DRC-2020-004161 - 0901a06880c018cf

ENERGYFUELS
February 25, 2020
VIA OVERNIGHT DELIVERY
Mr. Ty L. Howard
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84116
Re: State of Utah Radioactive Material License No. UT1900479
White Mesa Mill, Blanding, Utah
Semi-Annual Effluent Monitoring Report for Period
July 1 through December 31, 2019
Mr. Howard:
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.
UT1900479, enclosed is the Semi-Annual Effluent Monitoring Report for the White Mesa Mill
for the period July 1 through December 31, 2019.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
Yours very truly,
ttttyku4
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David Frydenlund
Terry Slade
Scott Bakken
Logan Shumway
Paul Goranson
Div of
and Radiation Control
FEB 2 7 2020
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140 D 13C- 20 ZO 11-1 www.enemvfuels.com
February 25, 2020
VIA OVERNIGHT DELIVERY
Mr. Ty L. Howard
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84116
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 Effluent Monitoring Report for Period
July 1 through December 31, 2019
Mr. Howard:
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.
UT1900479, enclosed is the Semi-Annual Effluent Monitoring Report for the White Mesa Mill
for the period July 1 through December 31, 2019.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
Yours very truly,
t~Y~
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David Frydenlmid
Terry Slade
Scott Bakken
Logan Shumway
Paul Goranson
White Mesa Uranium Mill
Radioactive Materials License UT900479
Semi-Annual Effluent Monitoring Report
(July through December 2019)
Prepared For:
Utah Department of Environmental Quality
Division of Waste Management and Radiation Control
Prepared by:
Energy Fuels Resources (USA) Inc.
225 Union Boulevard, Suite 600
Lakewood, CO 80228
February 25, 2020
TABLE OF CONTENTS
1.0 INTRODUCTION .................................................................................................. 1
1.1 Modificatio.ns to the Monitoring Programs ............................................................... 1
2.0 ENVIRONMENTAL AIR PARTICULATE SAMPLING ..................................... 2
2.1 Program Overview ............................................................................................... 2
2.2 Sampling Protocol and Analytical Results ........................................................... 3
2.3 General Observations ........................................................................................... 4
2.4 Site Specific Sampling Data ................................................................................. 5
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 ...................................................................... 9
7.0 SOIL SAMPLING ................................................................................................. 10
8.0 METEOROLOGICAL MONITORING ................................................................ 10
9.0 CELL 2 RADON FLUX ........................................................................................ 11
10.0 SIGNATURE AND CERTIFICATION ................................................................ 12
Table 1
Table 2
Table 3
Table 4
Table 5
Table 6
Table 7
Table 8
Table 9
LIST OF TABLES
NCRP Report 94-Global Pb-210 Concentration Example
Air Monitoring Station Results U-Nat (Comparison to Limits)
Air Monitoring Station Results Th-230 (Comparison to Limits)
Air Monitoring Station Results Ra-226 (Comparison to Limits)
Air Monitoring Station Results Pb-210 (Comparison to Limits)
Air Monitoring Station Results Th-232 (Comparison to Limits)
Environmental OSL Dosimeter Measurements (Gamma)
Stack Effluent Concentrations and Release Rates
Vanadium Stack Effluent Concentrations and Release Rates
INDEX OF TABS
A High Volume Air Monitoring Stations
B BHV Air Sampling Graphs and Data Tables
Tabl 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
Tab 7 BHV-7 Air Sampling Graphs and Data Table
Tab 8 BHV -8 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
J Radon Monitoring Graphs and Data
K Cell 2 Radon Flux Data
ii
WHITE MESA URANIUM MILL
SEMI-ANNUAL EFFLUENT REPORT, JULY THROUGH DECEMBER 2019
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 construction, 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).
1.1 Modifications to the Monitoring Programs
As stated above, the monitoring programs implemented to date are consistent with the
Mill's License and guidelines developed by the NRC and described in Regulatory Guide
4.14. The Mill's License modifies and expands the effluent monitoring programs
implemented at the Mill beyond what is regularly required by NRC Regulatory Guide
4.14. Specific changes to the individual monitoring programs are discussed in the
subsequent sections of this report.
In a letter dated July 23, 2014, DWMRC stated that because "Tailings Cell 2 is no longer
in operation (receiving tailings), the Division of Air Quality and the Division of
Radiation Control agree that Subpart W NESHAPs requirements (40 CFR Part 61) no
longer apply; however, at this phase of cell 2 closure activities, the requirements of 10
CFR Part 40, Appendix A, Criterion 6 do apply." The July 23, 2014 letter further
requires that radon flux measurements for Cell 2 be collected semi-annually in
accordance with methodology specified in 40 CFR Part 61, Appendix B, Method 115 and
that the measured results be included in the Semi-Annual Effluent Reports submitted to
DWMRC. As a result of the July 23, 2014 letter, Cell 2 radon flux monitoring data are
reported herein. Additional details regarding the monitoring and data collection activities
for the Cell 2 radon flux are included in Section 9.0.
As specified by the License and the documents described above, 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, BHV-2, and BHV-8
(north), BHV-5 and BHV-7 (east), and BHV-4 (south). BHV-1 and BHV-
8 serve as surrogates for the nearest resident (BHV-1 and BHV -8 are
1
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 (BHV-6);
b) External ( direct) gamma radiation measured at air monitoring stations BHV-1,
BHV-2, BHV-3, BHV-4, BHV-5, BHV-6, BHV-7, and BHV-8;
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 during the third quarter of each year;
g) Radon-222 at the air particulate monitoring stations (BHV-1 through BHV-8);
h) Meteorological conditions;
i) Radon flux of the Cell 2 cover as specified by the DWMRC in correspondence
dated July 23, 2014;
j) Groundwater (up and down gradient) of the Mill facility; and 1
k) 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
Prior to 2014, the environmental airborne particulate monitoring program at the Mill
utilized four air sampling stations. Four high-volume continuous air sampling stations
(BHV-1, BHV-2, BHV-4, and BHV-5) were required by the License. In addition to these
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.
2
four environmental air sampling locations, 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.
As stated in Section 1.1 above, the air pruticulate monitoring program has expanded to
include the following:
• The addition of two air monitoring stations (BHV-7 and BHV-8);
• The addition of thorium-232 ("Th-232") to the list of air particulate analytes;
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
and BHV-8 also serve as conservative surrogates for concentrations at the nearest
resident, because they are 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 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. The NRC approval to remove BHV-3
from the active air monitoring program specified background radionuclide concentrations
based on the historic data. These concentrations are shown on the graphs and tables in
Tab B3. While air sampling was discontinued at this location, gamma measurements,
radon measurements and soil sampling continue at BHV-3.
2.2 Sampling Protocol and Analytical Results
Airborne particulate monitors are operated continuously at each of the high-volume air
sampling stations except BHV-3. As noted above, BHV-3 was removed from the active
air monitoring program in November 1995, but the NRC specified background
concentrations are shown in Attachment B.
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, Th-232 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 monitoring stations are depicted on the figure
entitled Particulate 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.
3
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 1-8). 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 or the installation of the locations, whichever is
appropriate. 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.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. The analytical data are usable for their intended purpose.
Any deviations noted did not affect the quality or usability of the data.
For graphical illustration purposes, values reported at zero, values reported at less than
the prescribed detection limit(< 1 x 10-16 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, except as noted below.
It is notewmthy 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
result of the ubiquitous presence of radon in the earth's atmosphere. Accordingly, the
elevated Pb-210 presence in disequilibrium with parent radionuclides 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
4
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
in the Tables Tab of this report, 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 particulate Pb-210 was measured at the Mill site to
be 1.3E-14 uCi/ml (13.0E-3 pCi/m3)2.
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 6 in
the Tables Tab of this report. 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.
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 ten
of the several thousand total gross radionuclide determinations to date exceeded the
Mill's self-imposed 25% ALARA goal).
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
5
2.5 Radon-222
With the approval of the NRC, Radon-222 monitoring at BHV stations at the Mill was
discontinued in 1995 due to the unavailability of monitoring equipment to detect the
revised 10 CFR Part 20 standard. Instead, compliance with these limits and the
requirements of R313-15-301 was demonstrated by a calculation, authorized by the NRC
and as contemplated by R313-15-302(2)(a) which states "A licensee or registrant shall
show compliance with the annual dose limit in Section R313-15-301 by: (a)
Demonstrating by measurement or calculation that the total effective dose equivalent to
the individual likely to receive the highest dose from the licensed or registered operation
does not exceed the annual dose limit;". This calculation is performed by use of the
Mll...DOS code for estimating environmental radiation doses for uranium recovery
operations. R313-15-302(2)(a) contemplates demonstrating compliance either through
modeling or measurement.
In order to determine whether or not detection equipment has improved since 1995, EFRI
voluntarily began ambient Radon-222 monitoring at the BHV stations in 2013. The
Radon-222 data collected from 2013 through present are presented in Attachment J. As
stated in Section 1.1 above, the Mill's effluent monitoring programs were expanded in
2014. The expanded monitoring programs require the collection of Radon-222 data at all
of the BHV stations. For the BHV stations EFRI calculated ECLs using methodology
shown in Attachment J. The calculated ECLs for all of the BHV stations are included on
the data table included in Attachment J. The radon-222 results are below the calculated
ECLs and within the range of historic levels as shown in Attachment J.
Radon-222 monitoring is completed using detectors with an effective reporting limit of
0.06 pCi/L. Field blank detectors are collected quarterly and the results (with
background included) are included in Attachment J.
During the reporting period, one field blank was collected during each quarter. Field
blanks are opened at the beginning of the monitoring period and immediately sealed in
the manufacturer supplied packaging. The field blanks are stored in the environmental
office until the end of the monitoring period, when they are packaged with the field
samples and shipped to the laboratory for processing. While relatively low concentrations
were reported for the field blanks, the field blank data show detections which are greater
than the highest detection reported for any of the samples collected at the high volume
stations. The field blank data have been consistently higher than the samples. Despite
the detections reported for the field blanks, there is no indication that the results reflect
contamination during shipping. If the detections on the field blanks indicated
contamination resulting from shipment, then all of the detectors would be affected in the
same manner and the sample data are below the field blank levels. It appears that the
field blanks have been affected by the storage prior to shipping. EFRI is conducting an
investigation into the possible causes of the anomalous field blank detections.
6
3.0 EXTERNAL RADIATION (DIRECT GAMMA)
Gamma exposure rate estimates were measured for the repmting period utilizing optically
stimulated luminescence dosimeters ("OSLs"). Previously, 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). As
noted in Section 1.1 of this report, the effluent monitoring programs at the Mill were
expanded to include expansion of the gamma exposure monitoring program through the
addition of gamma monitoring at the two new air monitoring stations (BHV-7 and BHV -
8).
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 7 in the Tables Tab of
this repmt. In addition, measurement data obtained at these locations are graphically
presented in Attachment E to this report.
The results for this period indicate that above background measurements for stations
BHV-2, BHV-4, BHV-5, BHV-6, BHV-7, and BHV-8 are within historic levels. The
BHV-1 fourth quarter rnrem data (with background subtracted) is 9.9 rnrem, which is
higher than the majority of the historic levels for that station. BHV-1 and BHV-8 are at
the location of the nearest potential residence. The nearest actual residence is
approximately 0.4 miles north of BHV-1 and BHV-8. The annual limit for an individual
member of the public is 100 mrem/yr for combined internal and external exposure.
The BHV -1 2019 results were consistent for the first through third quarters with an above
background value of approximately 5 mrem per quarter. The fourth quarter result was
higher than the first three quarters of 2019, indicating that the fourth quarter result is
likely anomalous. The fourth quarter result is being considered anomalous because Mill
activity in 2019 was consistent and similar activities were conducted all year. There were
no activities in the fourth quarter that would have contributed to this variance. Further,
by comparison to BHV-8, which is due west of BHV-1 and somewhat closer to the Mill
facility, BHV-8 had reported values of 0.2 mrem above background for the third quarter
and O mrem above background for the fourth quarter. The dose at BHV-8 is significantly
lower (approximately 1 %) of the dose at BHV-1. A review of the air particulate data
indicates that air particulate for the fourth quarter was higher at BHV-8 than at BHV-1,
ruling out air particulate as being the cause of this difference. As noted above, BHV-1 is
located at the nearest potential resident. Future results will be reviewed and used to
determine if additional activities are necessary. In addition, the OSL results and the
laboratory will be investigated to assure results are representative of actual conditions.
7
4.0 VEGETATION SAMPLES
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. Two samples
were collected during the January through June reporting period. The third sample was
be collected on November 13, 2019. As noted in Section 1.1, Amendment 7 and the
associated RFI expanded the vegetation sampling program through the addition of Th-
232 and U-Nat.
During the January through June reporting period, samples were collected on April 25,
and June 6, 2019. During the July through December reporting period, a sample was
collected on November 13, 2019. The data from the sampling events are included in
Attachment F.
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
2019 data results are within the variation of previous sampling episodes.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. The analytical data are usable for their intended purpose.
Any deviations noted did not affect the quality or usability of the data.
The value in the MDC column in the data package is the sample-specific minimum
detectable concentration ("MDC"). The MDC is based on the sample moisture,
composition and other sample-specific variables. The lower limit of detection which is a
limit representing the detection capability of the measurement system is referred to as the
Reporting limit ("RL") in the data package.
5.0 STACKSAMPLING
Under Section 5.0 of Tab 1.4 of the Mill's EPM gas stack samples are collected at the
Mill in accordance with the schedule shown below:
8
Stack Sampling Requirements
Grizzly North and/or Yellowcake Vanadium South Packaging Vanadium Frequency Baghouse Yellowcake Baghouse Dryer Stack Packaging
Stack Dryer Stacks Stack Stack
Quarterly If operating, If operating, If operating, If operating, If operating,
U-nat, Th-U-nat, Th-U-nat, Th-U-nat, Th-U-nat, Th-
230, Ra-226, 230, Ra-226, 230, Ra-226, 230, Ra-226, 230, Ra-226,
Pb-210, Th-Pb-210, Th-Pb-210, Th-Pb-210, Th-Pb-210, Th-
232, Ra-228, 232, Ra-228, 232, Ra-228, 232, Ra-228, 232, Ra-228,
and Th-228. and Th-228. and Th-228. and Th-228. and Th-228.
The south yellowcake dryer and yellowcake baghouse did not operate during the
reporting period. The north yellowcake dryer has not been in operation since the third
quarter of 2012, and therefore, has not been sampled since it was last in operation.
The vanadium dryer and vanadium baghouse operated during the reporting period.
Vanadium stack samples were collected from the vanadium dryer and packaging
baghouse during third and fourth quarter.
The analytical results of stack sampling conducted in the reporting period, as well as for
the previous two quarters, are provided in Table 9 in the Tables Tab of this report. The
actual analytical results reported by the laboratory for the reporting period (third and
fourth quarters 2019) are provided in Attachment G to this report.
It is also important to note that uranium stack effluent concentrations are not comparable
to environmental air sampling station ECLs 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.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. The analytical data are usable for their intended purpose.
Any deviations noted did not affect the quality or usability of the data.
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
9
surface water was sampled in the first quarter of 2019. The Westwater data are included
in the SAER for January -June 2019, which was submitted on August 21, 2019.
The Mill's EPM 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 and dissolved and
suspended radionuclides during the fourth quarter. No sample was collected during the
third quarter because there was no water present during the quarter.
The field data sheets for the surface water sampling events, along with graphs showing
historic results are included as Attachment H.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. No data issues were noted and the data are usable for the
intended purpose.
7.0 SOIL SAMPLING
As mentioned in Section 1.1 above, specific changes to the individual monitoring
programs have been made.
In accordance with the Mill's EPM, 52 surface soils were collected in August 2019. The
soil samples were analyzed, on a dry basis, for Ra-226, U-nat, Pb-210, and Th-232. The
results of these samplings indicate that soil activity levels at the air monitoring stations
remain low and within the range of historic levels. A graphical presentation of the soil
results, together with analytical sample results for the August 2019 sampling event are
provided in Attachment I.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. The analytical data are usable for their intended purpose.
Any deviations noted did not affect the quality or usability of the data.
Field duplicate sample results were assessed as required by the SOP. Duplicate results
were within the acceptance limits specified in the SOP except as noted in Table 1-3.
Field duplicate results are shown in Attachment I.
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 reporting period. This
information is retained at the Mill site for agency review.
10
9.0 CELL 2 RADON FLUX
The July 23, 2014 letter, DWMRC stated that because "Tailings Cell 2 is no longer in
operation (receiving tailings), the Division of Air Quality and the Division of Radiation
Control agree that Subpart W NESHAPs requirements (40 CFR Part 61) no longer apply;
however, at this phase of cell 2 closure activities, the requirements of 10 CFR Part 40,
Appendix A, Criterion 6 do apply."
Further, the DWMRC July 23, 2014 letter states that "since the MILDOS-Area Models
that have been run to show compliance with dose limits for releases from the Mill were
based on a limit of 20 picocuries per square meter second (pCi/m2-sec ), in order to ensure
compliance with previously analyzed conditions, the DWMRC will require the licensee
to continue to measure the radon flux in accordance with [the latest revision of] 40 CFR
61, Appendix B, Method 115, "Monitoring for Radon-222 Emissions". The measured
radon flux for Cell 2 shall not exceed a value of 20 (pCi/m2-sec) until a new MILDOS-
Area Model to analyze a higher radon flux is completed and demonstrates compliance
with dose limits based on the releases from the Mill. As required by Method 115, a
minimum of 100 measurements are required and shall be performed on a semi-annual
basis."
Per the requirements detailed above, EFRI sampled Cell 2 radon flux in April 2019 for
the January through June 2019 reporting period and in October for the July through
December reporting period. The April 2019 measurement was 0.4 pCi/(m2-sec). The
October 2019 measurement was 2.3 pCi/(m2-sec). Both of the 2019 measurements were
below the 20.0 pCi/(m2-sec) standard. The full data report for the October 2019 Cell 2
radon flux sampling is provided in Attachment K. The full data report for the April 2019
Cell 2 radon flux sampling is provided in Attachment K of the January through June
SAER which was submitted on August 21, 2019.
The 2019 average radon flux is 1.35 pCi/(m2-sec) which is the arithmetic average of the
April 2019 measurement of 0.4 pCi/(m2-sec) and the October measurement of 2.3
pCi/(m2-sec). The arithmetic average is below the 20.0 pCi/(m2-sec) standard.
It is important to note that Cell 2 Phase 1 cover placement/construction commenced in
April 2016 and was completed in April 2017. The Phase 1 cover activities include the
placement and compaction of approximately 4.5 feet of soil materials.
11
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc.
Energy Fuels Resources (USA) Inc.
By:
Scott A. Bakken Date
Senior Director Regulatory Affairs
12
Certification:
I certify, under penalty of law, that this document and all attachments were
prepared under my direction or supervision in accordance with a system designed to
assure that qualified personnel properly gather and evaluate the information submitted.
Based on my inquiry of the person or persons who manage the system, or those persons
directly responsible for gathering the information, the information submitted is, to the
best of my knowledge and belief, true, accurate, and complete. I am aware that there are
significant penalties for submitting false information, including the possibility of fine and
imprisonment for knowing violations.
Scott A. Bakken
Senior Director Regulatory Affairs
Energy Fuels Resources (USA) Inc.
13
TABLES
Table 1-NCRP Report 94-Global Pb-210 Concentration Example
State Pb-210 Concentration
I
uBq/M3 uCi/mJ
California 600 1.60E-14
Illinois 1500 4.lOE-14
Ohio 300 8.lOE-15
Massachusetts 700 1.90E-14
111
Table 2 -Air Monitoring Station Results U-Nat (Comparison to Limits)
3rd and 4th Quarter 2019
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration PercentECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 1.00E-16 4.00E-17 9.00E-14 7.78E-02
BHV2 2.00E-16 2.00E-17 9.00E-14 1.22E-Ol
BHV4 1.00E-16 4.00E-17 9.00E-14 7.78E-02
BHV5 1.00E-16 4.00E-16 9.00E-14 2.78E-01
BHV6 7.00E-17 2.00E-16 9.00E-14 1.SOE-01
BHV7 2.00E-16 1.00E-16 9.00E-14 1.67E-01
BHVS 1.00E-16 4.00E-17 9.00E-14 7.78E-02
Table 3 -Air Monitoring Station Results Th-230 (Comparison to Limits)
3rd and 4th Quarter 2019
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 5.00E-16 3.00E-17 2.00E-14 1.33E+OO
BHV2 3.00E-17 l.OOE-17 2.00E-14 1.00E-01
BHV4 1.00E-16 6.00E-17 2.00E-14 4.00E-01
BHV5 1.00E-16 3.00E-16 2.00E-14 l .OOE+OO
BHV6 8.00E-17 1.00E-16 2.00E-14 4.SOE-01
BHV7 1.00E-16 5.00E-17 2.00E-14 3.75E-01
BHVS 2.00E-16 4.00E-17 2.00E-14 6.00E-01
Table 4 -Air Monitoring Station Results Ra-226 (Comparison to Limits)
3rd and 4th Quarter 2019
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration PercentECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml) I
BHVl 8.00E-16 6.00E-17 9.00E-13 4.78E-02
BHV2 3.00E-16 4.00E-17 9.00E-13 1.89E-02
BHV4 9.00E-17 4.00E-17 9.00E-13 7.22E-03
BHV5 6.00E-16 4.00E-16 9.00E-13 5.56E-02
BHV6 5.00E-17 1.00E-16 9.00E-13 8.33E-03
BHV7 3.00E-16 l.OOE-16 9.00E-13 2.22E-02
BHVS 1.lOE-15 l.OOE-16 9.00E-13 6.67E-02
Table 5 -Air Monitoring Station Results Pb-210 (Comparison to Limits)
3rd and 4th Quarter 2019
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration PercentECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCl/ml)
BHVl 1.00E-14 1.00E-14 6.00E-13 l.67E+OO
BHV2 9.00E-15 8.00E-15 6.00E-13 1.42E+OO
BHV4 l .OOE-14 9.00E-15 6.00E-13 l .58E+OO
BHV5 9.00E-15 9.00E-15 6.00E-13 1.50E+OO
BHV6 8.00E-15 1.00E-14 6.00E-13 1.50E+OO
BHV7 1.00E-14 1.00E-14 6.00E-13 1.67E+OO
BHV8 1.00E-14 7.00E-15 6.00E-13 1.42E+OO
Table 6 -Air Monitoring Station Results Th-232 (Comparison to Limits)
3rd and 4th Quarter 2019
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCl/ml)
BHVl 7.00E-18 3.00E-18 4.00E-15 l.25E-01
BHV2 9.00E-18 5.00E-18 4.00E-15 l.75E-01
BHV4 3.00E-18 3.00E-18 4.00E-15 7.50E-02
BHV5 6.00E-18 7.00E-18 4.00E-15 1.63E-01
BHV6 4.00E-18 4.00E-18 4.00E-15 l.OOE-01
BHV7 7.00E-18 2.00E-18 4.00E-15 1.13E-01
BHV8 9.00E-18 2.00E-18 4.00E-15 1.38E-01
Table 7 -Environmental Optically Stimulated Luminescence Dosimeter
2019
Jl'd & ]rd Quarter 4th fJua1~ter CmMu[atl~.e
Q't:1.'a1F,te.1• Glffl\l"ter Result Les, B.esuitit Le-. SeminMn'fd ,
¥tmi1l~l'lihg , r.&e 'LJllt R.es»O Dta:0Itg (UliJiJ (ij Ba~.9,on:_cl 'ffl •,ttm-ate
Sitiaffi.Gn: ~lilll~~J ,,(lilD'QJJlf 1G,,ru1emD I (mruern} ~A1~$1}1J),
BHVl 39 45.3 5.1 9.9 15
BHV2 36.5 37.9 2.6 2.5 5.1
BHV3 33.9 35.4 0 0 0
BHV4 32.5 34.2 0 0 0
BHV5 37.6 36.9 3.7 1.5 5.2
BHV6 35 37.1 1.1 1.7 2.8
BHV7 35 36.3 1.1 0.9 . 2
BHV8 34.1 34.1 0.2 0 0.2
Table 8 Uranium Stack Effluent Concentrations and Release Rates
IstQtr.WI9
No stack sampling was conducted as the dryers did not run. No packaging was completed during the I st quarter.
2od·Qtr. 2012
No stack sampling was co~ucted as the dryers did not run. No packaging was completed during the 2nd quaner.
lrd Qtr. 20]j ---· -------
No stack sampling was conducted as the dryers did not run. No packaging was completed during the 1st quarter.
4th Qtr.'2019•
No stack sampling was conducted as the dryers did not run. No packaging was completed during the 2nd quarter.
Table 9 Vandium Stack Effluent Concentrations and Release Rates
1st Qtr. 2019
U-Nat U-Nat. Th-228 Th-228 uCi/sec Th-230 Th-230 uCi/sec Th-232 Th-232 Pb-210 Pb-210 Ra-226 Ra-226 Ra-228 Ra-228
uCi/cc uCi/sec uCi/cc uCi/cc uCi/cc uCi/sec .uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
Vanadium
Dryer I l.09E-l2 3.67E-06 O.OOE+OO O.OOE+OO 2.65E-l4 8.94E-08 0.00E+OO O.OOE+OO 1.07E-12 3.62E-06 I.3LE-I2 4.42E-06 2.79E-13 9.41E-07
Vanadium
Dryer 2 9.86E-13 3.69E-06 3.37E-15 l.26E-08 3.74E-14 I .40E-07 3.37E-15 l.26E-08 2.62E-l2 9.81E-06 3.37E-13 J .'J6E-06 7.49E-l4 2.80E-07
Vanadium
Packaging
Baghouse I l.57E-l 2 3.94E-06 3.81E-15 9.55E-09 2.18E-13 5.46E-07 3.81E-15 9.55E-09 l.63E-l 2 4.09E-06 2.99E-13 7.50E-07 2.72E-13 6.82E-07
Vanadium
Packaging
Baghouse 2 1.46E-12 3.72E-06 7.87E-15 2.00E-08 3.87E-13 9.84E-07 7.87E-15 2.00E-08 2.54E-12 6.45E-06 4.67E-13 1.19E-06 2.27E-13 5.77E-07
2nd Qtr. 2019
U-Nat U-Nat. Th-228 Th-228 uCi/sec Th-230 Th-230 uCi/sec Th-232 Th-232 Pb-210 Pb-210 Ra-226 Ra-226 Ra-228 Ra-228
uCi/cc uCi/sec uCi/cc uCi/cc uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
Vanadium
Dryer I 3.54E-12 l .06E-05 2.19E-15 6.57E-09 l.25E-14 3.75E-08 2.19E-15 6.57E-09 1.53E-12 4.60E-06 2.81E-14 8.45E-08 I.56E-13 4.69E-07
Vanadium
Dryer 2 5.26E-12 l .55E-05 5.40E-16 1.59E-09 6.36E-15 l.88E-08 5.40E-16 l .59E-09 l.57E-l2 4.64E-06 4.77E-14 1.41 E-07 l.59E-13 4.69E-07
Vanadium
Dryer 3 7.43E-12 2.13E-05 6.79E-15 l.94E-08 l.98E-14 5.66E-08 6.79E-15 1.94E-08 9.43E-12 2.70E-05 3.77E-13 l.08E-06 9.43E-l 3 2.70E-06
Vanadium
Packaging
Baghouse I 3.39E-13 4.58E-07 6.34E-!6 8.55E-JO 6.48E-14 8.75E-08 6.34E-16 8.55E-IO 2.06E-12 2.79E-06 4.42E-14 5.97E-08 l.47E-13 l.99E-07
vanaaium
Packaging
Baghouse 2 4.78E-13 6.41E-07 l.59E-l 5 2.!4E-09 4.05E-l4 5.43E-08 l.59E-15 2. !4E-09 2.58E-l2 3.45E-06 4.91E-14 6.58E-08 J.23E-l 3 I.64E-07
3rd Q.tt. 2019
U-Nat U-Nat. Th-228 Th-228 uCi/scc Th-230 Th-230 uCi/sec Th-232 Th-232 Pb-210 Pb-210 Ra-226 Ra-226 Ra-228 Ra-228
uCi/cc uCi/sec uCi/cc uCi/cc uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
Vanadium
Dryer I 8.54E-l4 3.00E-07 O.OOE+OO O.OOE+OO 5.34E-l4 l .88E-07 0.00E+OO O.OOE+OO 3.47E-l l 1.22E-04 5.34E-14 l.88E-07 l.33E-13 4.69E-07
Vanadium
Dryer 2 l.97E-13 6.93E-07 O.OOE+OO O.OOE+OO 6.72E-14 2.36E-07 O.OOE+OO O.OOE+OO 5.SIE-12 1.93E-05 5.37E-14 l .89E-07 I.34E-l3 4.72E-07
Vanadium
Packaging
Baghouse I l.OOE-12 l .20E-06 4.95E-14 5.91E-08 6.76E-12 8.07E-06 3.30E-14 3.94E-08 3.30E-12 3.94E-06 4.95E-14 5.91E-08 l.65E-l 3 l.97E-07
vanaarum
Packaging
Baghouse 2 l.26E-12 l.59E-06 7.75E-14 9.84E-08 8.53E-12 l.OSE-05 3.IOE-14 3.94E-08 1.46E-12 1.85E-06 1.09E-13 I.38E-07 1.SSE-13 l.97E-07
4th Qtr. 2019
U-Nat U-Nat. Th-228 Th-228 uCi/sec Th-230 Th-230 uCi/sec Th-232 Th-232 Pb-210 Pb-210 Ra-226 Ra-226 Ra-228 Ra-228
uCi/cc uCi/sec uCi/cc uCi/cc uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
Vanadium
Dryer I 2.92E-13 9.29E-07 O.OOE+OO O.OOE+OO 6.00E-14 l.91E-07 O.OOE+OO O.OOE+OO l.l SE-12 3.76E-06 3.00E-14 9.53E-08 l.50E-13 4.76E-07
Vanadium
Dryer 2 4.20E-12 l.36E-05 4.47E-14 1.45E-07 2.39E-l3 7.72E-07 O.OOE+OO O.OOE+OO 1.79E-I2 5.79E-06 2.98E-14 9.66E-08 1.49E-13 4.83E-07
Vanadwm
Packaging
Baghouse I l.18E-12 J.79E-06 2.66E-14 4.03E-08 3.29E-12 4.98E-06 6.26E-15 9.49E-09 6.42E-12 9.73E-06 1.41E-13 2.14E-07 9.40E-14 1.42E-07
vanac11um
Packaging
Baghouse 2 l.39E-12 2.06E-06 6.42E-15 9.51 E-09 2.41E-12 3.57E-06 I .28E-14 1.90E-08 4.49E-l 2 6.66E-06 8.02E-14 l.19E-07 l.60E-13 2.38E-07
ATTACHMENT A
HIGH VOLUME AIR MONITORING STATIONS
,-..
'
" I
' ~ , •• BHV-3 " , .,. ... ..,._
""137S --
\
' ',
\
\ '-
)
\
Legend
w lU ~ N
/N (N I 0::: 0::: '
'' I I .. ( I I
I J I
/' ~ ( . ' }' (
/ '
+ Air Monitoring Station CJ Township and Range
U ll Property Boundary c=J Section
D Tailings Cell I Pond
--Road
·--·--·-Canyon Rim
Drainage
Coordinate System: NAO
1983 StatePlane Utah
South FIPS 4303 Feet
' \
\
~~RGYFUELS
REVISIONS Project: WHITE MESA MILL
Date: By: County: San Juan State; Utah
Location: -
ATTACHMENT A
PARTICULATE MONITORING STATIONS
Author: rellis Date 2/20/2017 Drafted By: rellis
ATTACHMENT B
BHV AIR SAMPLING GRAPHS AND DATA TABLES
TAB 1
BHV-1 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent SE-14 uCi/inl BHV-lU Effluent 2E-14 uCi/ml BHV-1T230 Effluent 9E-13 uCi/ml BHV-lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-15 uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration Concentration
Umit= Limit= Umit= Limit= ,Limit=
ALARAGoal= 2.ZSE-14 ucilml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC Not Applicable
Umit= limit= Limit= limit= limit=
Pre 1994 1.25E-12 uCl/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAl= ALARAGOAL=
Cone EFC .EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 2.35E-15 5.00E-12 -t.25E-12 7.82E-16 8.00E-14 2.00E-14 l.06E-15 2.00E-12 5.00E-13 2.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Am;,_licable
12/14/1981 l.56E-15 5.00E-12 1.25E-12 1.49E-15 8.00E-14 2.00E-14 1.93E-15 2.00E-12 5.00E-13 2.64E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable . Not Applicable
3/29/1982 2.16E-15 S.OOE-12 1.25E-12 2.93E-15 8.00E-14 2.00E-14 1.16£.15 2.00E-12 5.00E-13 2.09E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 /l.69E-15 5.00E-12 1.25E-12 3.46E-15 8.00E-14 2.00E-14 2.38E-15 2.00E-12 5.00E-13 2.14E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/27/1982 4.45E-15 5.00E-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 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
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 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 7.SlE-16 5.00E-12 1.2SE-12 2.13E-16 8.00E-14 2.00E-14 3.20E-16 '2.00E-12 5.00E-13 1.88E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 2.68E-16 S.OOE-12 l.2SE-12 6.92E-16 8.00E-14 2.00E-14 7.92E-16 2.00E-12 5.00E-13 2.00E-14 4.00E-12 l.OOE-12 r,lot Analyzed Not Applicable Not Applicable
10/3/1983 6.00E-12 , _1.25E-12 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1984 2.87E-15 's.OOE-12 1.25E-12 1.14E-16 8.00E-14 2.00E-14 l.79E-16 2.00E-12 5.00E-13 1.0GE-14 4.00E-12 1.00E-12 ,r,lot Analyzed Not Applicable Not Applicable
4/2/1984 1.59E-15 5.00E-12 l.25E-12 3.40E-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 .5.00E-13 3.34E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 3.lOE-15 5.00E-12 1.25E-12 l.OOE-15 8.00E-14 2.00E-14 2.09E-15 2.00E-12 5.00E-13 1.88E-14 4.00E-12 l.OOE-12 .Not Analyzed Not Applicable Not Applicable
10/1/1984 6.42E-16 S.OOE-12 l.2SE-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 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
1/2/1985 ·s.06E-16 5.00E-12 1.25E-12 4.56E-16 8.00E-14 2.00E-14 3.49E-16 2.00E-12 5.00E-13 3.03E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not AQi:>_licable
4/1/1985 fJ.OOE+OO 5.00E-12 l.25E-12 1.23E-15 8.00E-14 2.00E-14 4.88E-16 2.00E-12 5.00E-13 8.06E·15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/1/1985 7.17E-16 5.00E-12 1.25E-12 8.00E-14 2.00E-14 1.0SE-15 2.00E-12 5.00E-13 2.lSE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 6.13E-16 5.00E-12 l.25E-12 1.lSE-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 3.64E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 3.42E-15 S.OOE-12 l.25E-12 4.74E-16 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 3.98E·15 5.00E-12 l.25E-12 9.74E·16 8.00E-14 2.00E-14 1.SOE-15 2.00E-12 S.OOE-13 1.41E-14 4,00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable -6/30/1986 S.51E·17 -S.OOE-12 l.25E-12 3.52E-16 8.00E-14 2.00E-14 1.37E-15 2.00E-12 6,00E-13 1.23E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 1.99E·15 5.00E-12 1.25E-12 3.06E-16 8.00E-14 2.00E-14 l.25E·15 2.00E-12 5.00E-13 1.08E-14 4.00E-12 1.00E-12 .~ot Analyzed Not Applicable Not Applicable
12/15/1986 1.67E-15 S.OOE-12 1.25E-12 1.16E-16 8.00E-14 2.00E-14 S.98E-16 2.00E-12 6.00E-13 1.37E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 2.33E·15 5.00E-12 1.2SE-12 4.30E-16 8.00E-14 2.00E-14 1.92E-16 2.00E-12 5.00E-13 5.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
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 l.4SE-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable I Not Applicable -9/9/1987 2.27E-15 5.00E-12 1.2SE-12 2.44E-15 8.00E-14 2.00E-14 8,SlE-16 2.00E-12 5.00E-13 3.14E-14 4.00E-12 l.OOE-12 Not Analyzed Not A_Rplicable Not A1mlicable
11/2/1987 PSE-15 5.00E-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 1.07E·15 5.00E-12 ;1..25E-12 l.47E-16 8.00E-14 2.00E-14 4.44E·16 2.00E-12 5.00E-13 4.0lE-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 1.98E-15 5.00E-12 1.25E-12 1.2SE-15 8.00E-14 2.00E-14 6.40E·16 2.00E-12 S.OOE-13 1.07E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable -
8/15/1988 2.06E-15 5.00E-12 l.25E-12 3.41E·15 8.00E-14 2.00E-14 5.0SE-16 2.00E-12 5.00E-13 l.62E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 3.94E·15 S.OOE-12 1.25E-12 2.12E-15 8.00E-14 2.00E-14 l.OlE-15 2.00E-12 5.00E-13 2.47E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Al1Jllicable
2/13/1989 1.99E·15 5.00E-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 1.70E-15 S.OOE-12 1.2SE-12 6.32E·16 8.00E-14 2.00E-14 S.86E-16 2.00E-12 5.00E-13 6.16E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 2.31E-15 5.00E-12 ;1.25E-12 2.31E-16 8.00E-14 2.00E-14 1.77E·16 2.00E-12 S.OOE-13 7.65E·15 4.00E-12 l.OOE-12 Not Analyzed Not ARplicable Not Applicable
11/13/1989 4.72E-15 S.OOE-12 :l.25E-12 l.71E-15 8.00E-14 2.00E-14 l.52E·15 2.00E-12 5.00E-13 1.89E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Ap_111icable
2/12/1990 3.44E-16 S.OOE-12 l .2SE-12 8.39E-16 8.00E-14 2.00E-14 8.31E-16 2.00E-12 5.00E-13 2.57E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 3.03E-15 5.00E-12 1.2SE-12 1.47E-15 8.00E-14 2.00E-14 l.04E-15 2.00E-12 S.OOE-13 1.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.64E·15 S.OOE-12 1.25E-12 1.49E·15 8.00E-14 2.00E-14 3.34E·16 2.00E-12 S.OOE-13 8.27E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 l.48E·15 S.OOE-12 1.25E-12 7.SOE-16 8.00E-14 2.00E-14 S.80E·16 2.00E-12 S.OOE-13 2.16E-14 4.00E-12 l.OOE-12 Not Analyzed ,Not Applicable ' Not Applicable
2/11/1991 l.90E-16 5.00E-12 1.2SE-12 3.48E·17 8.00E-14 2.00E-14 7.91E-17 2.00E-12 5.00E-13 3.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A11plicable '
5/13/1991 3.42E·16 S.OOE-12 1.25E-12 1.34E·15 8.00E-14 2.00E-14 7.39E·16 2.00E-12 5.00E-13 l.46E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 2.77E-16 S.OOE-12 1.25E-12 4.17E-17 B.OOE-14 2.00E-14 1.4SE-16 2.00E-12 S.OOE-13 1.80E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 6.65E-17 S.OOE-12 1.25E-12 9.13E-17 8.00E-14 2.00E-14 2.77E-17 2.00E-12 5.00E-13 1,06E-14 4.00E-12 1.00E-12 Not Anajyzed 'Not Applicable Not Applicable
2/10/1992 1.94E-16 5.00E-12 1.25E-12 4.28E-17 8.00E-14 2.00E-14 4.0SE-17 2.00E-12 5.00E-13 :?..51E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Al1Jllicable
5/11/1992 2.54E·16 S.OOE-12 1.25E-12 6.49E-16 8.00E-14 2.00E-14 6.86E-17 2.00E-12 S.OOE-13 1.38E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 1.73E-16 S.OOE-12 1.25E-12_ l.SSE-16 8.00E-14 2.00E-14 1.20E·16 2.00E-12 5.00E-13 1.53E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 l.56E·16 S.OOE-12 1.25E-12 3.19E-17 8.00E-14 2.00E-14 4.90E·18 2.00E-12 5.00E-13 1.86E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.lOE-16 5.00E-12 1.25E-12 8.00E-14 2.00E-14 3.89E·17 2.00E-12 5.00E-13 2.52E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable lllot Applicable
5/10/1993 l.OOE-16 S.OOE-12 l.25E-12 4.llE-17 8.00E-14 2.00E-14 6.43E-17 2.00E-12 5.00E-13 1.26E-14 4,00E-12 l.OOE-12 Not Anajyzed Not Applicable Not Applicable
Date Effluent 9E·14 uCi/ml BHV-lU Effluent 2E-14 uCi/ml BHV-1T230 l.:ffluent 9E-13 uCi/ml BHV-lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-15 uCi/ml BHV·1T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= :pmit= Limit= Limit=
ALARAGoal = 2.25E-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
----
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml ,pre 1994 M PC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre 1994 l.25E·12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC j:FCA Cone EFC EFCA Cone EFC j;FCA Cone EFC EFCA Cone EFC EFCA
8/10/1993 2.30E-16 5.00E-12 1.25E-12 6.00E-17 8.00E-14 2.00E-14 6.43E-17 2.00E-12 5.00E-13 1.60E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable · ~ot Applicable
11/8/1993 5.00E-12 1.25E-12 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 1.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable !'Jot A_pE!fu:able
2/7/1994 1.82E-16 5.00E-12 ·1.25E-12 5.00E-18 8.00E-14 2.00E-14 4.30E-17 . 2.00E-12 5.00E-13 2.59E-14 4.00E-12 1.00E-12 Not Analyzed "Not Applicable Not Applicable l
5/9/1994 3.60E-16 5.00E-12 1.25E-12 2.70E-16 8.00E-14 2.00E-14 2.87E-16 2.00E-12 5.00E-13 1.60E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable !'Jot Applicable
8/9/1994 4.04E-16 5.00E-12 1.25E-12 2.70E-16 8.00E-14 2.00E-14 2.94E-16 02.00E-12 5.00E-13 2.00E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 9.lSE-17 5.00E-12 1.25E-12 3.60E-16 8.00E-14 2.00E-14 ·2.91E-16 2.00E-12 5.00E-13 2.00E-15 4.00E-12 1.00E-12 Not Anajyzed Not Applicable Not Applicable
2/7/1995 l..77E-16 9.00E-14 2.25E-14. 9.70E-17 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 8.60E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable : Not Applicable
5/9/1995 '9.40E-17 9.00E-14 2.25E-14 5.36E-16 2.00E-14 5.00E-15 1.60E-15 9.00E-13 2.25E-13 3.84E-15 6.00E-13 l.50E-13 Not Anajyzed Not Applicable Not Applicable
8/9/1995 2.70E-16 9.00E-14 2.25E-14 1.60E-16 2.00E-14 5.00E-15 2.76E-16 9.00E-13 2.25E-13 3.76E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable · Not Applicable
11/11/1995 4.80E-15 9.00E-14 2.25E-14 6.41E-16 2.00E-14 5.00E-15 '8.93E-16 9.00E-13 2.25E-13 5.20E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 ~.34E-15 9.00E-14 2.25E-14 2.30E-15 2.00E-14 5,00E-15 1.30E-15 9.00E-13 2.25E-13 4.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5}6/1996 5.llE-16 9.00E-14 2.25E-14 3.06E-16 2.00E-14 5.00E-15 1.40E-16 . 9.00E-13 2.25E-13 7.03E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable !'lot Applicable I
8/5/1996 5.99E-16 9.00E-14 ,2.25E-14 l.55E-15 2.00E-14 5.00E-15 2.03E-16 9.00E-13 2.25E-13 5.94E-15 6.00E-13 l.50E-13 Not Analyzed . 'Not Applicable Not Applicable
11/6/1996 3.38E-16 ~.OOE-14 ;2.25E-14 5.45E-16 2.00E-14 5,00E-15 1.00E-16 9.00E-13 2.25E-13 l.22E-14 6.00E-13 1.50E-13 Not Analyzed -Not Ap_plicable · !'lot Applicable
2/6/1997 1.00E-16 9.00E-14 2.25E-14 1.25E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 2.25E-13 5.68E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 1.09E-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 4.39E-15 6.00E-13 l.50E-13 Not Anajyzed Not Applicable Not Applicable
8/11/1997 2.SSE-16 9.00E-14 2.25E-14 3.83E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 5.29E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable I
1/5/1998 3.24E-16 : 9.00E-14 2.25E-14 3.47E-16 2.00E-14 5.00E-15 1.19E-16 9.00E-13 2.25E-13 4.73E-15 6.00E-13 l.SOE-13 Not Ana!Yzed Not A!!Plicable : Not Ap!)licable
4/28/1998 4.75E-16 9.00E-14 2.25E-14 6.73E-16 2.00E-14 5.00E-15 05.69E-16 9.00E-13 2.25E-13 5.94E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 8.84E-16 : 9.00E-14 2.25E-14_ l.93E-15 2.00E-14 5.00E-15 l.43E-15 9.00E-13 _?.25E-l] 5.22E-15 6.00E-13 l.SOE-13 Not Analyzed ' Not Applicable Not Applicable -
9/28/1998 2.SlE-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.SOE-13 Not Analyzed Not Applicable !'lot Applicable
12/28/1998 8.0SE-16 9.00E-14 2.25E-14 4.93E-16 2.00E-14 5.00E-15 5.0lE-16 9.00E-13 2.25E-13 1.06E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not A11plicable
3/29/1999 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 Not Analyzed Not Applicable , Not Applicable I
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 l.50E-13 Not Analyzed Not A!!Plicable !'lot Applicable
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 Not Analyzed • Not Applicable • Not Applicable
12/28/1999 1.48E-15 9.00E-14 2.25E-14 6.00E-16 2.00E-14 5.00E-15 S.57E-16 9.00E-13 2.25E-13 6.19E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable !'lot Applicable
3/27/2000 i.OOE-16 9.00E-14 2.25E-14 l.06E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.23E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
9/26/2000 2.SlE-16 9.00E-14 2.25E-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 1.50E-13 Not Analyzed · Not Applicable : Not Ap_plicable
12/26/2000 1.00E-16 9.00E-14 2.25E-14 1.42E-16 '2.00E-14 5.00E-15 l.31E-16 9.00E-13 2.25E-13 7.77E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 3.lOE-16 9.00E-14 2.25E-14 l.OOE-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 7.19E-15 6.00E-13 1.50E-13 Not Analyzed · Not Applicable : Not Applicable
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 Not Analyzed Not Applicable Not Applicable'
9/24/2001 1.03E-16 9.00E-14 2.25E-14 1.00E-16 '2.00E-14 5.00E-15 l.OOE-16 . 9,00E-13 2,25E-13 8.09E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable ' J'!ot Applicable
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 l.39E-15 6.00E-13 1.50E-13 Not Analyzed , Not Applicable : Not Applicable
4/1/2002 2.0SE-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 Not Analyzed Not Applicable Not Applicable
7/1/2002 3.SSE-16 '9.00E-14 -2.25E-14 4.85E-16 2.00E-14 5.00E-15 11.06E-16 9.00E-13 2.25E-13 7.65E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 1.17E-16 9.00E-14 2.25E-14 l.61E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.68E-15 6.00E-13 1.50E-13 Not Ana[yzed Not Applicable Not Applicable
12/30/2002 1.00E-16 9.00E-14 • 2.25E-14 1.03E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.46E-15 6.00E-13 l.50E-13 Not Anajyzed Not Applicable Not Ap.Qlicable
3/31/2003 1.20E-16 9.00E-14 2.25E-14 1.12E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 4.68E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2003 2.18E-16 9.00E-14 2.25E-14 3.40E-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 Not Anajyzed Not A11plicable : Not Applicable
9/29/2003 1.00E-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 7.28E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 1.00E-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.SOE-13 Not Analyzed ' Not Applicable ' !'lot Applicable
3/29/2004 1.00E-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 l.54E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 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 3.04E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AJ:1plicable
9/27/2004 1.00E-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 1.05E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable ~ Not Applicable
12/27/2004 1.00E-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 l.59E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 1.00E-16 9.00E-14 I 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.42E-15 6.00E-13 1.50E-13 Not Analyzed Not Applica~le Not Applicable
6/29/2005 1.00E-16 .9.00E-14 . 2.25E-14 l.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 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-lU Effluent 2E-14 uCi/ml BHV-1T230 Effluent 9E-13 uCi/ml BHV-lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-15 uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= limit=
ALARAGoal= Z.ZSE-14 uCi/ml ., ALARA Goal= SE-15 uCi/ml ALARAGoal= Z.ZSE·13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml l'ALARA Goal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC 8E·14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml 1,pre 1994 M PC Not Applicable
Limit= Limit= Limit= Limit= j'umit=
Pre 1994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi{ml Pre 1994 lE-12 uCi/ml I.Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
:(one EFC ~FCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/26/2005 1.00E-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 1.22E-14 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
1/3/2006 2.13E·16 9.00E-14 2.25E-14 1.04E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.73E-14 6.00E-13 l.50E-13 .Not Analyzed Not Applicable Not Applicable
4/3/2006 J..62E-16 -
-9.00E-14 2.25E-14 1.86E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 ~ 2.25E-13 8.36E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap_plicable Not Applicable
7/3/2006 1.86E-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 9.77E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AQQlicable
10/2/2006 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.30E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 1.00E-16 9.00E·14 2.25E-14 1.47E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.17E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 2.23E·16 9.00E-14 2.25E-14I 1.63E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.65E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 3.35E-16 9.00E-14 2.25E-14. 1.34E-16 2.00E-14 5.00E-15 1.36E-16 9.00E-13 2.25E-13 1.78E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2007 1.lSE-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.68E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 i.OOE-16 9.00E-14 2.25E-14 1.93E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2008 1.14E-16 9.00E-14 7.25E-14. 1.13E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap_plicable Not Applicable
6/30/2008 7.09E-16 9.00E-14 2.25E-14l 3.83E-16 2.00E-14 5.00E-15 2.27E-16 9.00E-13 ,Z.25E-13 6.52E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.25E-13 7.64E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.50E-13 Not Anal_yzed Not Ap_plicable Not Applicable
3/15/2009 2.14E-15 9.00E-14 2.25E-14 1.02E-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E·l3 4.44E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 5.97E-17 9.00E-14 ;1.25E-14 2.35E-16 2.00E-14 5.00E-15 2.18E-16 9.00E-13 2.25E-13 5.13E-15 6.00E-13 l.50E-13 Not Analyzed Not ~_plicable Not Applicable
9/15/2009 9.SSE-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not AQplicable
3/31/2010 1.97E-15 9.00E-14 2.25E-14 2.15E-16 2.00E-14 5.00E-15 3.27E-16 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2010 1.58E-15 -9.00E-14 • 2.25E-141 4.71E-16 2.00E-14 S.OOE-15 7.70E-16 9.00E-13 .2.25E-13 4.07E-15 6.00E-13 1.SOE-13 Not Analyzed Not Ap_plicable Not Applicable
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 ,Z.25E-13 6.80E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Ap_plicable
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 l.27E-14 6.00E-13 l.50E-13 .Not Analyzed Not Applicable Not Applicable
4/4/2011 9.0lE-16 9.00E-14 2.25E-141 1.90E-16 2.00E-14 5.00E-15 3.64E-16 9.00E-13 2.25E-13 l.09E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 1.59E-15 9.00E-14 2.25E-14 5.31E-16 2.00E-14 5.00E-15 4.99E-16 1 9.00E-13 2.25E-13 8.38E-15 6.00E-13 l.50E-13 Not Analyzed Not Aru>licable Not Applicable
10/3/2011 ;1.92E-16 9.00E-14 _2.25E-14 l.17E-16 2.00E-14 5.00E-15 6.76E-17 ; 9.00E-13 2.25E-13 l.14E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 6.00E-13 1.SOE-13 Not Anajyzed Not Ap_plicable Not Applicable
4/3/2012 7.87E-16 9.00E·14 ' 2.25E-14 2.64E-16 2.00E-14 5.00E-15 3.95E-16 9.00E-13 2.25E-13 l.25E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not ~plicable
7/2/2012 1.86E-15 9.00E-14 2.25E-14 8.33E-16 2.00E-14 5.00E-15 9.85E-16 9.00E-13 .2.25E-13 9.55E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 l.06E-15 9.00E-14 2.25E-14 2.llE-16 2.00E-14 5.00E-15 2.34E-16 9.00E-13 2.25E-13 l.13E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 6.86E-16 9.00E-14 , 2.25E-14 1.27E-16 2.00E-14 5.00E-15 1.38E-16 9.00E-13 2.25E-13 l.54E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 9.91E-16 9.00E-14 2.25E-14 1.86E-16 2.00E-14 5.00E-15 2.04E-16 9.00E-13 2.25E-13 l.82E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AQplicable
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 -,Z.25E-13 5.78E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 8.00E-15 6.00E-13 l.50E-13 .Not Analyzed Not Applicable Not Applicable
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 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.24E-14 6.00E-13 1.50E-13 Not Anajyzed Not Ap_plicable Not AQplicable
6/30/2014 2.24E-15 9.00E-14 2.25E-14 5.14E-16 2.00E-14 S.OOE-15 1.09E-15 -9.00E-13 2.25E-13 l.23E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 1.59E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.39E-14 6.00E-13 1.50E-13 1.00E-16 4.00E-15 1.00E-15
12/29/2014 2.00E-16 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 7.00E-17 :;l.OOE-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 7.00E-18 4.00E-15 1.00E-15
3/30/2015 1.90E-15 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 6.00E-17 • 9.00E-13 2.25E-13 2.80E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
6/29/2015 i;.OOE-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 7.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 1.00E-15
9/28/2015 1.60E-15 9.00E-14 2.25E-14 8.00E-17 2.00E-14 5.00E-15 6.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
12/28/2015 2.20E-16 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 l.20E-14 6.00E-13 1.SOE-13 1.00E-18 4.00E-15 1.00E-15
3/28/2016 2.00E-16 9.00E-14 ·2.25E-14 3.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 l.40E-14 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 1.00E-15
6/27/2016 ·1.10E-15 9.00E-14 2.25E-14 7.00E-17 2.00E-14 S.OOE-15 9.00E-16 9.00E-13 .2.25E-13 9.60E-15 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15
9/27/2016 1.lOE-15 9.00E-14 2.25E-14 8.70E-17 2.00E-14 5.00E-15 1.SOE-16 9.00E-13 2.25E-13 l.20E-14 6.00E-13 1.50E-13 9.SOE-18 4.00E-15 1.00E-15
12/27/2016 9.SOE-16 9.00E-14 2.25E-14 7.SOE-17 2.00E-14 5.00E-15 1.30E-16 . 9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.SOE-13 4.SOE-18 4.00E-15 1.00E-15
3/27/2017 1.40E-15 9.00E-14 2.25E-14 --8.00E-17 2.00E-14 5.00E-15 8.00E-16 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 1.00E-15
6/26/2017 _1.lOE-15 ---, 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 1.50E-13 8.00E-18 4.00E-15 1.00E-15
Date Effluent 9E·14 uCi/ml BHV-lU Effluent ZE-14 uCi/ml BHV-1T230 Effluent 9E·13 uCi/ml BHV-lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-15 uCi/ml 8HV-1T232
Concentration Concentration Concentration Concentration Concentration
limit= Limit: limit= Limit= limit=
ALARAGoal = 2.25£-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
limit= Limit= limit= Limit= limit=
Pre 1994 .1.25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml ·pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/25/2017 6.00E-16 9.00E-14 2.25E-14_ 6.00E-17 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 l.SOE-13 8.00E-18 4.00E-15 1.00E-15
12/26/2017 2.40E·15 9.00E-14 2.25E-14 S.OOE-17 2.00E-14 5.00E-15 7.00E-17 9.00E-13 2.2SE-13 1.BOE-14 6.00E-13 l.SOE-13 1.00E-17 4.00E-15 1.00E-15
3/26/2018 1.90E·16 9.00E-14 2.25E-14 5.30E-17 2.00E-14 5.00E-15 9.20E-17 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 1.SOE-13 5.30E-18 4.00E-15 1.00E-15
6/25/2018 8.00E-16 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 2.SOE-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.SOE-13 9.30E-18 4.00E-15 1.00E-15
9/24/2018 4.00E-16 9.00E-14 2.2SE-14 9.00E-17 2.00E-14 5.00E-15 7.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.SOE-13 l.OOE-17 4.00E-15 1.00E-15
12/31/2018 1.SOE-15 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 2.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 l.OOE-15
4/1/2019 8.00E-17 _ 9.00E-14 2.25E-14 S.OOE-17 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 l.OOE-15
7/1/2019 7.00E-17 9.00E-14 _ 2.25E-t41 2.00E-16 2.00E-14 5.00E-15 8.00E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
9/30/2019 1.00E-16 9.00E-14 2.25E-14 5.00E-16 2.00E-14 5.00E-15 8.00E-16 9.00E-13 2.25E-13 l.OOE-14 6.00E·l3 l.SOE-13 7.00E-18 4.00E-15 1.00E-15
1/6/2020 4.00E-17 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 6.00E-17 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 l.OOE-15
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0 0 Ill :, -0 II ID __., :, . -o -. m !2. I -• _. 0
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.,::. m . _.
