/10/14 23:59
1.5E-10 75 125 A
Run: ICPMS2-C_14071 OA 07/11/14 00:11
1.5E-10 75 125 2.1 20 A
Run: ICPMS2-C_140710A 07/11/14 00:23
1.5E-10 20
A -The analyte level was greater than four times the spike level. In
accordance with the method % recovery is not calculated.
MDC -Minimum detectable concentration
Page 18 of 22
EN:RGY
• '{I • C1.oo'l '
www.energylab.com
AII/Jfkl/~._,,!1
Helena, MT 877-472-0711 • Billings, MT 808·735-4489 • Casper, WY 888-235-0515
Gillette, WY 866-686-7175 • Rapid City, SD 888-672-1225 • Collage Station, TX 888-&90-2218
Workorder Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Corinne Wagner
Reviewed by: Bl2000\swaldrop
Reviewed Date: 7/3/2014
Shipping container/cooler in good condition?
Custody seals intact on all shipping container(s)/cooler(s)?
Custody seals intact on all 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 Cl, Sulfite, Ferrous Iron, etc.)
Temp Blank received in all shipping container(s)/cooler(s)?
Container/Temp Blank temperature:
Water-VOA vials have zero headspace?
Water-pH acceptable upon receipt?
Yes 0
Yes 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
N/A'C
Yes D
Yes D
C14070123
Date Received: 7/2/2014
Received by: dw
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
Carrier Next Day Air
name:
Not Present D
Not Present D
Not Present 0
Not Applicable 0
NoVOA vials submitted 0
Not Applicable 0
:::::::=====-----·---=======---==--==..-_-·:::::::==--==----_ --======---------==========-=--::.-=--========----------.
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.
Contact and Corrective Action Comments:
None
Page 19 of 22
. " Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: Energy Laboratories Contact: Garrin Palmer -=2::::39~3=-s~a..:::;lt:::;C::;r;.;.e;;.;ek~H:..::wy~------Ph: 435 678 4115
Casper, WY 82601 gpalmer@energy(uels.com
Chain of Custody/Sampling Analysis Request
Project Samplers Name Samplers S~nature
2nd Quarter Air 2014 Garrin Palmer I
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
BHV-1 3/31/14-6/30/14 NA U-NAT, TH-230. Ra-226, Pb-210
BHV-2 3/31/14-6/30/14 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-4 3/31/14-6/30/14 NA U-NAT, TH-230, Ra-226. Pb-210
BHV-5 3/31/14-6/30/14 NA U-NAT, TH-230, Ra-226, Pb-210
BHV-6 3/31/14-6/30/14 NA U-NAT, TH-230, Ra-226, Pb-210
Blank 3/31/14-6730/14 NA U-NAT, TH-230, Ra-226, Pb-210
Comments: Send report to David Turk at PO Box 809 Blanding, UT 84511
Relinquished By:(Signature)
Garrin Pal ~
Datemme Received By:(Signature) Date/Time
7/1/2014
1000
Date/Time Received By:(Signature) DeJ~e
4 -
ATTACHMENTD
AIR PARTICULATE LOADING GRAPHS AND SUPPORTING DATA
0 0 0 !=> .....
0 0 0 ..... 0 0 0 ...... 0 0 0 ..... 0 0 0 ..... 0 0 0 0
1/5/2009
3/5/2009
5/5/2009
7/5/2009
9/5/2009
11/5/2009
1/5/2010
3/5/2010
5/5/2010 . l>
+ -· .,
7/5/2010 . "' !P r+ I 9/5/2010 DJ < I r+ ..... -· 11/5/2010 0
+ ::::s 1/5/2011 "'0 !P DJ I 3/5/2011 < .,
I r+ N -· 5/5/2011 n
+ c
7/5/2011 --DJ !P r+ I 9/5/2011 tD < I
""' r-11/5/2011 0
+ DJ 1/5/2012 a.
!P -· I 3/5/2012 ::::s < OQ I V'l
5/5/2012 -
+ 3 7/5/2012 OQ
!P ......... I 9/5/2012 3 < I IN CTI
11/5/2012 -
1/5/2013
3/5/2013
5/5/2013
7/5/2013
9/5/2013
11/5/2013
1/5/2014
3/5/2014
5/5/2014
0 0 ~ 0 0 ..... ..... 0 0 ..... 0 0 ..... 0 0 0 0 0 0 0
1/5/2009
3/5/2009
5/5/2009 .
7/5/2009 .
9/5/2009
11/5/2009
1/5/2010
3/5/2010
5/5/2010
7/5/2010 . c:J
:I:
9/5/2010 < I
11/5/2010 .....
-g
1/5/2011 QJ ..,
3/5/2011 ~ -· n
5/5/2011 c
t -QJ
7/5/2011 ~ tD OJ I 9/5/2011 < r-
~ 0
11/5/2011 QJ a.. -· 1/5/2012 j
OQ
3/5/2012 -
5/5/2012 3 OQ
7/5/2012 .......
3
9/5/2012 . w -
11/5/2012
1/5/2013
3/5/2013
5/5/2013
7/5/2013 .
9/5/2013 .
11/5/2013
1/5/2014
3/5/2014 .
5/5/2014
!=' !=' !=' ......
0 0 ...... 0 0 ...... 0 0 ...... 0 0 0 0 0 0 0
1/5/2009
3/5/2009
5/5/2009
7/5/2009
9/5/2009
11/5/2009
1/5/2010
3/5/2010
5/5/2010 -
7/5/2010 c:J
::I:
9/5/2010 -< I
11/5/2010 -N
""C
1/5/2011 · OJ
3/5/2011 ~ -· n
5/5/2011 · c:
+
-OJ
7/5/2011 ~ It)
OJ
I 9/5/2011 < r-
I 0 N
11/5/2011 · OJ c. -· 1/5/2012 ::::J
OQ
3/5/2012 -
5/5/2012 3
OQ
7/5/2012 -....... 3
9/5/2012 -w -11/5/2012
1/5/2013
3/5/2013
5/5/2013 -
7/5/2013 -
9/5/2013
11/5/2013 -
1/5/2014
3/5/2014
5/5/2014
0 0 0 !=> 0 0 0
..... ..... 0 0 0 ..... 0 0 0 ..... 0 0 0 ..... 0 0 0 0
1/5/2009
3/5/2009
5/5/2009
7/5/2009
9/5/2009
11/5/2009
1/5/2010
3/5/2010
5/5/2010 ...
7/5/2010 g:,
:I:
9/5/2010 < I
11/5/2010 -~
"'C
1/5/2011 OJ ..,
3/5/2011
,.... -· n
5/5/2011 c
+
~ -OJ
7/5/2011 ~ ,....
t1)
OJ :I: 9/5/2011 < r-
.J:,. 0
11/5/2011 OJ c. -· 1/5/2012 ::::s
OQ
3/5/2012 -
5/5/2012 3
OQ
7/5/2012 .........
3
9/5/2012 -w
~ -
11/5/2012
1/5/2013
3/5/2013
5/5/2013
7/5/2013
9/5/2013 '
11/5/2013
1/5/2014
3/5/2014
5/5/2014
0 0 !=> 0 0
.... .... 0
0 .... 0 0 .... 0 0 0 0 0 0 0
1/5/2009
3/5/2009
5/5/2009
7/5/2009
9/5/2009
11/5/2009
1/5/2010
3/5/2010
5/5/2010
7/5/2010 O:J
::I:
9/5/2010 < I
11/5/2010 . U1
"'C
1/5/2011 Q) ..,
3/5/2011 r1' -· n
5/5/2011 r::::
+
-
7/5/2011 . Q)
r1' tD
OJ I 9/5/2011 < r-
I 0 ln
11/5/2011 · Q) a. -· 1/5/2012 -::::J
CJQ
3/5/2012 -
5/5/2012 3
CJQ
7/5/2012 ......... 3
9/5/2012 w -
11/5/2012
1/5/2013
3/5/2013
5/5/2013
7/5/2013 ~
9/5/2013
11/5/2013
1/5/2014
3/5/2014
5/5/2014 .
0 0 9 1-'
0 0 1-' 0 0 1-' 0 0
1-' 0 0 0
0 0 0 0
1/5/2009
3/5/2009
5/5/2009
7/5/2009
9/5/2009
11/5/2009
1/5/2010
3/5/2010 ..
5/5/2010
7/5/2010 aJ
:I:
9/5/2010 . < I
11/5/2010 . en
""0
1/5/2011 DJ
""'' 3/5/2011 r't' -· n
5/5/2011 s::::
+
-
7/5/2011
DJ
r't'
t1) co :::c 9/5/2011 . < ~
&. 0
11/5/2011 DJ a. -· 1/5/2012 :::l
C1Q
3/5/2012 -
5/5/2012 3
C1Q
7/5/2012 ........ 3
9/5/2012 w -
11/5/2012
1/5/2013
3/5/2013
5/5/2013
7/5/2013
9/5/2013 -
11/5/2013
1/5/2014 •.
3/5/2014
5/5/2014
Period: December 30, 2014 through March 31, 2014 (1st Quarter 2014)
BHV-1 on stream o/o
Week Filter Start
tl Number Pate
l 8398934 30-Dec-t3
2 8398931 06-Jan-14
3 8398926 13-Jan-14
4 8398915 20-Jan-14
5 8398913 27-Jan-14
6 8398908 03-Feb-14
7 8400197 10-Feb-14
8 8400195 17-Feb-14
9 8400185 24-Feb-14
10 8400183 03-Mar-14
II 8400174 10-Mar-14
12 8400171 17-Mar-14
13 8400162 24-Mar-14
Totals 91
BHV-2 on stream %
Week Filter Start
II Numbl!r Dale
1 8398935 30-Dec-13
2 8398930 06-Jan-14
3 8398925 13-Jan-14
4 8398916 20-Jan-14
5 8398912 27-Jan-14
6 8398907 03-Feb-14
7 8400198 10-Feb-14
8 8400194 17-Feb-14
9 8400186 24-Feb-14
10 8400182 03-Mar-14
11 8400175 10-Mar-14
12 8400170 17-Mar-14
13 8400163 24-Mar-14
Totals 91
BHV-4 on stream %
Week Filter Start
# Number Date
1 8398936 30-Dec-13
2 8398929 06-Jan-14
3 8398924 13-Jan-14
4 8398917 20-Jan-14
5 8398911 27-Jan-14
6 8398906 03-Feb-14
7 8400199 10-Feb-14
8 8400193 17-Feb-14
9 8400167 24-Feb-14
10 8400181 03-Mar-14
11 8400176 10-Mar-14
12 8400169 17-Mar-14
13 8400164 24-Mar-14
Totals 91
BHV-5 on stream %
Week Filter Start
0 t # N b :urn er 11.8
1 8398937 30-0ec-13
2 8396926 06-Jan-14
3 8398923 13-Jan-14
4 8398918 20-Jan-14
5 8398910 27-Jan-14
6 8398905 03-Feb-14
7 8400200 10-Feb-14
a 8400192 17-Feb-14
9 8400188 24-Feb-14
10 8400180 03-Mar-14
11 8400177 10-Mar-14
12 8400168 17-Mar-14
13 8400165 24-Mar-14
Totals 91
100.0%
Stop
Date
6-Jan-14
13-Jan-14
20-Jan-14
27-Jan-14
3-Feb-14
10-Feb-14
17-Feb-t4
24-Feb-14
3-Mar-14
10-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2184.0
100.0%
Stop
!:>ale
06-Jari-14
13-Jan-14
20-Jan-14
27-Jan-14
03-Feb-14
10-Feb-14
17-Feb-14
24-Feb-14
03-Mar-14
10-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2184.0
99.2%
Stop
l:l_ate_
06-Jan-14
13-Jan-14
20-Jan-14
27-Jan-14
03-Feb-14
10-Feb-14
17-Feb-14
24-Feb-14
03-Mar-14
10-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2184.0
99.2%
Stop
D I a a
06-Jan-14
13-Jan-14
20-Jan-14
27-Jan-14
03-Feb-14
10-Feb-14
17-Feb-14
24-Feb-14
03-Mar-14
1D-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2184.0
Gross Tare
4.3800 4.2984
4.4401 4.3256
4.4066 4.3245
4.4512 4.3263
4.4228 4.3208
4.3824 4.3206
4.4290 4.3376
4.4799 4.3329
4.4103 4.3091
4.4300 4.3473
4.5076 4.2810
4.5842 4.2655
5.7970 4.3069
4.547777 4.315115
Gross Tare
4.5'16'2 4.3505
4.5136 4.3039
4.5243 4.3209
4.6978 4.3268
4.5747 4.3372
4.3564 4.2699
4.4820 4.3175
4.5704 4.3233
4.4709 4.3266
4.4507 4.3294
4.5353 4.2767
4.6345 4.3048
5.0604 4.3138
4.568246 4.31548
Gress Tare
4.4091 4.3691
4.4670 4.3356
4.3786 4.3071
4.3474 4.2688
4.3973 4.2886
4.4070 4.3416
4.4187 4.3478
4.4759 4.3539
4.4052 4.3112
4.3661 4.2742
4.4616 4.3242
4.4627 4.3161
4.5536 4.2763
4.426938 4.3165
G rGSS T aro
4.3713 4.3000
4.4677 4.3326
4.4095 4.3131
4.4233 4.3122
4.4146 4.3053
4.4102 4.3462
4.4522 4.3381
4.4739 4.3328
4.4296 4.3329
4.4220 4.3368
4.5670 4.3213
4.5933 4.2636
4.8406 4.2750
4.482708 4.31615
Net
0.0816
0.1145
0.0821
0.1249
0.1020
0.0618
0.0914
0.1470
0.1012
0.0827
0.2266
0.3187
1.4901
0.2327
Net
0.1657
0.2097
0.2034
0.3710
0.2375
0.0865
0.1645
0.2471
0.1443
0.1213
0.2586
0.3297
0.7466
0.2528
Net
0.0400
0.1314
0,0715
0.0786
0.1087
0.0654
O.D709
0.1220
0.0940
0.0919
0.1374
0.1466
0.2773
0.1104
N t e
0.0713
0.1351
0.0964
0.1111
0.1093
0.0640
0.1141
0.1411
0.0967
0.0852
0.2457
0.3297
0.5656
0.1666
Stop
Time
52612.7
52779.7
52946.3
53117.2
53286.2
53450.6
53619.3
53791.6
53953.8
54121.9
54293.4
54458.2
54627.9
Stop
Time
62879:3
63046_0
63213.8
63382.9
63552.9
63717.2
63885.6
64057.6
64219.7
64388.2
64559.4
64727.5
64893.9
Stop
Time
38114.1
38279.3
38445.8
36618.4
38784.1
38950.2
39118.8
39290.9
39453.8
39622.6
39792.8
39945.1
40116.1
Stop
li InN!
61920.7
62085.9
62252.4
62425.0
62591.0
62756.7
62925.7
63097.9
63260.9
63429.2
63599.6
63752.0
63922.7
BHV-1
Start
Time
52444.1
52612.7
52779.7
52946.3
53117.2
53286.2
53450.6
53619.3
53791.6
53953.8
54121.9
54293.4
54458.2
BHV-2
Start
Time
62710.0
62879.3
63046.0
63213.8
63382.9
63552.9
63717.2
63885.6
64057.6
64219.7
64388.2
64559.4
64727.5
BHV-4
Start
Ttme
37950.7
38114.1
38279.3
38445.6
36616.4
38784.1
38950.2
39118.8
39290.9
39453.8
39622.6
39792.8
39945.1
BHV-5
Start
li 1me
61757.2
61920.7
62085.9
62252.4
62425.0
62591.0
62756.7
62925.7
63097.9
63260.9
63429.2
63599.6
63752.0
Total
Time
10113.6
10023.0
9995.4
10255.2
10138.8
9862.2
10125.0
10336.8
9729.0
10089.6
10287.6
9886.8
10183.8
131026.8
Total
Time
10154.4
10002.0
10073.4
10144.8
10196.4
9859.8
10104.0
10319.4
9729.6
10110.0
10269.6
10085.4
9987.0
131035.8
Total
T IO'lB
9806.4
9911.4
9991.2
10355.4
9939.6
9968.4
10115.4
10329.0
9774.0
10126.2
10210.2
9140.4
10260.0
129927.6
Total n lffiB
9808.2
9912.0
9991.8
10354.2
9960.6
9946.2
10138.2
10329.0
9782.4
10096.8
10227.6
9144.0
10237.8
129928.8
Total Volume: 4.82E+06
Total Loading, Per Cent
Liters mgfm3 0 n Slream
10,453,062 0.0078 100.3%
10,501,331 0.0109 99.4%
10,472,414 0.0078 99.2%
10,744,612 0.0116 101.7%
10,622,657 0.0096 100.6%
10,332,857 0.0060 97.8%
10,579,528 0.0086 100,4%
10,800,836 0.0136 102.5%
10,165,751 0.0100 96.5%
10,456,827 0.0079 100.1%
10,603,771 0.0214 102.1%
10,190,653 0.0313 98.1%
10.496,781 0.1420 101.0%
136,421,082 0.0222 100.0%
Total Volume: 4.82E+06
Total Loading, Per Cent
Liters I mglm3 On Stream
10,495,232 0.0158 100_7%
10,479,329 0.0200 99.2%
10,554.136 0.0193 99.9%
10,628,944 0.0349 100.6%
10,683,006 0.0222 101.2%
10,330,343 0.0084 97.8%
10,557,585 0.0156 100.2%
10,782,655 0.0229 102.4%
10,166,378 0.0142 96.5%
10,477,970 0.0116 100.3%
10,585,218 0.0244 101.9%
10,395,357 0.0317 100.1%
10,293,933 0.0725 99.1%
136.430 085 0.0241 100.0%
Total Volume: 4.78E+06
Total Loading. Per Cent
Uters roolm3 On Stream
10,135,551 0.0039 97.3%
10,384,405 0.0127 96.3%
10.468,013 0.0068 99.1%
10,849,594 0.0072 102.7%
10.413,951 0.0104 98.6%
10,444,125 0.0063 98.9%
10,569,497 0.0067 100.4%
10,792,686 0.0113 102.5%
10,212,771 0.0092 97.0%
10,494,759 0.0088 100.5%
10,523,992 0.0131 101.3%
9,421,314 0.0156 90.7%
10,575,323 0.0262 101.8%
135,285,-983 0.0106 99.2%
Total Volume: 4.78E+06
Total
L't 1 ets
10,137A11
10,385,034
10,468,642
10,848,337
10,435,953
10,420,866
10,593,321
10,792,686
10,221,548
10.464.289
10,541,927
9.425,025
10.552,441
135,287,479
Loading, Per Cent
I 3 0 S!r mg,m n earn
0.0070 97.3%
0.0130 98.3%
0.0092 99.1%
0.0102 102.7%
0.0105 98.8%
0.0061 98.7%
0.0108 100.6%
0.0131 102.5%
0.0095 97.0%
0.0081 100.2%
0.0233 101.5%
0.0350 90.7%
0.0536 101.6%
0.0161 99.2%
Page 1
SCF M
36.5
37.0
37.0
37.0
37.0
37.0
36.9
36.9
36.9
36.6
36.4
36.4
36.4
36.8
SO -M
36.5
37.0
37.0
37.0
37.0
37.0
36.9
36.9
36.9
36.6
36.4
36.4
36.4
36.8
SCFM
36.5
37.0
37.0
37.0
37.0
37.0
36.9
36.9
36.9
36.6
36.4
36.4
36.4
36.8
SCFM
36.5
37.0
37.0
37.0
37.0
37.0
36,9
36.9
36.9
36.6
36.4
36.4
36.4
36.8
Period: December 30, 2014 through March 31, 2014 (1st Quarter 2014)
BHV-6 on stream %
Week Filter Start
IJ. Number Date
1 8398938 30-Dec-13
2 8398927 06-Jan-14
3 8398922 13-Jan-14
4 8398919 20-Jan-14
5 8398908 27-Jan-14
6 8398904 03-Feb-14
7 8398901 10-Feb-14
8 8400191 17-Feb-14
9 8400189 24-Feb-14
10 8400179 03-Mar-14
11 8400178 10-Mar-14
12 8400167 17-Mar-14
13 8400166 24-Mar-14
Totals 91
ALL BHV on stream o/o
Week
# BlBnkS
Start
Date
1 8398932 30-Dec-13
2 8398921 06-Jan-14
3 8398920 13-Jan-14
4 8398914 20-Jan-14
5 8398903 27-Jan-14
6 8398902 03-Feb-14
7 8400196 10-Feb-14
8 8400190 17-Feb-14
9 8400184 24-Feb-14
10 8400173 03-Mar-14
11 8400172 10-Mar-14
12 8400161 17-Mar-14
13 8400160 24-Mar-14
Totals 91
99.1%
Stop
Date
06-Jan-14
13-Jan-14
20-Jan-14
27-Jan-14
03-Feb-14
10-Feb-14
17-Feb-14
24-Feb-14
03-Mar-14
10-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2f84.0'
99.5%
Stop
Dale
06-Jan-14
13-Jan-14
20-Jan-14
27-Jan-14
03-Feb-14
10-Feb-14
17-Feb-14
24-Feb-14
03-Mar-14
10-Mar-14
17-Mar-14
24-Mar-14
31-Mar-14
2184.0
Gross
4.43"94
4.4810
4.4235
4.4576
4.4825
4.3672
4.4581
4.4266
4.4495
4.4052
4.5073
4.5210
4.6986
4.470577
Net
4.3495
4.3245
4.2957
4.2864
4.3409
4.3619
4.3532
4.3618
4.3147
4.3199
4.3180
4.2386
4.3099
4.3212
BHV-6
Stop Start
Tare Net 11me Thne
4.3331 0.1063 10316.0 10152.6
4.2748 0.2062 10481.2 10316.0
4.3271 0.0964 10647.7 10481.2
4.3269 0.1307 10820.3 10647.7
4.3352 0.1473 10986.0 10820.3
4.3198 0.0474 11151.7 10986.0
4.3317 0.1264 11320.7 11151.7
4.2843 0.1423 11492.9 11320.7
4.3580 0.0915 11655.8 11492.9
4.3430 0.0622 11824.5 11655.8
4.2933 0.2140 11994.4 11824.5
4.2938 0.2272 12147.1 11994.4
4.3105 0.3881 12318.1 12147.1
4.31781 0.1528
Page2
Total Volume: 4. 78E+06
Total Total Loading, Per Cent
Time Uters ma/m3 On Stream SCFM
9802.8 10,131,830 0.0105 97.3% 36.5
9910.2 10,383,148 0.0199 98.3% 37.0
9991.2 10,468,013 0.0092 99.1% 37.0
10354.2 10,848,337 0.0120 102.7% 37.0
9941.4 10,415,837 0.0141 98.6% 37.0
9945.6 10,420,237 0.0045 98.7% 37.0
10138.8 10,593,948 0.0119 100.6% 36.9
10329.0 10,792,686 0.0132 102.5% 36.9
9778.2 10,217,160 0.0090 97.0% 36.9
10122.0 10,490,406 0.0059 100,4% 36.6
10194.0 10,507.295 0.0204 101.1% 36.4
9157.2 9,438,630 0.0241 90.8% 36.4
10260.6 10,575,941 0.0367 101.8% 36.4
129925.2 135.283.468 0.0147 99.1% 36.8
'Period: March 31, 2014 through, July 2, 2014 (2nd Quarter 2014) Page 1
#
I
2
3
4
s
6
7
8
9
10
II
12
13
Week
#
1
2
3
4
5
6
7
8
9
10
11
12
13
Week
11:
1
2
3
4
5
6
7
8
9
10
11
12
13
Week
It
1
2
3
4
5
6
7
8
9
10
11
12
13
BHV-1 on stream%
Number Date
8400159 31-Mar-14
8400150 07-Apr-14
8400147 14-Apr-14
8400141 21-Apr-14
8400132 28-Apr-14
8400128 05-May-14
8400120 12-May-14
8400117 19-May-14
8400111 26-May-14
8400102 02-Jun-14
8951299 09-Jun-14
8951290 16-Jun-14
8951286 23-Jun-14
Totals 91
BHV-2 on stream %
Filter Start
Number Date
8400158 31-Mar-1 4
8400151 07-Apr-14
8400146 14-Apr-14
8400140 21-Apr-14
8400133 28-Apr-14
8400129 05-May-14
8400121 12-May-14
8400116 19-May-14
8400110 26-May-14
8400103 02-Jun-14
8951298 09-Jun-14
8951291 16-Jun-14
8951285 23-Jun-14
Totals 91
BHV-4 on stream%
Filter Start
Numbcer Date
8400f57 31-Mar-14
8400152 07-Apr-14
8400145 14-Apr-14
8400139 21-Apr-14
8400134 28-Apr-14
8400127 05-May-14
8400122 12-May-14
8400115 19-May-14
8400109 26-May-14
8400104 02-Jun-14
8951297 09-Jun-14
8951292 16-Jun-14
8951284 23-Jun-14
T otals 91
BHV-5 on stream %
Filter Start
Numbor Date
8400156 31-Mar-14
8400153 07-Apr-14
8400144 14-Apr-14
8400138 21-Apr-14
8400135 28-Apr-14
8400126 05-May-14
8400123 12-May-14
8400114 19-May-14
8400108 26-May-14
8400105 02-Jun-14
8951296 09-Jun-14
8951293 16-Jun-14
8951283 23-Jun-14
Totals 91
98.8%
Oate Gro'ss Tare Net
7-Apr-14 4.8063 4.2971 0.5092
14-Apr-14 4.6346 4.3412 0.2934
21-Apr-14 4.8566 4.3218 0.5348
28-Apr-14 4.7298 4.1975 0.5323
S-May-14 4.7308 4.2644 0.4664
12-May-14 4.5391 4.2729 0.2662
19-May-14 4.5319 4.2590 0.2729
26-May-14 4,6629 4,2162 0.4467
2-Jun-14 4.4344 4.1909 0.2435
9-Jun-14 4.4623 4.2810 0,1813
16-Jun-14 4.9799 4.5222 0.4577
23-Jun-14 5.1655 4.5152 0.6503
30-Jun-14 4.7708 4.5006 0.2702
2184.0 4.715762 4.321538 0.3942
99.9%
Stop
Date Gross Tare Net
07-Apr-14 4.5918 4.2783 0.3135
14-Apr-14 4.6736 4.2849 0.3887
21-Apr-14 4.7082 4.3398 0.3684
28-Apr-14 4.8015 4.3331 0.4684
05-May-14 4.5305 4.2645 0.2660
12-May-14 4.7203 4.2497 0.4706
19-May-14 4.4577 4.1937 0,2640
26-May-14 4.7318 4.2443 0.4875
02-Jun-14 4.5476 4.2523 0.2953
09-Jun-14 4.5685 4.2733 0.2952
16-Jun-14 4.9192 4.5293 0.3899
23-Jun-14 5.2519 4.5034 0.7485
30-Jun-14 4.7890 4.4948 0.2942
2184.0 4.71473'8 4.32626 0.3885
99.8%
Stop
Date Gross Tare Net
07-Apr-14 4.5233 4.3132 0.2101
14-Apr-14 4.4959 4.3393 0.1566
21-Apr-14 4.4564 4.3082 0.1482
28-Apr-14 4.6815 4.3499 0.3316
05-May-14 4.4871 4.2187 0.2684
12-May-14 4.4879 4.2615 0.2264
19-May-14 4.4076 4.2468 0.1608
26-May-14 4.4733 4.2211 0.2522
02-Jun-14 4.3529 4.2575 0.0954
09-Jun-14 4.2784 4.2379 0.0405
16-Jun-14 4.6324 4.5053 0.1271
23-Jun-14 4.9105 4.4993 0.4112
30-Jun-14 4.6131 4.4796 0.1335
2184.0 4.5231 4.32602 0.1971
94.3%
Stop
Date GraS$ Tare Nee
07-Apr-14 4.5511 4.3099 0.2412
14-Apr-14 4.5757 4.3419 0.2338
21-Apr-14 4.4912 4.3236 0.1676
28-Apr-14 4.7322 4.3297 0.4025
05-May-14 4.6506 4.2623 0.3883
12-May-14 4.7119 4.2860 0.4259
19-May-14 4.4569 4.2558 0.2011
26-May-14 4.5856 4.2085 0.3771
02-Jun-14 4.4269 4.2320 0.1969
09-Jun-14 4.5284 4.2599 0.2685
16-Jun-14 4.8025 4.5117 0.2908
23-Jun-14 5.0595 4.4744 0.5851
30-Jun-14 4.7259 4.5147 0.2112
2184.0 4.-6-38492 4.33157 0.3009
BHV-1 Total Volume: 4.80E+06
Loading Percent
Stop Time Start Time Total Time Total Liters mg/m3 On Stream SCFM
54795.5
54961.7
55130,8
55297.0
55467.1
55609.4
55777.7
55969.6
56115.1
56280.9
56448.8
56641.4
56784.9
Stop
Time
65061 .7
65228.1
65397.1
65564.4
65733.1
65899.6
66068.2
66260.2
66405.4
66571.4
66739.4
66932.0
67075.4
Stop
Tlme
40283.2
40448.5
40616.8
40784.0
40952.7
41119.5
41287.9
41480.0
41623.7
41790.7
41958.5
42151.3
42296.3
Stop
Time
64090.2
64255.4
64423.8
64591.0
64759.8
64926.4
65094.8
65286.5
65309.6
65476.5
65644.0
65836.8
65981.8
54627.9
54795.5
54961.7
55130.8
55297.0
55467.1
55609.4
55777.7
55969.6
56115.1
56280.9
56448.8
56641.4
BHV-2
Start ,., m&
64893.9
65061.7
65228.1
65397.1
65564.4
65733.1
65899.6
66068.2
66260.2
66405.4
66571.4
66739.4
66932.0
BHV-4
Start
Tlrne
40116.1
40283.2
40448.5
40616.8
40784.0
40952.7
41119.5
41287.9
41480.0
41623.7
41790.7
41958.5
42151.3
BHV-5
Start
Tlmll
63922.7
64090.2
64255.4
64423.8
64591.0
64759.8
64926.4
65094.8
65286.5
65309.6
65476.5
65644.0
65836.8
10054.8
9972.0
10144.8
9972.0
10206.0
8537.4
10096.2
11518.8
8727.6
9945.6
10076,4
11557.8
8607.0
129416.4
Total
Time
10065.6
9981.0
10142.4
10036.2
10121.4
9995.4
10113.6
11519.4
8711.4
9961.2
10077.6
11556.6
8605.2
130887
Total
Tlme
10025.4
9920.4
10097.4
10032.6
10121.4
10005.6
10103.4
11525.4
8622.6
10018.2
10072.2
11567.4
8698.2
130810.2
Total
TlfTIB
10050.6
9912.0
10102.2
10033.8
10128.6
999'7.8
10105.2
11502.0
1386.0
10012.8
10050.0
11567.4
8697.6
123546
10,738,617 0.0474 99.8%
10,650,186 0.0275 98.9%
10,834,738 0.0494 100.6%
10,650,186 0.0500 98.9%
10,900,100 0.0428 101.2%
8,985,958 0.0296 84.7%
10,626,658 0.0257 100.2%
12,124,002 0.0368 114.3%
9,186,151 0.0265 86.6%
10,219,152 0.0177 98.7%
10,353,550 0.0442 100.0%
11,875,695 0.0548 114.7%
8,843.734 0.0306 85.4%
135,988,725 0.0372 98.8%
Total Volume: 4.86E+06
Total Loading, Per Cent
!-.item 1TIIl(m3 On Stream
10,750,151 0.0292 99.9%
10,659,798 0.0365 99.0%
10,832,174 0.0340 100.6%
10,718,752 0.0437 99.6%
10,809,746 0.0246 100.4%
10.520,562 0.0447 99.2%
10,644,972 0.0248 100.3%
12,124,633 0.0402 114.3%
9,169,100 0.0322 86.4%
10,235,181 0.0288 98.8%
10,354,783 0.0377 100.0%
11,874,462 0.0630 114.6%
8,841,885 0.0333 85.4%
137,536,199 0.0364 99.9%
Total Volume: 4.85E+06
Total
t Uens
10,707,217
10,595,076
10,784,114
10,714,907
10,809,746
10,531,298
10,634,236
12,130,949
9,075,634
10,293,749
10,349,234
loading, Per Cent
mt~frn3 On Stream
0.0196 99.5%
0.0148 98.4%
0.0137 100.2%
0.0309 99.5%
0.0248 100.4%
0.0215 99.3%
0.0151 100.2%
0.0208 114.3%
O.D105 85.5%
0.0039 99.4%
0.0123 99.9%
37.7 ill ----
. ____E;!__-
37.7
-37.7 ·-
•• 37.2 --
37.2 , ____
37.2
37.2
36.3
36.3
36.3
36.3
37.1
SCFM
r---m---37.7 ~-m-
~3'7:i'"" .
37:7-'37.2-
• 37.2 -
37.2 -372
"36.3
36.3
-36.3 --=
36.3
37.1
SCFM
37.7
37.7 --
37.7 ~~~ 37.7 ·-----37.2 ,_
37.2 .
-J 7.2 .
.... B2o.. ... 36.3 ·---36.3
11,885,559 0.0346 114.8% I' 36.3
8,937,443 0.0149 86.3% 36.3
137,449,163 0.0183 99.8% I 37.1
Total Volume: 4.58E+06
Total loading, Per Cent
Uters rna/m3 On Stream SCFM
10,734,131 0.0225 99.7% 1-..I!..:2._ -10,586,105 0.0221 98.3% 37.7
10,789,240 0.0155 100.2% 37.7
10,716,189 0.0376 99.5% "31:1-
10,817,436 0.0359 100.5% .. _"37J • ..
10,523.088 0.0405 99.2% 37.2 •• J 7.2 -10,636,131 0.0189 100.2% ·----12,106,319 0.0311 114.1% 37.2
1,458,821 0.1350 13.7% ---n2--
10,288,200 0.0261 99.3% 363
10,326,424 0.0282 99.7% -36.3 -•
11,885,559 0.0492 114.8% ~. 36.~-
8'.93b,826 0.0236 86.3% 36.3
129,804,469 0.0374 94.3% 37.1
Period: March 31,2014 through, July 2, 2014 (2nd Quarter 2014)
BHV-6 on stream%
Week Filter Start
# Number Dale
1 8400155 31-Mar-14
2 6400154 07-Apr-14
3 8400143 14-Apr-14
4 8400137 21 -Apr-14
5 8400136 28-Apr-14
6 6400125 05-May-14
7 6400124 12-May-14
8 8400113 19-May-14
9 6400107 26-May-14
10 8400106 02-Jun-14
11 8951295 09-Jun-14
12 8951288 16-Jun-14
13 8951282 23-Jun-14
Totals 91
ALL BHV on stream %
Week
# Blanks
Start
Date
1 8400149 31-Mar-14
2 8400148 07-Apr-14
3 8400142 14-Apr·14
4 8400131 21-Apr-14
5 8400130 28-Apr-14
6 8400119 05-May-14
7 8400118 12-May-14
8 8400112 19·May-14
9 8400101 26-May-14
10 8951300 02-Jun-14
11 8951289 09-Jun-14
12 8951287 16-Jun-14
13 8.951276 2.3-Jun-14
Totals 91
99.6%
Stop
Date
07-Apr-14
14-Apr-14
21-Apr-14
28-Apr-14
05-May-14
12-May-14
19-May-14
26-May-14
02-Jun-14
09-Jun-14
16-Jun-14
23-Jun-14
3Q-Jun-14
2184.0
98.5%
Stop
Date
07-Apr·14
14-Apr-14
21·Apr-14
28-Apr-14
05-May-14
12-May-14
19-May-14
26--May-14
02-Jun-14
09-Jun-14
16-Jun-14
23-Jun-14
~O-Jun·14
2184.0
Gross
4.5391
4.4706
4.5014
4.5892
4.5218
4.5757
4.3876
4.5858
4.4341
4.4956
4.8099
4.9500
4.6910
4.580923
Net
4.3292
4.3029
4.3273
4.2278
4.2608
4.2455
4.1979
4.2549
4.2409
4.5127
4.5030
4.4919
4.5445
4.3415.
Stop
Tare Net Tlme
4.2920 0.2471 12485.2
4.2914 0.1792 12652.2
4.3430 0.1564 164.1
4.2897 0.2995 331 .3
4.2683 0.2535 500.0
4.2441 0.3316 666.7
4.2126 0.1752 835.2
4.2617 0.3241 1027.2
4.2544 0.1797 1171.1
4.2648 0.2308 1336.0
4.5055 0.3044 1505.8
4.5046 0.4454 1698.4
4.5023 0.1887 1845.7
4.32572 0.2552
Page2
BHV-6 Total Volume: 4.85E+06
Start Total Total Loading, Per Cent
Tlma nme Liters mg/m3 On Stream SCFM
12318.1 10026.6 10,708.499 0.0231 99.5% ~-12465.2 10020.0 10,701,450 0.0167 99.4% 37.7
0.0 9844.8 10,514,335 0.0151 97.7% --3.,-:;----·-----164.1 10032.6 10,714,907 0.0280 99.5% 37.7
331.3 10124.4 10,812,950 0.0234 100.4% "'3-[i "''
500.0 10002.0 10,527,509 0.0315 99.2% "37.2 "
666.7 10!05.8 10.636,762 0.0165 100.3% -37.2·-
835.2 11524.2 12,129,665 0.0267 114.3% 37.2 -
1027.2 8630.4 9,083,844 0.0196 65.6% 37.2
1171.1 10014.0 10,289,433 0.0224 99.3% 36.3
1338.0 10071.0 10,348.001 0.0294 99.9% ")"6.3 -
1505.8 11557.2 11,875,079 0.0375 114.7% 36.3
1698.4 8834.4 9,077.389 0.0208 87.6% 36.3
130787.4 137,419,844 0.0239 99.8% 37.1
ATTACHMENT E
ENVIRONMENTAL GAMMA GRAPHS AND SUPPORTING DATA
I White Mesa Mill Ambient Gamma Levels Over Time BHV-=11
50.00 --------------------------------------------------------------------------------------------------------------------~
45.00 ~1--------------------------------------------------------------------------------------------------------------~
40.00 ~----------------------------------------------------------------------------------------------------------l
35.00 I
30.00
..... Q)
t ca 25.00
:::::1 o-........ E
Q) a: 20.00
E
15.00
10.00 II I
5.00 1 • I • II • ~
0.00 ~~~ , .. ~ -I '
9130it9st 91aol19sa 91aol19ss 9130it9B? 9130it9B9 9130it99t 91aolt993 91aolt99s 9130it99? 9130it999 913ol2oot 91aol2oo3 9130I2oos 91aol2oo? 913ol2oo9 9130I2ott 91aol2ot3
Background (BHV-3) Subtracted from BHV-1
I ......-.series1 I
I White Mesa Mill Ambient Gamma Levels Over Time BHV-21
50.00~----------------------------------------------~-------------------------------------------------------,
45.00 +-------------------------------------------------------------------------------------------------------~
40.00 +-------------------------------------------------------------------------------------------------------~
35.00 +-------------------------------------------------------------------------------------------------------~
30.00 ,_
CD t
ctS
::::l 0" 25.00 -E
CD 0:
E 20.00
15.00 +--------------------------------------------------------------------------------------------------------1
10.00 +---------------~~----------------------------------------------------------------------------------------~
5.00 i R H II W -
o.oo i'At,¥~··~=-t •••··•·--~·~~VSbt-ti· --.. :rtar -....... ~.-~·V:JAIStllt ·~··*Wi .-.se .ww:.:,.-.
30-sep.81 30-sep.e9
30-sep.97 3o.seP-Os 3o.sep.13
Background (BHV-3) Subtracted from BHV-2
I --+--BHV-2 -1
.....
Q) t
<U ::::J
-!2"" E Q) a:
E
I White Mesa Mill Ambient Gamma Levels OverTime BHV-3]
50.00 ~------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------------~
45.00 +-------------------------------------------------------------------------------------------------~~----------------------------1
40.00 -ll------------tll---------------------------------1
~ 35.00r-----------------------------------~--------------------------------------------1t--------------~~--~lrj~l-~~------------__j
~u.~ t-------------------~~-----~,_-----~~-----
4 ~
25.00i~l~11~~;-~~-:t\~rt-1'~~~Jtj~~fJ~i:~~1\~~~--il~~--~--~~~~-~~~~~~~JJ ·rit-----~U I
2o.oo ~--------~r1~~~---Wf4~~~~--------------------~~---U-ll~~ ~~1-------------------~----~--------1
15.00 -j ~----IL_----1
4
10.00~!--------------------------------------------------------------------------------------------------------------------~
5.00 i I
o.ooL---------------r---------------------~----------------------------------------~--------------~------------------------------~
3a..seP-Bt 3n ~ 3n ~ 3o.8 3o ... ~eP-83 ~eP-85 eP-87 vep.89 30-sep.g1 3o.sep.93 ao.8 3a..s 3o.s 3o.8 ep.gs ep.g7 ep.gg ep.ot 3o.sep.o3 3o-s 3o_.. 3o.8 3o-s ep.os vep.07 ep.og ep.11 30-sep.13
--BHV-3
I White Mesa Mill Ambient Gamma Levels Over Time BHV-4 1
50.00,-----------------------------------------------------------------------------------------------------------------------------,
45.00 1-----------------------------------------------------------------------------------------------------------------------------------,
40.00 +---------------------------------------------------------------------------------------------------------------------------~
35~o 1
30.00
..... Q) t: 25.00 ctl
:::::l
-!2"" E Q)
0: 20.00
E
15.00
10.00
5.oo -1--.-\-....a-\-l"f W _ H _ I
o.oo ..,_ " -, M
~s ~s ~s ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ eP-87 ep.83 ep-as "SP-87 ep.ag ep.g1 ep.g3 ep.gs ep.g7 ep.gg eP·Ot ep.03 ep.os ep.07 ep.Og ep.11 ep.13
Background (BHV-3) Subtracted from BHV-4
--BHV-4
I White Mesa Mill Ambient Gamma Levels Over Time BHv:s]
50.00~--------------------------------------------------------------------------------------------------~
45.00 +-----------------------------------------------------------------------------------------------------4
40.00 +-----------------------------------------------------------------------------------------------------~
35.oo L ----------------------------------------l
30.00 ......
Q)
t::: as
:::J
0" 25.00 -E
Q) a:
E 20.00
15.00 +---------------------------------------------------------------------------------------------------------~
10.00l_---------------------------------------------------------1t----.--~=---------------------~--------l
5.oo ~ I I 1e a. t•a n..-..,.. Ian. I I a -.a I I :l I I .L I I W I -lf-1-+\---------:e-J.d
o.oo •• -, .._ 1 ~•• , e e ·• • e • · 1 •.., -1
30-Sep-81 30-seP-84 30-SeP-87 30-Sep.90 30-sep.g3 30-Sep.96 3o..sep.g9 3o..sep.o2 30-Sep-o5 3o..seP-oa 30-seP-1t
Background (BHV-3) Subtracted from BHV-5
'I ~BHV-5 I
I White Mesa Mill Ambient Gamma Levels Over Time BHv:s l
50.00
45.00
40.00
35.00
30.00
.....
Q) t ro 25.00 -:::s 0" --E Q) a: 20.00
E
15.00 --
10.00
5.00
0.00
...
~ _.r-.. .~ ~~ -----~-~ft ~ft -s ~ft -s -s ~ft -s ~ft -s -s -s -s -s ~ft -s ~eP-81 """'eP-83 """'eP-85 eP-8-, --..eP-89 ep_91 ep.93 """'ep.95 ep.97 """'ep_99 eP-01 ep-o3 eP-05 eP-0-, eP-og """'ep.11 ep.13
Background (BHV-3) Subtracted from BHV-6
I -~ I
Badge
Number
Control
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
45
46
47
51
52
53
64
White Mesa Mill First Quarter 2014 Environmental Spherical Gamma Monitor Results
Location
Administration Vault
V205 Control Room
BHV-6
Ore Star. -Barrel Area
Vanadium Precip.Area
Yellowcake Drying Area
Leach
SAG Mill Control Room
Yellowcake Precip.
Central Control Room
Trammel Screen (ore pad)
North East Corner Ore Pad
Met. Lab
Filter Press Room
BHV-1
BHV-2
BHV-3
BHV-4
BHV-5
SAG Mill
Tails
CCD
North SX
Administration Building
Admin Parking Lot
Yellowcake Packaging
Yellowcake Storage
Bucking Room
Mill Lunch Room
South SX
Mtce. Super.'s Office
Ore Feed Grizzly
Scale house
Sample Plant (OBS)
Front Gate
AF -Barrel Dump Station
AF Circuit -South
AF Circuit-North
North Control # 1
North Control # 2
CaF2 Barrel Dump Station -
Operator Station
KF Barrel Dump Station
Date Issued
1/2/2014
1/2/2014
11212014
112/2014
112/2014
112/2014
1/2/2014
112/2014
11212014
1/2/2014
11212014
11212014
11212014
11212014
1/2/2014
11212014
112/2014
112/2014
11212014
112/2014
1/2/2014
112/2014
1/2/2014
112/2014
112/2014
1/2/2014
11212014
112/2014
112/2014
1/2/2014
11212014
112/2014
1/212014
112/2014
11212014
1/212014
1/2/2014
1/212014
112/2014
112/2014
1/2/2014
112/2014
Total
Days
Badge at
Date Returned WMM
3/27/2014 84
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/2712014
3/27/2014
3/27/2014
3/2712014
3127/2014
3/27/2014
3/2712014
3/27/2014
3127/2014
3/27/2014
3/27/2014
312712014
3/2712014
3127/2014
3/2712014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3127/2014
312712014
3/27/2014
3127/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3127/2014
3/27/2014
3/2712014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
84
Mean
Ambient
Dose
Equivalent
36.5
44.1
33.2
461.5
283.1
125.3
322.6
0
70.6
113
295.3
87.3
152.7
32
28.9
28.1
31.5
32.6
314.9
56.8
70.1
50.8
37.8
77.2
0
0
160.1
55.5
97.8
46.9
342.8
183.7
180.5
179
0
86.8
114.5
32.3
0
107.3
mRem/ mRem/
hour Day
0.02 0.435
0.02
0.02
0.23
0.00
0.14
0.06
0.16
0.00
0.04
0.06
0.15
0.04
0.08
0.02
0.01
0.01
0.02
0.02
0.16
0.03
0.03
0.03
0.02
0.04
0.00
0.00
0.08
0.03
0.05
0.02
0.17
0.09
0.09
0.09
0.00
0.04
0.06
0.00
0.02
0.00
0.05
0.525
0.395
5.494
0.000
3.370
1.492
3.840
0.000
0.840
1.345
3.515
1.039
1.818
0.381
0.344
0.335
0.375
0.388
3.749
0.676
0.835
0.605
0.450
0.919
0.000
0.000
1.906
0.661
1.164
0.558
4.081
2.187
2.149
2.131
0.000
1.033
1.363
0.000
0.385
0.000
1.277
mRem/
Week
3.04
3.68
2.77
38.46
0.00
23.59
10.44
26.88
0.00
5.88
9.42
24.61
7.28
12.73
2.67
2.41
2.34
2.63
2.72
26.24
4.73
5.84
4.23
3.15
6.43
0.00
0.00
13.34
4.63
8.15
3.91
28.57
15.31
15.04
14.92
0.00
7.23
9.54
0.00
2.69
0.00
8.94
Badge
Number
Control
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
45
46
47
51
52
53
64
White Mesa Mill Second Quarter 2014 Environmental Spherical Gamma Monitor Results
Location
Administration Vault
V205 Control Room
BHV-6
Ore Stor.-Barrel Area
Vanadium Precip.Area
Yellowcake Drying Area
Leach
SAG Mill Control Room
Yellowcake Precip.
Central Control Room
Ore pad -decontamination pad
North East Corner Ore Pad
Met. Lab
Filter Press Room
BHV-1
BHV-2
BHV-3
BHV-4
BHV-5
SAG Mill
Tails
CCD
North SX
Administration Building
Admin Parking Lot
Yellowcake Packaging
Yellowcake Storage
Bucking Room
Mill Lunch Room
South SX
Mtce. Super.'s Office
Ore Feed Grizzly
Scalehouse
Sample Plant (OBS)
Front Gate
AF-Barrel Dump Station
AF Circuit -South
AF Circuit-North
North Control # 1
North Control# 2
CaF2 Barrel Dump Station -
Operator Station
KF Barrel Dump Station
Date Issued
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
3/27/2014
Ambient
Total Days Dose
Badge at Equivalen mRem I
Date Returned WMM t hour
6/27/2014 92 35.3 0.02
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
6/27/2014
92
92
92
92
92
92
2
92
92
92
92
92
92
92
2
92
2
9-2
92
92
92
92
92
92
92
92
'2
2
92
92
'92
92
92
'92
92
92
2
92
92
92
92
51.4
31.1
508.1
116.7
0
165.2
359.9
0
86.9
117.4
379.9
93.9
179.6
37.7
30.8
33.6
32
37.2
354.4
63 .1
82.5
49.7
40.9
92.8
0
0
138.7
66.1
110.1
48.7
389.1
217
260.7
218.7
0
0
0
38.7
31.2
0
271.6
0.02
0.01
0.23
0.05
0.00
0.07
0.16
0.00
0.04
0.05
0.17
0.04
0.08
0.02
0.01
0.02
0.01
0.02
0.16
0.03
0.04
0.02
0.02
0.04
0.00
0.00
0.06
0.03
0.05
0.02
0.18
0.10
0.12
0.10
0.00
0.00
0.00
0.02
0.01
0.00
0.12
mRem/
Day
0.384
0.559
0.338
5.523
1.268
0.000
1.796
3.912
0.000
0.945
1.276
4.129
1.021
1.952
0.410
0.335
0.365
0.348
0.404
3.852
0.686
0.897
0.540
0.445
1.009
0.000
0.000
1.508
0.718
1.197
0.529
4.229
2.359
2.834
2.377
0.000
0.000
0.000
0.421
0.339
0.000
2.952
mRem/
Week
2.69
3.91
2.37
38.66
8.88
0.00
12.57
27.38
0.00
6.61
8.93
28.91
7.14
13.67
2.87
2.34
2.56
2.43
2.83
26.97
4.80
6.28
3.78
3.11
7.06
0.00
0.00
10.55
5.03
8.38
3.71
29.61
16.51
19.84
16.64
0.00
0.00
0.00
2.94
2.37
0.00
20.67
ATTACHMENT F
VEGETATION GRAPHS, DATA TABLE, LABORATORY RESULTS AND QAJQC
(Log Scale)
...... ...... ...... ......