C1I
C C') :::::.: 3
CD
:I: ~ .....
-t :::T 0
:::::!.
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TAB2
BHV-2 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-ZU Effluent ZE-14 uCi/ml BHV-ZTZ30 Effluent 9E-15 uCi/ml BHV-ZR Effluent GE-13 uCi/ml BHV-ZPB Effluent 4e-15 uCi/ml BHV-ZTZ3Z
Concentration Concentration Concentration Concentration Concentration
limit= Limit= Limit= Limit= Limit=
ALARAGoal= Z.ZSE-14 uCi7ml ALARAGoal = SE-15 uCi/ml ALARAGoal = Z.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-1Z uCi/ml Pre 1994 MPC Not Applicable
~imit= Limit= Limit= Limit= Limit=
"
pre 1994 ALARA 1.ZSE-12 uCi/mf Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml ,Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= .ALARA GOAL=
!=one EFC I EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 l.39E-15 5.00E-12 'l.25E-12 3.69E-16 8.00E-14 2.00E-14 5.92E-16 2.00E-12 S.OOE-13 l.67E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 4.62E-16 5.00E-12 ] l..25E-12 8.03E-16 8.00E-14 2.00E-14 3.62E-16 2.00E-12 5.00E-13 1.33E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 7.07E-16 5.00E-12 l.25E-12 1.lOE-15 8.00E-14 2.00E-14 7.27E-16 2.00E-12 5.00E-13 l.52E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
6/30/1982 8.84E-16 5.00E-12 '1.25E-12 7.73E-16 8.00E-14 2.00E-14 4.78E-16 2.00E-12 5.00E-13 1.98E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/27/1982 l.23E-15 5.00E-12 l.25E-12 3.60E-16 8.00E-14 2.00E-14 8.73E-16 2.00E-12 5.00E-13 2.35E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 2.64E-15 5.00E-12 l.25E-12 2.55E-16 8.00E-14 2.00E-14 l.98E-16 2.00E-12 5.00E-13 2.85E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 ·2.14E-16 5.00E-12 l.25E-12 l.02E-16 8.00E-14 2.00E-14 l.57E-16 2.00E-12 5.00E-13 2.48E-14 4.00E-12 ;l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 2.85E-16 5.00E-12 l.25E-12 2.06E-16 8.00E-14 2.00E-14 2.24E-16 2.00E-12 5.00E-13 l.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Aru>licable Not Applicable
10/3/1983 2.70E-16 5.00E-12 • l.25E-12 3.36E-16 8.00E-14 2.00E-14 4.37E-16 2.00E-12 5.00E-13. l.78E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not llru>licable
1/3/1984 2.78E-15 5.00E-12 l.25E-12 1.20E-16 8.00E-14 2.00E-14 6.64E-17 2.00E-12 5.00E-13 9.14E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not AQPlicable
4/2/1984 4.28E-16 5.00E-12 ll.25E-12 1.75E-16 8.00E-14 2.00E-14 4.57E-17 2.00E-12 5.00E-13 3.55E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 2.78E-15 5.00E-12 l.25E-12 8.12E-16 8.00E-14 2.00E-14 1.98E-16 2.00E-12 5.00E-13 l.68E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/1/1984 2.69E-16 5.00E-12 l.25E-12 2.66E-17 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 1.77E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/2/1985 2.15E-16 5.00E-12 , l.25E-12 7.55E-16 8.00E-14 2.00E-14 2.87E-16 2.00E-12 S.OOE-13 3.19E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 1.00E-16 5.00E-12 '1.25E-12 1.67E-16 8.00E-14 2.00E-14 6.75E-17 2.00E-12 S.OOE-13 7.56E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A_pplicable
7/1/1985 3.70E-17 5.00E-12 l.25E-12 9.00E-16 8.00E-14 2.00E-14 4.90E-17 2.00E-12 5.00E-13 l.31E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 ~.32E-17 5.00E-12 l.25E-12 2.18E-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 3.64E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 1.00E-16 5.00E-12 l.25E-12 2.16E-16 8.00E-14 2.00E-14 2.15E-17 2.00E-12 5.00E-13 3.04E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 1.31E-15 5.00E-12 1.25E-12 1.50E-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 2.90E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 2.23E-16 ,S.OOE-12 1.25E-12 1.32E-16 8.00E-14 2.00E-14 7.09E-17 2.00E-12 : 5.00E-13 2.53E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 6.41E-16 5.00E-12 l.25E-12 1.74E-16 8.00E-14 2.00E-14 3.67E-16 2.00E-12 5.00E-13 1.04E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 3.SGE-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 1.05E-16 2.00E-12 S.OOE-13 7.81E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 5.31E-16 5.00E-12 1.25E-12 l.30E-16 8.00E-14 2.00E-14 7.74E-17 2.00E-12 5.00E-13 3.80E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1987 4.0GE-16 S.OOE-12 l.25E-12 6.63E-17 8.00E-14 2.00E-14 1.34E-16 2.00E-12 '5.00E-13 l.lOE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/9/1987 2.74E-16 5.00E-12 l.25E-12 2.38E-16 8.00E-14 2.00E-14 1.38E-16 2.00E-12 , S.OOE-13 1.04E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/2/1987 3.73E-16 5.00E-12 l.25E-12 3.llE-16 8.00E-14 2.00E-14 l.83E-16 2.00E-12 S.OOE-13 1.17E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 2.78E-15 5.00E-12 .l.25E-12 2.31E-17 8.00E-14 2.00E-14 1.20E-16 2.00E-12 5.00E-13 3.55E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 4.63E-16 5.00E-12 l.25E-12 1.49E-16 8.00E-14 2.00E-14 2.30E-16 2.00E-12 5.00E-13 1.18E-14 4.00E-12 1.00E-12 Not Ana!Yzed Not Applicable Not Applicable
8/15/1988 8.0GE-16 5.00E-12 l.25E-12 8.69E-16 8.00E-14 2.00E-14 l.80E-16 -2.00E-12 6.00E-13 1.42E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 4.34E-16 5.00E-12 l.25E-12 6.76E-16 8.00E-14 2.00E-14 ;1.57E-16 2.00E-12 5.00E-13 2.25E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/13/1989 5.80E-16 5.00E-12 l.25E-12 2.85E-16 8.00E-14 2.00E-14 l.55E-16 2.00E-12 5.00E-13 2.80E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable ' Ncrr_Applicable
5/15/1989 5.0GE-16 5.00E-12 l.25E-12 2.28E-16 8.00E-14 2.00E-14 1.63E-16 2.00E-12 5.00E-13 6.05E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 4.71E-16 5.00E-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 1.00E-12 Not Analyzed Not Applicable '. Not Applicable I
11/13/1989 1.14E-15 5.00E-12 l.25E-12 4.08E-16 8.00E-14 2.00E-14 4.18E-16 :2.00E-12 S.OOE-13 l.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable · Not Applicable
2/12/1990 1.09E-15 5.00E-12 l.25E-12 3.25E-16 8.00E-14 2.00E-14 3.74E-16 2.00E-12 :S.OOE-13 l.98E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not ~plicable
5/14/1990 9.32E-16 ,5.00E-12 l.25E-12 5.27E-16 8.00E-14 2.00E-14 3.97E-16 2.00E-12 5.00E-13 l.69E-14 4.00E·12 1.00E-12 Not Analyzed · Not AQPlicable Not Ap_plicable
8/13/1990 1.66E-16 5.00E-12 l.25E-12 5.49E-16 8.00E-14 2.00E-14 1.75E-17 2.00E-12 5.00E-13 1.27E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 6.05E-16 5.00E-12 • l.25E-12 2.64E-16 8.00E-14 2.00E-14 :J..93E-16 2.00E-12 5.00E-13 2.25E-14 4.00E-12 1.00E-12 Not Analyzed · Not Applicable Not Applicable
2/11/1991 8.72E-17 5.00E-12 l.25E-12 7.00E-18 8.00E-14 2.00E-14 3.33E-17 2.00E-12 5.00E-13 3.49E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 1.16E-16 5.00E-12 1.25E-12 3.86E-16 8.00E-14 2.00E-14 2.80E-16 2.00E-12 5.00E-13 1.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 9.02E-17 5.00E-12 1.25E-12 8.82E-17 8.00E-14 2.00E-14 7.65E-17 2.00E-12 5.00E-13 1.58E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 4.SlE-17 S.OOE-12 1.25E-12 3.82E-17 8.00E-14 2.00E-14 2.54E-17 2.00E-12 5.00E-13 l.45E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable · Not Applicable
2/10/1992 1.54E-16 !i.OOE-12 l.25E-12 6.82E-17 8.00E-14 2.00E-14 ;l.40E-17 2.00E-12 5.00E-13 3.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1992 2.38E-16 S.OOE-12 l.25E-12 7.63E-17 8.00E-14 2.00E-14 '.3.07E-17 2.00E-12 5.00E-13 1.27E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable _J
8/10/1992 1.0lE-16 S.OOE-12 1.25E-12 7.07E-17 8.00E-14 2.00E-14 2.80E-17 2.00E-12 S.OOE-13 1.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable . Not Applicable
11/9/1992 5.20E-17 5.00E-12 l.25E-12 3.65E-17 8.00E-14 2.00E-14 'l.78E-17 2.00E-12 5.00E-13 l.71E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.39E-16 5.00E-12 1.25E-12 2.97E-17 8.00E-14 2.00E-14 6.31E-17 2.00E-12 5.00E-13 3.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ~plicable
5/10/1993 1.00E-16 5.00E-12 1.25E-12 7.llE-17 8.00E-14 2.00E-14 3.19E-17 2.00E-12 :S.OOE-13 1.34E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 1.90E-16 5.00E-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.80E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-2U Effluent 2E-14 uCi/ml BHV-2T230 Effluent 9E-15 uCi/ml BHV-2R Effluent 6E-13 uCi/ml BHV-2PB Effluent 4e-15 uCi/ml BHV-2T232
Concentration Concentration Concentration Concentration Concentration
µmit= Limit= Limit= Limit= Limit=
ALARAGoal= 2.ZSE-14 uCi/inl ALARAGoal = SE-15 uCi/ml ALARA Goal= 2.ZSE-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre1994MPC SE-UuCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-U uCi/ml Pre 1994 MPC 4E-12 uCi/ml ,Pre 1994 MPC Not Applicable
Limit= Limit= Limit= limit= Limit=
Pre 1994 ALARA l.2SE-U uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
tone . EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
11/8/1993 l.OOE-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.49E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1994 2.23E-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 1.84E-16 2.00E-12 5.00E-13 2.19E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
5/9/1994 2.16E-16 5.00E-12 1.25E-12 7.20E-17 8.00E-14 2.00E-14 9.89E-17 2.00E-12 5.00E-13 l.37E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/9/1994 9.29E-17 5.00E-12 1.25E-12 2.96E-16 8.00E-14 2.00E-14 3.04E-16 2.00E-12 S.OOE-13 1.00E-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 9.21E-17 5.00E-12 1.25E-12 2.35E-16 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 S.OOE-13 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1995 1.18E-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 7.42E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.40E-17 9.00E-14 2.2SE-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 Not Analyzed Not Applicable Not Applicable
8/9/1995 8.90E-17 9.00E-14 2.25E-14 9.67E-17 2.00E-14 5.00E-15 1.35E-16 9.00E-13 2.25E-13 2.38E-16 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Ap_plicable
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 l.50E-13 Not Analyzed Not Ap_plicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
5/6/1996 1.40E·16 9.00E-14 2.25E-14 1.15E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.85E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
8/5/1996 1.43E-16 9.00E-14 2.25E-14 2.78E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.83E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 1.45E-16 9.00E-14 2.25E-14 1.57E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.19E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 1.00E-16 9.00E-14 2.25E-14 1.00E-16 l.OOE-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.84E-16 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 1.00E-16 l!I.OOE-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.89E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
8/11/1997 1.00E-16 9.00E-14 2.25E-14 1.09E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.69E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/5/1998 2.5SE-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.llE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
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.SOE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 1.00E-16 9.00E-14 I 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.2SE-13 4.26E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/28/1998 2.54E-16 9.00E-14 2.25E-14 2.lSE-16 2.00E-14 5.00E-15 1.38E-16 9.00E-13 2.2SE-13 6.88E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/29/1999 1.07E-16 9.00E-14 2.25E-14 LOOE-16 2.00E-14 5.00E-1S l .OOE-16 9.00E-13 2.2SE-13 7.61E-15 6.00E-13 l .SOE-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 2.46E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-1S l.OOE-16 9.00E-13 2.25E-13 6.95E-1S 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/1999 2.81E·16 9.00E-14 2.25E-14" l.41E-16 2.00E-14 5.00E-1S 1.00E-16 9.00E-13 2.25E-13 7.35E-1S 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/28/1999 S.20E-16 9.00E-14 2.25E-14 2.60E-16 2.00E-14 5.00E-1S 2.0lE-16 9.00E-13 2.2SE-13 7.00E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 1.00E-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 ~.OOE-13 2.25E-13 7.12E-15 6.00E-13 1.50E-13 !'Jot Analyzed ,Not Applicable Not Applicable
6/26/2000 1.lOE-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 5.00E-15 1.16E-16 9.00E-13 2.25E-13 5.07E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2000 1.00E-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 5.31E-15 6.00E·l3 1.SOE-13 Not Analyzed Not Applicable Not A_pplicable
12/26/2000 1.26E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 9.45E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 l.OOE-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 6.95E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 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 6.56E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 1.00E-16 9.00E-14 2.25E-14 l .OOE·l6 2.00E-14 .5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.16E-15 6.00E-13 l.SOE-13 'Not Analyzed Not Applicable Not Applicable
12/31/2001 l .OOE-16 9.00E-14 .2.25E-14 1.00E-16 2.00E-14 S.OOE-1S 1.00E-16 9.00E-13 2.25E-13 2.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap_plicable Not Applicable
4/1/2002 1.00E-16 9.00E-14 ;2.2SE-14 1.00E-16 2.00E-14 5.00E-15 1.00E·16 9.00E-13 2.2SE-13 9.95E·15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 1.25E-16 9.00E-14 2.25E-14 l.43E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.2SE-13 8.25E·15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 1.00E-16 9.00E-14 ·~.2SE-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.69E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/30/2002 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 6.91E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 1.00E-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 5.00E·lS 1.00E-16 9.00E-13 2.25E-13 6.16E-15 6.00E-13 1.SOE-13 Not Analyzed Not A@licable Not Applicable
6/30/2003 1.00E-16 9.00E-14 2.25E-14 1.00E·16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 5.27E-15 6.00E·l3 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/29/2003 1.00E-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 7.23E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 1.00E-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 7.SOE-15 6.00E-13 'l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/29/2004 1.00E-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 2.04E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.00E-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 3.09E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-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 1.73E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/27/2004 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 nsE-13 1.30E·14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 1.00E-16 9.00E-14 2.25E·14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E·l3 2.25E-13 8.88E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/29/200S 1.00E-16 9.00E-14 2.2SE-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 . 2.2SE-13 8.8SE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 1.00E-16 9.00E-14 2.25E-14 l.99E-16 2.00E-14 5.00E-15 1.44E-16 9.00E-13 2.2SE-13 3.81E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
1/3/2006 1.29E-16 9.00E-14 2.25E-14 1.00E·l6 2.00E-14 5.00E-15 4.08E-16 9.00E-13 2.25E-13 6.58E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-2U Effluent 2E-14 uCi/ml BHV-2T230 Effluent 9E-15 uCi/ml BHV-2R Effluent 6E-13 uCi/ml BHV-2PB Effluent 4e-15 uCi/ml BHV-2T232
Concentration Concentration Concentration Concentration Concentration
pmit= Limit= limit= Limit= limit=
AlARAGoal= :Z-ZSE-14 uCi/ml AlARAGoal = SE-15 uCi/ml ALARAGoal = 2.ZSE-13 uCi/ml ALARA Goal: 1.SE-13 uCi/ml ALAllA Goal = lE-15 uCi/ml
Pre 1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Umlt: Limit= Limit= Limit= Limit=
Pre 1994 ALARA 1.25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml .Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cane EFC EFCA Cane EFC EFCA Cane EFC EFCA Cane EFC EFCA Cane EFC EFCA
4/3/2006 1.02E-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 1.0SE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/3/2006 1.00E-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 1.lOE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/2/2006 1.30E-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 1.68E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 ·1.24E-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 1.38E·14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 1.40E-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 1.63E·14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 1.04E·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 1.36E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2007 1.00E-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 8.24E·15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 1.91E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.18E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/30/2008 1.00E-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 6.49E·l5 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2008 1.29E-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 4.82E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ~plicable
9/30/2008 2.73E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 8.30E·15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2008 5.71E·16 9.00E-14 2.25E-14 1.61E·l6 2.00E-14 5.00E-15 1.2SE·16 9.00E-13 2.2SE-13 2.04E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 3.96E-16 9.00E-14 2.2SE-14 1.38E-16 2.00E-14 S.OOE-15 1.07E-16 9.00E-13 2.25E-13 4.81E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 1.24E-17 9.00E-14 2.25E-14 4.64E-17 2.00E-14 5.00E-15 S.llE-17 9.00E-13 2.25E-13 4.58E·15 6.00E-13 1.SOE-13 Not Analyzed !'lot Applicable Not Applicable
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.SOE-13 Not Analyzed Not Applicable !'lot Applicable
12/15/2009 S.72E·16 9.00E-14 2.25E-14 2.94E-17 2.00E-14 5.00E-15 2.57E-17 9.00E-13 2.25E-13 6.70E·l5 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 2.2SE·l3 8.24E·15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable !'lot Applicable
6/30/2010 3.SBE-16 9.00E-14 2.2SE-14 6.64E-17 2.00E-14 5.00E-15 9.90E·l7 9.00E-13 2.2SE·l3 2.0lE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2010 2.91E·16 9.00E-14 2.25E-14 4.48E-17 2.00E-14 5.00E-15 5.72E·17 9.00E-13 2.25E-13 1.08E-15 6.00E-13 l.50E·l3 Not Analyzed Not Applicable Not Applicable
12/31/2010 5.73E-16 9.00E-14 2.25E-14 7.24E·l7 2.00E-14 S.OOE-15 6.76E-17 9.00E-13 2.2SE-13 l .35E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 3.79E·16 9.00E-14 2.25E-14 4.0lE-17 2.00E-14 S.OOE-15 9.llE-17 9.00E-13 2.25E-13 l.06E-14 6.00E-13 1.SOE-13 Not Ana[yzed Not Applicable .Not Applicable
7/4/2011 3.07E-16 9.00E-14 2.2SE-14 8.54E-17 2.00E-14 5.00E-15 9.21E·l7 9.00E-13 ~ 2.25E-13 7.21E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 l.17E·16 9.00E-14 2.25E-14 3.04E-17 2.00E-14 S.OOE-15 2.81E-17 9.00E-13 2.2SE-13 1.03E·14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 2.2SE-13 1.58E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 4.22E-16 9.00E-14 2.25E-14 1.15E·16 2.00E-14 5.00E-15 2.77E-16 9.00E-13 2.25E-13 1.58E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable 'Not Applicable
7/2/2012 3.39E-16 9.00E-14 2.2SE-14 1.56E-16 2.00E-14 5.00E-15 1.74E-16 9.00E-13 2.25E·l3 8.60E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 3.13E-16 9.00E-14 2.25E-14 4.13E-17 2.00E-14 S.OOE-15 3.04E-17 9.00E-13 2.25E-13 1.03E-14 6.00E-13 1.50E-13 Not Analyzed Not A_pplicable Not Applicable
12/31/2012 2.76E-16 9.00E-14 l2.2SE-14 5.41E-17 2.00E-14 S.OOE-15 7.0SE-17 9.00E-13 2.25E-13 1.48E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 3.38E-16 9.00E-14 2.25E-14 3.94E-17 2.00E-14 5.00E-15 8.32E·l7 9.00E-13 2.2SE-13 1.42E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 4.06E·l6 9.00E-14 l.25E·14 4.89E-17 2.00E-14 5.00E-15 8.0GE-17 9.00E-13 2.25E-13 4.93E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 1.76E-16 9.00E-14 . ,1..2SE-14 2.52E-17 2.00E-14 5.00E-15 6.13E-17 9.00E-13 2.2SE·l3 4.90E·15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2013 6.20E-16 9.00E-14 2.2SE-14 4.19E-17 2.00E-14 5.00E-15 3.72E·l7 9.00E-13 2.25E-13 2.SOE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2014 4.63E-16 9.00E-14 l2.25E-14 4.97E-17 2.00E-14 5.00E-15 1.lSE-16 9.00E-13 2.25E-13 1.49E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2014 3.04E·16 9.00E-14 2.25E-14 7.92E-17 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.llE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 4.89E-16 9.00E-14 2.25E-14 6.0lE-17 2.00E-14 5.00E-15 4.47E-17 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 1.SOE-13 9.35E·18 4.00E-15 1.00E-15
12/29/2014 1.00E-16 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
3/30/2015 5.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 2.30E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
6/29/2015 1.00E-16 9.00E-14 2.2SE-14 4.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 1.40E-14 6.00E-13 1.50E-13 8.00E-18 4.00E-15 1.00E-15
9/28/2015 5.00E-16 9.00E-14 ',.25E-14 9.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-13 6.00E-18 4.00E-15 1.00E-15
12/28/2015 1.00E-16 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 !2.25E-13 2.20E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15
3/28/2016 7.00E-16 9.00E-14 2.25E-14 6.00E-18 2.00E-14 5.00E-15 8.00E-17 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
6/27/2016 2.00E-16 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 : 2.2SE-13 l.30E·l4 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 l.OOE-15
9/27/2016 4.20E-16 9.00E-14 2.25E-14 6.90E-17 2.00E-14 5.00E-15 8.lOE-17 9.00E-13 l .25E-13 l.OOE-14 6.00E-13 1.50E-13 S.20E-17 4.00E-15 1.00E-15
12/27/2016 4.lOE-16 9.00E-14 2.2SE·14 1.90E-17 2.00E-14 5.00E-15 S.OOE-17 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 2.20E-18 4.00E-15 1.00E-15
3/27/2017 1.lOE-15 9.00E-14 Z.2SE·14 4.00E-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 ,Z.25E·l3 1.SOE-14 6.00E-13 1.SOE-13 5.00E-18 4.00E-15 1.00E-15
6/26/2017 2.00E-17 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 1.SOE-13 9.00E-18 4.00E-15 1.00E-15
9/25/2017 2.00E-16 ,9.00E-14 2.25E-14 2.00E-17 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 1.30E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
12/26/2017 6.00E-16 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 S.OOE-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 9.00E-18 4.00E-15 1.00E-15
3/26/2018 6.70E·17 9.00E-14 2.25E-14 1.40E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.2SE·l3 1.20E-14 6.00E-13 l.SOE-13 5.30E-18 4.00E-15 ,1.00E-15 '
Date Effluent -9E-14 ua/ml BHV-2U Effluent ZE-14 uCi/ml BHV-2T230 Effluent 9E-15 uCi/ml BHV-2R Effluent 6E-13 uCi/ml BHV-ZPB Effluent 4e-15 uCi/ml BHV-2T232
Concentration Concentration Concentration Concentration Concentration
!,.imlt= limit= Limit= Limit= Limit=
AlARAGoal= , 2.25E-14 uO[ml -ALARAGoal = SE-15 uCi/ml ALARA Goal = , 2.25E-13 uCi/ml ALARA Goal= l .SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
,re1994MPC SE-12u0/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-UuCi/ml Pre 1994 MPC Not Applicable
Limit= limit= Limit= Limit= limit=
Pre 1994 ALARA 1.25E-12 uCl/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-UuCi/ml Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone ; EFC EFCA Cone EFC EFCA Cone 'EFC EFCA
6/25/2018 3.SOE-16 9.00E-14 2.25E-14 4.60E-17 2.00E-14 S.OOE-15 1.20E-16 9.00E-13 2_25E-13 UOE-14 6.00E-13 1.SOE-13 1.SOE-17 4.00E-15 1.00E-15
9/24/2018 l.OOE-16 9.00E-14 ·2-25E-14 2-00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.ZSE-13 1-00E-14 6.00E-13 1.SOE-13 7.00E·18 4_00E-15 1.00E-15
12/31/2018 5.00E-16 9.00E-14 2.25E·14 2.00E-17 2.00E-14 5.00E-15 1.00E-17 9_QOE-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 4.00E-18 4-00E-15 1.00E-15
4/1/2019 4.00E-17 9.00E-14 2.25E-14 3-00E-17 2.00E-14 5.00E-15 8.00E-17 9.00E-13 2.25E-13 1-DOE-14 6.00E-13 1.SOE-13 2.00E-18 4-DOE-15 1.00E-15
7/1/2019 3.00E-17 9.00E-14 2.25E-14 3.00E-17 2_QOE-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 8.00E-15 6.00E-13 1.SOE-13 .9.00E-18 4.00E-15 1.00E-15
9/30/2019 2.00E,16 9.00E-14 2.25E·14 3.00E-17 2.00E-14 5-00E-15 3.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 l.SOE-13 9.00E-18 4.00E-15 1.00E-15
1/6/2020 2.00E-17 9.00E-14 2.ZSE-14 1.00E-17 2-00E-14 S_OOE-15 4.00E-17 9.00E-13 2.ZSE-13 8.00E-15 6-00E-13 l _SOE-13 5.00E-18 4.00E-15 1.00E-15
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TAB3
BHV-3 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCirml BHV-3U Effluent ZE-14 uCi/ml BHV-3T230 Effluent 9E-13 uCi/ml BHV-3R Effluent 6E-13 uCi/ml BHV-3PB
Concentration Concentration Concentration Concentration
,Limit= Limit= limit= limit=
ALARAGoal= Z.ZSE-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal = 2.isE'13 ud/ml ALARAGoal = 1.SE-13 uCi/ml
Pre1994MPC SE·lZ uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC • ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
Limit= limit= Limit= limit=
Pre 1994 ALARA 1.25E-12 uCl/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
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 5.00E-13 l.54E-14 4.00E-12 1.00E-12
12/14/1981 l.59E-15 S.OOE-12 1.25E-12 5.03E-16 8.00E-14 2.00E-14 l.30E-16 2.00E-12 5.00E-13 2.25E-14 4.00E-12 l.OOE-12
3/29/1982 3.76E-16 5.00E-12 1.25E-12 5.25E-16 8.00E-14 2.00E-14 4.0BE-16 2.00E-12 5.00E-13 1.96E-14 4.00E-12 l.OOE-12
6/30/1982 3.83E-16 S.OOE-12 1.25E-12 2.16E-l6 8.00E-14 2.00E-14 1.41E-15 2.00E-12 5.00E-13 2.40E-14 4.00E-12 l.OOE-12
9/27/1982 5.95E-16 5.00E-12 1.25E-12 1.44E-15 8.00E-14 2.00E-14 5.36E-16 2.00E-12 5.00E-13 1.43E-14 4.00E-12 1.00E-12
1/3/1983 2.0SE-16 5.00E-12 1.25E-12_ l.23E-16 8.00E-14 2.00E-14 1.lOE-16 2.00E-12 5.00E-13 3.0lE-14 4.00E-12 l.OOE-12
4/4/1983 1.00E-16 5.00E-12 1.25E-12 6.94E-17 8.00E-14 2.00E-14 6.llE-17 2.00E-12 5.00E-13 1.39E-14 4.00E-12 1.00E-12
6/30/1983 3.06E-16 5.00E-12 1.25E-12 959E-17 8.00E-14 2.00E-14 2.08E-16 2.00E-12 5.00E-13 l.70E-14 4.00E-12 1.00E-12
10/3/1983 1.91E-16 5.00E-12 1.25E-12 3.05E-16 8.00E-14 2.00E-14 2.79E-16 2.00E-12 5.00E-13 l.76E-14 4.00E-12 l.OOE-12
1/3/1984 3.0lE-16 5.00E-12 1.25E-12 9.51E-17 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 5.00E-13 9.17E-15 4.00E-12 l.OOE-12
4/2/1984 8.22E-16 5.00E-12 1.25E-12 7.52E-16 8.00E-14 2.00E-14 5.20E-17 2.00E-12 'S.OOE-13 3.47E-14 4.00E-12 1.00E-12
7/2/1984 5.29E-16 5.00E-12 ,l..25E-12 6.18E-16 8.00E-14 2.00E-14 1.40E-16 ;2.00E-12 5.00E-13 l.32E-14 4.00E-12 1.00E-12
10/1/1984 1.74E-16 5.00E-12 1.2se-12· 7.lOE-17 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 l.08E-14 4.00E-12 l.OOE-12
1/2/1985 1.00E-17 5.00E-12 1.25E-12 7.lOE-17 8.00E-14 2.00E-14 7.BOE-17 2.00E-12 5.00E-13 2.73E-14 4.00E-12 l.OOE-12
4/1/1985 1.00E-16 5.00E-12 1.25E-12 2.76E-16 8.00E-14 2.00E-14 4.lOE-17 2.00E-12 S.OOE-13 1.12E-14 4.00E-12 1.00E-12
7/1/1985 1.04E-16 5.00E-12 l.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 l.64E-14 4.00E-12 1.00E-12
9/30/1985 l.OOE-16 5.00E-12 1.25E-12_ 1.00E-15 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 l.73E-14 4.00E-12 l.OOE-12
1/2/1986 l.03E-15 5.00E-12 l.2SE-12 3.17E-16 8.00E-14 2.00E-14 1.25E-16 2.00E-12 5.00E-13 1.21E-17 4.00E-12 l.OOE-12
4/1/1986 8.04E-16 5.00E-12 1.25E-12 l.93E-17 8,00E-14 2.00E-14 l.54E-16 2.00E-12 5.00E-13 1.69E-14 4.00E-12 l.OOE-12
6/30/1986 4.29E-16 5.00E-12 1.25E-12 1.77E-16 8.00E-14 2.00E-14 2.83E-16 _2.00E-12 5.00E-13 l.97E-14 4.00E-12 l .OOE-12
10/27/1986 6.45E-16 5.00E-12 1.25E-12 9.89E-17 8.00E-14 2.00E-14 4.16E-15 2.00E-12 5.00E-13 1.64E-l4 4.00E-12 l.OOE-12
12/15/1986 l.31E-16 -5.00E-12 ·1.25E-12 O.OOE+OO 8.00E-14 2.00E-14 4.16E-l7 2.00E-12 5.00E-13 4,60E-15 4.00E-12 l.OOE-12
3/16/1987 2.0lE-16 5.00E-12 1.25E-12 l.20E-16 8.00E-14 2.00E-14 5.73E-17 2.00E-12 5.00E-13 l.60E-14 4.00E-12 1.00E-12
5/11/1987 2.16E-16 5.00E-12 · t.ZSE-12 1.96E-16 8.00E-14 2.00E-14 7.38E-17 2.00E-12 5.00E-13 l.59E-14 4.00E-12 l.OOE-12
9/9/1987 2.41E-16 5.00E-12 l.25E-12 2.18E-16 8.00E-14 2.00E-14 3.52E-l7 2.00E-12 .S.OOE-13 l.46E-14 4.00E-12 1.00E-12
11/2/1987 2.44E-16 5.00E-12 1.25E-12 2.32E-16 8.00E-14 2.00E-14 2.37E-17 2.00E-12 'i;.OOE-13 2.48E-14 4.00E-12 l.OOE-12
2/16/1988 8.0BE-16 5.00E-12 1.25E-12 2.SSE-16 8.00E-14 2.00E-14 3.42E-16 2.00E-12 .5.00E-13 5.61E-14 4,00E-12 1.00E-12
5/18/1988 1.14E-16 a.OOE-12 l.25E-12_ 4.14E-17 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 S.OOE-13 1.20E-14 4.00E-12 1.00E-12
8/15/1988 2.0BE-16 5.00E-12 l.25E-12. 3.06E-16 8.00E-14 2.00E-14 3.65E-17 2.00E-12 5.00E-13 l.36E-14 4.00E-12 1.00E-12
11/14/1988 4.21E-16 5.00E-12 l.25E-12 2.93E-16 8.00E-14 2.00E-14 l.09E-16 2.00E-12 S.OOE-13 2.48E-l4 4.00E-12 l.OOE-12
2/13/1989 4.45E-16 5.00E-12 1.25E-12 4.78E-17 8.00E-14 2.00E-14 2.47E-17 2.00E-12 5.00E-13 3.34E-14 4.00E-12 l.OOE-12
5/15/1989 1.05E-16 5.00E-12 l.25E-12 l.OOE-16 8.00E-14 2.00E-14 2.45E-17 2.00E-12 5.00E-13 6.56E-15 4.00E-12 1.00E-12
8/14/1989 1.31E-16 5.00E-12 l.25E-12 5.85E-17 8.00E-14 2.00E-14 ~.97E-17 2.00E-12 5.00E-13 6.?SE-15 4.00E-12 1.00E-12
11/13/1989 1.67E-16 5.00E-12 l.25E-12 3.87E-17 8.00E-14 2.00E-14 8.03E-17 2.00E-12 5.00E-13 1.69E-14 4.00E-12 l.OOE-12
2/12/1990 4.43E-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 3.SOE-17 2.00E-12 5.00E-13 2.37E-14 4,00E-12 l.OOE-12
5/14/1990 3.84E-16 S.OOE-12 1.25E-12 254E-16 8,00E-14 2.00E-14 1.02E-16 2.00E-12 5.00E-13 l.68E-14 4.00E-12 l.OOE-12
8/13/1990 7.27E-17 5.00E-12 1.25E-12 2.87E-16 8.00E-14 2.00E-14 1.21E-17 2.00E-12 5.00E-13 7.86E-15 4,00E-12 l.OOE-12
11/12/1990 1.84E-16 S.OOE-12 1.25E-12 1.34E-16 8.00E-14 2.00E-14 8.53E-17 2.00E-12 5.00E-13 2.0lE-14 4.00E-12 l.OOE-12
2/11/1991 (l.66E-17 S.OOE-12 l.25E-12 8.48E-16 8.00E-14 2.00E-14 1.94E·l7 2.00E-12 5.00E-13 3.69E-14 4.00E-12 l.OOE-12
5/13/1991 5.05E-l7 5.00E-12 1.25E-12 7.40E-17 8.00E-14 2.00E-14 7.00E-18 2.00E-12 S.OOE-13 1.SOE-14 4.00E-12 1.00E-12
8/12/1991 7.14E-17 5.00E-12 1.25E-12 6.22E-17 8.00E-14 2.00E-14 7.95E-17 2.00E-12 5.00E-13 1.77E-14 4.00E-12 1.00E-12
11/11/1991 1.41E-17 J;.OOE-12 1.ZSE-12 2.19E-18 8.00E-14 2.00E-14 2.75E-17 2.00E-12 5.00E-13 1.18E-14 4.00E-12 1.00E-12
2/10/1992 8.12E-17 5.00E-12 1.25E-12 2.35E-17 8.00E-14 2.00E-14 2.76E-18 2.00E-12 5.00E-13 3.57E-14 4.00E-12 1.00E-12
5/11/1992 9.18E-17 5.00E-12 1.25E-12 5.80E-17 8.00E-14 2.00E-14 3.36E-17 2.00E-12 S.OOE-13 1.28E-14 4.00E-12 l.OOE-12
8/10/1992 ~.OOE-18 5.00E-12 1.25E·12 4,19E-17 8.00E-14 2.00E-14 2.00E-18 2.00E-12 5.00E-13 1.59E-14 4.00E-12 1.00E-12
11/9/1992 4.00E-17 5.00E-12 1.ZSE-12 2.68E-17 8.00E-14 2.00E-14 l.07E-17 2.00E-12 S.OOE-13 l.81E-14 4.00E-12 1.00E-12
2/9/1993 7.94E-17 5.00E-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.09E-16 2.00E-12 S.OOE-13 2.69E-14 4.00E-12 1.00E-12
5/10/1993 1_.60E-l7 5.00E-12 1.25E-12 5.07E-17 8.00E-14 2.00E-14 '7.64E-17 2.00E-12 S.OOE-13 l.26E-14 4.00E-12 l.OOE-12
8/10/1993 6.00E-17 5.00E-12 1.25E-12 6.00E-18 8.00E-14 2.00E-14 1.00E-16 '2.00E-12 5.00E-13 1.50E-14 4.00E-12 1.00E-12
Date Effluent 9E-14 uCi/ml BHV-3U Effluent 2E-14 uCi/ml BHV-3T230 Effluent 9E-13 uCi/ml IIHV-3R Effluent GE-13 uCi/ml BHV-3PB
Concentration Concentration Coneentnition Concentration
Umit= limit= Limit= Limit=
ALARAGoal= 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= ~25E-13 uCl/ml ALARA Goal= 1.SE-13 uCi/ml
Pre 1994MPC SE-12 uCi{ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ;zE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
Limit= Limit= Limit= Limit=
Pre 1994 AlARA 1.25E-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC . ~FCA Cone EFC EFCA
11/8/1993 l .00Ec_l6 5.00E-12 l.25E-12 ' 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 2.lOE-14 4.00E-12 1.00E-12
2/7/1994 l.61E-16 5.00E-12 l.25E-12 1.00E-16 8.00E-14 2,00E-14 2.22E-16 2.00E-12 5.00E-13 2.23E-14 4.00E-12 1.00E-12
5/9/1994 2.77E-16 5.00E-12 J..25E-12 2.80E-17 8.00E-14 2.00E-14 8.37E-18 2.00E-12 5.00E-13 1.40E-14 4.00E-12 1.00E-12
8/9/1994 7.39E-17 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 l.14E-16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-12
11/7/1994 9.0SE-17 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-12
2/7/1995 7.99E-17 9.00E-14 2.25E-141 9,60E-17 2.00E-14 5.00E-15 g.60E-17 (l.OOE-13 2.25E-13 9.0SE-15 6.00E-13 1.SOE-13
5/9/1995 9.40E-17 ~.OOE-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 2.00E-14 5.00E-15 4.40E-17 9.00E-13 2.25E-13 1.96E-15 6.00E-13 1.SOE-13
11/11/1995 i3.l6E0 l6 9.00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.SBE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
US/1996 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.SOE-13
5/6/1996 l.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
8/5/1996 3.00E-16 9.00E-14 2.25E-14 J.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
11/6/1996 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.SOE-13
2/6/1997 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.lSE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
S/5/1997 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
8/11/1997 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 l.31E-14 6.00E-13 1.SOE-13
1/5/1998 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.SOE-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 2.2SE-13 2.69E-14 6.00E-13 1.SOE-13
7/31/1998 l.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.SOE-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.SOE-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.SOE-13
3/29/1999 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
7/3/1999 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 1.SOE-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 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 ;2.25E-13 1.91E-14 6.00E-13 1.SOE-13
3/28/2000 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.SOE-13
6/26/2000 l.31E-16 9.00E-14 2.25E-14 l .39E-16 2.00E-14 5.00E-15 1.82E-16 g.OOE,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 l.31E-14 6.00E-13 1.SOE-13
12/26/2000 3.16E-16 l).OOE-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.SOE-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 l .SOE-13
7/2/2001 l.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 l.SOE-13
9/24/2001 :3.00E-16 ll.OOE-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
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.SOE-13
4/1/2002 ~.41E-16 9.00E-14 2.25E-14 2,26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
7/1/2002 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
9/30/2002 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
12/30/2002 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.SOE-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 7.25E-13 2.69E-14 6.00E-13 1.50E-13
6/30/2003 l.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
9/29/2003 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' l.31E-14 6.00E-13 1.SOE-13
12/29/2003 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.SSE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.SOE-13
3/29/2004 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
6/27/2004 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.SOE-13
9/27/2004 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
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 6.00E-13 1.SOE-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.SOE-13
6/29/2005 l.31E-16 9.00E-14 2.25E-14 l.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 l.31E-14 6.00E-13 1.SOE-13
1/3/2006 3.16E-16 9.00E-14 -?.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.SOE-13
Date Effluent 9E-14 uCi/ml BHV-3U Effluent 2E-14 uCi/ml BHV-3T230 Effluent 9E-13 uCi/ml BHV-3R Effluent 6E-13 uCi/ml BHV-3PB
Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit=
ALARAGoal= ~E-14 uCi/ml ALARAGoal = 5E-15 uCi/ml ALARAGoal = ~-25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
Limit= Limit= Limit= limit=
Pre 1994 AlARA 1.ZSE-U uCi/ml Pre 1994 ALARA :SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
' Cone EFC EFCA Cone EFC EFCA Cone EFC I EFCA Cone EFC EFCA
4/3/2006 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/3/2006 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 S.OOE-15 l.82E-16 ,9.00E-13 2.25E-13 l.53E-14 6.00E-13 l.50E-13
10/2/2006 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 l.31E-14 6.00E-13 l.50E-13
1/1/2006 .3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.SBE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.SOE-13
4/2/2007 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.SOE-13
7/2/2007 1.31E-16 9_llOH4 , Z.'!ZS~_l.4° l .39E-16 2.00E-14 S.OOE·lS 1:82,E-16 9'.00_E-E il.25E-13 l.53E-14 6.00E-13 l.SOE-13
9/30/2007 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 l.31E-14 6.00E-13 l.SOE-13
12/31/2007 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.SBE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.SOE-13
3/31/2008 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
6/30/2008 1.31E-16 9.00E-14 2025E-14 1.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 l.SOE-13
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 l.31E-14 6.00E-13 l.SOE-13
12/31/2008 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.SBE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/15/2009 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 l.50E-13
6/15/2009 1.31E-16 9.00E-14 '2.25E-14 l.39E-16 2.00E-14 5.00E-15 .l.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 1.SOE-13
9/15/2009 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 l.50E-13
12/15/2009 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 ~.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 1.SOE-13
3/31/2010 3.41E-16 9.00E-14 2.25E-l4° 2.26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
6/30/2010 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 l.50E-13
9/30/2010 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 l.31E-14 6.00E-13 l.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 l.91E-14 6.00E-13 1.SOE-13
4/4/2011 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
7/4/2011 l.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 l,53E-14 6,00E-13 l.SOE-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 l.31E-14 6.00E-13 l.SOE-13
1/3/2012 '3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6.SBE-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 l.SOE-13
4/3/2012 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 l.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
7/2/2012 l.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 'l.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 l.SOE-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 6.00E-13 l.SOE-13
12/31/2012 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 1.91E-14 6.00E-13 l.50E-13
3/25/2013 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E·l3
7/2/2013 l.31E-16 9.00E-14 2.2SE-14 l.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 l,53E-14 6.00E-13 LSOE-13
9/30/2013 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 l.31E-14 6.00E-13 l.SOE-13
12/30/2013 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 l.SOE·l3
3/31/2014 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 l.SOE-13
6/30/2014 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 l.53E-14 6.00E-13 1.50E-13
9/30/2014 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 l.31E-14 6.00E-13 l.50E-13
12/29/2014 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 l.50E-13
3/30/2015 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
6/29/2015 l.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 l.53E-14 6.00E-13 l.50E-13
9/28/2015 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' L31E-14 6.00E-13 l.SOE-13
12/28/2015 3.16E-16 9.00E-14 2.25E-14 l.31E·16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 1.SOE-13
3/28/2016 3.41E-16 9.00E-14 ~.25E-14 2.26E-16 2.00E-14 5.00E-15 l.lBE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
6/27/2016 l.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5,00E-15 l.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 l.50E-13
9/27/2016 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 l.31E-14 6.00E-13 l.50E-13
12/27/2016 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 L91E-14 6.00E-13 l.50E-13
3/27/2017 3.41E-16 9.00E-14 2.25E-14. 2.26E-16 2.00E-14 5.00E-15 l.lSE-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.SOE-13
6/26/2017 l.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 l.53E-14 6.00E-13 L50E-13
9/25/2017 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 l.SOE-13
12/26/2017 .3.16E-16 9.00E-14 2.25E-14 l.31E-16 2.00E-14 S.OOE-15 6.SBE-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 LSOE-13
Date Effluent-'9H§uef,'ml 1314Vi3U ' Effluent ZE-14 uCi/ml BHV-3TZ30 Effluent 9E;uuG/ml BHV:'3R Effluent 6E-13 uCi/ml BHV-3PB
toncentr.Jtloh Concentration c:::onq:ntmi:1111 Concentration
µm,f =""~ · Limit= Li~t,,:, Limit=
A1:ARA Goar= ~E"14 uO/inl AlARAGoal = ~·-,,_ .:u;. .... ' SE-15 uCi/ml A~G(¥!1= 1,25£-Uua/ml /1,lARAGoal = 1.SE-13 uCi/ml
J>ri·~l~ SE-.UuCi/mf Pre 1994MPC SE-14 uCi/ml Pre ~MltC ~12..0/ml Pre 1994 MPC 4E-12 uCi/ml
i,l~t'= Limit= Uniit~ Limit=
~'.199,il~ ~t:1) J:'°rm1 Pre~~LARA sJ-13 \!c.lfinl Pre 1994 ALARA lE-12 uCi/ml
G(lAI."':: G.OAL.-: GOAL=
£one EEC EfC:A Cone EFC EFCA Cone:·' EEC El'CA Cone EFC EFCA
3/26/2018 1 41E'l~6 !!Jil!'.iE,1.4 ~-19 2.26E-16 2.00E-14 5.00E-15 nsn:-~ ~:CiOf-'e· 2.25,E'-13 2.69E-14 6.00E-13 1.SOE-13
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TAB4
BHV-4 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-4U Effluent 2E-14 uCi/ml BHV-4T230 Effluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ALARAGoal= . lE-15 uCi/ml
Pre 1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre1994 l .ZSE-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 !'lot Applicable
ALARAGOAL= GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 5.20E-15 5.00E-12 1.2SE-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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 4.53E-15 5.00E-12 l.25E-12 l.78E-15 8.00E-14 2.00E-14 2.29E-15 2.00E-12 'S.OOE-13 2.54E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 1.06E-15 5.00E-12 1.25E-12 1.42E-14 8.00E-14 2.00E-14 l.07E-15 2.00E-12 5.00E-13 2.31E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 6.03E-15 5.00E-12 1.2SE-12 l.57E-14 8.00E-14 2.00E-14 2.62E-15 2.00E-12 S.OOE-13 2.25E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable !'lot Applicable
9/27/1982 1.26E-14 5.00E-12 1.25E-12 7.58E-16 8.00E-14 2.00E-14 5.35E-15 7.00E-12 5.00E-13 2.68E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 4.33E-15 .S.OOE-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 1.00E-12 Not Analyzed Not Applicable Not A_pplicable
4/4/1983 l.25E-15 5.00E-12 ;t.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 1.00E-12 Not Analyzed Not A_pplicable Not Applicable
6/30/1983 3.73E-16 S.OOE-12 1.2SE-12 ' 9.43E-16 8.00E-14 2.00E-14 4.13E-16 2.00E-12 5.00E-13 1.20E-14 4.00E-12 l.OOE-12 !'lot Analyzed Not Applicable Not Applicable
10/3/1983 2.54E-16 5.00E-12 l .25E-12 1.SlE-16 8.00E-14 2.00E-14 ;2.65E-16 2.00E-12 5.00E-13 2.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1984 2.76E-15 5.00E-12 1.2SE-12 1.60E-16 8.00E-14 2.00E-14 1.05E-16 2.00E-12 S.OOE-13 l.59E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 4.27E-16 5.00E-12 i.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 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 2.57E-15 5.00E-12 1.25E-12 1.36E-16 8.00E-14 2.00E-14 1.llE-16 2.00E-12 5.00E-13 1.58E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/1/1984 4.18E-16 5.00E-12 1.25E-12 3.54E-16 8.00E-14 2.00E-14 1.lOE-17 2.00E-12 5.00E-13 9.83E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/2/1985 5.30E-17 5.00E-12 1.2SE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 l.OOE-16 5.00E-12 1.25E-12 6.00E-16 8.00E-14 2.00E-14 4.3SE-17 2.00E-12 S.OOE-13 5.02E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/1/1985 9.36E-16 5.00E-12 1.25E-12 2.33E-16 8.00E-14 2.00E-14 l.36E-16 2.00E-12 S.OOE-13 7.48E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 l.46E-15 S.OOE-12 1.2SE-12 7.69E-16 8.00E-14 2.00E-14 S.38E-16 2.00E-12 5.00E-13 7.86E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 8.40E-15 S.OOE-12 1.25E·12 7.60E-16 8.00E-14 2.00E-14 2.99E-16 2.00E-12 5.00E-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 5.79E-15 6.00E-12 1.25E-12 5.80E-16 8.00E-14 2.00E-14 l.34E-15 2.00E-12 5.00E-13 1.33E-14 4.00E-12 1.00E-12 Not Analyzed Not ARplicable Not ARplicable
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 Not Analyzed Not Applicable Not Applicable
10/27/1986 4.60E-15 5.00E-12 1.2SE-12 4.67E-16 8.00E-14 2.00E-14 2.37E-15 2.00E-12 5.00E-13 1.13E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 2.75E-15 S.OOE-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 Not Analyzed Not Applicable Not Applicable
3/16/1987 4.64E-15 5.00E-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1987 4.35E-15 5.00E-12 1.25E-12 l.23E-14 8.00E-14 2.00E-14 1.13E-15 2.00E-12 5.00E-13 2.21E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ~plicable
9/9/1987 6.39E-15 p.OOE-12 l.25E-12 1.SOE-14 8.00E-14 2.00E-14 2.26E-15 2.00E-12 S.OOE-13 1.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable ,Not Applicable
11/2/1987 6.72E-15 5.00E-12 1.25E-12 4.53E-16 8.00E-14 2.00E-14 2.20E-15 2.00E-12 5.00E-13 2.55E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 l.91E-15 5.00E-12 l.2SE·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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 1.78E-14 5.00E-12 l.25E-12 4.39E-14 8.00E-14 2.00E-14 4.92E-16 2.00E-12 5.00E-13 l.38E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 7.SGE-15 5.00E-12 1.25E-12 3.31E-14 8.00E-14 2.00E-14 1.SlE-15 2.00E-12 S.OOE-13 l.97E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 1.47E-14 5.00E-12 1.25E-12 1.56E-15 8.00E-14 2.00E·14 2.57E-15 2.00E-12 S.OOE-13 2.12E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/13/1989 2.47E-15 5.00E-12 l.25E-12 3.14E-15 8.00E-14 2.00E-14 6.94E-16 2.00E-12 5.00E-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not A_p_plicable Not Applicable
5/15/1989 2.SOE-16 S.OOE-12 l.2SE-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 Not Analyzed Not Applicable Not Applicable
8/14/1989 6.SOE-15 5.00E-12 l.2SE-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 Not Analyzed Not Applicable Not Applicable
11/13/1989 9.63E-15 S.OOE-12 · ;t.25E-12 4.05E-15 8.00E-14 2.00E-14 4.03E-15 2.00E-12 5.00E-13 1.99E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 8.92E-15 S.OOE-12 1.2SE-12 3.56E-15 8.00E-14 2.00E-14 2.89E-15 2.00E-12 5.00E-13 2.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 8.90E-15 S.OOE-12 1.25E·12 3.58E-15 8.00E-14 2.00E-14 2.33E-15 2.00E-12 5.00E-13 2.09E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 l.92E-15 5.00E-12 1.25E-12 l.87E-15 8.00E-14 2.00E-14 5.06E-16 2.00E-12 S.OOE-13 8.86E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A_pplicable
11/12/1990 2.91E-15 S.OOE-12 1.2SE-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 1.00E-12 Not Analyzed Not Applicable Not A_pplicable
2/11/1991 l.67E-16 S.OOE-12 · 1.2se-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 Not Analyzed Not Applicable Not Applicable
5/13/1991 1.87E-16 5.00E-12 1.25E-12 2.61E-15 8.00E-14 2.00E-14 3.54E-16 2.00E-12 5.00E-13 1.40E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 4.BSE-16 5.00E-12 1.25E-12 4.38E-16 8.00E-14 2.00E-14 1.27E-16 2.00E-12 5.00E-13 2.20E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 l.77E-16 5.00E-12 1.25E-12 l.46E-16 8.00E-14 2.00E-14 3.76E-17 2.00E-12 5.00E-13 1.15E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 l.83E-16 5.00E-12 1.25E-12 l.95E-15 8.00E-14 2.00E-14 l.33E-16 2.00E-12 5.00E-13 3.35E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/11/1992 4.40E-16 S.OOE-12 1.25E-12 2.56E-16 8.00E-14 2.00E-14 4.04E-16 2.00E-12 5.00E-13 l.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 9.09E-17 5.00E-12 l.25E-12 l.lSE-16 8.00E-14 2.00E-14 4.SOE-17 2.00E-12 5.00E-13 l.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 2.07E·l6 -5.00E-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 3.62E-17 2.00E-12 5.00E-13 2.24E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
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 5.00E-13 3.08E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/10/1993 2.70E-17 S.OOE-12 1.25E-12 2.50E-17 8,00E-14 2.00E-14 8.74E-17 2.00E-12 5.00E-13 1.25E-14 4,00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 9.00E-17 S.OOE-12 l.2SE-12 1. 76E-16 8.00E-14 2.00E-14 O.OOE-+-00 2.00E-12 5.00E-13 l.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/8/1993 1.00E-16 S.OOE-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 6.00E-17 2.00E-12 S.OOE-13 1.75E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A~licable
Date Effluent 9E-14 uCi/ml BHV-4U Effluent 2E-14 uCi/ml BHV-4T230 Effluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4T232
Concentration Concentration Concentration Concentration Concentration
Umlt• Limit= Umlt= Limit= Limit= -
AlARAGoal= 2.ZSE-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre 1994 MPC SE-UuCi/ml Pre 1994MPC SE-14 uCi/ml Pre 1994 MPC 2E-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre1994 MPC Not Applicable
Umit= Limit= Umlt= Limit= Limit=
Pre 1994 l.25E-U uCi/ml Pre 1994 ALARA -SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= GOAL= ALARAGOAL= ALARAGOAL=
-~one EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1994 1.lOE-16 S.OOE-12 1.2SE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/9/1994 3.80E-16 S.OOE-12 1.2SE-12 2.82E-16 8.00E-14 2.00E-14 3.46E-16 2.00E-12 5.00E-13 l.73E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Ap_plicable
8/9/1994 3.SSE-16 5.00E,12 1.25E-12 3.53E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
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 5.00E-13 l.OOE-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
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 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.40E-17 9.00E-14 2.25E-14 2_86E-16 2.00E-14 5.00E-15 1.90E-16 9.00E-13 2.25E-13 2.90E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 1.45E-16 9.00E-14 2.25E-14 2.31E-15 2.00E-14 5.00E-15 7.lOE-17 9.00E-13 ~.25E-13 2.70E-15 6_QQE-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 5.60E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 1.19E-14 9.00E-14 2.25E-14 3.80E-16 2.00E-14 S.OOE-15 6.lOE-15 9.00E-13 ~.25E-13 6.48E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/6/1996 4.SSE-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 Not Analyzed Not Applicable Not Applicable
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.SOE-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 1.36E-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 4.21E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 l.OOE-16 9.00E-14 2.25E-14 l.40E-16 2.00E-14 5.00E-15 1.03E-16 9.00E-13 2.25E-13 6.76E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 1.00E-16 9.00E-14 2.2SE-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 1.50E-13 NotAnal~ed Not Applicable Not Applicable
8/11/1997 4.74E-16 9.00E-14 2.25E-14 9.07E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.55E-15 6.00E-13 l.50E-13 Not Analyzed Not ~pplicable Not Applicable
1/5/1998 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 Not Analyzed Not Applicable Not Applicable
4/28/1998 3.32E-16 9.00E-14 2.25E-14 4.43E-15 2.00E-14 S.OOE-15 .l.21E-16 9.00E-13 2.2SE-13 7.43E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 4.60E-16 9.00E-14 :2.25E-14 9.02E-16 2.00E-14 5.00E-15 3.54E-16 9-00E-13 2.25E-13 6.91E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 4.08E-16 9.00E-14 2.25E-14 4.93E-16 2.00E-14 5.00E-15 2.53E-16 9.00E-13 2.25E-13 4.52E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/1999 5.llE-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 S.90E-16 9.00E-14 2.25E-14 9.89E-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 Not Analyzed Not Applicable Not A~licable
9/27/1999 1.70£-15 9.00E-14 2.25E-14 7.SOE-16 2.00E-14 5.00E-15 4.61E-16 9.00E-13 2.25E-13 7.86E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 2.2SE-13 6.42E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 1.00E-16 9.00E-14 2.25E-14 2.BE-16 2.00E-14 5.00E-15 2.20E·l6 9.00E-13 2.25E-13 5.61E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/26/2000 1.75E-16 9.00E-14 ,2.2SE-14 3.08E-16 2.00E-14 5.00E-15 1.llE-16 9.00E-13 2.25E-13 3.92E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2000 3.65E-16 9.00E-14 2.25E-14 2.0lE-16 2.00E-14 5.00E-15 2.24E-16 9.00E-13 2.25E-13 7.79E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/26/2000 2.27E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 4.35E-16 9.00E-13 2.25E-13 8.45E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 l.45E·l6 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.37E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 1.00E-16 9.00E-14 2.25E-14 1.0SE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.99E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 1.91E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 2.0lE-16 9.00E-13 2.25E-13 8.04E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2001 1.38E-16 9.00E-14 2.25E-14 2.05E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.83E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AJWlicable
4/1/2002 2.20E-16 9.00E-14 2.25E-14 3.38E-16 2.00E-14 5.00E-15 1.26E-16 9.00E-13 2.25E-13 7.48E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 1.97E-16 9.00E-14 2.25E-14 4.lOE-16 2,00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.40E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 2.30E-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.SOE-13 Not Analyzed Not Applicable Not Applicable
12/30/2002 1.00E-16 'l!.OOE-14 2.25E-14 l .92E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.42E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 2.SOE-16 9.00E-14 2.2SE-14 1.69E-16 2.00E-14 5.00E-15 1.29E-16 9.00E-13 2.25E-13 4.55E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/30/2003 1.00E-16 9.00E-14 2.25E-14 2.87E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 4.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/29/2003 1.00E-16 9.00E-14 2.25E-14 8.53E-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 Not Analyzed Not Applicable l",lot Applicable
12/29/2003 1.02E-16 9.00E-14 2.25E-14 1.00E-16 .2.00E-14 5.00E-15 1.49E-15 9.00E-13 Z.25E-13 9.45E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/2004 1.00E-16 9.00E-14 2.2SE-14 l.26E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.00E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 l.OOE-16 9.00E-14 2.25E-14 Z.53E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.23E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-16 9.00E-14 2.25E-14 l.15E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.68E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/27/2004 1.00E-16 9.00E-14 2.25E-14, 2.30E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.37E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 1.00E-16 9.00E-14 2.25E-14 2.66E-16 2.00E-14 5.00E-15 3.lSE-16 9.00E-13 2.25E-13 9.22E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 l.47E-16 9.00E-14 2.25E-1{ 1.45E-15 2.00E-14 5.00E-15 1.42E-16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 7.0lE-16 9.00E-14 2.25E-14 2.06E-16 2.00E-14 5.00E-15 4.80E-16 9.00E-13 2.25E-13 2.12E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/3/2006 4.54E-16 9.00E-14 2.25E-14 1.24E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.60E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2006 ,l.99E-16 9.00E-14 2.25E-14 1.32E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 8.36E-15 6.00E-13 l,50E-13 Not Analyzed Not ~plicable ·Not Applicable
7/3/2006 2.76E-16 9.00E-14 2.25E-14 2.63E-16 2_ooe-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.03E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-4U Effluent ZE-14 uCi/ml BHV-4T230 Effluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4T232
Concentration Concentration Concentration Concentration Concentration
Umlt= limit= Limit= limit= Limit=
ALARA Goal= 2.ZSE-14 uCi/ml AlARAGoal = SE-15 uCi/ml ALARA Goal= 2.ZSE-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml l're 1994 MPC Not Applicable
Limit= limit= limit= limit= Limit=
Pre 1994 1.ZSE-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not,/~-ppRcable
ALARAGOAL: GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
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 l.SOE-13 Not Analyzed Not Applicable Not Apphc-abl,
1/1/2007 6.46E-16 ,. 9.00E-14 2.25E-14 2.81E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 7.0SE-16 9.00E-14 2.25E-14 3.20E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.54E-14 6.00E-13 1.50E-13 Not Anaiyied Not:Applfcab.le Not;Appllcable
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 ;z.25E-13 2.56E-14 6.00E-13 l.50E-13 Not Analyzed Not Ap_plicable Not Applicable
9/30/2007 3.30E-16 9.00E-14 2.25E-14 5.SOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.57E-15 6.00E-13 1.50E-13 Not Analyzed Not Apj)_IJµble Not Appifcabl_e
12/31/2007 1.42E-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 9.93E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2008 l.25E-16 9.00E-14 2.25E-14 7.72E-16 2.00E-14 5.00E-15 ·t.OOE-16 g.OOE-13 2.25E-13 4.09E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2008 l.28E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 3.61E-16 9.00E-13 2.25E-13 1.18E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2008 2.72E-15 9.00E-14 2.25E-14 l.27E-15 2.00E-14 5.00E-15 7.66E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not-Applica.ble
12/31/2008 2.SSE-15 9.00E-14 2.25E-14 1.lOE-15 2.00E-14 5.00E-15 6.56E-16 9.00E-13 2.25E-13 1.38E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap_plicable
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 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 5.67E-17 9.00E-14 2.25E-14 2.17E-16 2.00E-14 5.00E-15 1.SlE-16 9.00E-13 2.25E-13 4.47E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 4.0SE-15 9.00E-14 _2.25E-14 1.45E-15 2.00E-14 S.OOE-15 2.52E-16 9.00E-13 l.25E-13 l.24E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 6.SOE-15 9.00E-14 2.25E-14 3.48E-16 2.00E-14 5.00E-15 1.33E-16 . 9.00E-13 2.25E-13 7.60E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2010 6.0lE-15 9.00E-14 2.25E-14 l.26E-16 2.00E-14 S.OOE-15 1.34E-16 9.00E-13 2.25E-13 l.19E-14 6.00E-13 1.50E-13 Not Analyzed 'Not Applicable Not Applicable
6/30/2010 2.33E-15 9.00E-14 2.25E-14 7.29E-16 2.00E-14 5.00E-15 2.66E-16 9.00E-13 2.25E-13 3.27E-15 6.00E-13 l.50E·13 Not Analyzed Not Applicable Not Applicable
9/30/2010 4.77E-15 9.00E-14 2.25E-14 1.80E-15 2.00E-14 S.OOE-15 8.23E-16 9.00E-13 2.25E-13 5.llE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Nd} ~)>pli_cable
12/31/2010 3.93E-15 9.00E-14 2.25E·14 3.90E-16 2.00E-14 5.00E-15 2.56E-16 9.00E-13 2.25E-13 l.13E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 l.29E-15 9.00E-14 2.25E-14 1.40E-16 2.00E-14 5.00E-15 1.58E-16 9.00E-13 2.25E-13 LllE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Appl{c:~ble
7/4/2011 3.30E-15 9.00E-14 2.25E-14 5.44E-16 2.00E-14 5.00E-15 4.lSE-16 9.00E-13 2.25E-13 8.26E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 l.32E-15 9.00E-14 2.25E-14 7.89E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 2.25E-13 1.lSE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not-ApplJ.cabl!l
1/3/2012 l.04E-15 9.00E-14 2.25E-14 3.25E-16 2.00E-14 5.00E-15 2.28E-16 9.00E-13 2.25E-13 1.l4E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 2.51E-15 9.00E-14 2.25E-14 S.02E-16 2.00E-14 5.00E-15 2.27E-16 9.00E-13 2.25E-13 l.03E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable . Not Applicable
7/2/2012 2.62E-15 9.00E-14 :z:25E.-1'4 1.23E-15 2.00E-14 5.00E-15 2.97E-16 9.00E-13 2..2SE-13-9.27E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 4 .. 0_5E-:-:l5 9.00E-14 ?-:25E·t~ 8.33E-16 2.00E-14 5.00E-15 5:43E-1.6 9.00E-13 2.2~H3 1.21E-14 6.00E-13 l.50E-13 N_ot:Analyze!I. N.otApplltabl.e NotApplicable
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 l.50E-13 Not Analyzed Not Applicable Not A@licable
3/25/2013 3.04E-15 9.00E-14 2.2.5E'14 4.99E-16 2.00E-14 S.OOE-15 2.79E-16 9.00E-13 2.25E-13 2.13E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 2.50E-15 9,00E-14' 2.25E-.l4 3.62E-16 2.00E-14 5.00E-15 2.~E>16 9.00E·13 2.25E-13 4.93E-15 6.00E-13 l.SOE-13 NotAoalv.zed Not Api>ll.ca.ble Not Applicable
9/30/2013 2.98E-15 9.00E-14 2.25E-14 4.49E-16 2.00E-14 S.OOE-15 l.54E-16 9.00E-13 2.25E-13 7.49E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2013 3.SSE-15 9.00E-14 2.25E-14 1.03E-16 2.00E-14 5.00E-15 4.47E-17 9.00E-13 2.25E-13 2.93E-14 6.00E-13 1.50E·13 Not Analyzed Not Applicable lilolAppltcal>le
3/31/2014 4.69E-15 9.00E-14 2.25E-14 1.37E-16 2.00E-14 5.00E-15 3.53E-16 9.00E-13 2.25E-13 1.08E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2014 4.16E-15 9.00E-14 2.25E-14 6.96E-16 2.00E-14 5.00E-15 1.77E-15 9.00E-13 2.25E-13 l.06E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 6.56E-15 9.00E-14 2.25E-14 2.73E-16 2.00E-14 5.00E-15 2.77E-16 9.00E-13 2.25E-13 l.llE-14 6.00E-13 l.SOE-13 1.0lE-17 4:00E-15 '
0 1.00E-15
12/29/2014 2.00E-16 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 1.90E-14 6.00E-13 l.50E-13 l.OOE-17 4.00E-15 l.OOE-15
3/30/2015 5.90E-15 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.80E-14 6.00E-13 1.50E-13 'S.OOE-19 4.00E-15 1.00E-15
6/29/2015 1.SOE-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 l.20E-14 6.00E-13 l.50E-13 l.OOE-17 4.00E-15 l.OOE-15
9/28/2015 5.00E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.50E-13 7.00E-18 4.00E-15 1.00E-15
12/28/2015 4.SOE-16 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 6.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 l.50E-13 8.00E-19 4.00E-15 1.00E-15
3/28/2016 5.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 5.00E-15 5.00E-17 i).OOE-13 2.25E-13 1.70E-14 6.00E-13 l.50E-13 2.00E-18 4.00E-15 -1.00E-15
6/27/2016 2.90E-15 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 8.80E-15 6.00E-13 l.50E-13 5.00E-18 4.00E-15 1.00E-15
9/27/2016 6.20E-15 9.00E-14 2.25E-14 4.40E-16 2.00E-14 S.OOE-15 2.20E-15 9.00E-13 2.25E-13 3.40E-16 6.00E-13 1.50E-13 7.lOE-18 4.00E-15 1,00EilS,
12/27/2016 4.lOE-15 -9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 4.80E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 l.50E-13 4.50E-18 4.00E-15 t.OOE-15
3/27/2017 2.60E-15 9.00E-14 2.25E-14 3.00E-17 2.00E-14 S.OOE-15 3.00E-17 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-13 1.00E-18 4.00E-15 l.OOE-15
6/26/2017 2.00E-16 9.00E-14 -;2.25E-14 9.00E-17 2.00E-14 5.00E-15 8.00E-17 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 l.OOE-15
9/25/2017 2.50E-15 '9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 l .60E-14 6.00E-13 1.50E-13 4,00E-18 4.00E-15 l.OOE-15
12/26/2017 l.OOE-14 9.00E-14 2.25E-14 2.00E-16 2.00E-14 S.OOE-15 2.00E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 l.SOE-13 2.00E-17 /I.OOE-15 1.00E-15
3/26/2018 6.SOE-16 9.00E-14 2.25E-14 l.ZOE-16 2.00E-14 5.00E-15 5.70E-17 9.00E-13 2.25E-13 l .40E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
6/25/2018 l.50E-15 9.00E-14 2.25E-14 8.20E-17 2.00E-14 5.00E-15 3.70E-17 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 1.50E-13 1.20E-17 4.00E-15 1.00E-15
Date Effluent 9E-14 uCi/ml BHV-4U Effluent 2E-14 uCi/ml 8HV-4T230 Effluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4T232
(:oncentration Concentration Concentration Concentration Concentration
Umit= Limit= Limit= Limit= Limit=
ALARAGoal= Z.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml AlARAGoal = lE-15 uCi/ml
Pre1994MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre1994MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Umit= Limit= Limit= Limit= Limit=
Pre1994 1.25E-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC UCA
9/24/2018 2.20E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 1.00E-15
12/31/2018 3.40E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 6.00E-18 4.00E-15 1.00E-15
4/1/2019 1.ooe=16 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5.00E-15 8.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.SOE-13 II.OOE-18 4.00E-15 l.OOE-15
7/1/2019 6.00E-17 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 1.00E-15
9/30/2019 ;L.OOE-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 9.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 1.00E-15
1/6/2020 f.OOE-17 9.00E-14 2.25E-14 6.00E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 9.00E-15 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 1.00E-15
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TABS
BHV-5 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-SU Effluent ZE-14 uCi/ml BHV-STZ30 Effluent 9E-13 uCi/ml BHV-SR Effluent 6E-13 uCi/ml BHV-SPB Effluent 4e-15 uCi/ml BHV-STZ3Z
Concentration Concentration Concentration Concentration Concentration
Umit: Limit= Limit: Limit= Limit:
AlARAGoal: Z.25E-14 uCi/ml. ALARA Goal= 5E-15 uCi/ml AlARAGoal: Z.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml AlARAGoal: lE-15 uCi/ml
Pre1994MPC SE-12 uCi/rnJ Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC Not Applicable
Umlts Limit= Limit: Limit= Limit:
Pre 1994 l.ZSE-U uCi/ml Pre 1994 SE-13 uCi/ml pre 1994 ALARA lE-12 uCi/ml Pre 1994 l"ot Applicable
/\LARA GOAL : AlARAGOAL: GOAL= ALARAGOAL:
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 2.44E-15 5.00E-12 1.25E-12 l.53E-15 8.00E-14 2.00E-14 7.54E-16 2.00E-12 S.OOE-13 1.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 4.84E-15 5.00E-12 1.25E-12 2.78E-15 8.00E-14 2.00E-14 l.84E-15 2.00E-12 5.00E-13 1.53E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 1.04E-15 S.OOE-12 1.25E-12 2.62E-15 8.00E-14 2.00E-14 1.11E-15 2.00E-12 5.00E-13 2.98E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 3.61E-15 5.00E-12 1.25E·l2 7.61E-15 8.00E-14 2.00E-14 1.39E-15 2.00E-12 S.OOE-13 1.SOE-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/27/1982 1.71E-14 5.00E-12 1.25E-12 9.46E-15 8.00E-14 2.00E-14 3.80E-15 2.00E-12 5.00E-13 2.35E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 1.90E-14 5.00E-12 1.25E-12 5.77E·15 8.00E-14 2.00E-14 9.34E-17 2.00E-12 5.00E-13 4.32E·l4 4.00E-12 l.OOE-12 Not Analyzed Not A_pplicable Not Applicable
4/4/1983 5.00E-12 1.2SE·12 2.33E·l5 8.00E-14 2.00E-14 5.93E-16 2.00E-12 .5.00E-13 3.0lE-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 7.62E-16 5.00E-12 1.25E-12 3.25E-15 8.00E-14 2.00E-14 6.28E-15 2.00E-12 5.00E-13 2.69E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/3/1983 4.86E-16 5.00E-12 1.25E-12 1.lOE-15 8.00E-14 2.00E-14 3.63E-16 2.00E-12 5.00E-13 2.08E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1984 6.96E-15 . 5.00E-12 1.25E-12 9.69E-16 8.00E-14 2.00E-14 9.60E-16 2.00E-12 5.00E-13 1.83E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 1.64E-15 5.00E-12 1.25E-12 1.34E-15 8.00E-14 2.00E-14 3.SSE-15 2.00E-12 5.00E-13 4.67E-14 4.00E-12 l.OOE-12 Not Analyzed Not ~plicable Not Applicable
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·l4 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/1/1984 l.llE-15 S.OOE-12 1.25E-12-3.13E-16 8.00E-14 2.00E-14 4.21E-16 2.00E-12 5.00E-13 1.57E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
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 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 2.36E-16 5.00E-12 l.2SE·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 Not Analyzed Not Applicable Not Applicable
7/1/1985 7.58E-16 5.00E-12 l.25E-12 4.00E-16 8.00E-14 2.00E-14 6.90E-16 .2.00E-12 5.00E-13 2.lSE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 7.47E-15 5.00E-12 1.25E-12 l.16E-15 8.00E-14 2.00E-14 2.19E-15 2.00E-12 5.00E-13 9.20E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
-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 5.00E-13 l .13E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 2.99E·14 5.00E-12 1.ZSE-12 7.64E·l5 8.00E-14 2.00E-14 1.SlE-14 2.00E-12 5.00E-13 2.22E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 2.23E-14 5.00E-12 1.25E-12 5.19E-15 8.00E-14 2.00E-14 1.0SE-14 .2.00E-12 5.00E-13 2.16E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 2.33E-14 5.00E-12 l.ZSE-12 7.78E·l5 8.00E-14 2.00E-14 1.60E-14 .2.00E-12 5.00E-13 2.02E-14 4.00E-12 l.OOE-12 Not Analyzed Not AJ!Plicable Not Aru,licable
12/15/1986 3.40E-14 5.00E-12 l.25E-12 5.35E-15 8.00E-14 2.00E-14 1.47E-14 2.00E-12 5.00E-13 2.82E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 2.06E-14 5.00E-12 l.ZSE-12 4.SOE-15 8.00E-14 2.00E-14 6.74E-15 2.00E-12 5.00E-13 7.29E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable .Not Applicable
5/11/1987 2.SOE-14 5.00E-12 1.ZSE-12 8.54E-15 8.00E-14 2.00E-14 8.lSE-15 2.00E-12 5.00E-13 3.28E·l4 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/9/1987 i .65E-14 5.00E-12 1.25E-12 6.62E-15 8.00E-14 2.00E-14 9.34E-15 iz.OOE-12 5.00E-13 2.77E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/2/1987 l .SOE-14 5.00E-12 1.25E-12 7.09E-1S 8.00E-14 2.00E-14 7.20E-15 2.00E-12 5.00E-13 1.77E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 ~.OlE-14 5.00E-12 1.25E-12 2.98E-15 8.00E-14 2.00E-14 3.93E-15 2.00E-12 5.00E-13 3.36E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 1.78E-14 5.00E-12 1.25E-12 8.14E-15 8.00E-14 2.00E-14 7.43E-15 2.00E-12 5.00E-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 '1.79E-14 5.00E-12 1.25E-12 1.49E-14 8.00E-14 .2.00E-14 5.34E-15 2.00E-12 5.00E-13 2.45E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 4.46E-14 5.00E-12 1.25E-12 1.39E-14 8.00E-14 2.00E-14 l.17E-14 2.00E-12 5.00E-13 3.43E-14 4.00E-12 1.00E-12 Not Analyzed Not ARplicable Not Applicable
2/13/1989 l.67E-14 5.00E-12 l.25E·l2 S.54E-15 8.00E-14 2.00E-14 7.20E-15 2.00E-12 5.00E-13 5.02E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 2.03E-14 5.00E-12 1.25E-12 7.0SE-15 8.00E-14 2.00E-14 9.56E-16 2.00E-12 5.00E-13 1.43E·l4 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 2.SlE-15 5.00E-12 1.25E-12 3.78E-15 8.00E-14 2.00E-14 9.26E-15 2.00E-12 5.00E-13 1.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/13/1989 5.38E-14 5.00E-12 1.25E-12 8.0lE-15 8.00E-14 2.00E-14 1.SlE-14 2.00E-12 5.00E-13 4.09E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 4.48E-14 5.00E-12 :1.25E-12 1.48E-14 8.00E-14 2.00E-14 1.28E-14 2.00E-12 5.00E-13 3.88E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 2.lSE-14 5.00E-12 :1.ZSE-12 1.70E-14 8.00E-14 2.00E-14 l.59E-14 2.00E-12 5.00E-13 3.49E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 9.53E-15 5.00E-12 1.ZSE-12 1.70E-14 8.00E-14 2.00E-14 3.27E-15 2.00E-12 5.00E-13 1.27E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 1.llE-14 5.00E-12 'l.2SE·12 5.27E-15 8.00E-14 2.00E-14 5.38E-15 2.00E-12 5.00E-13 l.56E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/11/1991 6.35E-16 s.ooe-12 ' 1.25E-12 3.13E-16 S.OOE-14 2.00E-14 2.31E-16 2.00E-12 5.00E-13 '3,89E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 1.22E-15 5.00E-12 l.25E-12 6.14E·l5 8.00E-14 2.00E-14 4.41E-15 2.00E-12 5.00E-13 2.SOE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 7.84E-16 5.00E-12 1.25E-12 l.43E-15 8.00E-14 2.00E-14 4.47E-16 2.00E-12 5.00E-13 1.84E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 5.37E-16 5.00E-12 l.25E-12 4.20E-16 8.00E-14 2.00E-14 1.37E-16 2.00E-12 5.00E-13 l .27E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 3.54E-16 5.00E-12 l.25E-12 l.18E-16 8.00E-14 2.00E-14 4.08E-17 2.00E-12 ·s.OOE-13 .3.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1992 ~.71E-16 5.00E-12 . 1.25E-12 9.58E-16 8.00E-14 2.00E-14 8.31E-17 2.00E-12 5.00E-13 1.43E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 5.32E-15 5.00E-12 1.25E-12 3.36E-16 8.00E-14 2.00E-14 1.65E-16 2.00E-12 5.00E-13 1.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 3.66E-16_ 5.00E-12 l.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 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.0SE-16 5.00E-12 l.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 NotAna\}'zed Not Applicable Not Applicable
5/10/1993 ~.SOE-16 5.00E-12 1.ZSE-12 8.25E-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 5.00E-13 l.83E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 8.30E-16 5.00E-12 l.25E-12 1.90E-16 8.00E-14 2.00E-14 2.lOE-16 2.00E-12 6.00E-13 l .70E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-SU Effluent 2E-14 uCi/ml BHV-5T230 Effluent 9E-13 uCi/ml BHV-SR Effluent 6E-13 uCi/ml BHV-SPB Effluent 4e-15 uCi/ml BHV-5TZ32
Concentration Concentration Concentration Concentration Concentration
limit= limit= limit= limit= Limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARAGoal = 6E-15 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ALARAGoal = lE-lSuCl/ml -
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-1Z uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= limit= Limit= Limit=
Pre 1994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
/',LARA GOAL= ALARAGOAL= GOAL= ALARAGOAL=
Cone ~FC EFCA Cone EFC EFCA Cone EFC EFCA "Cone EFC EFCA Cone EFC EFCA
11/8/1993 2.70E-16 '. 6.00E-12 1.25E-12 8.00E-17 8.00E-14 2.00E-14 7.00E-17 2.00E-12 5.00E-13 2.34E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1994 3.18E-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 r ooe-14 5.18E-16 ;!.OOE-12 5.00E-13 3.64E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/9/1994 1.SOE-15 5.00E-12 1.25E-12 9.78E-16 8.00E-14 2.00E-14 1.lOE-15 2.00E-12 5.00E-13 8.30E-15 4.00E-12 1.00E-12 'Not Analyzed Not Applicable Not Applicable
8/9/1994 2.67E-15 5.00E-12 1.25E-12 1.llE-15 8.00E-14 2.00E-14 4.95E-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 9.21E-17 5.00E-12 1.25E-12 1.59E-15 8.00E-14 2.00E-14 1.66E-15 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable • Not Applicable
2/7/1995 l.51E-15 9.00E-14 2.25E-14 9.SOE-16 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 9.35E-15 6.00E-13 'l.SOE-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 2.21E-16 9.00E-14 2.25E-14' 8.56E-16 2.00E-14 5.00E-15 3.06E-15 9.00E-13 2.25E-13 4.34E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 1.66E-16 9.00E-14 2.25E-14 1.67E-15 2.00E-14 5.00E-15 3.90E-15 9.00E-13 2.25E-13 5.60E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not A11plicable
11/11/1995 2.04E-14 9.00E-14 ' 2.25E-14 6.70E·15 2.00E-14 5.00E-15 7.65E-15 9.00E-13 2.25E-13 4.47E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap_plicable
2/5/1996 4.50E-14 9.00E-14 2.25E-14 3.58E-14 2.00E-14 5.00E-15 2.39E-14 9.00E-13 2.25E-13 7.30E-15 6.00E-13 1.SOE-13 Not Analyzed Not A_i:>plicable Not Applicable
5/6/1996 1.76E·15 9.00E-14 '2.25E-14 3.57E-15 2.00E-14 5.00E-15 9.55E-16 9.00E-13 2.25E-13 7.54E-15 6.00E-13 l .50E-13 Not Analyzed Not Appllcabfe, Not Applicable
8/5/1996 2.37E-15 9.00E-14 2.25E-14 8.18E-15 2.00E-14 5.00E-15 7.46E-16 9.00E-13 2.25E-13 5.75E-15 6.00E-13 1.50E-13 Not Analyzed Noi Applrcable Not Applicable
11/6/1996 3.53E-15 9.00E-14 2.25E-14 5.31E-15 2.00E-14 5.00E-15 9.39E-16 9.00E-13 2.25E-13 L21E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 1.84E-16 9.00E-14 2.25E-14 2.0lE-16 2.00E-14 5.00E-15 1.87E-16 9.00E-13 2.25E-13 6.14E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 5.75E-16 9.00E-14 2.25E-14 7.24E·16 2.00E-14 5.00E-15 6.07E-16 9.00E-13 2.25E-13 4.75E·15 6.00E-13 1.50E-13 Not Analyzed Not ApplTc:,,ble Not Applicable
8/11/1997 1.21E-15 9.00E-14 2.25E-14 7.39E-16 2.00E-14 5.00E-15 5.05E·16 9.00E-13 2.25E-13 4.92E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable' Not Applicable
1/5/1998 9.89E-16 9.00E-14 2.25E-14 l.92E-15 2.00E-14 S.OOE-15 6.21E-16 9.00E-13 2.25E-13 4.68E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not ApJ>licable
4/28/1998 2.84E-15 9.00E-14 2.25E-14 2.38E·15 2.00E-14 5.00E-15 '1.72E-15 9.00E-13 2.25E-13 7.35E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not AJ!.plicable
7/31/1998 7.49E-16 9.00E-14 2.25E-14 1.49E-15 2.00E-14 S.OOE-15 8.34E·16 9.00E-13 2.25E-13 7.0lE-15 6.00E-13 1.50E-13 Not Analyzed Not l\i:>Plicable Not Applicable
9/28/1998 1.07E-15 ,9.00E-14 2.25E-14 9.20E-16 2.00E-14 5.00E-15 6.32E-16 9.00E-13 2.25E-13 3.95E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
3/29/1999 3.75E-15 ,9.00E-14 2.25E-14 2.45E-15 2.00E-14 5,00E-15 2.39E-15 9.00E-13 2.25E-13 8.46E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 1.53E-15 9.00E-14 i.25E-14 8.65E·l6 2.00E-14 5.00E-15 6.52E-16 9.00E-13 2.25E-13 7.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/27/1999 5.83E-15 9.00E-14 2.25E-14 3.52E-15 2.00E-14 5.00E-15 2.55E-15 9.00E-13 2.25E-13 8.22E·15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
12/28/1999 9.48.E."'15 9.00E-14 2.25E-14 6.20E-15 2.00E-14 5.00E-15 3.96E-15 9.00E-13 2.25E-13 7.56E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap_plicable Not Applicable
3/27/2000 02.06E-15 9.00E-14 2.25E-14 1.27E-15 2.00E-14 5.00E-15 1.09E-15 9.00E-13 2.25E-13 7.72E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/26/2000 1.50E-15 9.00E-14 2.25E-14 1.24E-15 2.00E-14 5.00E-15 1.0lE-15 9.00E-13 2.25E-13 4.36E-15 6.00E-13 1.50E-13 ['lot Analyzed Not Applicable Not Applicable
9/26/2000 1.04E-15 9.00E-14 2.25E-14 5.45E-16 2.00E-14 5.00E-15 6.0lE-16 9.00E-13 2.25E-13 7.67E-15 6.00E-13 1.50E-13 !"lot Analyzed Not Applicable Not J\pplicable
12/26/2000 1.48E-15 9.00E-14 2.25E-14 7.56E-16 2.00E-14 5.00E-15 6.84E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
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 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 4.52E-16 9.00E-14 2.25E-14 4.02E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.48E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 4.6SE-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 l .50E-13 Not Analyzed Not Applicable Not Applicable
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.SOE-13 Not Analyzed Not Applicable Not AJ>plicable
4/1/2002 1.26E-15 9.00E-14 2.25E-14 7.53E-16 2.00E-14 S.OOE-15 7.19E-16 9.00E-13 2.25E-13 9.65E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Appl[cabli!
7/1/2002 1.02E-15 9.00E-14 2.25E-14 l.03E-15 2.00E-14 5.00E-15 3.39E-16 9.00E-13 2.25E-13 7.20E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 S.82E-16 9.00E-14 2.25E-14 9,28E-16 2.00E-14 5.00E-15 3.14E-16 9.00E-13 2.25E-13 4.48E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2002 1.00E-16 9.00E-14 2.25E-14 7.67E·16 2.00E-14 5.00E-15 3.48E-16 9.00E-13 2.25E-13 9.56E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 1.13E-15 9.00E-14 2.25E-14 7.41E-16 2.00E-14 5.00E-15 4.41E-16 9.00E-13 2.25E-13 6.68E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/30/200B 4.35E-16 9.00E-14 2.25E-14 5.0SE-16 2.00E-14 5.00E-15 2.SlE-16 9.00E-13 2.25E-13 1.34E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/29/2003 1.SlE-16 9.00E-14 2.25E-14 1.02E·l6 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.28E·l5 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 1.52E-16 9.00E-14 2.25E-14 1.54E-16 2.00E-14 5.00E-15 1.SlE-16 9.00E-13 2.25E-13 7.02E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/29/2004 1.00E-16 9.00E-14 2.25E-14 l.12E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 8.82E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.18E-16 9.00E-14 2.25E-14 3.llE-16 2.00E-14 5.00E-15 1.25E-16 9.00E-13 2.25E-13 2.47E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.16E·16 9.00E-14 2.25E-14 1.72E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l .SOE-13 Not Analyzed Not Applicable Not Ap_plicable
12/27/2004 1.14E-16 9.00E-14 2.25E-14 1.06E·16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.59E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 1.00E-16 9.00E-14 2.25E-14 2.04E-16 2.00E-14 5.00E-15 1.83E-16 9.00E-13 2.25E-13 8.57E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 1.83E-16 9.00E-14 2.25E-14 3.81E-16 2.00E-14 5.00E-15 3.09E-16 9.00E-13 2.25E-13 1.06E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
1/3/2006 $.74E-16 9.00E-14 2.25E-14 3.79E-16 2.00E-14 5.00E-15 l.31E-16 9.00E-13 2.25E-13 4.32E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-SU Effluent ZE-14 uCi/ml BHV-5TZ30 Effluent 9E-13 uCi/ml BHV-SR Effluent 6E-13 uCi/ml BHV-SPB ~ffluent 4e-15 uCi/ml BHV-STZ32
Concentration Concentration Concentration Concentration Concentration
Umit= Limit= Limit= Limit= limit=
ALARA Goal = . 2.ZSE-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal = 2.ZSE-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Prel994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml pre1994MPC ~E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
limit= Limit= limit= Limit= Limit=
Pre 1994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
"'IARAGOAl= ALARAGOAL= GOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
4/3/2006 S.ZZE-16 9.00E-14 2.ZSE-14 6.66E-16 2.00E-14 5.00E-15 1.llE-16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/3/2006 3.0SE-16 9.00E-14 2.25E-14 1.lOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.25E-14 6.00E-13 1.SOE-13 Not Analyzed Not Ap_plicable Not Applicable
10/2/2006 9.14E-16 9.00E-14 2.ZSE-14 4.95E-16 2.00E-14 5.00E-15 1.86E-16 9.00E-13 2.25E-13 1.67E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable . Not Applicable
1/1/2007 9.49E-16 9.00E-14 2.25E-14 6.81E-16 2.00E-14 5.00E-15 2.02E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 l.64E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 1.54E-15 9.00E-14 2.25E-14 8.16E-16 2.00E-14 S.OOE-15 4.76E-16 9.00E-13 2.ZSE-13 2.12E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2007 4.90E-16 9.00E-14 2.ZSE-14 2.37E-16 2.00E-14 5.00E-15 1.00E-16 .9.00E-13 2.25E-13 6.65E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Appl,leable
12/31/2007 1.46E-15 9.00E-14 2.ZSE-14 5.67E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.02E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable !\lot Applicable
3/31/2008 3.16E-16 9.00E-14 2.ZSE-14 6.17E-16 2.00E-14 5.00E-15 3.71E-16 9.00E-13 2.ZSE-13 4.82E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable (':lot Applicable
6/30/2008 3.13E-15 9.00E-14 2.25E-14 l.SSE-15 2.00E-14 5.00E-15 9.27E-16 9.00E-13 2.25E-13 7.40E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2008 7.08E-15 9.00E-14 2.25E-14 3.41E-15 2.00E-14 5.00E-15 2.52E-15 9.00E-13 2.25E-13 1.lSE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Ap_plicable
12/31/2008 7.22E-15 9.00E-14 2.25E-14 2.82E-15 2.00E-14 5.00E-15 3.03E-15 9.00E-13 2.25E-13 l.59E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 4.13E-15 9.00E-14 2.25E-14 l.39E-15 2.00E-14 5.00E-15 1.41E-15 9.00E-13 2.ZSE-13 4.66E-15 6.00E-13 l.SOE-13 Not Analyzed ,Not Applicable N(!t Appl)cab)_e'
6/15/2009 2.31E-16 9.00E-14 . 2.25E-14 7.79E-16 2.00E-14 5.00E-15 6.37E-16 9.00E-13 2.25E-13 4.18E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 3.lOE-15 9.00E-14 2.25M4 9.ZOE-16 2.00E-14 5.00E-15 6.36E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 5.77E-15 9.00E-14 2.25E-14 3.13E-16 2.00E-14 5.00E-15 1.92E-16 9.00E-13 ,Z.25E-13 2.48E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2010 4.78E-15 9.00E-14 2.ZSE-14 3.73E-16 2.00E-14 5.00E-15 4.19E-16 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2010 4.35E-15 9.00E-14 2.ZSE-14 7.84E-16 2.00E-14 5.00E-15 1.0SE-15 9.00E-13 2.25E-13 4.40E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2010 3.57E-15 .9.00E-14 2.25E-14 l.14E-15 2.00E-14 S.OOE-15 7.97E-16 9.00E-13 2.ZSE-13 3.78E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2010 8.52E-15 9.00E-14 2.25E-14 1.45E-15 2.00E-14 S.OOE-15 l.29E-15 9.00E-13 2.25E-13 1.33E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 3.20E-15 9.00E-14 2.25E-14 8.89E-16 2.00E-14 5.00E-15 1.lOE-15 9.00E-13 2.25E-13 1.48E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 6.98:E'lS 9'.00E-1.4 2.2SE-l.4 2.03E-15 2.00E-14 S.OOE-15 Z..52E·.1S· 9.00E•l3 2 •. 25E-1'3 1.08E-14 6.00E-13 l.SOE-13 Not Analyzed NotAppUcab_le Not Applicable
10/3/2011 3.llE-15 9.00E-14 2.25E-14 1.14E-15 2.00E-14 S.OOE-15 5.75E-16 9.00E-13 2.25E-13 1.41E-14 6.00E-13 1.50E-13 Not Analyzed lllot Applicable Not Applicable
1/3/2012 4.44E-15 9.00E-14 ;2.25E-14 2.14E-15 2.00E-14 5.00E-15 1.53E-15 9.00E-13 2.25E-13 2.05E-14 6.00E-13 l.50E-13 Not Analyzed No.tApplfi:~jlle Not Applicable
4/3/20rl ?.52E-15 9.00E-14 2.25E-14 3.24E-15 2.00E-14 5.00E-15 1.79E-15 9.00E-13 2.ZSE-13 l.SSE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2012 5.87E-15 9.00E-14 .2.ZSE-14 3.06E-15 2.00E-14 5.00E-15 1.21E-15 9.00E-13 2.25E-13 l.llE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 6.73E-15 9.00E-14 2.25E-14 2.59E-15 2.00E-14 5.00E-15 2.43E-15 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 4.SOE-15 9.00E-14 2.25E-14 l.62E-15 2.00E-14 5.00E-15 1.79E-15 9.00E-13 2.ZSE-13 l.74E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 6.66[-15 9.00E-14 2.25E-14 1.48E-15 2.00E-14 5.00E-15 l.12E-15 9.00E-13 2.25E-13 1.80E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 7.35E-15 9.00E-14 2.25E-14 l.72E-15 2.00E-14 5.00E-15 2.02E-15 9.00E-13 2.25E-13 6.67E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap_plicable
9/30/2013 2.78E-15 9.00E-14 2.25E-14 6.92E-16 2.00E-14 S.OOE-15 3.29E-16 9.00E-13 2.25E-13 6.62E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Al!Plicable
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 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.50E-13 Not Analyzed Not Ap_plicable Not Applicable
6/30/2014 8.18E-15 9.00E-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 l.50E·13 Not Analyzed Not Applicable Not Applicable
9/30/2014 1.32E-14 9.00E-14 2.ZSE-14 7.76E-16 2.00E-14 5.00E-15 l.04E-15 9.00E-13 2.25E-13 1.23E-14 6.00E-13 l.SOE-13 4.66E-17 4.00E-15 1.00E-15
12/29/2014 8.00E-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 8.00E-18 4.00E-15 l.OOE-15
3/30/2015 l.OOE-14 9.00E-14 2.25E-14 5.00E-16 2.00E-14 5.00E-15 2.lOE-15 9.00E-13 2.25E-13 3.lOE-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 .1.00E-15
6/2!J/201S 4.60E·15 9.00E-14 2.ZSE-14 8.00E-16 2.00E-14 5.00E-15 3.70E-15 9.00E-13 2.2SE·13 1.40E-14 6.00E-13 1.SOE-13 2.00E-17 4.00E-15 1.00E-15
9/28/2015 1.ZOE-14 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 9.80E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 1.00E-15
12/28/2015 7.40E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.90E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 l.50E-13 2.00E-17 4.00E-15 1.00E-15
3/28/2016 l .40E-15 9.00E-14 2.25E-14 6.00E-16 2.00E-14 5.00E-15 6.ZOE-15 9.00E-13 2.ZSE-13 2.30E-14 6.00E-13 1.SOE-13 6.00E-17 4.00E-15 1.00E-15
6/27/2016 3.90E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 6.00E-16 9.00E-13 2.25E-13 1.50E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15
9/27/2016 7.lOE-15 9.00E-14 2.25E-14 7.60E-16 2.00E-14 5.00E-15 1.lOE-15 9.00E-13 2.25E-13 2.90E-16 6.00E-13 1.50E-13 3.00E-17 4.00E-15 1.00E-15
12/27/2016 5.lOE-15 9.00E-14 2.25E-14 6.60E-16 2.00E-14 5.00E-15 9.60E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.SOE-13 1.30E-17 4.00E-15 1.00E-15
3/27/2017 7.80E-15 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 2.lOE-15 9.00E-13 2.25E-13 l.SOE-14 6.00E-13 1.50E-13 2.00E-17 4.00E-15 · l:OJ)E:15
6/26/2017 8.00E-16 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.50E-13 6.00E-18 4.00E-15 l.OOE-15
9/25/2017 2.70E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
12/26/201J l.40E-14 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.ZSE-13 l.60E-14 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 1.00E-15
3/26/2018 7.lOE-16 9.00E-14 2.25E-14 1.70E-16 2.00E-14 5.00E-15 1.SOE-16 , 9.00E-13 2.25E-13 1.40E-14 6.00E-13 1.50E-13 2.00E-17 4.00E-15 1.00E-15
-Date Effluent 9E-14 uCi/ml BHV-SU Effluent 2E-14 uCi/ml BHV-5T230 Effluent 9E-13 uCi/ml BHV-SR Effluent 6E-13 uCi/ml BHV-SPB Effluent 4e-15 uCi/ml BHV-ST232
Concentration Concentration Concentration Concentration Concentration
µmit= limit= Limit= Limit= Limit=
ALARAGoal: 2.25E-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre1994MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
j.lmit= Limit= Limit= Limit= Limit=
Pre1994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL: ALARAGOAL= GOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
6/25/2018 2.60E-15 9.00E-14 2.25E-14 2.40E-16 2.00E-14 5.00E-15 5.90E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.SOE-13 9.40E-18 4.00E-15 l.OOE-15
9/24/2018 2.20E-15 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 '2.25E-13 1.00E-14 6.00E-13 l.SOE-13 8.00E-18 4.00E-15 1.00E-15
12/31/2018 6.00E-15 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 l.SOE-13 9.00E,18 4.00E-15 1.00E-15
4/1/2019 2.00E-16 9.00E-14 2.2SE-14 l.OOE-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 '2.25E-13 2.00E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 1.00E-15
7/1/2019 2.00E-16 9.00E'14 2.25E-14 7.00E-16 2.00E-14 5.00E-15 5.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
9/30/2019 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 6.00E-16 9.00E-13 l.25E-13 9.00E-15 6.00E-13 l.SOE-13 6.00E-18 4.00E-15 1.00E-15
1/6/2020 /I.OOE-16 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 l.SOE-13 7.00E-18 4.00E-15 1.00E-15
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TAB6
BHV-6 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent-9E-14 uCi/ml BHV-6U Effluent ZE-14 uCi/ml BHV-6T230 Effluent 9E-13 uCi/ml BHV-6R Effluent 6E-13 uCi/ml l)HV-6PB Effluent 4e-15 uCi/ml BHV-6T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= limit= Limit=
AlARA Goal = : ~.ZSE-14 uCi/ml ' AlARA Goal = 5E-13 uCi/ml AlARAGoal= 2.ZSE-13 uCi/ml AlARA Goal= 1.SE-13 uCi/ml AlARAGoal = lE-15 uCi/ml
Pre1994MPC SE-12 uCi{ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= limit= Limit=
Pre 1994 l.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
AlARAGOAL= AlARAGOAL: ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 ,2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 S.OOE-12 1.ZSE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 5.00E-12 1.ZSE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 5.00E-12 1.ZSE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
9/27/1982 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 I 5.00E-12 1.25E-12. 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/3/1983 5.00E-12 1.ZSE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not A_pplicable Not Applicable
1/3/1984 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/1/1984 5.00E-12 l.25E-12 8,00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not.Applicable
1/2/1985 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
7/1/1985 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4,00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 S.OOE-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 5.00E-12 1.25E-12 8.00E-14 2.00E-14 . 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A~licable
10/27/1986 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 -2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Ana!Yzed Not Applicable Not Applicable
12/15/1986 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 5.00E-12 1.25E·12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1987 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/9/1987 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/2/1987 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 5.00E-12 l .25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 S.OOE-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 S.OOE-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/13/1989 5.00E-12 . l .25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 S.OOE-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8)14/1989 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/13/1989 ?,OOE-12 1.2SE-12 8.00E-14 2,00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 s.ooE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 -S.OOE-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/11/1991 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 6.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 S.OOE-12 1.ZSE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 . 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 No"t Analyzed Not Applicable Not Applicable
5/11/1992 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 ·s.OOE-13 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 -5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not l\pplicable Not A~plicable
5/10/1993 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 ,· 5.00E-12 1.2SE-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-6U Effluent ZE-14 uCi/ml BHV-6TZ30 Effluent 9E-13 uCi/ml BHV-6R ~ffluent 6E-13 uCi/ml BHV-6PB Effluent 4e-15 uCi/ml BHV-6T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
ALARAGoal= 2.25E-14 uCi/ml ALARA Goal= SE-13 uCi/ml .ALARA Goal = 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml AlARAGoal= lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre 1994 1.25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL: ALARAGOAL=
Cone EFC EFCA Cone EFC ~FCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
11/8/1993 5.00E-12 1.25E-12 8.00E-14 2.00E-14 Z.OOE-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1994 5.00E-12 1.25E-12 8.00E-14 2.00E·14 2.00E-12 5.00E-13 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
5/9/1994 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/9/1994 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1995 9.00E-14 2.25E-14 2.00E-14 S.OOE-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.00E-14 2.25E-14_ 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 9.00E-14 2.25E·14 l.OOE-14 5.00E-15 9.00E-13 2.25E-13 -6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap_plicable
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·l3 Not Analyzed Not Applicable Not Applicable
2/5/1996 9.00E-14 2.ZSE-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
5/6/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
8/5/1996 9.00E-14 2.2SE-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 -9.00E-14 2.25E·14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 9.00E-14 2.2SE-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not· Applicable
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.SOE-13 Not Analyzed Not Applicable N_ot Apj)ll~te.