0 0 0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m m I I I I I I I 0 0 0 0 0 0 0 co -...1 0) 01 .j:>. w 1\)
8/27/1981
8/27/1982 .
8/27/1983 .
8/27/1984 -
8/27/1985
8/27/1986 .
8/27/1987
8/27/1988
JJ 8/27/1989 . D)
I N 8/27/1990 . N
0)
8/27/1991 . 0 0
8/27/1992 ::::J (")
CD
8/27/1993 ::::J -""t
8/27/1994 D) -t a·
8/27/1995 ::::J t/1
z 8/27/1996 ::::J m < 8/27/1997 . CD
T
<C
8/27/1998 CD -D) -z 8/27/1999 . a· :;! ::::J
8/27/2000 -t c 0 8/27/2001 . =:::.:
UJ 8/27/2002 . " :;! <C -8/27/2003
8/27/2004 .
8/27/2005
8/27/2006 .
8/27/2007 .
8/27/2008 -
8/27/2009 .
8/27/2010 -
8/27/2011 •.
8/27/2012
8/27/2013 -
(Log Scale)
...... ...... ...... ...... ......
0 0 0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m m I I I I I I I 0 0 0 0 0 0 0 co --.I 0) U1 ~ c.v 1\:)
8/27/1981
8/27/1982
8/27/1983
8/27/1984
8/27/1985
8/27/1986
8/27/1987
8/27/1988
"0 8/27/1989 C" I
8/27/1990 . N ......
0
8/27/1991 . (")
0
8/27/1992 ::::J (')
(I)
8/27/1993 ::::J -'"' 8/27/1994 I» -s· t 8/27/1995 ::::J 0
z 8/27/1996 -:; m < 8/27/1997 -(I)
f
(Q
8/27/1998 (I) -I» -z 8/27/1999 -s· :E ::::J
8/27/2000 -t c
8/27/2001 (") ::::::
(J) "' :E 8/27/2002 . (Q --8/27/2003
8/27/2004
8/27/2005 .
8/27/2006
8/27/2007
8/27/2008
8/27/2009
8/27/2010
8/27/2011
8/27/2012
8/27/2013
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED QTR. SAMPLED DATE
3rd '81 27-Aug-81
4th '81 20-0ct-81
2nd'82 15-Apr-82
3rd '82 01-Jul-82
4th '82 30-Nov-82
2nd '83 13-Apr-83
3rd '83 01-Jul-83
4th '83 30-Jan-84
2nd'84 28-Jun-84
4th '84 14-Nov-84
2nd'85 27-Mar-85
3rd '85 15-Jul-85
4th '85 09-0ct-85
2nd '86 24-Mar-86
3rd '86 10-Jul-86
4th '86 18-Dec-86
2nd '87 20-Apr-87
3rd'87 05-Jun-87
4th '87 22-Dec-87
2nd'88 19-Apr-88
3rd '88 28-Jul-88
2nd'89 07-Apr-89
3rd '89 06-Jun-89
4th '89 07-Nov-89
1st '90 17-Apr-90
2nd'90 20-Jun-90
3rd '90 17-0ct-90
1st '91 10-Apr-91
2nd '91 11-Jun-91
3rd '91 20-Nov-91
1st '92 22-Apr-92
2nd '92 10-Jun-92
3rd'92 10-Jun-92
1st '93 13-Apr-93
2nd '93 26-Jun-93
3rd'93 12-0ct-93
1st '94 11-May-94
2nd'94 19-Jul-94
3rd'94 28-Nov-94
1st '95 11-Apr-95
2nd'95 06-Jul-95
3rd '95 15-Nov-95
1st '96 23-Apr-96
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96
1st '97 21-Apr-97
3rd '97 05-Sep-97
4th '97 20-Nov-97
1st '98 23-Mar-98
2nd '98 16-Jun-98
4th '98 05-Nov-98
2nd '99 15-Apr-99
3rd'99 07-Jul-99
4th '99 02-Dec-99
2nd'OO 21-Apr-00
2nd'OO 22-Jun-00
Ra-226 Ra-226
VALUE (uCi/Kg) ERROR (uCi/Kg)
3.90E-04 1.00E-05
1.40E-04 1.00E-05
1.31E-04 1.30E-05
1.60E-04 l.OOE-05
2.67E-06 1.07E-06
9.36E-05 6.20E-06
1.12E-04 1.20E-05
1.09E-04 8.00E-06
3.47E-04 1.20E-05
5.61E-04 1.99E-04
1.05E-03 3.00E-05
8.20E-05 7.00E-06
1.15E-04 l.OOE-05
5.72E-04 2.10E-05
5.01E-04 1.30E-05
8.70E-04 5.00E-05
5.90E-04 7.00E-05
1.60E-04 3.00E-05
2.10E-04 4.00E-05
4.50E-04 7.00E-05
3.20E-05 2.20E-05
5.60E-04 4.00E-05
1.50E-04 2.00E-05
6.00E-04 5.00E-05
2.60E-04 3.00E-05
1.80E-04 2.00E-05
1.60E-04 2.00E-05
1.20E-04 2.00E-05
9.10E-05 1.60E-05
4.50E-04 4.00E-05
3.60E-05 1.00E-05
l.OOE-05 7.00E-06
7.90E-05 3.50E-05
3.70E-05 2.20E-05
3.00E-05 1.50E-05
6.60E-05 2.70E-05
1.80E-04 4.00E-05
1.71E-05 1.20E-06
2.40E-04 1.50E-05
6.70E-05 5.40E-06
1.50E-05 1.50E-06
5.50E-05 5.00E-06
5.20E-05 2.50E-06
3.00E-05 2.50E-06
l.lOE-05 4.70E-07
l.lOE-05 4.30E-07
8.00E-06 1.20E-06
<9.10E-05 9.10E-05
1.80E-05 1.20E-06
5.70E-05 1.00E-06
2.00E-04 3.00E-06
6.03E-05 1.40E-06
2.30E-05 l.OOE-06
1.50E-04 3.00E-06
1.20E-06 l.OOE-07
LLD Pb-210 Pb-210 LLD
uCi/Kg (S.OE-08) VALUE (uCi/Kg) ERROR (uCi/Kg) uCi/Kg (l.OE-06)
5.00E-08 1.10E-03 l.OOE-04 l.OOE-06
S.OOE-08 6.80E-04 8.00E-05 l.OOE-06
l.OOE-06 4.90E-04 7.00E-05 8.00E-05
5.00E-08 8.00E-04 1.70E-04 1.00E-07
l.OOE-06 1.08E-04 9.00E-06 l.OOE-05
8.00E-09 .4.97E-04 9.30E-05 l.OOE-04
6.00E-06 1.84E-04 1.20E-05 l.OOE-06
4.00E-06 7.80E-04 6.20E-05 6.00E-05
2.00E-09 3.75E-03 1.60E-04 4.00E-08
2.00E-07 7.82E-03 3.30E-04 7.00E-08
2.00E-06 3.22E-03 1.40E-04 2.00E-05
3.00E-06 7.70E-04 1.30E-04 2.00E-04
3.00E-06 5.10E-04 3.00E-05 2.00E-05
4.00E-06 2.49E-03 l.OOE-04 l.OOE-05
3.00E-06 1.57E-03 1.70E-03 2.00E-04
3.00E-06 6.80E-04 3.00E-05 3.00E-06
5.00E-08 1.50E-03 l.OOE-04 l.OOE-06
5.00E-08 9.50E-04 4.00E-05 1.00E-06
5.00E-08 1.70E-03 l.OOE-04 l.OOE-06
5.00E-08 1.40E-03 l.OOE-04 l.OOE-06
5.00E-08 1.50E-04 4.40E-04 l.OOE-06
*** 1.10E-03 1.00E-01 ***
*** 2.30E-04 2.00E-05 ***
7.00E-06 2.04E-03 7.00E-05 1.40E-05
4.00E-06 3.30E-04 2.00E-05 2.20E-05
5.00E-08 3.20E-04 2.00E-05 l.OOE-06
5.00E-08 3.30E-04 2.00E-05 l.OOE-06
5.00E-06 3.00E-04 2.00E-05 l.OOE-06
2.00E-07 1.90E-04 2.00E-05 2.00E-07
5.00E-08 1.09E-03 5.00E-05 l.OOE-06
2.00E-06 l.50E-04 2.00E-05 l.OOE-05
2.00E-07 7.50E-05 2.00E-05 l.OOE-06
3.00E-06 7.10E-04 7.00E-05 2.00E-05
3.00E-06 2.80E-04 3.00E-05 2.00E-05
3.00E-06 4.30E-05 3.50E-05 2.00E-05
3.00E-06 5.30E-04 6.00E-05 2.00E-05
3.00E-05 4.40E-04 6.00E-05 2.00E-04
9.00E-08 3.00E-05 6.10E-06 4.45E-06
1.70E-07 1.70E-04 1.10E-05 8.30E-07
1.60E-07 1.40E-04 1.30E-05 7.90E-07
1.50E-07 5.10E-05 4.50E-06 7.60E-07
1.80E-07 6.70E-05 1.00E-05 8.80E-07
1.50E-07 3.20E-05 4.50E-06 1.80E-07
1.80E-07 1.40E-04 7.10E-06 9.30E-07
1.21E-07 4.10E-05 3.60E-06 6.10E-07
1.33E-07 2.10E-05 7.30E-07 6.66E-07
5.60E-07 1.40E-04 4.60E-06 1.10E-07
9.10E-05 <4.50E-04 4.50E-04 4.50E-04
6.30E-08 4.00E-05 1.80E-06 3.20E-07
8.20E-08 8.70E-05 5.00E-06 4.10E-07
1.20E-07 3.00E-04 l.OOE-05 6.00E-05
8.30E-08 1.40E-04 4.70E-06 4.20E-07
2.30E-07 2.10E-05 l.OOE-06 1.10E-06
1.20E-07 1.60E-04 8.00E-06 5.90E-07
2.80E-07 1.60E-04 l.OOE-05 1.40E-06
4th '00 21-Dec-00 1.60E-06 l.lOE-06 3.70E-07 5.10E-05 5.00E-06 1.90E-06
1st '01 30-Apr-01 l.OOE-06 l.OOE-07 2.40E-07 <1.2E-06 l.OOE-07 2.40E-07
2nd '01 14-Jun-01 2.30E-06 2.00E-07 9.90E-08 3.80E-06 2.00E-07 5.00E-07
4th '01 17-Dec-01 9.10E-06 2.40E-06 1.20E-07 3.57E-05 2.97E-06 6.00E-07
1st '02 07-May-02 3.30E-05 1.80E-06 7.60E-07 4.50E-05 2.61E-06 l.OOE-05
2nd '02 07-Jul-02 5.55E-05 2.81E-06 7.60E-07 5.31E-05 3.90E-06 l.OOE-05
4th '02 15-Dec-02 7.75E-05 3.60E-06 7.60E-07 1.29E-04 6.15E-06 l.OOE-05
1st '03 21-Mar-03 9.10E-06 1.30E-06 3.60E-07 1.13E-05 1.61E-06 3.36E-06
2nd'03 10-Jun-03 2.50E-05 1.30E-06 3.60E-07 3.26E-06 2.00E-06 7.38E-08
4th '03 20-Nov-03 5.70E-05 3.50E-06 1.50E-07 4.05E-05 5.82E-06 8.30E-07
1st '04 08-Apr-04 9.38E-05 3.70E-06 l.lOE-07 5.88E-05 3.00E-06 5.50E-07
2nd '04 12-Jun-04 5.63E-05 3.40E-06 1.80E-07 6.42E-05 5.90E-06 9.00E-07
4th '04 30-Nov-04 8.41E-05 5.50E-06 2.00E-08 2.48E-04 1.40E-05 3.00E-07
1st 'OS 21-Apr-05 S.60E-OS 3.00E-06 1.40E-07 5.80E-05 4.00E-06 6.90E-07
2nd'OS 13-Jun-OS 9.10E-06 1.50E-06 1.80E-07 1.10E-05 1.20E-OS 9.00E-07
4th 'OS 10-Nov-OS 6.00E-OS 3.00E-06 l.lOE-10 1.70E-06 6.40E-07 S.SOE-10
1st '06 03-Apr-06 8.00E-05 S.OOE-06 5.00E-08 3.40E-04 1.20E-05 1.00E-06
2nd '06 16-Jun-06 4.10E-05 3.10E-06 5.00E-08 1.16E-04 6.10E-06 1.00E-06
4th '06 28-Nov-06 1.17E-04 4.60E-06 1.90E-07 3.28E-04 9.50E-06 9.50E-07
1st '07 30-Mar-07 9.70E-OS 4.40E-06 1.90E-07 3.40E-04 8.70E-06 8.4-07
2nd '07 1-Jun-07 1.30E-05 1.60E-06 1.90E-07 1.20E-04 6.60E-06 9.70E-07
4th '07 23-Nov-07 7.00E-05 8.20E-06 2.00E-07 5.00E-04 2.00E-05 1.20E-06
1st '08 22-Apr-08 3.60E-06 3.00E-06 5.20E-07 2.30E-04 1.40E-05 1.00E-06
2nd'08 18-Jun-08 3.20E-05 3.20E-06 1.80E-06 6.90E-OS 3.50E-OS S.SOE-OS
4th '08 12-Dec-08 l.SOE-04 5.20E-06 9.90E-07 3.60E-04 2.90E-OS 3.90E-OS
1st '09 28-Apr-09 S.90E-04 1.3SE-OS l.SOE-06 3.40E-04 1.30E-OS l.SOE-06
2nd '09 17-Jun-09 1.90E-05 1.4SE-06 4.90E-07 3.60E-OS l.lOE-OS 1.80E-OS
4th '09 18-Dec-09 1.70E-04 5.90E-06 4.80E-04 1.20E-05
1st '10 13-May-10 2.20E-04 7.20E-06 1.10E-06 1.90E-04 1.90E-05 2.90E-OS
2nd '10 18-Jun-10 6.SOE-05 3.40E-06 7.60E-07 1.40E-04 1.90E-05 2.90E-05
4th '10 20-Dec-10 2.30E-05 1.70E-06 5.20E-07 l.OOE-05 1.50E-06 2.30E-06
2nd '11 23-Jun-11 2.40E-07 1.40E-07 1.80E-07 <2.9E-06 1.70E-06 2.90E-06
3rd '11 27-Jul-11 4.90E-06 6.30E-07 3.20E-07 9.50E-05 2.10E-06 2.50E-06
4th '11 23-Nov-11 7.20E-06 7.50E-07 2.90E-07 8.80E-08 4.30E-07 7.20E-07
2nd'12 11-Apr-12 4.40E-05 1.90E-06 3.60E-07 2.10E-04 2.00E-06 l.OOE-06
3rd '12 11-Jun-12 2.20E-05 8.40E-07 1.10E-07 1.30E-04 7.60E-06 5.90E-06
4th '12 06-Nov-12 3.10E-05 4.82E-07 4.63E-08 4.26E-04 3.72E-06 6.52E-07
2nd '13 30-Apr-13 1.14E-04 1.74E-06 5.34E-07 2.6SE-04 4.41E-06 5.37E-06
3rd '13 20-Jun-13 8.91E-05 2.16E-06 1.42E-06 1.42E-04 3.68E-06 6.17E-06
4th '13 14-Nov-13 1.37E-04 3.87E-06 4.71E-06 5.33E-04 1.45E-05 2.27E-05
2nd '14 16-Apr-14 9.90E-05 1.01E-06 3.91E-07 1.99E-04 3.14E-06 3.38E-06
3rd '14 10-Jun-14 2.60E-05 8.46E-07 9.19E-07 5.60E-05 3.08E-06 7.12E-06
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected dunng th1s penod
(Log Scale) _.. _.. _.. _..
0 0 0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m m I I I I I I I 0 0 0 0 0 0 0 CXl ""-1 en 01 ~ c.u 1\)
01-Jan-81
01-Jan-82 =e ~ 01-Jan-83 =i
01-Jan-84 m
3:
01-Jan-85 m C/)
01-Jan-86 )>
3: 01-Jan-87 -r-r-01-Jan-88 I
01-Jan-89 z 0
01-Jan-90 -JJ -1 ~
01-Jan-91 -m )>
01-Jan-92 -C/)
-1
01-Jan-93 0
t
.,
01-Jan-94 s:
JJ 01-Jan-95 r-
iJl -r-r\J f,JJ 1\J 01-Jan-96 (l) -·D) -I
T
01-Jan-97 :;:ti:;N
CCN -en
-u 01-Jan-98 · D)
0" :::J r\J 01-Jan-99 c. ~
0 "tt 01-Jan-00 · C" I
01-Jan-01
1\) ......
0
01-Jan-02 0
0
01-Jan-03 :::J
(')
01-Jan-04 ' CD :::J -..,
01-Jan-05 D) -s· 01-Jan-06 :::J en
01-Jan-07 --· :::J
01-Jan-08 < CD
01-Jan-09
cg
!
01-Jan-10 " D) -s·
01-Jan-11 :::J
01-Jan-12
01-Jan-13
01-Jan-14
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHWEST OF MILL
SAMPLED QTR. SAMPLED DATE
3rd '81 27-Aug-81
4th '81 20-0ct-81
2nd'82 15-Apr-82
3rd'82 01-Jul-82
4th '82 30-Nov-82
2nd'83 13-Apr-83
3rd '83 01-Jul-83
4th '83 30-Jan-84
2nd'84 28-Jun-84
4th '84 14-Nov-84
2nd '85 27-Mar-85
3rd '85 15-Jul-85
4th '85 09-0ct-85
2nd '86 24-Mar-86
3rd'86 10-Jul-86
4th '86 18-Dec-86
2nd'87 20-Apr-87
3rd'87 05-Jun-87
4th '87 22-Dec-87
2nd'88 19-Apr-88
3rd '88 28-Jul-88
2nd'89 07-Apr-89
3rd'89 06-Jun-89
4th '89 07-Nov-89
1st '90 17-Apr-90
2nd '90 20-Jun-90
3rd '90 17-0ct-90
1st '91 10-Apr-91
2nd '91 11-Jun-91
3rd '91 20-Nov-91
1st '92 22-Apr-92
2nd '92 10-Jun-92
3rd '92 10-Jun-92
1st '93 13-Apr-93
2nd '93 26-Jun-93
3rd'93 12-0ct-93
1st '94 11-May-94
2nd'94 19-Jul-94
3rd'94 28-Nov-94
1st '95 11-Apr-95
2nd'95 06-Jul-95
3rd '95 15-Nov-95
1st '96 23-Apr-96
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96
1st '97 21-Apr-97
3rd '97 05-Sep-97
4th '97 20-Nov-97
1st '98 23-Mar-98
2nd '98 16-Jun-98
4th '98 05-Nov-98
2nd '99 15-Apr-99
3rd '99 07-Jul-99
4th '99 02-Dec-99
2nd '00 21-Apr-00
Ra-226
VALUE (uCi/Kg)
2.73E-03
2.00E-04
1.04E-04
2.00E-05
2.36E-06
8.58E-05
1.19E-04
9.78E-05
2.08E-04
6.05E-04
1.10E-04
6.10E-05
1.07E-04
8.86E-04
6.66E-04
5.20E-04
4.10E-04
1.60E-04
3.60E-04
2.60E-04
3.10E-05
6.20E-04
3.40E-04
5.10E-04
3.60E-04
1.70E-04
8.80E-05
3.00E-04
3.10E-04
5.00E-04
2.00E-05
6.50E-06
1.20E-04
1.80E-05
5.20E-05
5.10E-05
1.20E-04
3.73E-05
2.40E-04
8.40E-05
1.90E-05
1.20E-04
8.30E-05
3.60E-05
3.30E-05
5.40E-06
8.90E-06
<9.20E-05
< 6.50E-08
4.20E-05
6.20E-05
5.45E-05
l.lOE-04
3.70E-05
Ra-226 LLD Pb-210 Pb-210 LLD
ERROR (uCi/Kg) uCi/Kg (S.OE-08) VALUE (uCi/Kg) ERROR (uCi/Kg) uCi/Kg (1.0E-06)
S.OOE-05 5.00E-08 7.10E-03 3.00E-04 1.00E-06
l.OOE-05 5.00E-08 8.30E-04 5.00E-05 1.00E-06
9.00E-06 7.00E-06 6.40E-04 5.00E-05 4.00E-05
l.OOE-05 5.00E-08 2.20E-04 9.00E-05 l.OOE-07
9.50E-07 1.00E-06 8.00E-05 l.OOE-05 l.OOE-05
1.36E-05 2.00E-08 3.53E-04 1.90E-05 l.OOE-05
l.lOE-05 5.00E-06 1.58E-04 1.30E-05 l.OOE-05
7.00E-06 2.00E-06 2.16E-03 3.40E-04 3.00E-04
l.OOE-05 3.00E-09 1.60E-03 7.00E-05 3.00E-08
1.64E-04 2.00E-07 2.58E-03 l.lOE-04 3.00E-08
8.00E-06 3.00E-06 8.63E-04 4.20E-05 3.00E-05
6.00E-06 2.00E-06 5.40E-04 5.00E-05 5.00E-05
6.00E-06 2.00E-06 3.80E-04 3.00E-05 2.00E-05
1.80E-05 2.00E-06 4.40E-03 1.90E-04 3.00E-05
1.80E-05 3.00E-06 4.78E-03 2.10E-04 6.00E-05
l.OOE-04 3.00E-06 1.70E-03 l.OOE-04 6.00E-05
l.OOE-04 5.00E-08 1.60E-03 l.OOE-04 l.OOE-06
3.00E-05 5.00E-08 5.50E-04 4.00E-05 l.OOE-06
5.00E-05 5.00E-08 1.80E-03 l.OOE-04 l.OOE-06
5.00E-05 5.00E-08 1.90E-03 l.OOE-04 l.OOE-06
1.90E-05 5.00E-08 1.60E-04 4.00E-05 l.OOE-06
5.00E-05 *** 1.70E-03 l.OOE-04 ***
3.00E-05 *** 7.40E-04 3.00E-05 ***
6.00E-05 7.00E-06 1.00E-03 7.00E-05 1.40E-05
3.00E-05 4.00E-06 4.80E-04 2.00E-05 2.20E-05
2.00E-05 5.00E-08 3.20E-04 2.00E-05 1.00E-06
1.60E-05 5.00E-08 2.90E-04 2.00E-05 1.00E-06
3.00E-05 5.00E-06 4.10E-04 2.00E-05 l.OOE-06
3.00E-05 2.00E-07 4.70E-04 2.00E-05 2.00E-07
4.00E-05 5.00E-08 1.50E-03 l.OOE-04 l.OOE-06
8.00E-06 2.00E-06 9.60E-05 1.40E-05 l.OOE-05
6.00E-06 2.00E-06 1.20E-04 2.00E-05 l.OOE-06
4.00E-05 3.00E-06 1.21E-03 8.00E-05 2.00E-05
1.70E-05 3.00E-06 2.10E-04 3.00E-05 2.00E-05
1.90E-05 3.00E-06 1.70E-05 3.60E-05 2.00E-05
2.30E-05 3.00E-06 7.10E-04 6.00E-05 2.00E-05
l.OOE-05 3.00E-05 9.80E-04 1.60E-04 2.00E-04
1.60E-06 8.40E-08 7.80E-05 7.10E-06 4.20E-07
1.50E-05 1.70E-07 2.60E-04 1.30E-05 8.30E-07
6.10E-06 1.50E-07 1.20E-04 1.10E-05 7.50E-05
1.50E-06 1.40E-07 4.50E-05 4.30E-06 7.20E-07
6.80E-06 1.40E-07 l.OOE-05 5.80E-06 7.10E-07
3.30E-06 1.90E-07 6.80E-05 6.30E-06 1.80E-07
2.50E-06 1.60E-07 8.50E-05 5.60E-06 8.40E-07
2.30E-06 1.70E-07 4.40E-05 4.80E-06 8.40E-07
3.50E-07 1.56E-07 3.20E-05 9.00E-07 7.83E-07
7.20E-07 5.40E-07 3.40E-04 6.70E-06 l.lOE-07
9.20E-05 9.20E-05 <4.60E-04 4.60E-04 4.60E-04
6.50E-08 6.50E-08 <3.20E-07 3.20E-07 3.20E-07
l.OOE-06 l.lOE-07 1.70E-04 l.OOE-05 5.50E-07
l.OOE-06 l.OOE-07 1.40E-04 7.00E-06 1.00E-07
1.40E-06 8.30E-08 '9.20E-05 4.00E-06 4.20E-07
3.00E-06 2.20E-07 2.80E-05 l.OOE-06 l.lOE-06
l.OOE-06 2.40E-07 2.70E-04 l.OOE-05 1.20E-06
2nd '00 22-Jun-00 2.90E-05 l.OOE-06 3.30E-07 2.80E-04 2.00E-05 1.70E-06
4th '00 21-Dec-00 2.30E-06 1.40E-06 3.70E-07 3.30E-04 S.OOE-05 1.90E-06
1st '01 30-Apr-01 2.10E-05 1.00E-06 l.SOE-07 <7.6E-07 N/A 7.60E-07
2nd '01 14-Jun-01 1.30E-06 4.00E-08 1.20E-07 1.80E-06 3.00E-08 5.90E-07
4th '01 17-Dec-01 3.70E-05 7.67E-07 8.30E-08 6.72E-05 2.62E-06 6.00E-07
1st '02 07-May-02 4.90E-05 2.40E-06 7.60E-07 1.28E-04 5.61E-06 l.OOE-05
2nd'02 07-Jul-02 8.88E-05 4.32E-06 7.60E-07 8.33E-05 4.32E-06 l.OOE-05
4th '02 15-Dec-02 l.SOE-04 6.20E-06 7.60E-07 3.16E-04 1.07E-05 l.OOE-05
1st '03 21-Mar-03 S.OOE-05 3.40E-06 2.71E-06 <4.2e-6 4.20E-06
2nd'03 10-Jun-03 5.60E-05 2.00E-06 4.10E-07 1.88E-04 5.14E-06 8.20E-08
4th '03 20-Nov-03 3.20E-04 8.20E-06 1.70E-07 4.89E-04 1.25E-05 8.30E-07
1st '04 08-Apr-04 6.29E-05 4.10E-06 2.00E-07 1.94E-05 4.00E-06 l.OOE-06
2nd'04 12-Jun-04 6.51E-05 3.40E-06 1.30E-07 1.87E-05 3.90E-06 6.SOE-07
4th '04 30-Nov-04 7.50E-05 4.60E-06 2.00E-08 4.45E-04 1.40E-05 3.00E-07
1st 'OS 21-Apr-05 4.90E-05 2.70E-06 1.30E-07 1.27E-04 4.80E-06 6.SOE-07
2nd'OS 13-Jun-05 2.30E-05 2.10E-06 l.SOE-07 4.70E-05 5.10E-06 7.60E-07
4th 'OS 10-Nov-05 7.40E-05 3.SOE-06 1.20E-10 2.40E-06 8.10E-08 5.80E-10
1st '06 03-Apr-06 1.00E-04 6.00E-06 S.OOE-08 6.54E-04 l.SOE-05 l.OOE-06
2nd '06 16-Jun-06 9.50E-05 5.90E-06 S.OOE-08 4.48E-04 1.40E-05 1.00E-06
4th '06 28-Nov-06 8.13E-05 4.10E-06 2.20E-07 3.25E-04 1.12E-06 1.00E-05
1st '07 30-Mar-07 4.30E-05 2.60E-06 1.70E-07 2.64E-04 7.20E-06 8.60E-07
2nd '07 1-Jun-07 5.10E-05 3.20E-06 2.30E-07 5.30E-04 1.40E-06 1.20E-06
4th '07 23-Nov-07 7.30E-05 6.60E-06 S.OOE-08 7.00E-04 2.20E-05 1.10E-06
1st '08 22-Apr-08 2.80E-06 2.80E-06 7.20E-07 4.40E-04 2.00E-05 l.OOE-06
2nd '08 18-Jun-08 3.20E-06 3.30E-06 1.80E-06 1.40E-04 3.30E-05 S.SOE-05
4th '08 12-Dec-08 7.30E-05 3.20E-06 7.40E-07 4.40E-04 2.50E-05 3.20E-05
1st '09 28-Apr-09 5.25E-05 3.60E-06 l.lOE-06 1.90E-04 l.SOE-05 2.20E-05
2nd '09 17-Jun-09 2.30E-05 1.60E-05 5.20E-07 4.30E-05 l.OOE-05 1.70E-05
4th '09 18-Dec-09 S.SOE-05 3.50E-06 3.00E-04 1.10E-05
1st '10 13-May-10 1.90E-04 6.10E-06 9.40E-07 5.10E-04 2.40E-05 3.10E-05
2nd '10 18-Jun-10 2.30E-05 2.00E-06 7.70E-07 8.30E-05 1.80E-05 2.90E-05
4th '10 20-Dec-10 8.60E-06 9.10E-07 3.90E-07 l.lOE-07 6.80E-07 1.10E-06
2nd '11 23-Jun-11 2.10E-07 1.20E-07 1.40E-07 <2.2E-06 1.30E-06 2.20E-06
3rd '11 28-Jul-11 4.20E-06 5.40E-07 2.70E-07 2.30E-04 2.SOE-06 2.30E-06
4th '11 23-Nov-11 7.70E-06 6.80E-07 2.30E-07 <5.8E-08 3.40E-07 5.80E-07
2nd'12 11-Apr-12 l.SOE-05 9.50E-07 2.60E-07 <7.0E-07 6.00E-07 l.OOE-06
3rd '12 11-Jun-12 8.30E-06 5.40E-07 1.20E-07 1.40E-04 8.30E-06 6.SOE-06
4th '12 06-Nov-12 2.34E-05 4.10E-07 7.71E-08 4.59E-04 3.83E-06 6.18E-07
2nd'13 30-Apr-13 9.04E-05 1.68E-06 8.58E-07 2.24E-04 4.46E-06 4.68E-06
3rd '13 20-Jun-13 2.58E-06 9.59E-07 8.06E-07 1.06E-04 2.30E-06 3.28E-06
4th '13 14-Nov-13 1.43E-04 3.70E-06 2.17E-06 4.65E-04 1.17E-05 1.80E-05
2nd'14 16-Apr-14 2.53E-05 6.29E-07 5.51E-07 5.70E-05 2.21E-06 4.52E-06
3rd '14 10-Jun-14 2.53E-05 S.SSE-07 5.77E-07 7.68E-05 2.08E-06 3.66E-06
*2nd quarter of 1996 San Juan County, Utah, was declared a d1saster area due to drought, no samples were collected dunng th1s penod
0 0 0 0 0 0 m m m I I I 0 0 0 co ..._. O'l
01-Jan-81
01-Jan-82
01-Jan-83
01-Jan-84 -
01-Jan-85
01-Jan-86
01 -Jan-87
01-Jan-88
01-Jan-89 _,
01-Jan-90
01-Jan-91
01-Jan-92 •·
t 01-Jan-93
01 -Jan-94
JJ "' 01-Jan-95 N 1\) (j) 01-Jan-96
T 01-Jan-97
-u 01-Jan-98 • 0" ~ 01-Jan-99 -0
01-Jan-00
01 -Jan-01 -
01-Jan-02
01-Jan-03 -
01-Jan-04 -
01-Jan-05 -
01-Jan-06
01-Jan-07 -
01 -Jan-08
01-Jan-09
01-Jan-1 0
01-Jan-11
01-Jan-12
01-Jan-13
01-Jan-14
(Log Scale)
......
0 0 m I 0 01
0 0 m I 0 ~
......
0 0 m I 0 w
0 0 m I 0 1\)
:E
::I:
=t m s:: m en l> s::
r r
z 0
::tl -4 ::I: :E m en -4
0 "TI
3:
r -· f>::t~ -·I» -. "'I\) CCN
-0)
I»
:::::s c.
"'tJ C" N ......
0
0 0
:::::s (')
C'D
:::::s -a a·
:::::s
U)
5'
~ (Q
C'D -I» -a·
:::::s
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED QTR. SAMPLED DATE
3rd '81 27-Aug-81
4th '81 20-0ct-81
2nd '82 15-Apr-82
3rd '82 01-Jul-82
4th '82 30-Nov-82
2nd '83 13-Apr-83
3rd '83 01-Jul-83
4th '83 30-Jan-84
2nd '84 28-Jun-84
4th '84 14-Nov-84
2nd '85 27-Mar-85
3rd '85 15-Jul-85
4th '85 09-0ct-85
2nd'86 24-Mar-86
3rd '86 10-Jul-86
4th '86 18-Dec-86
2nd'87 20-Apr-87
3rd '87 05-Jun-87
4th '87 22-Dec-87
2nd '88 19-Apr-88
3rd '88 28-Jul-88
2nd '89 07-Apr-89
3rd'89 06-Jun-89
4th '89 07-Nov-89
1st '90 17-Apr-90
2nd'90 20-Jun-90
3rd '90 17-0ct-90
1st '91 10-Apr-91
2nd'91 11-Jun-91
3rd '91 20-Nov-91
1st '92 22-Apr-92
2nd '92 10-Jun-92
3rd'92 10-Jun-92
1st '93 13-Apr-93
2nd'93 26-Jun-93
3rd'93 12-0ct-93
1st '94 11-May-94
2nd'94 19-Jul-94
3rd'94 28-Nov-94
1st '95 11-Apr-95
2nd '95 06-Jul-95
3rd '95 15-Nov-95
1st '96 23-Apr-96
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96
1st'97 21-Apr-97
3rd'97 05-Sep-97
4th '97 20-Nov-97
1st '98 23-Mar-98
2nd'98 16-Jun-98
4th '98 05-Nov-98
2nd '99 15-Apr-99
3rd '99 07-Jul-99
4th '99 02-Dec-99
2nd'OO 21-Apr-00
Ra-226
VALUE (uCi/Kg)
9.50E-04
3.00E-05
1.37E-05
3.40E-04
1.75E-05
7.13E-04
5.39E-05
6.40E-05
8.27E-05
2.72E-04
4.73E-04
6.60E-05
2.83E-04
1.57E-04
3.78E-04
2.60E-04
4.10E-04
2.90E-04
1.80E-04
2.30E-04
1.50E-04
3.10E-04
1.30E-04
4.30E-04
2.50E-04
l.lOE-04
6.10E-05
3.40E-05
B.OOE-05
6.50E-05
1.60E-05
1.90E-05
1.60E-05
2.60E-05
3.00E-05
3.10E-05
2.00E-05
1.75E-05
l.OOE-04
1.70E-05
6.40E-06
2.30E-05
4.20E-05
2.10E-05
5.50E-06
5.30E-06
2.50E-05
<7.90E-05
3.60E-07
4.30E-05
2.40E-05
2.23E-05
1.50E-04
l.OOE-04
Ra-226 LLD Pb-210 Pb-210 LLD
ERROR (uCi/Kg) uCl/Kg (S.OE-08) VALUE (uCi/Kg) ERROR (uCi/Kg) uCI/Kg (l.OE-06)
2.00E-05 5.00E-08 1.50E-04 l.OOE-05 l.OOE-06
3.00E-06 5.00E-08 1.50E-04 2.00E-05 l.OOE-06
3.00E-06 3.00E-06 3.80E-04 4.00E-05 4.00E-05
2.00E-05 5.00E-08 3.68E-03 2.70E-04 l.OOE-07
3.00E-06 2.00E-06 7.92E-04 4.00E-06 2.00E-05
7.30E-05 9.00E-08 2.51E-03 3.00E-04 3.00E-04
4.50E-06 2.00E-06 6.88E-04 4.30E-05 4.00E-05
7.00E-06 4.00E-06 1.20E-03 l.OOE-04 4.00E-05
6.30E-06 3.00E-09 1.80E-03 l.OOE-04 9.00E-08
1.48E-04 2.00E-07 4.70E-03 7.20E-04 3.00E-07
1.60E-07 3.00E-06 7.07E-04 3.60E-05 3.00E-05
7.00E-06 4.00E-06 4.90E-04 3.00E-05 3.00E-05
2.00E-05 7.00E-06 1.50E-03 l.OOE-04 7.00E-05
1.00E-05 4.00E-06 4.14E-03 1.80E-04 3.00E-05
l.OOE-05 2.00E-06 1.65E-02 7.00E-04 l.OOE-04
2.00E-05 2.00E-06 1.70E-03 1.00E-04 l.OOE-04
7.00E-05 5.00E-08 2.20E-03 l.OOE-04 1.00E-06
4.00E-05 5.00E-08 7.50E-04 5.00E-05 l.OOE-06
3.00E-05 5.00E-08 2.40E-03 1.00E-04 l.OOE-06
5.00E-05 5.00E-08 2.90E-03 1.00E-04 l.OOE-06
3.00E-05 5.00E-08 4.30E-03 2.00E-04 1.00E-06
4.00E-05 *** 4.20E-03 l.OOE-04 ***
2.00E-05 *** 1.50E-03 l.OOE-04 ***
5.00E-05 1.40E-05 3.50E-03 1.40E-04 2.70E-05
3.00E-05 5.00E-06 2.39E-03 5.00E-05 2.50E-05
2.00E-05 5.00E-08 6.60E-04 3.00E-05 l.OOE-06
1.40E-05 5.00E-08 6.10E-04 3.00E-05 1.00E-06
1.10E-05 5.00E-06 2.20E-04 l.OOE-05 l.OOE-06
6.00E-06 2.00E-07 1.20E-04 l.OOE-05 2.00E-07
1.40E-05 5.00E-08 9.10E-04 5.00E-05 l.OOE-06
7.00E-06 2.00E-06 3.20E-04 2.00E-05 l.OOE-05
l.OOE-05 2.00E-07 2.20E-04 2.00E-05 1.00E-06
1.80E-05 3.00E-06 7.60E-04 6.00E-05 2.00E-05
2.00E-05 3.00E-06 3.40E-04 3.00E-05 2.00E-05
1.40E-05 3.00E-06 O.OOE+OO 3.00E-05 2.00E-05
1.60E-05 3.00E-06 4.20E-04 6.00E-05 2.00E-05
5.00E-06 3.00E-05 3.90E-04 8.00E-05 2.00E-04
1.70E-06 7.60E-08 1.30E-04 7.80E-06 3.80E-07
9.00E-06 1.50E-07 2.60E-04 1.20E-05 7.40E-07
1.50E-06 1.60E-07 1.60E-04 1.50E-05 8.10E-07
6.00E-07 1.40E-07 4.40E-05 4.20E-06 7.00E-07
2.20E-06 1.70E-07 6.60E-05 9.60E-06 8.30E-07
2.20E-06 1.70E-07 l.OOE-04 6.70E-06 1.80E-07
2.00E-06 1.60E-07 1.90E-04 7.30E-06 8.20E-07
4.20E-07 1.40E-07 3.30E-05 3.90E-06 7.00E-07
3.20E-07 1.26E-07 1.90E-05 6.90E-07 6.34E-07
9.50E-07 5.90E-07 1.30E-04 4.70E-06 1.20E-07
7.90E-05 7.90E-05 <3.90E-04 3.90E-04 3.90E-04
1.40E-07 3.30E-08 <1.7E-07 1.70E-07 1.70E-07
1.00E-06 7.60E-08 2.50E-04 l.OOE-05 3.80E-07
l.OOE-06 1.20E-07 1.70E-04 8.00E-06 6.20E-07
8.60E-07 1.20E-07 2.30E-04 7.00E-06 5.90E-07
3.00E-06 2.00E-07 1.70E-05 l.OOE-06 l.OOE-06
2.00E-06 1.20E-07 1.10E-04 7.00E-06 6.10E-07
2nd'OO 22-Jun-00 1.30E-06 1.00E-07 2.40E-07 2.00E-04 l.OOE-05 1.20E-06
4th '00 21-Dec-00 1.20E-06 9.00E-07 2.40E-07 1.20E-04 3.00E-05 1.20E-06
1st '01 30-Apr-01 1.80E-06 1.00E-07 1.70E-07 <::8.3E-07 N/A 8.30E-07
2nd'01 14-Jun-01 2.60E-06 2.00E-07 9.90E-08 l.lOE-06 2.00E-08 5.00E-07
4th '01 17-Dec-01 2.63E-06 4.60E-05 1.20E-07 9.40E-05 3.72E-06 6.00E-07
1st '02 07-May-02 3.50E-05 2.20E-06 7.60E-07 1.36E-04 5.61E-06 1.00E-05
2nd'02 07-Jul-02 4.02E-05 2.34E-06 7.60E-07 7.04E-05 4.11E-06 1.00E-05
4th '02 15-Dec-02 8.10E-05 3.90E-06 7.60E-07 2.87E-04 8.54E-06 l.OOE-05
1st '03 21-Mar-03 3.70E-05 2.60E-06 2.41E-06 2.69E-05 2.01E-06 3.73E-06
2nd '03 10-Jun-03 1.30E-05 l.OOE-06 5.20E-07 <l.OOE-07 1.00E-07
4th '03 20-Nov-03 1.60E-04 1.30E-05 1.20E-07 1.42E-04 6.42E-06 5.90E-07
1st '04 08-Apr-04 1.40E-04 7.70E-06 l.lOE-07 6.10E-06 2.70E-06 5.50E-07
2nd'04 12-Jun-04 6.51E-05 3.20E-06 1.50E-07 5.27E-05 4.90E-06 7.60E-07
4th '04 30-Nov-04 8.40E-05 5.70E-06 3.00E-08 3.39E-04 1.60E-05 3.00E-07
1st '05 21-Apr-05 1.70E-05 1.60E-06 1.30E-07 4.50E-05 3.50E-06 6.50E-07
2nd '05 13-Jun-05 1.50E-05 1.60E-06 1.40E-07 7.00E-05 5.10E-06 6.90E-07
4th '05 10-Nov-05 3.80E-05 2.10E-06 8.60E-10 1.20E-06 4.80E-08 4.30E-10
1st '06 03-Apr-06 l.OOE-04 6.00E-06 5.00E-08 3.30E-04 l.lOE-05 l.OOE-06
2nd '06 16-Jun-06 3.40E-05 2.50E-06 5.00E-08 1.37E-04 6.00E-06 1.00E-06
4th '06 28-Nov-06 7.31E-05 3.20E-06 1.60E-07 2.98E-04 8.50E-06 8.20E-07
1st '07 30-Mar-07 3.00E-05 2.20E-06 1.70E-07 3.20E-04 7.90E-06 8.40E-07
2nd'07 1-Jun-07 l.lOE-04 4.60E-06 2.3-07 3.20E-04 1.10E-05 1.10E-06
4th '07 23-Nov-07 5.60E-05 5.20E-06 5.00E-08 6.40E-04 1.90E-05 1.00E-06
1st '08 22-Apr-08 3.20E-05 2.30E-06 7.20E-07 2.30E-04 1.50E-05 l.OOE-06
2nd '08 18-Jun-08 1.25E-05 2.20E-06 1.80E-06 5.00E-05 3.00E-05 4.80E-03
4th '08 12-Dec-08 9.20E-05 4.10E-06 9.60E-07 4.10E-04 3.00E-05 4.00E-05
1st '09 28-Apr-09 2.60E-05 2.90E-06 1.40E-06 3.70E-05 1.50E-06 2.50E-05
2nd '09 17-Jun-09 2.40E-05 1.40E-06 3.90E-07 3.50E-05 7.90E-06 1.30E-05
4th '09 18-Dec-09 3.10E-05 2.30E-06 2.10E-04 8.40E-06
1st '10 13-May-10 2.00E-05 2.10E-06 9.40E-07 5.60E-05 1.50E-05 2.40E-05
2nd '10 18-Jun-10 1.10E-05 1.30E-06 6.60E-07 7.80E-05 1.60E-05 2.50E-05
4th '10 20-Dec-10 6.70E-06 9.10E-07 4.80E-07 8.00E-07 7.90E-07 1.30E-06
2nd '11 23-Jun-11 <1.7E-07 6.90E-08 1.70E-07 <2.5E-06 1.50E-06 2.50E-06
3rd '11 27-Jul-11 1.60E-05 1.00E-06 2.60E-07 9.50E-05 1.60E-06 1.70E-06
4th '11 23-Nov-11 7.80E-07 2.50E-07 2.30E-07 <5.9E-07 3.50E-07 5.90E-07
2nd'12 11-Apr-12 5.00E-06 6.00E-07 3.00E-07 <7.0E-07 7.00E-07 l.OOE-06
3rd '12 11-Jun-12 1.90E-08 6.20E-08 l.lOE-07 <::2.5E-07 1.30E-06 2.20E-06
4th '12 06-Nov-12 1.49E-05 3.41E-07 4.25E-08 4.45E-04 4.01E-06 8.57E-07
2nd '13 30-Apr-13 4.50E-05 1.19E-06 5.39E-07 3.62E-04 6.30E-06 9.90E-06
3rd '13 20-Jun-13 1.51E-05 1.06E-06 1.96E-06 6.71E-05 2.93E-06 6.24E-06
4th '13 14-Nov-13 1.18E-04 3.39E-06 2.97E-06 5.92E-04 1.27E-05 1.62E-05
2nd'14 16-Apr-14 4.65E-05 1.08E-06 7.35E-07 2.13E-04 5.93E-06 1.31E-05
3rd'14 10-Jun-14 1.23E-05 4.97E-07 6.97E-07 2.46E-05 1.84E-06 4.63E-06
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected during this period
(Log Scale)
.. .... .... .... .... -
0 0 0 0 0 0 0 0 0
0 0 0 0 0 0 0 0 0 m m m m m m m m m
I I I I I I I I + 0 0 0 0 0 0 0 0 0 co --.J (j) U1 .j:>. U) 1\) .... 0
01-Jan-81 :e
01-Jan-82 -::I:
::::j
01-Jan-83 -m
01-Jan-84 • s: m
01-Jan-85 en )>
01-Jan-86 s: -r-
01-Jan-87 r-
I
01-Jan-88 en 0
01-Jan-89 c: -1
01-Jan-90 ::I: :e
01-Jan-91 m en
01-Jan-92 -1
0
t 01-Jan-93 "T1
01-Jan-94 s:
JJ r-~ 01-Jan-95 c• 1\.) OJ:J 0) 01-Jan-96 -·D) -I
T
~N
01-Jan-97 <CN -en
-u 01-Jan-98 D) 0" :::s ~ Q.
0 01-Jan-99 -"'C
01-Jan-00 C" I N
01-Jan-01 .....
0
01-Jan-02 0 0
01-Jan-03 :::s
(')
(I)
01-Jan-04 -:::s -""'' 01-Jan-05 • D) -a·
01-Jan-06 -:::s tn
01-Jan-07 :::s
01-Jan-08 ~ < (I)
(Q
01-Jan-09 -(I) -D)
01-Jan-10 -a·
01-Jan-11 -:::s
01-Jan-12 -
01-Jan-13
01-Jan-14
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Certificate of Analysis
Report Date: May 28,2014
Company :
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Parameter
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North East
347128001
SOLID
16-APR-14 12:45
21-APR-14
Client
Qualifier Result Uncertainty __ ;;_
~ad Gas Flow Proportional Counting
JFPC, Pb210, Solid "As Received"
~ead-210 0.000199 +/-3.14E-06
JFPC, Total Alpha Radium, solid "As Received"
'otal Radium 9.90E-05 +/-1.01E-06
[he following Prep Methods were performed:
v1ethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Description
DOE RP280 Modified
EPA 900.1 Modified
;urrogate/Tracer Recovery
~ead Carrier
Test
GFPC, Pb210, Solid "As Received"
MDC
3.38E-06
3.91E-07
3arium Carrier GFPC, Total Alpha Radium, solid "As Received"
'llotes:
RL
1.00E-06
5.00E-08
Analyst
CXC1
::::ounting Uncertainty is calculated at the 68% confidence level ( 1-sigma) .
........
Project:
Client ID:
DNMI00101
DNMI001
Units DF Analyst Date Time Batch Method
uCi/kg
uCilkg
Date
04/22/14
Result
KSD1 05/27/14 1658 1385433
KSDI 05/27/14 1553 1385421
Time Prep Batch
1410 1382146
Analyst Comme-'-n_ts'-_
Nominal Recovery%
87.3
86.5
AcceEtable Limits
(25%-125%)
(25%-125%)
2
GEL LA BORA TORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Certificate of Analysis
Report Date: July 18,2014
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Parameter
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North East
350589001
Vegetation
10-JUN-14 08:45
13-JUN-14
Client
Qualifier Result Uncertainty -------'"--
{.ad Gas Flow Proportional Counting
}FPC, Pb210, Solid "As Received"
MDC
"ead-21 0 5.60E-05 +/-3.08E-06 7.12E-06
}FPC, Total Alpha Radium, solid "As Received"
'otal Radium 2.60E-05 +/-8.46E-07 9.19E-07
rhe following Prep Methods were perfo_rm_e.;_d.;_: __ ~-
V1ethod Description
)ry . Qil Prep Dry . oil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Description
DOE RP280 Modified
EPA 900.1 Modified
;urrogate/Tracer Recovery
"ead Carrier
3arium Carrier
'llotes:
Test
GFPC, Pb210, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
RL
\.OOE-06
5.00E-08
Analyst
KYW2
=::ounting Uncertainty is calculated at the 68% confidence level (1-sigma).