8/11/1997 • 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
1/5/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/28/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 !1.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 9.00E-14 2.25E-14 2.00E-14 S.OOE-15 '9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
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.SOE-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/1999 3.03E-15 ., 9.00E-14 2.25E-14 1.37E-15 2.00E-14 5.00E-15 8.72E-16 ~.OOE-13 2.25E-13 7.55E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/28/1999 5.0lE-15 9.00E-14 2.2SE-14 2.89E-15 2.00E-14 5.00E-15 l.31E-15 9.00E-13 2.25E-13 8.lOE-15 6.00E-13 1.SOE-13 Not Analyzed Not A_pplicable Not Applicable
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.SOE-13 !'Jot Analyzed Not Applicable Not Applicable
6/26/2000 5.40E-16 . 9.00E-14 2.25E-14 3.53E-16 2.00E-14 5.00E-15 6.llE-16 9.00E-13 2.25E-13 4.83E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/25/2000 3.75E-16 9.00E-14 2.25E-14 2.23E-16 2.00E-14 S.OOE-15 1.91E-16 9.00E-13 2.25E-13 6A1E-15 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not ~plicable
12/26/2000 .5.21E-16 9.00E-14 2.25E-14 3.39E-16 2.00E-14 5.00E-15 3.28E-17 9.00E-13 2.25E-13 8,57E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not ~_plicable
3/26/2001 1.42E-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 6.lSE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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·l3 Not Analyzed Not Applicable Not Applicable
9/24/2001 3.0SE-16 9.00E-14 2.25E-14 1.0lE-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.2SE-13 8.59E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 2.2SE-13 3.14E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable !'Jot Applicable
4/1/2002 4.77E-16 9.00E-14 2.25E-14 2.94E-16 2.00E-14 5.00E-15 1.96E-16 9.00E-13 2.2SE-13 8.61E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 3.68E-16 9.00E-14 ·i.25E-14 4.41E-16 2.00E-14 S.OOE-15 1.76E-16 9.00E-13 2.25E-13 8.20E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable No.t Appllca.ble
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.SOE-13 Not Analyzed Not Applicable Not Appllcable
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 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 l.98E-16 9.00E-14 2.25E-14 1.68E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.77E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Ap_plicable
6/30/2003 1.18E-16 9.00E-14 2.25E-14 1.15E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.92E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/29/2003 1.00E-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 l.SOE-13 Not Analyzed Not A(1plicable Not Applicable
12/29/2003 l.OOE-16 9.00E-14 2.25E-14 l.36E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.66E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/2004 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.17E·15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.00E-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 3.55£-15 6.00E-13 l.50E·13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-16 9.00E-14 2.25E-14 l.38E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 l.22E-14 6.00E-13 1.SOE-13 Not Analyzed Not A~licable Not Applicable
12/27/2004 l.OSE-16 9.00E-14 -2.25E-14 1.72E-16 2.00E-14 5.00E-15 l.OOE-16 .9.00E-13 2.2SE-13 1.52E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 l.OOE-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 9.34E-15 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not Applicable
6/29/2005 l.28E-16 9.00E-14 2.25E-14' 1.0lE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.8SE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 1.98E-16 9.00E-14 2.25E-14 5.98E-16 2.00E-14 S.OOE-15 3.55E-16 9.00E-13 2.25E-13 1.71E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/3/2006 7.67E-16 9.00E-14 2.2SE-14 2.88E-16 2.00E-14 5.00E-15 3.GOE-15 9.00E-13 2.25E-13 4.85E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14u0/ml BHV-6U Effluent ZE-14 uCi/ml BHV-6T230 Effluent 9E-13 uCi/ml BHV-6R Effluent 6E-13 uCi/ml BHV-6PB Effluent 4e-15 uCi/ml BHV-6T232
Concentratiori Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= 'Limit=
ALARAGoal= 2.ZSE-14 uCi/inl ALARA Goal= 5E-13 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml AlARAGoal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre 1994 1.25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone 'EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
4/3/2006 2.92E-16 -9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.llE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/3/2006 3.25E-16 9.00E-14 2.25E-14 2.36E-16 2.00E-14 5.00E-15 1.08E-16 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
10/2/2006 -S.03E-16 9.00E-14 2.25E·14 1.49E-16 Z.OOE-14 5.00E-15 1.19E-16 9.00E-13 2.25E-13 Z.BE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 8.31E-16 9.00E-14 2.25E-14 2.49E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 5.36E-16 9.00E-14 2.25E-14 3.lSE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.43E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 l.08E-15 9.00E-14 Z.25E-14 2.18E-16 2.00E-14 S.OOE-15 l.54E-16 9.00E-13 2.25E-13 Z.04E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2007 3.92E-16 9.00E-14 2.25E-14 1.02E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.38E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap~licable
12/31/2007 2.92E-15 9.00E-14 2.25E-14 1.SSE-15 2.00E-14 5.00E-15 3.16E-16 9.00E-13 2.25E-13 9.19E-15 6.00E-13 1.SOE-13 Not Analyzed Not Ap_plicable Not Applicable
3/31/2008 4.34E-16 9.00E-14 2.25E-14 3.SlE-16 Z.OOE-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 5.99E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 Not Analyzed Not Applicable Not Applicable
9/30/2008 4.82E-15 9.00E-14 2.25E-14 2.lOE-15 2.00E-14 5.00E-15 1.27E-15 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2008 4.80E-15 9.00E-14 2.25E-14 l.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 Not Analyzed Not Applicable Not Applicable
3/15/2009 2.77E-15 9.00E-14 2.25E-14 l.OlE-15 2.00E-14 5.00E-15 7.82E-16 9.00E-13 2.25E-13 6.46E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 1.41E-16 9.00E-14 2.ZSE-14 2.67E-16 2.00E-14 5.00E-15 l.81E-16 9.00E-13 2.ZSE-13 5.76E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 4.87E-15 9.00E-14 2.ZSE-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.SOE-13 Not Analyzed Not Applicable " Not Applicable
12/15/2009 9.24E-15 9.00E-14 2.25E-14. 2.26E-16 2.00E-14 5.00E-15 1.lSE-16 9.00E-13 2.ZSE-13 6.44E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2010 9.63E-15 9.00E-14 2.2SE-14 1.82E-16 2.00E-14 S.OOE-15 2.06E-16 9.00E-13 2.2SE-13 l.37E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/30/2010 3.62E-15 9.00E-14 _2.2SE-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 Not Analyzed Not Applicable Not Applicable
9/30/2010 5.42E-15 9.00E-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.SOE-13 Not Analyzed Not 11.pplicable Not A_p_plicable
12/31/2010 1.24E-14 9.00E-14 2.25E-14 1.ZlE-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.ZSE-13 1.53E-14 6.00E-13 LSOE-13 Not Anal)'Zed Not Applicable }lot Applicable
4/4/2011 2.70E-15 9.00E-14 l .ZSE-14 4.62E-16 2.00E-14 5.00E-15 6.SlE-16 9.00E-13 2.ZSE-13 1.29E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 3.0lE-15 9.00E-14 2.25E·14 7.07E-16 2.00E-14 5.00E-15 5.75E-16 9.00E-13 2.ZSE-13 7.97E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable illot Applicable
10/3/2011 2.0SE-15 9.00E-14 2.2SE-14 6.lZE-16 2.00E-14 5.00E-15 l .88E-16 9.00E-13 2.25E-13 9.93E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
1/3/2012 B.14E-15 9.00E-14 Z.25E-14 1.09E-15 2.00E-14 5.00E-15 7.65E-16 9.00E-13 2.25E-13 l.89E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 4.41E-15 9.00E-14 2.25E-14 l.82E-15 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.2SE-13 l.50E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2012 q.42E-15 jl.OOE-14 2.25E-14 2.25E-15 2.00E-14 5.00E-15 5.llE-16 9.00E-13 2.25E-13 9.54E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 6.63E,15 '9.00E-14 2.25E-14 l.31E-15 2.00E-14 5.00E-15 1.22E-15 9.00E-13 2.25E-13 1.34E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 3.83E-15 9.00E-14 2.25E·14 l.18E-15 2.00E-14 5.00E-15 9.30E-16 9.00E-13 .2.25E-13 1.GOE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A_p_!!licable
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 l.70E-14 6.00E-13 l.50E-13 Not Analyzed Not A_pplicable Not Applicable
7/2/2013 5.91E-15 .9.00E-14 2.25E-14 6.74E-16 2.00E-14 S.OOE-15 7.SSE-16 9.00E-13 2.2SE-13 5.18E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 2.68E-15 9.00E-14 2.25E-14 3.97E-16 2.00E-14 S.OOE-15 'l.04E-16 9.00E-13 2.2SE-13 6.13E-15 6.00E-13 l.50E-13 Not Analyzed !'lot Applicable Not Applicable
12/30/2013 l.60E-14 9.00E-14 2.25E-14 2.48E-16 2.00E-14 5.00E-15 :l.05E-16 9.00E-13 2.25E-13 2.67E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2014 8.92E-15 '9.00E-14 2.ZSE-14 7.68E-16 2.00E-14 S.OOE-15 l.50E-15 9.00E-13 2.25E-13 l.61E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2014 8.29E-15 9.00E-14 2.2SE-14 5.35E-16 2.00E-14 5.00E-15 6.72E-16 . 9.00E-13 2.25E-13 l.20E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 1.20E-14 9.00E-14 2.25E-14 5.54E-16 2.00E-14 5.00E-15 6.18E-16 9.00E-13 2.25E-13 1.38E-14 6.00E-13 1.50E-13 .l.OOE-16 4.00E-15 1.00E-15
12/29/2014 5.00E-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 2.30E-14 6.00E-13 1.SOE-13 !I.OOE-18 4.00E-15 1.00E-15
3/30/2015 2.80E-14 9.00E-14 2.2SE-14 2.00E-16 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 2.80E-14 6.00E-13 l.50E-13 l.OOE-18 4.00E-15 1.00E-15
6/29/2015 5.30E-15 9.00E-14 2.2SE-14 2.00E-16 2.00E-14 5.00E-15 5.00E-16 9.00E-13 2.2SE-13 l.70E-14 6.00E-13 l.50E-13 l.OOE-17 4.00E-15 1.00E-15
9/28/2015 l.OOE-14 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 .3.00E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 l.50E-13 2.00E-18 4.00E-15 l.OOE-15
12/28/2015 8.40E-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 6.00E-18 4.00E-15 1.00E-15
3/28/2016 7.00E-16 9.00E-14 · 2.2SE-14 1.00E-16 2.00E-14 5.00E-15 9.00E-16 9.00E-13 2.25E-13 1. 70E-14 6.00E-13 1.50E-13 l.OOE-17 4.00E-15 1.00E-15
6/27/2016 1.ZOE-14 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 6.00E-15 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.SOE-13 II.OOE-18 4.00E-15 1.00E-15
9/27/2016 6.90E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 7.20E-16 9.00E-13 2.25E-13 3.20E-15 6.00E-13 l.SOE-13 l .20E-17 4.00E-15 1.00E-15
12/27/2016 8.90E-15 9.00E-14 2.25E-14 3.30E-16 2.00E-14 5.00E-15 4.80E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.50E-13 9.50E-18 4.00E-15 1.00E-15
3/27/2017 8.lOE-15 9.00E-14 2.2SE-14 7.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.50E-14 6.00E-13 l.50E-13 3.00E-18 4.00E-15 1.00E-15
6/26/2017 2.30E-15 9.00E-14 2.2SE-14 7.00E-17 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 l.50E-13 8.00E-18 4.00E-15 1.00E-15
9/25/2017 3.SOE-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.90E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 'l.OOE-15
12/26/2017 1.40E-14 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 1.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 1.00E-15
3/26/2018 1.20E-15 9.00E-14 2.ZSE-14 1.lOE-16 2.00E-14 5.00E-15 1.lOE-16 9.00E-13 2.25E-13 1.50E-14 6.00E-13 l.SOE-13 9.00E-18 4.00E-15 1.00E-15
Date Effluent 9E-14 uCl/ml BHV-6U Effluent 2E-14 uCi/ml BHV-6T230 Effluent 9E-13 uCi/ml BHV-6R Effluent 6E-13 uCi/ml BHV-6PB Effluent 4e-15 uCi/ml BHV-6T232
Concentration Concentration Concentration Concentration Concentration
Umit= Limit= Limit= Limit= Limit=
ALARA Goal= , 2.ZSE-14 uCi/ml ALARA Goal= SE-13 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARAGoal = l.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre1994MPC SE-UuCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC 2E-12 uCi{ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Umit= Limit= Limit= Limit= Limit=
!"re 1994 1.2se,u uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone 'EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
6/25/2018 3.00E-15 9.00E-14 2.25E-14 9,70E-17 2,00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.SOE-13 1.40E-17 4.00E-15 1.00E-15
9/24/2018 3.lOE-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 1.00E-15
12/31/2018 7.90E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 1.00E-15
4/1/2019 2.00E-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 1.00E-14 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 1.00E-15
7/1/2019 9.00E-17 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 2.30E·l5 9.00E-13 2.25E-13 9.00E-15 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 1.00E-15
9/30/2019 7.00E-17 9.00E-14 2.25E-14 8.00E-17 2.00E-14 S.OOE-15 5.00E-17 9.00E-13 2.25E-13 8.00E-15 6.00E-13 l.SOE-13 4.00E-18 4.00E-15 1.00E-15
1/6/2020 2.00E-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 l.OOE-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
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TAB7
BHV-7 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml 8HV-7U Effluent 2E-14 uCi/ml BHV-7T230 ·effluent 9E-13 uCi/ml BHV-7R Effluent 6E-13 uCi/ml BHV-7PB Effluent 4e-15 uCi/ml BHV-7T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= 'Limit=
ALARAGoal = 2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARAGoal = 2.2SE-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml -Pre1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre 1994 L25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 j\lot Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
12/29/2014 NS 9.00E-14 2.25E-14 NS 2.00E-14 5.00E-15 NS 9.00E-13 2.2SE-13 NS 6.00E-13 1.SOE-13 NS 4.00E-15 1.00E-15
3/30/2015 6.00E-15 9.00E-14 2.25E-14 8.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.SOE-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
6/29/2015 1.40E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 1.30E-15 9,00E-13 2.25E-13 1.70E-14 6.00E-13 l.SOE-13 1.00E-17 4.00E-15 1.00E-15
9/28/2015 4.20E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 S.OOE-15 4.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 l.SOE-13 6.00E-18 4.00E-15 1.00E-15
12/28/2015 3.60E-16 9.00E-14 2.25E-14 7.00E-17 2.00E-14 S.OOE-15 2.00E-16 9.00E-13 2.25E-13-2.00E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15 -
3/28/2016 8.00E-16 ll-OOE-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.SOE-13 5.00E-18 4.00E-15 1.00E-15
6/27/2016 1.SOE-15 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5.00E-15 9.00E-16 9.00E-13 2.25E-13 1.50E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 1.00E-15
9/27/2016 2.60E-15 9.00E-14 2.25E-14 1.70E-16 2.00E-14 5.00E-15 4.lOE-16 . 9.00E-13 2.25E-13 2.80E-15 6.00E-13 1.SOE-13 5.SOE-18 4.00E-15 1.00E-lS
12/27/2016 1.60E-15 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 2.SOE-16 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 l.SOE-13 4.BOE-18 4.00E-15 l.OOE-15
3/27/2017 3.30E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.40E-15 9.00E-13 2.25E-13 1.40E-14 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 l.OOE-15
6/26/2017 3.40E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 1.SOE-15 9.00E-13 2.25E-13 1.40E-14 6.00E-13 1.50E-13 l.OOE-17 4.00E-15 l.OOE-15
9/25/2017 1.20E-15 9.00E-14 2.25E-14-6.00E-17 2.00E-14 5.00E-15 1.QOE-16 9.00E-13 2.25E-13 1.90E-14 6.00E-13 l .50E-13 4.00E-18 4.00E-15 l.OOE-lS
12/26/2017 4.60E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 :J..OOE-15
3/26/2018 4.lOE-16 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 2.60E-16 9.00E-13 2.25E-13 1.80E-14 6.00E-13 1.50E-13 8.70E-18 4.00E-15 i.OOE-15
6/25/2018 1.60E-15 9.00E-14 2.25E-14 2.20E-16 2.00E-14 5.00E-lS 4.30E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 l.70E-17 4.00E-15 1.00E-15
9/24/2018 1.00E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 · 2.25E-13 2.00E-14 6.00E-13 1.5DE-13 1.00E-17 4.00E-15 1.00E-15
12/31/2018 1.90E-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 2.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.50E-13 5.00E-18 4.00E-15 l.OOE-15
4/1/2019 8.00E-17 9.00E-14 2.25E-14 5.00E-17 2.00E-14 S.OOE-15 6.00E-17 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 1.00E-15
7/1/2019 2.00E-16 9.00E-14 2.25E-14 5.00E-16 2.00E-14 5.00E-15 1.50E-15 9.00E-13 2.2SE-13 l.OOE-14 6.00E-13 l.SOE-13 1.00E-17 4.00E-15 1.00E-15
9/30/2019 2.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-lS 3.00E-16 9.00E-13 ,2.25E-13 l.OOE-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
1/6/2020 1.00E-16 9.00E-14 i2.25E-14 5.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 '2.25E-13 l.OOE-14 6.00E-13 1.50E-13 l.OOE-18 4,00E-15 1.00E-15
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TABS
BHV-8 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-BU Effluent 2E-14 uCi/ml J!HV-8T230 Effluent 9E·13 uCi/ml BHV-BR Effluent 6E-13 uCi/ml BHV-SPB Effluent 4e-1S uCi/ml BHV•8T232
Concentration Concentration toncentration Concentration Concentration
limit= Umit = Limit= Limit= Limit=
ALARAGoal= ·2.ZSE-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARAGoal= ,2.ZSE-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml ALARAGoal = H-lSuCi/ml
Pre1994MPC SE-UuCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= limit= Limit= ~imit=
Prel994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
,ALARA GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC ~FCA
12/29/2014 4.00E-16 9.00E-14 2.25E-14. 2.00E-16 2,00E-14 5.00E-15 7.00E-17 9 OOE-13 2.25E-13 9.90E-15 6.00E-13 l.SOE-13 9.00E-18 4,00E-15 1.00E-15
3/30/2015 1.SOE-15 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 9.40E-15 6.00E-13 1.SOE-13 1.00E-16 4.00E-15 1.00E-15
6/29/2015 s.ooe-16 9.00E-14 2.2SE-14 1.00E-16 2.00E-14 S.OOE-15 S.OOE-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 1.00E-15
9/28/2015 1.SOE-15 9.00E-14 2.25E-14 4.00E-17 -2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 8.00E-15 6.00E-13 1.SOE-13 3.00E-18 4.00E-15 l.OOE-15
12/28/2015 2.lOE-16 9.00E-14 2.25E-14 9.00E-17 2.00E-14 S.OOE-15 9.00E-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
3/28/2016 2.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 l .50E-13 2.00E-18 4.00E-15 1.00E-15
6/27/2016 1.lOE-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.90E-15 9.00E-13 2.2SE-13 1.lOE-14 6.00E-13 l.SOE-13 2.00E-18 4.00E-15 1.00E-15
9/27/2016 1.20E-15 9.00E-14 2.25E-14 8.40E-17 2.00E-14 5.00E-15 3.30E-16 [9.00E-13 2.25E-13 7.60E-15 6.00E-13 1.SOE-13 4.70E-18 4.00E-15 1.00E-15
-12/27/2016 1.20E-15 9.00E-14 2.25E-14 6.00E-17 2.00E-14 5.00E-15 8.SOE-17 9.00E-13 2.25E-13 l.40E-14 6.00E-13 1.SOE-13 3.20E-18 4.00E-15 1.00E-15
3/27/2017 8.00E-16 9.00E-14 2.25E-14 9.00E-17 2.00E-14 S.OOE-15 1.30E-15 9.00E-13 2.25E-13 8.70E-15 6.00E-13 1.50E-13 l.OOE-18 4.00E-15 1.00E-15
6/26/2017 1.00E-16 9.00E-14 2.25E-14 S.OOE-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 7.80E-15 6.00E-13 1.SOE-13 5.00E-19 4.00E-15 1.00E-15 -
9/25/2017 6.00E-16 9.00E-14 2.25E-14 8.00E-17 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 2.00E-18 4.00E-15 1.00E-15
12/26/2017 Z.90E-15 9.00E-14 2.25E-14 S.OOE-17 2.00E-14 S.OOE-15 S.OOE-17 9.00E-13 2.25E-13 l.70E-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 i..OOE-15
3/26/2018 2.30E-16 9.00E-14 2.25E-14 S.80E-17 2.00E-14 5.00E-15 8.30E-17 9.00E-13 2.25E-13 1.30E-14 6.00E-13 1.SOE-13 5.lOE-18 /I.OOE-15 1.00E·lS
6/25/2018 9.40E-16 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 8.80E-15 6.00E-13 l.50E·l3 8.50E-18 4.00E-15 l.OOE-15
9/24/2018 6.00E-16 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5.00E-15 6.00E-17 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 6.00E-18 4.00E-15 l.OOE-15
12/31/2018 1.SOE-15 9.00E-14 2.25E-14 7.00E-17 2.00E-14 S.OOE-15 3.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l.50E-13 3.00E-18 4.00E-15 1.00E-15
4/1/2019 8.00E-17 9.00E-14 2.25E-14 1.00E-16 2.00E-14 S.OOE-15 2.00E-16 9.00E-13 2.2SE-13 l.OOE-14 6.00E-13 1.50E-13 :2.00E-18 4.00E-15 l.OOE-15
7/1/2019 8.00E-17 9.00E-14 2.25E-14 1.00E-16 2.00E-14 S.OOE-15 6.00E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.50E-13 4.00E-18 -4.00E-15 l.OOE-15
9/30/2019 t.OOE-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.lOE-15 9.00E-13 2.ZSE-13 1.00E-14 6.00E-13 l.SOE-13 9.00E-18 4.00E-15 1.00E-15 -
1/6/2020 4.00E-17 9.00E-14 2.25E-14 4.00E-17 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.2SE-13 7.00E-15 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 l.OOE-15
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ATTACHMENT C
BHV AIR SAMPLING LABORATORY RESULTS AND QA/QC
EI\ERGY
,1 1 '( 11 ... 11 i,Jlj <
Trust our People. Trust our Data.
www.energylab.com W' Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-1
REPORT DATE: November 11, 2019
Quarterillate Sampled Concentration Radionuclide Air Volume µCi/mL
CI9100256-00I nalu IE-16
3rd Quarter 2019 230Th 5E-16
Air Volume in mLs 226Ra 8E-16
l.20E+ll 210Pb IE-14
232Th 7E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
IE-16
2E-16
3E-l5
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2E-Ol
IE-17 IE-16 3E-14 2E+OO
2E-17 IE-16 9E0 13 9E-02
3E-16 2E-15 6E-13 2E+OO
2E-18 NIA 6E-15 IE-01
Page 5 of40
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium 2.1E-10 mg/L
Uranium, Activity 1.4E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.1E-14 uCi/mL
Lead 210 precision (±) 3.2E-15 uCi/mL
Lead 210 MDC 3.0E-16 uCi/mL
Radium 226 8.0E-16 uCi/mL
Radium 226 precision (±) 1.6E-16 uCi/mL
Radium 226 MDC 1.8E-17 uCi/mL
Thorium 230 5.3E-16 uCi/mL
Thorium 230 precision (±) 1.0E-16 uCi/mL
Thorium 230 MDC 1.1E-17 uCi/mL
Thorium 232 6.5E-18 uCi/mL
Thorium 232 precision (±) 2.0E-18 uCi/mL
Thorium 232 MDC 1.8E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1270 pCi/Filter
Lead 210 precision(±) 379 pCi/Filter
Lead 210 MDC 36.0 pCi/Filter
Radium 226 95.5 pCi/Filter
Radium 226 precision (±) 18.9 pCi/Filter
Radium 226 MDC 2.2 pCi/Filter
Thorium 230 63. 1 pCi/Filter
Thorium 230 precision (±) 12.0 pCi/Filter
Thorium 230 MDC 1.3 pCi/Filter
Thorium 232 0.78 pCi/Filter
Thorium 232 precision (±) 0.25 pCi/Filter
Thorium 232 MDC 0.21 pCi/Filter
Uranium, Activity 17.1 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.8E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 9.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.8E+OO %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.1E-01 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 11 /11 /19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 10/30/19 21 :01 / meh
SW6020 10/30/19 21 :01 I meh
E909.0 10/23/19 21 :24 / ajl
E909.0 10/23/19 21 :24 / ajl
E909.0 10/23/19 21 :24 / ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 I ajl
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/1917:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :08 / sec
RADCALC 11/06/1911:08/sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :OB/ sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 3 of 40
EN:RGY Trust our People. Trust our Data.
www.energyl~b.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-001
Client Sample ID: BHV-1
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.6E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
119908500 L
Qualifiers RL
MCU
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11/06/19 11 :08 / sec
11 /06/19 11 :08 / sec
11 /06/19 11 : 08 / sec
11 /06/19 11 : 08 / sec
09/30/19 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 40
EN:RGY
,t ,(., \II !I.'
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
I I. f .. HIGH VOLUME AIR SAMPLING REPORT • ... •
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV-1
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C200 I 0402-00 I nalu 4E-17
4th Quarter 2019 23°Th 3E-17
Air Volume in mLs 226Ra 6E-17
l.33E+IJ 2IOPb IE-14
232Th 3E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
6E-18
2E-17
4E-15
IE-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
p
,.
" I
I,
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 5E-02
2E-18 IE-16 3E-14 IE-OJ
IE-17 IE-16 9E-13 7E-03
4E-16 2E-15 6E-13 2E+OO
2E-18 NIA 6E-15 5E-02
Page 5 of 40
EJ\ERGY -. Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium ND mg/L
Uranium, Activity ND uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision(±) 3.5E-15 uCi/mL
Lead 210 MDC 3.5E-16 uCi/mL
Radium 226 6.4E-17 uCi/mL
Radium 226 precision (±) 1.9E-17 uCi/mL
Radium 226 MDC 1.4E-17 uCi/mL
Thorium 230 3.3E-17 uCi/mL
Thorium 230 precision (±) 6.2E-18 uCi/mL
Thorium 230 MDC 1.SE-18 uCi/mL
Thorium 232 3.0E-18 uCi/mL
Thorium 232 precision (±) 1.4E-18 uCi/mL
Thorium 232 MDC 1.7E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1590 pCi/Filter
Lead 210 precision (±) 475 pCi/Filter
Lead 210 MDC 48.2 pCi/Filter
Radium 226 8.5 pCi/Filter
Radium 226 precision (±) 2.5 pCi/Filter
Radium 226 MDC 1.9 pCi/Filter
Thorium 230 4.4 pCi/Filter
Thorium 230 precision (±) 0.83 pCi/Filter
Thorium 230 MDC 0.24 pCi/Filter
Thorium 232 0.39 pCi/Filter
Thorium 232 precision (±) 0.18 pCi/Filter
Thorium 232 MDC 0.22 pCi/Filter
Uranium, Activity 5.6 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.0E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 7.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.1E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 5.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 14:27 / meh
SW6020 01/24/20 14:27 I meh
E909.0 02/10/20 01 : 11 / ajl
E909.0 02/10/2001 :11 / ajl
E909.0 02/10/20 01 : 11 / ajl
E903.0 02/04/20 11 :50 / ajl
E903.0 02/04/20 11 :50 / ajl
E903.0 02/04/20 11 :50 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 01/31/20 15:07 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 3 of 40
EN:RGY
I ,I•
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-001
Client Sample ID: BHV-1
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
5.0E-02 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
133448200 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
01 /06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 4 of 40
EN:RGY
,,/ , •,",1r ,J'L
;
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-2
REPORT DATE: November 11, 2019
Quartermate Sampled Concentration Radionuclide Air Volume µCi/mL
C 19100256-002 natu 2E-16
3rd Quarter 2019 23°'fh 3E-17
Air Volume in mLs 226Ra 3E-16
1.2IE+I I z10Pb 9E-15
232Th 9E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
7E-18
6E-17
3E-15
2E-18
*Effluent Concentration from the NEW IO CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDC µCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2E-01
3E-18 IE-16 3E-14 IE-01
2E-17 IE-16 9E-13 3E-02
3E-16 2E-15 6E-13 2E+OO
2E-18 NIA 6E-15 IE-01
Page 8 of 40
EN:RGY . . .
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-002
Client Sample ID: BHV-2
Analyses
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
Thorium 232
Thorium 232 precision (±)
Thorium 232 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
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Uranium, Activity
Result Units
2.6E-10 mg/L
1.8E-16 uCi/mL
9.2E-15 uCi/mL
2.7E-15 uCi/mL
2.8E-16 uCi/mL
2.6E-16 uCi/mL
5.9E-17 uCi/mL
1. 7E-17 uCi/mL
3.5E-17 uCi/mL
6.6E-18 uCi/mL
3.2E-18 uCi/mL
8.6E-18 uCi/mL
1.6E-18 uCi/mL
2.4E-18 uCi/mL
1110 pCi/Filter
331 pCi/Filter
33.6 pCi/Filter
32.1 pCi/Filter
7 .1 pCi/Filter
2.1 pCi/Filter
4.2 pCi/Filter
0.80 pCi/Filter
0.39 pCi/Filter
1.0 pCi/Filter
0.20 pCi/Filter
0.29 pCi/Filter
21.6 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF
Lead 210, EFF Day
Lead 210, LLD
Radium 226, % of EFF
Radium 226, EFF Week
Radium 226, LLD
Thorium 230, % of EFF
Thorium 230, EFF Year
Thorium 230, LLD
Thorium 232, % of EFF
Thorium 232, EFF Year
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
1.5E+OO %
6.0E-13 uCi/mL
2.0E-15 uCi/mL
3.0E-02 %
9.0E-13 uCi/mL
1.0E-16 uCi/mL
1.2E-01 %
3.0E-14 uCi/mL
1.0E-16 uCi/mL
1.4E-01 %
6.0E-15 uCi/mL
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 11/11/19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 10/30/19 21 :06 / meh
SW6020 10/30/1921 :06 / meh
E909.0 10/23/19 21 :36 / ajl
E909.0 10/23/19 21:36 / ajl
E909.0 10/23/19 21 :36 / ajl
E903.0 10/22/19 12:02 / ajl
E903.0 10/22/19 12:02 / ajl
E903.0 10/22/19 12:02 / ajl
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/1917:17 / nsr
RADCALC 11/06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11/06/19 10:57 I sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 40
El'-ERGY
' ,. !
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
NIA uCi/mL
2.0E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
121009600 L
Qualifiers RL
MCU
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
QCL Method Analysis Date I By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 : 08 / sec
11 /06/19 11 :OB/ sec
11 /06/19 11 :08 / sec
11/06/19 11 :08 / sec
09/30/19 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 40
EI\ERGY
' ' '
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
I CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019 ..
' SAMPLE ID: BHV-2
REPORT DATE: February 13, 2020
Quarter/Date Sampled Radionuclide Air Volume
C200 I 0402-002 natu
4th Quarter 2019 230Th
Air Volume in mLs 226Ra
l.34E+I I 2'°Pb
232Tb
+LLD's are from NRC Reg. Guide 4. 14
Concentration
µCi/mL
2E-17
IE-17
4E-17
SE-15
SE-18
Counting
Precision
µCi/mL
NIA
2E-18
IE-17
2E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Ernuent Cone.* % ErDuent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2E-02
2E-18 IE-16 3E-14 4E-02
IE-17 IE-16 9E-13 SE-03
3E-16 2E-15 6E-13 lE+OO
lE-18 NIA 6E-15 9E-02
Page 8 of 40
El'J:RGY
'' '
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL 'REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-002
Client Sample ID: BHV-2
Analyses Result Units
METALS, IN AIR
Uranium ND mg/L
Uranium, Activity ND uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 7.3E-15 uCi/mL
Lead 210 precision(±) 2.2E-15 uCi/mL
Lead 210 MDC 2.8E-16 uCi/mL
Radium 226 4.4E-17 uCi/mL
Radium 226 precision (±) 1.4E-17 uCi/mL
Radium 226 MDC 1.5E-17 uCi/mL
Thorium 230 1.3E-17 uCi/mL
Thorium 230 precision (±) 2.5E-18 uCi/mL
Thorium 230 MDC 1.6E-18 uCi/mL
Thorium 232 5.2E-18 uCi/mL
Thorium 232 precision (±) 1.5E-18 uCi/mL
Thorium 232 MDC 1.0E-18 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 1090 pCi/Filter
Lead 210 precision(±) 328 pCi/Filter
Lead 210 MDC 40.4 pCi/Filter
Radium 226 6.0 pCi/Filter
Radium 226 precision (±) 1.9 pCi/Filter
Radium 226 MDC 2.0 pCi/Filter
Thorium 230 1. 7 pCi/Filter
Thorium 230 precision (±) 0.33 pCi/Filter
Thorium 230 MDC 0.22 pCi/Filter
Thorium 232 0. 70 pCi/Filter
Thorium 232 precision (±) 0.21 pCi/Filter
Thorium 232 MDC 0.14 pCi/Filter
Uranium, Activity 2.2 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.4E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 5.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.0E-02 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 9.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 14:44 / meh
SW6020 01/24/20 14:44 / meh
E909.0 02/10/20 01 :24 I ajl
E909.0 02/10/2001 :24 / ajl
E909.0 02/10/20 01 :24 I ajl
E903.0 02/04/20 11 : 51 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 I nsr
E908.0 02/05/20 13:09 I nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02107120 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02107120 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 01 /31 /20 15:07 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 6 of 40
EN:RGY
,, II
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www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
2.0E-02 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
134042200 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
QCL Method Analysis Date I By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 7 of 40
EN:RGY
,~ • \' '• , ,•, '' I• -
Trust our People. Trust our Data.
www.energylab.com
Toll Free, 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGII VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-4
REPORT DATE: November 11, 2019
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 19100256-003 na\u IE-16
3rd Quarter 2019 23°Th lE-16
Air Volume in mLs 226Ra 9E-17
l.20E+ll 210Pb IE-14
232Th 3E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
2E-17
2E-17
3E-15
2E-18
*Effluent Concentration from the NEW IO CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 IE-01
3E-18 IE-16 3E-14 3E-Ol
2E-17 IE-16 9E-13 IE-02
3E-16 2E-15 6E-13 2E+OO
2E-18 NIA 6E-15 SE-02
Page 11 of 40
EI\ERGV
I I. , ,
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-003
Client Sample ID: BHV-4
Analyses Result Units
METALS, IN AIR
Uranium 1.9E-10 mg/L
Uranium, Activity 1.3E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 9.6E-15 uCi/mL
Lead 210 precision (±) 2.9E-15 uCi/mL
Lead 210 MDC 2.9E-16 uCi/mL
Radium 226 8.9E-17 uCi/mL
Radium 226 precision (±) 2.5E-17 uCi/mL
Radium 226 MDC 1.8E-17 uCi/mL
Thorium 230 9.9E-17 uCi/mL
Thorium 230 precision (±) 1.9E-17 uCi/mL
Thorium 230 MDC 2.8E-18 uCi/mL
Thorium 232 3.1 E-18 uCi/mL
Thorium 232 precision (±) 1.5E-18 uCi/mL
Thorium 232 MDC 1.9E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1160 pCi/Filter
Lead 210 precision(±) 346 pCi/Filter
Lead 210 MDC 34.5 pCi/Filter
Radium 226 10. 7 pCi/Filter
Radium 226 precision (±) 3.0 pCi/Filter
Radium 226 MDC 2.2 pCi/Filter
Thorium 230 11.9 pCi/Filter
Thorium 230 precision (±) 2.3 pCi/Filter
Thorium 230 MDC 0.34 pCi/Filter
Thorium 232 0.37 pCi/Filter
Thorium 232 precision (±) 0.18 pCi/Filter
Thorium 232 MDC 0.23 pCi/Filter
Uranium, Activity 15.1 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.6E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/ml
Radium 226, % of EFF 1.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/ml
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 3.3E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 5.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCU
Rl QCL
1.5E-10
1.0E-16
0.20
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 10/30/19 21 : 10 / meh
SW6020 10/30/19 21 :10 / meh
E909.0 10/23/19 21 :50 / ajl
E909.0 10/23/19 21 :50 / ajl
E909.0 10/23/19 21 :50 / ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 / ajl
E903.0 10/22/19 12:02 I ajl
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/1917:17 / nsr
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17: 17 / nsr
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 I sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11/06/1911 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11/06/19 11:08 / sec
RADCALC 11/06/1911:08 / sec
RADCALC 11/06/19 11 :OB/ sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 9 of 40
EI\ERGY
' .. .
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www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.686. 7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.4E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
120305700 L
Qualifiers RL
MCU
Report Date: 11 /11 /19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 : 08 / sec
11 /06/19 11 : 08 / sec
11 /06/19 11 : 08 / sec
11 /06/19 11 :08 / sec
09/30/19 00:00 I***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 40
El'ERGY
•T'l) I"\ •\I
Trust our People. Trust our Data.
www.energylab.com
Toll Free, 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV-4
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C20010402-003 ""'U 4E-17
4th Quarter 2019 23°Th 6E-17
Air Volume in mLs 226Ra 4E-17
l.32E+l 1 210Pb 9E-15
232Th 3E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
IE-17
IE-17
3E-15
IE-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix 8 -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
...... ..