Project:
Client ID:
DNMI00101
DNMIOOI
Units DF Analyst Date Time Batch Method
uCi/kg
uCi/kg
Date
06/16/14
Result
TCI 07/16/14
TCI 07/15/14
Time Prep Batch
1756 1396221
Analyst Comments
Nominal Recovery~
113
93.1
0633 1396265
1636 1396264
Acceptable Limits
(25%-125%)
(25%-125%)
2
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Certificate of Analysis
Report Date: May 28,2014
Company :
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Parameter
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North West
347128002
SOLID
16-APR-14 13:15
21-APR-14
Client
Qualifier Result Uncertainty
~ad Gas Flow Proportional Counting
:JFPC, Pb210, Solid "As Received"
MDC
,ead-2!0 5.70E-05 +/-2.2lE-06 4.52E-06
]FPC, Total Alpha Radium, solid "As Received"
~otal Radium 2.53E-05 +/-6.29E-07 5.51E-07
rhe following Prep Methods were performed:
RL
l.OOE-06
5.00E-08
Vfethod De cription
)ry. II Pr.cp Dry Soil Prep GL-RAD-A-021
AnalysL --c""x=c(
The following Analytical Methods were performed:
\tlethod Description
DOE RP28-'--0 M-od-ifi-Jed
EPA 900.1 Modified
'UITogate/Tracer Recovery
,ead Carrier
3arium Carrier
~otes:
Test
GFPC, Pb21 0, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
:ounting Uncertainty is calculated at the 68% confidence level (1-sigma).
Project:
Client ID:
DNMI00101
DNMIOOl
Units DF Analyst Date Time Batch Method ----
uCilkg
uCi/kg
Date
04/22/14
Result
KSDl 05/27/14 1658 1385433
KSDl 05/27/14 1553 !385421
Time Prep Batch
----:1-:-4 '"""10,...-1382146
Anal st Comments
Nominal Recovery%
91.5
88.3
Acceptable Limits
(25%-!25%)
(25%-125%)
2
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Certificate of Analysis
Report Date: July 18,2014
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North West
350589002
Vegetation
10-JUN-14 08:15
13-JUN-14
Client
Parameter Qualifier Result Uncertainty
~ad Gas Flow Proportional Counting
}FPC, Pb210, Solid "As Received"
"ead-21 0 7.68E-05 +/-2.08E-06
}FPC, Total Alpha Radium, solid "As Received"
~otal Radium 2.53E-05 +/-5.55E-07
MDC
3.66E-06
5.77E-07
rhe following Prep Methods wer:..::.e..E.p:..::.e.:..:rfi:..:o.:..:rm=.:..ed=::...._ ______ _
\1ethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod De""s=-=cr~ip"-'t"-'io:..::n'-------
DOE RP280 Modified
EPA 900.1 Modified
;urrog~te/Tracer Recovery
"ead Carrier
3arium Carrier
'Jotes:
Test
GFPC, Pb210, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
RL
l.OOE-06
5.00E-08
Analyst
KYW2
:=ounting Uncertainty is calculated at the 68% confidence level (1-sigma).
Project:
Client ID:
DNMI00101
DNMI001
Units DF Analyst Date
uCi/kg
uCi/kg
Date
06/16/14
Result
TC1 07/16/14
TC1 07/15/14
Time Prep Batch
1756 1396221
Anal st Comments
Nominal Recovery%
114
96.7
Time Batch Method
0634 1396265
1636 1396264
Acceptable Limits
(25%-125%)
(25%-125%)
2
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Certificate of Analysis
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Parameter
Contact
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
South West
347128003
SOLID
16-APR-14 14:00
21-APR-14
Client
Qualifier Result Uncertainty
{ad Gas Flow Proportional Counting
:JFPC, Pb21 0, Solid "As Received"
MDC
"ead-21 0 0.000213 +/-5.93E-06 1.31E-05
:JFPC, Total Alpha Radium, solid "As Received"
'otal Radium 4.65E-05 +/-1.08E-06 7.35E-07
rhe following Prep Methods were performed:
vtethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Description
DOE RP280 Modified
EPA 900.1 Modified
;urr~ate/Tracer Recovery
"ead Carrier
3arium Carrier
'lotes:
Test
GFPC, Pb210, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
RL
l.OOE-06
5.00E-08
Analyst
CXCI
::::ounting Uncertainty is calculated at the 68% confidence level (1-sigma).
Report Date: May 28,2014
Project:
Client ID:
DNMI00101
DNMI001
Units OF Analyst Date Time Batch Method
uCi/kg
uCilkg
Date
04/22/14
Result
KSDl 05/27/14 1658 1385433
KSD1 05/27/14 1553 1385421 2
Time Prep Batch
1410 1382146
Analvst Comments
Nominal Recovery%
88.0
78.5
Acceptable Limit~
(25%-125%)
(25%-125%)
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www .gel. com
Certificate of Analysis
Report Date: July 18,2014
Company :
Address:
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
South West
350589003
Vegetation
10-JUN-14 07:45
13-JUN-14
Client
Project:
Client ID:
DNMI00101
DNMI001
Qualifier Result Uncertainty MDC RL Units DF Analyst Date Time Batch Method ------------------~----------~------------------------------Parameter
{ad Gas Flow Proportional Counting
]FPC, Pb210, Solid "As Received"
~ead-21 0 2.46E-05 +/-1.84E-06
:JFPC, Total Alpha Radium, solid "As Received"
~ota1 Radium 1.23E-05 +/-4.97E-07
fhe following Prep Methods were performed:
vtethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Description
DOE RP280 Modified
EPA 900.1 Modified
;urrogate/Tracer Recovery Test
~ead Carrier GFPC, Pb210, Solid "As Received"
4.63E-06
6.97E-07
~arium Carrier GFPC, Total Alpha Radium, solid "As Received"
~otes:
l.OOE-06
5.00E-08
Analyst
KYW2
:=ounting Uncertainty is calculated at the 68% confidence level (1-sigma).
uCi/kg
uCilkg
Date
06/16/14
Result
TC1 07/16/14 0634 1396265
TC1 07/15/14 1636 1396264 2
Time Prep Batch
1756 1396221
Analyst Comments
Nominal Recove~% Acc~table Limits
115 (25%-125%)
96.7 (25%-125%)
lij ij II Laboratories LLC
a member of The GEL Group INC PO Box 30712 Charleston, SC 29417
2040 Savage Road Charleston, SC 29407
P 843.556.8171 F 843.766.1178
May 22,2014
Ms. Kathy Weinel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
Work Order: 347128
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on April21, 2014. This original data report has been prepared and reviewed in accordance
with GEL's standard operating procedures.
Our policy is to provide high quality, personalized analytical services to enable you to meet your analytical needs
on time every time. We trust that you will fmd everything in order and to your satisfaction. If you have any
questions, please do not hesitate to call me at [phone], ext. 4505.
Purchase Order: DW16138
Enclosures
Sincerely,
Heather Shaffer
Project Manager
llll'lllllllllllllllllllllllllllll
www.gel.com
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 347128
Case Narrative
May 22,2014
Laboratory Identification:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 347128
Sample receipt: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on April21, 2014
for analysis. The samples were delivered with proper chain of custody documentation and signatures. All sample
containers arrived without any visible signs of tampering or breakage. There are no additional comments
concerning sample receipt.
Sample Identification: The laboratory received the following samples:
Laboratory ID Client ID
347128001 North East
347128002 North West
347128003 South West
Case Narrative:
Sample analyses were conducted using methodology as outlined in GEL's Standard Operating Procedures. Any
technical or administrative problems during analysis, data review, and reduction are contained in the analytical
case narratives in the enclosed data package.
The enclosed data package contains the following sections: Case Narrative, Chain of Custody, Cooler Receipt
Checklist, Data Package Qualifier Definitions and data from the following fractions: Radiochemistry.
Heather Shaffer
Project Manager
Chain of Custody and
Supporting
Documentation
Sheet 1 of 1
Samples Shipped to: Gel Laboratories Contact: Garrin Palmer ~2~0~40~S~av~a=g~e~R~o=a~d~--------------Ph:4356784115
Charleston, SC 29407 [e-mail]
Chain of Custody/Sampling Analysis Request
Project s amplers N a me s amp ers s· •gna~t,~re
Early Spring Vegetation I # ..__ ~ 2014 Garrin Palmer (:rvvv"
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
North East 4/16/2014 1245 Ra 226, PB 210
North West 4/16/2014 1315 Ra 226, PB 210
South West 4/16/2014 1400 Ra 226, PB 210
.. Please use caution when handling South West
samples. Some cactus included in the samples.
Comments:
Relinquished By:(Signature)
Garrin Palmer
Date/TimeR
4/16/2014
1200
Relinquished By:(Signature) Date/Time
-
m:3!1[ Laboratories u~c SAMPLE RECEIPT & REVIEW FORM
Client: 1~! \ I . SDG/ARICOC/Work Order: :Y-l 'l J L-)f
Received By: t 1~"1QU I (!'{ Date Received: 042 1/ll
I ~ ~ *If Net Counts> lOOcpm on samples not marked "radioactive", contact the Radiation Safety Group for further Suspected Hazard Information ;:.. ii_!.Yestigation.
COC/Samples marked as radioactive? /' Maximum Net Counts Observed* (Obs.crvttl Counts~ Area U<~ckgrountl Count$); (_,{ {-1V\.
Classified Radioactive II ol"ill by RSO? ../ 'fr )'CS, Were swipes taken of -sum1lle contatiners <action levels? I
COC/Samples marked containing PCBs? ""' _/
Package, CDC. and/or Samples marked as /
hc1~yllium 01 asbestos containing? / If yes, samples arc to be scgregeatecl as Safety Controlled Samples, and OIJened by the GEL Safety Group.
Shipped as a DOT Hazardous'! / fj';zard Class Shl.pllCd: UN#:
•. ~ruuruJ.W .. cdJts Forei1.m Sail? /
Sample Receipt Criteria ~ ~ 0 Conm1ents/Qualifiers (Required for Non-Conforming Items) ;:.. z
Shipping containers received intact I/ Circle Applicable:
1 Seals broken Damaged container Leaking container Other (describe) and sealed? / ~
Samples requiring cold preservation I~ I/ Preservation MeU10d: Ice bags Blue ice Dry ic~ (;~~Other (describe)
2 within (0 .::; 6 deg. C)?* / *all temperatures are recorded in 20
2a Daily check performed and passed on / Device Serial #: : k:irh~ ~ a.2f~L~rl/J
IR temperature gun? I/ Secondary Tempemture Device · .1• ~1.
3 Chain of custody documents included ~ with shipment?
Circle Applicable:
4 Sample containers intact and sealed? Seals broken Damaged container Leaking container Other (describe)
Samples requiring chemical l.,/'1/
Sample !D's, containers affected and observed pH:
5 preservation at proper pH? If Preservation added. Lol#:
VOA vials free of heads pace (defined ./ 1-Sample ID's and containers affected:
6 as < 6mm bubble)?
7 Are Encore containers present? I/
.~yes, immediately deliver to Volatiles laboratory)
Samples received within holding I D's and tests nffcct~d:
8 time? '
9 !Sample !D's on COC match llJ's on
bottles?
Date & time on COC match date & Sample ID's affected:
10 time on bottles?
Number of containers received match Sample ID's affected:
11 number indicated on COC?
12 Are sample containers identifiable as / 1,.....-
GEL provided?
13 COC form is properly signed in
relinquished/received sections?
Circle Applicable:
FcdEx Air FedEx Ground UPS Field Services Courier Other
!Z-/~{ ~l{y 02. Cf&Dlt 32.05
14 CatTier and tracking number. 97?9 ?Jqoq
901~ 57/'f
Comments (Use Continuation Form if needed):
( .
I t.-\ . « t.-.
~
t { ~f --r\---\ Dnlc~ 0-\_Lll'frage _j_, ·L l
PM (or PMA) review: Initials
~
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 347128 Early Spring Vegetation 2014
ClientSDG:
Project Manager:
Project Name:
Purchase Order:
Package Level:
EDD Format:
347128
Heather Shaffer
DNMI00101 Vegetation Analysis
DW16138
LEVEL3
EIM_DNMI
GELID Client Sample ID Client Sample Desc.
347128001 North East
347128002 North West
347128003 South West
Collect
Date & Time
16-APR-14 12:45
16-APR-14 13:15
16-APR-14 14:00
Work Order Due Date: 21-MAY-14
Package Due Date:
EDD Due Date:
Due Date:
HXS1
Receive Time #of
Date & Time Zone Cont.
21-APR-14 09:20 -2
21-APR-14 09:20 -2
21-APR-14 09:20 -2 1
18-MAY-14
20-MAY-14
21-MAY-14
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Report Date: 15-MAY-14
Work Order: 347128
Page 1 of 2
Collector: C
Prelogin #: 20140415619
Project Workdef ID: 1310529
SDG Status: Closed
Logged by:
Fax Days to
Due Date Process
30
30
30
CofC#
Prelog Lab Field
Group QC QC
Client Sample ID Status Tests/Methods
Product
Reference Fax Date PM Comments Aux Data
Receive
Codes
-001 North East
-002 North West
-003 South West
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
Product: LABCOMP _S Workdef ID: 1310628
Method:
In Product Group? No
Product Description: Laboratory Composite -Dry prep instructions
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
use caution when handling;
some cactus included in the
sample.
Group Name:
Client Matrix
Client Matrix
Client Matrix
Group Reference:
SOLID
SOLID
SOLID
Path: Rad Prep SPRP
Product Reference:
Moisture Correction: "As Received"
Client RDL or
PQL & Unit
Reporting
Units
Parm Included Included Custom
Function in Sample? in QC? List?
No
~
\
GEL Laboratories LLC -Login Review Report
Product: GFC_ PBS WorkdefiD: 1310600 In Product Group? No
Method: DOE RP280 Modified
Product Description: GFPC, Pb210, Solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS Workdef ID: 1310679 In Product Group? No
Method: EPA 900.1 Modified
Product Description: GFPC, Total Alpha Radium, solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Total Radium
Action Product Name Description
Contingent
Tests
Login Requirements:
Requirement
Are these vegetation sample?
Login Reminder?
Group Name:
Client RDL or
PQL & Unit
.000001
Group Name:
Client RDL or
PQL & Unit
.00000005
Samples
Reporting
Units
uCilkg
Reporting
Units
uCi/kg
Include? Comments
Group Reference:
Report Date: 15-MAY-14
Work Order:347128
Page 2 of 2
Path: Standard
Product Reference:
Moisture Correction: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y
Group Reference:
Path: Standard
Product Reference:
Yes
Moisture Correction: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
y
y
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry.
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry. Log
with lab comp.
Peer Review by: ____________ _ Work Order (SDG#), PO# Checked? ____ _ C of C signed in receiver location? _____ _
Laboratory
Certifications
List of current GEL Certifications as of 22 May 2014
State Certification
Alaska UST-110
Arkansas 88-0651
CLlA 4200904046
California NELAP 01151CA
Colorado SC00012
Connecticut PH-0169
Delaware SC000122013-10
DoD ELAP/ ISO 17025 A2LA 2567.01 -Florida NELAP E87156
Foreign Soils Permit P330-12-00283,P330-12-00284
Georgia SC00012 -Georgia SDWA 967 --Hawaii scooo 122013-10
Idaho Chemistry SC00012
Idaho Radiochemistry SC00012
Illinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332 -Kentucky 90129 ·-Louisiana NELAP 03046 (AI33904)
Louisiana SDWA LA130005
Maryland 270
Massachusetts M-SC012
Michigan 9976
Mississippi SC000122013-10
Nebraska NE -OS-26-13 -Nevada scooo 122014-1
New Hampshire NELAP 2054
New Jersey NELAP SC002
New Mexico SC00012 -New York NELAP 11501
North Carolina 233
-North Carolina SDWA 45709
Oklahoma 9904
Pennsylvania NELAP 68-00485
Plant Material Permit PDEP-12-00260
South Carolina Chemistry 10120001
South Carolina GVL 23611001
South Carolina Radiochemi 10120002
Tennessee TN 02934
TexasNELAP Tl04704235-14-9
Utah NELAP scooo 1220 13-11
Vermont VT87156
Virginia NELAP 460202
Washington C780-12
Wisconsin 999887790
Method/ Analysis Information
Radiochemistry Case Narrative
Energy Fuels Resources (DNMI)
SDG 347128
Product: GFPC, Total Alpha Radium, solid
Analytical Method: EPA 900.1 Modified
Prep Method: Dry Soil Prep
Analytical Batch Number:
Prep Batch Number:
1385421
1382146
SampleiD
347128001
347128002
347128003
1203081581
1203081582
1203081583
1203081584
Client ID
North East
North West
South West
Method Blank (MB)
347128002(North West) Sample Duplicate (DUP)
347128002(North West) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" basis.
SOP Reference
Procedure for preparation, analysis and reporting of analytical data are controlled by GEL Laboratories LLC as
Standard Operating Procedure (SOP). The data discussed in this narrative has been analyzed in accordance with
GL-RAD-A-010 REV# 15.
Calibration Information:
Calibration Information
All initial and continuing calibration requirements have been met.
Standards Information
Standard solutions for these analysis are NIST traceable or verified with a NIST traceable standard and used
before the expiration dates.
Sample Geometry
All counting sources were prepared in the same geometry as the calibration standards.
Quality Control (OC) Information:
Blank Information
The blank volume is representative of the sample volume in this batch.
Designated QC
The following sample was used for QC: 347128002 (North West).
QC Information
All of the QC samples meet the required acceptance limits with the following exceptions: The blank,
1203081581 (MB), did not meet the detection limit due to keeping the blank volume consistent with the other
sample aliquots. All other samples met the detection limits.
Technical Information:
Holding Time
All sample procedures for this sample set were performed within the required holding time.
Sample Re-prep/Re-analysis
None of the samples in this sample set required reprep or reanalysis.
Chemical Recoveries
All chemical recoveries meet the required acceptance limits for this sample set.
Recounts
None of the samples in this batch were recounted.
Miscellaneous Information:
Data Exception (DER) Documentation
Data exception reports are generated to document any procedural anomalies that may deviate from referenced
SOP or contractual documents. A data exception report (DER) was not generated for this SDG.
Sample-Specific MDAIMDC
The MD A/MDC reported on the certificate of analysis is a sample-specific MD A/MDC.
Additional Comments
Additional comments were not required for this sample set.
Qualifier Information
Manual qualifiers were not required.
Method/ Analysis Information
Product: GFPC, Pb210, Solid
Analytical Method: DOE RP280 Modified
Prep Method: Dry Soil Prep
Analytical Batch Number: 1385433
Prep Batch Number: 1382146
Sample ID Client ID
347128001
347128002
347128003
1203081601
1203081602
1203081603
1203081604
North East
North West
South West
Method Blank (MB)
347128002(North West) Sample Duplicate (DUP)
347128002(North West) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" basis.
SOP Reference
Procedure for preparation, analysis and reporting of analytical data are controlled by GEL Laboratories LLC as
Standard Operating Procedure (SOP). The data discussed in this narrative has been analyzed in accordance with
GL-RAD-A-018 REV# 13.
Calibration Information:
Calibration Information
All initial and continuing calibration requirements have been met.
Standards Information
Standard solutions for these analysis are NIST traceable or verified with a NIST traceable standard and used
before the expiration dates.
Sample Geometry
All counting sources were prepared in the same geometry as the calibration standards.
Quality Control (QC) Information:
Blank Information
The blank volume is representative of the sample volume in this batch.
Designated QC
The following sample was used for QC: 347128002 (North West).
QC Information
All of the QC samples meet the required acceptance limits with the following exceptions: The blank,
1203081601 (MB), did not meet the detection limit due to keeping the blank volume consistent with the other
sample aliquots. All other samples met the detection limits. The sample and the duplicate, 1203081602 (North
West) and 347128002 (North West), did not meet the relative percent difference requirement; however, they do
meet the relative error ratio requirement with value of 1. 71.
Technical Information:
Holding Time
All sample procedures for this sample set were performed within the required holding time.
Sample Re-prep!Re-analysis
None of the samples in this sample set required reprep or reanalysis.
Chemical Recoveries
All chemical recoveries meet the required acceptance limits for this sample set.
Recounts
Samples 1203081603 (North West) and 1203081604 (LCS) were recounted due to high recovery. The recounts
are reported.
Miscellaneous Information:
Data Exception (DER) Documentation
Data exception reports are generated to document any procedural anomalies that may deviate from referenced
SOP or contractual documents. A data exception report (DER) was not generated for this SDG.
Sample-Specific MDA/MDC
The MD A/MDC reported on the certificate of analysis is a sample-specific MD A/MDC.
Additional Comments
Additional comments were not required for this sample set.
Qualifier Information
Manual qualifiers were not required.
Certification Statement
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless otherwise noted in the analytical case narrative.
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Qualifier Definition Report
for
DNMIOOl Energy Fuels Resources (USA), Inc.
Client SDG: 347128 GEL Work Order: 347128
The Qualifiers in this report are defined as follows:
* A quality control analyte recovery is outside of specified acceptance criteria
** Analyte is a surrogate compound
U Analyte was analyzed for, but not detected above the CRDL.
Review/Validation
GEL requires all analytical data to be verified by a qualified data reviewer. In addition, all CLP-like deliverables
receive a third level review of the fractional data package.
The following data validator verified the information presented in this data report:
Signature: ~~-;1 ~
Date: 28 MAY 2014
Name: Theresa Austin
Title: Group Leader
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407-[phone] -www.gel.com
QC Summary
Contact:
Workorder:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado
Ms. Kathy Weinel
347128
Parmname
Rad Gas Flow
NOM Sample Qual QC
3atch 1385421
QC1203081582 347128002 DUP
Total Radium 2.53£-05
Uncertainty +/-6.29£-07
QC1203081584 LCS
Total Radium 0.000886
Uncertainty
QC1203081581 MB
Total Radium u
Uncertainty
QC1203081583 347128002 MS
Total Radium O.OOII 2.53£-05
Uncertainty +/-6.29£-07
3atch 1385433
QC 1203081602 347128002 DUP
Lead-210 5.70£-05
Uncertainty +/-2.21£-06
QC1203081604 LCS
Lead-210 0.00173
Uncertainty
QC1203081601 MB
Lead-210 u
Uncertainty
QC1203081603 347128002 MS
Lead-210 0.00212 5.70£-05
Uncertainty +/-2.21£-06
Notes:
Counting Uncertainty is calculated at the 68% confidence level (1-sigma).
The Qualifiers in this report are defined as follows:
**
<
>
Analyte is a surrogate compound
Result is less than value reported
Result is greater than value reported
The TIC is a suspected aldol-condensation product
2.83£-05
+/-6.38£-07
0.000797
+/-9.28£-06
-1.36£-07
+/-2.99£-07
0.00092
+/-I.OOE-05
8.08£-05
+/-2.55£-06
0.00202
+/-2.61£-05
2.78£-06
+/-2.98£-06
0.00258
+/-3.27£-05
Units
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
RPD%
11.3
34.5*
A
B
BD
c
D
F
H
For General Chemistry and Organic analysis 'the target analyte was detected in the associated blank.
Results are either below the MDC or tracer recovery is low
Analyte has been confirmed by GC/MS analysis
Results are reported from a diluted aliquot of the sample
Estimated Value
Analytical holding time was exceeded
Reoort Date: May 28, 2014
Page 1 of
REC% Range Anlst Date Time
(0%-20%) KSDI 05/27/14 15:5
89.9 (75%-125%) 05/27/14 16:2
05/27/14 15:5
81.3 (75%-125%) 05/27/14 15:5
(0%-20%) KSDI 05/27/14 16:5
]]6 (75%-125%) 05/28/14 ll:O
05/27/14 16:5
]]9 (75%-125%) 05/28/14 II :0
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407-[phone] -www.gel.com
QC Summary
Workorder: 347128
Parmname NOM Sample ual ~c Units RPD%
K Analyte present. Reported value may be biased high. Actual value is expected to be lower.
L Analyte present. Reported value may be biased low. Actual value is expected to be higher.
M M if above MDC and less than LLD
M Matrix Related Failure
N/A RPD or %Recovery limits do not apply.
See case narrative
Analyte concentration is not detected above the detection limit
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
One or more quality control criteria have not been met. Refer to the applicable narrative orDER.
Sample results are rejected
Analyte was analyzed for, but not detected above the CRDL.
Gamma Spectroscopy--Uncertain identification
Gamma Spectroscopy--Uncertain identification
REC% Range Anlst
Nl
NO
NJ
Q
R
u
Ul
UJ
UL
X
y
Not considered detected. The associated number is the reported concentration, which may be inaccurate due to a low bias.
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
1\
h
QC Samples were not spiked with this compound
RPD of sample and duplicate evaluated using +/-RL. Concentrations are <5X the RL. Qualifier Not Applicable for Radiochemistry.
Preparation or preservation holding time was exceeded
Page 2 of
Date Time
N/A indicates that spike recovery limits do not apply when sample concentration exceeds spike cone. by a factor of 4 or more or %RPD not applicable.
1\ The Relative Percent Difference (RPD) obtained from the sample duplicate (DUP) is evaluated against the acceptance criteria when the sample is greater than
five times (5X) the contract required detection limit (RL). In cases where either the sample or duplicate value is less than 5X the RL, a control limit of +I-the
RL is used to evaluate the DUP result. * Indicates that a Quality Control parameter was not within specifications.
For PS, PSD, and SOIL T results, the values listed are the measured amounts, not final concentrations.
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless qualified on the QC Summary.
[ij#ul Laboratories LLc
a member of The GEL Group INC PO Box 30712 Charleston, SC 29417
2040 Savage Road Charleston, SC 29407
P 843.556.8171 F 843.766.1178
July 18,2014
Ms. Kathy Weinel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
Work Order: 350589
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on June 13,2014. This original data report has been prepared and reviewed in accordance
with GEL's standard operating procedures.
Our policy is to provide high quality, personalized analytical services to enable you to meet your analytical needs
on time every time. We trust that you will find everything in order and to your satisfaction. If you have any
questions, please do not hesitate to call me at [phone], ext. 4505.
Purchase Order: DW16138
Enclosures
Sincerely.
Heather Shaffer
Project Manager
www.gel.com
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 350589
Case Narrative
July 18, 2014
Laboratory Identification:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 350589
Sample receipt: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on June 13,2014
for analysis. The samples were delivered with proper chain of custody documentation and signatures. All sample
containers arrived without any visible signs of tampering or breakage. There are no additional comments
concerning sample receipt.
Sample Identification: The laboratory received the following samples:
Laboratory ID Client ID
350589001 North East
350589002 North West
350589003 South West
Case Narrative:
Sample analyses were conducted using methodology as outlined in GEL's Standard Operating Procedures. Any
technical or administrative problems during analysis, data review, and reduction are contained in the analytical
case narratives in the enclosed data package.
The enclosed data package contains the following sections: Case Narrative, Chain of Custody, Cooler Receipt
Checklist, Data Package Qualifier Definitions and data from the following fractions: Radiochemistry.
Heather Shaffer
Project Manager
Chain of Custody and
Supporting
Documentation
3~589
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: Gel Laboratories Contact: Garrin Palmer
~2~0~40~S-av_a_g_e~R~o-a-d~--------------Ph:4356784115
Charleston, SC 29407 [e-mail]
Chain of Custody/Sampling Analysis Request
p . roJect S -I N amp1ers arne s amp ers s· t 1gna ure
Late Spring Vegetation I G-c~P~ 2014 Garrin Palmer
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
North East 6/10/2014 5571 Ra 226, PB 210
North West 6/10/2014 5220 Ra 226l PB 210
South West 6/10/2014 4950 Ra 226, PB 210
* Please use caution when handling South West
samples. Some cactus included in the samples.
Comments:
Rennquished By:(Signature) Datemme Received By:{Signature) Date/Tfme
Garrin PalmL 6/10/2014 C1rr (6 .. J3 ·J•-"(
&~"R 1000 0'/10
Relinquished By:(Signature) Date/Time Recei~ed By:(Signature) Datemme
<
m3) /Laboratories Lt.c SAMPLE RECEIPT & REVIEW FORM
Client: Df'\ffi\ SDG/ARJCOC/Work Order: 3Sos~
Received By: uP Date Received: u-1.3· Jl.{
Suspected Hazard Information ., Q "'IfNet Counts> IOOcpm on samples not marked "radioactive", contact the Radiation Safety Group for further ~ z investigation .
COC/Samples marked as radioactive? ./ Maximum Net Counts Observed• (Observed Counts-Area Background Counts): OcaY\
Classified Radioactive II or Ill by RSO? v If yes, Were swipes taken of sample contatiners <action levels? I
COC/Samples marked containing PCBs? /
Package, COC, and/or Samples marked as I/ beryllium or asbestos containing? If yes, samples are to be scgrogcllled.as Sarcty Controlled Snmplcs, and opened by the GEL Safety Group.
Shipped as a DOT Hazardous? i/ ~azard Class Shipped: UN#:
Samples identified as Foreign Soil? i/
Sample Receipt Criteria :E ~ ~ Comments/Qualifiers (Required for Non-Conforming Items)
Shipping containers received intact ,V Circle Applicable:
1 Seals broken Damaged container Leaking container Other (describe) and sealed? ...-""'h
Samples requiring cold preservation I--Preservation Method: Ice bags Blue ice Dry ice Ce~~ther (describe)
2
within (0 < 6 deg. C)?"' / (~ •all temperatures are recorded in
2a I Daily check performed and passed on (I-11 DeviceSerialll: ~~al !~~Lt l
IIR temperature gun? Secondary Temperature Device
3 Chain of custody documents included J with shipment?
Circle Applicable:
4 Sample containers intact and sealed? Seals broken Damaged container Leaking container Other (describe) •
5 Samples requiring chemical
/
S3mplc !D's, containers affected and observed pH:
preservation at proper pH? lfrtn.ntld~•l LtiW'
VOA vials free ofheadspace (defined /~ Sample !D's nnd containers affected:
6 as< 6mm bubble)?
pfyes, ;mmP<HotPiv deliver to Volatiles oaooraroryJ
7 Are Encore containers present? I/
Samples received within holding ID'sandtes~affected:
8 time? .I
Sample ID's on COC match ID's on I Sample: !D's and containers affected:
9 oomes?
Date & time on CDC match date & Sample I'D's uffectcd:
10 time on bottles? / ··tl'ff\1 OY\ C-lW'\tcU ~~ sw 014$ t\lW t'l~ IS .vE'~ ~
Number of containers received match I Sample !D's affected:
11 number indicated on COC? ID 1"'\V'\.P V).ef
Are sample containers identifiable as ' 12 I GEL provided?
13 COC form is properly signed in /I relinquished/received sections? --~FolE<Gro'"d Cir~Iicable:
PS Field Services Courier Other
g(-> qot~ qq3( Iz_ 187 l/~Y 12
14 Carrier and tracking number. qoyq 27~2 I (
I l 9Lf '2lo 21S3
(Use Continuation Form if needed):
PM (or PMA) review: Initials '--»P Date l.o-J1~JU Page_j r__j_ v
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 350589
Client SDG: 350589
Project Manager:
Project Name:
Purchase Order:
Package Level:
EDD Format:
Heather Shaffer
DNMI00101 Vegetation Analysis
DW16138
LEVEL3
EIM_DNMI
GELID Client Sample ID Client Sample Desc.
350589001 North East
350589002 North West
350589003 South West
Collect
Date & Time
10-JUN-14 08:45
10-JUN-14 08:15
10-JUN-14 07:45
Work Order Due Date: 21-JUL-14
Package Due Date:
EDD Due Date:
Due Date:
HXT1
Receive Time #of
Date & Time Zone Cont.
13-JUN-14 09:20 -2
13-JUN-14 09:20 -2
13-JUN-14 09:20 -2
18-JUL-14
20-JUL-14
21-JUL-14
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Report Date: 18-JUL -14
Work Order: 350589
Page 1 of 2
Collector: C
Prelogin #: 20140617731
Project Workdef ID: 1310529
SDG Status: Closed
Logged by:
Fax Days to
Due Date Process
30
30
30
CofC#
Prelog Lab Field
Group QC QC
Client Sample ID Status Tests/Methods
Product
Reference Fax Date PM Comments Aux Data
Receive
Codes
-001 North East
-002 North West
-003 South West
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
Product: LABCOMP _S Workdef ID: 1310628
Method:
In Product Group? No
Product Description: Laboratory Composite -Dry prep instructions
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Group Name:
Client RDL or
PQL& Unit
Cooler Seal Undisturbed
Temperature (C)
Cooler Seal Undisturbed
Temperature (C)
Cooler Seal Undisturbed
Temperature (C)
Group Reference:
y
19
y
19
y
19
Path: Rad Prep SPRP
Product Reference:
Moisture Correction: "As Received"
Reporting
Units
Parm Included Included Custom
Function in Sample? in QC? List?
'No
GEL Laboratories LLC -Login Review Report
Product: GFC_ PBS Workdef ID: 1310600 In Product Group? No
Method: DOE RP280 Mod ified
Product Description: GFPC, Pb210, Solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS WorkdefiD: 1310679 In Product Group? No
Method: EPA 900.1 Modified
Product Description:: GFPC, Total Alpha Radium, solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Total Radium
Action Product Name Description
Contingent
Tests
Login Requirements:
Requirement
Are these vegetation sample?
Login Reminder?
Group Name:
Client RDL or
PQL & Unit
.000001
Group Name:
Client RDL or
PQL & Unit
.00000005
Samples
Group Reference:
Report Date: 18-JUL-14
Work Order: 350589
Page 2 of 2
Path: Standard
Product Reference:
Moisture Correction: "As Received"
Reporting Parm Included Included Custom
Units Function in Sample? in QC? List?
uCilkg REG y y Yes
Group Reference:
Path: Standard
Product Reference:
Moisture Correction: "As Received"
Reporting Parm Included Included Custom
Units Function in Sample? in QC? List?
uCi/kg REG y y Yes
Include? Comments
y
y
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry.
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry. Log
with lab comp.
Peer Review by: ___________ _ Work Order (SDG#), PO# Checked? ____ _ C of C signed in receiver location? _____ _
Laboratory
Certifications
List of current GEL Certifications as of 18 July 2014
State I Certification l
Alaska I UST-110 I
Arkansas 88-0651 ·-' CLIA 42D0904046
California NELAP 01151CA
Colorado SC00012 -Connecticut PH-0169
Delaware scooo 122013-10
DoD ELAP/ ISO 17025 A2LA 2567.01
Florida NELAP E87156
Foreign Soils Permit P330-12-00283,P330-12-00284
Georgia SC00012
Georgia SDWA 967
Hawaii scooo 122013-10
Idaho Chemistry SC00012
Idaho Radiochemistry SC00012
lllinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332
Kentucky 90129
Louisiana NELAP 03046 (AI33904)
Louisiana SDWA LA130005
Maryland 270
Massachusetts M-SCOI2
Michigan 9976
Mississippi SC000122013-10
Nebraska NE-OS-26-13
Nevada scooo 122014-1
New Hampshire NELAP 2054
New Jersey NELAP SC002
New Mexico SCOOOI2
New YorkNELAP 11501
North Carolina 233
North Carolina SDWA 45709 r-Oklahoma 9904
Pennsylvania NELAP 68-00485
Plant Material Permit PDEP-12-00260
South Carolina Chemistry 10120001
South Carolina GVL 23611001
South Carolina Radiochemi 10120002
Tennessee TN 02934
TexasNELAP T104704235-14-9
UtahNELAP scooo 122014-13
Vermont VT87156
Virginia NELAP 460202
Washington C780-12
Wisconsin 999887790
. "'
Method/ Analysis Information
Radiochemistry Case Narrative
Energy Fuels Resources (DNMI)
SDG 350589
Product: GFPC, Total Alpha Radium, solid
Analytical Method: EPA 900.1 Modified
Prep Method: Dry Soil Prep
Analytical Batch Number: 1396264
Prep Batch Number: 1396221
Sample ID
350589001
350589002
350589003
1203110048
1203110049
1203110050
1203110051
Client ID
North East
North West
South West
Method Blank (MB)
350589001(North East) Sample Duplicate (DUP)
350589001(North East) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" basis.
SOP Reference
Procedure for preparation, analysis and reporting of analytical data are controlled by GEL Laboratories LLC as
Standard Operating Procedure (SOP). The data discussed in this narrative has been analyzed in accordance with
GL-RAD-A-010 REV# 15.
Calibration Information:
Calibration Information
All initial and continuing calibration requirements have been met.
Standards Information
Standard solutions for these analysis are NIST traceable or verified with a NIST traceable standard and used
before the expiration dates.
Sample Geometry
All counting sources were prepared in the same geometry as the calibration standards.
Quality Control <QC) Information:
Blank Information
The blank volume is representative of the sample volume in this batch .
Designated QC
The following sample was used for QC: 350589001 (North East).
QC Information
All of the QC samples meet the required acceptance limits with the following exceptions: The blank,
1203110048 (MB), did not meet the detection limit due to keeping the blank volume consistent with the other
sample aliquots. All other samples met the detection limits. The blank, 1203110048 (MB), result is greater than
the required detection limit but less than the MDC.
Technical Information:
Holding Time
All sample procedures for this sample set were performed within the required holding time.
Sample Re-prep/Re-analysis
None of the samples in this sample set required reprep or reanalysis.
Chern ical Recoveries
All chemical recoveries meet the required acceptance limits for this sample set.
Recounts
None of the samples in this sample set were recounted.
Miscellaneous Information:
Data Exception (DER) Documentation
Data exception reports are generated to document any procedural anomalies that may deviate from referenced
SOP or contractual documents. A data exception report (DER) was not generated for this SDG.
Sample-Specific MDA!MDC
The MD A/MDC reported on the certificate of analysis is a sample-specific MD A/MDC.
Additional Comments
Additional comments were not required for this sample set.
Qualifier Information
Manual qualifiers were not required.
Method/Analysis Information
Product: GFPC, Pb210, Solid
Analytical Method: DOE RP280 Modified
Prep Method: Dry Soil Prep
Analytical Batch Number: 1396265
Prep Batch Number: 1396221
Sample ID
350589001
350589002
350589003
1203110052
1203110053
1203110054
1203110055
Client ID
North East
North West
South West
Method Blank (MB)
35058900l(North East) Sample Duplicate (DUP)
350589001(North East) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" basis.
SOP Reference
Procedure for preparation, analysis and reporting of analytical data are controlled by GEL Laboratories LLC as
Standard Operating Procedure (SOP). The data discussed in this narrative has been analyzed in accordance with
GL-RAD-A-018 REV# 13.
Calibration Information:
Calibration Information
All initial and continuing calibration requirements have been met.
Standards Information
Standard solutions for these analysis are NIST traceable or verified with a NIST traceable standard and used
before the expiration dates.
Sample Geometry
All counting sources were prepared in the same geometry as the calibration standards.
Ouality Control (QC) Information:
Blank Information
The blank volume is representative of the sample volume in this batch.
Designated QC
The following sample was used for QC: 350589001 (North East).
QC Information
All of the QC samples meet the required acceptance limits with the following exceptions: The blank,
1203110052 (MB), did not meet the detection limit due to keeping the blank volume consistent with the other
sample aliquots. All other samples met the detection limits. The blank 1203110052 (MB) result is greater than
the required detection limit but less than the MDC.
Technical Information:
Holding Time
All sample procedures for this sample set were performed within the required holding time.
Sample Re-prep!Re-analysis
None of the samples in this sample set required reprep or reanalysis.
Chemical Recoveries
All chemical recoveries meet the required acceptance limits for this sample set.
Recounts
None of the samples in this sample set were recounted.
Miscellaneous Information:
Data Exception (DER) Documentation
Data exception reports are generated to document any procedural anomalies that may deviate from referenced
SOP or contractual documents. A data exception report (DER) was not generated for this SDG.
Sample-Specific MDA/MDC
The MD A/MDC reported on the certificate of analysis is a sample-specific MD A/MDC.
Additional Comments
Additional comments were not required for this sample set.
Qualifier Information
Manual qualifiers were not required.
Certification Statement
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless otherwise noted in the analytical case narrative.
,.. ....
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407-[phone] -www.gel.com
Qualifier Definition Report
for
DNMIOOl Energy Fuels Resources (USA), Inc.
Client SDG: 350589 GEL Work Order: 350589
The Qualifiers in this report are defined as follows:
* A quality control analyte recovery is outside of specified acceptance criteria
** Analyte is a surrogate compound
U Analyte was analyzed for, but not detected above the CRDL.
ReviewN alidation
GEL requires all analytical data to be verified by a qualified data reviewer. In addition, all CLP-like deliverables
receive a third level review of the fractional data package.
The following data validator verified the information presented in this data report:
Signature: ~~ Name: Kate Gellatly
Date: 18 JUL 2014 Title: Analyst I
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407-[phone] -www.gel.com
Contact:
Workorder:
Parmname
Rad Gas Flow
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado
Ms. Kathy Weinel
350589
NOM
3atch 1396264
QC1203110049 350589001 DUP
Total Radium 2.60E-05
Uncertainty +/-8.46E-07
QC1203110051 LCS
Total Radium 0.00104
Uncertainty
QCI203110048 MB
Total Radium
Uncertainty
QC1203110050 350589001 MS
Total Radium 0.0023 2.60E-05
Uncertainty +/-8.46£-07
3atch 1396265
QC1203110053 350589001 DUP
Lead-210 5.60E-05
Uncertainty +/-3.08£-06
QC1203110055 LCS
Lead-210 0.00202
Uncertainty
QCI203110052 MB
Lead-210
Uncertainty
QC1203110054 350589001 MS
Lead-210 0.00442 5.60E-05
Uncertainty +/-3.08£-06
Notes:
QC Summary
QC Units
2.35E-05 uCi/kg
+/-8.07£-07
0.000855 uCi/kg
+/-1.06E-05
u 3.62E-07 uCi/kg
+/-1 .53E-07
0.00182 uCi/kg
+/-1.96£-05
4.87E-05 uCilkg
+/-2.75£-06
0.00222 uCi/kg
+/-3 .08£-05
u 2.41E-06 uCi/kg
+/-1 .56£-06
0.00486 uCi/kg
+/-6.11 E-05
Counting Uncertainty is calculated at the 68% confidence level (!-sigma).
The Qualifiers in this report are defined as follows:
**
<
>
Analyte is a surrogate compound
Result is less than value reported
Result is greater than value reported
The TIC is a suspected aldol-condensation product
RPD%
10.0
13.9
A
B
BD
c
D
F
H
For General Chemistry and Organic analysis the target analyte was detected in the associated blank.
Results are either below the MDC or tracer recovery is low
Analyte has been confirmed by GCIMS analysis
Results are reported from a diluted aliquot of the sample
Estimated Value
Analytical holding time was exceeded
Reoort Date: July 18, 2014
Page 1 of
REC% Ran e An-=ls..:...t __ D=at:..:.e__;:T...;cim==-e
(0%-20%) TCI 07/15/14 16:3
82.4 (75%-125%) 07/15/14 16:3•
07/15/14 16:3·
77.9 (75%-125%) 07/15/14 16:3·
(0%-20%) TCl 07/16114 06:J
110 (75%-125%) 07/16/14 06:3'
07/16/14 06:3·
109 (75%-125%) 07116/14 06:J
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407-[phone] -www.gel.com
QC Summary
Workorder: 350589
Parmname NOM Sample Qual QC Units RPD%
K Analyte present. Reported value may be biased high. Actual value is expected to be lower.
L Analyte present. Reported value may be biased low. Actual value is expected to be higher.
M M if above MDC and less than LLD
M Matrix Related Failure
N/A RPD or %Recovery limits do not apply.
See case narrative
Analyte concentration is not detected above the detection limit
Nl
ND
NJ Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
One or more quality control criteria have not been met. Refer to the applicable narrative orDER.
Sample results are rejected
Analyte was analyzed for, but not detected above the CRDL.
Gamma Spectroscopy--Uncertain identification
Gamma Spectroscopy--Uncertain identification
REC%
Q
R
u
UI
UJ
UL
X
y
Not considered detected. The associated number is the reported concentration, which may be inaccurate due to a low bias.
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
QC Samples were not spiked with this compound
Anlst
1\
h
RPD of sample and duplicate evaluated using +/-RL. Concentrations are <5X the RL. Qualifier Not Applicable for Radiochemistry.
Preparation or preservation holding time was exceeded
Page 2 of
Date Time
N/A indicates that spike recovery limits do not apply when sample concentration exceeds spike cone. by a factor of 4 or more or %RPD not applicable.
1\ The Relative Percent Difference (RPD) obtained from the sample duplicate (DUP) is evaluated against the acceptance criteria when the sample is greater than
five times (5X) the contract required detection limit (RL). In cases where either the sample or duplicate value is less than 5X the RL, a control limit of+/-the
RL is used to evaluate the DUP result. * Indicates that a Quality Control parameter was not within specifications.
For PS, PSD, and SDIL T results, the values listed are the measured amounts, not final concentrations.
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless qualified on the QC Summary.
ATTACHMENT G
STACK SAMPLE LABORATORY RESULTS
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
January 30, 2014
FIRST QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
SOUTH YELLOW CAKE SCRUBBER
YELLOW CAKE DRYER BAGHOUSE
BLANDING, UTAH
January 14-15, 2014
by:
TETCO
391 East 620 South
American Fork, UT 84003
Phone [phone]
Fax [phone] fax
.·
'· l
.,
1
-'
' . il: .. ~ ·~ 1. •
CERTIFICATION OF REPORT INTEGRITY
Technical Emissions Testing Company (TETCO) certifies that this report represents the truth as
well as can be derived by the methods employed. Every effort was made to obtain accurate and
representative data and to comply with procedures set forth in the Federal Register.
Dean Kitchen
Reviewer: /b~ c?' ~ ---------;rp~==~~~?~~=-----
Date: ______ !_-~):_,_9_----4--,J-ri--
Reviewer: _ _,_~....:..._....--_.fh_· _________
0
_
0
u_g_
0
_
1
s-en
Date:_......:....\ \.:....:....;--+v\-.!1~-----
ii
..
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ......................................................................................................................... 1
Test Location and Type of Process ...................................................................................... 1
Test Dates ............................................................................................................................. I
Pollutants Tested and Methods Applied .............................................................................. }
Test Participants ................................................................................................................... 2
Deviations from EPA Methods ............................................................................................ 2
Quality Assurance ................................................................................................................ 2
Summary of Results
Emission Results .................................................................................................................. 3
Process Data ......................................................................................................................... 3
Description of Collected Samples ....................................................................................... .3
Discussion of Errors or Irregularities ................................................... , ....... , ....................... 3
Percent Isokinetics ............................................................................................................... 4
Source Operation
Process Control Devices Operation ..................................................................................... 5
Process Representativeness ............................................................................................ ' ........ 5
Sampling and Analysis Procedures
Sampling Port Location ....................................................................................................... 6
Sampling Point Location ...................................................................................................... 6
Sampling Train Description ................................................................................................. 6
Sampling and Analytical Procedures ................................................................................... 7
Quality Assurance ................................................................................................................ ?
Appendices
A: Complete Results and Sample Calculations
B: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
iii
LIST OF TABLES
Table
I Measured Radionuclide Emissions ..................................................................................... .3
II Percent Isokinetics ................................................................................................................ 4
III Sampling Point Location ...................................................................................................... 6
IV Complete Results, South Yell ow Cake Scrubber .............................................. Appendix A
V Complete Results, Yell ow Cake Dryer Baghouse ............................................. Appendix A
LIST OF FIGURES
Figure
1 Facility Schematic Representation South Yellow Cake Scrubber ..................... Appendix D
2 Facility Schematic Representation Yellow Cake Dryer Baghouse .................... Appendix D
3 Schematic of Method 5/114 Sampling Train ..................................................... Appendix E
iv
INTRODUCTION
Test Purpose
This test project was conducted to determine the total radionuclide emissions from the South
Yell ow Cake Scrubber and the Yell ow Cake Dryer Baghouse exhausts in terms of Curies per dry
standard cubic foot (Ci/dscf).
These tests were for U-Nat only.
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Uranium ore is
processed into yellow cake, which is shipped to other facilities for additional processing. There
are two yellow cake dryers with individual scrubbers. Both dryer enclosures discharge into the
Yellow Cake Dryer Baghouse. The packaging enclosure also discharges into the Yellow Cake
Dryer Baghouse. The South Yellow Cake (SYC) dryer was the only operating dryer at the time
ofthe test. The North Yellow Cake dryer is currently not operational. The Grizzly Baghouse
serves as the main dust control device for the raw ore unloading and conveying to the processing
building.
Stack schematics are shown as Figures 1 and 2 in Appendix D.
Test Dates
The first test run on the SYC Scrubber was completed January 14, 2014 and the second run on
January 15,2014.
One run was completed on the Yellow Cake Dryer Baghouse January 15, 2014.
Pollutants Tested and Methods Applied
The tests were a determination ofradionuclide emissions in accordance with EPA Method 5/114.
Test run filters and front wash residues were sent to Test America located in Richland,
Washington for radionuclide analysis.
Test Participants
Test Facility
State Agency
TETCO
:
Garrin Palmer
None
Doug Olsen
Jeff Graton
Deviations From EPA Methods
None.
Quality Assurance
Mike McNamara
Testing procedures and sample recovery techniques were according to those outlined in the
Federal Register and the Quality Assurance Handbook for Air Pollution Measurement Systems.
2
SUMMARY OF RESULTS
Emission Results
Table I presents the findings of the test in Curies per dry standard cubic foot. Tables IV-VI in
Appendix A have more detailed information.
Table I. Measured Radionuclide Emissions
Run#
1
2
AVE
Process Data
South Yell ow Cake Scrubber
pCi/dscf
7.17
7.80
7.49
pCilhr
5.921E +05
6.748E+05
6.334E+OS
Yell ow Cake Dryer Baghouse
pCi/dscf pCilhr
27.92 6.596E+06
27.92 6.596E+06
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Scrubber water flow, pressure drop readings (..::lp)
were recorded and are found in Appendix D. The Dryer Baghouse pressure drop readings (..::lp)
were recorded and are found on the test run sheets. Production data will be submitted by Energy
Fuels Resources.
Description of Collected Samples
The test filters for the South Yell ow Cake Scrubber were heavily covered with a white colored
particulate. The front washes were cloudy in appearance.
The test filters for the Yell ow Cake Dryer Baghouse were lightly colored with a tan colored
particulate. The front wash was clear in appearance.
Discussion of Errors or Irregularities
None
3
Percent Isokinetic Sampling
Each test run was isokinetic within the ±10% of 100% criterion specified in the Federal Register.
Isokinetic values for each test run are presented in Table II.
Table II. Percent Isokinetic Sam
Run#
2
South Yell ow Cake
Scrubber
99
99
4
Yell ow Cake Dryer
Baghouse
97
.-., • • • T
L ·, . ·.·-
• ' • 4 ~ ~--·--.. --···-_....__
SOURCE OPERATION
Process Control Devices Operation
All process control devices were operated normally. Recorded scrubber water flow, pressure and
baghouse ~p readings were recorded and are found on the test run sheets or in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND ANALYSIS PROCEDURES
Sampling Port Location
The inside diameter ofthe South Yellow Cake Scrubber stack is 12.75 inches. The two, four-inch
diameter sample port are located 28.24 diameters (30 feet) downstream from the last disturbance
and 6.59 diameters (7 feet) upstream from the next disturbance. Figure 1 in Appendix Dis a
schematic of the stack.
The inside diameter of the Yellow Cake Dryer Baghouse stack is 16.0 inches. The two, four-inch
diameter sample ports are located 28.38 diameters (454 inches) downstream from the last
disturbance and 3.56 diameters (57 inches) upstream from the next disturbance. The sample port
locations are depicted in Figure 2 in Appendix D.
Sampling Point Location
Table III shows the distance of each sampling point from the inside wall according to EPA
Method 1. Each point is marked and identified with a wrapping of glass tape and numbered.
These points are determined by measuring the distance from the inside wall.
Distance (inches) from Inside Wall
Sample Point SYC Scrubber Dryer Baghouse
1
2
3
4
5
6
Sampling Train Description
0.85
3.19
9.56
11.90
[-. .
t . ~~,~-·, --r•· ,-~·~~ 1' •• ·j/
::..:. ... _----.__ --·.:.
0.70
2.34
4.74
11.26
13.66
15.30
To determine the actual emission rates for this stack, 40 CFR 60, Appendix A, Methods 1-51114
were followed.
All sampling trains were made of inert materials, (Teflon, stainless steel and glass) to prevent
interference ofthe sampled gas and particulate. The stack analyzers used to conduct Methods 1-
6
5/114 are constructed to meet the specifications outlined in the CFR. The temperature sensors are
K-type thermocouples. Heater, vacuum and pitot line cmmections have been designed to be
interchangeable with all units used by the tester. A 316 stainless steel probe liner was used for the
tests. Figure 4 in Appendix Eisa sketch of the Methods 5/114 sampling train.
Sample boxes were prepared for testing by following the prescribed procedures outlined in
Methods 5/114.
Sampling and Analytical Procedures
All sampling and analytical test procedures were as specified in 40 CFR 60, Appendix A,
Methods 5/114.
Quality Assurance
All equipment setup, sampling procedures, sample recovery and equipment calibrations were
carried out according to the procedures specified in 40 CFR 60 and the Quality Assurance
Handbook for Air Pollution Measurement Systems.
7
APPENDIX
A: Complete Results and Sample Calculations
B: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
8
APPENDIX A
Table IV Complete Results, South Yellow Cake Scrubber
Table V Complete Results, Yellow Cake Dryer Baghouse
Nomenclature
Sample Equations
A
• SVC Scrubbor .. ~ TABLE IV ..
• .J. COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UTAH
SOUTH YELLOWCAKE SCRUBBER EXHAUST
Symbol Descrietion Dimensions Run #J Run #2
Date 1/14/2014 1/15/2015
Filter# 6108 6112
Begin Time Test Began 9:55 7:49
End Time Test Ended 18:17 16:11
Pbm Meter Barometric Pressure ln. Hg. Abs 24.75 24.75
.1-H Orifice Pressure Drop ln. H20 1.518 1.707
y Meter Calibration Y Factor dimensionless 1.002 1.002
Vm Volume Gas Sampled-Meter Conditions cf 377.457 395.092
Tm Avg Meter Temperarure "F 84.9 85.4
V.1.P Sq Root Velocity Head Root in H20 0.5517 0.5842
Wt.vc Weight Water Collected Grams 421.6 498.8
T, Duration ofT est Minutes 480 480
cp Pita! Tube Coefficient Dimensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.2755 0.2755
C02 Volume %Carbon Dioxide Percent 1.10 2.00
02 Volume% Oxygen Percent 18.90 18.00
N2 &CO Volume% Nitrogen and Carbon Monoxide Percent 80.00 80.00
Ymsrd Volume Gas Sampled (Standard) dscf 304.524 318.637
Vw Volume Water Vapor scf 19.878 23.518
B W s (measured) Frnction H20 in Stack Gas (Measured) Fraction 0.061 0.069
Bws (saturated) Fraction H20 in Stack Gas (Saturated) Fraction 0.084 0.090
Bw. Fraction H10 in Stack Gas * Fraction 0.061 0.069
xd Fraction of Dry Gas Fraction 0.939 0.931
Md Molecular Wt. Dry Gas lbllbmol 28.93 29.04
M. Molecular Wt. Stack Gas lbllbmol 28.26 28.28
%1 Percentlsokinetic Percent 98.8 98.6 AVG
T. Avg Stack Temperature OF 102.5 104.5 103.5
As Stack Cross Sectional Area Sq. Ft. 0.887 0.887
Po Stack Static Pressure ln. H20 -0.310 -0.310
PbP Sample Pon Barometric Pressure ln. Hg Abs 24.68 24.68
P. Stack Pressure ln. Hg. Abs 24.657 24.657
Q. Stack Gas Volumetric Flow Rate (Sid) dscfin 1.38E+03 1.44E+03 1.4IE+03
Q. Stack Gas Volumetric Flow Rate (Actual) cfin 1.89E+03 2.01E+03 1.95E+03
v. Velocity of Stack Gas fpm 2.14E+03 2.26E+03 2.20E+03
Curies Radionuclides per sample pCi 2184.5 2485.2
Crad Concentration of Radio nuclides pCi/dscf 7.173 7.799 7.486
ERrad Emission Rate ofRadionuclides pCi/hr 5.921E+05 6.748E+05 6.334E+05
* If the measured moisture content is greater than the saturated moisture level (supersaturated),
the saturated moisture value will be used in all calculations (40 CFR 60, Method 4, Section 12. I. 7).
Symbol
Date
Filter#
Begin
End
Pbm
ilH
y
Vm
Tm
.YilP
Wfwc
T,
cp
Dn
C02
02
N2 &CO
Ymstd
Vw
Bw5
xd
Md
M,
%1
T.
A,
Pa
PbP
Ps
Q,
Q.
v.
Curies
Crad
ERrad
f . ";.
f Ti\BLEV
COMPLETE RESULTS, PM
ENERGY FUELS CORPORATION, BLANDING, UTAH
YELLOW CAKE DRYER BAGHOUSE
Descri~tion Dimensions Run #I
Dale 1115/2014
6107
Ttme Test Began 10:57
Time Test Ended 13:0 I
Meter Barometric Pressure ln. Hg. Abs 24.75
Orifice Pressure Drop ln. H20 2.033
Meter Calibration Y Factor dimensionless 1.002
Volume Gas Sampled-· Meter Conditions cf 108.674
Avg Meter Temperalure "F 77.6
Sq Root Velocily Head Root In_ H,O 0.9327
Weight Water Collected Grams 6.9
Duration of Test Minutes 120
Pilot Tube Coefficient Dimensionless 0.84
Nozzle Diameter Inches 0.2230
Volume% Carbon Dioxide Percent 0.00
Volume% Oxygen Percent 20.90
Volume% Nitrogen and Carbon Monoxide Percent 79.10
Volume Gas Sampled (Standard) dscf 89.002
Volume Water Vapor scf 0.325
Fraction HP in Stack Gas Fraction 0.004
Fraction of Dry Gas Fraction 0.996
Molecular Wt. Dry Gas lbllbmol 28.84
Molecular Wt. Stack Gas lb/lbmol 28.80
Percenllsokinelic Percent 97.0
Avg Stack Temperature "F 75.9
Stack Cross Sectional Area Sq. Ft. 1.396
Stack Static Pressure ln. H20 -1.30
Sample Port Barometric Pressure ln. Hg Abs 24.68
Stack Pressure ln. Hg. Abs 24.584
Stack Gas Volumetric Flow Rate (Sid) dscfm 3.94E+03
Stack Gas Volumetric Flow Rate (Actual) cfm 4.88E+03
Velocily of Stack Gas fpm 3.50E+03
Radionucl ides per sample pCi 2485.2
Concentration of Radionuclides pCildscf 27.923 I
Emission Rate of Radionuclides pCilhr 6.596E+06
Dryer Bag house 13
General Npmenclature
%1 = percent isokinetic, percent
A.=(D/14)•1t
AStlP = see VilP
Btu = unit heat value (British thennal unit)
Bws = fraction of water in stack gas (may have designation of "measured" or "saturated")
"measured" represents measured moisture based upon sample volume and water collected
"saturated" is a calculated value based upon stack pressure and temperature
C0 = average of initial and final system zero gas calibration bias checks (ppm, percent)
Cavg = average gas concentration (as measured)
C8 = concentration of particulate matter, back half(gr/dscf,lb/dscf, etc.)
Ccand = concentration of condensibles (grain/dscf)
Ccors = concentration of coarse particulate (gr/dscf)
Coor = measured concentration of a calibration gas when introduced in direct calibration mode
Cr. = concentration of particulate matter, front half, actual stack flow (gr /act)
CF = concentration of particulate matter, front half (gr/dscf,lb/dscf, etc.)
C805 = Cavs corrected for initial and final system bias checks (Equation 7E-5)
Cm = average of initial and final system upscale gas calibration bias checks (ppm, percent)
Cma = actual concentration of upscale calibration gas
Cmetal = concentration of metals (ppm, 11glfe, etc.) atomic symbol replaces "metal"
C02 = percent carbon dioxide in the stack gas
CP = pitot tube coefficient (0.84)
Cp~110 = concentration ofPM10 particulate (gr/dscf)
C,.d = concentration ofradionuclides (pCi/dscf)
CS = measured concentration of a calibration gas when introduced in system calibration mode
Cx = Any species symbol may replace X. Units may be expressed as ppm, lb/dscf, etc.
Cx (corr) = actual gas concentration corrected to required percent 0 2
Curies= Measured radionuclides per sample. Units may be pCi or uCi.
De= jet diameter (em)
DIF = Dioxins and Furans (See laboratory report for DIF descriptions and nomenclacture)
tlH = orifice pressure drop (inches H20)
tlH@ = orifice pressure (inches H20)
t1Hd = orifice pressure head (inches H20) needed for impactor flow rate
Dn = nozzle diameter (inches)
tlP = stack flow pressure differential (inches H20)
Dp50 = 50% effective cutoff diameter of particle (em)
D.= diameter of the stack (feet)
EA = percent excess air
ER8 = emission rate of back half particulate (lblhr)
ERcond = emission rate of condensibles (lblhr)
ERcors = emission rate of coarse particulate (lblhr)
ERF = emission rate affront half particulate (lb/hr)
ER~a.r = emission rate of a gas (lblhr)
ERmmBtu = emission rate per mmBtu of fuel
ERpt.11o = emission rate ofPM10 particulate (lblhr)
ERrad = emission rate of radionuclides (pCilhr)
ER~ = emission rate of compound which replaces X. Units are usually in lblhr.
F0 = Dry based fuel factor. Ratio of the gas volume of the products of combustion to the heat content
See 40 CFR 60, Appendix A, Method 19, Table 19-2 for fuel factor values.
Kc = Cunningham slip correction factor
A.= mean free path of molecules in gas phase (em)
mmBtu = million Btu
..
General Nomenclature
Mcond = mass ofcondensibles (milligrams)
Mco" = mass of coarse particulate (milligrams)
Md = molecular weight of stack gas, dry basis (lb/lb-mol)
Mr = mass of particulate on filter (mg)
Mrp = mass of particulate matter on filter and probe (mg)
mmBtu = million Btu
Mp = mass of particulate matter in probe and front wash (mg)
MPMIO = mass ofPM10 particulate (milligrams)
M, = molecular weight of stack gas, wet basis (lb/lbmol)
Mx = mass of species "X". Units may vary and other descriptive subscripts may apply.
J..ls = gas viscosity (poise)
Mwx = molecular weight of gas species (g/gmol)
N = number of jets per plate
N2 = percent nitrogen in the stack gas
0 2 = percent oxygen in the stack gas
..J/lP = average of the square roots of /lP (may also be referred to as AS/lP}
..Jflp1 = square root of llP at point I of the current test, Method 20 I A
..J/lP 1' = square root of /lP at point I of the previous traverse, Method 20 I A
..J/lP'ave = average of the square roots of /lP from the previous traverse, Method 20 I A
Pbm = absolute barometric pressure at the dry gas meter (inches Hg)
Pbp = absolute barometric pressure at the sample location (inches Hg)
P0 = stack static pressure (inches H20)
P5 = absolute stack pressure (inches Hg)
P51d = absolute pressure at standard conditions (29.92 inches Hg.)
e = time of test (minutes)
81 = sample time (duration in minutes) at first sample point for Method 20IA
8n = sample time (duration in minutes) at sample point "n" for Method 20IA
81esr= target test time for Method 201A (minutes)
Oa = stack gas volumetric flow rate (acfm)
Q, = stack gas volumetric flow rate (dscfm)
Osc = actual gas flow rate through the cyclone (acfm)
Osee = actual gas flow rate through the impactor (acfm)
Ow= wet stack gas std . volumetric flow ere/min, wscfm)
R = gas constant (2 I .85 inches Hg*ft3/(lbmol*R))
Pp = particle density (I g/cm3)
Ps = stack gas density (g/cm3)
T m = stack temperature {°F)
T, = stack temperature (°F)
T,1d = absolute temperature at standard conditions (528°R)
Tt = Duration oftest run in minutes. Also see 8
Um = mean molecular speed (cm/s)
Ym = sample volume (fe) at meter conditions
Vm51d = volume standard (dscf), sample volume adjusted to 68°F and 29.92 inches Hg.
V, = velocity of stack gas (fpm)
y w = volume water vapor (set) at 68°F and 29.92 inches Hg.
Wfwc = weight of the condensed water collected (grams)
xd = fraction of dry gas
Y = meter calibration Y-factor (dimensionless)
II'= dimensionless inertial impaction parameter, O.I4
,p. ...
• .., .& General Sample Equations
? As= (05-I 4) • 1t
8"5 = Vw I (Vmstd +Vw)
C8 =Me • 0.01543 I Vmstd
Ccond = Mcond • 0.01543 I Vmstd
Ccors = Mcors • 0.01543 I Vmstd
Cra = Tstd • Crp • Ps • Xd I [Pstd • (Tm + 460)]
Cr= Mrp • 0.01543 I Vmstd
CPMIO = MPMIO • 0.01543 I Vmstd
Crad = CuriesNmstd
Cga1 (corr) = Cgas • (20.9-desired %02) I (20.9-actual %02)
case Dpso = -,J [)..lS • \jJ • N • 1t • D/ • 18 I (Kc • Pp • Osee • 4)]
PM,. Dp;o = 0.15625 • [(T5 + 460) I (Ms • P5)]0'2091 • ()..1.5 I Osc)0·7091
ERcond = Ccond • Os • 0.00857
ERcors = Ccors • Os • 0.00857
ERF = Cr • Os • 0.00857
6 ERK"·' = Pstd • Os • Mwgas • Cgas • 60 I (R • Tstd • I 0 )
ERgm = Cgas(lbldscf) • Os • 60
(Either ERgas equation gives equivalent lblhr values to 3 sig. figures)
ERmmBtu = Cgas(lb/dscf) • Fd • (20.91(20.9-%02), Method 19 Equation 19-1
ERPMIO:::: CPMIO • Os • 0.00857
ERrad :::: Crad • Qs • 60
Kc:::: 1 + 2 • A. • 1.257 I Dpso
A :::: Jls I (0.499 • Ps • U m)
Md = C02 • 0.44 + 0 2 • 0.32 + N2 •0.28
Ms = (Md • Xd) +(I 8 • Bws)
)..ls = [51.05 + 0.207 • (T5 + 460) + 3.24 •10'5 • (T5 + 460)2 + 0.53147 • %02-74.143 • Bwsl • 10'6
Ps:::: PbP +(Po 113.6)
8, = (-,JllP1' I -,JllP'ave) • (81est I pts)
8n:::: 8, • -,JllPn I...JllP1
Oa = Ys • As
Qs = Qa • Xd • Ps • Tstd I [(Ts + 460) • P51d]
Osc = [(Ts + 460) • Pstd I (Tstd • P5)] • [(Vmstd + V w) I 8]
Osee = [(T5 + 460) • Pstd I (Tstd • P5)] • [(Vmstd + V w) I 8]
Ow= QsiXd
Ps = P5 • M5 • 3386.39 • 10-61 [R • (T5 + 460) I 1.8]
Urn= 100 • -,J {[R • (T5 + 460) 11.8 • 8 • 103] I [1t • M5]}
Vmstd = Vm • Y • Tstd • (Pbm + llH I 13.6) I [Pstd • (T m + 460)]
V5 = 85.49 • 60 • Cp • -,Jflp • -,J [(T5 + 460) I (P5 • M5)]
Yw= Wtwc•0.04715
Xd = 1 -Bws
APPENDIXB
South Yell ow Cake Scrubber
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
Yellow Cake Dzyer Baghouse
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
B
South Yell ow Cake Dryer Scrubber
Facility Energy Fuels . ..
Stack Identification South Yellow Cake Dry_er Scrubber
i A Date
Barometric Pressure
N Pbn, in Hg Pbp in Hg
8 Static Pressure (PG) in H:O
Estimated Moisture (Bw,) 4-6% %
Sample Height from Ground 70 feet
Comments:
Stack Dm 12.75 Rcterence 0
Pons arc 7' Upmeam from nc\t disturbance
Pons are 30' DOIIllStream from last disturbance
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B I c D E F
I 6.7 0.85 0.85
2 25.0 3.19 3.19
3 75.0 9.56 9.56
4 93.3 I 1.90 11.90
Averages:
Ts ___ _ L. FlO\\ ----
C.P .Vt.P --------
KEY=>
IM5: Field Data Sheet
Plant:~
Date:~
Traverse II Time ---.-
Point
1
1
1
2
2
2
3
3
3
4
4
4
1
1
1
2
2
2
3
3
3
4
4
4
Total
, Avernge
DGM
Operator: __ -1----+--------
aP II aH (~H,OI II Vacuum II I Te~peratures :'F) I ~ DGMT~p (T,.)
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r
8 0 N
Slack Diameter 12. 75" Port Reference --"'0-" __
J
?:__Upstream from next disturbance
30' Downstream fll)m Jnst distut:bance
Assumed Moisture _ 4-6 %
.Probe -z """f). S Cp 0.84
NozzlcQllibml~on / ...,,---~ t....J.u -l-"t t:D . c..."+S
AvgD. ~b --
Gas Bag If:-0 ::}
Console_____},
Y-Foctor (-·C) 1.) c:_
aHa I . L f> in H20
Barometric Pressures
Pbm "'2-'-/.. ]=~ in Hg
PbP 2 '-( · ftJ<;r in Hg
Pc -• 3 d) in H20
Leak Check: Pre Post L/-
fl'imin (? .oD4 0 ·6D (
vocinHg 2} ( <:
Pilol Rale 0 • U
lnH,O UJ · S
Water Collected
Time Sampled
Review
a·D
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i-{'Zt \ .lJ
K=
K=
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rn i__ Field Data Sheet
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..,, Eni'~;r~~ Date: ""'
Travene
Point
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( 2
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t.toctlO
{ .1 01-( ot.\·s--
tAOl, <(
~ ~ . ..:,
Ports arc 7' Upstream from next disturbance
~orts arc 30' Downstream from last disturbance
Assumed Moistu_r; ~ 4-6 %
Probe 1· t Cp 0.84
Ni1~Calib'i~ .1 t{ 1 t5
• _A_v_g_D" 1 W'~ in-ch_c_s - . ---
Gas Bag~
Console__,.~.:__-
y -Factor / ' l)b :Z:
t.Hg /· ~ )CJ in H20
Barometric l'rtss~
Pbm zy.1~ in Hg
l'bP li-~l6 inHg
Pc ( 0 • / J in H20
Leok Cheek: Pre Post .--
R1/min 0 --:QD 1 o7oo 5
VIle in Hs '7 1... __2_Q
Pilol Rllte Q . 0 D·o
lnH,O ~·~ ~
Water Collected '-1~ &-· 5r
Time Sampled~
Review
K=
K =
@Tm
@Tm
. {ol"i" ) ,-.€6\~ z_.ou..s
. lt \\
g
min
Yell ow Cake Dryer Baghouse
~. .. Prelim 6 pts
i
Facility Energy Fuels
B Stack Identification South Yellow Cake Dryer Baghouse
Date
N
Barometric Pressure
A Pbm in Hg PbP in Hg
Static Pressure (P0) in H20
Estimated Moisture (Bw5) 1 %
Sample Height from Ground feet
Comments:
Stack Dia 16" Reference: 0
Ports are 57" I Upstream rrom next disturbance
Ports are 454" iJ Downstream from last disturbance Time:
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B c D E F
1 4.4 0.70 0.70
2 14.6 2.34 2.34
3 29.6 4.74 4.74
4 70.4 11.26 11.26
5 85.4 13.66 13.66
6 95.6 15.30 15.30
Averages:
Ts LFiow --------
~P ___ _ v~P __ _
KEY=> ~p L Flow!
It '-{ Field Data Sheet
~
Plant: Denison Mines
Date; I{ I f"f \~
Traverse Time
Point Clock Min (9)
1 1o:-&1-0
2 !(0
3 120
4 }.Q
5 !.{€)
6 50
1 1t:o1 lc.o
2 ::w
3 80
4 qo
5 too
6 110
\'!l:ol \'Z.O
Total
A -·-.g-
Commenls: Time
tl \oo
~~~ 1})
l\~~01
TETCO
Filter (,10""1-SampleBox_A __
OOM AP AH tnH,OI Vocuum
(O'J (mHp, Desired
131 .l..o'1 .7C[ 1.9,--r
1'41.>. 'Z-~0 ·~lo 'l.o'-1.
ISS. z~.( ·~.S '1,.~e
h.~. 3")0 ·~tO -z..o~
113.~~0 ·t"'t ·-z. .ot.,
IS Z. ·'-~0 ·t{ 2.01
t~l.l,.fy •93 z."l.o
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BaghouseAP
S.t.
5,"'1.,
s.t..--
Location: Yellowcake Dryer Baghousc
Operator: M. · ~ ~ lJ [JJJ-tAl ,_
Temperatures m
Stack (T,) Probe Probe: Out Filter
,-( 27:< Z'' •') z;'-{
7{ 7.70 ~)\ 2-5'\
15 210 Z..~.o; ?.:){
'1) l"Cf t<B l.fS ,_, 110 1'(~ "Z.£10
1-l "2.30 "?,..~{{ Zli-(
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l(o Z-ro 2.{8 Z.(.q
11 l,i;.o 'Z,.c.{"'{ l<H
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ll 1,S:( ~d"t{ ?..,4
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ct tl /
/ l'J. ~1--
DGM Te:mp(i;.,
Effluent Out In
53 10 '-6
'1-{ '1-z.. c.."'(
l.f-:r 1€> -,o
"l't '?>0 1t
s t ~1..-11..
51. 4lN 11..
'iCf Bo ?-;
Lf1 gj "1'1
'ire B<f 1i
~~ 9A' )(
'i~ ~'? f':r
't~ ~ 7\?
rt& ~
ll.~
~ Loc;J,e,C-. -:r tJo..(feJS
.
i Page _\ of -Run# I_-
B t ·0 N
Stack Diameter _16" __ Port Reference _0.0"_
P/f arc ~T Upstream from next disturbance •
POrts arc ¥.sy'~ Downstream from last disturbance
Assumed Moisture • o/o
Probe •13-b Cp~
Nozzle Calibration
I "'2-'Z.."$ l l'2.3 I 2_2."3, ....J..3:?:2
Avg D. '2.'Z. ) inches
Gas Bag Ambienl Air
Console ---'91---
Y-Foctor I· 00 L.
liH0 ~ •to) L-in H20
Barometric Pressures
Pbm 24,71 inHg
Pb• 2 Lf · f.. tQ in Hg
Pq -l· ~ . in H20
l..ai:Chec:k: Pre
11'/min 0 00(..
\'lcinH~<..O· 0
PilocRaleo .o
lnH,O t•O
~
O·Oo Z..,. n.o
o.o
"')A}
Water Collected {., · ~ g
Time Sampled ''2. 0 min
Review ~
K•
K-
@Tm
@T. -...
"'
South Yell ow Cake Scrubber
Sample Recovery
Gas Analysis Data (ORSA T)
Yell ow Cake Dryer Baghouse
Sample Recovery
Gas Analysis Data (Ambient)
Chain of Custody
Lab Analysis
APPENDIX C
c
South Yell ow Cake Dryer Scrubber
.... METHODS
Facility: Energy Fuels
Stack Identification: SYC Scrubber
Date: l(t<i / l 1 ----~-;__.!...._
~~~~~-------------------------
WJ!W{IEBS \ ~ ~ Run: Sample Box:
~
·(o tOi
'~ !0 C{
L? \ ro
(ol I (
IMI!IJS{I~BS
"II 2-
IMPINGEBS
Final (g)
Initial (g)
Net (g)
1
Run:
1
drop out
I
(., 7o ,{
t{"T=J-.3
I l:l3 1 "L
Run:
1
drop out
I
Iiiipinger l"'um6er
2 I 3 I 4 I 5 6
Initial Volume.ofliquid (H20) in imp!ngcrs, (ml)
100 I droE out I 100 I Silica Gel
Total (g)
(J
---
1---Sample Box: 8
)m~inger l"'umlier
2 I 3 I 4 I 5 6
Initial Volume of liquid (H20) in impingcrs, (ml)
100 I drop out I 100 I Silica Gel
I , • , •
813.2.. ~~1.5 ~q:l ·l. 5 Jv ·LJ 111'1C..· -:3
~35-r s(,t)L/.O & f-IP· ¥ s-z.l ? ~~o.'l
\(I . '-\ 31 .5" I~ ·'-l 8., (o)·'\
Total (g) tt9B.8
Sample Box:
lmp10ger Number
2 I 3 I 4 I 5 6
Initial Volume of liqui<l(H20) in ·impingers; (ml)
WO I drop out I 100 I Silica Gel ,
Final (g)------+-------+-------+------+-----+-------
Initial (g)------+-------+------+------+------+------
Net (g) ======d=====~==================~======
Total (g) ---------~ --=-========= IMPINGERS
Run: Sample Box:
1 2
Iiiipinger Number
I 3 I 4 I s 6
Initial Volume ofliquid (H20) in impfngers, (ml)
drop out 100 I drop out I 100 J Silica Gel
I J
Final (g) -------1-------+-----~------1------+-----
Initial (g) ____ --+------+-----+------+-----1-------
Net {g)==========::::b====:!:========::b:===
--~ ---------Total (g)::==~===::==:
wr~
1/1'~ I I~
_. -L'
Plant t:: VI e.r" vI +--.~~ _) c::::. '.{ (_ Location ...; ·--------~----~--------------------Analytical Method ORSA T
I[,,\.~ Average
Actual Net Net Actual Net Net
Date Gas Reading Volume
Test No.
Gas Bag No. C: -o 1-\. . \ \. l \. l Ambient Temp t! L \ I· I.
Operator
Date~ Average
Actual Net Net Actual Net Net
Gas Volume
TestNo.~ Gas Bag No. .....o
Ambient Temp · 2•0 Z·b 2•0 Z,o -z,o z.a
Operator
·()
Actual Net
lr-------T-------~r------~----~r------~------41 Average Net Actual Actual Net Net
Date Gas Volume -----Test No. ____ _
Gas Bag No. ____ _
Ambient Temp ____ _
Operator ____ _
CO is not me85ured, 85 it h85 the same molecular weight 85 N2
Yell ow Cake Dryer Baghouse
,tf ., .•. ~
f'l Method 5
Facility: Energy Fuels Date: ~~I ) /11 ______ __:_.....:..
Stack Identification: Yellow Cake Dryer Baghouse
IMPINGERS l
Filter Numb#
~2135"
lolol
IMPINGERS
Filter Number
IMPINGERS
Filter Number
Final (g)
Initial (g)
Net (g)
Run:
1
100
I
5Cft.O
(,/,.(o
-2.7 .~
Run:
l
Sample Box:
2
lmfnger Number
I 3 I 4 I s
Initial Volume ofliquid.{H10) in impingers, (ml)
100 I I SilicaGel I
1 ' .
~14 ·11 c, I {. t/J'l t:t ~0. '-{.
{011.~ v W.<t 9o~.6
1-PJ "f.~ Z.l ' &
Total (g)
=====~
'
Sample Box:
lmpinger Number
2 I 3 I 4 I 5
Initial Volume ofliquid (H20) in impingers, (mi)
100 100 I I SilicaGet I
6
~
6
Final (g) ___ --t----+----+----+------11-----
Initial (g) -----t----+-----+----+------11-----Net (g) ============~==========================
Run: Sample Box:
lmpmger Number
] 2 I 3 I 4 I 5 6
Initial Volume of liquid {H10) in impingers; (ml)
100 100 I I SiticaGel I
Final (g) -----t----+-----+----+----lr----
Initial (g) ___ --t----+----+----+----lr----
Net (g) ============~==========================
Total (g) =======
Chain of
Custody Record
Temperatura on Receipt ---Test America
Drinking Water? Yes 0 NoD THE LEADER IN ENVIRONMENTAL TESTING
TAL-4124 0!Xm
Client
Tetco
~·
-P{Ofl!t:f ¥D!t89'J!f
__ Dean Kitchert. .. _ .... . .....
Telephone Numb9r (Area Code )/Fax Numb6r
391 East 620 South 1801-492-9106
~ -· . I Stato I Zip Code Site Contact
· Amencan Fork Ut :_ 84003
I Lab Contact
Proj4a Natmt and Location (StaiB)
"' Energy Fuels 2014 1st Quarter
ContracilPurchase Orrflllf/QuoiB No.
Sample I.D. Na. and Description
(ContslnetS for tMCh sample may be combined on one line} Date
' R1 Baghouse filter (6107) and beaker 01/15/14 "l-
R1 SYC filters (6108, 09, 10, 11) and beaker 01/14/14
R2 SYC filters (6112,13,14, 15) and beaker 01/15/14
-. I ·L__---=--...
··---------
Scott Chrilt~nsen, Garren P•lmer I cariiei-twaybffl Nuiiibar
Containers &
PreseNatives Matrix
Time ~~ ~~~~~~ I I i I ~ I ~ I ~ ~~~I
n :oo :! X
8:00 X
8:00 X
l
0 1;;. ::1 z. ' ::) i!:
·, -. • X., o I -,
X I -' .,
Date
-+ 1/17/2014 ----1 LBb Number
Analysis (Attach list ff
more space is neBded)
0 ~ ;;
.... "0 1:. ~·
-,
-.
x, -.--
Chain of_ c~ [;prrper-
Page or
Special Instructions!
CondffionsofRece~t
Possible HBZBrd !denlilitlltloil ---,Sample D/$posiJ
0 Non-Hazard 0 Fltlmrnable 0 Skin kritatrl 0 Poison 8 0 Unknown 0 Rerum To Cllant 0 Disposal By Lab (A fee may be B6SIIISS6d if samples am retained 0 Arr:hive For ___ Months ~ lhml1 month)
TumArOUndT(m~
0 24 Hours ~ ~rs @{Days ..,0 14 Days 0 21 Days 0 ()ttJBJ; a~ per method
0C: Raqult!U719/ItS (Spedty}
1:-~~ NJ--fl-:_ ~r l,r_ ('{1!_-;,/;cf I /z 1. Rt~Cflivtld.By (lito (NM
:t. fWt:alvtld By IDDI~r I~
S. RllCfiMtd By !Oatil
'Tmo
2.~~ -....-I'"" 'TifJlO 1
Date
3. R6JiriQ(Jl$hedB_y (~ ,Do~
Commllllts
When Complete Email to: Dean or Paul [e-mail] DISTRIBUTION: WHITE :·Re!Uiiiiii:lto Client with Rej>ort; CANARY ~·Shlys Wfth-·ltle"'~Si""m""IP071e"';'P"'1N"'Kv--F""l"'el""CJ.,.C""op='y:------------------------------------
SDGNo. Ordct·No.
47741
TestAmerlca Inc
l'piSTLRchTitle v3.73
Tes!America Laboratories, Inc.
Analytical Data Pac){age Prepared For
Denison Mines (USA) Corp.
Energy Fuels 2014 1st Quarter
Radiochemical Analysis By
TestAmerica Inc
2800 G.W. Way, Richland Wa, 99354, (509)-375-3131.
A.!isigned Laboratory Code:
Data Package Contains 14 Pages
Report No.: 58580
Results in this report relate only to the sample(s) analyzed.
Client Sample ID (List Order) Lot-Sa No. Work Order Report DB lD
R1 Baghouse J4A210418-1 M2WD61AA 9M2WD610
filter(61 07)and be
R1 SYC J4A210418-2 M2WEQ1AA 9M2WEQ10
fllters(6108,09, 10,11)a
R2SYC J4A210418-3 M2WET1AA 9M2WET10
filters(6112,13,14,15)a
Batch No.
4023018
4023018
4023018
Test America
THE LEADER IN ENVIRONMENTAL TESTING
January 29, 2014
Denison Mines (USA) Corp
1050 17th Street, Suite 950
Denver, CO 80265
Attention: Dean Kitchen
Date Received at Lab
Project Name
Sample Type
SDGNumber
I. Introduction
Certificate of Analysis
January 21, 2014
Energy Fuels 2014 1st Quarter
Three (3) Stack Filter Samples
47741
CASE NARRATIVE
On January 21,2014, three stack filter samples were received at TestAmerica's Richland laboratory for
radiochemical analysis. Upon receipt, the samples were assigned the TestAmerica identification
numbers as described on the cover page of the Analytical Data Package report form. The samples were
assigned to Lot Numbers J4A210418.
IT. Sample Receipt
The samples were received in good condition and no anomalies were noted during check-in.
ill. Analytical Results/Metbodology
The analytical results for this report are presented by laboratory sample ID. Each set of data includes
sample identification information; analytical results and the appropriate associated statistical
uncertainties.
The analysis requested was:
Alpha Spectroscopy
Uranium-234, -235, -238 by method RL-ALP-004
Tes!America Laboratories, Inc. 2
Denison Mines (USA) Corp
January 29, 2014
IV. Quality Control
-·
The analytical result for each analysis performed includes a minimum of one laboratory control sample
(LCS), and one reagent blank sample analysis. Any exceptions have been noted in the "Comments"
section.
V. Comments
Alpha Spectroscopy
Uranium-234. 235. 238
The achieved MDA of the batch exceeds the detection limit due to the reduced aliquot sizes taken due to
historical process knowledge. Data is accepted. Except as noted; the LCS, batch blank and sample
results are within acceptance limits.
I certify that this Certificate of Analysis is in compliance with the SOW and/or NELAC, both technically
and for completeness, for other than the conditions detailed above. The Laboratory Manager or a
designee, as verified by the following signature has authorized release of the data contained in this hard
copy data package.
Reviewed and approved:
TestAmerica Laboratories, Inc. 3
....• '
Drinking Water Method Cross References .T --,--··
DRINKING WATER ASTM METHOD CROSS REFERENCES
Referenced Method lsotope(s) Test:Amerlca Richland's SOP No.'--
EPA 901.1 Cs-134, 1-131 RL-GAM-001
EPA 900.0 Alpha & Beta RL-GPC-001
EPA 00-02 Gross Alpha (Coprecipltatlon) RL-GPC-002
EPA 903.0 Total Alpha Radium (Ra-226) RL-RA-002
EPA 903.1 Ra-226 RL-RA-001
EPA 904.0 Ra-228 RL-RA-001
EPA 905.0 Sr-89/90 RL-GPC-003
ASTM D5174 Uranium RL-KPA-003
EPA 906.0 Tritium RL-LSC-005 ___ .,. ·----·-
·---.. ~
Results in this report relate only to the sample(s) analyzed.
Uncertainty Estimation
TestAmorica Richland has adopted the internationally accepted approach to estimating
uncertainties described in ''NIST Technical Note 1297, 1994 Edition". The approach, "Law of Propagation
of Errors", involves the identification ofall variables in an analytical method which are used to derive a
result. These variables are related to the analytical result (R) by some functional relationship, R =constants
• f(x,y,z, ... ). The components (x,y,z) are evaluated to determine their contribution to the overall method
uncertainty. The individual component uncertainties (uu are then combined using a statistical model that
provides the most probable overall uncertainty value. All component uncertainties arc categorized as type
A, evaluated by statistical methods, or type B, evaluated by other means. Uncertainties not included in the
components, such as sample homogeneity, are combined with the component uncertainty as the square root
of the sum-of-the-squares of the individual uncertainties. Tho uncertainty associated with the derived result
is the combined uncertainty (uc) multiplied by the coverage factor (1,2, or 3).
When three or more sample replicates are used to derive the analytical result, the type A
uncertainty is the standard deviation of the mean value (S/?n), where Sis the standard deviation of the
derived results. The type B uncertainties are all other random or non-random components that arc not
included in the standard deviation.
The derivation of the generai"Law of Propagation of Errors" equations and specific example are
available on request.
TestAmarlca lne
ratGcncrallafo v3.72
TestAmerica Laboratories, Inc. 4
-------
~-
·--· 1---
--·
Action Lev
Bntch
Bias
COCNo
Count Error (#s)
Total Uncert (#s)
u. _ Comblued
Uncertainty.
(#s), Coverage
Factor
CRDL(RL)
Lc
Lot-Sample No
MDCIMDA
Primary Detector
Ratio U-234/U-238
Rst/MDC
RstrrotUcert
Report DB No
RER
SDG
Sum Rpt Alpha
Spec Rst(s)
Wori<Ordcr
Yield
Tes!Amerlca Inc
rotGenct·allofo v3.7:Z
TestAmerica Laboratories, Inc.
Report Definitions _
An ngn.cd upon nt ti\llly love! used to trigger some 11ctlon when the Cimil result is greater than or equol to the Action
Level. Often the Action Level Is relnted to the Decision Limit.
The QC preparation balch number that relates laboratllry samples to QC sample's that were prepared and nnalyzed
together.
Defined by the equation (Result/Expected)-! as defined by ANSI Nl3.30.
Chain of Custody Number assigned by the Client or TestAmeriCII.
Poisson counting statistics of the gross sample count and background. The uncertainty is absolute and in the same
units as the result For Liquid Scintillation Counting (LSC) the batch blank count is the background.
All known uncertainties associated with the preparation and 1111alysis of the sample are propagated lo give a measure
of the uncertainty associated with the result, Uc the combined uncer/alnty. The uncertainty is absolute and in the
same units as the result
The coveruge factor defines the width of the confidence interval, I, 2 or 3 standard d~viations.
Contractual Required Detection Llmlt as defined in the Client's Stutement Of Work or TestAmerica "default"
nominal detection limit. Ofien referred to the reporting level (RL)
Decision Level based on inslrument background or blllllk, adjusted by the Efficiency, Chemical Yield, ami Volume
associated with the sample. The Type I error probability is approximately 5%. Lc=(1.645 •
Sqrt(2•(BkgmdCnt/BkgrndCntMin)/SCntMin)) • (ConvFct/(Efi*Yid•Abn•Vol) • Tngrl'ct). ror l.SC methods the
batch blank is used as a measure oflhe background variability. Lc cannot be calculated when the background count
is 7cro.
The number assigned by the LIMS software to track samples received on the same day for a given client. The
sample number is a sequential number assigned to each sample in the Lot
Detection Level based 011 Instrument background or blank, adjusted by the Iifficlency, Chemical Yield, and Volume
with a Type I and TT error probability of approximately 5%. MDC~ (4.6S •
Sqrt((BkgrndCnt/BkgrndCntMin)ISCntMin) + 2.71/SCntMin) • (CunvFct/(Eff • Yld • Abn • Vol)' lngrFct). For
LSC methods the bntch blank Is used as a measure of the background variability.
The instrument identifier associated with the analysis of the sample aliquot.
The U-234 result divided by the U-238 result The U-234/U-238 ratio for natural uranium in NIST SRM 432JC is
1.038.
Ratio of the Result to the MDC. A value greater than I may indicate activity above background at a high level of
confidence. Caution should be used when applying this factor and it should be used in concert with the quulifiers
associated with the result
Rntio of the Result to the Total Uncertainty. If the uncertainty has a coverage factor of2 a value greater than 1 may
indicate activity above background at approximately the 95% level of confidence as~'Uming n two-sided confidence
interval. Caution should be used when applying this factor and it should be used in concert with the qualifiers
associated with the result
Sample Identifier used by the report system. The number is based upon the first five digits of tl1e Work Order
Number.
The equution Replicate Error Ratio"' (S-D)/[sqrt(TPUs2 + TPUd2)] as defined by !CPT BOA where S is the original
sample result, Dis the result of the duplicate, TPUs is the total uncertainty of the original sample and TPUd is the
total uncertainty of the dupliCIIte sample.
Sample Delivery Group Number assigned by the Client or assigned by TestAmerica upon sample receipt.
The ~urn of the reported alpha spec results for tests derived from the same sample excluding duplicate result where
the results arc in the same units.
The LIMS software assign test specific Identifier.
The recovery of tha tmcer added tll the sample such as Pu-242 used to trace a Pu-239/40 method.
5
Report No. : 58580
Cllentld
Batch Work Order Parameter
4023018 FFSR
R1 Baghouse filter(6107)and be
M2WD61AA U-234
U-235
U-238
R1 SYC filters(6108,09,10,11)a
M2WEQ1AA U-234
U-235
U-238
R2 SYC filters(6112,13,14,15)a
M2WET1AA U-234
U-2.35
U-238
No. of Results: 9
Sample Results Summary
TestAmerica Inc
Ordered by Method, Batch No., Client Sample ID.
Result+· Uncertainty ( 2a) Qual Units
1.17E-03 +-2.6E-04 uCi/Sample
4.52E-05 +· 3.5E-05 uCI/Sample
1.27E-03 +-2.7E-04 uCi/Sample
1.08E-03 +-2.4E-04 uCi/Sample
3.45E-05 +-3.1E-06 u uCI/Sample
1.07E-03 +-2.4E-04 uCi/Sample
1.22E-03 +· 2.6E-04 uCifSample
1.85E·05 +· 2.4E-05 u uCIISample
9.73E-04 +· 2.2E-04 uCI/Sample
Date: 29-Jan-14
SDG No: 47741
Tracer
Yield MDL CRDL RER2
69% 4.04E-05 S.OOE-15
69% 2.63E-05 9.00E-15
69% 3.26E-05 S.OOE-15
77% 5.96E-05 S.OOE-15
77% 3.48E-05 9.00E-15
77% 5.30E-05 9.00E-15
81% 4.82.E-05 S.OOE-15
81% 4.19E-05 S.OOE-15
81% 4.07E-05 S.OOE-15
TestAmerlca Inc RERl ·Replicate Error Ratio • (S-D)I[sqrt(lq(TPUa)+sq(J'l'Ud))] aa denned by ICPT DOA.
rptTALRchSaSum
mary2 V6.2.26
A2002
U Qunl • AnRiyzed for but not cletccted above limiting crltcriR. Limit criteria Is less thaD the Mdc/Mdnfl\ofdl, Total Unccrt, CRDL, RDL Ol'
not Identified by gamma .sun software.
TestAmerica Laboratories, Inc. 6
Report No. : 58580
Batch
Work Order Parameter
FFSR
4023018 BLANK QC,
M2WRQ1AA U-234
U-235
U-238
4023018 LCS,
M2WRQ1AC U-234
U-238
No. of Results: 5
QC Results Summary
TestAmcrica Inc
Ordered by Method, Batch No, QC Type,.
Result-t· Uncertainly ( 2e) Qual Unit&
1.09E-07 +-2.2E-07 u uCUSample
-2.43E-08 +-1.5E-07 u uCUSample
-6.98E-08 +-1.6E-07 u uCUSample
7.37E-06 +-1.8E-06 uCUSample
7.41E-06 +-1.8E·06 uCI/Sample
TestAmerlca Inc Diu • (ResuiUF.xpceletl)-1 ns defined by ANSI N13.30.
Date: 29-Jan-14
SDG No.: 47741
Tracer LCS
Yield Recovery Bias MDL
75% 4.69E-07
75% 4.05E-07
76% 6.94E-07
71% 98% 0.0 3.32E-07
71% 95% -0.1 3.91 E-07
rptSTLRchQcSum U Qunl -Annlyzed for but not detected a hove lhnltlng criteria. Limit criteria is Ius thMn the MdrJMdn/Mdl, Total Uncert, CRDL, RDL or
mary V&.2.26 notltlenllfletl by gammn scan soOwue.
A2002
TestAmerica Laboratories, Inc. 7
-! CD (/) );
3
CD :::1. g
r "' cr
0 ~ 0 :::1. CD _rn
5" p
GD
Lab Name: TestAmerlcalnc
Lot-sample No.: J4A210418-1
Client Sample ID: R1 Baghouse filter(6107)and be
FORM I
SAMPLE RESULTS
SDG: 47741
Report No. : 58580
COC No.:
Date: 29-Jan-14
Collection Date: 1/15/201411:00:00 AM
Received Date: 1/21/2014 11:55:00 AM
Matrix: FILTER
Energy Fuels 2014 1st_Qu~rter _ _ _ _ __ Ordered by Client Sample 10, Batch No.
Result Count Total MDL, RptUnlt, Yleld Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error( 2&) Uncert(2 s) Action lev lc CRDL(Rl) Rst/TotUcert Prep Date Size Size Detector
Batch: 4023018 FFSR Work Order. M2WD61AA Report DB ID: 9M2WD610
U-234 1.17E-03 1.8E-04 2.6E-04 4.04E-05 uCVSample 69% (29.) 1/28/14 06:48 p 1.0 0.00129 ALP2
1.10E-05 9.00E-15 (9.1) Sample Sample
U-235 4.52E-05 3.5E-05 3.5E-05 2.63E-05 uCi/Sample 69% (1.7) 1/28/14 06:48 p 1.0 0.00129 ALP2
6.11E-06 9.00E-15 (2.6) Sample Sample
U-238 1.27E-03 1.8E-04 2.7E-04 3.26E-05 uCi/Sample 69% (38.8) 1/28/14 06:48 p 1.0 0.00129 ALP2
8.19E-06 9.00E-15 (9.3) Sample Sample
RaUo U-2~8 -0.9
No. of Results: 3 Comments:
TestAmerlca Inc MDCIMDA,lc-Detllctlon, Decision Laval based on Instrument background or blank, adjustlld by the sample Efficiency, Yleld, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detectlld above limiting criteria. llmlt criteria ls less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not Identified by gamma scan software.
V5.2.26 A2002
..
a;t
"' > 3 Ill :::!. lil
r IP C" Q ... 0 :::1. Ill !."
:;
f'
CD
Lab Name: TestAmerica Inc
Lot-Sample No.: J4A210418-2
Client Sample ID: R1 SYC filters(6108,09,10,11)a
FORM I
SAMPLE RESULTS
SDG: 47741
Report No. : 58580
COCNo.:
Date: 29-Jan-14
Collection Date: 1114/2014 8:00:00 AM
Received Date: 1/21/2014 11:55:00 AM
Matrix: FILTER
Energy_fuels 2014 1st Q!JC!rtf:!r Ordered by Client Sample ID, Batch No.