L.L.D.+ EfOuent Cone.* % Effluent MDC µCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 SE-02
2E-18 IE-16 3E-14 2E-01
IE-17 IE-16 9E-13 4E-03
3E-16 2E-15 6E-13 IE+OO
2E-18 NIA 6E-15 4E-02
Page 11 of 40
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-003
Client Sample ID: BHV-4
Analyses Result Units
METALS, IN AIR
Uranium ND mg/L
Uranium, Activity ND uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 8.5E-15 uCi/mL
Lead 210 precision (±) 2.5E-15 uCi/ml
Lead 210 MDC 3.0E-16 uCi/ml
Radium 226 3.9E-17 uCi/mL
Radium 226 precision (±) 1.5E-17 uCi/mL
Radium 226 MDC 1.5E-17 uCi/mL
Thorium 230 5.BE-17 uCi/mL
Thorium 230 precision (±) 1.1 E-17 uCi/mL
Thorium 230 MDC 1.7E-18 uCi/mL
Thorium 232 2.6E-18 uCi/mL
Thorium 232 precision (±) 1.3E-18 uCi/mL
Thorium 232 MDC 1.6E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1160 pCi/Filter
Lead 210 precision(±) 346 pCi/Filter
Lead 210 MDC 41 .2 pCi/Filter
Radium 226 5.1 pCi/Filter
Radium 226 precision (±) 2.0 pCi/Filter
Radium 226 MDC 2.0 pCi/Filter
Thorium 230 7.7 pCi/Filter
Thorium 230 precision (±) 1.5 pCi/Filter
Thorium 230 MDC 0.23 pCi/Filter
Thorium 232 0.34 pCi/Filter
Thorium 232 precision (±) 0.17 pCi/Filter
Thorium 232 MDC 0.21 pCi/Filter
Uranium, Activity 5.4 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.5E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 4.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.9E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 4.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 14:49 I meh
SW6020 01 /24/20 14:49 I meh
E909.0 02/10/20 01 :44 / ajl
E909.0 02/10/2001 :44 / ajl
E909.0 02/10/20 01 :44 / ajl
E903.0 02/04/20 11 :51 I ajl
E903.0 02/04/20 11 :51 I ajl
E903.0 02/04/20 11 : 51 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 01/31/20 15:07 I dmf
RADCALC 02/07120 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 9 of 40
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
NIA uCi/mL
5.0E-02 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
131899600 L
Qualifiers RL
MCU
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02107120 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 10 of 40
EI\ERGY
: • , / I, ~ j ) • •
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-5
REPORT DATE: November 11, 2019
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl 9100256-004 natu lE-16
3rd Quarter 2019 230Th IE-16
Air Volume in mLs 226Ra 6E-16
l.19E+l 1 210Pb 9E-15
232Th 6E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
3E-17
IE-16
3E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 IE-01
2E-18 IE-16 3E-14 SE-01
2E-17 IE-16 9E-13 7E-02
3E-16 2E-15 6E-13 IE+OO
IE-18 NIA 6E-15 IE-01
Page 14 of 40
E"-ERGY
, d H 11
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-004
Client Sample ID: BHV-5
Analyses
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
Thorium 232
Thorium 232 precision (±)
Thorium 232 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
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Uranium, Activity
Result Units
2.0E-10 mg/L
1.3E-16 uCi/mL
8.6E-15 uCi/mL
2.6E-15 uCi/mL
2.7E-16 uCi/mL
6.1 E-16 uCi/mL
1.2E-16 uCi/mL
1.9E-17 uCi/mL
1.5E-16 uCi/mL
2.8E-17 uCi/mL
1.9E-18 uCi/mL
6.5E-18 uCi/mL
1.9E-18 uCi/mL
1.3E-18 uCi/mL
1020 pCi/Filter
305 pCi/Filter
32.6 pCi/Filter
72.8 pCi/Filter
14. 7 pCi/Filter
2.2 pCi/Filter
17 .6 pCi/Filter
3.3 pCi/Filter
0.23 pCi/Filter
0.77 pCi/Filter
0.23 pCi/Filter
0.15 pCi/Filter
15.9 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF
Lead 210, EFF Day
Lead 210, LLD
Radium 226, % of EFF
Radium 226, EFF Week
Radium 226, LLD
Thorium 230, % of EFF
Thorium 230, EFF Year
Thorium 230, LLD
Thorium 232, % of EFF
Thorium 232, EFF Year
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
1.4E+OO %
6.0E-13 uCi/mL
2.0E-15 uCi/mL
7.0E-02 %
9.0E-13 uCi/mL
1.0E-16 uCi/mL
4.9E-01 %
3.0E-14 uCi/mL
1.0E-16 uCi/mL
1.1E-01 %
6.0E-15 uCi/mL
MDC -Minimum detectable concentration
Qualifiers RL
1.5E-10
1.0E-16
0.20
MCU
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
QCL Method Analysis Date I By
SW6020
SW6020
E909.0
E909.0
E909.0
E903.0
E903.0
E903.0
E908.0
E908.0
E908.0
E908.0
E908.0
E908.0
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
10/30/19 21 :15 / meh
10/30/19 21 :15 / meh
10/23/19 22:03 / ajl
10/23/19 22:03 I ajl
10/23/19 22:03 I ajl
10/22/19 12:02 I ajl
10/22/19 12:02 I ajl
10/22/19 12:02 / ajl
10/23/19 17:16 / nsr
10/23/19 17: 16 / nsr
10/23/19 17:16 / nsr
10/23/19 17:16 / nsr
10/23/19 17:16 / nsr
10/23/19 17: 16 / nsr
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11/06/19 10:57 / sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11/06/19 10:57 / sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11 /06/19 11 :08 I sec
11 /06/19 11 :08 I sec
11 /06/19 11 :08 I sec
11/06/1911:08 /sec
11/06/19 11:08 / sec
11/06/1911 :08 / sec
11 /06/19 11 :08 / sec
11/06/1911 :08 / sec
11/06/19 11 :08 / sec
11 /06/19 11 :08 I sec
11/06/19 11 :08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 12 of 40
EN:RGY . . '
Trust our People. Trust our Data.
www energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 191 00256-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.5E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
119154300 L
Qualifiers RL
MCL/
Report Date: 11 /11 /19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
QCL Method Analysis Date I By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 :08 / sec
11/06/1911:08/sec
11 /06/19 11 : OB / sec
11/06/19 11 :OB/ sec
09/30/19 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 13 of 40
EN:RGY
~ ' '' •" ' I'
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307 .235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
T HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV -5
REPORT DATE: February 13, 2020
Quarterffiate Sampled Concentration Radionuclide Air Volume µCi/mL
C200 I 0402-004 ""u 4E-16
4th Quarter 2019 23°Th 3E-16
Air Volume in mLs 226Ra 4E-16
l.33E+l l 210Pb 9E-15
232Th ?E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
SE-17
9E-17
3E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 4E-Ol
2E-18 lE-16 3E-14 9E-Ol
IE-17 IE-16 9E-13 SE-02
3E-16 2E-15 6E-13 2E+OO
IE-18 NIA 6E-15 lE-01
Page 14 of 40
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-004
Client Sample ID: BHV-5
Analyses Result Units
METALS, IN AIR
Uranium 5.7E-10 mg/L
Uranium, Activity 3.9E-16 uCi/ml
RADIONUCLIDES -IN AIR
Lead 210 8.5E-15 uCi/mL
Lead 210 precision(±) 2.6E-15 uCi/ml
Lead 210 MDC 3.0E-16 uCi/mL
Radium 226 4.5E-16 uCi/mL
Radium 226 precision (±) 9. 1 E-17 uCi/ml
Radium 226 MDC 1.4E-17 uCi/mL
Thorium 230 2.8E-16 uCi/mL
Thorium 230 precision (±) 5.3E-17 uCi/mL
Thorium 230 MDC 1.7E-18 uCi/mL
Thorium 232 6.6E-18 uCi/mL
Thorium 232 precision (±) 1.9E-18 uCi/mL
Thorium 232 MDC 1.3E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1250 pCi/Filter
Lead 210 precision (±) 373 pCi/Filter
Lead 210 MDC 42.9 pCi/Filter
Radium 226 59.2 pCi/Filter
Radium 226 precision (±) 12.1 pCi/Filter
Radium 226 MDC 1.9 pCi/Filter
Thorium 230 36.7 pCi/Filter
Thorium 230 precision (±) 7.0 pCi/Filter
Thorium 230 MDC 0.22 pCi/Filter
Thorium 232 0.87 pCi/Filter
Thorium 232 precision (±) 0.25 pCi/Filter
Thorium 232 MDC 0.18 pCi/Filter
Uranium, Activity 51.4 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.6E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 5.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 9.2E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.1E-01 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01 /06/20
DateReceived: 01/13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 14:53 / meh
SW6020 01/24/20 14:53 / meh
E909.0 02/10/20 02:52 / ajl
E909.0 02/10/20 02:52 / ajl
E909.0 02/10/20 02 :52 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07 /20 09:45 / dmf
RADCALC 01 /31 /20 15:07 / dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 12 of 40
EN:RGY
11 .,1
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
NIA uCi/mL
4.3E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
132780300 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 / dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 13 of 40
EI\ERGY
, • (, I j ~ ,•, I { ) l I, '
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-6
REPORT DATE: November 11, 2019
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl9100256-005 nalu 7E-17
3rd Quarter 2019 23°Th 8E-17
Air Volume in mLs 226Ra SE-17
l.18E+l 1 z10Pb 8E-15
232Th 4E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
2E-17
2E-17
2E-15
2E-18
*Effluent Concentration from the NEW IO CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 7E-02
2E-18 IE-16 3E-14 3E-OJ
2E-17 IE-16 9E-13 6E-03
3E-16 2E-15 6E-13 IE+OO
IE-18 NIA 6E-15 7E-02
Page 17 of 40
El'J:RGY
I • I •
Trust our People. Trust our Data.
www.energylab com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-005
Client Sample ID: BHV-6
Analyses Result Units
METALS, IN AIR
Uranium ND mg/L
Uranium, Activity ND uCi/ml
RADIONUCLIDES -IN AIR
Lead 210 8.1E-15 uCi/mL
Lead 210 precision (±) 2.4E-15 uCi/mL
Lead 210 MDC 2.7E-16 uCi/mL
Radium 226 5.0E-17 uCi/mL
Radium 226 precision (±) 1.9E-17 uCi/mL
Radium 226 MDC 1.8E-17 uCi/mL
Thorium 230 8.0E-17 uCi/mL
Thorium 230 precision (±) 1.5E-17 uCi/mL
Thorium 230 MDC 1.8E-18 uCi/mL
Thorium 232 4.0E-18 uCi/mL
Thorium 232 precision (±) 1.5E-18 uCi/mL
Thorium 232 MDC 1.3E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 957 pCi/Filter
Lead 210 precision (±) 286 pCi/Filter
Lead 210 MDC 31.5 pCi/Filter
Radium 226 5.9 pCi/Filter
Radium 226 precision (±) 2.3 pCi/Filter
Radium 226 MDC 2.1 pCi/Filter
Thorium 230 9.4 pCi/Filter
Thorium 230 precision (±) 1.8 pCi/Filter
Thorium 230 MDC 0.21 pCi/Filter
Thorium 232 0.47 pCi/Filter
Thorium 232 precision (±) 0. 18 pCi/Filter
Thorium 232 MDC 0.15 pCi/Filter
Uranium, Activity 8.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.3E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 6.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 2.7E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 7.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 11/11/19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 10/30/19 21 : 19 / meh
SW6020 10/30/19 21 :19 / meh
E909.0 10/23/19 22: 18 / ajl
E909.0 10/23/19 22: 18 / ajl
E909.0 10/23/19 22: 18 / ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 I ajl
E908.0 10/23/19 17:16 / nsr
E908.0 10/23/19 17: 16 / nsr
E908.0 10/23/19 17:16 / nsr
E908.0 10/23/19 17:16 / nsr
E908.0 10/23/19 17:16 / nsr
E908.0 10/23/1917:16 / nsr
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911:08 / sec
RADCALC 11/06/1911:08 /sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 15 of40
EI\ERGY .· . . '
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
7.0E-02 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
118315000 L
Qualifiers RL
MCU
ReportDate: 11/11/19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 :08 / sec
11/06/19 11 :08 / sec
11 /06/19 11 : 08 / sec
11/06/19 11 :08 / sec
09/30/19 00: 00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 16 of 40
EN:RGY
,, I ,,,\( '
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
• HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV-6
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C200 I 0402-005 na,u 2E-16
4th Quarter 2019 230Tb IE-16
Air Volume in mLs 226Ra IE-16
l.32E+l l 210Pb IE-14
232Tb 4E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
3E-l7
3E-17
4E-15
IE-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
•
'1
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-l4 2E-Ol
2E-18 IE-16 3E-14 SE-01
2E-17 IE-16 9E-13 2E-02
4E-16 2E-15 6E-13 2E+OO
IE-18 NIA 6E-15 6E-02
Page 17 of 40
EI\ERGY •' Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, ,MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-005
Client Sample ID: BHV-6
Analyses Result Units
METALS, IN AIR
Uranium 2.3E-10 mg/L
Uranium, Activity 1 .6E-16 uCi/mL
RADIONUCLIDE$ -IN AIR
Lead 210 1.1E-14 uCi/mL
Lead 210 precision(±) 3.2E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 1.4E-16 uCi/mL
Radium 226 precision (±) 3.4E-17 uCi/mL
Radium 226 MDC 1.5E-17 uCi/mL
Thorium 230 1.4E-16 uCi/mL
Thorium 230 precision (±) 2.7E-17 uCi/mL
Thorium 230 MDC 1.6E-18 uCi/mL
Thorium 232 3.8E-18 uCi/mL
Thorium 232 precision (±) 1.4E-18 uCi/mL
Thorium 232 MDC 1.2E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1570 pCi/Filter
Lead 210 precision(±) 468 pCi/Filter
Lead 210 MDC 47.8 pCi/Filter
Radium 226 18.7 pCi/Filter
Radium 226 precision (±) 4.5 pCi/Filter
Radium 226 MDC 2.0 pCi/Filter
Thorium 230 18.9 pCi/Filter
Thorium 230 precision (±) 3.6 pCi/Filter
Thorium 230 MDC 0.21 pCi/Filter
Thorium 232 0.50 pCi/Filter
Thorium 232 precision (±) 0.18 pCi/Filter
Thorium 232 MDC 0.16 pCi/Filter
Uranium, Activity 20.9 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.0E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 2.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.8E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 6.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 14:57 I meh
SW6020 01/24/20 14:57 I meh
E909.0 02/10/20 03: 10 / ajl
E909.0 02/10/20 03: 10 / ajl
E909.0 02/10/20 03: 10 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 01 /31 /20 15:07 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07120 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detEJcted at the Reporting Limit (RL)
Page 15 of40
EI\ERGY
j , ,,
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
NIA uCi/mL
1.8E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
132204000 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 / dmf
02/07/20 09:47 I dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 16 of 40
EN:RGY
,\l l( )L, r,, 1 ,r.111
Trust our People. Trust our Data.
www.energylab.com ,( I t.lr"t) 111/'( ~r r!.H,
Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HlGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-7
REPORT DATE: November 11, 2019
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl 9100256-006 ""U 2E-16
3rd Quarter 2019 2,oTh IE-16
Air Volume in mLs 226Ra 3E-16
1.20E+ll 210Pb IE-14
232Th ?E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
2E-17
7E-17
3E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2E-01
2E-18 IE-16 3E-14 4E-Ol
2E-17 IE-16 9E-13 4E-02
3E-16 2E-15 6E-13 2E+OO
IE-18 NIA 6E-15 IE-01
Page 20 of 40
EN:RGY . '
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-006
Client Sample ID: BHV-7
Analyses
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
Thorium 232
Thorium 232 precision (±)
Thorium 232 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
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Uranium, Activity
Result Units
2.9E-10 mg/L
1.9E-16 uCi/mL
1.0E-14 uCi/mL
3.0E-15 uCi/mL
2.9E-16 uCi/mL
3.4E-16 uCi/mL
7.3E-17 uCi/mL
1.7E-17 uCi/mL
1.2E-16 uCi/mL
2.2E-17 uCi/mL
2.0E-18 uCi/mL
6.7E-18 uCi/mL
1.8E-18 uCi/mL
1.1E-18 uCi/mL
1210 pCi/Filter
363 pCi/Filter
35.2 pCi/Filter
40.8 pCi/Filter
8.7 pCi/Filter
2.0 pCi/Filter
14.0 pCi/Filter
2. 7 pCi/Filter
0.24 pCi/Filter
0.80 pCi/Filter
0.22 pCi/Filter
0.13 pCi/Filter
23.2 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF
Lead 210, EFF Day
Lead 210, LLD
Radium 226, % of EFF
Radium 226, EFF Week
Radium 226, LLD
Thorium 230, % of EFF
Thorium 230, EFF Year
Thorium 230, LLD
Thorium 232, % of EFF
Thorium 232, EFF Year
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
1.7E+OO %
6.0E-13 uCi/mL
2.0E-15 uCi/mL
4.0E-02 %
9.0E-13 uCi/mL
1.0E-16 uCi/mL
3.9E-01 %
3.0E-14 uCi/mL
1.0E-16 uCi/mL
1.1E-01 %
6.0E-15 uCi/mL
MDC -Minimum detectable concentration
Qualifiers RL
1.5E-10
1.0E-16
0.20
MCL/
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
SW6020
SW6020
E909.0
E909.0
E909.0
E903.0
E903.0
E903.0
E908.0
E908.0
E908.0
E908.0
E908.0
E908.0
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
RADCALC
11 /02/19 14:20 / meh
11 /02/19 14:20 / meh
10/23/19 22:34 / ajl
10/23/19 22:34 / ajl
10/23/19 22:34 / ajl
10/22/19 12:02 / ajl
10/22/19 12:02 / ajl
10/22/19 12:02 / ajl
10/23/19 17:17 / nsr
10/23/19 17: 17 / nsr
10/23/19 17: 17 / nsr
10/23/1917:17 / nsr
10/23/19 17: 17 / nsr
10/23/19 17: 17 / nsr
11/06/19 10:57 / sec
11 /06/19 10:57 I sec
11/06/19 10:57 / sec
11 /06/19 10:57 I sec
11 /06/19 10:57 I sec
11/06/19 10:57 / sec
11 /06/19 10:57 / sec
11/06/19 10:57 / sec
11 /06/19 10:57 / sec
11 /06/19 10:57 I sec
11/06/19 10:57 / sec
11 /06/19 10:57 I sec
11 /06/19 10:57 / sec
11 /06/19 11 : 08 / sec
11 /06/19 11 :08 / sec
11 /06/19 11 :08 / sec
11 /06/19 11 : 08 / sec
11/06/1911 :08 / sec
11/06/19 11 :08 / sec
11/06/1911 :08 / sec
11 /06/19 11 : 08 / sec
11/06/19 11 :08 / sec
11/06/1911 :08 / sec
11 /06/19 11 : 08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of40
EN:RGY
, I ,,II
Im~
----~--
Trust our People. Trust our Data.
www energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
2.2E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
119824200 L
Qualifiers RL
MCU
Report Date: 11 /11 /19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 :08 / sec
11 /06/19 11 :08 / sec
11/06/19 11 :08 / sec
11 /06/19 11 :08 / sec
09/30/19 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of 40
EI\ERGY
, (I•" 1,
/
Trust our People. Trust our Data.
www.energylab.com
Toll Free, 888.235.0515 • 307.235.0515 • F, 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
"
,, CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV-7
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration
Air Volume Radionuclide µCi/mL
C20010402-006 "''U IE-16
4th Quarter 2019 230Th SE-17
Air Volume in mLs 226Ra IE-16
l.33E+l l 210Pb IE-14
232Th 2E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
9E-18
3E-17
3E-15
IE-18
*Effluent Concentration from the NEW IO CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA lE-16 9E-14 IE-01
2E-18 IE-16 3E-14 2E-01
IE-17 lE-16 9E-13 IE-02
3E-16 2E-15 6E-13 2E+OO
2E-18 NIA 6E-15 3E-02
Page 20 of 40
EN:RGY . ,,
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-006
Client Sample ID: BHV-7
Analyses Result Units Qualifiers
METALS, IN AIR
Uranium 1.5E-10 mg/L
Uranium, Activity 1.0E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.0E-14 uCi/mL
Lead 210 precision (±) 3.1 E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 1.3E-16 uCi/mL
Radium 226 precision (±) 3.1 E-17 uCi/mL
Radium 226 MDC 1 .4E-17 uCi/mL
Thorium 230 4.9E-17 uCi/mL
Thorium 230 precision (±) 9.3E-18 uCi/mL
Thorium 230 MDC 1.9E-18 uCi/mL
Thorium 232 1.6E-18 uCi/mL
Thorium 232 precision (±) 1.2E-18 uCi/mL
Thorium 232 MDC 1.7E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1470 pCi/Filter
Lead 210 precision (±) 439 pCi/Filter
Lead 210 MDC 46.1 pCi/Filter
Radium 226 17.3 pCi/Filter
Radium 226 precision (±) 4.2 pCi/Filter
Radium 226 MDC 1.9 pCi/Filter
Thorium 230 6.6 pCi/Filter
Thorium 230 precision (±) 1.2 pCi/Filter
Thorium 230 MDC 0.26 pCi/Filter
Thorium 232 0.22 pCi/Filter
Thorium 232 precision (±) 0.16 pCi/Filter
Thorium 232 MDC 0.23 pCi/Filter
Uranium, Activity 13.5 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF
Lead 210, EFF Day
Lead 210, LLD
Radium 226, % of EFF
Radium 226, EFF Week
Radium 226, LLD
Thorium 230, % of EFF
Thorium 230, EFF Year
Thorium 230, LLD
Thorium 232, % of EFF
Thorium 232, EFF Year
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
1.8E+OO %
6.0E-13 uCi/mL
2.0E-15 uCi/mL
1.0E-02 %
9.0E-13 uCi/mL
1.0E-16 uCi/mL
1.6E-01 %
3.0E-14 uCi/mL
1.0E-16 uCi/mL
3.0E-02 %
6.0E-15 uCi/mL
U -Not detected at Minimum Detectable Concentration
(MDC)
u
u
MCL/
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
Method Analysis Date I By
SW6020 01/24/20 15:02 / meh
SW6020 01/24/20 15:02 I meh
E909.0 02/10/20 03:24 / ajl
E909.0 02/10/20 03:24 / ajl
E909.0 02/10/20 03:24 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 I nsr
E908.0 02/05/20 13:09 I nsr
E908.0 02/05/20 13:09 I nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13: 09 / nsr
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 01 /31 /20 15:07 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 18 of 40
EN:RGY
., ,11
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.1E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
133462200 L
Qualifiers RL
MCU
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01/13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 19 of 40
EN:RGY
;\ 1 l d' • I , 1,
Trust our People. Trust our Data.
www.energylab.com WY Toll Free: 888.235.0515 • 307.235.0515 • F: 307.234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: BHV-8
REPORT DATE: November 11, 2019
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
CI9100256-007 nalu IE-16
3rd Quarter 2019 23°'fh 2E-16
Air Volume in mLs 226Ra l.lE-15
l.19E+l 1 210Pb IE-14
232Th 9E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
SE-17
2E-16
4E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2E-01
2E-18 IE-16 3E-14 SE-01
2E-17 IE-16 9E-13 l.3E-01
6E-17 2E-15 6E-13 2E+OO
IE-18 NIA 6E-15 2E-Ol
Page 23 of 40
EN:RGY
I I I I
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium 2.0E-10 mg/L
Uranium, Activity 1.4E-16 uCi/mL
RADIONUCLIDE$ -IN AIR
Lead 210 1.4E-14 uCi/mL
Lead 210 precision (±) 4.0E-15 uCi/mL
Lead 210 MDC 6.2E-17 uCi/mL
Radium 226 1.1E-15 uCi/mL
Radium 226 precision (±) 2.2E-16 uCi/mL
Radium 226 MDC 1.8E-17 uCi/mL
Thorium 230 2.5E-16 uCi/mL
Thorium 230 precision (±) 4.7E-17 uCi/mL
Thorium 230 MDC 1.9E-18 uCi/mL
Thorium 232 9.0E-18 uCi/mL
Thorium 232 precision (±) 1. 7E-18 uCi/mL
Thorium 232 MDC 1.4E-18 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 1640 pCi/Filter
Lead 210 precision(±) 482 pCi/Filter
Lead 210 MDC 7.4 pCi/Filter
Radium 226 136 pCi/Filter
Radium 226 precision (±) 26.5 pCi/Filter
Radium 226 MDC 2.2 pCi/Filter
Thorium 230 29.5 pCi/Filter
Thorium 230 precision (±) 5.6 pCi/Filter
Thorium 230 MDC 0.23 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.20 pCi/Filter
Thorium 232 MDC 0.16 pCi/Filter
Uranium, Activity 16.5 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.3E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 1.3E-01 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 8.3E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.5E-01 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 11/11/19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 11/02/1914:36 / meh
SW6020 11/02/19 14:36 / meh
E909.0 10/24/19 02:50 I ajl
E909.0 10/24/19 02:50 I ajl
E909.0 10/24/19 02:50 I ajl
E903.0 10/22/19 12:02 I ajl
E903.0 10/22/19 12:02 / ajl
E903.0 10/22/19 12:02 I ajl
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17: 17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 I nsr
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 I sec
RADCALC 11/06/1910:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911:08 / sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/1911 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11/06/1911 :08 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 21 of 40
EN:RGY
• I, I I
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C19100256-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.5E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
119027300 L
Qualifiers RL
MCU
Report Date: 11/11/19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11 /06/19 11 : 08 / sec
11 /06/19 11 :08 / sec
11 /06/19 11 : 08 / sec
11/06/19 11 :08 / sec
09/30/19 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of 40
EN:RGY ,, ' . ...
Trust our People. Trust our Data.
www.energylab.com
Toll Free: 888.235.0515 • 307 .235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
--HIGH VOLUME AIR SAMPLING REPORT .,
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: BHV-8
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C200 !0402-007 natu 4E-17
4th Quarter 2019 230Th 4E-17
Air Volume in mLs 226Ra IE-16
l.33E+ll 210Pb 7E-15
232Th 2E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
N/A
7E-18
3E-17
2E-15
IE-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 4E-02
2E-18 IE-16 3E-14 IE-01
IE-17 IE-16 9E-13 IE-02
3E-16 2E-15 6E-13 IE+OO
IE-18 N/A 6E-15 4E-02
Page 23 of 40
EN:RGY . . '
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium ND mg/L
Uranium, Activity ND uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 6.2E-15 uCi/mL
Lead 210 precision(±) 1.9E-15 uCi/mL
Lead 210 MDC 2.6E-16 uCi/mL
Radium 226 9.5E-17 uCi/mL
Radium 226 precision (±) 2.6E-17 uCi/mL
Radium 226 MDC 1.4E-17 uCi/mL
Thorium 230 3.6E-17 uCi/mL
Thorium 230 precision (±) 6.8E-18 uCi/mL
Thorium 230 MDC 1.8E-18 uCi/mL
Thorium 232 2.4E-18 uCi/mL
Thorium 232 precision (±) 1.1E-18 uCi/mL
Thorium 232 MDC 1.3E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 867 pCi/Filter
Lead 210 precision(±) 260 pCi/Filter
Lead 210 MDC 36.4 pCi/Filter
Radium 226 12.7 pCi/Filter
Radium 226 precision (±) 3.4 pCi/Filter
Radium 226 MDC 1.9 pCi/Filter
Thorium 230 4.8 pCi/Filter
Thorium 230 precision (±) 0.91 pCi/Filter
Thorium 230 MDC 0.24 pCi/Filter
Thorium 232 0.32 pCi/Filter
Thorium 232 precision (±) 0.15 pCi/Filter
Thorium 232 MDC 0.18 pCi/Filter
Uranium, Activity 5.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.1E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 1.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.2E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 4.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte Reporting Limit
Definitions: QCL -Quality Control Limit
Qualifiers
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 15:23 / meh
SW6020 01/24/20 15:23 / meh
E909.0 02/10/20 03:39 / ajl
E909.0 02/10/20 03:39 / ajl
E909.0 02/10/20 03:39 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02107/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 01/31/20 15:07 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02107/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02107/20 09:47 I dmf
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 21 of 40
EN:RGY
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
4.0E-02 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
133118400 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01 /06/20
DateReceived: 01/13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
02/07/20 09:47 I dmf
01/06/20 00:00 I sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 22 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 888.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
November 11 , 2019
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C19100256
Project Name: 3rd Quarter Air 2019
Quote ID: C5470
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 10/3/2019 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C19100256-001 BHV-1 09/30/19 00:00 10/03/19 Filter Composite of two or more samples
Client Provided Field Parameters
Metals, Total
Digestion, Total Metals,
Radiochemistry
Radiochemistry Air Filter Compliance
Calculations
RAD-AIR, Routine Radiological
Reports
RAD Alternate Unit Reporting Air
Filters
Lead 210
Radium 226
Thorium, Isotopic
C 191 00256-002 BHV-2 09/30/19 00:00 10/03/19 Filter Same As Above
C 191 00256-003 BHV-4 09/30/19 00:00 10/03/19 Filter Same As Above
C 191 00256-004 BHV-5 09/30/19 00:00 10/03/19 Filter Same As Above
C 191 00256-005 BHV-6 09/30/19 00:00 10/03/19 Filter Same As Above
C19100256-006 BHV-7 09/30/19 00:00 10/03/19 Filter Same As Above
C19100256-007 BHV-8 09/30/19 00:00 10/03/19 Filter Same As Above
C 19100256-008 Blanks 09/30/19 00:00 10/03/19 Filter Same As Above
The analyses presented in this report were performed by Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601 , unles
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. Any issues encountered during sample receipt are documented in the Work Order Receipt Checklist.
The results as reported relate only to the item(s) submitted for testing. This report shall be used or copied only in its entirety. Energy
Laboratories, Inc. is not responsible for the consequences arising from the use of a partial report.
If you have any questions regarding these test results, please contact your Project Manager .
Report Approved By:
Digitally signed by
Tracey Archer
Date: 2019.11 .11 15:31: 17 -07:00
Page 1 of40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.4 72.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
3rd Quarter Air 2019
C19100256
ORIGINAL SAMPLE SUBMITIAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (±2°C)
Report Date: 11 /11 /19
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 acce1ptable 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 ELI 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 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
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
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C19100256-008
Client Sample ID: Blanks
Analyses Result Units Qualifiers
METALS, IN AIR
Uranium 0.00091 mg/L L
Uranium, Activity 6.2E-10 uCi/mL L
RADIONUCLIDES -IN AIR
Lead 210 -5.0E-09 uCi/mL u
Lead 210 precision(±) 5.0E-09 uCi/mL
Lead 210 MDC 8.5E-09 uCi/mL
Radium 226 1.4E-09 uCi/mL u
Radium 226 precision (±) 1.1 E-09 uCi/mL
Radium 226 MDC 2.3E-09 uCi/mL
Thorium 230 5.9E-10 uCi/mL
Thorium 230 precision (±) 2.6E-10 uCi/mL
Thorium 230 MDC 3.4E-10 uCi/mL
Thorium 232 O.OE+OO uCi/mL u
Thorium 232 precision (±) 1.3E-10 uCi/mL
Thorium 232 MDC 2.8E-10 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 -4.7 pCi/Filter u
Lead 210 precision (±) 4. 7 pCi/Filter
Lead 210 MDC 8.1 pCi/Filter
Radium 226 1.3 pCi/Filter u
Radium 226 precision (±) 1.1 pCi/Filter
Radium 226 MDC 2.1 pCi/Filter
Thorium 230 0.56 pCi/Filter
Thorium 230 precision (±) 0.24 pCi/Filter
Thorium 230 MDC 0.32 pCi/Filter
Thorium 232 0 pCi/Filter u
Thorium 232 precision (±) 0.13 pCi/Filter
Thorium 232 MDC 0.27 pCi/Filter
Uranium, Activity 0.59 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF -8.0E+05 %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 1.6E+05 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 2.0E+06 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF O.OE+OO %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
MCL/
RL QCL
0.00035
2.4E-10
0.20
Report Date: 11 /11 /19
Collection Date: 09/30/19
DateReceived: 10/03/19
Matrix: Filter
Method Analysis Date / By
SW6020 11 /02/19 14:40 / meh
SW6020 11 /02/19 14:40 I meh
E909.0 10/23/19 22:47 I ajl
E909.0 10/23/19 22:47 I ajl
E909.0 10/23/19 22:47 / ajl
E903.0 10/22/19 12:03 / ajl
E903.0 10/22/19 12:03 / ajl
E903.0 10/22/19 12:03 / ajl
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 I nsr
E908.0 10/23/19 17:17 / nsr
E908.0 10/23/19 17:17 / nsr
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11/06/19 10:57 I sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 10:57 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :OB / sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 I sec
RADCALC 11/06/19 11:08 / sec
RADCALC 11 /06/19 11 :08 I sec
RADCALC 11 /06/19 11 :08 I sec
RADCALC 11 /06/19 11 :08 I sec
RADCALC 11/06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
L -Lowest available reporting limit for the analytical method
used.
Page 24 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2019
Lab ID: C 19100256-008
Client Sample ID: Blanks
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
NIA uCi/mL
6.9E+05 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1 L
Qualifiers RL
MCU
Report Date: 11/11/19
Collection Date: 09/30/19
Date Received: 10/03/19
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 :08 / sec
RADCALC 11 /06/19 11 : 08 / sec
RADCALC 11 /06/19 11 :08 / sec
FIELD 09/30/19 00:00, •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 25 of 40
EN:RGY
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Toll free: 888.235.0515 • 307 .235.0515 • f: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2019
SAMPLE ID: Blanks
REPORT DATE: November 11, 2019
Quartermate Sampled Concentration Radionuclide Air Volume µCi/mL
Cl9100256-008 natu 5E-I8
3rd Quarter2019 23°'fh 5E-18
Air Volume in mLs 226Ra lE-17
l.24E+l I 210Pb -4E-17
232Th OE+OO
Counting L.L.D.+ Precision MDC µCi/mL
µCi/mL µCi/mL
NIA NIA JE-16
2E-18 3E-18 IE-16
9E-18 2E-17 JE-16
4E-17 ?E-17 2E-15
IE-18 2E-18 NIA
NOTE: This report uses 124,000,000 L air for comparison purposes, the routine report uses a 1 L system default.
+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, Thorium-232
Week for Radium-226
Day for Lead-210
Effluent Cone.* % Effluent
µCi/mL Concentration
9E-14 5E-03
3E-14 2E-02
9E-13 JE-03
6E-13 -6E-03
6E-15 OE+OO
Page 26 of 40
EN:RGY
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19100256 Report Date: 11 /08/19 ------------
Analyte Count Result Units
Method: E903.0
Lab ID: LCS-55515
Radium 226
Lab ID: MB-55515
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C19100175-002AMS
Radium 226
Lab ID: C19100175-002AMSD
Radium 226
Laboratory Control Sample
105 pCi/L
3 Method Blank
0.2 pCi/L
0.3 pCi/L
0.4 pCi/L
Sample Matrix Spike
6.15E-05 pCi/L
Sample Matrix Spike Duplicate
6.79E-05 pCi/L
Lab ID: C19100408-001ADUP 3 Sample Duplicate
Radium 226 6.1 OE-08 pCi/L
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
2.72E-08
4.09E-08
pCi/L
pCi/L
RL %REC Low Limit High Limit
Run: G542M_191016C
105 80 120
Run: G542M_191016C
Run: G542M_ 191016C
110 70 130
Run: G542M_ 191016C
122 70 130
Run: G542M_ 191016C
ND -Not detected at the reporting limit.
RPD RPDLimit Qual
9.9
20
Batch: 55515
10/22/19 10:22
10/22/19 10:22
u
10/22/19 10:22
10/22/19 10:22
20
10/22/19 12:03
20
U -Not detected at minimum detectable concentration
Page 27 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19100256 Report Date: 11 /08/19
Method: E908.0
Lab ID: MB-55515
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: LCS-55515
Thorium 230
Lab ID: C19100408-001AMS
Thorium 230
Count Result Units
6 Method Blank
0.2 pCi/L
0.2 pCi/L
0.3 pCi/L
0.2 pCi/L
0.1 pCi/L
0.2 pCi/L
Laboratory Control Sample
48.4 pCi/L
Sample Matrix Spike
1.88E-06 pCi/L
Lab ID: C1910040B-001AM5D Sample Matrix Spike Duplicate
Thorium 230 1.95E-06 pCi/L
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
RL %REC Low Limit High Limit
Run: EGG-ORTEC_ 191022A
Run: EGG-ORTEC_ 191022A
101 80 120
Run: EGG-ORTEC_ 191022A
98 70 130
Run: EGG-ORTEC_ 191022A
101 70 130
ND -Not detected at the reporting limit.
RPO RPDLimit
3.9
Batch: 55515
10/23/19 17:17
u
u
10/23/19 17:17
10/23/19 17:17
10/23/19 17:17
20
U -Not detected at minimum detectable concentration
Page 28 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19100256 Report Date: 11 /08/19 ,----------------
Analyte Count Result Units
Method:
Lab ID:
Lead 210
E909.0
LCS-55515
Lab ID: MB-55515
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Lab ID: C19100175-001AMS
Lead 210
Lab ID: C19100175-001 AMSD
Lead 210
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Laboratory Control Sample
156 pCi/L
Method Blank
-0.4 pCi/L
1 pCi/L
2 pCi/L
Sample Matrix Spike
9.05E-05 pCi/L
Sample Matrix Spike Duplicate
9.29E-05 pCi/L
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: TRICARB LSC_191016A
86 80 120
Run: TRICARB LSC_191016A
Run: TRICARB LSC_191016A
99 70 130
Run: TRICARB LSC_191016A
102 70 130 2.7
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 55515
10/23/19 00:35
10/23/1901 :44
u
10/23/19 11 :00
10/23/19 11 :58
20
Page 29 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19100256 Report Date: 11 /06/19
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method:
Lab ID:
Uranium
SW6020
QCS
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-55515
Uranium
Lab ID: LCS2-55515
Uranium
Lab ID: C19100175-001ADIL
Uranium
Lab ID: C19100175-001APDS
Uranium
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-55515
Uranium
Lab ID: C19100256-006ADIL
Uranium
Lab ID: C19100256-00SAPDS
Uranium
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Initial Calibration Verification Standard
0.0187 mg/L 0.00030
Interference Check Sample A
-3.65E-06 mg/L 0.00030
Interference Check Sample AB
-9.05E-06 mg/L 0.00030
Method Blank
0.0003 mg/L 0.0001
Laboratory Control Sample
0.100 mg/L 0.00014
Serial Dilution
9.71E-10 mg/L 1.5E-10
Post Digestion/Distillation Spike
1.21E-08 mg/L 1.5E-10
Initial Calibration Verification Standard
0.0180 mg/L 0.00030
Interference Check Sample A
1.17E-05 mg/L 0.00030
Interference Check Sample AB
9.14E-07 mg/L 0.00030
Method Blank
0.0003 mg/L 0.0001
Serial Dilution
3.10E-10 mg/L 1.5E-10
Post Digestion/Distillation Spike
6.36E-10 mg/L 1.5E-10
94 90
Analytical Run: ICPMS5-C_191030A
10/30/19 15:16
110
10/30/19 15:51
10/30/19 15:56
Run: ICPMS5-C_191030A
Batch: 55515
10/30/19 19:51
Run: ICPMS5-C_191030A 10/30/19 19:56
95 85 115
Run: ICPMS5-C_191030A 10/30/19 20:04
0 0 20 N
Run: ICPMS5-C_ 191030A 10/30/19 20:09
94 75 125
Analytical Run: ICPMS5-C_ 191101 A
11/01/19 18:58
90 90 110
11/01/19 19:43
11/01/19 19:48
Batch: 55515
Run: ICPMS5-C_ 191101 A 11/02/19 14:16
Run: ICPMS5-C_ 191101A 11/02/19 14:24
0 0 7.9 20
Run: ICPMS5-C 191101A 11/02/19 14:28 -
81 75 125
ND -Not detected at the reporting limit.
N -The analyte concentration was not sufficiently high to calculate a
RPD for the serial dilution test.
Page 30 of 40
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Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: Steve Carlston
Reviewed Date: 10/6/2019
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 D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
·c
Yes D
Yes D
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
C19100256
Date Received: 10/3/2019
Received by:
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
Carrier name:
Not Present D
Not Present D
Not Present 0
Not Applicable 0
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 31 of 40
r· --
(_~RGYFUELS RESOURCES
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: ..;;;E;.;.;n_er.g""'y_L_ab_o_ra-t;;..;;ie_s _________ Contact: Ta;..nn_e __ r-H_ol-lid-a;.;il,y _____ _
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY. 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
ProJect Samplers Name Samnlera Signature
3rd Quarter Air 2019 Tanner Hollidav I :\,.~UICs Ll/////
V
Time
Sample ID Date Collected Collected Laboratorv Analvsis Renuested
BHV-1 7/1/2019-9/30/2019 NA U-NAT, TH-230. Ra-226, Pb-210, TH-232
BHV-2 7/1/2019-9/30/2019 NA U-NAT. TH-230, Ra-226, Pb-210. TH-232
BHV-4 7/1/2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-5 7/1 /2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-6 7/1/2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-7 7 /1/2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-8 7 /1 /2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
Blanks 7/1/2019-9/30/2019 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
f"' \C\ \ 1-. ")~::'-l.-9
Comments: Please send report to Kathy Weinel at [e-mail]
Relinquished By:{Signature) Date/Time Received By:(Signature)
10/2/2019
1130
Date/Time rc->11
Page 32 of 40
i..T.;..-~.~~~.-~.~
~
.t..:,_. "':>-'-. -~,:-~ ~ C'i ,': t{:4~~ ,.-;;,._:~
Week i mt~ I Strut
# Number Date
9673045 7/1/2019
2 9673037 7/8/2019
3 9673029 7/15/2019
4 9673016 7/22/2019
s 9673013 7/29/2019
6 9673005 8/5/2019
7 9429697 8/12/2019
8 9429689 8/19/2019
9 9429681 8/26/2019
10 9429673 9/3/2019
11 9429665 9/9/2019
12 9429652 9/16/2019
I
Energy Fuels Resources -White Mesa Mill
Period: July l 2019 -September 30 2019
Mi
Stop I Start I Stop -S1aning
Date Time Time Manometer
(in. H20)
7/8/2019 142.84 311.32 10108.8 4.0
7/15/2019 311.32 480.19 10132.2 4.0
7/22/2019 480.19 650.74 10233.0 4.0
7/29/2019 650.74 815.2 9867.6 4.0
815/2019 815.2 984.14 10136.4 4.0
8/12/2019 984.14 1151.49 10041.0 4.5
8/19/2019 1151.49 1318.43 10016.4 4.5
8/26/2019 1318.43 1486.3 10072.2 4.0
9/3/2019 l4S6.3 1678.56 11535.6 4.0
9/9/2019 1678.56 1823.38 8689.2 4.0
9/16/2019 1823.38 1993.99 10236.6 4.0
9/23/2019 1993.99 2158.79 9888.0 4.0
2326.97 10090.8 3.5
,tals 131047.8 ..
Avera_g_es 10080.6 4.0
Calibration Date: 10/1/2018
Calibration Slope & Intercept:
Orifice SIN: 8091779
Mi
Stopping
Manometer
(in. H20)
4.0
4.0 4.0 25.0 298.1 621.5 I.I I
4.0 4.0 26.5 299.7 619.4 1.12
4.0 4.0 25.2 298.3 622.5 1.11
4.0 4.0 24.0 297.1 622.0 I.I I
4.0 4.3 24.6 297.7 620.57 1.15
4.0 4.3 24.6 297.7 620.42 1.15
4.0 4.0 25.1 298.2 619.51 1.12
4.0 4.0 24.9 298.1 620.95 I.I I
4.0 4.0 24.7 297.8 620.57 I.I I
4.0 4.0 18.7 291.8 621.21 1.10
4.0 4.0 17.7 290.9 618.87 1.10
4.0 3.8 17.7 290.9 617.37 1.07
.-
14.49
4.0 4.0 23.2 296.4 620.34946 I.I I
m= 1.24054 b= 0.00251
0.91 32.18 9231.9 4.4342
0.91 32.04 9283.4 4.4430
0.91 32.19 8994.4 4.4068
0.91 32.24 9254.5 4.3765
0.94 33.17 9429.9 4.3710
0.94 33.16 9405.6 4.5125
0.91 32.12 9160.7 4.5012
0.91 32.16 10506.5 4.5200
0.91 32.17 7914.4 4.5159
0.92 32.51 9423.8 4.5000
0.92 32.50 9100.8 4.5009
0.89 31.43 8981.4 4.5198
11.90 420.09 119908.5 58.022
0.92 32.31 9223.7 4.463
First Monitoring Quarter 2015
Updated: 7/30/14
4.6054 171.2 0.0185 100.5
4.5839 140.9 0.0152 101.5
4.4780 71.2 0.0079 97.9
4.5203 143.8 0.0155 100.6
4.5159 144.9 0.0154 99.6
4.6803 167.8 0.0178 99.4
4.6934 192.2 0,0210 99.9
4.7210 201.0 0.0191 114.4
4.7128 196.9 0.0249 86.2
4.6814 181.4 0.0192 101.6
4.5798 78.9 0.0087 98.1
4.7416 221.8 0.0247 JOO.I
60.061 2039.1 0.2218
4.620 156.9 o.om I 100.0
Energy Fuels Rt:Sou.rces-:-Whire Mesa Mill ___ ----Calibration Date: 10/1/2018 First Monitoring Quarter 2014
Period: July l 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
01ifice SIN: 8091779
6H 6H
Week I Filter I Start I Stop I Start Stop Slarting Stopping
# Nwnber Date Date Time Time Manometer Manome1er·
(in.H20) (in.H20)
9673044 7/1/2019 7/8/2019 10858.59 11027.04 10107.0 4.0 4.0
2 9673036 718/2019 7/15/2019 11027.04 11195.97 10135.8 4.5 4.0 4.3 25.0 298.1 621 . .54 1.15 0.94 33.17 9519.9 4.4288 4.7185 289.7 0.0304 100.6
3 9673028 7/15/2019 7/22/2019 11195.97 11367.46 10289.4 4.0 4.0 4.0 26.5 299.7 619.40 1.12 0.91 32.04 9334.5 4.4330 4.7038 270.8 0.0290 102.1
4 9673018 7/22/2019 7/29/2019 11367.46 11S30.92 9807.6 4.0 4.0 4.0 25.2 298.3 622.48 1.11 0.91 32.19 8939.7 4.4342 4.6709 236.7 0.0265 97.3
5 9673012 7/29/2019 8/512019 11530.92 11699.38 10107.6 4.0 4.0 4.0 24.0 297.1 622.05 1.11 0.91 32.24 9228.2 4.3740 4.5728 198.8 0.0215 100.3
6 9673004 8/5/2019 8/1.212019 11699.38 11867.24 10071.6 4.5 4.0 4.3 24.6 297.7 620.57 1.15 0.94 33.17 9458.6 43756 4.5695 193.9 0.0205 99.9
7 9429696 8112/2019 8/19/2019 11867.24 12034.17 10015.S 4.5 4.0 4.3 24.6 297.7 620.42 1.15 0.94 33.16 9405.1 4.4938 4.7424 248.6 0.0264 99.4
8 9429688 8/19/2019 8/261.2019 12034.17 12201.88 10062.6 4.0 4.0 4.0 25.1 198.2 619.51 1.12 0.91 32.12 9152.0 4.5011 4.8540 352.9 0.0386 99.8
9 9429680 8/26/2019 9/3/2019 12201.SS 12394.97 11585.4 4.0 4.0 4.0 24.9 298.I 620.95 1.11 0.91 32.16 10551.9 4.5105 4.8345 324.0 0.0307 114.9
10 9429672 9/3/2019 9/9/2019 12394.97 12539.77 8688.0 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8157.3 4.5308 4.8663 335.5 0.041 I 86.2
11 9429664 9/9/2019 9/1612019 12539.77 12710.36 10235.4 4.0 4.0 4.0 18.7 291.8 621.21 I.ID 0.92 32.51 9422.7 4.5038 4.6146 110.8 O.OJIS 101.5
12 94296S3 9/1612019 9/23/2019 12710.36 !'2874.46 9846.0 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9062.1 4.5131 4.8507 337.6 0.0373 97.7
13 9429648 9/23/2019 9130/2019 12874.46 13042.56 10086.0 4.5 4.0 4.3 17.7 290.9 617.37 1.14 0.95 33.47 9558.0 4.5163 4.9073 391.0 0.0409 100.1 --· ---131038.2 .. 14.63 12.01 424.10 121009.6 58.061 61.700 3638.2 0.3924
10079.9 4.2 4.0 4.1 23.2 296.4 620.34946 1.13 0.92 32.62 9308.4 4.466 4.746 279.9 0_0302 I 100.0
,ts:
Insert weekly flow check values in yellow columns. .. ~-. : ~.~---: •. -·C -•• -. -
,-, q,lumns ~ calcul~. ~~ fiQ!n llle met \lllition.
Energy Fuels Resources -White Mesa Mill icalibration Date: 10/1/2018
Period: July I 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251
l1H l1H
Weeki Filla Stan Stop Stan Stop Staning Stopping
# Number Date Date Time Time Manometer Manometer
(in.11,0> (in.H,O)
9673043 7/1/2019 7/8/2019 16391.19 16559.61 10105.2 4.0 4.0
2 9673035 7/8/2019 7/15/2019 16559.61 16728.57 10137.6 5.0 4.0 4.5 25.0 298.1 621.54 1,18 0.97 34.13 9798.1 4.4382 4.6046 166.4 0.0170 100.6
3 9673027 7/15/2019 7/2212019 16728.57 16901.01 10346.4 4.0 4.0 4.0 26.5 299.7 619.40 1.12 0,91 32.04 9386.3 4.4420 4.6035 161.5 0.0172 102.6
4 9673017 7/22/2019 7/29/2019 16901.01 17056.44 9325.8 4.5 4.0 4.3 25.2 298.3 622.48 1.15 0.94 33.18 8762.7 4.4218 4.5145 92.7 0.0106 92.5
5 9673011 7/29/2019 8/5/2019 17056.44 17224.96 10111.2 4.0 4.0 4.0 24.0 297.1 622.05 I.II 0.91 32.24 9231.5 4.3816 4.5855 203.9 0.0221 100.3
6 9673003 8/5/2019 8/12/2019 17224.96 17393.94 10138.8 4.0 4.0 4.0 24.6 297.7 620.57 I.I I 0.91 32.17 9236.9 4.3755 4.5097 134.2 0.0145 100.6
7 9429695 8/12/2019 8/19/2019 17393.94 17559.73 9947.4 4.0 4.0 4.0 24.6 297.7 620.42 I.II 0.91 32.17 9061.4 4.5000 4.6453 145.3 0.0160 98.7
8 9429687 8/19/2019 8/26/2019 17559.73 17733.79 10443.6 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9498.5 4.4985 4.6841 185.6 0.0195 103.6
9 9429679 8/26/2019 9/3/2019 17733.79 17919.94 11169.0 4.0 4.0 4.0 24.9 298.1 620.95 I.I I 0.91 32.16 10172.6 4.5267 4.7025 175.8 0.0173 110.8
10 9429671 9/3/2019 9/9/2019 17919.94 18064.81 8692.2 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8161.3 4.5075 4.6643 156.8 0.0192 86.2
11 9429663 9/9/2019 9/16/2019 18064.81 18236.48 10300.2 4.0 4.0 4.0, 18.7 291.8 621.21 I.IO 0.92 32.51 9482.4 4.5073 4.6415 134.2 0.0142 102.2
12 9429654 9/16/2019 9/23/2019 18236.48 18399.9 9805.2 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9024.6 4.5051 4.6481 143.0 O.Ol58 97.3
18567.99 10085.4 4.0 4.0 4.0 17.7 290.9 617.37 I.JO 0.92 32.47 9271.5 4.4950 4.6417 146.7 0.0158 100.1
130608.0 . .. 14.60 l l.98 423.07 120305.7 58.044 60.025 1981.1 0.2139
10046.8 4.2 4.0 4.1 23.2 296.4 620.34946 1.12 0.92 32.54 9254.3 4.465 4.617 152.4 0.0165 I 99.7
mien colmn,,s-'trc calcldaled ~from ibc IIICll-swion.
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/1/2018 -I First Monitoring Quarter 2014
Period: July 1 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN: 8091779
Ml Ml
Week I Filter I Start Stop Start Stop II '-Stopping
# Number Date Dale Time Time Manometer Manometer
(in. H,O) (in.H20)
9673042 7/1/2019 7/8/2019 9473.99 9642.38 10103.4 4.5 4.0
2 9673034 718/2019 7115/2019 9642.38 981 l.37 10139.4 5.0 4,0 4.5 25.0 298.1 621.54 1.18 0.97 34.13 9799.9 4.4427 4.4909 48.2 0.0049 100.6
3 9673026 7115/2019 7/22/2019 9811.37 9983.67 10338.0 3.0 4.0 3.5 26.5 299.7 619.40 1.05 0,85 29.96 877l.8 4.4462 4.6037 157.5 0.0180 102.6
4 9673019 7122/2019 7/2912019 9983.67 10139.41 9344.4 4.0 4.0 4.0 25.2 298.3 622.48 1.11 0.91 32.19 8517.5 4.4147 4.5084 93.7 0.0110 92.7
5 9673010 7/29/2019 815/2019 10139.41 10307.8 10103.4 4.0 4.0 4.0 24.0 297.1 622.05 1.11 0.91 32.24 9224.4 4.3665 4.4903 123-8 0.0134 100.2
6 9673002 8/5/2019 8/12/2019 10307.8 10476.77 10138.2 4.0 4.0 4.0 24.6 297.7 620.57 I.II 0.91 32.17 9236.4 4.3802 4.4900 109.8 0.0119 100.6
7 9429694 8/12/2019 8119/2019 10476.77 to642.56 9947.4 4.0 4.0 4.0 24.6 297.7 620.42 I.I I 0.91 32.17 9061.4 4.5058 4.6335 127.7 0.0141 98.7
8 9429686 8119/2019 8/2612019 10642.56 10816.54 10438.8 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9494.1 4.5371 4.7165 179.4 0.0189 103.6
9 9429678 8/2612019 913/2019 10816.54 11002.77 11173.8 3.5 4.0 3.8 24.9 298.1 620.95 1.08 0.88 31.14 9853.3 4.5139 4.7190 205.1 0.0208 110.9
10 9429670 913/2019 919/2019 11002.77 11147.64 8692.2 4.0 4.0 4.0 24.7 297.8 620.57 I.I I 0.91 32.17 7917.1 4.5213 4.6889 167.6 0.0212 86.2
II 9429662 919/2019 9116/2019 11147.64 11319.7 10323.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9503.9 4.5036 4.6542 150.6 0.0158 102.4
12 9429655 9/16/2019 9/23/2019 11319.7 11482.71 9780.6 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9001.9 4.4869 4.6096 122.7 0.0136 97.0
11650.81 10086.0 4.0 4.0 4.0 17.7 290.9 617.37 I.IO 0.92 32.47 9272.1 4.5086 4.6513 142.7 0.0154 JOO.I
'otals 130609.2 ~ 14.45 11.86 418.99 119154.3 58.064 59.885 1820.8 0.1992
10046.9 4.0 4.0 4.0 23.2 296.4 620.34946 1.11 0.91 32.23 9165.7 4.466 4.607 140.1 0.0153 I 99.7
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/1/2018 I First Monitoring Quarter 2014
Period: July 1 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN: 8091779
Ml llli Week i Filter Stan Stop Stan Stop Starting Stopping
# Number Date Date Time Time Manometet Manometer
(in. H20) (in. H20)
9673041 7[1/2019 7/8/2019 25866.62 26035.06 10106.4 4.0 4.0
2 9673033 7/8/2019 7/15/2019 26035.06 26203.95 10133.4 4.5 4.0 4.3 25.0 298.1 621.54 1.15 0.94 33.17 9517.7 4.4443 4.5802 135.9 0.0143 100.5
3 9673025 7/15/2019 7/22/2019 26203.95 26376.04 10325.4 4.5 4.0 4.3 26.5 299.7 619.40 1.15 0.94 33.03 9656.0 4.4370 4.5801 143.1 0.0148 102.4
4 9673020 7/22/2019 7/29/2019 26376.04 26531.67 9337.8 4.0 4.0 4.0 25.2 298.3 622.48 I.I I 0.91 32.19 8511.5 4.4285 4.5157 87.2 0.0102 92.6
5 9673009 7/29/2019 8/5/2019 26531.67 26700.24 10114.2 4.0 4.0 4.0 24.0 297.1 622.05 I.I I 0.91 32.24 9234.3 4.3665 4.4661 99.6 0.0108 100.3
6 9673001 8/5/2019 8/12/2019 26700.24 26869.21 10138.2 4.0 4.0 4.0 24.6 297.7 620.57 I.I I 0.91 32.17 9236.4 4.3723 4.4667 94.4 0.0102 100.6
7 9429693 8/12/2019 8/19/2019 26869.21 27035.02 9948.6 4.0 4.0 4.0 24.6 297.7 620.42 I.I I 0.91 32.17 9062.5 4.5018 4.6216 119.8 0.0132 98.7
8 9429685 8/19/2019 8/26/2019 27035.02 27202.61 10055.4 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.]2 9145.4 4.4992 4.6600 160.8 0.0176 99.8
9 9429677 8/26/2019 9/3/2019 27202.61 27369.92 10038.6 3.5 4.0 3.8 24.9 298.1 620.95 1.08 0.88 31.14 8852.2 4.4984 4.6759 177.5 0.0201 99.6
10 9429669 9/3/2019 9/9/2019 0 143.82 8629.2 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8102.1 4.5330 4.6703 137.3 0.0169 85.6
11 9429661 9/9/2019 9/16/2019 143.82 315.5 10300.8 4,0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9482.9 4.5037 4.6234 119.7 0.0126 102.2
12 9429656 9/16/2019 9/23/2019 315.5 478.88 9802.8 4.0 4.0 4.0 17.7 290.9 618.87 I.JO 0.92 32.50 9022.3 4.5126 4.6320 119.4 0.0132 97.3
13 9429645 9/23/2019 9/30/2019 478.88 646.99 10086.6 4.0 4.0 4.0 17.7 290,9 617.37 1.10 0.92 32.47 9272.6 4.4983 4.6203 122.0 0.0132 100.1
Totals 129017.4 ~ -14.53 11.92 421.08 118315.0 58.036 59.670 1633.4 0.1798
Averages 9924.4 4.1 4.0 4.0 23.2 296.4 620.34946 1.12 0.92 32.39 9101.2 4.464 4.590 125.6 0.0138 I 98.5
Replaced Elapsed time indicntor on~
Energy Fuels Resources -White Mesa Mill
Period: July 1 2019 -September 30 2019
Ml Ml
Week i Filter I Stut I Stop I Stut I Starting Stopping
# Number Date Date Time Manometer Manometer
(in. H20) (in.H20)
9673040 7/112019 71812019 502.36 670.82 10107.6 4.0 4.0 4.0
2 %73032 718/2019 7115/2019 670.82 839.7 10132.8 4.0 4.0 4.0
3 9673024 71!5/2019 7/2212019 839.7 1010.29 10235.4 4.0 4.0 4.0
4 9673021 7122120!9 7/2912019 1010.29 ll74.77 9868.8 4.0 4.0 4.0
5 9673008 7/2912019 81512019 1174.77 1343.62 10131.0 4.0 4.0 4.0
6 9429700 8/512019 8/1212019 1343.62 1511.07 10047.0 4.0 4.0 4.0
7 9429692 8/1212019 8/19/2019 1511.07 1677.98 10014.6 4.0 4.0 4.0
8 9429684 811912019 8/2612019 1677.98 1845.67 10061.4 4.0 4.0 4.0
9 9429676 8/2612019 913/2019 1845.67 2038.06 11543.4 3.5 4.0 3.8
10 9429668 913/2019 919/2019 2038.06 2182.88 8689.2 4.5 4.0 4.3
11 9429660 919/2019 9116/2019 2182.88 2353.44 10233.6 4.0 4.0 4.0
9429657 9/1612019 9/23/2019 2353.44 2518.14 9882.0 4.0 4.0 4.0
2686.28 10088.4 4.5 4.0 4.3
Totals 131035.2
Avera_g_es 10019.6 I 4.0 I 4.0 4.0
Calibration Date: 1011/2018
Calibration Slope & Intercept:
Orifice SIN: 8091779
m= 1.24054 b= 0.00251
&aiiliiiF"'._~=awi:i;iii!iiil:.F Pa
Wkly.Avg.
'Pi'eSS\I~
(mrnHg)
::,:.c·.,:: :.· ;,;(;::{ jj§,
23.3 296.5 619.61 I.! I 0.91 32.21 9220.1
25.0 298.1 621.54 I.I] 0.91 32.18 9232.4 4.4217
26.5 299.7 619.40 l.!2 0.91 32.04 9285.6 4.4338
25.2 298.3 622.48 I.! I 0.91 32.19 8995.5 4.4288
24.0 297.l 622.05 I.I I 0.91 32.24 9249.6 4.3703
24.6 297.7 620.57 I.I I 0.91 32.17 9153.3 4.5192
24.6 297.7 620.42 1.11 0.91 32.17 9122.7 4.4918
25.1 298.2 619.51 1.12 0.91 32.12 9150.9 4.5080
24.9 298.1 620.95 1.08 0.88 31.!4 10179.2 4.5300
24.7 297.8 620.57 1.15 0.94 33.16 8158.4 4.4907
18.7 291.8 621.21 1.10 0.92 32.51 9421.1 4.5303
17.7 290.9 618.87 I.IO 0.92 32.50 9095.2 4.4938
17.7 290.9 617.37 1.14 0.95 33.47 9560.2 4.5091
l l 1620.34946 23.2 296.4
14.49 11.90 420.10 119824.2 58.164
I.I! 0.92 32.32 9217.2 4.474
First Monitoring Quarter 2014
Updated: 7/30/14
4.5913 169.6 0.0184 100.5
4.6223 188.5 0.0203 101.5
4.5408 112.0 0.0125 97.9
4.5169 146.6 0.0158 100.5
4.6657 146.5 0.0160 99.7
4.6206 128.8 0.0141 99.4
4.7255 217.5 0.0238 99.8
4.7355 205.5 0.0202 114.5
4.6676 176.9 0.0217 86.2
4.6917 161.4 0.0171 IOl.5
4.6648 171.0 0.0188 98.0
4.6353 126.2 0.0132 100.1
60.266 2102.7 0.2284
4.636 161.7 0.0176 100.0
;Energy Fu.els Resources -White Mesa Mill Calibration Date: 10/1/2018 I First Monitoring Quarter 2014
Period: July I 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN: 8091779
lllf lllf
Week I Filter Start Stop Start Stqp Starting Stopping
# Number Date Date Time Time Mnnomete• Mano1ooter
(in.HP) (in.H20)
1 9673039 7/1/2019 7/8/2019 7330.45 7498.94 10109.4 4.0 4.0 4.0 23.3 296.5 619.61 I.I I 0.91 32.21 9221.7 4.4299 4.5427 112.8 0.0122 100.3
2 9673031 7/8/2019 7/15/2019 7498.94 7667.82 10132.8 4.0 4.0 4.0 25.0 298.1 621.54 l.11 0.91 32.18 9232.4 4.4430 4.5605 117.5 0.0127 100.5
3 9673023 7/15/2019 7/22/2019 7W.82 7838.37 10233.0 4.0 4.0 4.0 26.5 299.7 619.40 1.12 0.91 32.04 9283.4 4.4375 4.5058 68.3 0.0074 101.5
4 9673022 7/22/2019 7/29/2019 7838.37 8002.86 9869.4 4.0 4.0 4.0 25.2 298.3 622.48 I.I! 0.91 32.19 8996.J 4.4438 4.4770 33.2 0.0037 97.9
5 9673007 7/2912019 8/5/2019 8002.86 8171.72 10131.6 3.5 4.0 3.8 24.0 297.1 622.05 1.08 0.88 31.22 8955.9 4.3620 4.4143 52.3 0.0058 100.5
6 9429699 8/5/2019 8/12/2019 8171.72 8339.16 10046.4 3.0 4.0 3.5 24.6 297.7 620.57 1.04 0.85 30.09 8560.5 4.4988 4.5784 79.6 0.0093 99.7
7 9429691 8/12/2019 8/19/2019 8339.16 8506.08 10015.2 4.0 4.0 4.0 24.6 297.7 620.42 I.I I 0.91 32.17 9123.2 4-5165 4.5869 70.4 0.0077 99.4
8 9429683 8/1912019 8/26/2019 8506.08 8673.85 10066.2 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 91SS.2 4.5102 4.6383 128.l 0.0140 99.9
9 9429675 8/26/2019 9/3/2019 8673.85 8866.21 11541.6 4.5 4.0 4.3 24.9 298.1 620.95 1.15 0.94 33.16 10836.1 4.5356 4.6539 118.3 0.0109 I 14.5
to 9429667 9/3/2019 9/9/2019 8866.21 9011.01 8688.0 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0,94 33.16 8157.3 4.4895 4.6112 121.7 0.0149 86.2
11 9429659 9/9/2019 9116/2019 !1011.01 9181.67 10239.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9426.6 4.4863 4.6289 142.6 0.0151 101.6
9346.42 9885.0 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9098.0 4.4901 4.5539 63.8 0.0070 98.l
9514.59 100!10.2 3.5 4.0 3.8 17.7 290.9 617.37 1.07 0.89 31.43 8980.9 4.5138 4.6691 155.3 0.0173 100.1
131048.4 ~ 14.39 11.81 416.98 119027.3 58.157 59.421 1263.9 0.1381
IAverages I 10080.6 3.9 4.0 4.0 23.2 296.4 620.34946 I.I 1 0.91 32.08 9155.9 4.474 4.57] 97.2 0.0106 I 100.0
CommenlS:
Insert weekly flow check values in yellow columns.
Blank Period: July 1 2019 -September 30
2019
Week Filter Start Stop Net # Number Date Date
1 9673038 01-Jul-19 08-Jul-19 4.4266
2 9673030 08-Jul-19 15-Jul-19 4.4528
3 9673015 15-Jul-19 22-Jul-19 4.3885
4 9673014 22-Jul-19 29-Jul-19 4.3974
5 9673006 29-Jul--19 05-Aug-19 4.3783
6 9429698 05-Aug-19 12-Aug-19 4.4921
7 9429690 12-Auq-19 18-Aug-19 4.5111
8 9429682 18-Auq-19 26-Auq-19 4.5118
9 9429674 26-Auq-19 03-Sep-19 4.5313
10 9429666 03-Sep-19 09-Sep-19 4.4910
11 9429651 09-Sep-19 16-Sep-19 4.5089
12 9429650 16-Sep-19 23-Sep-19 4.5265
13 9429635 23-Sep-19 30-Sep-19 4.5051
Totals
EN:RGY •' Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 866.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
February 13, 2020
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C20010402
Project Name: 4th Quarter Air 2019
Quote ID: C5470
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 1/13/2020 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C20010402-001 BHV-1 01 /06/20 00:00 01/13/20 Filter Composite of two or more samples
Client Provided Field Parameters
Metals, Total
Digestion, Total Metals,
Radiochemistry
Radiochemistry Air Filter Compliance
Calculations
RAD-AIR, Routine Radiological
Reports
RAD Alternate Unit Reporting Air
Filters
Lead 210
Radium 226
Thorium, Isotopic
C20010402-002 BHV-2 01/06/20 00:00 01/13/20 Filter Same As Above
C20010402-003 BHV-4 01/06/20 00:00 01/13/20 Filter Same As Above
C20010402-004 BHV-5 01/06/20 00:00 01/13/20 Filter Same As Above
C20010402-005 BHV-6 01106/20 00:00 01/13/20 Filter Same As Above
C20010402-006 BHV-7 01/06/20 00:00 01/13/20 Filter Same As Above
C20010402-007 BHV-8 01 /06/20 00:00 01/13/20 Filter Same As Above
C20010402-008 Blanks 01/06/20 00:00 01/13/20 Filter Same As Above
The analyses presented in this report were performed by Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601, unles
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. Any issues encountered during sample receipt are documented in the Work Order Receipt Checklist.
The results as reported relate only to the item(s) submitted for testing. This report shall be used or copied only in its entirety. Energy
Laboratories, Inc. is not responsible for the consequences arising from the use of a partial report.
If you have any questions regarding these test results, please contact your Project Manager .
Report Approved By:
Digitally signed by
Tracey Archer
Date: 2020.02.13 13:07:38 -07:00
Page 1 of 40
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
4th Quarter Air 2019
C20010402
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (±2°C)
Report Date: 02/13/20
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 ELI 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 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
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
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of 40
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LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-008
Client Sample ID: Blanks
MCU
Analyses Result Units Qualifiers RL QCL
METALS, IN AIR
Uranium 0.00094 mg/L L 0.00014
Uranium, Activity 6.4E-10 uCi/mL L 9.3E-11
RADIONUCLIDES -IN AIR
Lead 210 2.3E-10 uCi/mL u
Lead 210 precision(±) 6.9E-09 uCi/mL
Lead 210 MDC 1.2E-08 uCi/mL
Radium 226 1.9E-09 uCi/mL u
Radium 226 precision (±) 1.4E-09 uCi/mL
Radium 226 MDC 2.0E-09 uCi/mL
Thorium 230 4.0E-10 uCi/mL
Thorium 230 precision (±) 1.7E-10 uCi/mL
Thorium 230 MDC 2.0E-10 uCi/mL
Thorium 232 1.5E-10 uCi/mL u
Thorium 232 precision (±) 1.1E-10 uCi/mL
Thorium 232 MDC 1.6E-10 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 -2.1 pCi/Filter u
Lead 210 precision (±) 6.8 pCi/Filter
Lead 210 MDC 11 .5 pCi/Filter
Radium 226 1.8 pCi/Filter u
Radium 226 precision (±) 1.3 pCi/Filter
Radium 226 MDC 1.9 pCi/Filter
Thorium 230 0.38 pCi/Filter
Thorium 230 precision (±) 0.17 pCi/Filter
Thorium 230 MDC 0.19 pCi/Filter
Thorium 232 0.14 pCi/Filter u
Thorium 232 precision (±) 0.10 pCi/Filter
Thorium 232 MDC 0.15 pCi/Filter
Uranium, Activity 0.61 pCi/Filter 0.20
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF -4.0E+05 %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 2.2E+05 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.3E+06 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.5E+06 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 8&&.&8&.7175 • Helena, MT 877.472.0711
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
Method Analysis Date / By
SW6020 01/24/20 15:28 / meh
SW6020 01/24/20 15:28 / meh
E909.0 02/10/20 04:02 / ajl
E909.0 02/10/20 04:02 I ajl
E909.0 02/10/20 04:02 I ajl
E903.0 02/04/20 11 :51 / ajl
E903.0 02/04/20 11 :51 I ajl
E903.0 02/04/20 11 :51 / ajl
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
E908.0 02/05/20 13:09 / nsr
RADCALC 02107/20 09:45 / dmf
RADCALC 02107/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 I dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 02/07/20 09:45 / dmf
RADCALC 01/31/20 15:07 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 / dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
L -Lowest available reporting limit for the analytical method U -Not detected at Minimum Detectable Concentration
used (MDC)
Page 24 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 4th Quarter Air 2019
Lab ID: C20010402-008
Client Sample ID: Blanks
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
Report
Definitions:
RL -Analyte Reporting Limit
QCL -Quality Control Limit
N/A uCi/mL
7.1E+05 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1 L
Qualifiers RL
MCL/
Report Date: 02/13/20
Collection Date: 01/06/20
DateReceived: 01 /13/20
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
RADCALC 02/07/20 09:47 I dmf
FIELD 01 /06/20 00:00 / sec
MCL -Maximum Contaminant Level
ND -Not detected at the Reporting Limit (RL)
Page 25 of 40
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Toll Free: 888.235.0515 • 307 .235.0515 • F: 307 .234.1639
PO Box 247, Casper, WY 82602-0247 • 2393 Salt Creek Hwy (82601)
HIGH VOLUME AIR SAMPLING REPORT I I I
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 4th Quarter Air 2019
SAMPLE ID: Blanks
REPORT DATE: February 13, 2020
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C20010402-008 natu SE-18
4th Quarter 2019 230Th 3E-18
Air Volume in mLs 226Ra IE-17
l.24E+ll 210Pb -2E-17
232Th IE-18
Counting L.L.D.+ Precision MDCµCi/mL
µCi/mL µCi/mL
NIA NIA IE-16
JE-18 2E-18 IE-16
IE-17 2E-17 IE-16
6E-17 9E-17 2E-15
8E-19 IE-18 NIA
NOTE: This report uses 124,000,000 Lair for comparison purposes, the routine report uses a 1 L system default.
+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, Thorium-232
Week for Radium-226
Day for Lead-210
Effluent Cone.* % Effluent
µCi/mL Concentration
9E-14 SE-03
3E-14 IE-02
9E-13 2E-03
6E-13 -3E-03
6E-15 2E-02
Page 26 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C20010402 Report Date: 01/30/20
Analyte
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-56565
Uranium
Lab ID: LCS2-56565
Uranium
Lab ID: C20010402-001ADIL
Uranium
Lab ID: C20010402-001APDS
Uranium
Qualifiers:
RL -Analyte Reporting Limit
Count Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
Initial Calibration Verification Standard
0.0191 mg/L 0.00030
Interference Check Sample A
1.32E-05 mg/L 0.00030
Interference Check Sample AB
1.36E-05 mg/L 0.00030
Method Blank
ND mg/L 0.0001
Laboratory Control Sample
0.0495 mg/L 0.00013
Serial Dilution
6.31E-11 mg/L 1.5E-10
Post Digestion/Distillation Spike
4.10E-10 mg/L 1.5E-10
95 90
Analytical Run: ICPMS5-C_200124A
01/24/20 13:05
110
01 /24/20 13:36
01/24/20 13:40
Run: ICPMS5-C_200124A
Batch: 56565
01/24/20 14:14
Run: ICPMS5-C_200124A 01 /24/20 14:19
99 70 130
Run: ICPMS5-C_200124A
0 0
Run: ICPMS5-C_200124A
90 75 125
01/24/20 14:32
20
01 /24/20 14:36
ND -Not detected at the Reporting Limit (RL)
Page 27 of 40
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QA/QC Summary Report
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.888. 7175 • Helena, MT 877.472.0711
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C20010402 Report Date: 02/12/20 --------------
Analyte
Method: E903.0
Lab ID: LCS-56565
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: MB-56565
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C20010402-001ADUP
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte Reporting Limit
Count Result Units
3 Laboratory Control Sample
105 pCi/L
20.6 pCi/L
2.14 pCi/L
3 Method Blank
0.2 pCi/L
0.3 pCi/L
0.4 pCi/L
3 Sample Duplicate
7.39E-08 pCi/L
2.09E-08 pCi/L
1.44E-08 pCi/L
U -Not detected at Minimum Detectable Concentration (MDC)
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: G542M-2_200128B
105 80 120
Run: G542M-2_200128B
Run: G542M-2_200128B
ND -Not detected at the Reporting Limit (RL)
15
Batch: 56565
02/04/20 11 :50
02/04/20 11 : 50
u
02/04/20 11 : 51
20
Page 28 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C20010402 Report Date: 02/12/20
Analyte
Method: E908.0
Lab ID: MB-56565
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: LCS-56565
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Lab ID: C20010563-004ADUP
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Count Result Units
6 Method Blank
0.5 pCi/L
0.2 pCi/L
0.3 pCi/L
0.08 pCi/L
0.2 pCi/L
0.3 pCi/L
3 Laboratory Control Sample
51.4 pCi/L
9.77 pCi/L
0.232 pCi/L
6 Sample Duplicate
9.20E-08 pCi/L
7.81E-08 pCi/L
1.24E-07 pCi/L
3.07E-08 pCi/L
5.31E-08 pCi/~
1.10E-07 pCi/L
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_2_200131A
Run: EGG-ORTEC_2_200131A
108 80 120
Run: EGG-ORTEC_2_200131A
41
190
Batch: 56565
02/05/20 13:09
u
02/05/20 13:09
02/05/20 13:09
20 UR
20 UR
-Duplicate RPD is outside of the acceptance range for this analysis. However, the RER is less than the limit of 2,0.
Qualifiers:
RL -Analyte Reporting Limit ND -Not detected at the Reporting Limit (RL)
R -Relative Percent Difference (RPD) exceeds advisory limit U -Not detected at Minimum Detectable Concentration (MDC)
Page 29 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C20010402 Report Date: 02/12/20
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: E909.0
Lab ID: LCS-56565
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Lab ID: MB-56565
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Lab ID: C20010402-003AMS
Lead 210
Lead 210 precision(±)
Lead 210 MDC
3
3
3
Laboratory Control Sample Run: TRICARB LSC_200128D
204 pCi/L 112 80 120
62.5 pCi/L
20.2 pCi/L
Method Blank Run: TRICARB LSC_200128D
-0.7 pCi/L
pCi/L
2 pCi/L
Sample Duplicate Run: TRICARB LSC_200128D
9.45E-06 pCi/L 11
2.84E-06 pCi/L
4.60E-07 pCi/L
-The sample used for the MS/MSD pair had much higher response than the spike added. The MS/MSD pair is reported as a Duplicate pair instead.
Lab ID: C20010402-003AMSD 3 Sample Duplicate
Lead 210 1.34E-05 pCi/L
Lead 210 precision(±)
Lead 210 MDC
4.02E-06
5.29E-07
pCi/L
pCi/L
Run: TRICARB LSC_200128D
45
-The sample used for the MS/MSD pair had much higher response than the spike added. The MS/MSD pair is reported as a Duplicate pair instead.
-Duplicate RPO is outside of the acceptance range for this analysis. However, the RER is less than the limit of 2.0.
Qualifiers:
RL -Analyte Reporting Limit ND -Not detected at the Reporting Limit (RL)
Batch: 56565
02/09/20 16:49
02/09/20 18:00
u
02/10/20 02:02
20
02/10/20 02:31
20 R
R -Relative Percent Difference (RPO) exceeds advisory limit U -Not detected at Minimum Detectable Concentration (MDC)
Page 30 of 40
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Casie C. Peppersack
Reviewed by: Steve Carlston
Reviewed Date: 1/14/2020
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 D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
N/A°C N/A
Yes D
Yes D
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.686. 7175 • Helena, MT 877.472.0711
C20010402
Date Received: 1/13/2020
Received by: CCP
Carrier name: 2nd Day Air
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No@
No D
No D
Not Present D
Not Present D
Not Present 0
Not Applicable D
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 31 of 40
Sheet 1 of 1 1~·/~
(_ 11.,,~NERGYFUELS RESOURCES
CHAIN OF CUSTODY
Samples Shipped to: _E_n_er...,gy...._La_b __ o_ra_tie_s _________ Contact: Tanner Holliday
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samplers N ame s ampers s lgoature
4th Quarter Air 2019 Tanner Holliday b~}fJ/,/,
V
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
BHV-1 9/30/2019-1 /6/2020 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-2 9/30/2019-1/6/2020 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-4 9/30/2019-1 /6/2020 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-5 9/30/2019-1 /6/2020 NA U-NAT. TH-230, Ra-226, Pb-210, TH-232
BHV-6 9/30/2019-1/6/2020 NA U-NAT. TH-230, Ra-226, Pb-210. TH-232
BHV-7 9/30/2019-1 /6/2020 NA U-NAT. TH-230, Ra-226, Pb-210, TH-232
BHV-8 9/30/2019-1 /6/2020 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
Blanks 9/30/2019-1 /6/2020 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
Comments: Please send report to Kathy Weinel at [e-mail]
Date/Time Received By:(Signature)
1/9/2020
1130
Date/Time
De,temme 1/!fzb?V
')
Page 32 of 40
Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019
b= -0.02636 1
First Monitoring Quarter2015
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 Updated: 7/30/14
Orifice SIN: 8091779
f.H t.H
Week I Filter I Start I Stop I Start I Stop -Starting Stopping
# Number Date Da1e Time Time Manometer Manometer
(in. H20) (in. H20) ...
9429636 9130/20 19 1onno19 2326.97 2495.82 1013LO 4.5 4.0
2 9429627 10/7/2019 10/14/2019 2495.82 2663.77 10077.0 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9432.2 4.5055 4.6796 174.1 0.0185 100.0
3 9429619 10/14/2019 10/21/2019 2663.77 2830.92 10029.0 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9638.7 4.50? I 4.6710 163.9 0.0170 99.5
4 9429611 10/21/2019 !0/28/20 !9 2830.92 2998.77 10071.0 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9463.2 4.5262 4.6499 123.7 0.0131 99.9
5 9429609 10/28/2019 lt/4/2019 2998.77 3170.47 !0302.0 4.0 4.0 4.0 0.4 273.6 621.69 1.07 0.95 33.67 9822.9 4.5183 4.5986 80.3 0.0082 102.2
6 9650995 I !/4/2019 1111 1/2019 3170.47 3359.1 11317.8 4.0 4.0 4.0 7.7 280.8 622.45 l.08 0.94 33.25 10655.8 4.3640 4.4814 117.4 0.0110 112.3
7 9650994 11/11/2019 ll/18/2019 3359.1 3504.02-8695.2 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8202..2 4.3564 4.4701 113.7 0.0139 86.3
8 9650985 11/18/2019 I l/25/2019 3504.02 3675.3 10276.8 4.0 4.0 4.0 4.7 277.8 618.0 1 l.08 0.94 33.31 9693.2 4.3843 4.4333 49.0 0.0051 102.0
9 9650977 t !n5/2019 12/2/2019 3675.3 3843.37 10084.2 3.5 4.0 3.8 -0.1 273.0 614.76 1.04 0.92 32.47 9272.5 4.3867 4.4302 43.5 0.0047 100.0
10 9650969 12/2/2019 12/9/2019 3843.37 4011.71 10100.4 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9579.9 4.3454 4.3807 35.3 0.0037 100.2
11 9650961 12/9/2019 12/16/2019 4011.71 4179.04 10039.8 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9547.4 4.3795 4.4056 26.1 0.0027 99.6
12 9650953 12/16/2019 12/23/2019 4179.04 4342.3 9795.6 4.0 4.0 4.0 -2.I 271.1 623.82 1.06 0.96 33.89 9400.1 4.3438 4.3808 37.0 0.0039 97.2
13 9650945 12/23/2019 12/30/2019 4342.3 4515.82 10411.2 3.5 4.0 3,8 -1.6 271.5 615.65 1.04 0.92 32.59 9606.7 4.3359 4.3611 25.2 0.0026 103.3
4679.46 98 18.4 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9447.2 4.3010 4.3276 26.6 0.0028 97.4
!Totals 141149.4 15.10 13.24 467.49 133448.2 61.765 62.913 1147.8 0.1208
Averages 10082.1 4.0 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.39 9532.0 4.412 4.494 82.0 0.0086 l 100.0
Commcnis:
tnsen weekly How check values in yellow colu11V1s.
Energy Fuels Resources -White Mesa Mill Calibrat.ion Date: 9/3/2019 -
b= --0.02636 I First Monitoring Quarter20l4
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 Updated: 7 /30/14
Orifice SIN: 8091779
• llli llli
Week I Filter I Start Stop Start Stop Starting Stopping
# Number Date Date Time Time f'x!onome{cr Manometer
(in.H20) (in. H20)
9429637 9130/2019 IOn/2019 13042.56 13210.91 10101•.0 4.0 4.0
2 9429628 IM/2019 10/14/2019 13210.91 13379.46 IOll3.0 4.0 4.0 4.0 9.4 2S2.6 619.18 1.09 0.94 33.06 9465.9 4.5085 4.7949 286.4 0.0303 100.3
3 9429620 1.0/1412019 10/21/2019 13379.46 13546.17 10002.6 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9613.4 4.5251 4.7681 243.0 0.0253 99,
4 9429612 1012l/2019 10/28/2019 t:3546.17 13715.12 IOl37.0 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9525.2 4,5253 4.7286 203.3 0.0213 100.6
5 9429604 10/2812019 11/4/2019 13715.12 13887.11 10319.4 4.0 4.0 4.0 0.4 273.6 621.69 l.07 0.95 33.67 9839.5 4.5265 4.7121 185.6 0.0189 102.4
6 9650996 I l/4!2019 11/11/2019 13887.11 14075.73 11317.2 4.0 4.0 4.0 7.7 280.8 622.45 !.OS 0.94 33.25 1.0655.3 4.3556 4.6089 253.3 0.0238 112.3
7 9650993 11/11/2019 11/lS/2019 14075.73 14219.63 8634.0 4.0 4.0 4.0 6,.S 279.7 622.25 I.OS 0.94 33.31 8144.5 4.3455 4.5888 • 243.3 0.0299 85.7
8 9650984 11/18/2019 11/25/2019 14219.63 14391.63 10320,0 4.5 4.0 4.3 4.7 277.8 618.01 I.II 0.97 34.31 10027.7 4.3843 4.5157 131.4 0.0131 102.4
9 9650976 11/25/2019 12/2/2019 14391.63 14559.87 10094.4 4.0 4.0 4.0 -0.1 273.0 614.76 l.07 0.95 33.52 95S0.2 4.4117 4.4827 71.0 0.0074 100,I
IO 9650968 12/2/2019 12/9/2019 14559.87 14727.37 10050.0 4.0 4.0 4.0 3.0 276.1 621.01 !.OS 0.95 33.50 9532.1 4.3480 4.4150 67.0 0.0070 99.7
11 9650960 12/9/2019 12/1612019 14727.37 14895.38 10080.6 4.5 4.0 4.3 0.6 273.8 61S.S7 I.I I 0.98 34.60 9875.5 4.38(;4. 4.4258 39.4 0.0040 100.0
12 %50952 12/16/2019 1212312019 14895.38 15057.99 9756.6 4.0 4.0 4.0 -2.1 271.1 623.82 l.06 0.% 33.89 9362.7 4.3323 4,4118 79.5 0.0085 96.8
15057.99 IS231 10380.6 3.5 4,0 3.8 ·l.6 171.5 615.65 1.04 0.92 32.59 9578.4 4.3486 4.4444 95.8 0.0100 !03.0
15394.99 9839.4 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9467.4 4.3320 4.3773 45.3 0.0048 97.6
141145.8 15.17 13.30 469.57 134042.2 61.842 64.036 2193.9 0.2308 -
Averages I 10081.8 4.l 4.0 4.0 4.l 277.2 619.7765 1.08 0.95 33.54 9574.4 4.417 4.574 156.7 o.0165 I 100.0
lnsen weekly flow check Yalues in )·ellow columns.
Energy Fue.ls Resources -While Mesa Mill
Period: September 30, 2019 -January 6, 2020
IL~ Mi Ill-I
Week Filter Start Stop Start Stop ~~ Starting Stopping
# Number Date Date Time Time • Milll<>meter Monomctct
(in. H,O) (in. H,O)
l 9429638 9/3Dn019 IDn/2019 18567.99 18736.36 10102.2 4.5 4.0 4.3
2 9429629 lOn/2019 !011412019 18736.36 18902.69 9979.8 4.0 4.0 4.0
3 9429621 l(),'(4/2019 10/21/2019 18902.69 19066.39 9822.0 4.0 4.0 4.0
4 9429613 10/21/2019 IOn.812019 19066.39 19234.71 10099.2 4.0 4.0 4.0
5 9429605 I 0/2812019 I 114/2019 19234.11 19392.54 9469.8 3.5 4.0 3.8
6 9650997 11/412019 ll/11/2019 19392.54 19584.11 11494.2 3.5 4.0 3.8
7 9650992 11111/2019 11/1812019 19584.11 19728.34 8653.8 4.0 4.0 4.0
8 9650983 1111812019 11125/2018 19728.34 19899.78 10286.4 4.0 4.0 4.0
9 9650975 I l/2512019 12/212019 19899.78 20067.83 10083.0 4.0 4.0 4.0
10 9650967 12/2/2019 1219/201.9 20067.83 20236.16 10099.8 4.0 4·.o 4.0
11 9650959 121912019 12/16/2019 20236.16 20403.78 10057.2 4.0 4.0 4.0
12 9650951 12/16/2019 I '21'...'.112019 20403.78 20566.88 9786.0 4.0 4.0 4.0
13 9650943 12123/2019 12/30/2019 '2.0566.SS 20739.6 10363.2 • 3.5 4.0 3.8
20903.85 9855.0 4.0 4.0 4.0
TOlols 140151.6
Avern_g_es 10010.8 I 3.9 l 4.0 4.0
Calibration Date: 9/3/2019
Calibration Slope & Intercept:
Orifice SIN: 8091779
m= 1.26445 b= -0.02636
~...:iia.F ;::;;_;:===iiiiiiiiiiiiifi;;..iiiir= ea
Wkly._A"l!,
~
~ ;IJ~W?i1J~E'.!:~!: ,
14.4 287.6 6[9.68 1.13 0.96 33.76 9658.5 4.5298
9.4 282.6 619.18 1.09 0.94 33.06 9341.2 4.5055
10.8 284.0 618.26 1.09 0.93 32.95 9163.2 4.5030
7.6 280.7 619.86 1.09 0.94 33.lS 9489.7 4.5263
0.4 273.6 621.69 1.04 0.92 32.62 8748.3 4Sl30
7.7 280.8 622.45 1.05 0.91 32.21 10484.9 4.3365
6.5 279.7 622.25 I.OS 0.94 33.31 . S163.2 4.3574
4.7 277.8 618.01 1.08 0.94 33.31 9702.2 4.3669
-0.1 273.0 614.76 1.07 Oc95 33.52 9569.4 4.3418
3.0 276.1 621.01 1.08 0.95 33.50 9579.3 4.3395
0.6 273.S 618.87 1.07 0.95 33.58 9563.9 4.3698
-2.1 271.1 623,82 1.06 0.96 33.S9 9390.9 4.3421
-1.6 271..5 615.65 1.04 0.92 32.59 9562.4 4.3530
.4.5 268.6 621.39 1.06 0.96 33.98 9482.4 4.3088
-
' ' 619~765 I 4.1 277.2
15.03 13.18 465.46 131899.6 61.703
1.07 0.94 33.25 9421.4 4.407
4.6436
4.6207
4.6527
4.6462
4.5596
4.4640
4.4410
4.4223
4.4120
4.3808
4.3977
4.3832
4.3825
4.3411
62.747
4.482
First Monitoring Quarter 2014
Updated: 7/30/14
113.8 0.0118 100.2
115.2 0.0123 99.0
149.7 0.0163 97.4
119.9 0.0126 100.2
36.6 0.0042 93.9
127.5 0.0122 114.0
83.6 0.0102 85.9
55.4 0.0057 102.0
70.2 0.0073 JOO.O
41.3 0.0043 100.2
27.9 0.0029 99.8
41.1 0.0044 97.1
29.5 0.0031 102.8
32.3 0.0034 97,8
1044.0 0.1108
74.6 0.0019 I 99.3
Bnergy Fuels Resources · White Mesa Mill -1CaUbra1fon Dace:-9/3/2019 ---r -Firs1 Monitoring Quarter 2014
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= l.26445 b= -0.02636 Updated: 7/30/14
Orifice SIN: 8091779 ===;;=====;;a;;:;;iiii1:;;;;;;;====;;;:'ii~n
... ,,.._"' .11.H .11.H
Week I Filter I Start Stop Start Stop • Starting Stopping
# Number Date Date Time Time : Ma\K)mctcr Nfanomctcr J (in. H20) (in. H20)
9429639 9/30/2019 10n12019 11650.81 11819.1 10097.4 4.5 4.0
2 9429630 10/7/2019 10/14/2019 11819.1 11990.03 10255.8 4.0 4.0 4.0 9.4 282.6 619.!8 1.09 0.94, 33.06 9599.6 4.4950 4.6560 16!.0 0.0168 101.7
3 9429622 10/14/2019 10/21/2019 ll990.03 12153.77 9824.4 4.0 4.0 4.0 10.8 284.0 618.26 l.09 0.93 32.95 9165.4 4.5107 4.6469 136.2 0.0149 97.5
4 9429614 lMl/2019 10/28/2019 12153.77 !2322.09 10099.2 4.0 4.0 4.0 7.6 280.7 6!9_86 1.09 0.94 33.18 9489.7 4.526'.l 4.6623 136.0 0.0143 100.2
5 9429606 10/28/2019 11/4/2019 12322.09 12479.92 9469.8 3.5 4.0 3.8 0.4 273.6 621.69 1.04 0.92 32.62 8748.3 4.5281 4.5997 71.6 0.0082 93.9
6 9650998 111412019 1111112019 12419,92 12611.45 11491.8 4.o 4.o ~.o 1.1 280.8 622.45 1.os o.94 33.25 1os19.6 4.3517 4.4842 1n.s 0.0122 114.o
7 9650991 11/11/2019 lt/18/2019 [2671.45 12815.73 8656,8 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8166.0 4.3539 4.4701 116.2 0.0142 85.9
8 9650082 11/18/2019 11/25/2019 12815:73 129S7.17 10286.4 4.0 4.0 4.0 4.7 277.8 61 8.01 1.08 0.94 33.31 9702.2 4.3598 4.42 18 62.0 0,0064 102.0
9 9650974 11/25/2019 12/2/2019 12987.17 131.55.24 10084.2 4.0 4.0 4.0 -0.I 273.0 614.76 1.07 0.95 33.52 9570.5 4.3383 4.4119 73.6 0.0077 100.0
10 9650966 1212/2019 1219/2019 13155.24 13323.55 10098.6 4.0 4.0 4.0 3.0 276.1 621.01 I.OS 0.95 33.50 9578.2 4.3584 4.4096 51.2 0.0053 100.2
11 9650058 12/9/2019 12/16/2019 1.3323.55 I 349L18 10057.8 4.5 4.0 4.3 0.6 273.8 618.87 1.11 0.98 34.60 9853.2 4.3703 4.4126 423 0.0043 99.8
12 9650950 12/16/2019 12/23/2019 13491.18 13654.28 9786.0 4.0 4.0 4.0 -2.I 271.l 623.82 1.06 0.96 33.89 9390.9 4.3338 4.3884 54.6 0.0058 97.1
13 9650942 12/23/2019 12/30/2019 13654.28 13826.82 10352.4 4.0 4.0 4.0 -1.6 271.5 615.65 1.07 0.95 33.63 9859.4 4.3453 4.3833 38.0 0.0039 102.7
13991 98S0.8 3.5 4.0 3.8 -4.5 268.6 621.39 1.03 0.93 32.9'2 9183.3 4.3450 4.3904 45.4 0.0049 97.7
Totals 140411.4 -~ 15.10 13.24 467.50 132780.3 61.739 62.997 1258-5 0.1332
Averag~s 10029.4 4.0 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.39 I 9484.3 4.410 4.500 89.9 0.0095 I 99.5
ltiJm Ifie ffll!I .mtion.
Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019
b= -0.026361
First Monitoring Quarter 2014
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 Updated: 7/30/14
Orifice SIN: 8091779
AH AH
Week I Filter Start Stop Start Stop • Starting Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in. H20)
9429640 9/30/2019 !On/2019 646.99 815.37 10102.8 4.0 4.0
2 9429631 1on12019 10/14/2019 815.37 986.21 10250.4 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9594.5 4.5190 4.6649 145.9 0.0152 101.7
3 9429623 10/14/2019 10/21/2019 986.21 1149.91 9822.0 4.0 4.0 4.0 10.8 284.0 618.26 1.09 0.93 32.95 9163.2 4.5040 4.6338 129.8 0.0142 97.4
4 9429615 10/21/2019 10/28/2019 1149.91 1318.23 10099.2 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9489.7 4.5235 4.6402 116.7 0.0123 100.2
5 9429607 10/28/2019 11/4/2019 1318.23 1476.54 9498.6 3.5 4.0 3.8 0.4 273.6 621.69 1.04 0.92 32.62 8774.9 4.5475 4.6296 82.1 0.0094 94.2
6 9650999 11/4/2019 11/11/2019 1476.54 1667.68 11468.4 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10797.6 4.3502 4.4939 143.7 0.0133 113.8
7 9650990 11/11/2019 11/18/2019 1667.68 1811.9 8653.2 4.0 4.0 4,0 6.5 279.7 622.25 1.08 0.94 33.31 8162.6 4.3855 4.4990 113.5 0.0139 85.8
8 96S0981 11/18/2019 11/25/2019 1811.9 1983.47 10294.2 4.5 4.0 4.3 4.7 277.8 618.01 I.I I 0.97 34.31 10002.7 4.3545 4.3955 41.0 0.0041 102.1
9 9650973 11/25/2019 12/2/2019 1983.47 2151.42 10077.0 3.5 4.0 3.8 --0.1 273.0 614.76 1.04 0.92 32.47 9265.9 4.3480 4.4105 62.5 0.0067 100.0
10 9650965 12/2/2019 12/9/2019 2151.42 2319.79 10102.2 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9581.6 4.3697 4.4179 48.2 0.0050 100.2
11 9650957 12/9/2019 12/16/2019 2319.79 2487.35 10053.6 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9560.5 4.3490 4.3850 36.0 0.0038 99.7
!2 9650949 12/16/2019 12/23/2019 2487.35 2650.42 9784.2 4.0 4.0 4.0 -2.1 271.1 623.82 1.06 0.96 33.89 9389.2 4.3643 4.4152 50.9 0.0054 97.1
13 9650941 12/23/2019 12/30/2019 2650.42 2823.26 10370.4 3.5 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9569.0 4.3419 4.3838 41.9 0.0044 102-9
12/30/2019 1/6/2020 2823.26 2987.41 9849.0 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9476.7 4.3396 4.3857 46.l 0.0049 97.7 ---· -=· ._.,.. ~ .. -Totals 140425.2 15.03 13.18 465.47 132204.0 61.810 62.978 1168.5 0.1243
Averages 10030.4 3.9 4.0 4.0 4.1 277.2 619.7765 1.07 0.94 33.25 9443.1 4.415 4.498 83.5 0.0089 I 99.5
Energy Fuels Resources -White Mesa Mill Callbralion Date: 9/3/2019 I First Monitoring Quarter 2014
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 b= -0.02636 Updated: 7/30/14
Orifice SIN: 8091779
lllI lllI -.
Week I Filter I Start I Stop I Start I Stop ~ Starting Stopping
# Number Date Dale Time Time l~ Mnnometer Mnnometer
(in. H20) (in. H20)
9429641 9/30fl019 10/7/2019 2686.28 2855.1.7 10133.4 4.0 4.0 4.0 14.4 2S7.6 619.68 1.10 0.93 32.77 9404.4 4-5043 4.6672 162.9 0.0173 100.5
2 9429632 10/712019 10/1412019 2855.17 3023.1 10075.S 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9431.1 4.5016 4.7143 212.7 0.0226 100.0
3 9429624 10/14/2019 10/21/2019 3023.1 31 90.29 10031.4 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9641.0 4.5155 4.6899 174.4 0.0181 99.5
4 9429616 10/21/2019 10/28/2019 3190.29 3357.97 10060.8 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9453.6 4.5127 4.6869 174.2 0.0184 99.8
5 9429608 I0/2812019 11/4/2019 3357.97 3530.39 10345.2 4.0 4.0 4.0 0.4 273.6 621.69 1.07 0.95 33.67 9864.1 4.5355 4.6677 132.2 0.0134 102.6
6 9651000 11/4/2019 11/1112019 3530.39 3719.06 11320.2 4.0 4.0 4.0 7.7 280.S 622.45 1.08 0.94 33.25 10658.1 4.3575 4.4570 99.5 0.0093 112.3
7 9650989 11/IL/2019 1111812019 3719.06 3863.33 8656.2 4.0 4.0 4.0 6.5 279.7 622.25 LOS 0.94 33.31 8165.5 4.3763 4.S249 148.6 0.0182 85.9
8 9650980 I l/1812019 11/25/2019 3863.33 ,4034.68 10281.0 4.0 4.0 4.0 4.7 277.8 618.0 l 1.08 0.94 33.31 9697.1 4.3581 4.4334 75.3 0.0078 102.0
9 9650972 11/25/2019 121'.12019 4034.68 4202.8 10087.2 4.0 4.0 4.0 -0.1 273.0 614.76 1.07 0.95 33.52 9573.4 4.3275 4.3920 64.5 0.0067 100.1
1.0 9650964 12/2/2019 1219/2019 4202.8 4371.1 10098.0 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9577.6 ' 4.3491 4.3877 38.6 0.0040 100.2
11 9650956 1219/2019 12116/2019 4371.1 4538.51 10044.6 4.0 4.0 4.0 0.6 273.S 618.87 1.07 0.95 33.58 95S2.0 4.3702 4.41 16 41.4 0.0043 99.6
12 9650948 12/16/2019 12/23/2019 45)8.51 4701.73 9793.2 4.0 4.0 4.0 -2.1 271.1 623.82 1.06 0.96 H.89 9397.8 4.3608 4.4109 50.1 0.0053 97.2
13 9650940 12i'23/2019 12130/2019 470 1.73 4874.96 10393.8 3.5 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9590.6 4.3610 4.3979 36.9 0.0038 103.1
5038.75 9827.4 4-.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9455.9 4.3322 4.3745 42.3 0.0045 97.5
141148.2 -., 15.10 13.24 467.55 133462.2 61.762 63.216 1453.6 0.1538
10082.0 4.o 4.o 4.o 4.1 211.2 619.7765 1.08 o.95 33.40 9533.o 4.412 4.515 103.8 0.0110 I 100.0
Energy Fuels Resources -White Mesa Mill
Period: September 30, 2019 -January 6, 2020
~....-.;,,. liH Ml
Week I Filler Start Stop Start Stop .( Starting Stopping
# Number Date Date Time Time ~ Manometer Manometer
(in. H,O) (in. H20)
9429642 9/30/2019 1on12019 9514.59 9683.47 10132.8 4.0 4.0 4.0
2 9429633 10/7/2019 10/14/2019 9683.47 9851.4 10075.8 4.0 4.0 4.0
3 9429625 10/14/2019 10/21/2019 9851.4 10018.55 10029.0 4.5 4.0 4.3
4 9429617 10/21/2019 10/28/2019 10018.55 10186.26 10062.6 4.0 4.0 4.0
5 9429609 10/2&/2019 11/4/2019 10186.26 10357.74 10288.8 4.0 4.0 4.0
4 9429601 11/4/2019 11/11/2019 10357.74 10546.63 11333.4 4.0 4.0 4.0
7 9650988 11/11/2019 11/18/2019 10546.63 10691.27 8678.4 4.0 4.0 4.0
8 9650979 11/18/2019 11/25/2019 10691.27 10862.55 10276.8 4.5 4.0 4.3
9 9650971 11/25/2019 12/2/2019 10862.55 11030.68 10087.8 3.5 4.0 3.8
10 9650963 12/2/2019 12/9/2019 11030.68 11198.99 10098.6 4.0 4.0 4.0
11 9650955 12/9/2019 12/16/2019 11198.99 11366.37 10042.8 4.0 4.0 4.0
12 9650947 12/16/2019 12/23/2019 11366.37 11529.57 9792.0 4.0 4.0 4.0
13 9650939 12/23/2019 12/30/2019 11529.57 11703.04 10408.2 3.0 4.0 3.5
14 9650938 12/30/2019 1/6/2020 11703.04 11866.74 9822.0 4.0 4.0 4.0
Totals 141129.0
Averages 10080.6 I 4.0 I 4.0 4.0
Lost Lhe motor between 10/28/2019 and 11/4/2019. Motor was replaced on 11/4/2019.
lnsen weekly flow check values in yellow columns.
Calibration Date: 9/3/2019
Calibration Slope & Intercept: m= 1.26445 b= -0.02636
AA g nfice SIN: 8091779
Pa
Wkly,A-..g.