Result Count Total MDL, Rpt Unit, Yield Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2 s) Uncert( 2 s) Action Lev Lc CRDL.(RL) Rst/TotUcert Prep Date Size Size Detector
Batch: 4023018 FFSR Work Order: M2WEQ1M Report DB 10: 9M2WE010
U-234 1.08E-03 1.6E-04 2.4E-04 5.96E-05 uCi/Sample n% (18.1) 1/28/14 06:48 p 1.0 0.00124 ALP3
1.81E-05 9.00E-15 (9.1) Sample Sample
U-235 3.45E-05 u 3.0E-05 3.1E-05 3.48E-05 uCI/Samp!e n% 0.99 1/28/14 06:48 p 1.0 0.00124 ALP3
9.16E-06 9.00E-15 (2.2) Sample Sample
U-238 1.07E-03 1.6E-04 2.4E-04 5.30E-05 uCi/Sample n% (20.2) 1/28/14 06:48 p 1.0 0.00124 ALP3
1.57E-05 9.00E-15 (9.1) Sample Sample
Ratio U-2341238 = 1.0
No. of Results: 3 Comments:
TestAmerlca Inc MDCIMDA,Lc-Detection, Decision Level based on Instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detected above limiting criteria. Lindt cr1ter1a Is less than the Mck:/Mda/Mdl, Total Uncart, CRDL, RDL or not Identified by gamma scan softwaro.
V5.2.26 A2002
,
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0 iil 0 :::1. (1)
!"
5" fl
......
0
Lab Name: TestAmerica Inc
Lot-Sample No.: J4A210418-3
Client Sample ID: R2 SYC fllters(6112,13,14,15}a
FORM I
SAMPLE RESULTS
SDG: 47741
Report No. : 58580
CCC No.:
Date: 29-Jan-14
Collection Date: 1/15/2014 8:00:00 AM
Received Date: 1/21/201411:55:00 AM
Matrix: FILTER
Energy Fuels 2014 1~t Quarter _ _ _ _ Ordered by Client Sample 10. Batch No.
Result Count Total MDL, RptUnft, Yield Rst/MOL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2s) Uncert(2 s] ktion Lev Lc CRDL(RL) Rst/TotUcert Prep Data Size Size Detector
Batch: 4023018 FFSR Work Order. M2WET1AA Report DB ID: 9M2WET10
U-234 1.22E-03 1.7E-04 2.6E-04 4.82E-05 uCi/Sample 81% (25.3) 1128114 06:49 p 1.0 0.00128 ALP4
1.41E-05 9.00E-15 (9.4) Sample Sample
U-235 1.85E-05 u 2.4E-05 2.4E-05 4.19E-05 uCVSample 81% 0.44 1128/14 06:49 p 1.0 0.00128 ALP4
1.18E-05 9.00E-15 (1.5) Sample Sample
U-238 9.73E-04 1.5E-04 2.2E-04 4.07E-05 uCi/Sample 81% {23.9) 1128114 06:49 p 1.0 0.00128 ALP4
1.14E-05 9.00E-15 (9.) Sample Sample
Ratio U-2341238 = 1.3
No. of Results: 3 Comments:
TestAmertca Inc MDCJMDA,Lc • Detection, Decision Level based on Instrument background or blank, adjusted by tho sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual ·Analyzed for but not detected abova limiting criteria. Limit criteria Is less than the MdciMda/Mdl, Total Uncert, CRDL, RDL or not Identified by gamma scan software.
V5.2.26 A2002
. .,
•
-1 CD "' s;
3 CD g·
r ... c::r 0 iil 0 :::>. CD !."
5" p
..... .....
Lab Name: TestArnericalnc
Matrix: FILTER
Count
Parameter Result Qual Error (2 s)
Batch: 4023018 FFSR
U-234 1.09E-07 u 2.2E-07
U-235 -2.43E-08 u 1.5E-07
U-238 -6.98E-08 u 1.6E-07
No. of Results: 3 Comments:
Total MDL.,
Uncert(2 s) Lc
FORM II
BLANK RESULTS
RptUnlt,
CRDL Yield
Rst/MDL,
Rst!T ottJcert
Work Order: M2WRQ1AA Report DB 10: M2WRQ1AB
2.2E-07 4.69E-07 uCi/Sample 75% 0.23
1.27E-07 9.00E-15 (1.)
1.5E-07 4.05E-07 uCi!Sample 75% -0.06
1.04E-07 9.00E-15 -0.32
1.6E-07 6.94E-07 uCI/Sample 75% -0.1
2.09E-07 S.OOE-15 -0.86
Ratio U-2341238 = -1.6
SDG: 4n41
Report No.: 58580
Analysis, Total Sa
Prep Date Size
1/28/14 06:49 p 1.0
Sample
1/28/14 06:49 p 1.0
Sample
1/28/14 06:49 p 1.0
Sample
TestAmerica Inc MDC(MDA,lc-Detection, Decision Level based on Instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
Date: 29-Jan-14
Aliquot Primary
Size Detector
0.1 ALPS
Sample
0.1 ALPS
Sample
0.1 ALPS
Sample
rptSTLRchBiank U Qual-ADalyud for but not detected above limlling criteria. Limit criteria Is Jess than the MddMda/Mcll, Total Uncut, CRDL, RDL or not identified by gaiiiiiUI scan software.
V5.2.26 A2002
•
~ "' ~ 3 !!! i:i"
r Dl C" 0 iil 0 ::I. Ill !"
5" p
~
"'
Lab Name: TestAmerica Inc
Matrix: FILTER
Count Total
Parameter Result Qual Error ( 2 s) Uncert(2 s) MDL
FORM II
LCS RESULTS
SDG: 47741
Report No. : 58580
Report
Unit
Erpected Recovery,
Yield Expectro Uneert Bias
Analysis,
Prep Date
Batch: 4023018
U-234
FFSR Work Order: M2WRQ1AC Report DB ID: M2WRQ1CS
7.37E-06 1.3E-06 1.8E-06 3.32E-07 uCi/Sample 71% 7.49E-06 2.31E-07 98% 1/28/14 06:49 p
RecLimlts: 70 130 0.0
U-238 7.41E-06 1.3E-06 1.8E-06 3.91 E-07 uCI/Sample 71% 7.84E-06 2.42E-07 95% 1/28/14 06:49 p
RecLimlts: 70 130 -0.1
No. of Results: 2 Comments:
TestAmerlca Inc Bias -(ResllltiE:s:pected)-lAS defined by ANSI NI3.30.
rptSTLRchLcs
V5.2.26 A2002
Date: 29-Jan-14
Aliquot
Size
0.13
Sample
0.13
Sample
Primary
Detector
ALPS
ALPS
·-· -·-····--··---
mt ~ 3 CD :::1. g
r "' CT 0
iil 8" :::1. CD !!'
5" "
....
c.>
..
Chain of
Custody Record
TAIA1a4 (llllm
Temperature on Receipt ---
Drinking Water? YesO ·NoD
Test America
THE LEADER IN ENVIRONMENTAL TESTING
c:rlotJt. " -/'rDjtlct MlltZglr .. -- -- ---lfua
i Tetco _ __I ! De<!.fl._Ki~n _ _ ------= ~=------; r iliiizo14 ~ • -----• ---T~.Fil (Mill~~ ,L.to~
1391East 620South ~-492.9~----·--I
~ I ~~Siltf4 Z1P c.-. &1a Ci>n:u.J: Ub ~ Amll}'sfs (A11Bch list If l !~eri;a_!!Fork ---' Ut-~84003 l..,.:;;;.w..;~:....,_;._.--~~ 1'-~.-IS~ :~~~ct;;;.;;,,:-=---:__:_=~-1 ~ I I J i J .
~ · . eontamer.; & J
MaiJVr PI'BSfJrvatives ~ 10! ;:ll ~ I.D. No. and DMctfp"on I i I ~ a ~ ~· ~. :;11 iJ ~foreach~mayl»coml>lnedarotrfiiiM) Dale Tune :1! l ;J ~ -:1! ~ =11 l ~ S!
FvJ.=i=... j Rl Baghouse filter (6107) and beaker 01/15/14 u:OO: XJ X· •j '
! Rl SYC filters 16101,09, 10, lll and beaker ; 01/14/14 8:00: rx I ! X ·::o ~
IR2 SYC filters (6112. 13.14, 15) and beaker I ! 01/15/14 [a:oo , Xl · 7 l ;.~ c=-~1\1~ Willi\\ \\\\\II\ l\1
1,---1
I ~ --4 10418
J I I --I ~ . ..
-:s~ ~ -a Vu'·~.v:.f '
~ -'-V'V\"-\'
~~ d-\~-\'-\
,C;!.:ioof~~ -
P#ga of ~
Special lnstructtonsl
Conditions of Receipt
~ 0. \.A..)\::)~
\'V\~~
'{Y\'a\..0~
~~~tm ~~....,~~ D (A'"" maybll~ if samples""' retained o~ D F18mtn8b1r D Sl<in ,_ D PrMm B -D lkll<nawn D -7b Cllllnt 0 D/llpOuJ By w ~For ___ ~"'-'~
7llm~'Bno.~ cc:~ (Sp«tfy}
0 24Houts ~Houts rl7a-0 14aq, 021Days D Otllet[as.uer metbod_
Uidr~bW/:;;Lz,C)~ ~ L lir.ld..rln; ~ 1.~8/ JOB (me v.-.C:t.~. -:5.~-rflt-ut.-'~a ,_,L\ \ \SS.
Z.~B.)! lvar. l»n<t 2.~ I~ ln.
3. . ..,. 8y Ia. Inn. 3.-...tO)o ln."' lli?:c
-CCiUilbot<
. When Complete Email to: Dean or Paul tetco@teb:,:::o-;;:u~.t~.co=.i:m,:.,...,,.,.,==->=,...=~=------...!.' --------------------------Dirmf~Bqntilf:>9Htrt:-=-Ffiiiimiili0d;.ntii#h~ ~IWIY · .511ys w~~~~·fl':<l SiiiiiP10ii P1r1K • Rer:~CiY>Y'
TestAmerica Sample Check-in List
THE LEACER IN I!HVIRON ... INTAl TE8TIN~ ~ \
Date!fime Received:-----1..::--=....:. V\_!._-_,\'-'-\-\--t----'\u.\S........_S~-Container GM Screen Result: (Airlock) ~cpm Initial~t-;;
Sample GM Screen Result (Sample Receiving) ~cpm Initials~
Client.: ~f;10 SDG #: \.....\II\ Y'\"-\ \ SAF -#:, ___________ .
LotNumbc:r: =:S'U.-~ d,Y\:::>'·-\\'(
ChainofC1.1stodyff. _________________________ ---------
Shipping Container ID or Air Bill Number : NA ~ ]
Samples received inside :;hipping container/cooler/box Yes\-, ] Continue with 1 through 4. Initial appropriate response.
No Q ] Go to 5, add comment to #16.
1. Custody Seals on shipping container intact? Yes [ ] No [ No C\lslody So~~ ]
2. Custody Seals dated and signed? Yes [ J No [ No ~:tody Seal \~ J
3. Cooler tempenmrre: oc NA r ]
4. Vermiculiteipaoking materials is ~ Wet [ ) Dry [ )
5. ChainofCwit<>dy rccprd presenl7 Yes ] No [
Item 5 through 16 for SR!llples. lnitinlappropriate response. ~
6. Nnruber of samples received (Ei\ch Gatnpla llUIY contain mul spit bottles):_,....__--=-----------
7. Containers receive(\:~. t' ~ ·1 ~ i-'cAAY...u ·
8.
9.
10.
11.
12.
13.
14.
15.
16.
Yes [ ; No~ ]
__ custody seals ~~p;jprlnte sample labels
__ S (Air, Niosh 74bQ) ~T (Biological, Ni-63)
es:
Sample holding times exceeded? NA [
Samples have: ___ tape __ hazard labels
Matrix: __ A (FLT, Wipe, Solid, Soil) __ I (Water)
are in good condition · __ are leaking __ are broken
__ have air bubbles (Only for samples requiring no head space) __ Oth~
Sample pH appropriate for analysis requested Yes [ ] No [ ] NA ]
(If acidification is necessary go to pH area & documllnt sample lD, initial pH, amount t 0) added and pH after addition on table)
Were any anomalies identified in sample receipt? k Yes [ ] No 'r )
Description of anomalies (include sample numbers): NA Ll ] ------------------
Sample Location, Sample Collector Listed on COC? "'
•For documentation only. No corrective action needed.
Yes [ ) No~'?]
Additional InformRtlon:4~'-----------------------------
T ] Client/Courier denied temperature check. ] Client/Courier unpack cooler.
Sample Chec-k-i
Signature: ___ , ~~~"""~~~:::_ ___ . ______ Date: \·d..\-l'j
Dnte:
By:
\/, Person contacted:
[ .\J No nction necessary; process ~is . _ _J
Project 'Mllnngcr 2. A ~ ~'-------"-1_-..... ?"""-""2'----I_L-.J--/-
LS-023 Rev. 17,05/13 Page 1 ofl
TeslAmerica Laboratories, Inc.
:• ..
APPENDIXD
South Yellow Cake Scrubber
Figure 1. Facility Schematic Representation
Yell ow Cake Dryer Baghouse
Figure 2. Facility Schematic Representation
Process Data
(Retained by Energy Fuels Resources)
D
Facmty: Energy Fuels Resources
t
CL
t
y
Stack Identification: South yell ow Cake Scrubber
1~0~1
J3
a: Distance upstream from next disturbance, feet ----
~: Distance downstream from last disturbance, feet
y: Distance of Sample Level to Ground, feet -
0: Stack Inside Diameter, inches . -
Estimated Moisture, percent
Estimated Velocity, fpm _-_· ·'-~-----
Control Unit
Type:
Scrubber
Number of Ports
Figure I. Facility Schematic Representation
Process
Type:
Yell ow Cake Processing
•
Facility: Energy Fuels Resources
t
ex
t
).
y
Stack Identification: yellow Cake Dryer Baghouse
1~0 -+-I
13
ex: Distance upstream from next disturbance, inches 57"
~: Distance downstream from last disturbance, inches 454"
y: Distance of Sample Level to Ground, feet 65'
0: Stack Inside Diameter, inches ~
Estimated Moisture, percent 0-2%
Estimated Temperature, °F 125
Estimated Velocity, fpm I ,400
Control Unit
Type:
Baghouse
Number of Ports 2
oE
Figure 2. Facility Schematic Representation
Process
Type:
Yellow Cake Processing
·.
,
' .. .. •./.\
..
''
:i
~-~··" !r
Energy Fuels Resources, Blanding, UT Process Data
Source: South Yellow Cake loate: 1 J,v_f,l!
Scrubber Flow GPM 4
c~y..trv
Time #1 #2 ilP
~:;,o t>'.o 1..:-{· ~ /u·1-
to.' o o 1 s~ u (..,'-'t•e:} {0·1-
tv: so \c.\ ~'-t-"1 (v·-4
l(.'oo l~.V Z£1·<6 /D. :f
l/.' J 0
t '.I l~·1 ,u.~
tz·.oo I~-I z "''~ r o .-::;
{t~3l>
l c;-,\ 2'-{ .,
( 0 ·-=1
l) :o 0 \ 5'. \ 24-l·ti /0·"'::/.
t > .' 3 o f} ,'Z.. 24·~ Jl)•-=l
l 4 ~ .:JD I~ .. ') '2'-{~ I o .'-f
\ L( : ~D ,(·-~ '2. '-\ ~ I b 1-
tr: o o 1)·---f 'Z-fr'1 {c-+
tS:~o ~~.) zLf.~ fD·-:J-
f(p.' 00 15·) z~.~ ( 6 ·-:!
/f?.' ,)0 /~·1-Z'i ·1 ( C:Y 1
f 1 : aD /(p·Z. 2.-"t .j (c·'1-
r:J ... 3 o { (R ·t 2-'-< ·1-(t~.--1
I tr.. C)l> 1G·t. ~·~·~ Jc .1----'
rr-:7u l(p-f..., -zu -1-1 o·-t'
Energy Fuels Resources, Blanding, UT Process Data
Source: South Yellow Cake Date: J1s,i_
Scrubber Flow GPM
c~,.,.. fc...J.-r I} ..... ~
Time #1 #2 ~p
}. : (.) i) ''1·¥' "Z'f· '1 VD. :+
b-_· 10 tLi·'i 2 Lf. ·f I lJ ·1-
'1.: 0 0 pJ• s 2 '-1·1 ( {) ·+-
4.: 3 ~ 1'1·'1 2 L(, i ro·t-
to.'c.Jc Jt..f·~ z l.( • y { ().-;}
/O.'Jo I b · ( 2 '-(, '1 ( o·1
/(: (.) 0 \ ~·> -z_~·U ( 0·1
l( ,• S D IS ·<1 2 v('') t o·1
IZ~.::>D l~·r;-'7 ~· () (0·-+
tZ.') o f~. t, z S"· 0 L o ·1
I J: o D
/5". ~ 2(;.0 I 0 ·1-{'~;e>D
1'$.' "$0 liP. 0 ztf. 4 t0·1-
('-{.' 0 j) l& ,-z_, 25-.0 (6.-:j
It{: 3 o I lP . c..( 2.(. 6 ( () . t
(5: oo I~·~ 2'-l· I lo·.:.?
r~: 3 o {(,. ~ 't {., (D·:}
tv: i)o { (, . ) t').D /0·1
/6 : 56 lG ·~ v1.v ro·t'
I
J
APPENDIXE
Calibration of the console dry gas meter(s), pitot tubes, nozzles diameters, and temperature
sensors were carried out in accordance with the procedures outlined in the Quality Assurance
Handbook. The appropriate calibration data are presented in the following pages. The nozzle
calibrations are recorded on the first page of the field data sheets.
Figure 3 Schematic of Method 5/114 Sampling Train
Meter Box Calibration Data and Calculations Forms
Post-test Dry Gas Meter Calibration Data Forms
Type S Pitot Tube Inspection Data
Sample Box Temperature Sensor Calibration
E
Temperature Sensor
t ~Probe
TypeS Pitot
Tube Temperature
sensor
lrqqerTrain Q:llional, M!r;'BeRepaced 8f hi EqUvalert Condenser
l Temperature
Sensor Te~~~~re
Gooseneck
Nozzle j H:lliltTr.mf
"" ~
/ R'Obe
~--------------
lmpingers
-~
/
TypeS Pitot
Tube ~
Stack
Wall
Glass Filter
Holder
Heated Area
Manometer Temperature
Sensors
Orifice
Air-Tight
Pump
Figure 3 Schematic of Method 5/114 Sampling Train
Vacuum
Gauge
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES y bhiiG@IIQ0@d@iii!h
1) Select three critical orifices to calibrate the dry gas meter \\tlich bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure. ENVIRONMENTAL SUPPLY COMPANY
3) Run attested vacuum (from OrifiCe Calibration Report), for a period of lime
necessary to achieve a minimum total volume or 5 cubic feet.
4) Record data and information in lhe GREEN cells, YELLOW cells are calculated.
DATE::) ·~~"',..._ I METER SERIAL ,,1522588 I
CRmCAL ORIFICE SET SERIAL ~: 1oi63S EQUIPMENT ID II:
G
G
G
RUN I
2
3
2
3
2
K' TESTED
FACTOR I VACUUM
(AVG) (In Hg)
0.8137 13 951.176
G.l1l7 13 963.468
0.8137 13 9611.784
0.5317 12 941.2114
0.5317 12 946.l&D
0.6317 12 951.636
0.3~? 13 975.015
0.3~7 1l 980.846
0.3307 13 916.447
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
963.4CI
9!i8,7a4
974.125
946.360
951.536
957.031
980.1146
986.447
992.040
5.293
5.316
5.341
5.156
5.176
U9S
5.130
5.602
5.593
76 71
75 7<&
75 76
66 66
65 67
66 61
75 76
75 74
75 73
74
76.
71
67
68
70
74
73
73
77 ao
ao 11
13 83
73 71
71 70 '
70 75
78 74
74 74
74 74
DGM
AVG
76.5
77.5
79.75
69.26
69.00
70.15
75.50
73.75
73.50
Facility
FINAL
I 25-40 I
ELAPSED
TIME(MIN)
a
AVG (P,.,)
25.4
§§90
2.90
2.90
§§.20
1.20
1.20
13.50
13.00
13.00
New Calibration 2013
~
4.£12
.!.mi
4,3827
~
~
~
.!:!.1.n
4.71151
IF Y VARIATION EXCEEDS 2.110%,
ORIFICE SHOULD BE RECALIBRATED
~
4.4691
~
AVG•
~
~
4.71i7
AVG•
4.9040
4.7224
Yill
AVG:
~
!,!!!!!!
.Y!!
l.!!!!2
l,!!!J2
l:J!!!!
~
1.009
~
~
~
1.003
1
:Ml
~
::!!:!!!.
The following equations are used ID calculate lhe standard volumes of air passed through lhe DGM, V m (sld), and lhe critical orifiCe, V.
(sld}, and lhe DGM calibration factor. Y. These equalions are aulomalicaHy calculated in !he srreadshee! above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = [JJW{]
(1)
(2)
(3)
Vm,,.,,, = K, • f·'m • Pbnr+!,l!.H /13 6)
Tm
Vc.·r 1 .. .,,~ = K '•
= Net volume of gas sample passed through DGM, corrected to standard condrtions
K, = 17.64 'Rim. Hg (English), 0.3858 'Kimm Hg (Melric)
T.., = Absolute DGM avg. temperature ("R • English. 'K -Mel ric)
= Volume or gas sample passed through the critical orifice, corrected to standard conditions
T-= Absolute ambient temperature ('R-English, 'K-Meine)
K' = Average K' factor tram Critical Orifoce Calibration rc'i .. llll Y= -J"1n,,.,,,J
= DGM calibration factor
AVERAGE 6.Ha =I 1Ji5Q
2
6.He = ( 0.75 9 ) .<l.H (Vm{std)\
v.,(sld) v.. J
Temperature Sensors
Reference In Out
"F
33
67
202
"F
34
68
203
"F
34
68
203
!:ill
1.717
.1:Zl!!
.till
l.ill
~
.1&!!!
.!ill
j,ill
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES -:S-.. ;,
1) Select three cntical orifices to calibrate the dry gas meter wh1ch bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure.
3) Run attested vacuum (from Onfice Calibration Report). for a penod of \1me
necessary to achieve a mmimum total volume of 5 cubic feet.
4) Record data and mformat1on m the cells. YELLOW cells are calculated.
METER SERIAL ll:j.....:=:..:.::::=~
CRITICAL ORIFICE SET SERIAL II:.._ _ __;;...__, EQUIPMENT ID II:
K' TESTED
.----.----l FACTOR I VACUUM I I RUN II I IAVG) (In Hg}
0
G
G
2
3
2
3
2
J
0.8137 12
0.8137 12
0.8137 12
0.5317 12
0.5317 12
0.5317 12
O.JJ07 12
0.3307 12
0.3307 12
88.612
94.007
99.387
105.106
110.310
115.878
121.205
126.327
131.458
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
94.007 5.395 65 78
99.387 5.380 65 79
104.803 5.416 ~ 79
110.310 5.204 m 75
115.878 5.568 m n
121.084 5.206 m n
126.327 5.122 72 76
131.458 5.131 72 76
137.053 5.595 72 76
79 75
79 75
80 ~
n " n n
~ n
76 71
76 72
76 72
75
75
75
n
n
n
72
72
72
DGM
AVG
76.75
71.00
77.25
72.75
74.00
75.00
73.75
74.00
74.00
FINAL
,-25.45 J
ELAPSED
TlME(MIN)
8
5.00
5.00
5.00
7.50
8.00
7.50
12.00
12.00
13.00
ENVIRONMENTAL SUPPLY COMPANY
AVG tp,.,)
25.45
3.00
3.00
3.00
1.20
1.20
1.20
§ 44
44
2014 Pre-Calibration Console 9
~
~
4.5676
4.4031
~
~
~
4.3217
4,7125
IF Y VARIATION EXCEEDS 2.00',(,,
ORIFICE SHOULD BE RECALIBRATED
l
~ !!.!ru.
~ 0.996
4.5203 ~
AVG= 0.993 ~.96
4.4097 1.,.W
~ 1.001
4.4097 1.005
AVG= ~ !1m
~ !,Q1i
4.380 .till
4,7450 L.QQ!
AVG= 1.012 !1.2!
The following equations are used to calculate the standard volumes of air passed through the DGM, V m (std), and the critical orifice, v. (std). and the DGM calibration factor. Y. These equatiOns are automatically calculated 1n the spreadsheet above. AVERAGE DRY GAs METER CALIBRATION FAcToR, Y = Qooi I
(1)
(2)
(3)
I·,,.,,, ~ 1\ I • I'm• !'hell'+ (Mill J 6)
1iu
I#Lr _A:' l'har • (:-) ,,,. .. J l'anlh
= Net volume of gas sample passed through DGM, corrected to standard condi\1ons
K, = 17 64 "Riin, Hg !English) 0 3858 "Kimm Hg IIVIetroc)
T m = Absolute DGM avg. temperature ("R-English, "K -IVIetroc)
= Volume of gas sample passed through the critical orifice, corrected to standard conditions
T ~• = Absolute ambient temperature ("R -English "K -IVIetroc)
K' = Average K' factor from Crollcal Onfrce Cahbratran _l'cr!_~
-,~, •• M•
= DGM cahbratron factor
AVERAGE li.He =( 1.652 I
2
£\.HI!!!= ( 0.75 B ) Ll.H (Vm(std))
V.,(stdl Vm
Temperature Sensors
Reference In Out
•F
32
72
201
•F
33
73
202
•F
33
73
203
.1.lli
!,ill
1.741
!,ill
1.648
1.,lli
.1lli
1.565
~
Console 9 Pre-test 2014
. . .I
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES ~ !ifflii!tDifi ... RM<fi@·'m·-=: iii! -......... ----
1
1) Select three crrtical onfices lo calrbrate the dry gas meter whrch bracket lhe expected operaling range
2) Record barometric pressure before and after calibrallon procedure ENVIRONMENTAL SUPPLY COMPANY
0
0
G
3) Run at tested vacuum (from Onlice Cahbratron Report), for a period or lrme
necessary to achreve a minimum total volume of 5 cubrc feet
4) Record data and rnlonnation rn the cells, YELLOW cells are calculated
METER SERIAL #:I ·-----I
CRITICAL ORIFICE SET SERIAL U:1 ·----1 EQUIPMENT 10 #:
K' TESTED
FACTOR !VACUUM
RU;;, (AVG) (In Hg)
2
J
2
3
2
3
0.8137
0.8137
0.8137
0.5317
0.5317
0.5317
0.3307
0.3307
0.3307
13
13
13
12
12
12
13
13
13
§
141.101 148.155
148.165 154.241
164.241 159.683
§
.0
.D
.0
7.054
6.086
5.442
.0
.D
.0
I ll 1-l I
75 57 65 63 72
76 65 70 72 77
76 70 c__]!__ 77 78
~--
Fl-1111
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
DGM
AVG
0
0.00
64.25
71.00
75.50
0.00
0.00
0.00
Facility
~ AVG(P.,,)
I zs.8o I 25.80
ELAPSED
TIME {MIN)
0
§§
§ 0
20
10.50
9.00
8.00
§§
Energy Fuels
6.1483
6.Z371
~
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
AVG=
6.2291 1.013
~ !.ill
4.7460 1.022
AVG= 1.018 ~
AVG=
The loliolwlg equa110ns are used lo calculate lhe standard volumes of ar passed through lhe OGM, V~ (sld). and lhe critical ortftee, V0
(Sid). and lhe DGM cabbfalion faclor Y These equalions are automatically calculaled rn the Sjl(eadsheet above AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = r-1.018 ]
(1)
(2)
(3)
I"m,.,,,, "J.:,•l"m• f'har+( \11113 6) ]-.~~--~~
J l 'I",HI, J..·•,. l'h11r • (-) ,_;,,,,,
" Net volume or gas sample passed through DGM, corrected to standard condrtions
K1 = 17 64 °R/tn Hg (English), 0 31158 "KKmm Hg (Metric)
T m = Absolute DGM avg temperature (0R -English. "K -Metric)
= Volume or gas sample passed through the critical orifice corrected to standard conditions
T,mo = Absolute ambtenl temperature ("R-English "K-Meine)
K' = Average K' factor !rom Crihcal Onlice Cahbrahon l"n ;,l-1, = DGM cahbrahon factor
l"m,.:.ll
AVERAGE ~HI!!=[ -a5rJ
~HII! = ( 0.75 0 )2 dH (Vm(std))
Vc1(std) Vm
Temperature Sensors
Reference In Out
"F
33
67
202
"F
34
68
203
"F
34
68
203
1.672
1.650
!,ill
Type S Pitot Tube Inspection Oat<~
Date _____.::\_?..,__( I_Z.,__{ :..=11_ Pttot Tube ldcntilicauon __ ..:.1....;€;>:.._-_(].:::_ _____ _
..
C< Tcchnic tan
,.,.
Dt= ·3"'t-) Ill
r. = .... ,~(.. In
rs = . '-1 '1 L In
[tl < 10" a,= •
((1<100 u!= ,0
p, < 5" B I = __ ,;.2=----
Pl= ___ 2 __ _
Z $0 125 in Z = _..;.•_o_:o:...~.:._ __ in.
·Y ~ =------... w w .. -+ __.....~-·--·~--
W :S 0 03125 in w = __ . o_o__:e __ m
W > J mches w = __ ....;(.._._)_-__ In
Z > 3/4 inch Z= ______ m
I I r t:, ., •. ,. ..•.
. · ··{ ·:~ 1]-··-• -~-----y ~ 3 inche.s Y = __ 3_, _.(' __ .... m
The pilot tube meets the spccilications for a calibration factor of0.84? 'I~ ~
Tcmpt'rn!Urc Sensor CnlihmiiO'.::n:_.. _____ _
Reference
:J ~df Temperature Tcm ncrature Tompcrntnn::
Source Reference Sensor Dit1crence ~::{·· :;Ji-< (Medium) (''f) ("f) t·"F>
AIR /2.. lL 0
Probe Continuity '(e. s
Heat Check 248 y~s L{O
AIR 71.. lz.. 0
ICE WATER 33 1y [
Stack BOIL WATER Z-ol. 2.o L 0
SILICONE OIL
£
1 ypc ~ l'tlol J ubc Inspection Data
Dat~ . Ptt~t Tube ldrntificntion: ___ 'l_;__:f.!.--_-____.:{;1~----
...
Dt= ·'1 "=1 ~ 10
r ..... ·~52. In
Is P A = P !l ? _ _.'{'-~:;::.:~::...._ ____ _
Is L05 • D1 !> 01 !> 1.50 • D, ? __ '{.._-e..-=--~-----
Pa = . <i) 2... In
q, < 10" CLt = 0
CJ.1 < 10° al = {)
r11 <.so ~~=------·
z ]~ z~ o 125m .oH, Z= Ill
~ ~
~~w -~ -·--· -· --~~ W ,; 0.03125 in. W= •ooB m
~-\V > 3 IIICh~S \V= 1-In
,., ... -""" .... ·@-E-}.:mJ ___ ~, Z > 314 inch Z= In
/
Y= 3, l
The pi tot tube meets the specifications for a cahbralion factor ofO.R-P
~-·
Stack
Tcltt(!Cll\hue ScnsorC:~hht~uon
Temperatur~
Source
(Medium)
AIR
Continuitv
Heat Check 248
AIR
ICE WATER
BOIL WATER
SILICONE OIL
Reference Sensor
("f) ("f)
"2.50
2o3
Tclllpcratllt~
Dtffcrence
(qF)
TETCO
Sample Box Temperature Sensor Calibration
Dare: 12/13113 Cal ibraror. Dean Kitchen Rel;:rcncc: Ome~a CL3512A
Thermocouple Temperature Temperature Temperature
Unit ID Source Reference Sensor Difference Location (:\ledium) ("F) ("F) ("F)
Water .,., 34 2 Oven .J_
Water 204 203 -I
A Oven (4) Water 33 34 I
Water 204 202 -2
lmpinger Out Water 33 34 I
Water 204 203 -I
Oven Water 33 33 0
Water 204 202 -2
B Oven (4) Water 33 34 I
Water 203 203 0
lmpinger Out Water 32 33 I
Water 204 202 -2
Water 32 .,., I Oven .J.J
Water 204 203 -I
c Oven (4) Water 33 34 I
Water 204 204 0
Water .,., .,., 0 lmpinger Out .J.J .J.J
Water 203 202 -I
Oven Water 33 34 I
Water 203 203 0
D Water .,., 34 I Oven (4) .J.J
Water 204 204 0
Water .,., 33 0 lmpinger Out .J.J
Water 204 202 -2
Oven Water 33 34 I
Water 203 202 -I
E Oven (4) Water 33 33 0
Water 204 203 -I
Water .,., 34 I lmpinger Out .J.J
Water 204 203 -I
Oven Water 33 34 I
Water 204 202 -2
F Oven (4) Water 33 34 I
Water 204 202 -2 '
lmpinger Out Water 33 33 0
Water 203 202 -I
Water .,., 34 I lmpinger Out G .J.J
Water 204 203 -1
Impinger Out H Water 33 34 I
Water 204 202 -2
Water 33 .,., 0 lmpinger Out I .).J . Water 204 202 -2
Water ..,., 34 I Jmpinger Out J .J:)
Water 203 202 -I
APPENDIX F
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
August 27, 2014
SECOND QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGYFUELSRESOURCES
SOUTH YELLOW CAKE SCRUBBER
YELLOW CAKE DRYER BAGHOUSE
GRIZZLY BAGHOUSE
BLANDING, UTAH
June 16-18, 2014
by:
TETCO
391 East 620 South
American Fork, UT 84003
Phone [phone]
Fax [phone] fax
•
CERTIFICATION OF REPORT INTEGRITY
Technical Emissions Testing Company (TETCO) certifies that this report represents the truth as
well as can be derived by the methods employed. Every effort was made to obtain accurate and
representative data and to comply with procedures set forth in the Federal Register.
Dean Kitchen
R vi.e\1 er: ______ _,c,/&~· .:::..e:z_c'---~--'-==--
Date: _______ __,tf"~:).-.__6_-....:..../_t.f.:..____
jj
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ................................................. , ........... 1
Test Location and Type of Process ........................................... 1
Test Dates ........................................................... , ... 1
Pollutants Tested and Methods Applied. . ..................................... 1
Test Participants .......................................................... 2
Deviations From EPA Methods .............................................. 2
Quality Assurance. . . . . . . . . . . . . . . . . . . . . . . . .. . . . . . . . . . . . . . . . . . . . . ........... 2
Summary of Results
Emission Results ......................................................... 3
Process Data ............................................................. 3
Description of Collected Samples ................................ , ..... , ..... 3
Discussion of Errors or Irregularities .......................................... 4
Percent Isokinetics ........................................................ 4
Source Operation
Process Control Devices Operation. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ............. 5
Process Representativeness ................................................. 5
Sampling and Analysis Procedures
Sampling Port Location .................................................... 6
Sampling Point Location ................................................... 6
Sampling Train Description ................................................. 7
Sampling and Analytical Procedures .......................................... 7
Quality Assurance ......................................................... 7
Appendices
A: Complete Results and Sample Calculations
B: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
Ill
Table
I
II
ill
N
v
VI
Figure
LIST OF TABLES
PAGE
Measured Radionuclide Emissions ........................................... 3
Percent Isokinetics ......................................................... 4
Sampling Point Location ................................................... 6
Complete Results, South Yell ow Cake Scrubber ....................... Appendix A
Complete Results, Yell ow Cake Dryer Baghouse ....................... Appendix A
Complete Results, Grizzly Baghouse. . .............................. Appendix A
LIST OF FIGURES
1 Facility Schematic Representation South Yellow Cake Scrubber. .......... Appendix D
2 Facility Schematic Representation Yellow Cake Dryer Baghouse .......... Appendix D
3 Facility Schematic Representation Grizzly Baghouse .................... Appendix D
4 Schematic ofMethod 5/114 Sampling Train ........................... Appendix E
iv
INTRODUCTION
Test Purpose
This test project was conducted to determine the total radionuclide emissions from the South
Yell ow Cake Scrubber, Yell ow Cake Dryer Baghouse, and Grizzly Baghouse exhausts in terms
of Curies per dry standard cubic foot (Ci/dsct).
These tests were for U-Nat and Th-230 on the Grizzly Baghouse and U-Nat, Th-230, Ra-226,
and Pb-210 on the South Yellow Cake Scrubber and Yellow Cake Dryer Baghouse.
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Uranium ore is
processed into yellow cake, which is shipped to other facilities for additional processing. There
are two yellow cake dryers with individual scrubbers. Both dryer enclosures discharge into the
Dryer Baghouse. The Packaging enclosure also discharges into the Dryer Baghouse. The South
Yellow Cake (NYC) dryer was the only operating dryer at the time of the test. The North Yellow
Cake Dryer was not operating at the time of the test. The Grizzly Baghouse serve as the main
dust control device for the raw ore unloading and conveying to the processing building.
Stack schematics are shown as Figures 1 though 3 in Appendix D.
Test Dates
The first test run on the SYC Scrubber commenced the afternoon of June 16, 2014 and was
completed the following morning. The second run started June 17t, 2014 and was completed the
morning ofJune 18,2014.
One test run was completed on the Yellow Cake Dryer Baghouse June 17, 2014.
One run was completed on the GrizzlyBaghouse June 18,2014.
Pollutants Tested and Methods Applied
The tests were a determination of radio nuclide emissions in accordance with EPA Method 5/114.
Test run filters and front wash residues were sent to Test America located in Richland,
Washington for radionuclide analysis.
Test Participants
Test Facility
State Agency
TETCO
Garrin Palmer
None
Doug Olsen
Jeff Graton
Deviations From EPA Methods
None
Quality Assurance
Mike MeN amara
Testing procedures and sample recovery techniques were according to those outlined in the
Federal Register and the Quality Assurance Handbook for Air Pollution Measurement Systems.
2
SUMMARY OF RESULTS
Emission Results
Table I presents the findings of the test in pi co Curies per dry standard cubic foot and pounds per
hour. Tables IV-VI in Appendix A have more detailed information.
Grizzly Baghouse
1
2 0.06
AVE 25.4
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Scrubber water flow, pressure drop readings (~p)
were recorded and are found in Appendix D. The Dryer Baghouse pressure drop readings (~p)
were recorded and are found on the test run sheets. Production data is retrained by Energy Fuels
Resources.
Description of Collected Samples
The test filters for the South Yell ow Cake Scrubber were heavily covered with an off-white
colored particulate. The front washes were clear in appearance.
The test filters for the Yellow Cake Dryer Baghouse were lightly colored with a tan colored
particulate. The front wash was clear in appearance.
The test filters for the Grizzly Baghouse were had no visible particulate. The front wash was clear
m appearance.
3
Discussion of Errors or Irregularities
None.
Percent lsokinetic Sampling
Each of the tests were isokinetic within the ±10% of 100% criterion specified in the Federal
Register. They also meet the Utah State Department of Environmental Quality, Division of Air
Quality specification of isokinetic sampling point by point. !so kinetic values for each test run are
presented in Table II.
Run#
1
2
South Yell ow Yell ow Cake
Cake Scrubber Dryer Baghouse
101 98
I
100
Grizzly
Baghou e
97
--------
4
SOURCE OPERATIO
Process Control Devices Operation
All process control devices were operated normally. Recorded scrubber water flow, pressure and
baghouse ~p readings were recorded and are found on the test run sheets or in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND ANALYSIS PROCEDURES
Sampling Port Location
The inside diameter of the South Yellow Cake Scrubber stack is 12.75 inches. The two, four-inch
diameter sample port are located 28.24 diameters (30 feet) downstream from the last disturbance
and 6.59 diameters (7 feet) upstream from the next disturbance. Figure 1 in Appendix Dis a
schematic of the stack.
The inside diameter of the Yellow Cake Dryer Baghouse stack is 16.0 inches. The two, four-inch
diameter sample ports are located 28.38 diameters (454 inches) downstream from the last
disturbance and 3.56 diameters (57 inches) upstream from the next disturbance. The sample port
locations are depicted in Figure 2 in Appendix D.
The inside diameter of the Grizzly Baghouse stack is 18.75 inches. There are two, three-inch
diameter sample ports located 2.56 diameters (48 inches) downstream from the last disturbance
and 1.31 diameters (24.5 inches) upstream from the next disturbance. The sample port locations
are depicted in Figure 3 in Appendix D.
Sampling Point Location
Table III shows the distance of each sampling point from the inside wall according to EPA
Method 1. Each point is marked and identified with a wrapping of glass tape and numbered.
These points are determined by measuring the distance from the inside wall.
Sample Point
2
3
4
5
6
7
8
9
10
11
12
NYC Scrubber
0.85 0.70 0.50
3.19
9.56
11.90
6
2.34
4.74
11.26
1.26
2.21
3.32
4.69
6.68
12.08
14.06
15.43
16.54
17.48
18.25
Sampling Train Description
To determine the actual emission rates for this stack, 40 CFR 60, Appendix A, Methods 1-51114
were followed.
All sampling trains were made of inert materials, (Teflon, stainless steel and glass) to prevent
interference of the sampled gas and particulate.
The stack analyzers used to conduct Methods 1-5/114 are constructed to meet the specifications
outlined in the CFR. The temperature sensors are K-type thermocouples. Heater, vacuum and
pi tot line connections have been designed to be interchangeable with all units used by the tester.
A 316 stainless steel probe liner was used for the tests. Figure 4 in Appendix E is a sketch of the
Methods 5/114 sampling train.
Sample boxes were prepared for testing by following the prescribed procedures outlined in
Methods 5/114.
Sampling and Analytical Procedures
All sampling and analytical test procedures were as specified in 40 CFR 60, Appendix A,
Methods 5/114.
Quality Assurance
All equipment set-up, sampling procedures, sample recovery and equipment calibrations were
carried out according to the procedures specified in 40 CFR 60 and the Quality Assurance
Handbook for Air Pollution Measurement Systems.
7
APPENDIX
A: Complete Results and Sample Calculations
B: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
8
APPENDIX A
Table IV Complete Results, South Yell ow Cake Scrubber
Table V Complete Results, Yellow Cake Dryer Baghouse
Table VI Complete Results, Grizzly Baghouse
Nomenclature
Sample Equations
A
TABLE IV SYC Scrubber
COMPLETE RESULTS
Energy Fuels CORPORATION, BLANDING, UTAH
SOUTH YELLOWCAKE SCRUBBER EXHAUST
Symbol DescriEtion Dimensions Run #1 Run#2
Date 6/16,17/2014 6/17,18/2014
Filter# 6206 6208
Begin Time Test Began 13:53 13:14
End Time Test Ended 12:09 12:22
Pbm Meter Barometric Presswe In, Hg. Abs 24.30 24.30
dH Orifice Pressure Drop In H20 1.103 1.066
y Meter Calibration Y Factor dimensionless 1.000 1.000
Vm Volwne Gas Sampled--Meter Conditions cf 343.714 337.542
Tm Avg Meter Temperature of 76.9 76.2
;/M Sq Root Velocity Head Root ln. H20 0.5060 0.4998
Wt_.c Weight Water Collected Grams 434.1 433.1
Tt Duration of Test Minutes 480 480
cp Pilot Tube Coefficient Dimensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.2745 0.2745
C02 Volume %Carbon Dioxide Percent 2.00 1.20
Oz Volwne% Oxygen Percent 17.50 18.70
N 2 &CO Volume% Nitrogen and Carbon Monoxide Percent 80.50 80.10
Vmstd Volwne Gas Sampled (Standard) dscf 275.442 270.819
Vw Volwne Water Vapor scf 20.468 20.421
Bws (measured) fraction H20 in Stack Gas (Measured) Fraction 0.069 0.070
Bw, (saturated) fraction H20 in Stack Gas (Saturated) Fraction 0.118 0.114
Bw, Fraction H20 in Stack Gas * Fraction 0.069 0.070
xd Fraction of Dry Gas Fraction 0.931 0.930
Mct Molecular Wt Dry Gas lb/Jbmol 29.02 28.94
M, Molecular Wt. Stack Gas lbllbmol 28.26 28.17
%1 Percent Isokinetic Percent 100.9 100.2 AVG
T, Avg Stack Temperature OF 113.2 112.0 112.6
A, Stack Cross Sectional Area Sq Ft. 0.887 0.887
PG Stack Static Pressure In H20 -0.280 -0.280
PbP Sample Port Barometric Pressure ln. Hg. Abs 24.23 24.23
Ps Stack Pressure ln. Hg. Abs 24.209 24.209
Q, Stack Gas Volumetric Flow Rate (Std) dscfin 1.23E+03 l.21E+03 1.22E+03
Oa Stack Gas Volumetric Flow Rate (Actual) cfin 1.77E+03 1.75E+03 1.76E+03
Ys Velocity of Stack Gas fjJm 2.00E+03 1.97E+03 1.98E+03
Curies Radionuclides per sample pCi 13957.4 17.3
Crad Concentration ofRadionuclides pCi/dscf 50.673 0.064 25.368
ERr ad Emission Rate ofRadionuclides pCilbr 3.734E+06 4.646E+03 1.869E+06
* If the measured moisture content is greater than the saturated moisture level (supersaturated),
the saturated moisture value will be used in all calculations (40 CFR 60, Method 4, Section 12.1. 7),
Dryer Bag house 13
TABLEV
COMPLETE RESULTS, PM
Energy Fuels CORPORATION, BLANDING, UTAH
YELLOW CAKE DRYER BAGHOUSE
Symbol DescriEtion Dimensions Run #1
Date Date 6/17/2014
Filter# 6207
Begin Time Test Began 14:00
End Time Test Ended 16:04
Pbm Meter Barometric Pressure In, Hg. Abs 2430
~H Orifice Pressure Drop In. H20 1344
y Meter Calibration Y Factor dimensionless 1.002
Vm Volwne Gas Sampled--Meter Conditions cf 89.030
Tm Avg Meter Temperature OF 84.3
>/M Sq Root Velocity Head Rootln H20 0.7690
Wtwc Weight Water Collected Grams 6.1
Tt Duration of Test Minutes 120
cp Pilot Tube Coefficient Dimensionless 0.84
Dn Nozzle Diameter Inches 0.2220
C02 Volwne% Carbon Dioxide Percent 0.00
02 Volwne% Oxygen Percent 20.90
N 2 &CO Volume% Nitrogen and Carbon Monoxide Percent 79.10
Ymstd Volume Gas Sampled (Standard) dscf 70.568
Vw Volwne Water Vapor scf 0.288
Bws Fraction H20 in Stack Gas Fraction 0.004
xd Fraction of Dry Gas Fraction 0.996
Md Molecular Wt. Dry Gas Jb/lbmol 28.84
Ms Molecular Wt. Stack Gas lb/lbmol 28.79
%1 Percent Isokinetic Percent 97.6
T. Avg Stack Temperature OF 107.1
As Stack Cross Sectional Area Sq. Ft. 1.396
Po Stack Static Pressure In. H20 -0.24
PbP Sample Port Barometric Pressure In. Hg. Abs 24.23
ps Stack Pressure In Hg. Abs 24.212
Qs Stack Gas Volwnetric Flow Rate (Std) dscfin 3.13E+03
Qa Stack Gas Volwnetric Flow Rate (Actual) cfin 4.17E+03
Ys Velocity of Stack Gas fi>m 2.99E+03
Curies Radionuclides per sample pCi 1693.8
Crad Concentration ofRadionuclides pCildscf 24.0021
ERr ad Emission Rate ofRadionuclides pCitbr 4.508E+06
Grizzly (2)
TABLE VI
COMPLETE RESULTS, PM
DENISON MINES CORPORATION
GRIZZLY BAGHOUSE
Symbol DescriEtion Dimensions Run#1
Date Date 6118/2014
Filter# 6210
Begin Time Test Began 8:13
End Time Test Ended 16:21
Pbm Meter Barometric Pressure ln. Hg Abs 24.30
Mf Orifice Pressure Drop In H20 1.837
y Meter Calibration Y Factor dimensionless 1.002
Vm Volume Gas Sampled--Meter Conditions cf 416.247
Tm Avg Meter Temperature "F 84.9
.,ff'l.p Sq Root Velocity Head Root ln. H20 0.2595
Wt_.c Weight Water Collected Grams 12.9
Tt Duration of Test Minutes 480
cp Pita! Tube Coefficient Dimensionless 0.84
Dn Nozzle Diameter Inches 0.4088
C02 Volume% Carbon Dioxide Percent 0.00
Oz Volume% Oxygen Percent 20.90
N 2 &CO Volume% Nitrogen and Carbon Monoxide Percent 79.10
Vmstd Volume Gas Sampled (Standard) dscf 330.057
Vw V olwne Water Vapor scf 0.608
Bws Fraction H20 in Stack Gas Fraction 0.002
xd Fraction of Dry Gas Fraction 0.998
Md Molecular Wt. Dry Gas lb/lbmol 28.84
Ms Molecular Wt Stack Gas lb/lbmol 28.82
%1 Percent Jsokinetic Percent 97.2
Ts Avg Stack Temperature "F 82.7
As Stack Cross Sectional Area Sq Ft 1.917
Pa Stack Static Pressure In H20 -0.056
PbP Sample Port Barometric Pressure In. Hg. Abs 24.27
Ps Stack Pressure In_ Hg. Abs 24.266
Qs Stack Gas Volwnetric Flow Rate (Std) dscfin 1.49E+03
Q. Stack Gas Volwnetric Flow Rate (Actual) cfin 1.89E+03
vs Velocity of Stack Gas tpm 9.85E+02
Curies Radionuclides per sample pCi 103.7
Crad Concentration of Radionuclides pCi/dscf 0.3142
ERr ad Emission Rate ofRadionuclides pCi!br 2.804E+04
APPENDIXB
South Yell ow Cake Scrubber
Preliminary Velocity Traverse and Sampling Point Location Data
Field Data Sheet
Yell ow Cake Dryer Baghouse
Preliminary Velocity Traverse and Sampling Point Location Data
Field Field Data
Grizzly Baghouse
Preliminary Velocity Traverse and Sampling Point Location Data
Field Field Data
B
s = fraction ofwater in stack gas (may have designation of"measured" or "saturated")
"measured" represents measured moisture based upon sample volume and water collected
"saturated" is a calculated value based upon stack pressure and temperature
) = average of initial and final system zero gas calibration bias checks (ppm, percent)
average gas concentration (as measured)
3 = concentration of particulate matter, back half (gr/dscf,lb/dscf, etc.)
i = concentration of condensibles (grain/dscf)
concentration of coarse particulate (gr/dscf)
measured concentration of a calibration gas when introduced in direct calibration mode
concentration of particulate matter, front half, actual stack flow (gr /act)
concentration of particulate matter, front half (gr/dscf,lb/dscf, etc.)
Cavg corrected for initial and final system bias checks (Equation 7E-5)
average of initial and final system upscale gas calibration bias checks (ppm, percent)
actual concentration of upscale calibration gas
1 = concentration of metals (ppm, J..lg/fe, etc.) atomic symbol replaces "metal"
~ = percent carbon dioxide in the stack gas
pitot tube coefficient (0.84)
) = concentration of PM10 particulate (gr/dscf)
i = concentration of radionuclides (pCi/dscf)
; = measured concentration of a calibration gas when introduced in system calibration mode
-= Any species symbol may replace X. Units may be expressed as ppm, lb/dscf, etc.
) = actual gas concentration corrected to required percent 0 2
; = Measured radionuclides per sample. Units may be pCi or uCi.
; = jet diameter (em)
~=Dioxins and Furans (See laboratory report for D/F descriptions and nomenclacture)
[ = orifice pressure drop (inches H20)
l = orifice pressure (inches H20)
1 = orifice pressure head (inches H20) needed for impactor flow rate
nozzle diameter (inches)
> = stack flow pressure differential (inches H20)
) = 50% effective cutoff diameter of particle (em)
diameter of the stack (feet)
, = percent excess air
l = emission rate of back half particulate (lb/hr)
i = emission rate of condensibles (lb/hr)
emission rate of coarse particulate (lb/hr)
emission rate of front half particulate (lb/hr)
emission rate of a gas (lb/hr)
emission rate per mmBtu of fuel
) = emission rate ofPM10 particulate (lb/hr)
i = emission rate of radionuclides (pCi/hr)
-= emission rate of compound which replaces X. Units are usually in lb/hr.
> = Dry based fuel factor. Ratio ofthe gas volume of the products of combustion to the heat content
See 40 CFR 60, Appendix A, Method 19, Table 19-2 for fuel factor values.
Cunningham slip correction factor
mean free path of molecules in gas phase (em)
1 = million Btu
1 = million Btu
, -mass of particulate matter in probe and front wash (mg)
) -mass ofPM10 particulate (milligrams)
molecular weight of stack gas, wet basis (lb/lbmol)
c-mass of species "X". Units may vary and other descriptive subscripts may apply.
gas viscosity (poise)
molecular weight of gas species (g/gmol)
I= number of jets per plate
2 = percent nitrogen in the stack gas
2 = percent oxygen in the stack gas
> = average of the square roots of l'lP (may also be referred to as ASL'lP)
1 = square root of l'lP at point 1 of the current test, Method 201A
'-square root of l'lP at point 1 of the previous traverse, Method 201A
average of the square roots of l'lP from the previous traverse, Method 201A
n absolute barometric pressure at the dry gas meter (inches Hg)
absolute barometric pressure at the sample location (inches Hg)
1 -stack static pressure (inches H20)
absolute stack pressure (inches Hg)
j = absolute pressure at standard conditions (29.92 inches Hg.)
) = time of test (minutes)
t = sample time (duration in minutes) at first sample point for Method 201A
sample time (duration in minutes) at sample point "n" for Method 201A
st = target test time for Method 201 A (minutes)
stack gas volumetric flow rate (acfm)
stack gas volumetric flow rate (dscfm)
actual gas flow rate through the cyclone (acfm)
actual gas flow rate through the impactor (acfm)
1 -wet stack gas std. volumetric flow (ft3/min, wscfm)
~ = gas constant (21.85 inches Hg*ft3/(lbmol*R))
particle density (1 g/cm3)
stack gas density (g/cm3)
stack temperature (°F)
stack temperature CF)
j = absolute temperature at standard conditions (528°R)
t = Duration of test run in minutes. Also see 8
mean molecular speed ( cm/s)
1 = sample volume (ft3) at meter conditions
j-volume standard (dscf), sample volume adjusted to 68°F and 29.92 inches Hg.
velocity of stack gas (fpm)
volume water vapor (set) at 68°F and 29.92 inches Hg.
weight of the condensed water collected (grams)
j = fraction of dry gas
meter calibration Y-factor (dimensionless)
1 = dimensionless inertial impaction parameter, 0.14
General Sample Equations
%1 = Vmstct • (Ts + 460) • 1039 I (8 • Vs • Ps • Xct • Dn2)
As= (Ds2 I 4) • 1t
Bws = Yw I (Vmstd +Vw)
C8 = M8 • 0.01543 I Vmstd
Ccand = Mcand • 0.01543 I Vmstd
Ccars =Mears • 0.01543 I Vmstd
Cra = Tstd • ClP • Ps • Xd I [Pstd • (T m + 460)]
Cr= MlP • 0.01543 I Vmstd
CPMIO = MPMJO • 0.01543 I Vmstd
Crad = CuriesiVmstd
Cgas (carr)= Cgas • (20.9-desired %02) I (20.9 -actual %02)
case DPso = --J [J.LS • \jl" N • 7t • D/ • 18 I (Kc • Pp • Qsce • 4)]
I 0.2091 0 7091
PM10 DPso = 0.15625 • [(T5 + 460) (Ms • P5)] • (J-L5 I Qsc)
EReanct = Ccond • Qs • 0.00857
ERears = Ccars • Qs • 0.00857
ERF = Cr • Qs • 0.00857
6 ERgas = Pstd 0 Qs • Mwgas • Cgas • 60 I (R 0 Tstd • 10)
ERgas = Cgas(lb/dscf) • Qs • 60
(Either ERgas equation gives equivalent lblhr values to 3 sig. figures)
ERmmBtu = Cgas(Ib/dscf) • Fd • (20.91(20.9-%02), Method 19 Equation 19-1
ERPMIO = CPMIO • Qs • 0.00857
ERrad = Crad • Qs • 60
Kc = 1 + 2 • A • 1.257 I Dp5o
A= J-Ls I (0.499 • Ps • Urn)
Md = C02 • 0.44 + 02 • 0.32 + N2 •0.28
Ms = (Md • Xd) + (18 • Bws)
J..ls = [51.05 + 0.207 • (T5 + 460) + 3.24 •10-5 • (T5 + 460)2 + 0.53147 • %02-74.143 • Bws] • 10-6
Ps = PbP + (PG I 13.6)
81 = (--Jl'iP1' I --Jl'iP'ave) • (81est I pts)
en = el • .YL1P n I .Y!'iP I
Qa = Ys • As
Qs = Qa • Xd • Ps • Tstd I [(Ts + 460) • Pstd]
Qsc = [(T5 + 460) • Pstd I (Tstd • P5)] • [(Vmstd + Yw) I 8]
Qsce = [(T5 + 460) • Pstd I (Tstd • P5)] • [(Vmstd + Yw) I 8]
Qw= QsiXd
Ps = Ps • Ms • 3386.39 • 10-6 I [R • (Ts + 460) I 1.8]
Urn= 100 • --J {[R • (T5 + 460) I 1.8 • 8 • 103] I [1t • M5]}
Vmstd = Vm • Y • Tstd • (Pbm + L\H I 13.6) I [Pstd • (T m + 460)]
Vs = 85.49 • 60 • Cp • --J!'iP • --J [(Ts + 460) I (Ps • M5)]
Yw = Wtwc 0 0.04715
Xd = 1-Bws
South Yell ow Cake Dryer Scrubber
Facility Energy Fuels
Stack Identification South Yellow Cake Dryer Scrubber
r
A Date
Darornetric Pressure
N Pb01 in Hg PbP in Hg
B Static Pressure (P0 ) inHp
Estimated Moisture (Bw,) 4-6% ~~
Sample Height from Ground 70 feet
Comments:
I•
Stack Dia 12.75 Reference: 0
Po1 ts are 7' Upstream from next disturbance
Ports are 30' Downstream from las\ disturbance
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B c D E F
' 1 6.7 0.85 0.85
2 25.0 3.19 3.19
, 75.0 9.56 9.56 .J
4 93.3 11.90 11.90 .. -
Averages:
Ts L. Flow ----
i\.P Vi\.P ---------
L. Flow!
~p .
KEY=>
~ ~ '? Field Data Sheet \Q TETCO r
Fil!er&ZD Sample Box C 4-
Plant: Energy F!lels • \
Date: <tl l(v (t\J{ {p L1-\ty{ Location: Souti;r"'(ellow Cake Dryer Scrubber
Operator: "' '
Traverse 11 Ti~e II DGM Tonp (T .J
Clock I Min {!l) II c•'> II ''" HP> I Out I In
c.P DGM
Pomt
1
1
1
2
2
2
3
3·
3
4
4
4
1
1
1
2
2
2
3
3
3
4
4
4
Total
Avmsge
i?,'-7)1 o 11~\''-\--500 lr-z.}d"l[TI\1-\~'Z.-nf'/ ~ t(,_o l1JR~ 1~2V ]'Z.-7l l s-11!1-¥:11~
C£0 ~~~-W-tr{J]-z~] f. v_Z) I l· u'il:?ll \l i? I "l§fll--s7t& )8j _ _Loj,ll;:tl2~-;f.>
tDv 112.:rQ.&tl{][.J-~llt-(~]~[ If~ I -z-Ctzt-z.'?:OI--2--~~u rrf:-L:l -=tcs-
11. o I~D~s-o_][_-J{ )fTu'"'fL l·dc.~~ll!w I ZC;z_lz1s-l1. 3~T&3~r7I I 1
tv\ o 11 wl~-~ >rl .1-~ 1r 1-o--f I t·u1 1r-Z?JI 1 ~o I zvviZ--t, 1 I '2.. ~or=~ ?l ?il 1-f5
\~U II[P'7Z-·'72Vl1 -2--~1r [-o~l (~ o~][ 5 ILIJ'1 I wz_[ l~~T 1-s='11Sb--ll 1-&1 -::t-1
\ ((O llf_p..{!P.1-z"t41.1-1JlJ·lS".I J-~~~-~II'TI~!Zs-:3fl'-{PI z. )rl 5'~ II 1~ s-o .k I~ Gv .Jiu {; I . 'l-{Z-!1. t --:1-lrl· t s T1:-I 5lr51Jt-vD I -t1') I1-5YT t 7 TI 6) II _7-fl 9-~
1, 7.-~ If" r~._{~ (.p J-z. Lt II H\_ 1'-:11 lr-~JI l \ Ct lzs \ 1~?-z:..Tz' \I 5"'o II rt I ~\
'¥.:D'1 11-~v l[ &~'1-~vr II. 1-~ 11-.,~ --, ·"~ ~ 1~11 i os 11. ') 7:1 z 30T2 > t I u. Lf J[ 3-_ol_7_0 ~
1,o0 1113 1 :soolf~ ~r I\.\~ IRII \\ -~T'l~:Z:,IZ:-N TZtf?if~Tll 1li czr r
~~\{~-~z_~LITJ~r l[./c/ICLJI 1D( 1~\_u ~~~z~r~ll 7 ~1 y ~ ~ ~D_._<TV~TlL l-\-t..-ISJ tt/fL.--;5 ~~I 1'"1{ ~ 'ti-O ~
"-~" 0 111-:t~. x-"1?1[ -is-r TO?-[ (. 0 y /!Til ll D I Zl/'/ r-z>s-=rz3b I (p 'l ll +& I ~0
"74:~ I~·IMl~ II{. r c. I r.t c. /Ia! 1o ~ I ~031 '2 3~1 -z ~s-=~r 0~-r--=r=-lr <K-D
~~~'"1-Joo:J[~/ I·IZ It· !7 /~I ros-[-z..u.7 [ ~ 3Sf"Z3&I ~0 if'~~ I ~D
~~o ll~lS!" ~ c;~o11 -2_ ~~ ~s 1-.~ c.,JI-z;--_]IJolt IZ:'z:l [ 1-_Z_"L[-'Z 7~1-'~7 l ~I ~ o
,xu\.0 lr<6"~1.~ U.~l . z.=l Ill-v 2Ll·o~'Jf---.-01Lro~ D'f'ZTZ. ~srrz3 ~I ~ t II :4-C.., 1 go
~~o 11 %'-flP ·1¥111-z c,+-11 f·o~ IT·D~~] c;-][ i o?j ~'PIT~~T T Z.7vl e:~ II -:;.&I b--o rZ:o~ I.>...I&D-11~&/. 2/L{ j r-~~-+-~---!...f~..:.....j...::::::....L.::....j......:;
~'J.J-Ii -J f 2.· N ~ () z_{p-'-{-+
i-10~ -.' · s-ob()
Additional (Extra) Leak Check Information
DGM before Leak Check Vac ("Hg)
---·-
-z-1-( lP
ll3·'Z..--
Rate lfe/min) DGM After Leak Check
~b'1 1..-
1--{;· I
Vac ("Hg)
I
N
,.
Pa~e Lof---l.-Run #_j_
Bo
12.7 5" Port Reference ___,0,__" _
T___ Upstream from next disturbance
30' Downstream from !asl disW.rb:!.n~
Assumed Moisture 4-6%
Probe 1.\ ----Cp 0.84
Nozzle ~alibration / ~ '1. -:r--~ ,/ 11-r 2--r->
A vg Dn Z y-<-~ .;ches
Gas Bag f-' -i>
Console C(
Y-Factor \.. {;o C7 /
C.Hs l , -t. "'\:')in H,O
Barometr\:(.l¥su.res
Pbm 1, '? [) in Hg
Pb z_"( • z_.'') in Hg P'---,;;:-----
Pa • t.8: in H20
Leak Check: pre
ft'tmin o-·ObY
voc in Hg "2-2-
Post , f
O·OD'1
tv
o·o
G-. S.:
Water Collected ~ ~ • \ g
Time Sampled~ min
Review ~
K=
K=
"' @Tm
@Tm
Rate (ft3/min)
p'V) 7 Field Data Sheet
Plant: Enerr. Fuels ,
Date: fa r~. (f< /, L/ : I ,
TETCO . . -::;:) E J4
Filter t, coy Sample Box .J,:2../ ·---
Location: Sout~llow Cake Dryer Scrubber
Operator: 8
Trav<r.>< Jl Time It
Point
aP
Clock I Min (9) II en'> II c;" H,O) I In
DGM
Page_l_orl Run# L
--
1 Do N
1
1
12~{t1 1 o ll~GuooojlldJ t·o'-r.o~c2-=r~ll~lz;,ll(3Zlz3z_lc,~l~o! =t-o
2 o 1f '+ ~ q~ ~ ["ZiJ I · o 'L r. o t: 131 ~ t 1 _ z ) 0 _ ¥J ~~1-5 G_ '1 '1-/ Stack Diameter 12. 75" Port Reference --"0'-"---
1
2
2
2
3
3
3
4
4
4
1
1
1
2
2
2
3
3
3
4
4
4
Total
Average
'2. 'i?'" {£J I ~-2J ~ IPortsare 7' Upstream from next disturbance C.,-{p 7, 1-"2-• _..-'Ports are 30' Otr.\1fistret~m from li!St disturbance ~~;--r~~~~~~~~~ 7~ Assumed Moisture 4-6%
tOO II t17.."1. ~-(~.LV ]II· Ll ITifiKll, I cj, 12.~( 11_ ~2-'S-~ l s--!l~ 1li!s:-5
1 zo ll<1~-~1.2-? II :.z711 i-o:F--1 t·o111"'5li\E\~I01 IJz -51-ll;-3T.75T~~ ?r'f
NO II q~-z..--2-.sj II z '{ II [-OI.l-1. i)1/113. II ., (CfT?_u.vr· z 53TZ'o/'lfr 5.~ II ~0 17>-;,
t&D II'Tr~Z--<i'lf 11-1:) II~~ -GJ Yll z:r1f-ll~ j'b&o -1 z.s~J-z_5'bf_/P-&-II 1~1 B-1
~~-b-Jiqt)(?D"'h ll-t-5"'11\·o-+l\-611~1 I() 1-z-~~ z.)C)!z.5H l?Z-11--:t-71-~b-
zooii/OCLj.2) -\ 11-i..{> II ~tlt~~ll\l3 lzs--ti'Zk'fl z-v?_l"£.?3 _11 f-01 1-CJ
/~-~~ I zzolltot~.t 1-'111 ~~II r-o-t:ITQllf-l.PJITI1-f-z-s~rz."5<tr'Z~1f-& Lfll1-c.rl +Y
'f; -z-Z--1 z {v-II;O) L C) ·Db II·~(, !It-f/ [I -({ 1!2lll f o q I z~L( I Z-3'-{ I Z J~l t s-11 Ct7 G I f;_h
zC,OIItD'-I-6-:(r:,IILs--llt·o1-l\·crl~l ll0 lz_-q-o lz.&~J ?~VJ I q-~r~oT-=1:,
zfollro5~.'1z-<l!I~J 1-J/+:J Lu'f i~IT\~&~ I ~liS1t~01~11L---I f~.
3 ocll;o ~~ <{"(rt_._L.t:JI r·l) J f·csjiLfll a~[ I z6tf z. 3 vfz..Js--l ~7-11 1-.s-11-CJ
3zoll 1ut5:t-.&Y /II ·7.-q.;IIH\1t·~lll 11\..I I z0:SIZ-3irz3ol ~ez II -:Ji-1 &I
! tt'oll 1 lo \.s-zld-~>II f,\)-1-l r-:-f!ITll~ I -L-vi.!z -si I z 31[ ~ -z_ll1? I :;-~-
3 Wilt I 15" & tiJI 1--s II r. f) 1-1 1. o :}11~1 1 r ~..f lz&5ll3D I Z-3 / I G7'f!IT?T Yo
s~o 111-1. q (~_!~~ tli: I L~~ 11-3(~7~~~ II t-~t -;+.~
'fbC> "c.3-'1 zo ~~[?] tl~l-z 3 7)1-z.-.,[51 . +s ::;. ~
'{ZO 111\.)}. 5'7z-l[. ~~ "JI!-_v 'l:_l t-o ::rll-v-102--rz:q3 r-t351 ,n.>1 >& II 1& I ~ D
--No lit t-:f-1. r--;r II ~--~ II, -o z; I t-b" IWll r 11..-IZi 1 I"L~.;-1 7 ~l.9 I c; ~ II 1-1-l yf
...! ~ o lit ( ~ ~ -1 >lf'll~ll c · o"L--·1 ~-C)vll011 \ ~ -t,-11)LS{ I~~~ I~ -5 t, I & z7111i=l-g I
111; 1 t.l ,,q--uIll { ti ~ . .:;---t-Fl
3)t -~i-~q_1~~
~ .L\~~~
Additional (Extra) Leak Check Information
l ') -S"~
\ -o~~
'[,~~~
l\l·<=>
DGM before Leak Check Vac ("Hg) Rate (fe/min) DGM After Leak Check
)b5-~
1""~ .-u
Vac ("Hg)
Probe _z~f!,__ __ Cp 0.84
Nozzle Calibration
z 14 7:1~-2"±<;-2-1 ~
Avg Dn 7. f. 'j ~inches
Gas Bag (-0 )
Console l{
Y-Factor / -0 () o
AH~ f.'--{~ sJn H20
Barometric Pressures
Pb 'Z'i-JO -H m m g
PbP 2 'f . 2-'J in Hg
Po G · -z.. ~.) in H20
Leak Check: Pre-Post J
ft'tmin o -oo ~ 0 ·C:.O 1
vacinHg '2.. Z.., ~
Pi rot Rare {) -0
lnH,O 5-S:
Water Collected
Time Sampled
Review
Rate (ft3/min) I
I
O·u
~·5
L-/33-j_
K=
K=
'f'}'iJ D '
lA
@Tm
@Tm
g
min
Yell ow Cake Dryer Baghouse
riCIIIJI U l-Jl!) Uii:liU\
Facility Denison Mines
Stack Identification North Yellow Cake Dryer Baghouse
Date
r Barometric Pressure
B Pbm in Hg Pbp in Hg
N Static Pressure (P0 ) in H20
A Estimated Moisture (Bw,) I %
Sample Height from Ground feet
Comments:
Stack Dia 16 Reference 0
Pons are 57" Upstream from next disturbance
Ports arc 468" Downstream from last disturbance
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B c D E F
1 4.4 0.70 0.70
2 14.6 2.34 2.34
3 29.6 4.74 4.74
4 70.4 11.26 11 .26
5 85.4 13.66 13.66
6 95.6 15.30 15.30
-
Averages:
Ts LFiow ----
ll.P -JtJ.P --------
KE'r' =>
IM~
t3
A.
Field Data Sheet
Plant: Denison Mines
Date ~/t7/l "f.
Traverse Time
Point Clock Min (B)
1 l'{~tJ> 0
2 lO
3 2o
4 3o
5 LfO
6 so
1 l5~cM c.o
2 '10
3 80
4 'to
5 leO
6 .iO
. IC.~<i l't.O
DGM
(f'l))
--zq_'{,gl,C(
~01 • (.-=J.5'"
309. t:l:JJ
"'Jl~-770
)Zl . c.r:r
3 Jo, (~f
3~9. ~1{
"3"t<.. t~u
35'{. !Bo
3£, l· ezo
13c..W.·uo
3:-K..I.l~)
~ Sl. esLf
~p 6.H (;n H,OI
(inHaO) Desired Actual
•So LJ~ L.~
•"(t-• t('{ .cr'{ .,:so •'-1 ·'~ •1'2.-L • C.{ '·f. ( ·SC t, f,( I. 8t . ,r,. L, '-l f. f. (
.(, ~ \d·o t.{J
·c. a t..{ z.. (,{L
·G.( t.~~ L.:r-;-
•C.o •. ,&.~ ,, 3"(
·57' 4 ·Zf> t~ z.~
1 b0 L ·:!>~ h~ -
TETCO
Filter (gZo T Sample Box~
Vacuum
(inH!I)
-'i_
'"{
'{
"( s
S_
'I
'l
'{
"{
I(
"{
Location: Yellowcake Dryer Baghouse
Operator: J(\1. M Q~ o-
Temperatures (F)
Stack (T,) Probe Probe Out Filter Effluent
lO~ l.'-ro 230 l.3o .£5
io1-'2.3o 1..:;H' l,"j{' '4't
to~ ?.(.~ Z..lo 2.'10> Sl
l41"+-270 'Z.JZ. 'Z.H ... 5«.t '0 '":l-l.~ Z30 !3'0 5'1
lioc,. IZ.·ft 23\ 231 !ir....
1.07' 170 Z2.( 2-f:f' SB
l() .... ZSo Z.C.l-u.t-c.o
lo'f l(.Q 2.10 no '0 to8 1SS Lit. Z.1 z. ~~
tc8 Z<(~ Z72. ZT'Z. ~0
lot{ Z•fl· lio Z{O 5":J-
Total 9q. o~O l ,r j :z.Z83 / \(.. .!~'U./ \'Z,S ( ./
A ,~ . 71,~v \· '1"t4 \07"·\
Comments: Time Baghou.se ~P Time Baghouse ~P 9 f>tA.trt.\5 ~"' !D"( ct·O ~s~oo g.t,
4'-\'·f\ q.o IS'tU> '\.~
\~:')"! s·r ,s~~ li. \
f"'\ : s ~~ r'it ~ ~<. 5-e ----
DGMI~Il)p (T,.)
Out In
,_-[ 1-":1-'
11 1~
.~( 71"
8) 7{ cro ," ~z. '":fr_
S't :~
t:fu 80
1_(._ 8t
Cf8 8l'
'18 6'{
ere s~
-
'1.0 Z,"Z-a/
s '-{, :>
Page_\_or_l_ Run# __
i B
N ·0
Stack Diameter 16" __ Port Reference _ 0.0"_
Po1'1S are g:___ Upstream from next disturbance
Ports are 466'' Downwt:am from last dlStu.rbanc.:
Assumed Moisture _....:.....___%
Probe "Z.1~l Cp~
Nozzle Calibration
. tn •Z.'t~ -Zz.2.. ··u.~
AvgD, • "Z.l2. inches
Gas Bag Ambient Air
Console ___j
Y-Factor I . oot.
6H@ j.fe-;'L inH,O
Barometric Pressures
Pbm Z. c.{, '3 i) in Hg
Pb0 Z '{ · ·t~ in Hg
P0 -• '!,&.{ in H20
Leak Check: Pre
ft'lmin 0 :-;o:('
,•..:lnHll '2.0·~
~
0.0<'3
~
Pitm,ii= Q•O e>O
lnHP ,.~ 1.0
Water Collected G:, ·l g
Time Sampled ____1_10 min
Review ~
K=
K
@Tm
rn:.-T -..
Grizzly Baghouse
Prelim 12 pts blank
Facility Denison Mines
Stack Identification Grizzlv Baghouse
Date i,( ·~ ft't
r Barometric Pressure
Pbm ~'(. ~0 in Hg Pbr 'lc.4., z~ in Hg
N 'AOB Static Pressure (PG) _ .l'l{'C., in 1-1,0
Estimated Moisture (Bw,) I ~-0
Sample Height from Ground 'lo feet
Comments:
Slack Dia , 18.75 Rcli:rcnce: 3.0 Must use 36" probe or longer to keep bo:-: outside handrail
P<lilS are 24.5" UpstreJm from ne.\t disturbance
Ports ar~ 48" Dm111strearn from last disturbance
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B c D E F
I 2.1 0.50 3.50 ' CJ (,O 1o
2 6.7 1.26 4.26
3 I 1.8 2.21 5.21 .o)~ l/
4 17.7 3.32 6.32
5 25.0 4.69 7.69
6 35.6 6.68 9.68 •&1'-f , ..
7 64.4 12.08 15.08
8 75.0 14.06 17.06
9 82.3 15.43 18.43 ''"6 11(
10 88.2 16.54 19.54
II 93.2' 17.48 20.48
,,,., ""'1
12 97.9 18.25 21.25
Averages:
Ts L Flow ----
t.P v'~P --------
L Flow!
."lP .
KEY=>
IV"~ Field Data Sheet riiter~TETCO ~ lt{) Sample Go,,__£_ Pnge _\__or_l_ Run #_f_
Plant: Denison Mines
Dute: V ( \ "!{ 1 '"(
Location: Grizzly Baghouse
Operator: l't\ . M ~AAt!l\ltoJtt-
6
Travers~ Time DGM L;J 6H !w-.H;Ol Vacuum T;!mperaturcs ('F; DGM TernD (f.)
PO!tJi Clock Min (e) Ill'! Desired Actual (nof/,:) StadqT.) Probe Ph:::bcOul Filter Effiuent Out In .
1 -~·.t~ 0 ~Sol Cl•l .n .,,., L<1-L<:~ ~ 70 7.:FJ 1.."70 27'0 5_"'\ -:t'f (,~
...
I AO B N
2 lo 'ioo-110 ·•":1-o ''· .,0 u~o 3 12. ,,I.. I) z t-) 2C. ,)' 5( 9~ ":f-2-~lad. Diamerc:r I~. 75" Pon Reference ~
3 40 'lll. 4C.o ·CG.S ~.. S<.( L. SL{ 3 ;{' zc,, 'Z-38 '2.38 Sl 93 "1--1-Por\s are 24.5" Upstr~am from next disturbance
4 (,o r.t~S.o1) • 6"1'1. 1·111 i·'f.. L{ 1"1 l.So 1.40 Zo.fO 57. t:{) So Por~are 48• • Downme3m from last disturbance
5 So 't{3. ''30 • o4'-\.~o '·So 'i IB l7() 'Z.'-{1 t."f't S'Z. <-i.3 St Assumed ~~1visture 1 %,
6 IOO "'( '\oo .l ,.0 •o'l~ 1. <iZ. "2-·e.l.. 'I IS 270 2,{{ 2(? 52. Ci"! f?2 Probe 3~ -l7 Cp 0.84
7 JZO 'f 8~LS?c: • •'lO I ·'t I Lctl 'i ,q 210 Z'3o l~ 54 '\3 -~~
8 l~o 5 Dl. .300 ·1170 t ·•U "~ l I.( -RQ 2'i& '2. L(o 'Z.,'to s~ '13 B~
L Nozzk Calibr:.tion
.'-(o'{ ·'to'\ _:j-aC(. .'-lo0
9 11#0 52. 'i. 13;' -o~8 l-S{ '· sr 4 an zso z<oo Z"O 55 'io 83 A•!; Do • "\v ll{ inches
J 10 ,go s 41 . itt:~i> ... <.., 1. R8 l.i~ '{ 19 lf.C z. 70 Z"'TO C.o 8+ ec Gas Bag Ambient Air
11 too 551.. II{ •07( l.. oc.{ z.oo.l t{ So
't '" l. "~ u .. ~ '{'{ 8't g, Console __ ,._ __
12 2.20 5'1~·,l0 .elo l·''tl I.Cf I '{ 'af 7r.f '-z. C.(<; 'l Y'l 4{l s' ~'2.. Y-Factor I.OO 1..
1 •1:zt 'Z.'lo S'~ 4 . (. "'l-'2. .o~1 t. St t·8Z.. 4 ~0 1. £,~ tq'\ l'i.3 ,, 83 6(
2 zc.o Ltl.€6~ ·01Z. l· 'lC.! J.C\(, '1 Bt 2(,l z'iq 2-'fli. ~~ Jl{ Bo ~"( t>H@ \..(e{2)nH20
Barorn~tric Prc:ssures
3 290 (.2.'l,,11 . .,;'-(_ t.ct.. Z-o'-t.{ -~1.t z~ 'Z'fU Zf'i S\ i't et Pbm z..q, ~ in Hg
4 3oO (.,.•,P.Cflf' .e8'z. z.t~ 2.z3 " g~ 't,(,Z. z-r) z.;, 5<i ea fl'Z.. 5 4 II J 3oO IJ f_'4,.Cflf' ll .eB?..II 1·t'!>I 2.Z"\II 'i II gt.{ I 't,(,Z.I Z-{)1 2l',15<i II ee I B'Z.. Pbr "Z.Y.•z:r inHg
5
6
~ 7
8
9 , 10
11
12
~
Total
Av~r:~ge.
Comments
31.0 G.fo (.o"f-f ·¥1~ '2-\'j'
~40 t-es. '&Jo .o'1) l.o~
3"o '1o'i. O"li> • 0"'( l·1c.(
38o 71-'0 ·B'S-( •oSlo-t.{{
~oo ,3&>.79o ··~~ ,.-( (
4ZD '15"2 .ql-{ ·•){ l·fo
'l{tfo it..R~:( •0~3 ._,o{l.o{
LfC,, 1B'f · 'i~o ·<>55 •·10
\f.: t.l Y Qu eco .1.qr
/ 4l~ .2 tt+--" ,; ~. z.B~
~s~ ft s~~
J8&.{.o5o
v • 2,{<'f>/
'l-lf y
't ·ocf ~
, .. ., cf 4 '-~ -1{ It ,,.{f '-j
l.(O Lf
v~"{ ~
lrfO l{
'{ "l.octo
l-~3~
/
RCf z 'fo
90 z.z.{
~z.. 130
9'2.. z.'{'{ .,_,. 7_ l1o
'\'2.-Z.!>~ set -t.C.~
8'f isa
ttf Qt.{/
82..1-
1.'t~ tc.t$ .H~
[')'[ Z31 C:T
Zl.Cf zz.q ({3
2 "t'{ 'L'I'f. {.l(,
z. 1" 2.. l~Z. (f~
2.{:5 .2..1:) .57_
'Z.-D"B z76 s~
'Z'10 Z7o '0
8B_ i6z. Pc; --c)(, inH.,O
m, e'l,., Leak Check Pre Post
~b ~2. ft 'im:nO• &:IO{q
tafo '8-:., voconllg_l_~ ~.Q
~B g'{
Sct gt{ P1:vtR:ue .'20 .1. v
(;H B_L lnH,O ~ ~
'f't 9~
Water CoJiected 12 • 't g
Time Sampled '180 mm
4,013 Rcvtew ~
<a£4·~ K~ @T"'
K= @Tm
South Yellow Cake Scrubber
Sample Recovery
Gas Analysis Data (ORSAT)
Yellow Cake Dryer Baghouse
Sample Recovery
Gas Analysis Data (Ambient)
Grizzly Baghouse
Sample Recovery
Gas Analysis Data (Ambient)
Chain of Custodies
Lab Analysis
APPENDIXC
c
South Yell ow Cake Dryer Scrubber
lVlt 1 t1VU )
Facility: Em:rt>.v Fuels
Stack Identification: SYC Scrubber ~~~~~--------------------------
IMPINGERS
Run: \ Sample Box: E.
Impinge•· Number
2 I 3 1 4 1 5 6
Initial Volume Df hquid (H,O) in impmgC , (ml)
100 I drc pout I 100 I '>1lica <fd
--< ~
Final (g)
Initial (g)
Net (g)
Total (g) y::,~, I j<:,
TM£1NGERS
Run: 2 Sample Box: E.
{,20~
lmpmgcr Num6er
2 I 3 I 4 I ~ 6
hllti:ll Volume of liqltitl (HzO) in impingers, (m[)
dt·o~ out 10 I dr p ClUI I 100 I Silic:1 Gd
I
Initial (g)
Net (g)
Total (g) L-( 3 7 .cz
!MI!U'sGERS
Run: Sample Box:
lmpinger Number
2 I 3 I 4 I s G
Initial Volume of liquid (H20) in ill1t>ingcrs; (ml)
drop out 100 I dro p out I 100 I Sili"a Gd
"
Final (g.)
Initial (g)
Net (g)
Total (g)
IMfi~GERS
Run: Sample Box:
lmpinger ~um6cr
1 2 I 3 I 4 I 5 6
..
Final (gl
Initial (g)
Net (g)
Total (g)
~
Plant &, ~/ tTr fi, ~ U
Analytical Method 7 0RSA T
Date &I~)~/ Gas
Test No. I
;: -(.),5 ....
Gas Bag No .
Ambient Temp . F* Operator
Date & It<; IlL/ Gas
Test No. "'2---
Gas Bag No. E--os-
Ambient Temp ~ Operator
Date Gas
Test No. ____ _
Gas Bag No. ____ _
Ambient Temp _____ _
Operator ------
Location. ___ 7-r--'t-/-'C;;;..._ ___________ _
lr----,----~~---~---~l~---~---~l Average
Aetual
Ruding
Actual
Net
Net
Aclunl
Actual
Net
Net
Net
Actual
Reading
Actual
Reading
Actual
Reading
Net
Nrt
(. (:
I ~·l-
Net
Net
Volume
I Js--
Average
Net
Volume
(. c
( &-
Average
Net
Volume
CO is not measured, as it has the same molecular weight as N2
Yell ow Cake Dryer Baghouse
"t1ITZZLy ,.,.,.. '
Facility: 1-nt:l~t;v Fuels Date:_~__._/ 1-'-7 .:......:{/_Lj_,___
Stack Identification: leJ \o t0 (..:a. \.<..e... :Du ~Ia ov ~--(
IMPJNGERS
Run: l Sample Box: D
Filter Number lmpinger Number
(j 1_.o;f' 2 I 3 I 4 I s 6
IMPJ~GEB~
Filter Number
IMJ!II:':IGER~
Fi Iter Number
Final (g)
Initial (g)
Net (g)
Final (g)
Initial (g)
Net (g)
Final (g)
Initial (g)
Net (g)
100 I
I
C,O'i.o
{p(~-1
-I(.L3
Run:
110
Run:
iOO
Initial Volume ofllquicl {1-110) in imping.~rs. (ml)
100 I . I !i•Ji,:u ( •<'~ I I I 1 ' • ' .
(..( b I l ~1~·3 9tO,~
utll-1 (,J }·' 71<61. 7f
-·3 . (._ l 0·.5
Total (g) Co • {
Sample Box:
[mpmger Number
2 I 3 I 4 I 5 6
Silica Gel
Total (g)
Sample Box:
Impinger Number
2 I 3 I 4 I 5 6
Silica Gd
Total (g)
Grizzly Baghouse
Method 5
Facility: Energy Fuels Date: __ ~ ....... (J...:r 8 .... 1~/....:Y __
Stack Identification: ..:G::..:r.=izz=l~y _______________ _
IMPINGERS
Filter Number
IMPINGERS
Filter Number
IMPINGERS
Filter Number
Final (g)
Initial (g)
Net (g)
Run:
100
I t>-ss.o
(po '-l · 0
-c.!'i-0
Sample Box:
2
lmpinger Number
I 3 I 4 I s
Initial Volume ofnc1uiil (A~O) in impingcrs, {ml)
I 00 I I Silica Gel I
' • • ~
1..31 J «...( (p( fj I -:r-q51 . .s
C.l(,,\ "l ~. 3 910·3
IS-3 5'.~ 1.( l· z..
_______ Total (g)==:===:::I'Z.=· =9==-
Run: Sample Box:
Lmpinge•· Number
1 2 3 I 4 I s
Initial Volume of liquid (H10) in implngcr.;, (rill)
100 100 I I Silica Gel I
D
6
.
6
Final (g) ----f--------4-----4-----+----1-----
Initial (g) ___ -lf--------4-----4-----+----1-----
Net (g)====:!'======'====:!===='====::::!:====
Total (g)
Run: Sample Box:
1 2
lmpinger Number
I 3 I 4 I 5 6
Initial Volume of liquid (H20) in lmping~:rs, (ml)
100 100 I I 'ilic;J Oct I
Final (g) ----11------l-----f~-----+----+---­
lnitial (g) ----11------1-----f-----+----+----
Net (g)===:=!:===::::!::::===!:::·===='=====:!====
Total (g)========
Temperature on Receipt __ _ Test America
Custody Record ·. Drinking Water? Yes 0 ·No 0 THE LEADER IN ENVIRONMENTAL TESTING
T~-4124 (1007)
Glism --pr(J/iJr;t.Mans.oiJr _ D?t~. Chsln of Cusrodv Number
Tetco Deao Kit.!=hen \6/19/2014 ..
Addre$$1 T~ Nfm:112~(Ates ~]If~ Numbpr _ ~bfl/umlifN' I 1 · · 391 East 620 South 801-492-9106 Page of
City I State !ZiD Code Site Contact Lab Contact Analysis (Attach list if American Fork Ut 84003 Stott Christensen, Garren Palmer more space is needed) .
P.CJii85<t Namfl:M:d L<lW!lioo lStatsl c;.msrM'sy6ill Nunlber
Energy Fuels 2014 2nd Quarter ,, Special Instructions!
CQ(Jirai;tlP·Jt'r:JIItse Ottfor/Dubco No. Containers & 1 0 Conditions of Receipt Matrix PreseNatives 0 "' ....
~ "" N N "' ":' N -b Sample 1.0. No. and Description I
~ ~ @ 8 ei ~5 z :r .. "' ::) .. Date Time ~ "ti 'a ! ~ H a: .... (Containers for each sample may be combined on one line) _, ~ ~ ~ ~ ~ ~:1! I ... « II)
6/17/~ R1 Dryer BH filter (6207) and beaker 10:00 -. ' '1 X Klx X X -,-8:00 lx· R1 SYC Scrubber filter (6206) and beaker 6/16,17/14 X X! X X
R2 SYC Scrubber filter (6208) and beaker 6/17;18/14 i ,I 13:00 ;I X X )( I X. X
r R1 Grizzly filter (6210) and beaker 6/18/14 8:00 X X X -r
--I I .
r--I
I
I I
I '
;
Pcssible Hazatd li;/QfllirtaBtl::m I St~mple D<'SpG$jll (A fee may be assessed if samples are retained 0 Non-Hazard 0 Flammable 0 Skin Irritant 0 PoisonS 0 Unknown 0 Retum TD Client 0 Disposal By Lab 0 Archive For ___ Months Ienger than 1 month)
----------~ Rilquliilments (SpedljJ.
0 7 Days 0 14 Days 0 21 Days
1.R~d8y Time
2.R~ed8y
:I; ReJinquiShiid 8y 3. ReceiVed flU' I ~me
ComtrdJn:r;-
When Complete Email to: Dean or Paul, tetco@ tetco·l,lt.com
DISTRIB!Jr/ON: I'YP.fTC • RelutT>ed k> Cilent wilh Repotl[ CAili'AI'fY • Sl!lys t>~frh the SStTip/e; Pllm • AeitiC::OI>'I
·'""'·
SDGNo. Order No.
48381
TestAmerlca Inc
rptSTLRchTitle v3.73
Analytical Data Package Prepared For
Denison Mines (USA) Corp.
Radiochemical Analysis By
TestAmerica Inc
2800 G. W. Way, Richland Wa, 99354, (509)-375-3131.
Assigned Laboratory Code:
Data Package Contains 16 Pages
Report No.: 61895
Results in this report relate only to the sample(s) analyzed.
Client Sample ID (List Order) Lot-Sa No. Work Order Report DB ID
R1 Dryer BH J4F240448-1 M36EH1AE 9M36EH10
filter(6207)and be
R1 Dryer BH J4F240448-1 M36EH1AA 9M36EH10
filter(6207)and be
R1 Dryer BH J4F240448-1 M36EH1AC 9M36EH10
filter(6207)and be
R1 Grizzly filter(6210)and J4F240448-4 M36EL1AC 9M36EL10
be a
R1 Grizzly filter(6210)and J4F240448-4 M36EL1AA 9M36EL10
be a
R1 SYC Scrubber J4F240448-2 M36EJ1AE 9M36EJ10
filter(6206)an
R1 SYC Scrubber J4F240448-2 M36EJ1AA 9M36EJ10
filter(6206)an
R1 SYC Scrubber J4F240448-2 M36EJ1AC 9M36EJ10
filter(6206)an
R2 SYC Scrubber J4F240448-3 M36EK2AE 9M36EK20
filter(6208)an
R2 SYC Scrubber J4F240448-3 M36EK1AA 9M36EK10
filter(6208)an
R2 SYC Scrubber J4F240448-3 M36EK1AC 9M36EK10
filter(6208)an
Batch No.
4176035
4176037
4176039
4176035
4176037
4176035
4176037
4176039
4176035
4176037
4176039
1 of 16
Test America
THE LEADER IN ENVIRONMENTAL TESTING
Certificate of Analysis
August 22, 2014
Denison Mines (USA) Corp
I 050 17th Street, Suite 950
Denver, CO 80265
Attention: Dean Kitchen
Date Received at Lab
Project Name
Sample Type
SDGNumber
I. Introduction
June 24, 2014
Energy Fuels 2014 2nd Quarter
Four (4) Stack Filter Samples
48381
CASE NARRATIVE
On June 24, 2014, four stack filter samples were received at TestAmerica's Richland laboratory for
radiochemical analysis. Upon receipt, the samples were assigned the TestAmerica identification numbers
as described on the cover page of the Analytical Data Package report form. The samples were assigned to
Lot Numbers J4F240448.
II. Sample Receipt
The samples were received in good condition and no anomalies were noted during check-in.
III. Analytical Results/Methodology
The analytical results for this report are presented by laboratory sample ID. Each set of data includes
sample identification information; analytical results and the appropriate associated statistical
uncertainties.
The analysis requested was:
Alpha Spectroscopy
Thorium-228, -230, -232 by method RL-ALP-001
Uranium-234, -235, -238 by method RL-ALP-004
Gas Proportional Counting
Pb-210 by method RL-GPC-011
Alpha Scintillation
Radium-226 by method RL-RA-001
2 of 16
Denison Mines (USA) Corp
August 22, 2014
IV. Quality Control
The analytical result for each analysis performed includes a minimum of one laboratory control sample
(LCS), and one reagent blank sample analysis. Any exceptions have been noted in the "Comments"
section.
V. Comments
Alpha Spectroscopy
Thorium-228, 230, 232
The batch blank result for Th-230 was above the achieved MDA; a recount confirmed results and there is
no sample remaining for reanalysis. The achieved MDA of the batch exceeds the detection limit from
reduced aliquot sizes taken due to historical process knowledge. There is no sample volume remaining for
re-analysis. Data is reported. Except as noted, the LCS, batch blank and sample results are within
acceptance limits.
Uranium-234, 235, 238
Sample R2 SYC Scrubber had smeared spectra in the original count of this batch. The sample was
stripped and rerun through cartridges. Upon completion of reanalysis, tracer yield recovered low at 12%.
This sample fails and data is reported for client review.
Initial count for blank had a result for U-238 and U-234 that exceeds MDA. This sample was stripped
and reprocessed, with acceptable results. The achieved MDA of samples exceed CRDL. Except as noted,
the LCS, batch blank and sample results are within acceptance limits.
Gas Proportional Counting
Pb-210
Tracer yield for batch 4176038 were insufficient for completion of the required analysis. No remaining
sample for reanalysis. No data reported.
Alpha Scintillation
Radium-226
The CRDL was not met for the samples or QC for batch 4176039 due to method limitations for the
matrix. The tracer yields and LCS recovery meet acceptance criteria. The blank activity is below the
MDA and sample results show no indication of method contribution. Except as noted, the LCS, batch
blank and sample results are within acceptance limits.
I certify that this Certificate of Analysis is in compliance with the SOW and/or NELAC, both technically
and for completeness, for other than the conditions detailed above. The Laboratory Manager or a
designee, as verified by the following signature has authorized release of the data contained in this hard
copy data package.
Reviewed and approved:
~Ma~ Robin Ebe1-
Project Manager
3 of 16
Drinking Water Method Cross References
DRINKING WATER ASTM METHOD CROSS REFERENCES
Referenced Method lsotope(s) TestAmerica Richland's SOP N o.
EPA 901 .1 Cs-134, 1-131 RL-GAM-001
EPA 900.0 Alpha & Beta RL-GPC-001
EPA 00-02 Gross Alpha (Copreclpitation) RL-GPC-002
EPA 903.0 Total Alpha Radium (Ra-226) RL-RA-002
EPA 903.1 Ra-226 RL-RA-001
EPA 904.0 Ra-228 RL-RA-001
EPA 905.0 Sr-89/90 RL-GPC-003
ASTM D5174 Uranium RL-KPA-003
EPA 906 .0 Tritium RL-LSC-005
-1
Results in this report relate only to the sample(s) analyzed.
Uncertainty Estimation
TestAmerica Richland has adopted the internationally accepted approach to estimating
uncertainties described in "NIST Technical Note 1297, 1994 Edition". The approach, "Law of Propagation
of Errors", involves the identification of all variables in an analytical method which are used to derive a
result. These variables are related to the analytical result (R) by some functional relationship, R = constants
* f(x,y,z, ... ). The components (x,y,z) are evaluated to determine their contribution to the overall method
uncertainty. The individual component uncertainties (ui) are then combined using a statistical model that
provides the most probable overall uncertainty value. All component uncertainties are categorized as type
A, evaluated by statistical methods, or type B, evaluated by other means. Uncertainties not included in the
components, such as sample homogeneity, are combined with the component uncertainty as the square root
of the sum-of-the-squares of the individual uncertainties. The uncertainty associated with the derived result
is the combined uncertainty (uc) multiplied by the coverage factor (1,2, or 3).
When three or more sample replicates are used to derive the analytical result, the type A
uncertainty is the standard deviation of the mean value (S/?n), where Sis the standard deviation of the
derived results. The type B uncertainties are all other random or non-random components that are not
included in the standard deviation.
The derivation of the general "Law ofPropagation of Errors" equations and specific example are
available on request.
TestAmerica Inc
rptGenerallofo vJ. 72
I
l
4 of 16
Action Lev
Batch
Bias
COCNo
Count Error (#s)
Total Uncert (#s)
Uc-Combined
Uncertainty.
(#s), Coverage
Factor
CRDL (RL)
Lc
Lot-Sample No
MDCI MDA
Primary Detector
Ratio U-234/U-238
Rst/MDC
RstffotUcert
Report DB No
RER
SDG
Sum Rpt Alpha
Spec Rst(s)
Work Order
Yield
TestAmerica Inc
rptGenerallnfo v3. 72
Report Definitions
An agreed upon aetivity level used to trigger some action when the final result is greater than or equal to the Action
Level. Often the Action Level is related to the Decision Limit.
The QC preparation batch number that relates laboratory samples to QC samples that were prepared and analyzed
together.
Defined by the equation (Result/Expected)-! as defined by ANSI Nl3.30.
Chain of Custody Number assigned by the Client or TestAmerica.
Poisson counting statistics of the gross sample count and background. The uncertainty is absolute and in the same
units as the result. For Liquid Scintillation Counting (LSC) the batch blank count is the background.
All known uncertainties associated with the preparation and analysis of the sample are propagated to give a measure
of the uncertainty associated with the result, Uc the combined uncertainty. The uncertainty is absolute and in the
same units as the result.
The coverage factor defines the width ofthe confidence interval, I, 2 or 3 standard deviations.