~on:
(m!DIW ~! :i~'i:f f ;i~f 'if I~
14.4 287.6 619.68 1.10 0.93 32.77 9403.8 4.5271
9.4 282.6 619.18 1.09 0.94 33.06 9431.1 4.5041
10.8 284.0 618.26 1.13 0.96 33.94 9638.7 4.5325
7.6 280.7 619.86 1.09 0.94 33.18 9455.3 4.5163
0.4 273.6 621.69 1.07 0.95 33.67 9810.4 4.5262
7.7 280.8 622.45 1.08 0.94 33.25 10670.5 4.5222
6.5 279.7 622.25 1.08 0.94 33.31 8186.4 4.3821
4.7 277.8 618.01 1.11 0.97 34.31 9985.7 4.3643
-0.1 273.0 614.76 1.04 0.92 32.47 9275.8 4.3581
3.0 276.1 621.01 1.08 0.95 33.50 9578.2 4.3715
0.6 273.8 618.87 1.07 0.95 33.58 9550.3 4.3713
-2.1 271.1 623.82 1.06 0.96 33.89 9396.7 4.3491
-1.6 271.5 615.65 1.00 0.89 31.50 9284.8 4.3600
-4.5 268.6 621.39 1.06 0.96 33.98 9450.7 4.3558
l "l 1619.7765 4.1 277.2
15.06 13.21 466.43 133118.4 62.041
1.08 0.94 33.32 9508.5 4.431
First Monitoring Quarter 2014
Updated: 7/30/14
.... ;"""'";"Tl" -==-----·.,·--.----:-. ..,..........,, '.!'.:'i=: . .-:1 ==;; .":) ;" ,. •I" .~1 tifl~:'.Jt~~~::tt~:
4.6648 137.7 0.0146 100.5
4.6663 162.2 0.0172 100.0
4.6860 153.5 0.0159 99.5
4.6310 114.7 0.0121 99.8
4.5327 6.5 0.0007 102.1
4.6450 122.8 O.Gl 15 112.4
4.4850 102.9 0.0126 86.1
4.4120 47.7 0.0048 102.0
4.4183 60.2 0.0065 100.1
4.4040 32.5 0.0034 100.2
4.3942 22.9 0.0024 99.6
4.3690 19.9 0.0021 97.1
4.3755 15.5 0.0017 103.3
4.3702 14.4 0.0015 97.4
63.054 1013.4 0.1070
4.504 72.4 0.0016 I 100.0
Blank Period: September 30, 2019 -
Januarv 6 2020 ___._
Week Start Stop Net # Filter Number Date Date
1 9429634 30-Sep-19 07-0ct-19 4.5102
2 9429626 07-0ct-19 14-0ct-19 4.5234
3 9429618 14-0ct-19 21-0ct-19 4.5273
4 9429610 21 -0ct-19 28-0ct-19 4.5261
5 9429602 28-0ct-19 04-Nov-19 4.5150
6 9650987 04-Nov-19 11-Nov-19 4.3692
7 9650986 11 -Nov-19 18-Nov-19 4.3853
8 9650978 18-Nov-19 25-Nov-19 4.3688
9 9650970 25-Nov-19 02-Dec-19 4.3573
10 9650962 02-Dec-19 09-Dec-19 4.3823
11 9650954 09-Dec-19 16-Dec-19 4.3840
12 9650946 16-Dec-19 23-Dec-19 4.3507
13 9650931 23-Dec-19 30-Dec-19 4.3944
14 9650930 30-Dec-19 06-Jan-20 4.3857
Totals
ATTACHMENT D
AIR PARTICULATE LOADING GRAPHS AND SUPPORTING DAT A
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03/29/15
05/29/15
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09/29/15
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03/29/20
05/29/20
07/29/20
09/29/20
11/29/20
Energy Fuels Resources -White Mesa Mill ralibration Date: 10/1/2018
b= 0.00251 I First Monitoring Quarter 2015
Period: July 1 2019 -September 30 2019 m= 1.24054 Updated: 7/30/14 Calibration Slope & Intercept:
Orifice SIN: 8091779
Afi Afi
Week I Filter I Start I Stop I Start I Stop
-Starting
Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in.H20)
9673045 7/1/2019 7/8/2019 142.84 311.32 10108.8 4.0 4.0
2 9673037 7/8/2019 7/15/2019 311.32 480.19 IOL32.2 4,0 4.0 4.0 25.0 298.l 621.5 I.I I 0.91 32.18 9231.9 4.4342 4.6054 171.2 0.0185 100.5
3 9673029 7/15/2019 7/22/2019 480.19 650.74 10233.0 4.0 4.0 4.0 26.5 299,7 619.4 1.12 0.91 32.04 9283.4 4.4430 4.5839 140.9 0.0152 101.5
4 9673016 7/W2019 7/29/2019 650.74 815.2 9867.6 4.0 4.0 4.0 25.2 298.3 622.5 1.11 0.91 32.19 8994.4 4.4068 4.4780 71.2 0.0079 97.9
5 9673013 7/29/2019 8/5/2019 815.2 984.14 10136.4 4.0 4.0 4.0 24.0 297.l 622.0 1.11 0.91 32.24 9254.5 4.3765 4.5203 143.8 0.0155 100.6
6 9673005 8/5/2019 8/12/2019 984.14 1151.49 10041.0 4.5 4.0 4.3 24.6 297.7 620.57 1.15 0.94 33.17 9429.9 4.3710 4.5159 144.9 0.0154 99.6
7 9429697 8/12/2019 8/19/2019 1151.49 1318.43 10016.4 4.5 4.0 4.3 24.6 297.7 620.42 1.15 0.94 33.16 9405.6 4.5125 4.6803 167.8 0.0178 99.4
8 9429689 8/19/2019 8/26/2019 1318.43 1486.3 10072.2 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9160.7 4.5012 4.6934 192.2 0.0210 99.9
9 9429681 8/26/2019 9/3/2019 1486.3 1678.56 11535.6 4.0 4.0 4.0 24.9 298.l 620.95 1.11 0.91 32.16 10506.5 4.5200 4.7210 201.0 0.0191 114.4
IO 9429673 9/3/2019 9/9/2019 1678.56 1823.38 8689.2 4.0 4.0 4.0 24.7 297.8 620.57 I.I I 0.91 32.17 7914.4 4.5159 4.7128 196.9 0.0249 86.2
II 9429665 9/9/2019 9/16/2019 1823.38 1993.99 10236.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9423.8 4.5000 4.6814 181.4 0.0192 101.6
12 9429652 9/16/2019 9/23/2019 1993.99 2158.79 9888.0 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9100.8 4.5009 4.5798 78.9 0.0087 98.1
2326.97 10090.8 3.5 4.0 3.8 17.7 290.9 617.37 1.07 0.89 31.43 8981.4 4.5198 4.7416 221.8 0.0247 100.l
131047.8 I 14.49 11.90 420.09 119908.5 58.022 60.061 2039.1 0.2218 -
10080.6 4.0 4.0 4.0 23.2 296.4 620.34946 1.11 0.92 32.31 9223.7 4.463 4.620 156.9 0.0,11 I 100.0
Insert weekly flow check values in yellow columns.
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/1/2018 I First Monitoring Quarter 2014
Period: July 1 2019 -September 30 2019 Calibration Slope & Intercept: m= l.24054 b= 0.00251 Updated: 7 /30/14
Orifice SIN: 8091779 II ,.:., 6H
Week Filter Start Stop Stan Stop Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in.H20)
I 9673044 7{1/2019 7/8/2019 10858.59 11027.04 10107.0 4.0 4.0
2 9673036 7/8/2019 7/15/2019 11027.04 11195.97 10135.8 4.5 4.0 4.3 25.0 298.1 621.54 1.15 0.94 33.17 9519.9 4.4288 4.7185 289.7 00304 100.6
3 9673028 7/15/2019 7/22/2019 11195.97 11367.46 10289.4 4.0 4.0 4.0 26.5 299.7 619.40 1.12 0.91 32.04 9334.5 4.4330 4.7038 270.8 0.0290 102.1
4 9673018 7/22/2019 7/29/2019 11367.46 11530.92 9807.6 4.0 4.0 4,0 25.2 298.3 622.48 I.I I 0.91 32.19 8939.7 4,4342 4.6709 236.7 0.0265 97.3
5 9673012 7/29/2019 8/5/2019 11530.92 11699.38 10107.6 4.0 4.0 4.0 24.0 297.1 622.05 I.I I 0.91 32.24 9228.2 4.3740 4.5728 198.8 0.0215 100.3
6 9673004 8/5/2019 8/12/2019 11699.38 11867.24 10071.6 4.5 4.0 4.3 24.6 297.7 620.57 1.15 0.94 33.17 9458.6 4.3756 4.5695 193.9 0.0205 99.9
7 9429696 8/12/2019 S/191.?019 11867.24 12034.17 10015.8 4.5 4.0 4,3 24.6 297.7 620.42 1.15 0.94 33.16 9405.1 4.4938 4.7424 248.6 0.0264 99.4
8 9429688 8/19/2019 8/26/2019 12034.17 12201 .88 10062.6 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32,12 9152.0 4.5011 4.8540 352.9 0.0386 99.8
9 9429680 8/26/2019 9/3/2019 12201.88 12394.97 11585.4 4.0 4.0 4.0 24.9 298.1 620.95 I.I I 0.91 32.16 10551.9 4.5105 4.8345 324,0 0.0307 114.9
10 9429672 9/3/2019 9/9/2019 12394.97 12539.77 8688.0 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8157.3 4.5308 4.8663 335.5 0.0411 86.2
II 9429664 9/9/2019 9/16/2019 12539.77 12710.36 !0235.4 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9422.7 4.5038 4.6146 110.8 0.0118 lOJ.5
12 9429653 9/16/2019 9/23/2019 12710.36 12874.46 9846.0 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9062.1 4.5131 4.8507 337.6 0.0373 97.7
13 9429648 9/23/2019 9/30/2019 l2874.46 13042.56 10086.0 4.5 4.0 4.3 17.7 290.9 617.37 1.14 0.95 33.47 9558.0 4.5163 4.9073 391.0 0.0409 JOO.I ·-. T -Totals 131038.2 14.63 12.01 424.10 121009.6 58.061 61.700 3638.2 0.3924
Averages 10079.9 4.2 4.0 4.1 23.2 296.4 620.34946 1.13 0.92 32.62 9308.4 4.466 4.746 279.9 0.0302 I 100.0
Comments:
Insert weekly flow check values in yellow columns.
~ .. ~. ~=-~ ~--. -= ~-:--·-: .. :.·.~-=---1-:-·
Green col11mns~~Ia\ed a~fi:om the mc:1,siation.
Energy Fuels Resources -White Mesa Mill --Calibration Date:-10/1/2~--------I --First Monitoring Quarter 2014
Period: July I 2019-September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN : 8091779
-II ~ .. fill
Week I Filter Start Stop Start Stop Stopping
# Number Date Date Time Time Manometer ManQtncicr
(in.H,O) (in. H20)
%73043 7/1/2019 7/S/20!9 16391.19 16559.61 10105.2 4.0 4.0
2 9673035 7/8/2019 7/15/2019 16559.61 16728.57 10137.6 5.0 4.0 4.5 25.0 298.1 621.>I 1.18 0.97 34.13 9798.1 4.4382 4.6046 166.4-0.0170 100.6
3 9673027 7/15/2019 7/22/2019 16728.57 16901.01 10346.4 4.0 4.0 4.0 M,5 299.7 619.40 1.12 0.91 32.04 9386.3 4.4420 4.6015 161.5 0.0172 1026
4 %73017 7/22/2019 7129/2019 16901.01 17056.44 9325.8 4.5 4.0 4.3 25.2 298.3 622.48 1.15 0.94 33.18 8762.7 4.4218 4.5145 92..7 0.0106 92.5
5 9673011 7n.9f20l9 8/5/2019 17056.44 17224.96 10111.2 4.0 4.0 4.0 24.0 297.1 622.05 111 0.91 32.24 9231.5 4.3816 4.5855 203.9 0.0221 100.3
6 9673003 8/5/201 9 8/1212019 17224.96 17393.94 10138.8 4.0 4.0 4.0 24.6 297.7 620.57 1.11 0.91 32.17 9236.9 4.3755 4.5097 134.2 0.0145 100.6
7 9429695 8/12/2019 8/19/2019 17393.94 17559.73 9947.4 4.0 4.0 4.0 24.6 297 7 620.42 1.11 0.91 32.17 9061.4 4.5000 4.6453 145.3 0.0160 98.7
8 9429687 8/19/2019 8/26/201 9 17559.73 17733.79 10443.6 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9498.5 H98S 4.6841 185.6 0.0195 103.6
9 9429679 8/26/2019 913/2019 17733.79 17919.94 11169.0 ,to 4.0 4.0 24.9 298.1 620.95 1.11 0,91 32.16 10172.6 4.5267 4.7025 175.8 0.0173 110.8
10 9429671 9/3/2019 9/9/2019 17919_94 18064.81 8692.2 4.5 4_0 4.3 24.7 297.S 610.57 1.15 0.94 33.16 8161.3 4,5075 4.66.U 156.S 0.0192 86.2
II 9429663 919/2019 9/16/2019 18064.81 IS236.4S 10300.2 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9482.4 4.5073 4.6415 134.2 0.0142 102.2
12 9429654 9/16/2019 9/2312019 18236.48 18399.9 9805.2 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9024.6 4.5051 4.6481 143.0 0.0158 97.3
13 9429647 9/23/2019 9/30/2019 18399.9 IS5(i7.99 10085.4 4.0 4.0 4.0 17.7 290.9 617.37 1.10 0.92 32.47 9271.5 4.4950 4.6-117 146.7 0.0158 100.1
ToUlls 130608.0 14.60 11.98 423.07 120305.7 58.044 60.025 1981.1 0.2139
IAvcrn1tes 10046.8 4.2 4.0 4.1 23.2 296.4 620.34946 1.12 0.92 32.54 9254.3 4.465 4.617 152.4 0.0165 I 99.7
IO,=, col)llllllSSUl' COlcull!.~ a.,~1118\'S-from lhc: mctstmion.
Energy Fuels Resources -White Mesa Mill 'CalibraifonDrue: 101112018 ~~~-F,rstMonitoring Qiiarier2014
Pe.riod: July I 2019-September 30 2019 Calibrmion Slope & Intercept: m= 1.24054 b== 0.00251 I Updated: 7/30/14
Orifice SIN: 8091779
=t:.=H=:;==t:.H==;;;;;.:;;;;;.;;;;;;sr====*.e===
Week Filter Start Stop Start Stop II Starting Stopping
# Number Date Date Time Time Manometer Manomc1cr
--+---+----+----+----+----1-·~· . (in. H20) (in. H20)
I 96730-12 7/1/2019 7/8/2019 9473.99 9642.3S 10103.4 4.5 4.0
2 9673034 7/8/2019 7/15/2019 9642.'.lS 9811.37 !0139.4 5.0 4.0 4.5 25.0 298.1 621.54 1.18 0.97 34.13 9799.9 4.4427 4.4909 48.2 0.0049 100.6
3 9673026 7/15/2019 7/22/2019 9811 .37 9983.67 10338.0 3.0 4.0 3.5 26.5 299.7 619.40 1.05 0.85 29.96 8771.8 4.4462 4.6037 157.5 0.0180 102.6
4 %73019 7/22/2019 7/29/2019 9983.67 10139.41 9344.4 4.0 4.0 4.0 25.2 298.3 622.48 1.11 0.91 32.19 8517.5 4.4147 4.508-4 93.7 0.0110 92.7
5 9673010 7/29/2019 8/5/2019 10139.41 10307.8 10103.4 4_0 4.0 4.0 24.0 297.1 62.2.0S I.I I 0.91 32.24 9224..1 4.3665 4.4903 123.S 0.0134 100.2
6 9673002 8/5/2019 8/12/2019 10307.8 10476.77 10138.2 4.0 4.0 4.0 24.6 297.7 620.57 I.I I 0.91 32.17 9236.4 4.3802 4.4900 109.8 0.0119 100.6
7 9429694 8/12/2019 8/19/2019 10476.77 10642.56 9947.4 4.0 4.0 4.0 24.6 297.7 620.42 I.I I 0.91 32.17 9061.4 4.5058 4.6335 127.7 0.0141 98.7
8 9429686 8119/2019 8/26/2019 10642.56 10816.54 10438.8 4.0 4.0 4.0 25.1 298.2 619.51 l.12 0.91 32.12 9494.l 4.5371 4.7165 179.4 0.0189 103.6
9 9429678 S/26/2019 9/3120)9 10816.54 11002.77 11 173.S 3.5 4.0 3.8 24.9 l9S.l 620.95 1.08 O.SS 31.14 9853.3 4.5139 4.7190 205.1 0.0208 110.9
10 9429670 9/3/2019 919/2019 11002.77 11147.64 8692.2 4.0 4.0 4.0 24.7 297.S 620.57 I.I I 0.91 32.17 7917.1 4.5213 4.6889 167.6 0.0212 86.2
11 9429662 9/9/2019 9/16/2019 11147.64 11 319.7 10323.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9503.9 4.5036 4.6542 150.6 0.015S 102.4
12 9429655 9116/2019 9/23/2019 11319.7 I 1~82.71 9780.6 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9001.9 4.4869 4.6096 122.7 0.01 36 97.0
13 9429646 9/23/2019 9130/2019 l 1482.71 l 1650.81 10086.0 4.0 4.0 4.0 17.7 290.9 617.37 1.10 0.92 32.47 9272.1 4.5086 4.6513 142.7 0.0154 100.1
Totals 130609.2 1 14.45 11.86 418.99 t 19154.3 58.064 59.885 1820.8 0.1992
Avc111ses 10046.9 4.0 4.0 4.0 23.2 296.4 620.34946 I.I I 0.91 32.23 9165.7 4.466 4.607 140.J 0.0153 I 99.7
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/1/2018 --1--First Monitoring Quarter 2014
Period: July l 2019-September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN: 8091779 ~~---·-·--llli llli
Week I Filter I Start I Stop I Start I Stop 1•1 Stfilting Stopping
# Number Date Date Time Time , ~: Manometc1 Mallometer
(io.H20) (in.H20)
I 9673041 7/1/2019 7/8/2019 25866.62 26035.06 10106.4 4.0 4.0
2 9673033 7/8/2019 7/15/2019 26035.06 26203.95 10133.4 4.5 4.0 4.3 25.0 298.l 621.54 l.15 0.94 33.17 9517.7 4.4443 4.5802 135.9 0.0143 100.5
3 9673025 7/15/2019 7/22/2019 26203.95 26376.04 10325.4 4.5 4.0 4.3 26.5 299.7 619.40 1.15 0.94 33.03 9656.0 4.4370 4.5801 143.1 0.0148 102.4
4 9673020 7/22/2019 7/29/2019 26376.04 26531.67 9337.8 4.0 4.0 4.0 25.2 298.3 622.48 l.l I 0.91 32.19 8511.5 4.4285 4.5157 87.2 00102 92.6
5 9673009 7/29/2019 8/5/2019 26531.67 26700.24 10114.2 4.0 4.0 4.0 24.0 297.1 622.05 I.I l 0.91 32,24 9234.3 4.3665 4.4661 99.6 0.0108 100.3
6 9673001 8/5/2019 8/12/2019 26700.24 26869.21 10138.2 4.0 4.0 4.0 24.6 297.7 620.57 1.11 0.91 32.17 9236.4 4.3723 4.4667 94.4 0.0102 100.6
7 9429693 8/12/2019 8/19/2019 26869.21 27035.02 9948.6 4.0 4.0 4.0 24.6 297.7 620.42 I. I I 0.91 32.17 9062.5 4.5018 4.6216 l 19.8 0.0132 98.7
8 9429685 8/19/2019 8/26/2019 27035.02 27202.61 10055.4 4.0 4.0 4.0 25.l 298.2 619.51 l.12 0.91 32.12 9145.4 4.4992 4.6600 160.8 0.0176 99.8
9 9429677 8/26/2019 9/3/2019 27202.61 27369.92 10038.6 3.5 4.0 3.8 24.9 298.1 620.95 1.08 0.88 31.14 8852.2 4.4984 4.6759 177.5 0.0201 99.6
IO 942966/) 9/3/2019 9/9/2019 0 143.82 8629.2 4.5 4.0 4.3 24.7 297.8 620.57 U5 0.94 33.16 8102.1 4.5330 4.6703 137.3 0.0169 85.6
11 9429661 9/9/2019 9/16/2019 143.82 315.5 10300.8 4.0 4.0 4.0 18.7 291.8 621.21 I.IO 0.92 32.51 9482.9 4.5037 4.6234 119.7 0.0126 102.2
12 9429656 9/16/2019 9/23/2019 315.5 478.88 9802.8 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9022.3 4.5126 4.6320 l 19.4 0.0132 97.3
13 9429645 9/2312019 9/30/2019 478.88 646.99 10086.6 4.0 4.0 4.0 17.7 290.9 617.37 I.IO 0.92 32.47 9272.6 4.4983 4.6203 122.0 0.0132 100.1
Totals 129017.4 14.53 ll.92 421.08 118315.0 58.036 59.670 1633.4 0.1798
Averages 9924.4 4.l 4.0 4.0 23.2 296.4 620.34946 1.12 0.92 32.39 9101.2 4.464 4.590 125.6 o.ot38 I 98.S
Replaced Elapsed time indico1or on 9/3/2019
Insert weekly flow check values in yellow columns. :~·,·:.·: :~·:-.. ~·~-.:--~::.,:.~::~
Green.colulllllS.are·ceJ.culotea,ave£118flS fi:omlik; ~ ~ati~.
)~ -·?· ·;-:;.~-;.:.~~··t .' Energy Fuels Resources . White Mesa Mill Calibration Date: 10/1/2018 First Monitoring Quarter 2014
.. flDv.f-7 ···· Period: July l 2019 · September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
' ' .. -...-----~-· ' .............. Orifice SIN: 8091779
~I Af{ i m; Tn, I P•-;; · -~ -;,r..J.1L~Oi Af{ •
I ;. -• .. . -'· ·..,. 11 I . · ·•• . • .iGnisa-I ...c-...-............ ~-~ 4 • Week Filter Start Stop Start Stop Starting Stopping l)S::-::_~ Wkly.Avg., Wkly. Av.g.. .. . liiie. -· # • Pres.<rore · · · · · \~'-j ..... _.; Number Date Date Time Time I Manometer Manomete-Temp.
(in. H20) (in. H20) · _ l'°C) (Jlllllfi&) ·-· __ . . ~ I . fiL . '..J'~ .
I 9673040 7/1/2019 7/8/2019 502.36 670.82 10107.6 4.0 4.0 4.0 23.3 296.5 619.61 I.I I 0.91 32.21 9220.1 4.4361 4.5883 152.2 0.0165 100.3
2 9673032 7/8/2019 7/15/2019 670.82 839.7 10132.8 4.0 4.0 4.0 25.0 298.1 621.54 I.I I 0.91 32.18 9232.4 4.4217 4.5913 169.6 0.0184 100.5
3 9673024 7/15/2019 7/22/2019 839.7 1010.29 10235.4 4.0 4.0 4,0 26.5 299.7 619.40 1.12 0.91 32.04 9285.6 4,4338 4.6223 188.5 0.0203 101.5
4 9673021 7/22/2019 7/29/2019 1010.29 1174.77 9868.8 4.0 4.0 4.0 25.2 298.3 622.48 I.I I 0.91 32.19 8995.5 4.4288 4.5408 112.0 0.0125 97.9
5 9673008 7/29/2019 8/5/2019 1174.77 1343.62 10131.0 4.0 4.0 4.0 24.0 297.1 622.05 I.II 0.91 32 24 9249.6 4.3703 4.5169 146.6 0.0158 100.5
6 9429700 8/5/2019 8/12/2019 1343.62 1511.07 10047.0 4.0 4.0 4.0 24.6 2.97.7 620.57 I.II 0.91 32.17 9153.3 4.5192 4.6657 146.5 0.0160 99.7
7 9429692 8/12/2019 8/19/2019 1511.07 1677.98 10014.6 4.0 4.0 4.0 24.6 297.7 620.42 1.11 0.91 32.17 9122.7 4.4918 4.6206 128.8 0.0141 99.4
8 9429684 8/19/2019 8/26/2019 1677.98 1845.67 10061.4 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9150.9 4.5080 4.7255 217.5 0.0238 99.8
9 9429676 8/26/2019 9/3/2019 1845.67 2038.06 11543.4 3.5 4.0 3.8 24.9 298.1 620.95 1.08 0.88 31.14 10179.2 4.5300 4.7355 205.5 0.0202 114.5
10 9429668 9/3/2019 9/9/2019 2038.06 2182.88 8689.2 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8158.4 4.4907 4.6676 176.9 0.0217 86.2
11 9429660 9/9/2019 9/16/2019 2182.88 2353.44 10233.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9421.J 4.5303 4.6917 161.4 0.0171 101.5
12 9429657 9/16/2019 9/23/2019 2353.44 2518.14 9882.0 4.0 4.0 4.0 17.7 290.9 618.87 1.10 0.92 32.50 9095.2 4.4938 4.6648 171.0 0.0188 98.0
13 9429644 9/23/2019 9/30/2019 2518.14 2686.28 10088.4 4.5 4.0 4.3 17.7 290.9 617.37 1.14 0.95 33.47 9560.2 4.5091 4.6353 126.2 0.0132 100.1
~~ ~~ ~~-,:~:~ ·~ ~.~!3~·-~.~~·~. --~-~ . I Totals 131035.2 -14.49 11.90 420.10 119824.2 58.164 60.266 2102.7 0.2284
.--~--. Tl..J·""•~.! __ .,~1~ . --~__: Averages 10079.6 4.0 4.0 4.0 23.2 296.4 620.34946 I.I I 0.92 32.32 9217.2 4.474 4.636 161.7 0.0176 100.0
Comments:
lnsen weekly flow cbeck values in yellow columns. I
. -..:-::ru
~n i;o_tumns 3!~ ciil!)lil:u¥d 3Vl:r:I~ from ll;le ·mc1 ~uon, I ,, -,
Energy Fuels Resources -White :\1esa Mill ICnlibration Date: 10/1/2018 I First Monitoring Quarter 201 4
Period: July 1 2019 -September 30 2019 Calibration Slope & Intercept: m= 1.24054 b= 0.00251 Updated: 7/30/14
Orifice SIN: 8091779
==tili===;====MI===;;;::::::;;;=.;;:;:::;:;;=====~~
Week I Filter Stan Stop Swt Stop ~ • Slarting Stopping
# Number Date Date Time Time ~l~ Manometer Manometer ~ (in. H20) (in. H20)
9673039 7/l/2019 7/8/2019 7330.45 7498.94 10109.4 4.0 4.0
2 9673031 7/8/2019 7/15/2019 7498.94 7667.P.. !0132.8 4.0 4.0 4.0 25.0 298.1 621.54 1.1 I 0.91 32.18 9232.4 4.4430 4.5605 117.5 0.0127 100.S
3 9673023 7/15/2019 7/22/2019 7667.82 7838.37 10233.0 4.0 4.0 4.0 26.5 299.7 619.40 1.1 2 0.91 32.04 9283.4 4.4375 4.5058 68.3 0.0074 101.5
4 9673022 7/22/2019 7/29/2019 7838.37 8002.86 9869.4 4.0 4.0 4.0 25.2 298.3 622.48 1.11 0.91 32.19 8996.1 4.4438 4.4770 33.2 0.0037 97.9
5 9673007 7/29/2019 8/5/2019 8002.86 8171.72 10131.6 3.5 4.0 3.8 24.0 297.1 622.05 1.08 0.88 31.22 89SS.9 4.3620 4.4143 52.3 0.0058 100.5
6 9429699 8/5/2019 8/12/2019 8171.72 8339.16 10046.4 3.0 4.0 3.5 24.6 297.7 620.57 l.04 0.85 30.09 8560.5 4.4988 4.5784 79.6 0.0093 99.7
7 9429691 8/12/2019 8/19/2019 8339.16 8506.08 10015.2 4.0 4.0 4.0 24.6 297.7 620.42 I.I I 0.91 32.17 9123.2 4.5165 4.5869 70.4 0.0077 99.4
8 9429683 8/19/2019 8/26/2019 8506.08 8673.85 10066.2 4.0 4.0 4.0 25.1 298.2 619.51 1.12 0.91 32.12 9155.2 4.5102 4.6383 128.1 0.0140 99.9
9 9429675 8/26120 19 9/3/2019 8673.85 8866.21 11541.6 4.5 4.0 4.3 24.9 298.1 620.95 1.15 0.94 33.16 10836,1 4,5356 4.6539 118.3 0.0109 114.5
10 9429667 9/3/2019 9/9/2019 8866.21 9011.01 8688.0 4.5 4.0 4.3 24.7 297.8 620.57 1.15 0.94 33.16 8157.3 4.4895 4.6112 121.7 0.0149 86.2
11 9429659 9/9/2019 9/16/2019 9011.01 9181.67 10239.6 4.0 4.0 4.0 18.7 291.8 621.21 1.10 0.92 32.51 9426.6 4.4863 4.6289 142,6 0.0151 101.6
12 9429658 9/16/2019 9123/2019 9181.67 9346.42 9885.0 4.0 4.0 4.0 17.7 290.9 61&.87 1.10 0.92 32.50 9098.0 4.4901 4.5539 63.8 0.0070 98.1
9346.42 9514.59 10090.2 3.~ 4.0 3.8 17.7 290.9 617.37 1.07 0.89 31.43 89S0.9 4.5138 4.6691 155.3 0.0173 100.1
Totals 131048.4 14.39 11.81 416.98 119027.3 58.157 59.421 1263.9 0.1381
Avera_ges 10080.6 3.9 4.0 4.0 23.2 296.4 620.34946 I.I I 0.91 32.08 9155.9 4.474 4.571 97.2 0.0106 100.0
Blanks Period: July 1 2019 -September 30
2019
Week Filter Start Stop Net # Number Date Date
1 9673038 01-Jul-19 08-Jul-19 4.4266
2 9673030 08-Jul-19 15-Jul-19 4.4528
3 9673015 15-Jul-19 22-Jul-19 4.3885
4 9673014 22-Jul-19 29-Jul-19 4.3974
5 9673006 29-Jul-,19 05-Auq-19 4.3783
6 9429698 05-Auq-19 12-Auq-19 4.4921
7 9429690 12-Auq-19 18-Auq-19 4.5111
8 9429682 18-Auq-19 26-Auq-19 4.5118
9 9429674 26-Auq-19 03-Sep-19 4.5313
10 9429666 03-Sep-19 09-Sep-19 4.4910
11 9429651 09-Sep-19 16-Sep-19 4.5089
12 9429650 16-Sep-19 23-Sep-19 4.5265
13 9429635 23-Sep-19 30-Sep-19 4.5051
Totals
Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019
b= -0.026361
First Monitoring Quarter 2015
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 Updated: 7/30/14
Orifice SIN: 8091779
····-11.H 11.H
Week i Filter St.an Stop Stan a., 111 som,, Stopping
# Number Date Date Time Time / Manometer Manometer
•1 (in.H20) (in.H20)
I 9429636 9/30/2019 10/7/2019 2326.97 2495.82 10131.0 4.5 4.0
2 9429627 10/7/2019 10/14/2019 2495.82 2663.77 10077.0 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9432.2 4.5055 4.6796 174.1 0.0185 100.0
3 9429619 10/14/2019 10/21/2019 2663.77 2830.92 10029.0 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9638.7 4.5071 4.6710 163.9 0.0170 99.5
4 9429611 10/21/2019 10/28/2019 2830.92 2998.77 10071.0 4.0 4.0 4,0 7.6 280.7 619.86 1.09 0.94 33.18 9463.2 4.5262 4.6499 123.7 0.0131 99.9
5 9429609 10/28/2019 11/4/2019 2998.77 3170.47 10302.0 4,0 4.0 4.0 0.4 273.6 621.69 1.07 0.95 33.67 9822.9 4.5183 4.5986 80.3 0.0082 102.2
6 9650995 11/4/2019 11/11/2019 3170.47 3359.1 J 1317.8 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10655.8 4.3640 4.4814 117.4 0.0110 112.3
7 9650994 11/11/2019 11/18/2019 3359.1 3504.02 8695.2 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8202.2 4.3564 4.4701 113.7 0.0139 86.3
8 9650985 11/18/2019 11/25/2019 3504.02 3675.3 10276.8 4.0 4.0 4.0 4.7 277.8 618.01 1.08 0.94 33.31 9693.2 4.3843 4.4333 49.0 0.0051 102.0
9 9650977 11/25/2019 12/2/2019 3675.3 3843.37 10084.2 3.5 4.0 3.8 -0.1 273.0 614,76 1.04 0.92 32.47 9272.5 4.3867 4.4302 43.5 0.0047 100.0
10 9650969 12/2/2019 12/9/2019 3843.37 4011.71 10100.4 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9579.9 4.3454 4.3807 35.3 0.0037 100.2
II 9650961 12/9/2019 12/16/2019 4011.71 4179.04 10039.8 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9547.4 4.3795 4.4056 26.1 0.0027 99.6
12 9650953 12/16/2019 12/23/2019 4179.04 4342.3 9795.6 4.0 4.0 4.0 -2.1 271.1 623.82 1.06 0.96 33.89 9400.1 4.3438 4.3808 37.0 0.0039 97.2
13 9650945 12/23/2019 12/30/2019 4342.3 4515.82 10411.2 3.5 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9606.7 4.3359 4.3611 25.2 0.0026 103.3
4515.82 4679.46 9818.4 4,0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9447.2 4.3010 4.3276 26.6 0.0028 97.4
Totals 141149.4 -15.10 13.24 467.49 133448.2 61.765 62.913 1147.8 0.1208
Averages 10082.1 4.0 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.39 9532.0 4.412 4.494 82.0 0.0086 I 100.0
~~~··0: k;-~~ ~ ;:; i!. Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019 First Monitoring Quarter 2014 ~m~~i ~-'. Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 b= -0.02636 Updated: 7/30/14
(:,~ ~ -:.-~.-~·. ·~_:l .. -··~ Orifice SIN: 8091779 "-~ t.H 6H II Tu ~'~~--1:.~1 ~i . .,~~~ ' -··.J , . ·-I . ,,., 1.--~ ' Week Filter Start Stop Start Stop • Starting Stopping Wkly.Ayg, , Wl!Jy. Avg. , I !I*· ~, · · ~urc · · -•. · ,-1 ·w'~ ~u>~.· ~ # Number Date Date Time Time Manometer Manometer Temp. '•'-'.'•""!!""~ . c·c, ti;;~ ..... ',r"7ii .,~. I -,r.:.::=.. r-, (in.H20 ) (in.H20) . . -fnlmHg) .· _ . ~ .
1 9429637 9/30/2019 10n12019 13042.56 13210.91 IOIOI.O 4.0 4.0 4.0 14.4 287.6 619.68 1.10 0.93 32.77 9374.3 4.5125 4.7621 249.6 0.0266 100.2
2 9429628 IOn/2019 10/14/2019 13210.91 13379.46 10113.0 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0,94 33.06 9465.9 4.5085 4.7949 286.4 0,0303 100.3
3 9429620 I0/14/2019 I0/21/2019 13379.46 13546.17 10002.6 4.5 4.0 4.3 I0,8 284.0 618.26 1.13 0.96 33.94 9613.4 4.5251 4.7681 243.0 0.0253 99.2
4 9429612 10/21/2019 10/28/2019 13546.17 13715.12 10137.0 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9525.2 4.5253 4.7286 203.3 0.0213 100.6
5 9429604 10/28/2019 11/4/2019 13715.12 13887.11 10319.4 4.0 4.0 4.0 0.4 273.6 621.69 1.07 0.95 33.67 9839.5 4.5265 4.7121 185.6 0.0189 102.4
6 9650996 11/4/2019 11/11/2019 13887.11 14075.73 11317.2 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10655.3 4.3556 4.6089 253.3 0.0238 112.3
7 9650993 ll/11/2019 ll/18/2019 14075.73 14219.63 8634.0 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8144.5 4.3455 4.5888 243.3 0.0299 85.7
8 9650984 11/18/2019 11/25/2019 14219.63 14391.63 10320.0 4.5 4.0 4.3 4.7 277.8 618.01 I.I I 0.97 34.31 10027.7 4.3843 4.5157 131.4 0.0131 102.4
9 9650976 11/25/2019 12/2/2019 14391.63 14559.87 10094.4 4.0 4.0 4.0 -0.1 273.0 614.76 1.07 0.95 33.52 9580.2 4.4117 4.4827 71.0 0.0074 JOO.I
10 9650968 12/2/2019 12/9/2019 14559.87 14727.37 10050.0 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9532.1 4.3480 4.4150 67.0 0.0070 99.7
II 9650960 12/9/2019 12/16/2019 14727.37 14895.38 10080.6 4,5 4,0 4.3 0.6 273.8 618.87 1.11 0.98 34.60 9875.5 4.3864 4.4258 39.4 0.0040 100.0
12 9650952 12/16/2019 12/23/2019 14895.38 15057.99 9756.6 4.0 4.0 4,0 -2.1 271.1 623.82 1.06 0.96 33.89 9362.7 4.3323 4.4118 79.5 0.0085 96.8
13 9650944 12/23/2019 12/30/2019 15057.99 15231 10380.6 3.5 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9578.4 4.3486 4.4444 95,8 0.0100 103.0
14 9650933 12/30/2019 1/6/2020 15231 15394.99 9839.4 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9467.4 4.3320 4.3773 45.3 0.0048 97.6
:};-~ ~;:11~( :-~i ::--~ .'' · __ .;' Totals 141145.8 i 15.17 13.30 469.57 134042.2 61.842 64.036 2193.9 0.2308
Averages 10081.8 4.1 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.54 9574.4 4.417 4.574 156.7 0.0165 100.0
Comments:
Insert weekly flow check values in yellow columns. I
. . ~ ~·~~,r;_:,,~ ~ ~ \\(>lumns_are CQbslate<f~,'cnlgail·nom thl, mcl1,Wi&.
= ·,.............. '
Energy Fuels Resources -White Mesa Mill Calibratfon Date: 91.V1019
b= -0.02~36-,
First Monitoring Quarter W 14
Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 Updated: 7/30/14
Orilice SIN: 8091779
fill fill
Weeki Filter I Start Stop Start Stop
1-=-..... Starting Stopping ,~,
# Number Date Date Time Time ~ Manomc1cr Manometer I .• (in. H20) (in.H20)
942%38 9/30/2019 1(){7/2019 18567.99 18736.36 10102 2 4.5 4.0
2 9429629 10nno19 10/.14/2019 18736.36 18902.69 9979.8 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9341.2 4.5055 4.6207 115.2 0.0123
3 9<129621 10114/2019 10/21/2019 18902.69 19066.39 9822.0 4.0 4.0 4.0 10.8 284.0 618.26 1.09 0.93 32.95 9163.1 4.5030 4.6527 1~9.7 0.0163 97.4
4 9429613 1onino19 10/28/2019 19066.39 19234.71 10099.2 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9489.7 4.5263 4.6462 119.9 0.0126 100.2
.s 9429605 10/28/2019 ll/4/2019 19234.71 19392.54 9469.8 3.5 4.0 3.8 0.4 273.6 621.69 1.04 0.92 32.62 8748.3 4.5230 4.55% 36.6 0_0042 93.9
6 96S0997 11/4/2019 11/11/2019 1939254 19584.11 11494.2 3.5 4.0 3.8 7.7 280.8 622.45 I.OS 0.91 32.21 1().184.9 4.3365 4.4640 127.5 0.0122 114.0
7 %50992 11111/2019 11/18/2019 19584.11 19728.34 8653.8 4.0 4.0 4.0 6.S 279.7 622.25 I.OS 0.94 33.31 8163.2 4.3574 4.4410 83.6 0.0102 85.9
s 9650983 11/18/2019 11/25/2018 1972834 19899.78 !0286.4 4.0 4.0 4.0 4.7 277.8 618.01 1.08 0.94 33.31 9702.2 4.3669 4.4223 55.4 0.0057 102.0
9 9650975 11/25/2019 12/2/2019 19899.78 !0067.83 10083.0 4.0 4.0 4.0 -0.1 273.0 614.76 1.07 0.95 33.52 9569.4 4.3418 4.4120 70.2 0.0073 100.0
10 %50967 12/212019 12/9/2019 20067.83 20236.16 10099.8 4.0 4.0 4.0 3.0 276.1 621.01 I.OS 0.95 33.50 9579.3 4.3395 4.3808 41.3 0.0043 100.2
II 96S0959 12/9/2019 12/16/2019 20236.16 20403.78 10057.2 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9563.9 4.3698 4.3977 27.9 0.0029 99.S
12 9650951 12/16/2019 12/23/2019 20403.78 20566.88 9786.0 4.0 4.0 4.0 -2.1 271.J 623.82 1.06 0.96 33.89 9390.9 4.3421 4.3832 41.1 0.0044 97.1
13 9650943 l 21'-3/2019 12/30/2019 20566.88 20739.6 !0363.2 3.5 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9562.4 ~.3S30 4.3825 29.5 0.0031 102.8
20739.6 20903.SS 9855.0 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.9S 9482..4 4.3088 4.3411 32.3 0.0034 97.8
Totals 140151.6 15.03 13.18 465.46 131899.6 61.703 62.747 1044.0 0.1108
Averages 10010.8 3.9 4.0 4.0 4.1 277.2 619.7765 1.07 0.94 33.25 9421.4 4.407 4.482 74.6 0.0019 I 99.3
.:.: ·::.. ·-:;_]_:__ . -::;;.:-:·, 1 .. ·. Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019 First Monitoring Quaner 2014 ··aJ.~~s .. Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 b= -0.02636 Updated: 7/30/14 :-... : _~ _: -J ·:-r ~,.,.. Orifice SIN; 8091779
J 'l --~ fill fill ~ ~IJ Ta ·-,, M'·· ; I~· I ~=', ,~-Bl ~'" ~ :~ ,rm, ~ . ~ ]-II Week Filter Start Stop Start Stop • ) •. 1 Starting Stopping .. ! Wkly. 'Avg, : · Wktr. Avg, • · .,;c ! ~ I! # Number Date Date Time Time ' •• J Manometer Manometer " • · T~•t:i· ~ ~ ...... ,d~ . ~ ~ ...... 1 ......
J :I_ i c-(in. H20) (in. H20) ~~· . . '(0Cl ·-· I (.;mHg) .·" ·= · · !~ .. , r.i . ;M i_ .
I 9429639 9/30/2019 IM/2019 11650.81 11819.1 10097.4 4.5 4.0 4.3 14.4 287.6 619.68 1.13 0.% 33.76 9653,9 4.5223 4.6602 137.9 0.0143 100.2
2 9429630 10/712019 10/,14/2019 11819.1 11990.03 10255.8 4.0 4.0 4.0 9.4 282.6 619,18 1.09 0.94 33.06 9599.6 H 9SO 4.6560 161.0 0.0168 101.7
3 9429622 10/1412019 10/21/2019 I 1990.03 12153.77 9824.4 4.0 4.0 4.0 10.8 2&4.0 618.26 1.09 0.93 32.95 9165.4 4.5107 4.6469 136.2 0.0149 97.5
4 9429614 10/21/2019 J0/28/2019 12153.77 12322.09 10099.2 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 94S9.7 4.5263 4.6623 136.0 0.0143 100.2
5 9429606 IO/W2019 11/412019 12322.09 12479.92 9469.S 3.5 4.0 3.8 0.4 273.6 621.69 1.().1 0.92 32.62 874$.3 4.52$1 4.5997 71.6 0.0082 93.9
6 9650998 11/4/2019 11/111..!019 12479.92 12671.45 11491.8 4.0 4.0 4.0 7.7 280.S 622.45 1.08 0.94 33.25 10819.6 4.3517 4.4842 132.5 0.0122 114,0
7 96S0991 l l/11/2019 11/18/2019 12671.45 12$15.73 8656.8 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.3 1 8166.0 4.3539 -1.4701 116.2 0.0142 85.9
8 9650982 11/18/2019 11/25/2019 12815.73 12987.17 10286.4 4.0 4.0 4.0 4,7 277.8 618.01 1.08 0.94 33.31 9702.2 4.3598 4.4218 62,0 0.006-I 102.0
9 9650974 11/25/2019 12/2/2019 12987.17 13155.24 10084.2 4,0 4.0 4.0 -0.1 273.0 614.76 1.07 0.95 33.52 9570.5 4.3383 4.4119 73.6 0.0077 100.0
10 9650%6 12/212019 12/9/2019 l3J5S.24 13323.55 10098.6 4.0 4.0 4.0 3.0 276.1 621.01 1.08 0.95 33.50 9578.2 4.3584 4.4096 51.2 0.0053 100.2
11 9650958 1wno19 12/16/2019 13323.55 13491.18 10057.8 4.5 4.0 4.3 0.6 273.8 618.87 l.11 0.98 34.60 9853.2 4.'.l703 4.4126 42.3 0.0043 99.8
12 %50950 12116/2019 12/2312019 13491.18 13654.28 9786.0 4.0 -1.0 4.0 -2.1 271.1 623.82 1.06 0.96 33.89 9390.9 4.3338 4.3884 54.6 0.0058 97.1
13 9650942 12/2112019 12/30/2019 13654.28 13826.82 10352.4 4.0 4.0 4.0 -1.6 271.5 615.65 1.07 0.95 33.63 98:59.4 4.3453 4.3833 38.0 0.0039 102.7
14 9650935 12/30/2019 116/2020 13826.82 13991 9850.8 3.S 4.0 3.8 -4.5 268.6 621.39 1.03 0.93 32.92 9183.3 4.3450 4,1904 45.4 0.0049 97.7
: :.: \ -;, ::.J : t·~,.~ '.-' :-. . . Tomls 140411.4 15.10 13.24 467.50 132780.3 61.739 62.997 1258.5 0.1332 I :_:
Averages 10029 4 4.0 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.39 9484.3 4.410 4.500 89.9 0.0095 99.5
Commenl,S:
loscn weekly flow check values in yellow columns. ' • _-:,. -_'w.__' i -=~. :7.:.J
G~ columns nc:rucuhucd·.a.~,fmm the met smuon. I --.:---. . -,-.. -,
~ Xf~-~-~-;t Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019 First Monitoring Quarter 2014
~'.&~&' Period: September 30, 2019 -January 6, 2020 Calibration Slope & Intercept: m= 1.26445 b= -0.02636 Updated: 7/30/14 .• -1 1 ., _; :-:.. .. ~,
... --=--.. :..__ (~: ~-~· ·.~_·· Orifice SIN: 8091779
I l'ili l'ili ~~I 'Fa
Week Filter Start Stop Start Stop Starting Stopping
# Number Date Date Time Time Manometer Manometer TeDJp.
(in.H20) (in.H20) ' {1'0) l, ~
1 9429640 9/30/2019 10/7/2019 64699 815.37 10102.8 4.0 4.0 4.0 14.4
2 9429631 10/7/2019 10/14/2019 81S.37 986.21 10250.4 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 0.0152
3 9429623 10/14/2019 10/21/2019 986.21 1149.91 9822.0 4.0 4.0 4.0 10.8 284,0 618.26 l.09 0.93 9163.2 4.5040 4.6338 0.0142 97.4
4 9429615 10/21/2019 10/28/2019 1149.91 1318.23 10099.2 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9489.7 4.5235 4.6402 116.7 0.0123 100.2
5 9429607 10/28/2019 1114/2019 13 18.23 1476.54 9498.6 3.5 4.0 3.8 0.4 273.6 621.69 1.04 0.92 32.62 8774.9 4.5475 -1.6296 82.1 0.0094 94.2
6 9650999 11/4/2019 11111no19 1476.54 1667.68 11468.4 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10797.6 4.3502 4.4939 143.7 0.0133 113.8
7 9650990 11/11/2019 11/18/2019 1667.68 1811.9 8653.2 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8162.6 4.3855 4.4990 11'.l.5 0.0139 85.8
8 9650981 l l/18/2019 1112512019 1811.9 198147 10294.2 4.5 4.0 4.3 4.7 277.8 618.01 1.11 0.97 34.31 10002.7 4.3545 4.3955 41.0 0.0041 102.1
9 9650973 11/25/2019 12/212019 1983.47 2151.42 10077.0 3.5 4.0 3.8 -0.1 273.0 614.76 1.04 0.92 32.47 9265.9 4.3480 4.4105 62.5 0.0067 100.0
10 9650965 12/'>J.!019 12/9/2019 2151.42 2319.79 10102.2 4,0 4.0 4.0 3.0 276.1 621.0l 1.08 0.95 33.50 9581.6 4.3697 4.4179 48.2 0.0050 100.2
II 9650957 12/9/2019 12/16/2019 2319.79 2487.35 10053.6 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9560.5 4.3490 4.3850 36.0 0.0038 99.7
12 9650949 12/16/2019 12/23/2019 2487.35 2650.42 9784.2 4.0 4.0 4.0 -2.1 271.1 623.82 1.06 0.96 33.89 9389.2 4.364J 4.4152 50.9 0.0054 97.1
13 9650941 12/!3/2019 12/30/20 19 2650.42 2823.26 10370.4 3-~ 4.0 3.8 -1.6 271.5 615.65 1.04 0.92 32.59 9569.0 4.3419 4.3838 41.9 0.0044 102.9
14 9650936 12/30/2019 1/6/2020 2823.26 2987.41 9849.0 4.0 4.0 4.0 4.5 268.6 62L39 1.06 0.96 33.98 9476.7 4.3396 4.3857 46.1 0.0049 97.7
'\ ·; '., I -• -' Totols 140425.2 15.03 13.18 465..47 132204.0 61.810 62.978 1168.5 0.1243
.:: •• '.-;:-; ~1• i f
1
• :· .. :· -r ,--Averages 10030.4 3.9 4.0 4.0 4.1 277.2 619.7765 l.07 0.94 33.25 9443.1 4.415 4.498 83.5 0.0089 99.5
Comments:
lnsen weekly flow check values in yellow columns.
~~ ··::~ ;-:.;J-~.-~=-~~:----:,.·-.~[ -::: ..
6-.;.o,lumtis ~ ~~~31eita~·from the mcJ.s'\11tj!)!I.
Calibration Date: 9/3/2019 First Monitoring Quarter 2014
Calibration Slope & Intercept: m= 1.26445 b= -0.02636 Updated: 7/30/14
Orifice SIN: 8091779
'.i -• ,•~T·~· Ml Ml Pa ._~ .. _ 'Tr
,:~-• f..~
Week Filter Start Stop Start Stop 'I • -• Starting Stopping ..... ·:ar-, . .;:~ ... -.·
,:· ..... -.. -..... ·' # Number Date Date Time Time Mnnomcrer Manometer Pressure 'Wa!Wit ; . !' > r (in.H20) (in.H20) •. Jal· .1~ •. 1: •..