Contractual Required Detection Limit as defined in the Client's Statement Of Work or TestAmerica "default"
nominal detection limit. Often referred to the reporting level (RL)
Decision Level based on instrument background or blank, adjusted by the Efficiency, Chemical Yield, and Volume
associated with the sample. The Type I error probability is approximately 5%. Lc=(l.645 *
Sqrt(2*(BkgmdCnt!BkgmdCntMin)/SCntMin)) * (ConvFct/(Eff*Yld*Abn*Vol) * IngrFct). For LSC methods the
batch blank is used as a measure of the background variability. Lc cannot be calculated when the background count
is zero.
The number assigned by the LIMS software to track samples received on the same day for a given client. The
sample number is a sequential number assigned to each sample in the Lot.
Detection Level based on instrument background or blank, adjusted by the Efficiency, Chemical Yield, and Volume
with a Type I and II error probability of approximately 5%. MDC= ( 4.65 *
Sqrt((BkgmdCnt/BkgmdCntMin)/SCntMin) + 2.7l/SCntMin) * (ConvFct/(Eff * Yld * Abn *Vol)* lngrFct). For
LSC methods the batch blank is used as a measure of the background variability.
The instrument identifier associated with the analysis of the sample aliquot.
The U-234 result divided by the U-238 result. The U-234/U-238 ratio for natural uranium in NIST SRM 4321C is
1.038.
Ratio of the Result to the MDC. A value greater than 1 may indicate activity above background at a high level of
confidence. Caution should be used when applying this factor and it should be used in concert with the qualifiers
associated with the result.
Ratio of the Result to the Total Uncertainty. If the uncertainty has a coverage factor of2 a value greater than 1 may
indicate activity above background at approximately the 95% level of confidence assuming a two-sided confidence
interval. Caution should be used when applying this factor and it should be used in concert with the qualifiers
associated with the result.
Sample Identifier used by the report system. The number is based upon the first five digits of the Work Order
Number.
The equation Replicate Error Ratio= (S-D)/[sqrt(TPUs2 + TPUd2)] as defined by ICPT BOA where S is the original
sample result, Dis the result of the duplicate, TPUs is the total uncertainty of the original sample and TPUd is the
total uncertainty ofthe duplicate sample.
Sample Delivery Group Number assigned by the Client or assigned by TestAmerica upon sample receipt.
The sum of the reported alpha spec results for tests derived from the same sample excluding duplicate result where
the results are in the same units.
The LIMS software assign test specific identifier.
The recovery of the tracer added to the sample such as Pu-242 used to trace a Pu-239/40 method.
5 of 16
Sample Results Summary Date: 22-Aug-14
TestAmerica Inc
Ordered by Method, Batch No., Client Sample ID.
Report No. : 61895 SDG No: 48381
Client ld Tracer
Batch Work Order Parameter Result+-Uncertainty ( 2s) Qual Units Yield MDL CRDL RER2
4176037 RICHRC5011
R1 Dryer BH filter(6207)and be
M36EH1AA Th-228 3.74E-09 +-1.5E-08 u uCi/Sample 41% 3.47E-08 3.00E-15
Th-230 5.55E-07 +-1.3E-07 uCi/Sample 41% 9.77E-09 3.00E-15
Th-232 4.33E-09 +-1.1E-08 u uCi/Sample 41% 2.48E-08 3.00E-15
R1 Grizzly filter(621 O)and bea
M36EL1AA Th-228 1.03E-07 +-4.5E-08 uCi/Sample 35% 4.34E-08 3.00E-15
Th-230 1.87E-05 +-3.0E-06 uCi/Sample 35% 2.89E-08 3.00E-15
Th-232 2.38E-07 +-6.9E-08 uCi/Sample 35% 2.63E-08 3.00E-15
R1 SYC Scrubber filter(6206)an
M36EJ1AA Th-228 2.08E-08 +-2.4E-08 u uCi/Sample 24% 3.27E-08 3.00E-15
Th-230 1.47E-07 +-6.5E-08 uCi/Sample 24% 4.79E-08 3.00E-15
Th-232 5.57E-09 +-1.2E-08 u uCi/Sample 24% 1.51 E-08 3.00E-15
R2 SYC Scrubber filter(6208)an
M36EK1AA Th-228 2.69E-09 +-1.1 E-08 u uCi/Sample 41% 2.63E-08 3.00E-15
Th-230 2.25E-07 +-6.2E-08 uCi/Sample 41% 2.79E-08 3.00E-15
Th-232 2.14E-08 +-1.8E-08 uCi/Sample 41% 1.84E-08 3.00E-15
4176035 FFSR
R1 Dryer BH filter(6207)and be
M36EH1AE U-234 7.08E-04 +-1.6E-04 uCi/Sample 99% 3.10E-05 9.00E-15
U-235 1.48E-05 +-1.8E-05 u uCi/Sample 99% 2.39E-05 9.00E-15
U-238 9.70E-04 +-2.1E-04 uCi/Sample 99% 2.61E-05 9.00E-15
R1 Grizzly filter(6210)and bea
M36EL1AC U-234 2.45E-05 +-3.0E-05 u uCi/Sample 77% 4.70E-05 9.00E-15
U-235 1.40E-05 +-2.1 E-05 u uCi/Sample 77% 2.94E-05 9.00E-15
U-238 4.65E-05 +-4.0E-05 u uCi/Sample 77% 4.70E-05 9.00E-15
R1 SYC Scrubber filter(6206)an
M36EJ1AE U-234 6.75E-03 +-1.1 E-03 uCi/Sample 84% 1.24E-04 9.00E-15
U-235 2.67E-04 +-9.6E-05 uCi/Sample 84% 6.19E-05 9.00E-15
U-238 6.94E-03 +-1.2E-03 uCi/Sample 84% 1.18E-04 9.00E-15
R2 SYC Scrubber filter(6208)an
M36EK2AE U-234 7.92E-06 +-2.4E-06 uCi/Sample 12% 3.28E-07 9.00E-15
U-235 5.02E-07 +-3.5E-07 uCi/Sample 12% 2.33E-07 9.00E-15
U-238 8.35E-06 +-2.5E-06 uCi/Sample 12% 2.54E-07 9.00E-15
4176039 RL-RA-001
R1 Dryer BH filter(6207)and be
M36EH1AC Ra-226 4.21 E-07 +-1.1 E-07 uCi/sample 100% 7.19E-08 9.00E-14
R1 SYC Scrubber filter(6206)an
M36EJ1AC Ra-226 2.65E-07 +-9.6E-08 uCi/sample 66% 1.02E-07 9.00E-14
TestAmerlca Inc RER2 -Replicate Error Ratio= (S-D)/[sqrt(sq(TPUs)+sq(TPUd))) as defined by ICPT BOA.
rptTALRchSaSum U Qual-Analyzed for but not detected above limiting criteria. Limit criteria is less tban tbe Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or
mary2 V5.3.3 not identified by gamma scan software.
A2002
6 of 16
Report No. : 61895
Client ld
Batch Work Order Parameter
4176039 RL-RA-001
R2 SYC Scrubber filter(6208)an
M36EK1AC Ra-226
No. of Results: 27
Sample Results Summary
TestAmerica Inc
Ordered by Method, Batch No., Client Sample 10.
Date: 22-Aug-14
SDG No: 48381
Result+-Uncertainty ( 2s) Qual Units
Tracer
Yield
2.64E-07 +-9.5E-08 uCi/sample 91%
MDL CRDL RER2
7.93E-08 9.00E-14
TestAmerica Inc RER2 -Replicate Error Ratio= (S-D)/[sqrt(sq(TPUs)+sq(TPUd))) as defined by ICPT BOA.
rptTALRchSaSum
mary2 V5.3.3
A2002
7 of 16
QC Results Summary Date: 22-Aug-14
TestAmerica Inc
Ordered by Method, Batch No, QC Type,.
Report No. : 61895 SDG No.: 48381
Batch Tracer LCS
Work Order Parameter Result+-Uncertainty ( 2s) Qual Units Yield Recovery Bias MDL
RICHRC5011
4176037 BLANK QC,
M36K11AA Th-228 1.02E-10 +-1.3E-10 u uCi/Sample 31% 2.10E-10
M36K12AA Th-228 -2.87E-11 +-7.7E-11 u uCi/Sample 26% 2.66E-10
M36K11AA Th-230 7.53E-10 +-3.1E-10 uCi/Sample 31% 7.04E-11
Th-232 4.16E-11 +-7.7E-11 u uCi/Sample 31% 1.47E-10
4176037 LCS,
M36K11AC Th-230 1.11E-08 +-1.7E-09 uCi/Sample 79% 98% 0,0 2.19E-11
FFSR
4176035 BLANK QC,
M36KT2AA U-234 2.05E-08 +-9.0E-08 u uCi/Sample 45% 2.23E-07
U-235 3.26E-08 +-5.4E-08 u uCi/Sample 45% 1.11 E-07
U-238 9.14E-08 +-1.0E-07 u uCi/Sample 45% 1.98E-07
4176035 LCS,
M36KT1AC U-234 7.54E-07 +-2.1E-07 uCi/Sample 81% 77% -0.2 2.84E-08
U-238 9.78E-07 +-2.6E-07 uCi/Sample 81% 95% -0.1 3.99E-08
RL-RA-001
4176039 BLANK QC,
M36K41AA Ra-226 2.99E-10 +-2.3E-10 u uCi/sample 93% 3.41E-10
4176039 LCS,
M36K41AC Ra-226 4.15E-08 +-8.5E-09 uCi/sample 100% 83% -0.2 4.04E-10
No. of Results: 12
TestAmerica Inc Bias -(Result/Expected)-I as defined by ANSI N13.30.
rptSTLRchQcSum U Qual-Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or
mary V5.3.3 A2002 not identified by gamma scan software.
a of 16
FORM I Date: 22-Aug-14
SAMPLE RESULTS
Lab Name: T estAmerica Inc SDG: 48381 Collection Date: 6/17/201410:00:00 AM
Lot-Sample No.: J4F240448-1 Report No.: 61895 Received Date: 6/24/2014 10:40:00 AM
Client Sample ID: R1 Dryer BH filter(6207)and be COC No.: Matrix: SOLID
Ordered b~ Client Sample I D. Batch No.
Result Count Total MDL, Rpt Unit, Yield Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2 s) Uncert(2 s) Action Lev Lc CRDL(RL) Rst/TotUcert Prep Date Size Size Detector
Batch: 4176035 FFSR Work Order: M36EH1AE Report DB ID: 9M36EH10
U-234 7.08E-04 1.2E-04 1.6E-04 3.1 OE-05 uCi/Sample 99% (22.8) 7/15/14 10:04 p 1.0 0.00116 ALP1
8.28E-06 9.00E-15 (8.7) Sample Sample
U-235 1.48E-05 u 1.8E-05 1.8E-05 2.39E-05 uCi/Sample 99% 0.62 7/15/14 10:04 p 1.0 0.00116 ALP1
5.81E-06 9.00E-15 (1.6) Sample Sample
U-238 9.70E-04 1.4E-04 2.1 E-04 2.61 E-05 uCi/Sample 99% (37.2) 7/15/14 10:04 p 1.0 0.00116 ALP1
6.55E-06 9.00E-15 (9.4) Sample Sample
Ratio U-2341238 = 0.7
Batch: 4176037 RICHRC5011 Work Order: M36EH1AA Report DB ID: 9M36EH1 0
Th-228 3.74E-09 u 1.5E-08 1.5E-08 3.47E-08 uCi/Sample 41% 0.11 7/24/14 03:49 a 1.0 0.98985 ALP126
1.33E-08 3.00E-15 0.51 Sample Sample
Th-230 5.55E-07 9.0E-08 1.3E-07 9.77E-09 uCi/Sample 41% (56.8) 7/24/14 03:49 a 1.0 0.98985 ALP126
5.36E-09 3.00E-15 (8.9) Sample Sample
Th-232 4.33E-09 u 1.1 E-08 1.1 E-08 2.48E-08 uCi/Sample 41% 0.17 7/24/14 03:49 a 1.0 0.98985 ALP126
9.43E-09 3.00E-15 0.79 Sample Sample
--
Batch: 4176039 RL-RA-001 Work Order: M36EH1AC Report DB ID: 9M36EH10
Ra-226 4.21E-07 6.5E-08 1.1 E-07 7 .19E-08 uCi/sample 100% (5.9) 8/21/14 08:17 p 1.0 0.9898 ASC1MB
3.40E-08 9.00E-14 (7.9) g g
No. of Results: 7 Comments:
TestAmerica Inc MDCIMDA,Lc -Detection, Decision Level based on instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not identified by gamma scan software.
V5.3.3 A2002
9 of 16
FORM I Date: 22-Aug-14
SAMPLE RESULTS
Lab Name: TestAmerica Inc SDG: 48381 Collection Date: 6/18/2014 8:00:00 AM
Lot-Sample No.: J4F240448-4 Report No.: 61895 Received Date: 6/24/2014 10:40:00 AM
Client Sample ID: R1 Grizzly filter(6210)and bea COC No.: Matrix: SOLID
Ordered b~ Client SamEie 10, Batch No.
Result Count Total MDL, Rpt Unit, Yield RstJMDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2 s) Uncert(2 s) Action Lev Lc CRDL(RL) RstJTotUcert Prep Date Size Size Detector
Batch: 4176035 FFSR Work Order: M36EL 1AC Report DB ID: 9M36EL 10
U-234 2.45E-05 u 2.9E-05 3.0E-05 4.70E-05 uCi/Sample 77% 0.52 7/15/14 10:06 p 1.0 0.00102 ALPS
1.29E-05 9.00E-1S (1 .6) Sample Sample
U-235 1.40E-05 u 2.1E-OS 2.1 E-OS 2.94E-OS uCi/Sample 77% 0.48 7/15/1410:06 p 1.0 0.00102 ALPS
6.83E-06 9.00E-1S (1 .3) Sample Sample
U-238 4.65E-05 u 3.9E-OS 4.0E-OS 4.70E-OS uCi/Sample 77% 0.99 7/1S/14 10:06 p 1.0 0.00102 ALPS
1.29E-OS 9.00E-15 (2.3) Sample Sample
Ratio U-2341238 = 0.5
Batch: 4176037 RICHRC5011 Work Order: M36EL 1AA Report DB ID: 9M36EL 10
Th-228 1.03E-07 4.2E-08 4.SE-08 4.34E-08 uCi/Sample 3S% (2.4) 7/24/14 03:SO a 1.0 0.98825 ALP129
1.70E-08 3.00E-1S (4.6) Sample Sample
Th-230 1.87E-05 S.OE-07 3.0E-06 2.89E-08 uCi/Sample 35% (646.5) 7/24/14 03:SO a 1.0 0.98825 ALP129
1.11E-08 3.00E-1S (12.3) Sample Sample
Th-232 2.38E-07 5.7E-08 6.9E-08 2.63E-08 uCi/Sample 3S% (9.1) 7/24/14 03:50 a 1.0 0.98825 ALP129
1.00E-08 3.00E-1S (6.9) Sample Sample
-~ --~ ·---
No. of Results: 6 Comments:
TestAmerica Inc MDCjMDA,Lc-Detection, Decision Level based on instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not identified by gamma scan software.
V5.3.3 A2002
10 of 16
FORM I Date: 22-Aug-14
SAMPLE RESULTS
Lab Name: TestAmerica Inc SDG: 48381 Collection Date: 6/16/2014 8:00:00 AM
Lot-Sample No.: J4F240448-2 Report No.: 61895 Received Date: 6/24/2014 10:40:00 AM
Client Sample ID: R1 SYC Scrubber filter(6206)an COC No.: Matrix: SOLID
Ordered b~ Client Sample 10, Batch No.
Result Count Total MDL, Rpt Unit, Yield Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2 s) Uncert( 2 s) Action Lev Lc CRDL(RL) Rst/TotUcert Prep Date Size Size Detector
Batch: 4176035 FFSR Work Order: M36EJ1AE Report DB ID: 9M36EJ10
U-234 6.75E-03 4.3E-04 1.1E-03 1.24E-04 uCi/Sample 84% (54.4) 7/15/1410:05 p 1.0 0.00105 ALP3
4.14E-05 9.00E-15 (11.8) Sample Sample
U-235 2.67E-04 8.7E-05 9.6E-05 6.19E-05 uCi/Sample 84% (4.3) 7/15/14 10:05 p 1.0 0.00105 ALP3
1.87E-05 9.00E-15 (5.5) Sample Sample
U-238 6.94E-03 4.3E-04 1.2E-03 1.18E-04 uCi/Sample 84% (58.9) 7/15/14 10:05 p 1.0 0.00105 ALP3
3.91E-05 9.00E-15 (11 .9) Sample Sample
Ratio U-2341238 = 1.0
Batch: 4176037 RICHRC5011 Work Order: M36EJ1AA Report DB ID: 9M36EJ10
Th-228 2.08E-08 u 2.4E-08 2.4E-08 3.27E-08 uCi/Sample 24% 0.64 7/24/14 03:49 a 1.0 0.98916 ALP127
1.25E-08 3.00E-15 (1.7) Sample Sample
Th-230 1.47E-07 6.0E-08 6.5E-08 4.79E-08 uCi/Sample 24% (3.1) 7/24/14 03:49 a 1.0 0.98916 ALP127
1.83E-08 3.00E-15 (4.6) Sample Sample
Th-232 5.57E-09 u 1.2E-08 1.2E-08 1.51 E-08 uCi/Sample 24% 0.37 7/24/14 03:49 a 1.0 0.98916 ALP127
8.28E-09 3.00E-15 0.93 Sample Sample ----
Batch: 4176039 RL-RA-001 Work Order: M36EJ1AC Report DB ID: 9M36EJ10
Ra-226 2.65E-07 7.6E-08 9.6E-08 1.02E-07 uCi/sample 66% (2.6) 8/21/14 08:17 p 1.0 0.9892 ASCMAD
4.79E-08 9.00E-14 (5.5) g g
No. of Results: 7 Comments:
TestAmerica Inc MDCIMDA,Lc-Detection, Decision Level based on instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not identified by gamma scan software.
V5.3.3 A2002
11 of 16
FORM I Date: 22-Aug-14
SAMPLE RESULTS
Lab Name: TestAmerica Inc SDG: 48381 Collection Date: 6/17/2014 1:00:00 PM
Lot-Sample No.: J4F240448-3 Report No.: 61895 Received Date: 6/24/201410:40:00 AM
Client Sample ID: R2 SYC Scrubber filter(6208)an COC No.: Matrix: SOLID
Ordered by Client Sample 10, Batch No.
Result Count Total MDL, Rpt Unit, Yield Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Qual Error ( 2 s) Uncert( 2 s) Action Lev Lc CRDL(RL) Rst/TotUcert Prep Date Size Size Detector
Batch: 4176035 FFSR Work Order: M36EK2AE Report DB ID: 9M36EK20
U-234 7.92E-06 1.3E-06 2.4E-06 3.28E-07 uCi/Sample 12% (24.2) 7/24/14 03:06 p 1.0 1.0 ALP1
8.99E-08 9.00E-15 (6.7) Sample Sample
U-235 5.02E-07 3.2E-07 3.5E-07 2.33E-07 uCi/Sample 12% (2,2) 7/24/14 03:06 p 1.0 1.0 ALP1
5.67E-08 9.00E-15 (2.9) Sample Sample
U-238 8.35E-06 1.3E-06 2.5E-06 2.54E-07 uCi/Sample 12% (32.8) 7/24/14 03:06 p 1.0 1.0 ALP1
6.39E-08 9.00E-15 (6.8) Sample Sample
Ratio U-2341238 = 0.9
Batch: 4176037 RICHRC5011 Work Order: M36EK1AA Report DB ID: 9M36EK1 0
Th-228 2.69E-09 u 1.1 E-08 1.1 E-08 2.63E-08 uCi/Sample 41% 0.1 7/24/14 03:50 a 1.0 0.98665 ALP128
1.00E-08 3.00E-15 0.51 Sample Sample
Th-230 2.25E-07 5.5E-08 6.2E-08 2.79E-08 uCi/Sample 41% (8.1) 7/24/14 03:50 a 1.0 0.98665 ALP128
1.07E-08 3.00E-15 (7.2) Sample Sample
Th-232 2.14E-08 1.7E-08 1.8E-08 1.84E-08 uCi/Sample 41% (1.2) 7/24/14 03:50 a 1.0 0.98665 ALP128
7.03E-09 3.00E-15 (2.4) Sample Sample --
Batch: 4176039 RL-RA-001 Work Order: M36EK1AC Report DB ID: 9M36EK10
Ra-226 2.64E-07 6.2E-08 9.5E-08 7.93E-08 uCi/sample 91% (3.3) 8/21/14 08:18 p 1.0 0.9866 ASCKMF
3.74E-08 9.00E-14 (5.5) 9 9
No. of Results: 7 Comments:
TestAmerica Inc MDCIMDA,Lc -Detection, Decision Level based on instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchSample U Qual -Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not identified by gamma scan software.
V5.3.3 A2002
12 of 16
FORM II Date: 22-Aug-14
BLANK RESULTS
Lab Name: TestAmerica Inc SDG: 48381
Matrix: SOLID Report No.: 61895
Count Total MDL, Rpt Unit, Rst/MDL, Analysis, Total Sa Aliquot Primary
Parameter Result Qual Error ( 2 s) Uncert( 2 s) Lc CRDL Yield Rst!TotUcert Prep Date Size Size Detector
Batch: 4176039 RL-RA-001 Work Order: M36K41AA Report DB ID: M36K41AB
Ra-226 2.99E-10 u 2.2E-10 2.3E-10 3.41E-10 uCi/sample 93% 0.88 8/21/14 08:18 p 1.0 202.11 ASCLMD
1.60E-10 9.00E-14 (2.6) 9 9
Batch: 4176035 FFSR Work Order: M36KT2AA Report DB ID: M36KT2AB
U-234 2.05E-08 u 9.0E-08 9.0E-08 2.23E-07 uCi!Sample 45% 0.09 7/24/14 03:06 p 0.25 0.25 ALP3
7.39E-08 9.00E-15 0.45 Sample Sample
U-235 3.26E-08 u 5.3E-08 5.4E-08 1.11 E-07 uCi/Sample 45% 0.29 7/24/14 03:06 p 0.25 0.25 ALP3
3.27E-08 9.00E-15 (1.2) Sample Sample
U-238 9.14E-08 u 1.0E-07 1.0E-07 1.98E-07 uCi!Sample 45% 0.46 7/24/14 03:06 p 0.25 0.25 ALP3
6.45E-08 9.00E-15 (1.8) Sample Sample
Ratio U-2341238 = 0.2
Batch: 4176037 RICHRC5011 Work Order: M36K11AA Report DB ID: M36K11AB
Th-228 1.02E-10 u 1.3E-10 1.3E-10 2.10E-10 uCi/Sample 31% 0.49 7/24/14 03:50 a 1.0 202.11 ALP130
8.02E-11 3.00E-15 (1.6) Sample Sample
Th-230 7.53E-10 2.8E-10 3.1E-10 7.04E-11 uCi/Sample 31% (10.7) 7/24/14 03:50 a 10 202.11 ALP130
3.86E-11 3.00E-15 (4.9) Sample Sample
Th-232 4.16E-11 u 7.6E-11 7.7E-11 1.47E-10 uCi/Sample 31% 0.28 7/24/14 03:50 a 1.0 202.11 ALP130
5.62E-11 3.00E-15 (1.1) Sample Sample
Batch: 4176037 RICHRC5011 Work Order: M36K12AA Report DB ID: M36K12AB
Th-228 -2.87E-11 u 7.7E-11 7.7E-11 2.66E-10 uCi!Sample 26% -0.11 7/31/14 02:17 a 1.0 202.11 ALP126
1.02E-10 3.00E-15 -0.74 Sample Sample
No. of Results: 8 Comments:
TestAmerica Inc MDCIMDA,Lc-Detection, Decision Level based on instrument background or blank, adjusted by the sample Efficiency, Yield, and Volume.
rptSTLRchBiank U Qual-Analyzed for but not detected above limiting criteria. Limit criteria is less than the Mdc/Mda/Mdl, Total Uncert, CRDL, RDL or not identified by gamma scan software.
V5.3.3 A2002
13 of 16
Lab Name: TestAmerica Inc
Matrix: SOLID
Count
Parameter Result Qual Error ( 2 s)
Batch: 4176039 RL-RA-001
Ra-226 4.15E-08 1.2E-09
Batch: 4176035 FFSR
U-234 7.54E-07 1.5E-07
U-238 9.78E-07 1.7E-07
Batch: 4176037 RICHRC5011
Th-230 1.11E-08 6.0E-10
No. of Results: 4 Comments:
Total
Uncert( 2 s) MDL
FORM II
LCS RESULTS
Report
Unit Yield
Expected
Expected Uncert
Work Order: M36K41AC Report DB ID: M36K41CS
8.5E-09 4.04E-10 uCi/sample 100% 5.02E-08 5.10E-10
Rec Limits: 75 125
Work Order: M36KT1AC Report DB ID: M36KT1CS
2.1E-07 2.84E-08 uCi/Sample 81% 9.84E-07 3.05E-08
Rec Limits: 75 125
2.6E-07 3.99E-08 uCi/Sample 81% 1.03E-06 3.20E-08
Rec Limits: 75 125
Work Order: M36K11AC Report DB ID: M36K11 CS
1.7E-09 2.19E-11 uCi/Sample 79% 1.14E-08 1.18E-10
Rec Limits: 75 125
TestAmerica Inc Bias -(Result/Expected)-1 as defined by ANSI N13.30.
rptSTLRchlcs
V5.3.3 A2002
Date: 22-Aug-14
SDG: 48381
Report No.: 61895
Recovery, Analysis, Aliquot Primary
Bias Prep Date Size Detector
83% 8/21/14 08:18 p 199.96 ASCNMA
-0.2 g
77% 7/15/14 10:06 p 0.26 ALP12
-0.2 Sample
95% 7/15/14 10:06 p 0.26 ALP12
-0.1 Sample
98% 7/24/14 03:51 a 199.96 ALP131
0.0 Sample
14 of 16
(.n
!a, .....
0)
Custody Record
'W..;.l24(11l0?)
Cl/Qflf
Tetco
Aetressl 391 East 620 South -CilY . ~~-IZ(DC¥e American Fork ~ Ut 84003 -. . .. ~. --~~--------'
Energy Fuels 2014 2nd Quarter
Gontrcct/PtJn:JJase OJWI'fOlKJ<e No.
Sample f. D. No. and Description Date (Containers for each sample may be combined on osj!l/JOO)
[ R1 Dryer BH filter (6207) and beaker .ll 6/17/JM<f
R1 SYC Scrubber filter (6206) and beaker 6/16,17/14 .
! R2-SYC Scr~b~er fl_!.ter (6208) and beaker
.
6/17,18/14
I R1 Grizzly filter {6210) and beaker -'
• J 6/18/14
. .--·---·-
l
L i -~-.. --1 ·-.
-
Temperature on Receipt __ _ Test America
Drinking Water? Yes 0 ·No 0 THE LEADER IN ENViRONMENTAL TESTING
P..mire.9fM?J]f,lSlf![ _ _ __ ---··----·· -~-------
Dean Kit!;.hen l.6i.1912 Ol 9:
=~:;:~;aCodevrax.r:r~L-.-----l.2b Nu/rJier
J~e Crotact.. __ -. ---i Lab Con!acl Analysis (Attach list if
Scott Christensen, GaJT~n Palmer more space is needed}
I ·-~rM'aytJ//1 Number
I Containers & Matrix Preservatives J ~ ... ~ "' ~ N ,; "' ... ~ ~ l! I'! 0 ., "' 'bi§ ..
Time g -g ~I ... "' Q ~ ~ I 1-' : !! ·" ~ § ~ ~ ~~ "< 0) 0)
10:00 ·' X1 X 'x X I '!X
8:00 l xj X x 1 I ' .K X
13:00 -, I .X~ I -~x ; 2cl x I I -... I I 8:00 ! X X X
I I
I l
I I
I I
I
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'3\:)\s--~ '1:?.:§b\
·~ iJ-0. ~-""-'
rCJraiocf~Number l
Page I of _j__
Special lnstiUctionSI
Concflfions of Receipt
vY\ 7:> \.e ~ \\
-~V'i~ \.o f:(\
I '(Y'-.~~·~
'M ~\...o .k:. L.
I
!
1\1111 ~lllllllllllllllllllllll J4 240448
.. ·-
----•!..:J'._ t . .l --1.1..1--.0.:~-~c:-'""--'""'·nl -;..J
0 Non-Hazard 0 Flammable 0 Skin Irritant 0Poison8 0 Unknovm I 0 Return To Client
(A fee may be assessea if samples are retained 0 Disposal By Lab 0 Archive For ___ Months longsr than 1 month)
~ 8eqlii~ (Spgi;ify)
0 T Days 0 14 Days 0 21 Days
~Jn . \C)4C ~ '-'J f''-l<-... i.D-~'4-''\ 2. .,_
3. Rdmqv!shed By
~Is --·-·-· ·---··---When Co~ete_Email to: Dean or Paul,_ ~[e-mail] _
tJiSTRIBVTION:WrllTE-R.e!umed to aieiit<'tirn R~ cANARY-Stay.< •vi/fl~the $8ITij){ef F'IN((~--t'fiir(f"Ccpy
Test America !+'+§-. Samffie Check-in List
THE I. EADER IN ENVIRONMENTAL TESTIN9 J I .._ ... I lti-JD y ~;;f..t-\'-t
Date/Time Received :_,~"4Jc..f .J.ttn f.(>'"'t.~ Co~falner OM Screen 1 estllt (Airlock) (9 () ~pm Initials[ 6=-]
I SaJ:Ilple GM Scl·een l{.e-suh ( ample Receiving) -Ej)__ cpm lnilials[ f=-)
Client:_s)~ SDG#: \_\C£,~"(\ SAF #: NA~J
Lot Number: ~ \...\.. ( d. \..lt:)L\ '-\ cj
Chain of Custody# 0 !-!~'--· -------------------------------
Shipping Container ID or Air Bill Number : _____________ NA ~]
Yes~ ) Continue with 1 through 4. Initial appropriate response.
No [\ ] Go to 5, add comment to #16.
Samples received inside shipping container/cooler/box
Ye [ ] No [ No Custody Seal \tp]
Yes [ ] No [ No Custody Seal [~]
°C NA ~) N~~ Wet[ ] D1y[ ]
1. Custody Seals on shipping container intact?
2. Custody Seals dated and signed?
3. Cooler temperature:
4. Vermiculite/packing materials is
Item 5 through 16 for samples. Initial appropriate response. ~
5. Chain of Custody record present? Yes L :\" ] No [ ]
6. Number of samples received (Each sample may contain multiple bottles):,__t.f~--------------
7. Containers received: lfv f,'f fey ; 4 'l(J ·c..:QV\'
8.
9.
10.
11.
12.
13.
14.
15.
16.
Sample holding times exceeded? NA [ ] Yes [ ] No [ , ]
Samples have: __ tape __ hazard labels ~custody seals ~ appropriate sample'labels
Matrix: ___ A (FLT, Wipe, Solid, Soil) __ I (Water) 'S (Air, Niosh 74~ __ T (Biological, Ni-63)
Samples: ~are in good condition __ are leaking __ are broken
-.l--have air bubbles (Only for samples requiring no head space) __ Ot~r
Sample pH appropriate for analysis requested Yes [ ] No [ ] NA . ]
(If acidification is necessary go to pH area & document sample ID, initial pH, amount~· 3 a.dded and pH after nddltlM .. on table)
Were any anomalies identified in sample receipt? Yes [ ] No LY ]
Description of anomalies (include sample numbers): NA ~ ] -------------------
Sample Location, Sample Collector Listed on COC? *
*For documentation only. No corrective action needed.
Yes [
Additional Information:~l-'-'---~----.---.--.-------..----.--=--...,.....--=-"'---,~-~-----~-
] Client/Courier denied temperature check. ] Client/Courier unpack cooler.
LS-023 Rev. 17, 05/13 Page 1 ofJ
16 of 16
APPENDIX D
South Yellow Cake Scrubber
Figure 1. Facility Schematic Representation
Yell ow Cake Dryer Baghouse
Figure 2. Facility Schematic Representation
Grizzly Baghouse
Figure 3. Facility Schematic Representation
Production and Control Equipment Data
South Yellow Cake (Scrubber Flow Rates)
Yellow Cake Dryer Baghouse (Delta P readings on Field Data Sheets)
Grizzly (tph of material and belt speed)
D
Fadl;ty Energy Fuels Resources
t
a
t
y
Stack Identification: South yell ow Cake Scrubber
l+--0~1
~
a: Distance upstream from next disturbance, feet 7' ------------------
~: Distance downstream from last disturbance, feet 30'
y: Distance of Sample Level to Ground, feet 65'
0: Stack Inside Diameter, inches 1 :2_75" ------------------
Estimated Moisture, percent 4-8
100-120 Estimated Temperature, °F ------------------
3.000 Estimated Velocity, fpm _______________ __
Control Unit
Type:
Scrubber
Number of Ports 2
~
Figure I. Facility Schematic Representation
Process
Type:
Yellow Cake Processing
Fao;,;,y Energy Fuels Resources
t
a
t
y
Stack Identification: ·yell ow Cal(e Dryer Bagh.ouse
l+--0--+ I
~
a: Distance upstream from next disturbance, inches 57 H -----------------
~: Distance downstream fi·om last disturbance, inches 454"
y: Distance of Sample Level to Ground, feet 65'
0: Stack Inside Diameter, inches 16" --------------------
Estimated Moisture, percent 0-:?%
125 Estimated Temperature, °F -----------------
Estimated Velocity, fpm 1.400
Control Unit
Type:
Baghouse
Number of Ports 2
<('
Figure 2. Facility Schematic Representation
Process
Type:
Y e!!mv Cake Processing
F•cH;ty, Energy Fuels Resources
t
a
t
y
Stack Identification: Grizzly B agh 0 use
1~0~1
p
a: Distance upstream from next disturbance, inches '4.5" -----------------
0: Distance downstream from last disturbance, inches 48''
y: Distance of Sample Level to Ground, feet 28' ------------------
0: Stack Inside Diameter, inches 1?:75" -----------------
Estimated Moisture, percent 1%
Estimated Temperature, °F Ambient
775 Estimated Velocity, fpm ______________ _
Number of Ports 2
Process
Type:
Control Unit
Type: r--..1.---------IOre Unloading and Conveying
<f
l:3aghousc
Figure 3. Facility Schematic Representation
..
L
Energy Fuels ~soulces, Blanding, UT Process Data tj.,,__.. I I
Source: South Yel;ow Cake Date: [}t(~ { L/ : ..: /.-lf._.
Time
/If 'l t)
I'~ ~ i>
I r / ·-::-'_-::
( t ·~ ~ ' ...
I '1/.· -·) r -. ;.... ..
i~ " )
c.. )D
I ·~
._/
Scrubber Flow GPM
#1 #2 L1P
' l ·) -(3 +
• ll . l .. <7-1 ,/-__, /?p 1-
> 7 /1 \ ..
....... -..-1 ~ . · . ...:; ---,!...., • --/
~-I
--/ v '--._/ ~~-/ '
·--c--1 (
"-:-• -
/ ;) ~
( (!.--,.)
~ --:) ~-......-' < ( ~ ·-(
~ ,-t -(~ -,_
~j-l/ '/ )"
'? -l. . { 1 -~ :; 2'. u
..,. ,.., 1 ,' --~
2. z__ ~ . .--
/ ·-. '-. ./
.2, 7 . \
/ -I ~-
'I. ") -~ . ~I
)
) 2. I.J
·; ( l. { 1-s-
J I
f ~-·{
~i ,' l -t-,..-,....._
) -' l~.c;-
1--"¥ :;.~ ~z ./
/ .t>\ 1' ~--') -/ .. I ·.·( .
--.::., J_ ~ ~ I
\
\
'.:.. :.· ... ~ . .. • f ..
Energy F~ls Resources, Blanding, UT Process Data fl. 7 '-"'f_.-_ -'
Source: South Yellow Cake Date: G1t+~(4
Scrubber Flow GPM
Time #1 #2 ~p
Uj :~~ 3.'L 1·~ 3/-~ 1 <=i. '9. s,-
, $.: t..{ 5!:7 ). ) 7·'-/ 3z.o 2o. oo
!Sf; l~ 5 .z._ 1.5,-3 2. ( t "l. '\ ...S'-
l'f _. <-i.S 5 ·Z. -:J ·s-5-l--~a I <=t .7;
1 s~: ts-1;.1._ .1· ~ ~~ ·'1 I""-, f-
1 s~; L(.,~-3 .z_ l·~ 3\ -~ zo-o>
,c.:..ts-+·~ ) {· ~ Z D· o o '?· "t.-
ll;'-ts-1·Z-i·<J" .?! . s. {~.'1'1
n-: ~~-3' l ;r.~ 3t-1 fl. g _) .
roo s·+ 1·) 7l·s (S,. ( D
~so s· r ~-'Z.. 3 1 . )-·. t ~-'1 D
OJ;oo ?·y r:J-~ ~ \ .L( I 4 · ""l s--
'1:3o 'S-· ~ 1·( )\· ~ '10,..)
j"O! ll D $·~ 1~ 3!·y 11.. qo
~a; 30 ),q lO ?2·0 1'\.ov ·. ~.
1 (: 0 0 5· v; l.l 3' ·4 It-Is-
1/: > 0 )·0 1·0 )2· u 1'1 .( z ..
, z_: 0 0 ~, 'l5 1 ~~ ~ (-C, I~, \ D
ll:)D ~·v 9·D ~~-~ 1~·2)
13 .. . c)O
Energy Fuels Resources, Blanding, UT Process Data
jt. .
Source: Grizzly Baghouse Date: 'ltB f lt.(_ .
Time Tons (Integrator) tph fpm
0'.19 ~ 3 58oo ' (.., cJ l( l, 6
e:t.t li (, 5S815 3'2..0 \It·~
\ ·. ( PJ "'358 3 J \L./),.,-t~L '-I
1~44 -~558So It-t { l tL ~
i()'.\1 (p~5870 3~ lll· 4
10 '.Lf q ~ ") 5 58) 7_0 I l (. ~
\ } t. 2-L-~ ).5 ~ o8 Lt~ t t( .-q-
\t:L--t~ ~ 7 (910 L{) tllt'::f-
l~'-L 3 G,'!> Sq2--(" t_l:) 1115
~z:qc:r / [p)5~3) y{ l t(. s
\ ~ ~ 2l ~ 3 S<=t 5o 3o \((·:>
1-:):iPJ (cJ) 59 b) Zo lllri
t '-{ '. ?..2-"3 59 B r z_o ,/ {{{,j
1'-t', )O (p)(,U)00 yl( pl.-)'
l5'. 2.-'2-(., ';:)~ b "LO 3S \ llr ~
\ 5 ~~ { ~"3G. Q)O 2) lll, 0
~· / l · I) lo)G, e'1~ lS l u '(p
-
APPENDIXE
Calibration of the console dry gas meter(s), pitot tubes, nozzles diameters, and temperature
sensors were carried out in accordance with the procedures outlined in the Quality Assurance
Handbook. The appropriate calibration data are presented in the following pages. The nozzle
calibrations are recorded on the first page of the field data sheets.
Figure 4 Schematic of Method 5/114 Sampling Train
Meter Box Calibration Data and Calculations Forms
Post-test Dry Gas Meter Calibration Data Forms
Type S Pitot Tube Inspection Data
Sample Box Temperature Sensor Calibration
E
Temperature Sensor t ~Probe ~
TypeS Pitot
Tube
Temperature
Temperature
Sensor
lmpingerTrain Optional, M3YBeReplaced
By An Equivalent Condenser
l Temperature
Sensor
Nozzle 1-SE:tT;acect
Sensor~ Gooseneck I ~--·---·---------
lmplngers "' ~ "'~~
/
TypeS Pitot
Tube ~
Stack
Wall
f--~ I Glass Filter
Holder
~ I I Heated Area
Manometer
Orifice
Dry Gas
Meter
Water Empty Silica
Gel
Air-Tight
Pump
Figure 4 Schematic ofMethod 5/114 Sampling Train
Vacuum
Line
Vacuum
Gauge
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three Cl'itical orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure
3) Run at tested vacuum (from Orifice Calibration Report). for a period of time
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information 1n the GREEN cells, YELLOW cells are calculated.
METER SERIAL .l .. ·--I
CRITICAL ORIFICE SET SERIAL et 1453S EQUIPMENT !D #:
K' I TESTED
..------r---1 FACTOR I VACUUM
0
G
G
RUN# I /AVGI I /in Hg)
0.1!113.1 13
l C.S137 13
0.8137 13
0,5317 13
2 0,5317 13
0.5317-1l
0.3307 13
(1.:1307 13
S· 0.3~07 13
261.525
268.512
275.475
3.00JI21
3.06.25.1
312.128
242.1140
248.398
.254.428
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
1U.512 6.987 .. 75
2ZSA75 6,963 •• 76
281.8~8 6.403 69 7Z
306.251 6.230 69 67
312.12.8 5.877 69 sa
311.~40 6.212 69 68
248.198 5.558• !ill 65
154.428 6~030 .. 59
260.240 5.812 s·g &t
The followirlf! equations are used to c-Cllculale the 11!andard volumes of air passed through the DGM, V,., (std), and the critical crifice,
V:1 (std), and the DGM calibr3~on factor, Y Thesto equations are automaliGally calculated rn the 5preadshaet above
75 n
75 76
71 75
68 " 69 68
71 67
64 sa
70 69
71 75
lis 'NWi1·iiiWM!W.., ~ •... ~?~ -!~·-
1 . .
2014 Pre-calibration
INITiAL FtNAL AVG (Pa01) ~ 25.35 IFYVARIAT!ON EXCEEDS 2.00%.
ORIFICE SHOULD BE RECAUBRATED
ELAPSED I l ;J [rtMEe(MtNII r:;J I I I I ~
40
80
02
76.75 ~ ~ 5.!683 5.8312 ~ ~
76.75 0 D 5 84S1 5.8312 !:ill, .l.:.an
76.50 D D. .Y!!!l !d!l! 1:.Q.!U! .Ul!.
AV G = .!!.ru :J!4!
n 68.00 9.00 1.10 s 2963 5.2758 ~ 1.:lli
7j 69.00 8.50 ~ 4 9827 !!J1! ~
70 69.00 9.0D llill ~ .!Jm! ~
AVG :c Qa!!! :Q.J..!
70 67.00 1).00 4.7244 4,7397 ~ ~
71 69.75 1uo 5.p•a• 5.1043 1J!ll LID
76 72.75 13.50 0.40 ~ ~ J..,Q,Ql Llli
AVG • .!J!2! !!d!!.
AVERAGE DRY GAS METER CALIBRATION FACTOR, y = r:J!iiO I
AVERAGE ~H,. .,-1..495 I
(1) 1/-mu•.tJ = K, * Vm• l'boi"-l~ ~f3~(1) 't = Net volume of gas sample passed through DGM, corrected to standard conditions
K, = 17,64 aRlin. Hg (English) I a 3858 ~Kimm Hg (Melric)
(2)
(3)
v",.t•t" == K '• Pbur * 0 .. ,f!;mh-
= Vc~~ .... ,
Vn1r.rdJ
T'" = Absolute DGM avg, temperature COR~ English, oK-Metric)
= Volume of gas sample passed through the critical orifice corrected to standard conditions
T ~e = Absolute amblenl temperature ('"R-English, ~K • Metnc)
K' = A11erage K' ractor from Critical Orifice Calibration
= DGM calibration fector
Ice Bath
Amb1entA1r
8o1JinaWater
<~.HI!!=
( D.75 e )2 dH (Vm(std))
V~(std) Vm
Temperature SensorS
Reference In Out
'F 'F 'F
33
62
202
33
62
203
33
62
203
PRE Console #4 Calibralian 2014
---"is ""'"*""'*N'M''MV ~ I -,. 1' ~---, METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range
2) Record barometric pressure before and after calibration procedure, ENVIRONMENTAL SUPPLY COMPANY
3) Run at tested vacuum (from Orifice Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet. 2014 Pre-Calibration Console 9
4) Record data and informalion in the (~: :J-t. cells, YELLOW cells are calculated,
FINAL AVG [P,.,)
METER SERIAL #:1 '·-· ---~-I
CRITICAL ORIFICE SET SERIAL#: 1453~ EQUIPMENT ID #:
I 25.45 I 25.45 IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATEO
K' TESTED
.-----:---~ FACTOR I VACUUM
0
G
G
RUN# I (AVG)
0.8137
0.8137
0.8137
0,5317
2 0.5317
0,5317
0.3307
2 0.3307
0.3307
(in Hg}
12
12
12
12
12.
12
12
12
12
88.612
94.007
99.367
105.106.
110,310
115.871!
121.2-05
126.327
131.458
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
94.007
99.387
104.803
110.310
115.878
121.084
126.327
UL458
1J7,053
5.395
5.380
5.416
5.204
5.568
5.206
5.122
5.131
5.595
65
fi5
65
70
TO
70
n
n
n
ELAPSED D~ TIME (MIN) A~~-I ft ..;..__._..L,;......;..,.;..r,
78 7~ 75 75
79 79 75 75
79 80 75 75
7&.75 5.00 § 4.5541
77.00 5.00 0 4.5393
T7.25 5.00 o 4,5676
4,5203 !Mll
4.5203 lhlli.
4.5203 l!,.lli
AVG= .!hill.
75 76 69 71 72.75 7.50 4.4031 4.4097 ll!!!
76 78 71 71 74,00 8.00 4.70 4 703& 1.QQ1
78 80 71 71 75.00 7.50 1.20 4.3862 ~ .1....I!M
AVG= ,!,QQI n!n " n
niR n n
J& In n n
73.75 12,00 § 4.3161
74.00 12.00 44 4.3217
74.00 13.00 .44 ~
~ L.!!ll
~ 1.Qll
~ .1..22!
AVG= .1..l!11.
The following equations are used to calculate the standard volumes of air passed through the DGM, V m (std), and the critical orifice,
V ~ (sld), and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, y =I 1.002 J
(1)
(2)
(3)
i 'm,.,,;, = K, • ~-111 • Pb(lr+(AH 113 61
Tm
I1cr .rc/; :;
l)har * e
K'• -Jn;;,"
= Net volume of gas sample passed through DGM, corrected to standard conditions
K1 = 17.64 'R/in. Hg (English), o 3656 'Kimm HQ (Metnc)
T m = Absolute DGM avg temperature (c:R ~ English, °K-Metric)
= Volume of gas sample passed through the critical orifice, corrected to standard conditions
T111"b = Absolute ambient temperature ("R-English,~-Metric)
K' = Average K' factor from Critical Orifice Calibration Vcr~~IJ, l"= --= DGM calibration factor
Vrn,,,,J;
AVERAGE llHe =r 1 .ssz 1
z
.!!Hi!!!= ( 0.75 !l ) .!!H (Vm(std))
V01(std) Vm
Temperature Senson;
Reference In Out
"F
32
72
201
"F
33
73
202
"F
33
73
203
l
::!!,!!§.
.Q.,ll
(1.94
1.743
ug
1,741
1.652
1M!!.
1.6'!5
1.565
1.565
1.565
Console 9 Pre-test 2014
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure.
b \!""'"• \',n,., llrll.tl>ll•o~4 -~i,~_-,
3) Run at tested vacuum (from Orifice Calibration Report). for a period of time
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and information in the GREEN cells, YELLOW cells are calculated,
DAre:! ...... y,. I
METER PART~ Conoole 4
METER SERIAL #;I .. DDO I
CRITICAL ORIFICE SET SERIAL#: 14535 EQUIPMENT ID #:
K' TESTED
FACTOR I VACUUM
RUN II (AVG) Qn Hg]
0
G
G
0,8137
0.9137
0.8137
13
13
13 § .o I I T r -11 I
I I
.0
.0
0.5317 13 21U04 -217.:!&5
z 0.5317 13 217.365 222.939
0.5317 13 222.!139 228.520
z
0.3307 ·p
0.3307 13
0.3307 13 §
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
5.561
5.574
5.581
.o
.o
.o
M ~ ~ ~ n
~ ~ ro n n
~ ro ro n n I
I lll-11
DGM
AVG
0
0.00
72.75
73.25
73.50
0,00
o.oo
o.oo
FINAL AVG (P .. ,)
I 25~55 I
ELAPSED
TIME (MIN)
e
25.55
§§
§ a
00
§§
ilm
4.7268
.um.
Energy Fuels
SYC Dryer
IF YVARJATION EXCEEDS 2.00o/o,
ORIFICE SHOULD BE RECALIBRATED
l
AVG=
4.7311 1.002
4.7311 1.000
4.7311 1.000
AVG= 1.001 ~
AVG
~
~
MQQ
The following equations are used to calculatethesta11dard volumes of air passed through the DGM, v. (sld), and the critical orifice, V0 (sld), and the DGM calibration factor, Y. These equalions are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, y =I 1.001 I
(1)
(2}
(3)
Vm,,,,; = K,•l'm• l'hot· .. (~/1 11~.61
1'111
= Net volume oi gas sample passed through DGM. corrected to standard conditions
K, = 17 64 'Riin Hg (English), 0 3656 'Kimm Hg (Metric)
T m = Absolute OGM avg temperature (0R -English, °K-Metric)
= Volume of gas sample passed through the critical orifice, corrected to standard conditions
T;meo-= Absolute ambient temperature tR-English, °K-Melric)
K' =-Average K' factor from Critical On free Calibration V'ct;\r.l) f-----= DGM calibration factor
-Vm1,:J, Ice B~th
Ambient Air
Bmhng Weter
AVERAGE .<1HC!! =c:!501 :J
&H@ = ( 0.75 E! )~ AH (Vm(std))
V.,(std) Vm
Temperature Sensors
Reference In Out
OF
33
62
202
OF OF
33
62
203
33
62
203
POST-TEST Console #4 Calibration 2014
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES '.:S --·~, ·..,.';~
r-
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure. ENVIRONMENTAL SUPPLY COMPANY
3) Run at tested vacuum (from Orifice Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and information in the C-! ::'·Fe\ cells, YELLOW cells are calculated
FINAL AVG (P.,,)
Energy Fuels
Dryer Baghouse
DATE:' ....... .• I
METER PART#: Console 9
METER SERIAL If:' ·--· -~-I
CRITICAL ORIFICE SET SERIAL ll: . 14535
I 25.55 I 25.55
EQUIPMENT ID #:
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
K' TESTED
FACTOR !VACUUM
RUN# (AVG) (in Hg)
G: 0.5317 13
0.5317 13
0.5317 13
833.506 838.984
838.984 844.124
844.124 849.259
D:EB EB o:rn EB
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
5.478
5.140
5.135
.0
.0
.o
.o
.0
.0
72 69 72 56 67
72 72 75 67 68
72 75 75 liS 58
I I I I I I
I I I I I I
I ELAPSED ::1 TIME (MIN)
~9--~~~~~~~
68.50 ~ 4.7019
70.60 0 4.3962
71.50 0 4.3826
0.00 §§
0.00
0.00
:::PH
0.00 bD
4.7132 .tm
4.4186 .t.!!Q§.
4.4186 1.00B
AVG= .t.!!Q§.
AVG=
AVG=
The following equations are used to calculate the standard volumes of air passed through the DGM, Vm (sld). and the critical orifice. V"
(sld), and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, y =I 1.005 -,
(1) r·m,,,,, = K, * Vm• ?bar+ (M-f /13.6)
Tm
= Net volume of gas sample passed through DGM, corrected to standard conditions
K1 = 17,64 'Riin Hg (English), 0 3858 'Kimm Hg (Metric)
AVERAGE ~H1'1 =r 2.843 ,
l'har * e
f/cri.''·'· = K'*-...Jl~rnh
T m = Absolute DGM avg temperature ('R -English, 'K-Metric) 2 t.H~= ( 0.75 e) ~H (V.,(std))
V0,(std) Vm
(2)
(3) Vc~•rdr l' = _--~m\lld)
= Volume of gas sample passed through the critical orifice, corrected to standard conditions
T,mb = Absolute ambient temperature i'R-English, 'K-Metric)
K' = Average K' factor from Critical Orifice Calibration
= DGM calibration factor
Temperature Sensors
Reference In Out
'F
32
72
201
'F
33
73
202
OF
33
73
203
1
!!J!Q
2.862
2.841
k.ill
Console 9 Post-test 2014
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range
2) Record barometric pressure before and after calibration procedure.
3) Run at tested vacuum (from Orifice Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and information in the U'"-" :-;cells, YELLOW cells are calculated.
METER SERIAL II:! ····--·-I
CRITICAL ORIFICE SET SERIAL II: 145JS EQUIPMENT ID #:
K' TESTED
FACTOR VACUUM l ORIFICE II ) RUN# (AVG) (in Hg)
0: 0.6808 13
0.6808 13
0.6808 13
INITIAL FINAL
814.600 820.406
820.405 827.109
827.109 832.485
5.805
6.704
5.376
68 76
68 79
68 80
7~ 63
80 $3
U1 85
63
65
66
D:EBE
D:EBE
.0
.0
.0 I I I I I I
.0 I -~-I I I I .0
.0
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
The following equations are used to calculate the standard volumes of air passed through the DGM, V m (sld), and the critical orifice. Va
(std), and the DGM calibration factor, Y These equalions are automatically calculated in the spreadsheet above
DGM
AVG
70.25
71.75
73.00
0.00
0.00
0.00
0.00
0.00
0.00
2~ :l -··~i---•.:~ *fflli&IMI#i1Ppiffli!M1!.W
1· • --
ENVIRONMENTAL SUPPLY COMPANY
~ AVG(P._,)
I 25.65 I 25.55
ELAPSED
TIME(MIN)
9
§§.05 _
2.05
2.05
§§
§§
~
Hill
4.5754
Energy Fuels
Grizzly
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
1
(3) J y
Y VARIATION(%)
4.9219 0.991
5.6791 0.993
~ Q,ID
AVG= 0.992 2d!Q
AVG=
AVG=
AVERAGE DRY GAS METER CALIBRATION FACTOR, y =I 0.992 I
AVERAGE <loH~ =I 1.716 I
(1) r··m""" = K, *I'm* Pbar+(J}.H /13.6)
Tm
= Net volume of gas sample passed through DGM. corrected to standard conditions
K1 = 17 64 'Rtin. Hg (English). o 3858 'Ktmm Hg (Metric)
(2)
(3)
Vc.~,~: ,~.,,, = K '* l)har * 0
.J'J'wnh
Vc'(j/,,j r = . --~ /11t \I;/:
T rn = Absolute DGM avg temperature ('R -English, 'K-Metric)
= Volume of gas sample passed through the critical orifice. corrected to standard conditions
T,""' = Absolute ambienltemperaiUre ('R · English, 'K ·Metric)
K' = Average K: factor from Critical Orifice Calibration = DGM calibration factor
6H® = ( 0. 75 e )z 6H (V m(std))
Vcr(std) Vm
Temperature Sensors
Reference In Out
'F
32
72
201
'F
33
73
202
'F
33
73
203
1ll!!
1.7]6
gg
Console 9 Post-test 2014
Type S Pi tot Tube Inspection Dattt
Date: _):....:l...:..l _tl.-__:{~13 __ _ Pitot Tube Identification: __ 2._\ ---------
Technician: __ M_._;,IY\_..:~:....:':....~...:o..M:..:::...;....::C\..:.::::.:..(...:t.A..::....::. _____ _
r)~ ~ --"/v Dt~ '31) ill, Is 1\ = P0 ?
Is 1.05 • D, s D, $ 1.50 • D,? Y-eS
PA= • { 2-)-in
2
?
B
........-( a,
I
~a:
z: -;~-
~ .. -.. --·r· w --""'"~ -··-··-··-~·
··--~ F '" _ ... ! ..
CF:IJ ,
I
,. L. -(' Pn= ,")
rt1 <tO"
n,< !0°
llr < .S"
p, < 5"
Z :S 0.125 in
W s 0 03125 in.
W > 3 i11chcs
Z > 3/4 inch
1\.
u.~ D 0
aJ ~ z...
p,=
0 p, =
Z"-,\)18 ln.
W = ' 0\ Lf in
\Y -~c.r In,
Z= '\ Ill.
•"·~ ~-·r-----y <': 3 inches
,,,
Y = ______ in.
Th•• pi tot tube 1\lects the specifications for a calibration factor ofO 84?
Tempernturc Sensor Calibrnt1on
Reference·
·;' ... Temperature Tcmncrnltll\! Temperature
.. !';. ' ... -;.;·~ Source Reference Sensor Ditlhence
IMediulll) rn ("I') <"fl
AIR (, 8 (,'1 I
Probe Continuity '{e ~
tleat Check 248 \[(.) l.~ 0
AIR (.,~ <..6 0
ICE WATER ~~ 3 Ll l
Stack BOIL WATER 2~l. 2.o L. I
SILICONE OIL .
Type S Pitot Tube Inspection Data
Date:_\~l-_/_I'Z-_____:__;/1...;:.)_ Pilot Tube Jdentification: __ "Z_T.:........·_....:\ _______ _
(I
Technician: /V\ • M S rJCI.,Mil,./ (,)-....
Dt=_:} )O __ in ls P A = Pa ? '( ~.s __..;. ______ _
.:..l'.t;.,_=_·_?.=-1.....:)_~~----in .
ls 1.05 • D, s D, ~ 1.50 • D, '? _"/...!.-2:-e..::...}~-----
.:..1'-'"B-~_._z..._{._)_"" _____ in
-o -'d
-~~-·~.w
............. -r... ,., . ·~
a,< 10°
a2 < 10"
fl, < 5"
lh <5''
Z~0.\25 in
~ !'' ........... (:) ·~ ~:.~ ~;~ 1-·"""" ·--::--~---Y::0:3 inches . .
a, "'--=0;.._ ___ ·0
·
U) "' __ "2..;:_ __ _
p,= __ .=,.3 __ _
p,= _____ _
. o!l( Z= ------in.
_...;,.. _ ___._ __ ln.
-----'------'"
Y = --~::.:...:,'2::.. • .:...·(_'_in
lhe pitot tube meets the spccilications for n calibration factor of0.84? '{e)
"I'CIII(!CIUlurc Sfur$11r C~lihr1111011
'-: .~.4t Temperature TelllO<\tntur~ Ttmpomture
~ . ' Source Refetem~c Sensor Dilkr~nce t,,~· ~~ (Medium) (''F) (UF) ("Fl
AIR II 17... I
Probe Continuity '(-<:~
11cat Check 248 'kS 2.)0
AIR Co cl "l 0 I
TCEWATER ~ .3 11 I
Stack BOIL WATER (oL <..o \ I
SILICONE OIL
Type S Pito! Tube Inspection Data
Dale: _ __:_1"1..___:_/1_~_/_1_3 Pi tot Tube ldenlification: _ _::.3~B~-~~(;.,.·7::__ _____ _
Technician: _,_v_\:....._...JM!....-l--=~"-'NL:. ~o..:=vV\.-=.....:~v....:....:...(_v--,;___:_ ____ _
l Pl.
t P(l
Dt= .~f-) ln.
PA = .1..\{po in
lsP"=Pn? 'f~> __ ,;,.__ __ _
ls 1.05 • D1 ~ D1 ~ 1.50 • D1 ? __ '(:._4.:..:~~----
Ps = I 1..11o t> in
a 1 < 10" a,=
u 2 < to• o.l=
~1= __ 1. __ _
~' < s• ~,= __ .J __ ~
-] -• ol~ z Z :-; 0 125 in Z= in.
? ( _ ........
~ ~0?FA·:=r.-~~. w \V:;; 0.01125 in W= ·ooB in
W > 3 inehes w~ ~ in~
Z > 3/4 inch Z= 3/c..i in
The pilot lube meets the specifications for a c.11ibration factor ofO 84? \IQ.S
Temperature Sensor Cnlibrntion
Reference·
''\\ .,._ -.' Temperahlre Temperature T~!11(1ei'Ol1UIO: !~ ·'~ SClurte Reference Sensor Difference ., ..... ~ .. (Medium) ("F) (vF) C"l·l
AJR r...<o (,1-\
Probe ContinuitY \I~~
Heat Check 248 '-ro ~-e..':;
AlR lo+ (,~ I
ICE WATER 3'i 3'1 0
Stack BOlL WATER 2.0 ~ 1.~3 l
SILl CONE OIL
TETCO
Sample Box Temperature Sensor Calibration
Date: 12/13/13 Calibrator: Dean Kitchen Reterence: Ome~o~a CL3512A
Thermocouple Temperature Temperature Temperature
lJnit ID Location Source Reference Sensor l)ifference
(Mctlium) ("F) ("F) ("F)
Oven Water 32 34 2
Water 204 203 -I
A Oven (4) Water 33 34 1
Water 204 202 -2
Impinger Out
Water 33 34 I
Water 204 203 -I
Oven Water 33 33 0
Water 204 202 -2
B Oven (4) Water 33 34 I
Water 203 203 0
lrnpinger Out Water 32 33 1
Water 204 202 -2
Oven Water 32 33 l
Water 204 203 -I
c Oven (4) Water 33 34 I
Water 204 204 0
lmpinger Out Water 33 33 0
Water 203 202 -I
Oven Water 33 34 I
Water 203 203 0
D Oven (4) Water 33 34 I
Water 204 204 0
Water 33 -.-. 0 lmpinger Out .).)
Water 204 202 -2
Oven Water 33 3'4 I
Water 203 202 -I
E Water 33 -.-. 0 Oven (4) .u
Water 204 203 -I
1mpinger Out Water 33 34 I
Watet· 204 203 1
Oven Water 33 34 I
Water 204 202 -2
F Oven (4) Water 33 34 I
Water 204 202 -2
lmpinger Out Water 33 33 0
Water 203 202 -I
lmpinger Out G Water 33 34 I
Water 204 203 -I
Impinger Out 1-1 Water 33 34 I
Water 204 202 -2
-Water 33 33 0 Impinger Out I Water 204 202 -2
lmpinger Out J Water 33 34 I
Water 203 202 -I
APPENDIX F
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
ATTACHMENTH
SURFACE WATER GRAPHS AND FIELD DATA SHEETS
1.00E-05
1.00E-06
1.00E-07
-.!!
C'CI ~.OOE-08
C)
0 ...J -
1.00E-09
1.00E-10
1.00E-11
•• • •
• • ... . -• --
---:. _, ~--:....._ ------
Ia ---
~ o_,CO'l,
~" ~
~~Oj ~~
Cottonwood Creek Dissolved Radionuclide Concentrations
(uCi/ml)
... --
•
•
-----
.
o_,OJ'),
~" ~rV"'
-
•
--
........ -
•
• •
•
-
• • ~ • • .. -
• ... .._. __ .._....._ ____
PJCO ':!..~Oj ~ro
~n;, ~ ~ ~"
1----;u:_Nat. • Th-230 • Ra-226 I
.
~0; ~ <,j.~Oj
..
•
.. .. •
-.-
--r:;)~l><
~rc ~"
r::::,rf' <,j.~rc
1.00E-06
1.00E-07
1.00E-08
-.!!
C'CI ~.OOE-09
C)
0 ...J -
1.00E-10
1.00E-11
1.00E-12
fb<t;,
':\to..Oj ~"'
Cottonwood Creek Suspended Radionuclide Concentrations (uCi/ml)
•
... -• -.. • -• ... --•• • I. ... ~· • • .. ... • ..
i ..... .-i . -=-· ... • • • • • ·-· ··--·------·-·-····-----••• • ... ..
. . '
~ 2><::) 2>n;, 2><,;, 2>'0 &)to.. ~ &)co &)<?> to..~ to..Oj Qj to..Qj ~to..Qj ~to..Qj ~ ~ ~ ~ ~ ~ ~to;. ~ ~€)1 ~€)1 ~€)1 ~€)1 ~f); to..rV~ ~to..f;j rJ. n} ~ q}cv <.j."-~ n} to.."
[ • U-Nat. • Th-230 • Ra-226 [
* ••• -
-
to..<,;, ~ ~ ~ ~€)1 ~€)1
rVto.. to..~
1
0.1
0.01
0.001
0.0001
0.00001 -Cl)
~.000001
C/)
tn ~0000001 -
1 E-08
1 E-09
1 E-10
1 E-11
1 E-12
1 E-13
~r:::,OJ /\,.,r&~
-
"r:::, ~ ~<),.'1)
Westwater Creek Dissolved Radionuclide Concentrations
(uCi/ml)
"r:::, fVr:::,
c6-"<::j
............ ~ cV~
...... ...... ~ cy."t:;.
~
~"<),. ~~~
[ • U-Nat. •Th-230 & Ra-226 J
~"<),. c6-~
...... r:S-"
-
...
...... ~ ~ ~'1)
""
......~ ~ <,j.ro
0.1
0.01
0.001
0.0001
0.00001 -Cl)
11J.000001
en
~000001 ...J -
1 E-08
1 E-09
1 E-10
1 E-11
1 E-12
1 E-13
~OJ '\\ro
Westwater Creek Suspended Radionuclide Concentrations (uCi/ml)
~"~ ~~f))
-
~"~ c8-"~ ':!.."'-" ~~ ~"" cy.~ ~"~ ~~
I • U-Nat • Th 230 • Ra-226 I
I
':!.."'-~ ~"co "~
'
':!.."-0;) <d-ro
_._
"1'-."-0;) ~f)) "~
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Date: 2/07 Revision: DUSA-1
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURFACE WATER
WHITE MESA MILL
LOCATION (Circle o~onwood ~estwater Canyon Other (describe). ___ _
DATE: 3/5 I ~0 /~
pHBUFFER 7.0 _7_,_0 ___ _
BY: I"H
(Sampler's initials)
pH BUFFER 4.0 __ L/!,_. 0 __ _
SPECIFIC CONDUCTIVITY __ 1._.1'--'Cf'---------.....t:uMH==O=s
STEAM DEPTH:
pHofVVATER __ 7~~~9~l~-------TENW __ ~I=3~.6~1 __ _
. '
COND !!mhos £71 COND !lmhos £8'-f
pH Units _7_..!...!.....7'-~=----pH units 7, $55
Temp °C L?,. 7 S Temp °C l~. Sb
COND J.tmbos b3Y COND !lmhos t,gL.f
pH units 7,SD pH units 7, g 7
Temp °C l'?:>,f:.O Temp °C 13 .SS
Conunents:
Acr •\lc.J o" ~fi-e a..~ 12.10 G-ro.b 5o-r>1fles. pe,Qrl""'c.J o-.t 12.15
LeG $.-~}c. J-·.\2(7 . _,;tJJ'lC(i Ga-r r1r1 •' Cl~(j otll prc;y:Y'~
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Date: 2107 Revision: DUSA-1
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURFACE WATER
WHITE MESA MILL
LOCATION (Circle one):Cononwood Creek('}§Stwater Canyog)Other (describe) ____ _
DATE: 3/5/Z.or'-\
pH BUFFER 7.0 __ /-'-'#=0"------
BY: G-o..r-r-lii\. Po..l-"""c.r { (,.,e.
(Sampler's initials)
pH BUFFER 4.0 __ 4_,_,_ . .....,0=-----
SPECIFIC CONDUCTIVITY _ _.9_.9__,lt.___ _____ -==u=MH=O=s
STEAM DEPTH:
pHofWATER _____________________ _ TE~---------------
'I
COND cbll=nho=s<---------COND ll=mh=os,__ ______ _
pH Units -------------pH units --------------
Temp °C ____________ _ Temp °C ____________ _
COND ll-=mh=os::.-___ _ COND!.i=mh==os~-------
pH units ----------pH units-----------
Temp °C ------------Temp °C ___________ _
Comments:
Anl J(.·l """ s-a.. c.. I--\ 'Z.'"i y k.-..re· ..... rw-... w L ' L(h¥ p r<S ..... ±. k[Ll b !.o,)L;._( l>ev' p kot,-, .....>.:...I ~~-
LR"' .,;; f. c.. t?--1-rZ.-1:h. .3/p=t /I '1 A,.,.,.,,.), l'lb !:;'/L .;.l-IQ('l.). G·w.cd<>i p.:.u;J ~ et-(,::.o.h
~1'2.7/1'-\
L ru:.l<-Wo\.5 J..'"'f , SU. p\..o..ah.!, Arrwc,ol oe= s .±c.. D-.t I Soo. C rr-t \L '-o,.l....S J.."y .. Sc.c, 9 b--o+o.
EN:RGY
1_/\0CH:;J\ t C'HI!.___~-.
www.enBfEYiab.com
A1llltflal £'""'-Slltu 1/BZ
Helena, MT 877-472-0711 • Billings, MT 801-735-448! • Casper, WY 888-235-0515
Gillette, WY 816-188-7175 • Rapid City, SO 888-672-1225 • College Station, TX 888-690-2218
March 12, 2014
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Workorder No.: C14030228
ANALYTICAL SUMMARY REPORT
Project Name: 1st Quarter Surface Water 2014
Energy Laboratories, Inc. Casper WY received the following 1 sample for Energy Fuels Resources (USA) Inc on 3/7/2014 for
analysis.
Sample ID Client Sample ID Collect Date Receive Date Matrix Test
C14030228-001 Cottonwood Creek 03/05/14 12:15 03/07/14 Aqueous Solids, Total Dissolved
Solids, Total Suspended
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 QAIQC Summary Report, or the Case Narrative.
If you have any questions regarding these test results, please call.
Report Approved By: 4j'~ c\:k nv',g_____
Report Proofing Specialist
Digitally signed by
Kathy Hamre
Date: 2014.03.12 14:46:12-06:00
Page 1 of?
••·• -••·• -·-_,._ ~,.• __ .,, "' .. ,,,. ........ --· .......... -~r··• •• ...... -·---...~-
Gillette, WY 866-688-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690-2218
CLIENT: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Surface Water 2014 Report Date: 03/12/14
Sample Delivery Group: C14030228 CASE NARRATIVE
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4"C (±2"C)
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.
SOIUSOLID 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 Ell 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, SD
eli-cs -Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
USEPA: WY00002, Radiochemical WY00937; FL-DOH NELAC: E87641, Radiochemical E871017; California: 02118CA;
Oregon: WY200001, Radiochemical WY200002; Utah: WY00002; 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 Ell's certification coverage by visiting www.energylab.com
Ell 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?
EI\ERGY
t 1\.-... C•I-id C::',ol: •
www.energylab.com
Aul1flai~SMIB!2
Helena, MT 877-472-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-1515
Gillette, WY 868-188-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Surface Water 2014
LabiD: C14030228-001
Client Sample ID: Cottonwood Creek
Analyses Result Units
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS@ 180 C
Solids, Total Suspended TSS@ 105 C
Report
Definitions:
RL -Analyte reporting limit.
QCL-Quality control limit.
419
86
0 -RL increased due to sample matrix.
mgll
mgll
Qualifiers
0
MCLI
RL OCL
10
10
Report Date: 03/12/14
Collection Date: 03/05/14 12:15
Date Received: 03/07/14
Matrix: Aqueous
Method Analysis Date I By
A2540 C 0311 0114 16:08 I tmm
A2540 0 03111114 10:04 I alp
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
Page 3 of7
EN:RGY
t .-q-\tJI• A10f.f l ~ '...J
www.enel&)'lab.com
~ flullltlcl Slllu /til
Helena, MT 877-472-0711 • Billings, MT 801·735·4489 • Casper, WY 888-235-0515
Gillette, WY 8&6-186-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Surface Water 2014
Analyte Count Result
Method: A2540 c
Sample ID: MB·1_140310A Method Blank
Solids, Total Dissolved TDS@ 180 C NO
Units
mg/L
Sample ID: LCS-2_140310A Laboratory Control Sample
Solids, Total Dissolved TDS@ 180 C 1960 mg/L
Sample ID: C14030198-002A DUP Sample Duplicate
Solids, Total Dissolved TDS@ 180 C 16.0 mg/L
Sample ID: C14030198-003A MS Sample Matrix Spike
Solids, Total Dissolved TDS@ 180 C 1130 mg/L
Qualifiers:
RL -Analyte reporting limit.
RL %REC
7
20 98
10
11 99
Report Date: 03/12/14
Work Order: C14030228
Low Limit High Limit RPD RPDLimit Qual
Batch: TDS140310A
Run: BAL-19_140310A 03/10/14 16:05
Run: BAL-19_140310A 03/10/14 16:06
90 110
Run: BAL-19_140310A 03/1 0/14 16:06
3.8 5
Run: BAL-19_140310A 03/1 0/14 16:07
90 110
NO -Not detected at the reporting limit.
Page 4 of7
EN:RGY
t ·\hC..)f• o1·~r ... ,_._,
www.energylab.com
Aa/ftlell Clullfllu Sitler I BSZ
Helena, MT 877-472-0711 • Billings, MT 808-735-4489 • Casper, WY 888-235-0515
Glllatte, WY 8611-&86-7175 • Rapid City, SD 888-672-1225 • College Station, 1X 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Surface Water 2014
Analyte Count Result
Method: A2540 D
Sample ID: MB-1_140311A Method Blank
Units
Solids, Total Suspended TSS@ 105 C NO mg/L
Sample ID: LCS-2_140311A Laboratory Control Sample
Solids, Total Suspended TSS@ 105 C 100.0 mg/L
Sample 10: C14030214-001A DUP Sample Duplicate
Solids, Total Suspended TSS@ 105 C NO mg/L
Qualifiers:
RL-Analyte reporting limit.
Report Date: 03/12/14
Work Order: C14030228
RL %REC Low Limit High Limit
Run: BAL-19_140311A
2
Run: BAL-19_140311A
10 100 80 120
Run: BAL-19_140311A
10
NO -Not detected at the reporting limit.
RPD RPDLimit Qual
Batch: TSS140311 A
03/11/14 1 0:03
03/11/1410:03
03/11/14 1 0:04
5
Page 5 of?
EN:RGY
t ·,.,, H ."'l•:l-11. ;
www.energylab.com
Mll/ffbi~SIIa IISI
Helena, MT 877-472-0711 • Billings, MT 801-135-4489 • Casper, WY 888-235-8515
Gillatte, WY 86&-18&-7175 • Rapid City, SD 888-172-1225 • Collage Station,TX 888-&90-2218
Workorder Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: BL2000\khelm
Reviewed Date: 3/10/2014
Shipping container/cooler in good condition?
Custody seals intact on all shipping container(s)/cooler(s)?
Custody seals intact on all 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 Cl, Sulfite, Ferrous Iron, etc.)
Temp Blank received in all shipping container(s)/cooler(s)?
Container/Temp Blank temperature:
Water-VOA vials have zero headspace?
Water-pH acceptable upon receipt?
Standard Reporting Procedures:
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
2.4'C On Ice
Yes O
Yes 0
C14030228
Date Received: 3/7/2014
Received by: dw
Carrier NDA
name:
No 0
No 0
No 0
No O
No 0
No 0
No 0
No O
No 0
No O
No 0
No 0
Not Present O
Not Present D
Not Present 0
Not Applicable O
No VOA vials submitted 0
Not Applicable 0
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.
Contact and Corrective Action Comments:
None
Page 6 of7
Samples Shipped to: Energy Laboratories Contact: Garrin Palmer ..:::2~39~3:><S~a~lt~C~re..;.;:e~k;.;,H;.;.wy.:;...._________ Ph: 435 678 4115
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
ProJect Samplers Name Sample-rs Signature
1st Quarter Surface l /~ A';:-·~ 1-=--Water2014 Garrin Palmer
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
Cottonwood Creek 315/2014 1215 Total O'lssolved Solids, Total Suspended Solids
Comments: Samp!e5·are not P!eserved or filtered.
RelltlQUished By:(Signature)
Garri.n Pai~{J~ Date/Time Received By:(Signature)
3/6/2014
1030
Date/Time Received By:(Sfgnature)
-C..l3D~
C..\4030~
Datemme
Page 7ofT
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Date: 2/07 Revision: DUSA-1
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURFACE WATER
WHITE MESA MILL
LOCATION (Circle one?.£ottonwood S£,.eekJ Westwater Canyon Other (describe). ___ _
BY: ~""'-9.....\ .... >-l.-c (..,
(Sampler's initials)
pH BUFFER 7.0 ___ +~· L.=-1')--pH BUFFER 4.0 __ ....:..tl.:_' u __ _
SPECIFIC CONDUCTIVITY ___ ...:..q ....!..'f...l.9 ___ ----!:u~MH~O~s
STEAM DEPTH:
pHofWATER _~~~-~1~7 _______ _ TEMP _...LI~g..._. Cf.!..C2.==-----
• I
COND umhos £$· jyl,, 3 -COND 1-1mhos l-'[(o.C(
pH Units ~.00 pH units '?. 2f
Temp°C /ca.er-+ Temp°C /f".ct (
COND 1-1mhos l-oz.-t COND 1-lmhos 1 '?y.;;
pH units )?''' t':t-pH units 0.-z.{
Temp°C ' ~-'iter Temp°C 1?:1?
Comments:
b'ji)K.-J_ on '3• .k_ cA I 3 I D L, .;-r s . (•c-r c .-r. Q c.. [ l"".g c r.,.._,J ]) ru•·d T.A k """"....._
t f.u ... ,. bH'IL~ "'"'"J Co/d . LJ /"(,. 7
s....""""f'')
Corle.dec-l o-f-1315.
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Date: 2/07 Revision: DUSA-1
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURFACE WATER
WHITE MESA MILL
LOCATION (Circle one):Cottonwood Creek ~estwa er can;gyot.her (describe) ___ _
DATE:_3) I ':1/ Zol L{ BY: &&..ell', .A.. .Po.. LAA.e-C
(Sampler's initials)
pH BUFFER 7.0 __ 7.L...l'.__:C)=----· pH BUFFER 4.0 Ll, Q
SPECIFIC CONDUCTIVITY __ _,_q--lq._9..__ ___ ~u=MH=O:::..::<s
STEAM DEPTH: .AlA
pHofWATER ___ ~A/~A~----------TEMP _J-_!1/X..,.,A~-------
COND umbos COND w:m1os
pH Units pH units
Temp°C Temp °C
COND J.Lmhos COND J.Lmhos
pH units pH units
Temp°C Temp°C
Comments:
6·/6/1'1 -Ar,.l!)(.Gl. o,.._ sdc.. c..± oqoo. C,tc.et.l..)&<r by~ l~r.~ pkat-w)
tl3o/it..l-Art~vc.c).. Q~ nil' l'..t-\..3JD. (rce.\C.. Wk$ tAt'( Ls'-'-pk-1-o ).
l)A..~bk. "\-o ,Sc...~ l~ lou-.+~oA bc.c.&...uJ~ "'-D w"-+~ w&<-..S fr-tSe.~-L
W ll\ .>t--"""-f k. c:So; Is o.. + locv-. +-. OA.. &lur;~ A ~.5u .. d· ~l.)e.v-... +.
J
•• . .. '. ·~ ..
I
EN:RGY
l J\--± \-11 • •'· I ~. T 'I~ •
Helena, MT 877-47Z-0711 • Billings, MT 801-735-4489 • Casper, W'f 811-235-1515
Glllatta, W'f 11&-186-7175 • Rapid City, SD 818-&72-1225 • Collage Station, TX 881-610-2211
April 29, 2014
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C14040518
ANALYTICAL SUMMARY REPORT
Project Name: 2nd Quarter Surface Water 2014
Energy Laboratories, Inc. Casper WY received the following 1 sample for Energy Fuels Resources (USA) Inc on 4/16/2014 for
analysis. --------------------------------------------------------------------------------Lab ID Client Sample ID Collect Date Receive Date Matrix
C 1404051 8-001 CottonWood Creek 04/14/14 13:15 04/16/14 Filter
Test
Sample Filtering
Uranium, Dissolved
Uranium, Suspended
Digestion, Total Metals
Gross Alpha, Gross Beta
Radium 226, Dissolved
Radium 226, Suspended
Thorium, Isotopic
Thorium, Suspended Isotopic
Solids, Total Dissolved
Solids, Total Suspended
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: 41~ c\:k )%'&___.
Report Proofing Specialist
Digitally signed by
Kathy Hamre
Date: 2014.04.29 12:48:59 -06:00
Page 1 of 12
Gilletta, WY IIB-181-7115 • Rapid City, SD 118-172-1225 • Collage Station, TX BIUID-221 8
CLIENT: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014 Report Date: 04/29/14
Sample Delivery Group: C14040518 CASE NARRATIVE
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4"C (±2"C)
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.
SOIUSOLID 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 Ell reflects the results for seven
individual Aroclors. When the results for all seven are ND (not detected), the sample meets EPA compliance criteria for PCB
monitoring.
SUBCONTRACTING ANAL YSJS
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, SD
eli-cs-Energy Laboratories, Inc. -College Station, TX
CERTIFICATIONS:
US EPA: WY00002, Radiochemical WY00937; FL-DOH NELAC: E87641, Radiochemical E871 017; California: 02118CA;
Oregon: WY200001 , Radiochemical WY200002; Utah: WY00002; 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 Ell's certification coverage by visiting www.energylab.com
Ell 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 12
EN:RGY
I ,"'.·tOfo"\l O I.JI. _
www.energytab.com
Allll1tlal EDflla !*a llfZ
Helena, MT 877 .... 72-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-1515
Gillette, WY 866-186-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-690-2218
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
LabiD: c 1404051 8-001
Client Sample ID: CottonWood Creek
Analyses
PHYSICAL PROPERTIES
Solids, Total Dissolved TDS@ 180 C
Solids, Total Suspended TSS@ 105 C
METALS-DISSOLVED
Uranium
METALS-SUSPENDED
Uranium
RADIONUCLIDES-DISSOLVED
Gross Alpha
Gross Alpha precision (±)
Gross Alpha MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
RADIONUCLIDES-SUSPENDED
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
485 mgll
12 mgll
0.0086 mgll
NO mgll
13.0 pCii L
2.3 pCi!L
2.5 pCil l
0.39 pCil l
0.15 pCiiL
0.16 pCii L
-0.004 pCii L
0.08 pCill
0.2 pCi!L
0.01 pCiiL
0.12 pCiiL
0.20 pCiiL
0.1 pCill
0.07 pCiiL
0.09 pCiiL
MDC -Minimum detectable concentration
Qualifiers
D
u
u
U -Not detected at minimum detectable concentration
Report Date: 04/29/14
Collection Date: 04/14/14 13:15
Date Received: 04/16/14
Matrix: Aqueous
MCL!
RL QCL Method Analysis Date I By
10 A2540 C 04117114 15:21 I tmm
10 A2540 D 04118114 11 :13 I alp
0.0003 E200.8 04117114 20:49 I elm
0.0003 E200.8 04122114 21 :16 I elm
E900.0 04125114 17:28 I lbb
E900.0 04125114 17:28 I lbb
E900.0 04125114 17:28 I lbb
E903.0 04123114 06:32 I lmc
E903.0 04123114 06:32 I lmc
E903.0 04123114 06:32 I lmc
E908.0 04123114 09:01 I dmf
E908.0 04123114 09:01 I dmf
E908.0 04123114 09:01 I dmf
E903.0 04128114 07:48 I lmc
E903.0 04128114 07:48 I lmc
E903.0 04128114 07:48 I lmc
E9'o8.0 04125114 08:52 I dmf
E908.0 04125114 08:52 I dmf
E908.0 04125114 08:52 I dmf
MCL -Maximum contaminant level.
NO -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 3 of 12
EI\ERGY
l ~\· C.f .tol 01"1L 'j
www.enefiY)eb.com
Alll/tllal E"laiRw .Qallll
Helena, MT 871-472-0711 • Billings, MT 801-735-4489 • Casper, WY 8811-235-1515
Gillette, WY 118-18&-7175 • Rapid City, SD 118-&72-1225 • College Station, TX 888-&90-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Analyte Count Result Units
Method: A2540 c
Lab ID: MB-1_140417A Method Blank
Solids, Total Dissolved TDS@ 180 C ND mg/L
Lab ID: LCS-2_140417A Laboratory Control Sample
Solids, Total Dissolved TDS@ 180 C 1980 mg/L
Lab ID: C14040512-001 B DUP Sample Duplicate
Solids, Total Dissolved TDS@ 180 C 370 mg/L
Lab ID: C14040518-001A MS Sample Matrix Spike
Solids, Total Dissolved TDS@ 180 C 1600 mg/L
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
RL
7
20
10
11
Report Date: 04/29/14
Work Order: C14040518
%REC Low Limit High Limit RPD RPDLimit Qual
Batch: TDS140417A
Run: BAL-19_140417A 04/17/14 15:20
Run : BAL-19_14041 7A 04/17/14 15:20
99 90 110
Run : BAL-19_140417A 04/17/1415:20
0.3 5
Run: BAL-19_140417A 04/17/14 15:21
101 90 110
ND -Not detected at the reporting limit.
Page 4 of 12
EN:RGY
!... .. ·\J !D! -t ..... ~TC-1 .. 11 •;
www.energylab.com
Aalttlal Ezulaa Sl8a 111Z
Helena, MT 877 .... 72-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-0515
Gillette, WY 81&-18&-7175 • Rapid City, SD BBB-&72-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Analyte Count Result
Method: A2540 D
Lab ID: MBLK Method Blank
Solids, Total Suspended TSS@ 105 C ND
Units
mg/L
LabiD: LCS Laboratory Control Sample
Solids, Total Suspended TSS@ 105 C 92.0 mg/L
Lab ID: C14040507-002B DUP Sample Duplicate
Solids, Total Suspended TSS@ 105 C 22.0 mg/L
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
RL
2
10
10
Report Date: 04/29/14
Work Order: C14040518
%REC Low Limit High Limit RPD RPDLimit Qual
Batch: TSS140418A
Run: BAL-19_140418A 04/1 8/14 11 : 12
Run: BAL-19_140418A 04/18/14 11 :12
92 80 120
Run: BAL-19 140418A 04/18/14 11:13 -
4.7 5
ND -Not detected at the reporting limit.
Page 5 of 12
EN:RGY
l ."l.t!UftAT:.;fJII ~
www.energytab.com
AltMftJal &r:e~wa .a. rw Helena, MT 877--472-0711 • Billings, MT 801-735-4488 • Casper, WY 888-235-0515
Gillette, WY 8&6-186-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
I Analyte Count Result Units RL
Method: E200.8
Lab ID: ICV Initial Calibration Verification Standard
Uranium 0.0507 mg/L 0.00030
Method: E200.8
Lab ID: LAB Method Blank
Uranium NO mg/L 1E-05
Lab ID: LFB Laboratory Fortified Blank
Uranium 0.0498 mg/L 0.00030
Lab ID: C14040511-001 AMS Sample Matrix Spike
Uranium 0.0555 mg/L 0.00030
Lab ID: C14040511-001AMSD Sample Matrix Spike Duplicate
Uranium 0.0564 mg/L 0.00030
Method: E200.8
Lab ID: ICV Initial Calibration Verification Standard
Uranium 0.0500 mg/L 0.00030
Method: E200.8
Lab ID: MB-41163 Method Blank
Uranium NO mg/L 0.0003
Lab ID: LCS2-41163 Laboratory Control Sample
Uranium 0.100 mg/L 0.00030
Lab ID: C14040560-007AMS Sample Matrix Spike
Uranium 0.242 mg/L 0.00030
Lab ID: C14040560-007AMSD Sample Matrix Spike Duplicate
Uranium 0.242 mg/L 0.00030
Qualifiers:
Report Date: 04/29/14
Work Order: C14040518
%REC Low Limit High Limit RPD RPDLimit Qual
Analytical Run: ICPMS2-C_140417A
04/17/1412:35
101 90 110
Batch: R185609
Run: ICPMS2-C_140417A 04/17/1413:10
Run: ICPMS2-C_140417A 04/17/14 13:14
100 85 115
Run: ICPMS2-C 140417A 04/17/14 20:29 -
107 70 130
Run: ICPMS2-C_140417A 04/17/14 20:32
109 70 130 1.7 20
Analytical Run: ICPMS2-C_140421A
04/21 /1416:20
100 90 110
Batch: 41163
Run: ICPMS2-C_140421A 04/22/14 20:57
Run: ICPMS2-C_140421 A 04/22114 21 :00
100 85 115
Run: ICPMS2-C_140421A 04/22/14 21 :58
97 70 130
Run: ICPMS2-C_140421A 04/22/14 22:01
97 70 130 0.1 20
RL -Analyte reporting limit. NO-Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 6 of 12
EI\ERGY
I .'\UOC.-/d•J!.tll:.:;
www.energylab.com
Aa/fflal ~ S111a 1SSZ
Helena, MT 877-472-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-0515
Gillette, WY 81&-18&-7175 • Rapid Ctty, SD 888-&72-1225 • College Station, 1X 888-&90-2218
QAJQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Analyte
Method: E900.0
Lab ID: Th230-GrAB-1724
Gross Alpha
Lab ID: MB-GrAB-1724
Gross Alpha
Gross Alpha precision (±)
Gross Alpha MDC
Lab ID: C 14040086-003ADU P
Gross Alpha
Gross Alpha precision (±)
Gross Alpha MDC
Lab ID: C14040415-001 FMS
Gross Alpha
Lab ID: C14040415-001 FMSD
Gross Alpha
Count Result Units
3
3
Laboratory Control Sample
135 pCi/L
Method Blank
3 pCi!L
0.8 pCi/L
1.0 pCi/L
Sample Duplicate
645
27.4
11.3
pCi!L
pCi!L
pCi!L
Sample Matrix Spike
356 pCi/L
Sample Matrix Spike Duplicate
292 pCi!L
Report Date: 04/29/14
Work Order: C14040518
RL %REC Low Limit High Limit
Run: TENNELEC-3_140422A
115 80 120
Run: TENNELEC-3_140422A
Run: TENNELEC-3_140422A
Run: TENNELEC-3_140422A
84 70 130
Run: TENNELEC-3_140422A
32 70 130
RPD RPDLimit Qual
2.8
20
Batch: GrAB-1724R
04/25/14 17:27
04/25/14 17:27
04/25/14 17:28
18.5
04/25/14 17:27
04/25/14 17:27
20 s
· Sample activity for this radionuclide is much larger than the spike activity added. Therefore the matrix spike recovery could not be calculated. The LCS and the RPD of the
MS/MSD pair are acceptable; this batch is approved.
Qualifiers:
RL-Analyte reporting limit. NO -Not detected at the reporting limit.
MDC -Minimum detectable concentration S -Spike recovery outside of advisory limits.
Page 7 of 12
EN:RGY
~ 1\. ~ l) f </I. t ·...:.11111 ~.
www.energylab.com
AlalftJAI fl&:llllla .. 11ft
Helena, MT 877-472-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-0515
Gillette, WY 86&-186-7175 • Rapid City, SD 888-672-1225 • College Station, TX 888-&90-2218
QAIQC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Analyte Count Result Units
Method:
Lab 10:
Radium 226
E903.0
C14040518-001 OMS
LabiD: C14040518-001DMSD
Radium 226
Lab ID: LCS-41163
Radium 226
Lab ID: MB-41163
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Method: E903.0
Lab ID: C14040519·001DMS
Radium 226
Lab ID: C14040519-001DMSD
Radium 226
Lab ID: LCS-RA226·7150
Radium 226
Sample Matrix Spike
18 pCi/L
Sample Matrix Spike Duplicate
17 pCi/L
Laboratory Control Sample
22.6 pCi/L
3 Method Blank
·0.02 pCi/L
0.1
0.3
pCi/L
pCi/L
Sample Matrix Spike
19 pCi/L
Sample Matrix Spike Duplicate
20 pCi!L
Laboratory Control Sample
7.8 pCi!L
Report Date: 04/29/14
Work Order: C14040518
RL %REC Low Limit High Limit RPD RPDLimit
Run: BERTHOLD 770-2_140422A
110 70 130
Run: BERTHOLD 770-2_140422A
104 70 130 5.8
Run: BERTHOLD 770-2_140422A
105 80 120
Run: BERTHOLD 770·2__140422A
Run: G542M_140417A
84 70 130
Run: G542M_140417A
88 70 130 4.3
Run: G542M_140417A
69 80 120
Batch:41163
04/28/14 07:48
04/28/14 07:48
18.8
04/28/14 11 :15
04/28/14 11 :15
u
Batch: RA226-7150
04/23/14 06:32
04/23/14 06:32
21.6
04/23/14 06:32
s
· LCS response is outside of the acceptance range for this analysis. Since the MB, MS, and MSD are acceptable the batch is approved.
Lab ID: MB-RA226-7150 3 Method Blank
Radium 226 0.04 pCi/L
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
0.1
0.2
U -Not detected at minimum detectable concentration
pCi/L
pCi/L
Run : G542M_140417A
ND-Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
04/23/14 06:32
u
Page 8 of 12
EN:RGY
l t\·.~or. YIOr .. JL _;
www.energylab.com
Aal1tJa/ E.rallll.w Sllu IIJZ
Helena, MT 877-472-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-1515
Gillette, WY 86&-186-7175 • Rapid City, SO 888-672-1225 • College Station, TX 888-690-221 B
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Analyte Count Result Units
Method: E908.0
Lab ID: LC5-RA-TH-150-2032
Thorium 230
Lab ID: C14040518-001 CM5
Thorium 230
LabiD: C14040518-001CM5D
Thorium 230
LabiD: M B-RA· TH-150-2032
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Method: E908.0
Lab ID: C14040518-001 OMS
Thorium 230
Lab ID: C14040518-001 DMSD
Thorium 230
LabiD: LC5-41163
Thorium 230
Lab ID: MB-41163
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Qualifiers:
RL -Analyte reporting limit.
3
3
MDC - Minimum detectable concentration
Laboratory Control Sample
6.5 pCi/L
Sample Matrix Spike
13 pCi/L
Sample Matrix Spike Duplicate
13 pCi/L
Method Blank
0.05 pCi/L
0.08 pCi/L
0.2 pCi/L
Sample Matrix Spike
19 pCi/L
Sample Matrix Spike Duplicate
17 pCi/L
Laboratory Control Sample
16.4 pCi/L
Method Blank
0.2 pCi/L
0.1 pCi/L
0.2 pCi/L
Report Date: 04/29/14
Work Order: C14040518
RL %REC Low Limit High Limit RPD RPDLimit Qual
Batch: RA-TH-IS0-2032
Run: ALPHANAL YST_140421 B
98 80 120
Run:ALPHANALYST_140421B
102 70 130
Run:ALPHANALYST_140421B
103 70 130 0.3
Run:ALPHANALYST_140421B
Run:ALPHANALYST_140423A
109 70 130
Run: ALPHANAL YST _140423A
98 70 130 11
Run:ALPHANALYST_140423A
94 80 120
Run:ALPHANALYST_140423A
NO -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
04/23/14 09:01
04/23/14 09:01
04/23/14 09:01
44.3
04/23/14 09:01
u
Batch:41163
04/25/14 08:52
04/25/14 08:52
29.9
04/25/14 08:52
04/25/14 08:52
Page 9 of 12
EN:RGY
I ...,,,<.>ri"•IOI~r~:_.
www.energylab.com
AM/ftlal E.allllaSW. IIU
Helena, MT 817--472-0711 • Billings, MT 801-735-4489 • Casper, WY 888-235-1515
Gillette, WY 116-186-7175 • Rapid City, SD 188-&72-1225 • College Station,TX 888-&90-2218
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Surface Water 2014
Ana lyle Count Result Units
Method: SW6020
Lab ID: C 14040560-002ADI L Serial Dilution
Uranium 3.28E-08 mg/L
Lab ID: C 14040560-007 AM S Sample Matrix Spike
Uranium 0.242 mg/L
Lab 10: C14040560-007 AMSD Sample Matrix Spike Duplicate
Uranium 0.242 mg/L
Lab ID: MB-41163 Method Blank
Uranium 4E-05 mg/L
Lab ID: LCS2-41163 Laboratory Control Sample
Uranium 0.100 mg/L
Qualifiers:
RL-Analyte reporting limit.
MDC -Minimum detectable concentration
Report Date: 04/29/14
Work Order: C14040518
RL ·%REC Low Limit High Limit RPD RPDLimit Qual
Batch: 41163
Run: ICPMS2-C_140421A 04/22/14 21 :29
1.5E-10 5.3 20
Run : ICPMS2-C_140421A 04/22/14 21 :58
4.3E-05 97 75 125
Run: ICPMS2-C_140421A 04/22/14 22:01
4.3E-05 97 75 125 0.1 20
Run: ICPMS2-C 140421A 04/22/14 20:57 -
4E-05
Run: ICPMS2-C_140421 A 04/22/14 21 :00
4.3E-05 100 85 115
ND -Not detected at the reporting limit.
Page 10 of 12
EI'.ERGY
I '• ·• C .I~ t'> I . • ~I _.
www.energylab.com
Mtt/ft/al~~ IISZ
Helena, MT 871-412-0111 • Billings, MT 800-735-4489 • Caspel', WY 888-235-1515
Gillette, WY 88&-686-7175 • Rapid City, SD 888-&72-1225 • College Station, TX 888-690-2218
Workorder Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Debra Williams
Reviewed by: BL2000\khelm
Reviewed Date: 4/17/2014
Shipping container/cooler in good condition?
Custody seals intact on all shipping container(s)/cooler(s)?
Custody seals intact on all 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 Cl, Sulfite, Ferrous Iron, etc.)
Temp Blank received in all shipping container(s)/cooler(s)?
Container/Temp Blank temperature:
Water -VOA vials have zero headspace?
Water-pH acceptable upon receipt?
Yes 0
Yes 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
2.0"C On Ice
Yes D
Yes 0
C14040518
Date Received: 4/16/2014
Received by: dw
Carrier NDA
name:
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
NoD
No 0
NoD
NoD
Not Present D
Not Present D
Not Present 0
Not Applicable D
No VOA vials submitted 0
Not Applicable D
-----------------------------------------------------------------------------·----,-
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.
Contact and Corrective Action Comments:
Sample will be filtered and preserved as necessary.
Page 11 of 12
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: ..;;;E;;;,;n~e~rg~y..:;;La;.;;,b;;;,.;o;.;.r.;;;.at;;.;;.o~rle~s;...__ ______ Contact: Garrin Palmer
2393 Salt Creek Hwy Ph: 435 678 4115
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
ProJect Samplers Name Samplers Signature
2nd Quarter Surface I &~P~ Water 2014 Garrin Palmer
Time
SampleiD Date Collected Collected Laboratory An~is Rf!_q_uested
CottonWood Creek 4/14/2014 1315 TDS
TSS
Dissolved Gross Alpha
Su~ended U-nat
Dissolved U-nat
Su~ended Ra-226
Dissolved Ra-226
Su~ended Th-230
Dissolved Th.:230
Comments:
Relinquished By:{Signature). Daterrime Received By:(Signature)
Garrln Palmer C-;s-~ 4/14/2014
1200
Date/Time
Relinquished By:(Signature)
C { Lf0Lf(J5! Zf
ATTACHMENT I
SOIL SAMPLE GRAPHS, DATA TABLE, LABORATORY RESULTS AND QAIQC
*Soil samples are collected during the third quarter. This attachment has been deliberately left
blank.