1 9429641 9/30/2019 1on120,19 2686.28 2855.17 10133.4 4.0 4.0 619.68 l.10 0.93 32.77 9404.4 4 . .5043 4.6672 162.9 0.0173 100.5
2 9429632 10/7/2019 10/14/2019 2855.17 3023.1 10075.8 4.0 4.0 4.0 9.4 282.6 619.18 1.09 0.94 33.06 9431.1 4.5016 4.7143 212.7 0.0226 100.0
3 9429624 10/14/2019 l0/21/2019 3023.1 3190.29 10031.4 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9641.0 4.5155 4.6899 174.4 0.0181 99.5
4 9429616 10/21/2019 10/28/2019 3190.29 3357.97 10060.8 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9453.6 4.5127 4.6869 174.2 0.0184 99.8
5 9429608 10/28/2019 11/4/2019 3357.97 3530.39 10345.2 4.0 4.0 4.0 0.4 273.6 621.69 1.07 0.95 33.67 9864.1 4.5355 4.6677 132.2 0.0134 102.6
6 96.5 1000 11/4/2019 11/11/2019 3530.39 3719.06 11320.2 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10658.1 4.3575 4.-1570 99.5 0.0093 112.3
7 9650989 11/11/2019 1 l/lS/2019 3719.06 3863.33 8656.2 4.0 4.0 4.0 6.5 279.7 6222.5 1.08 0.94 33.31 8165.5 4.3763 4.5249 148.6 0.0182 85.9
8 9650980 11/18.120 19 11/25/2019 3863.33 4034.68 10281.0 4.0 4.0 4.0 4.7 277.8 618.01 LOS 0.94 33.3! 9697.1 4.3581 4.4334 75.3 0.0078 102.0
9 9650972 11/25/2019 12/2/2019 4034.68 4202.S IOOS7.2 4.0 4.0 4.0 -0.1 273.0 614.76 1.07 0.95 33.52 9573.4 4.3275 4.3920 64.5 0.0067 100.1
JO 9650964 12/2/2019 12/9/2019 4202.8 4371.1 10098.0 4.0 4.0 4.0 3.0 276.1 621 .0J I.OS 0.95 33.50 9577.6 " 4..3491 4.3877 38.6 0.0040 100.2
11 9650956 12/9/2019 12/16/2019 4371.1 4538.51 10044.6 4.0 4.0 4.0 0.6 273.8 61S.S7 1.07 0.95 33.58 955.2.0 -1.3702 4.4116 41.4 0.0043 99.6
12 9650948 12/1612019 12/23/2019 4538.51 -1701.73 9793.2 4.0 4,0 4.0 -2.I 271.1 623.82 1.06 0.96 33.89 9397.8 4.3608 4..4109 50.1 0.0053 97.2
13 9650940 1212.1/2019 12/30/2019 4701.73 4874.96 10393.8 3.5 4.0 3.8 -1.6 271.5 615.65 U)4 0.92 32.59 9590.6 4.3610 4.3979 36.9 0.0038 103.1
14 9650937 12/30/2019 1/6/2020 4874.96 5038.75 9827.4 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9455.9 4.3322 4_,745 42.3 0.0045 97.5
-~ C,: I .. . __ ::~-' -.. ••· .. • • -. Totals 141148.2 15.10 13.24 467.55 133462.2 61.762 63.216 1453.6 0.1538 ·--·,,t . ' ... )i.~· 4-....... l' . 'l. .. -•, ·,~· ~ . ...__ --_ .. !_-:.· l ... ,· ~ -. -Avero es 10082.0 4,0 4.0 4.0 4.1 277.2 619.7765 1.08 0.95 33.40 9533.0 4.412 4.515 103.8 0.0110 100.0
Comments:
Insert weekly flow cbeck values in yellow columns. I
-."~ -=:;-, ,-. • -, -~-r-w,;-•'7i::~~ ~ -Gre,eii .COIUIM;!·~ cal~uln~ i!,'~U'Om Ji,•IJ!l)I Slal!On,
;,:. f ~-~ ::,;._:.. ... ;.", .. Energy Fuels Resources -White Mesa Mill Calibration Date: 9/3/2019 First Monitoring Quarter 2014 r::r».~.8.\·l'I, Period: September 30, 2019-January 6, 2020 m= 1.26445 b= -0.02636 Updated: 7/30/14
(':'•-:·.: L\H L\H
Week Filter Stan Stop Stan Stop '· Starting Stopping
# Number Date Date Time Time Manometer Manometer
(in. H20) (in. H20) I
I 9429642 9/30/2019 lOn/2019 9514.59 9683.47 10132.8 4.0 4.0
2 9429633 10/7/2019 10/14/2019 9683.47 9851.4 10075.8 4.0 4.0 282.6 619.18 t.09 0.94 33.06 9431.1 4,5041 4.6663 162.2 0.0172 100.0
3 9429625 10/14/2019 10/21/2019 9851.4 10018.55 10029.0 4.5 4.0 4.3 10.8 284.0 618.26 1.13 0.96 33.94 9638.7 4.5325 4.6860 153.5 0.0159 99.5
4 9429617 10/21/2019 10/28/2019 10018.55 10186.26 10062.6 4.0 4.0 4.0 7.6 280.7 619.86 1.09 0.94 33.18 9455.3 4.5163 4.6310 l 14.7 0.0121 99.8
5 9429609 10/28/2019 ll/4/2019 10186.26 10357.74 10288.8 4.0 4.0 4.0 0.4 273.6 621.69 t.07 0.95 33..67 9810.4 4.5262 4.5327 6.5 0.0007 102.1
4 9429601 ll/4/2019 I 1/11/2019 10357.74 10546.63 11333.4 4.0 4.0 4.0 7.7 280.8 622.45 1.08 0.94 33.25 10670.5 4.5222 4 .. 6450 122.8 O.Oll5 112.4
7 9650988 tl/ll/2019 tl/18/2019 10546.63 10691.27 8678.4 4.0 4.0 4.0 6.5 279.7 622.25 1.08 0.94 33.31 8186.4 4.3821 4.4850 102.9 0.0126 86.1
8 9650979 ll/18/2019 ll/25/2019 10691.27 10862.55 10276.8 4.5 4.0 4.3 4.7 277.8 618.01 I.II 0.97 34.31 9985.7 4.3643 4.4120 47.7 0.0048 102.0
9 9650971 ll/25/2019 12/2/2019 10862.55 11030.68 10087.8 3.5 4.0 3.8 -0.1 273.0 614.76 1.04 0.92 32.47 9275.8 4.3581 4.4183 60.2 0.0065 100.1
IO 9650963 12/2/2019 12/9/2019 11030.68 11198.99 10098.6 4.0 4.0 4.0 3.0 276.l 621.01 t.08 0.95 33.50 9578.2 4.3715 4.4040 32.5 0.0034 100.2
11 9650955 12/9/2019 12/16/2019 III98.99 11366.37 10042.8 4.0 4.0 4.0 0.6 273.8 618.87 1.07 0.95 33.58 9550.3 4.3713 4.3942 22,9 0.0024 99.6
12 9650947 12/16/2019 12/23/2019 11366.37 11529.57 9792.0 4.0 4.0 4.0 -2.1 271.1 623.82 1.06 0.96 33.89 9396,7 4.3491 4.3690 19.9 0.0021 97.I
13 9650939 12/23/2019 12/30/2019 11529.57 11703.04 10408.2 3.0 4.0 3.5 -1.6 271.5 615.65 t.00 0.89 31.50 9284.8 4.3600 4.3755 15.5 0.0017 103.3
14 9650938 12/30/2019 1/6/2020 11703.04 l 1866.74 9822.0 4.0 4.0 4.0 -4.5 268.6 621.39 1.06 0.96 33.98 9450.7 4.3558 4.3702 14.4 0.0015 97.4
:-. ,:--. --... ·,· : .. ·.' .•. ~:.... .. Totals 141129.0 15.06 13.21 466.43 133118.4 62.041 63.054 1013.4 0.1070 . -, , .. ''' . '
1 '. :-: -• ·-• Averages 10080.6 4.0 4 0 4.0 4.1 277.2 619.7765 l.08 0.94 33.32 9508.5 4.431 4.504 72.4 0.0076 100.0
Comments: Lost the motor between 10/28/2019 and 11/412019. Motor was replaced on 1114/2019.
lnsen weekly flow check values in yellow columns. --~~---~ ~ ,._-'l _____ ...._-1..--:-; .... ~,.-~-;:--: .•
G.tam.colu~ ~~ed a,~ from the mer.'8~<!nl I
~.l..tiL.:._ H..:;._0 '~~•.,I.•:~....:-'.l!.J ..• -~•,,....,!.!__ ______ .,.
Blanks Period: September 30, 2019 -
Januarv 6 2020
Week Start Stop Net # Filter Number Date Date
1 9429634 30-Sep-19 07-0ct-19 4.5102
2 9429626 07-0ct-19 14-0ct-19 4.5234
3 9429618 14-0ct-19 21-0ct-19 4.5273
4 9429610 21-0ct-19 28-0ct-19 4.5261
5 9429602 28-0ct-19 04-Nov-19 4.5150
6 9650987 04-Nov-19 11-Nov-19 4.3692
7 9650986 11-Nov-19 18-Nov-19 4.3853
8 9650978 18-Nov-19 25-Nov-19 4.3688
9 9650970 25-Nov-19 02-Dec-19 4.3573
10 9650962 02-Dec-19 09-Dec-19 4.3823
11 9650954 09-Dec-19 16-Dec-19 4.3840
12 9650946 16-Dec-19 23-Dec-19 4.3507
13 9650931 23-Dec-19 30-Dec-19 4.3944
14 9650930 30-Dec-19 06-Jan-20 4.3857
Totals
ATTACHMENT E
ENVIRONMENT AL GAMMA GRAPHS AND SUPPORTING DATA
! White Mesa Mill Ambient Gamma Levels Over Time BHV-1 j
50.00 ~------------------------------------------------------,
45.00 -t--------------------------------------------------------------1
40.00 I
35.00 -t------------------------------------------------------------1
30.00
,._
Q)
t::: CCI 25.00 ::::::1 C" -E
Q) er: 20.00 E
15.00
10.00 L ----------------------------t ----------~~.-------1r--~-:--11
5.00 I a ll • II • 1 e I I :1L II I II ,../ I I-H--r-9--..Jll'I I -I
o.oo Iii iilli ; 7 • 11iii ¥ w, ,-.: I r= 4' .• 'I I ,.,. 14 I
9/3011981 9/3011984 9/301198? 9/3011990 9/3011993 9/3011998 9/3011999 9/3012002 9/3012005 9/3012008 9/3012011 9/3012014 9/301201., 9/3012020
Background (BHV-3) Subtracted from BHV-1
...,._Series1
!White Mesa Mill Ambient Gamma Levels Over Time BHV-2 j
50.00 ...... ---------------------------------------------------,
45.00 .i-----------------------------------------------------1
40.00 L-------------------------------------------------1
35.00 .i---------------------------------------------------------1
30.00 ... Q)
t
(lS ::::,
O" 25.00 -E
Q) a:
E 20.00
15.00 +--------------------------------------------------------1
10.00 r-----------i,-------------------------------------------J
5.oo I lF II 11• e -..a. l'I" -• I
0.00
30-SeP-87 30.seP-89 30.sep.97 30-seP-os 30.seP-13
Background (BHV-3) Subtracted from BHV-2
~BHV-2
I White Mesa Mill Ambient Gamma Levels Over Time BHV-3 j
60.00 ~-----------------------------------------------------------~
50.00 -11----------------------------------------•
40.00
'-Q)
t cu ::::I CT 30.00 --E
Q) a:
E
20.00
10.00 r ----------------------------------------------------------------_J
0.00 --~----------,-...... ---...------+---...._-...-...... ----;-----'--+--------...... --;----'--+-....... -------------'--I
30.seP-81 3o.seP-&t 30.seP-87 3o.seP-90
30.SeP-93 30-SeP-9(, 3D-seP-99 JO-seP-02 30-SeP-05 30-SeP-08
30.seP-11 30-seP-14 Jo-sep..17 30-SeP-20
-BHV-3
! White Mesa Mill Ambient Gamma Levels Over Time BHV-4 !
50.00 ------------------------------------------------,
45.00 +--------------------------------------------------1
40.00 --------------------------------------------------1
35.00 +--------------------------------------------------1
30.00 r---------------------------------------_J
'lo.. a, ~ 25.00 r-----------------------------------------------J
~ E a, i 20.00 r-----------~-------------------------------_J
15.00 --------------------------------------------------1
10.00 +----+1-----------------------------------------------;
s.oo ~ • 1 ..i..nr-~•rr.;.~-=---t,------tt----=---~------:::-----=----..--_JL __ .__J \ y I
0.00
3D-seP..81 30.Sep.85 30.Sep.89 30.sep..93 30.sep.97 30.Sep.07 30.Sep.05 3o.sep..09 30.sep..73 30.Sep.77
Background (BHV-3) Subtracted from BHV-4
--+-BHV-4
! White Mesa Mill Ambient Gamma Levels Over Time BHV-5 !
50.00 ..-------------------------------------------------.
45.00 -----------------------------------------------
4~00 I
35.00 +-------------------------------------------------;
30.00 ....
Q)
t:: m ::J
CT 25.00 -E
Q) a: E 20.00
15.00 r----------------------------------------J
10.00 I
5.00 I I I le &. !Jira rut. I~ -a I I ±I 1:.1.: II 'IP H IU\ ..... ,,., I I 'I" I
0.00 .. -~ -i.. . -. , . a 1
30--seP--81 3D-seP--85 30,seP-89 30-Sep.93
30-Sep.97 3o.sep.01 30.sep.05 3o.sep.09 30.Sep..13
3D--sep..77
Background (BHV-3) Subtracted from BHV-5
~BHV-5
! White Mesa Mill Ambient Gamma Levels Over Time BHV-6 !
50.00 -r-------------------------------------------------------------
45.00 r--------------------------------------------------------J
40.00 +-------------------------------------------------------------1
35.00 r--------------------------------------------_J
30.00
,._
Q)
t::: m 25.00 ::I O" ---E Q) a: 20.00
E
15.00
10.00 r ------------------------------------+1--------_J
5.00 +-------------------------------------------------t-t--w~-ai-----------i
o.oo I '~W)1
30-Sep-81 30-Sep..84 30-seP-8? 30-Sep..90 30-Sep..93 30-Sep-96 30-Sep..99 30-SeP-02 30-seP-os 30-seP-08 30..seP-11 30-Sep..74 30-SeP-1? 30-seP-20
Background (BHV-3) Subtracted from BHV-6
...,...__BHV-6
! White Mesa Mill Ambient Gamma Levels Over Time BHV-7 !
50.00
45.00
40.00
35.00
30.00
,_
Q)
t:::: m 25.00 ::::,
C" ..._
E Q) a: 20.00
E
15.00
10.00
"" __ )\ /\_ ~ ~ ---~ ·------.~ ------~ ~ -.... ... ..... .... ... -·---... -· ·-
5.00
0.00
1-Sep.74 1-/:eb.75 1-Ju/.75 1·Dee-75 1-May.76 1-0ct.75 1·"'1ar.77 1-Aug.77 1-Jan.78 1-Jun.78 1-fVoi,.18 1-Apr.79 1-Sep.79 1-/:eb-<o 1-Juixo
Background (BHV-3) Subtracted from BHV-7
-+-BHV-7
I White Mesa Mill Ambient Gamma Levels Over Time BHV-s j
50.00
45.00
40.00
35.00
30.00
,._
Q)
1:: ro 25.00 ::, er ..._
E
Q) a: 20.00
E
15.00
{\
-----J \_ -= ~~ --~---------.... ·------... _, ... ...... --·
10.00
5.00
0.00
1-seP-14 1-Feb-15 1-Jut-15 1-Dec.75 1-May.16 1-0ct-15 1-Mar-17 1-Aug.17 1-Jan.78 1-Jun.78 1-No,.,._,8 1-Ap,_19 1-seP-19 1-Feb-zo 1-Jut-zo
Background (BHV-3) Subtracted from BHV-8
-BHV-8
White Mesa Mill Third Quarter 2019 Environmental Spherical Gamma Monitor Results
Total Mean
Days Ambient
Badge Date Date Badge at Dose mRem/ mRem/ mRem/
Number Location Issued Returned WMM Equivalent hour Day Week
Control Administration Vault 7/8/2019 10/9/2019 93 7.9 0.00 0.085 0.59
1 V205 Control Room 7/8/2019 10/9/2019 93 8.4 0.00 0.090 0.63
2 BHV-6 7/8/2019 10/9/2019 93 35 0.02 0.376 2.63
3 Ore Stor. -Barrel Area 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
4 Vanadium Precip.Area 7/8/2019 10/9/2019 93 8.1 0.00 0.087 0.61
5 Yellowcake Drying Area 7/8/2019 10/9/2019 93 7.6 0.00 0.082 0.57
6 Leach 7/8/2019 10/9/2019 93 7.5 0.00 0.081 0.56
7 SAG Mill Control Room 7/8/2019 10/9/2019 93 7.8 0.00 0.084 0.59
8 Yellowcake Precip. 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
9 Central Control Room 7/8/2019 10/9/2019 93 7.5 0.00 0.081 0.56
10 re pad -decontamination p, 7/8/2019 10/9/2019 93 8.1 0.00 0.087 0.61
11 North East Corner Ore Pad 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
12 Met. Lab 7/8/2019 10/9/2019 93 7.5 0.00 0.081 0.56
13 Filter Press Room 7/8/2019 10/9/2019 93 7.6 0.00 0.082 0.57
14 BHV-1 7/8/2019 10/9/2019 93 39 0.02 0.419 2.94
15 BHV-2 7/8/2019 10/9/2019 93 36.5 0.02 0.392 2.75
16 BHV-3 7/8/2019 10/9/2019 93 33.9 0.02 0.365 2.55
17 BHV-4 7/8/2019 10/9/2019 93 32.5 0.01 0.349 2.45
18 BHV-5 7/8/2019 10/9/2019 93 37.6 0.02 0.404 2.83
19 SAG Mill 7/8/2019 10/9/2019 ,93 8 0.00 0.086 0.60
20 Tails 7/8/2019 10/9/2019 93 50.6 0.02 0.544 3.81
21 CCD 7/8/2019 10/9/2019 93 8.2 0.00 0.088 0.62
22 North SX 7/8/2019 10/9/2019 93 8.2 0.00 0.088 0.62
23 Administration Building 7/8/2019 10/9/2019 93 7.7 0.00 0.083 0.58
24 Admin Parking Lot 7/8/2019 10/9/2019 93 8.2 0.00 0.088 0.62
25 Yellowcake Packaging 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
26 Yellowcake Storage 7/8/2019 10/9/2019 93 7.7 0.00 0.083 0.58
27 Bucking Room 7/8/2019 10/9/2019 93 8.2 0.00 0.088 0.62
28 Mill Lunch Room 7/8/2019 10/9/2019 93 8.5 0.00 0.091 0.64
29 South SX 7/8/2019 10/9/2019 93 7.8 0.00 0.084 0.59
30 Mtce. Super.'s Office 7/8/2019 10/9/2019 93 7.6 0.00 0.082 0.57
31 Ore Feed Grizzly 7/8/2019 10/9/2019 93 7.9 0.00 0.085 0.59
32 Scalehouse 7/8/2019 10/9/2019 93 7.6 0.00 0.082 0.57
33 Sample Plant (OBS) 7/8/2019 10/9/2019 93 7.7 0.00 0.083 0.58
34 Front Gate 7/8/2019 10/9/2019 93 7.8 0.00 0.084 0.59
45 AF -Barrel Dump Station 7/8/2019 10/9/2019 93 8.1 0.00 0.087 0.61
46 AF Circuit -South 7/8/2019 10/9/2019 93 7.8 0.00 0.084 0.59
47 AF Circuit -North 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
51 North Control # 1 7/8/2019 10/9/2019 93 43.5 0.02 0.468 3.27
52 North Control # 2 7/8/2019 10/9/2019 93 36.5 0.02 0.392 2.75
CaF2 Barrel Dump
53 Station -Operator Station 7/8/2019 10/9/2019 93 8.1 0.00 0.087 0.61
64 KF Barrel Dump Station 7/8/2019 10/9/2019 93 8 0.00 0.086 0.60
70 BHV-7 7/8/2019 10/9/2019 93 35 0.02 0.376 2.63
71 BHV-8 7/8/2019 10/9/2019 93 34.1 0.02 0.367 2.57
White Mesa Mill Fourth Quarter 2019 Environmental Spherical Gamma Monitor Results
Mean
Total Days Ambient
Badge Date Badge at Dose mRem/ mRem/ mRem/
Number Location Date Issued Returned WMM Equivalent hour Day Week
Control Administration Vault 7/8/2019 1/8/2020 184 66.5 0.02 0.361 2.53
1 V205 Control Room 7/8/2019 1/8/2020 184 0.00 0.000 0.00
2 BHV-6 10/9/2019 1/8/2020 91 37.1 0.02 0.408 2.85
3 Ore Star. -Barrel Area 7/8/2019 1/8/2020 184 1398 0.32 7.598 53.18
4 Vanadium Precip.Area 7/8/2019 1/8/2020 184 121.7 0.03 0.661 4.63
5 Yellowcake Drying Area 7/8/2019 1/8/2020 184 734.3 0.17 3.991 27.94
6 Leach 7/8/2019 1/8/2020 184 201.7 0.05 1.096 7.67
7 SAG Mill Control Room 7/8/2019 1/8/2020 184 443 0.10 2.408 16.85
8 Yellowcake Precip. 7/8/2019 1/8/2020 184 1236.7 0.28 6.721 47.05
9 Central Control Room 7/8/2019 1/8/2020 184 210.1 0.05 1.142 7.99
10 Ore pad -decontamination pac 7/8/2019 1/8/2020 184 204.4 0.05 1.111 7.78
11 North East Corner Ore Pad 7/8/2019 1/8/2020 184 515.5 0.12 2.802 19.61
12 Met. Lab 7/8/2019 1/8/2020 184 268.1 0.06 1.457 10.20
13 Filter Press Room 7/8/2019 1/8/2020 184 275.4 0.06 1.497 10.48
14 BHV-1 10/9/2019 1/8/2020 91 45.3 0.02 0.498 3.48
15 BHV-2 10/9/2019 1/8/2020 91 37.9 0.02 0.416 2.92
16 BHV-3 10/9/2019 1/8/2020 91 35.4 0.02 0.389 2.72
17 BHV-4 10/9/2019 1/8/2020 91 34.2 0.02 0.376 2.63
18 BHV-5 10/9/2019 1/8/2020 91 36.9 0.02 0.405 2.84
19 SAG Mill 7/8/2019 1/8/2020 184 463.6 0.10 2.520 17.64
20 Tails 10/9/2019 1/8/2020 91 54.4 0.02 0.598 4.18
21 CCD 7/8/2019 1/8/2020 184 204.4 0.05 1.111 7.78
22 North SX 7/8/2019 1/8/2020 184 261.6 0.06 1.422 9.95
23 Administration Building 7/8/2019 1/8/2020 184 75.l 0.02 0.408 2.86
24 Admin Parking Lot 7/8/2019 1/8/2020 184 138.3 0.03 0.752 5.26
25 Yellowcake Packaging 7/8/2019 1/8/2020 184 486.9 0.11 2.646 18.52
26 Yellowcake Storage 7/8/2019 1/8/2020 184 1844.8 0.42 10.026 70.18
27 Bucking Room 7/8/2019 1/8/2020 184 357.7 0.08 1.944 13.61
28 Mill Lunch Room 7/8/2019 1/8/2020 184 104.3 0.02 0.567 3.97
29 South SX 7/8/2019 1/8/2020 184 170 0.04 0.924 6.47
30 Mtce. Super.'s Office 7/8/2019 1/8/2020 184 94.5 0.02 0.514 3.60
31 Ore Feed Grizzly 7/8/2019 1/8/2020 184 443.1 0.10 2.408 16.86
32 Scalehouse 7/8/2019 1/8/2020 184 427.1 0.10 2.321 16.25
33 Sample Plant (OBS) 7/8/2019 1/8/2020 184 403.6 0.09 2.193 15.35
34 Front Gate 7/8/2019 1/8/2020 184 330.4 0.07 1.796 12.57
45 AF -Barrel Dump Station 7/8/2019 1/8/2020 184 257.7 0.06 1.401 9.80
46 AF Circuit -South 7/9/2019 1/8/2020 183 195.1 0.04 1.066 7.46
47 AF Circuit -North 7/10/2019 1/8/2020 182 165.7 0.04 0.910 6.37
51 North Control# 1 10/9/2019 1/8/2020 91 45.3 0.02 0.498 3.48
52 North Control# 2 10/9/2019 1/8/2020 91 36.1 0.02 0.397 2.78
CaF2 Barrel Dump Station -
53 Operator Station 7/8/2019 1/8/2020 184 209.9 0.05 1.141 7.99
64 KF Barrel Dump Station 7/8/2019 1/8/2020 184 0.00 0.000 0.00
70 BHV-7 10/9/2019 1/8/2020 91 36.3 0.02 0.399 2.79
71 BHV-8 10/9/2019 1/8/2020 91 34.1 0.02 0.375 2.62
ATTACHMENT F
VEGETATION GRAPHS, DATA TABLE, LABORATORY RESULTS AND QA/QC
(Log Scale)
...... ...... ..... ...... ...... ...... ......
0 0 0 ·8 0 0 0 0 0 0 0 0 0 m m m m m m m
I I I 6 I I I 0 0 0 0 0 0
CX> ...... C1> c.n .j::,,. w I\)
8/27/1981
8/27/1982
8/27/1983
8/27/1984
8/27/1985
8/27/1986
8/27/1987
8/27/1988
8/27/1989
8/27/1990 :::c m
8/27/1991 I I\)
I\)
8/27/1992 0)
0 8/27/1993 0
8/27/1994 ::::s n (D
8/27/1995 ::::s -""' 8/27/1996 m -
t 8/27/1997 s·
::::s
8/27/1998 en
z ::::s m 8/27/1999 <
8/27/2000 (D
Ul ' (D
8/27/2001 -m -z 8/27/2002 s· :E ::::s 8/27/2003 -C t 8/27/2004 0 ::::.:
en 8/27/2005 " :E Ul
8/27/2006 -
8/27/2007
8/27/2008
8/27/2009
8/27/2010
8/27/2011
8/27/2012
8/27/2013
8/27/2014
8/27/2015
8/27/2016
8/27/2017
8/27/2018
8/27/2019 -
(Log Scale)
...... ...... ...... ...... ...... ...... ......
0 0 0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m m 6 I I 6 6 I I 0 0 0 0 0) ""-I 0) 0, ~ (,I) I\)
8/27/1981
8/27/1982
8/27/1983
8/27/1984
8/27/1985
8/27/1986
8/27/1987
8/27/1988
8/27/1989
8/27/1990 "'C C"
8/27/1991 I "' ......
8/27/1992 0
8/27/1993 C')
0
8/27/1994 ::::s n CD
8/27/1995 ::::s -..,
8/27/1996 D) -t 8/27/1997 er ::::s
8/27/1998 tn -z ::::s m 8/27/1999 <
8/27/2000 CD
' ca CD
8/27/2001 -D)
z -:E 8/27/2002 o·
8/27/2003 ::::s -t C
8/27/2004 C') :::.:
Ul 8/27/2005 " :E ca
8/27/2006 -
8/27/2007
8/27/2008
8/27/2009
8/27/2010
8/27/2011
8/27/2012
8/27/2013
8/27/2014
8/27/2015
8/27/2016
8/27/2017
8/27/2018
8/27/2019
{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 6 I I I I 0 0 0 0 0 0
CX) "' 0) 01 .j::,. (.,.) I\)
4/1/2015
6/1/2015
8/1/2015
10/1/2015
12/1/2015
2/1/2016
4/1/2016 . I -C I
6/1/2016 I I I I ll.. i<I ,, I I z ~ 8/1/2016 I I ~~ I I 0 0
101112016 I I I I / I "-""-...J I ::::J n (I)
121112016 I I I I '\. I \ I/ I ::::J -... m
2/1/2017 1 M -c>" t ::::J
4/1/2017 en
z ::::J m 6/1/2017 < (I)
' 8/1/2017
cg
(I) -m -z 10/1/2017 s· :E ::::J
12/1/2017 -C t 0
2/1/2018 :::::.:
(/) " :E cg
4/1/2018 -
6/1/2018
8/1/2018
10/1/2018
12/1/2018
2/1/2019
4/1/2019
6/1/2019
8/1/2019
10/1/2019
(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 6 I
0 0 0 0 0 0 CX) -...J 0) c.n """ w I\)
4/1/2015
6/1/2015
8/1/2015
10/1/2015
12/1/2015
2/1/2016
4/1/2016 I I I ""l I ..,------I I I -t
6/1/2016 I I I ..,..--I I I I :c I N w
8/1/2016 I I I A \ I I I I N
0
101112016 I I I I \ \ I I I I 0 ::::s
(")
CD
121112016 I I '\.\ I I I I I ::::s -"'I
~ Q) 2/1/2017 1 -er
f ::::s 4/1/2017 en
z ::::s
m 6/1/2017 < CD
8/1/2017 (C
' CD -Q)
10/1/2017 -z s· ~ ::::s
12/1/2017 -C
f 0
2/1/2018 === ;::,i;;
(/) (C ~ 4/1/2018 -
6/1/2018
8/1/2018
10/1/2018
12/1/2018
2/1/2019
4/1/2019
6/1/2019
8/1/2019
10/1/2019
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 3.90E-04
4th '81 20-0ct-81 l.40E-04
2nd '82 15-Apr-82 l.31E-04
3rd '82 Ol-Jul-82 l.60E-04
4th '82 30-Nov-82 2.67E-06
2nd '83 13-Apr-83 9.36E-05
3rd '83 Ol-Jul-83 l.12E-04
4th '83 30-Jan-84 l.09E-04
2nd '84 28-Jun-84 3.47E-04
4th '84 14-Nov-84 5.61E-04
2nd '85 27-Mar-85 l.OSE-03
3rd '85 15-Jul-85 8.20E-05
4th '85 09-0ct-85 l.lSE-04
2nd '86 24-Mar-86 5.72E-04
3rd '86 10-Jul-86 5.0IE-04
4th '86 18-Dec-86 8.70E-04
2nd '87 20-Apr-87 5.90E-04
3rd '87 05-Jun-87 l.60E-04
4th '87 22-Dec-87 2.IOE-04
2nd '88 19-Apr-88 4.SOE-04
3rd '88 28-Jul-88 3.20E-05
2nd '89 07-Apr-89 5.60E-04
3rd '89 06-Jun-89 J.50E-04
4th '89 07-Nov-89 6.00E-04
1st '90 17-Apr-90 2.60E-04
2nd '90 20-Jun-90 l.80E-04
3rd '90 17-0ct-90 l.60E-04
1st '91 10-ADr-91 1.20E-04
2nd '91 1 l-Jun-91 9.!0E-05
3rd '91 20-Nov-91 4.SOE-04
1st '92 22-Apr-92 3.60E-05
2nd '92 IO-Jun-92 l.OOE-05
3rd '92 IO-Jun-92 7.90E-05
1st '93 13-Apr-93 3.70E-05
2nd '93 26-Jun-93 3.00E-05
3rd '93 12-0ct-93 6.60E-05
1st '94 11-May-94 l.80E-04
2nd '94 19-Jul-94 J.71E-05
3rd '94 28-Nov-94 2.40E-04
1st '95 l 1-Apr-95 6.70E-05
2nd '95 06-Jul-95 J.SOE-05
3rd '95 15-Nov-95 5.50E-05
1st '96 23-Apr-96 5.20E-05
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96 3.00E-05
1st '97 21-Apr-97 l.lOE-05
3rd '97 05-Seo-97 l.lOE-05
4th '97 20-Nov-97 8.00E-06
1st '98 23-Mar-98 <9.lOE-05
2nd '98 16-Jun-98 1.80E-05
4th '98 05-Nov-98 5.70E-05
2nd '99 15-Apr-99 2.00E-04
3rd '99 07-Jul-99 6.03E-05
4th '99 02-Dec-99 2.30E-05
2nd '00 21-Apr-00 I.SOE-04
2nd '00 22-Jun-00 l.20E-06
4th '00 21-Dec-OO l.60E-06
1st '01 30-Apr-01 l.OOE-06
2nd '01 14-Jun-01 2.30E-06
4th '01 17-Dec-01 9.IOE-06
!st '02 07-May-02 3.30E-05
2nd '02 07-Jul-02 5.55E-05
4th '02 15-Dec-02 7.75E-05
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
J.OOE-05 5.00E-08
J.OOE-05 5.00E-08
l.30E-05 J.OOE-06
J.OOE-05 5.00E-08
J.07E-06 l.OOE-06
6.20E-06 8.00E-09
l.20E-05 6.00E-06
8.00E-06 4.00E-06
l.20E-05 2.00E-09
l.99E-04 2.00E-07
3.00E-05 2.00E-06
7.00E-06 3.00E-06
l.OOE-05 3.00E-06
2.IOE-05 4.00E-06
J.30E-05 3.00E-06
5.00E-05 3.00E-06
7.00E-05 5.00E-08
3.00E-05 5.00E-08
4.00E-05 5.00E-08
7.00E-05 5.00E-08
2.20E-05 5.00E-08
4.00E-05 ***
2.00E-05 ***
5.00E-05 7.00E-06
3.00E-05 4.00E-06
2.00E-05 5.00E-08
2.00E-05 5.00E-08
2.00E-05 5.00E-06
J.60E-05 2.00E-07
4.00E-05 5.00E-08
l.OOE-05 2.00E-06
7.00E-06 2.00E-07
3.SOE-05 3.00E-06
2.20E-05 3.00E-06
l.SOE-05 3.00E-06
2.70E-05 3.00E-06
4.00E-05 3.00E-05
l.20E-06 9.00E-08
I.SOE-OS l.70E-07
5.40E-06 l.60E-07
l.SOE-06 l.SOE-07
5.00E-06 l.80E-07
2.SOE-06 l.SOE-07
2.SOE-06 l.80E-07
4.70E-07 l.21E-07
4.30E-07 l.33E-07
l.20E-06 5.60E-07
9.JOE-05 9.lOE-05
l.20E-06 6.30E-08
l.OOE-06 8.20E-08
3.00E-06 l.20E-07
J.40E-06 8.30E-08
J.OOE-06 2.30E-07
3.00E-06 l.20E-07
1.00E-07 2.80E-07
l.lOE-06 3.70E-07
I.OOE-07 2.40E-07
2.00E-07 9.90E-08
2.40E-06 l.20E-07
l.80E-06 7.60E-07
2.81E-06 7.60E-07
3.60E-06 7.60E-07
Pb-210 Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
VALUE ERROR LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(uCi/Kg) (uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
l.lOE-03 I.OOE-04 I.OOE-06 NS NA NA NS NA NA
6.80E-04 8.00E-05 l.OOE-06 NS NA NA NS NA NA
4.90E-04 7.00E-05 8.00E-05 NS NA NA NS NA NA
8.00E-04 l.70E-04 l.OOE-07 NS NA NA NS NA NA
l.08E-04 9.00E-06 J.OOE-05 NS NA NA NS NA NA
4.97E-04 9.30E-05 !.OOE-04 NS NA NA NS NA NA
l.84E-04 l.20E-05 I.OOE-06 NS NA NA NS NA NA
7.80E-04 6.20E-05 6.00E-05 NS NA NA NS NA NA
3.75E-03 l.60E-04 4.00E-08 NS NA NA NS NA NA
7.82E-03 3.30E-04 7.00E-08 NS NA NA NS NA NA
3.22E-03 l.40E-04 2.00E-05 NS NA NA NS NA NA
7.70E-04 l.30E-04 2.00E-04 NS NA NA NS NA NA
5.IOE-04 3.00E-05 2.00E-05 NS NA NA NS NA NA
2.49E-03 1.00E-04 l.OOE-05 NS NA NA NS NA NA
l.57E-03 l.70E-03 2.00E-04 NS NA NA NS NA NA
6.80E-04 3.00E-05 3.00E-06 NS NA NA NS NA NA
l.SOE-03 J.OOE-04 !.OOE-06 NS NA NA NS NA NA
9.SOE-04 4.00E-05 !.OOE-06 NS NA NA NS NA NA
l.70E-03 l.OOE-04 l.OOE-06 NS NA NA NS NA NA
l.40E-03 l.OOE-04 l.OOE-06 NS NA NA NS NA NA
l.50E-04 4.40E-04 l.OOE-06 NS NA NA NS NA NA
l.lOE-03 J.OOE-01 *** NS NA NA NS NA NA
2.30E-04 2.00E-05 *** NS NA NA NS NA NA
2.04E-03 7.00E-05 l.40E-05 NS NA NA NS NA NA
3.30E-04 2.00E-05 2.20E-05 NS NA NA NS NA NA
3.20E-04 2.00E-05 l.OOE-06 NS NA NA NS NA NA
3.30E-04 2.00E-05 l.OOE-06 NS NA NA NS NA NA
3.00E-04 2.00E-05 J.OOE-06 NS NA NA NS NA NA
l.90E-04 2.00E-05 2.00E-07 NS NA NA NS NA NA
l.09E-03 5.00E-05 l.OOE-06 NS NA NA NS NA NA
l.SOE-04 2.00E-05 l.OOE-05 NS NA NA NS NA NA
7.SOE-05 2.00E-05 l.OOE-06 NS NA NA NS NA NA
7.IOE-04 7.00E-05 2.00E-05 NS NA NA NS NA NA
2.80E-04 3.00E-05 2.00E-05 NS NA NA NS NA NA
4.30E-05 3.SOE-05 2.00E-05 NS NA NA NS NA NA
5.30E-04 6.00E-05 2.00E-05 NS NA NA NS NA NA
4.40E-04 6.00E-05 2.00E-04 NS NA NA NS NA NA
3.00E-05 6.JOE-06 4.45E-06 NS NA NA NS NA NA
1.70E-04 l.lOE-05 8.30E-07 NS NA NA NS NA NA
l.40E-04 l.30E-05 7.90E-07 NS NA NA NS NA NA
5.IOE-05 4.SOE-06 7.60E-07 NS NA NA NS NA NA
6.70E-05 I.OOE-05 8.80E-07 NS NA NA NS NA NA
3.20E-05 4.SOE-06 l.80E-07 NS NA NA NS NA NA
NS NA NA NS NA NA
l.40E-04 7.IOE-06 9.30E-07 NS NA NA NS NA NA
4.IOE-05 3.60E-06 6.IOE-07 NS NA NA NS NA NA
2.IOE-05 7.30E-07 6.66E-07 NS NA NA NS NA NA
J.40E-04 4.60E-06 l.lOE-07 NS NA NA NS NA NA
<4.SOE-04 4.SOE-04 4.SOE-04 NS NA NA NS NA NA
4.00E-05 l.80E-06 3.20E-07 NS NA NA NS NA NA
8.70E-05 5.00E-06 4.lOE-07 NS NA NA NS NA NA
3.00E-04 l.OOE-05 6.00E-05 NS NA NA NS NA NA
l.40E-04 4.70E-06 4.20E-07 NS NA NA NS NA NA
2.lOE-05 I.OOE-06 l.lOE-06 NS NA NA NS NA NA
l.60E-04 8.00E-06 5.90E-07 NS NA NA NS NA NA
l.60E-04 l.OOE-05 l.40E-06 NS NA NA NS NA NA
5.lOE-05 5.00E-06 l.90E-06 NS NA NA NS NA NA
<1.2E-06 I.OOE-07 2.40E-07 NS NA NA NS NA NA
3.80E-06 2.00E-07 5.00E-07 NS NA NA NS NA NA
3.57E-05 2.97E-06 6.00E-07 NS NA NA NS NA NA
4.50E-05 2.61E-06 l.OOE-05 NS NA NA NS NA NA
5.31E-05 3.90E-06 l.OOE-05 NS NA NA NS NA NA
l.29E-04 6.JSE-06 !.OOE-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
Isl '03 21-Mar-03 9.lOE-06
2nd '03 10-Jun-03 2.SOE-05
4th '03 20-Nov-03 5.70E-05
1st '04 08-Apr-04 9.38E-05
2nd '04 12-Jun-04 5.63E-05
4th '04 30-Nov-04 8.4!E-05
!st '05 21-Apr-05 5.60E-05
2nd '05 !3-Jun-05 9.lOE-06
4th '05 !O-Nov-05 6.00E-05
!st '06 03-Apr-06 8.00E-05
2nd '06 16-Jun-06 4.lOE-05
4th '06 28-Nov-06 l.l?E-04
!st '07 30-Mar-07 9.70E-05
2nd '07 1-Jun-07 l.30E-05
4th '07 23-Nov-07 7.00E-05
1st '08 22-Apr-08 3.60E-06
2nd '08 18-Jun-08 3.20E-05
4th '08 12-Dec-08 l.SOE-04
1st '09 28-Aor-09 5.90E-04
2nd '09 17-Jun-09 l.90E-05
4th '09 18-Dec-09 l.?OE-04
1st 'IO 13-May-lO 2.20E-04
2nd '10 18-Jun-10 6.SOE-05
4th '10 20-Dec-IO 2.30E-05
2nd 'II 23-Jun-ll 2.40E-07
3rd 'I I 27-Jul-1 l 4.90E-06
4th '11 23-Nov-11 7.20E-06
2nd'l2 ll-Apr-12 4.40E-05
3rd '12 11-Jun-12 2.20E-05
4th '12 06-Nov-12 3.!0E-05
2nd '13 30-Apr-13 1.14E-04
3rd '13 20-Jun-13 8.91E-05
4th '13 14-Nov-13 1.37E-04
2nd '14 16-Apr-14 9.90E-05
3rd '14 10-Jun-14 2.60E-05
4th '14 25-Nov-14 2.98E-05
1st '15 21-Apr-15 7.15E-04
2nd '15 15-Jun-15 l.52E-04
4th '15 23-Nov-15 2.34E-04
2nd '16 14-Apr-16 4.08E-04
2nd '16 14-Jun-16 5.92E-05
4th '16 11-Nov-16 4.56E-05
2nd '17 13-Apr-17 1.71E-04
2nd '17 19-Jun-17 2.40E-05
4th '17 02-Nov-17 8.03E-05
2nd '18 26-Apr-18 9.48E-05
2nd '18 20-Jun-18 1.92E-04
4th '18 02-Nov-18 9.76E-05
2nd '19 25-Apr-19 8.0IE-05
2nd '19 06-Jun-19 4.20E-05
Ra-226 MDC¥ Pb-210 Pb-210
ERROR LLD uCi/Kg VALUE ERROR
(uCi/Kg) (5.0E-08) (uCi/Kg) (uCi/Kg)
J.30E-06 3.60E-07 1.13E-05 l.61E-06
1.30E-06 3.60E-07 3.26E-06 2.00E-06
3.50E-06 1.50E-07 4.0SE-05 5.82E-06
3.?0E-06 l.lOE-07 5.88E-05 3.00E-06
3.40E-06 1.80E-07 6.42E-05 5.90E-06
5.50E-06 2.00E-08 2.48E-04 J.40E-05
3.00E-06 J.40E-07 5.80E-05 4.00E-06
!.50E-06 l.80E-07 l.lOE-05 l.20E-05
3.00E-06 1.lOE-10 1.70E-06 6.40E-07
5.00E-06 5.00E-08 3.40E-04 l.20E-05
3.IOE-06 5.00E-08 1.16E-04 6.IOE-06
4.60E-06 l.90E-07 3.28E-04 9.50E-06
4.40E-06 l.90E-07 3.40E-04 8.70E-06
l.60E-06 l.90E-07 l.20E-04 6.60E-06
8.20E-06 2.00E-07 5.00E-04 2.00E-05
3.00E-06 5.20E-07 2.30E-04 l.40E-05
3.20E-06 l.80E-06 6.90E-05 3.50E-05
5.20E-06 9.90E-07 3.60E-04 2.90E-05
1.35E-05 !.50E-06 3.40E-04 1.30E-05
l .45E-06 4.90E-07 3.60E-05 l.lOE-05
5.90E-06 4.80E-04 l.20E-05
7.20E-06 1.IOE-06 l.90E-04 1.90E-05
3.40E-06 7.60E-07 1.40E-04 l.90E-05
l.70E-06 5.20E-07 1.00E-05 l.SOE-06
l.40E-07 l.80E-07 <2.9E-06 !.70E-06
6.30E-07 3.20E-07 9.50E-05 2.IOE-06
7.50E-07 2.90E-07 8.80E-08 4.30E-07
l.90E-06 3.60E-07 2.IOE-04 2.00E-06
8.40E-07 l.lOE-07 l.30E-04 7.60E-06
4.82E-07 4.63E-08 4.26E-04 3.72E-06
!.74E-06 5.34E-07 2.65E-04 4.41E-06
2.16E-06 !.42E-06 !.42E-04 3.68E-06
3.87E-06 4.71E-06 5.33E-04 l.45E-05
J.O!E-06 3.91E-07 l.99E-04 3.14E-06
8.46E-07 9.19E-07 5.60E-05 3.08E-06
1.23E-06 l.30E-06 2.46E-04 5.38E-06
8.0IE-06 3.SOE-06 5.85E-04 l.27E-05
3.48E-06 2.60E-06 4.49E-04 1.SOE-05
5.79E-06 3.89E-06 9.34E-04 l.36E-05
7.26E-06 5.42E-06 l.34E-03 2.16E-05
2.?0E-06 4.00E-06 2.61E-04 2.09E-05
2.IOE-06 3.47E-06 2.?0E-04 l.43E-05
(5.00E-08)
4.59E-06 4.06E-06 6.1 IE-04 l.34E-05
(5.00E-08)
9.69E-07 1.15E-06 7.52E-06 J.72E-06
(5.00E-08)
2.I8E-06 2.31E-06 6.13E-04 l. IOE-05
(5.00E-08)
l.83E-06 l.16E-06 4.53E-04 9.39E-06
(5.00E-08)
4.37E-06 3.52E-06 4.65E-04 l.19E-05
(5.00E-08)
2.96E-06 3.23E-06 4.52E-04 l.04E-05
(5.00E-08)
5.67E-06 3.69E-06 l.07E-04 l.74E-05
(5.00E-08)
1.64E-06 l.36E-06 5.87E-04 3.12E-05
(5.00E-08)
MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(l.OE-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
3.36E-06 NS NA NA NS NA NA
7.38E-08 NS NA NA NS NA NA
8.30E-07 NS NA NA NS NA NA
5.SOE-07 NS NA NA NS NA NA
9.00E-07 NS NA NA NS NA NA
3.00E-07 NS NA NA NS NA NA
6.90E-07 NS NA NA NS NA NA
9.00E-07 NS NA NA NS NA NA
5.50E-10 NS NA NA NS NA NA
I.OOE-06 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
9.SOE-07 NS NA NA NS NA NA
8.4-07 NS NA NA NS NA NA
9.70E-07 NS NA NA NS NA NA
1.20E-06 NS NA NA NS NA NA
!.OOE-06 NS NA NA NS NA NA
5.50E-05 NS NA NA NS NA NA
3.90E-05 NS NA NA NS NA NA
!.SOE-06 NS NA NA NS NA NA
l.80E-05 NS NA NA NS NA NA
NS NA NA NS NA NA
2.90E-05 NS NA NA NS NA NA
2.90E-05 NS NA NA NS NA NA
2.30E-06 NS NA NA NS NA NA
2.90E-06 NS NA NA NS NA NA
2.SOE-06 NS NA NA NS NA NA
7.20E-07 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
5.90E-06 NS NA NA NS NA NA
6.52E-07 NS NA NA NS NA NA
5.37E-06 NS NA NA NS NA NA
6.17E-06 NS NA NA NS NA NA
2.27E-05 NS NA NA NS NA NA
3.38E-06 NS NA NA NS NA NA
7.12E-06 NS NA NA NS NA NA
7.41E-06 NS NA NA NS NA NA
2.SIE-05 6.36E-04 2.70E-05 8.62E-06 l.OIE-04 3.06E-06 4.04E-07
3.33E-05 3.1 IE-04 1.58E-05 6.45E-06 4.19E-05 2.67E-06 6.78E-07
l.37E-05 2.73E-04 l.91E-05 6.31E-06 6.67E-06 7.98E-07 7.06E-07
2.93E-05 !.69E-04 l.29E-05 5.76E-06 !.66E-05 J.28E-06 7.67E-07
4.92E-05 2.IOE-04 5.52E-06 !.70E-06 4.27E-06 8.IOE-07 9.31E-07
3.81E-05 3.94E-05 5.94E-06 5.02E-06 2.IOE-06 5.45E-07 5.66E-07
(l.OOE-06) (2.00E-07) (2.00E-07)
2.l?E-05 2.38E-04 5.7 IE-06 2.31E-06 l.54E-05 l.59E-06 2.09E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
5.42E-06 l.31E-04 4.21E-06 l.15E-06 7.18E-06 1.09E-06 6.48E-07
(J.OOE-06) (2.00E-07) (2.00E-07)
l.58E-05 1.15E-04 3.99E-06 l.74E-06 1.04E-05 l.02E-06 J.05E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
l.57E-05 3.15E-04 6.25E-06 l.87E-06 3.36E-06 1.41E-06 2.88E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
2.37E-05 2.97E-04 6.57E-06 l.85E-06 !.92E-05 l.58E-06 l.22E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
1.78E-05 7.34E-04 l.64E-05 3.49E-06 6.44E-06 8.0!E-07 l.90E-06
(I.OOE-06) (2.00E-07) (2.00E-07)
4.50E-05 l.79E-04 7.85E-06 5.53E-06 l.08E-05 1.28E-06 1.68E-06
(I.OOE-06) (2.00E-07) (2.00E-07)
4.47E-05 2.29E-04 l.64E-05 2.48E-06 2.43E-05 l.89E-06 l.96E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
4th 2019 13-Nov-19 4.91E-04
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
4.77E-06 J.73E-06
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLDuCVKg VALUE ERROR
(uCVKg) (uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg)
8.60E-04 l.SIE-05 2.4JE-05 l.66E-04 4.JOE-06
(l.OOE-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected during this penod
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
l.19E-06 1.0IE-05
(2.00E-07)
t NRC Regulatory Guide does not specify a Lower Limit of Detection (LLD) for Thorium 232 in vegetation (or any matrix). The LLD for Thorium 230 was used.
NS = Not Sampled
NA= Not Applicable
Th-232 MDC¥
ERROR LLD
(uCi/Kg) uCi/Kg
(2.0E-07)t
I.24E-06 l.68E-06
(2.00E-07)
¥ The value in the MDC column is the sample-specific minimum detectable concentration. The MDC is based on the sample moisture, composition and other sample-specific variables. The
value in parantheses is the method-specific lower limit of detection (LLD), which is a limit representing the detection capability of the measurement system. The LLDs in the data package are
referred to as the Reporting limit (RL) .
•
(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 6 I I 0 0 0 0 0 0 ex, --.J C1l C11 ~ w I\)
01-Aug-81 :e 01-Jul-82 ::I:
01-Jun-83 =i
01-May-84 m
s: 01-Apr-85 -m
01-Mar-86 en )>
01-Feb-87 s:
01-Jan-88 -r
01-Dec-88 r
I
01-Nov-89 z
01-0ct-90 0 lJ
01-Sep-91 -f
t ::I:
01-Aug-92 m )>
JJ 01-Jul-93 en Ill -f I\) 01-Jun-94 I\) 0 0)
01-May-95 'Tl
' 01-Apr-96 s:
01-Mar-97 r
lJ r CT I\J 01-Feb-98 lJ ~ D> 0 01-Jan-99 C.
t 01-Dec-99 er :::,
01-Nov-OO C
C n z 01-0ct-01 C: )> -t 01-Sep-02 CD
0 t 01-Aug-03 0 :::,
01-Jul-04 n -t CD I 01-Jun-05 :::, I\J -ul 01-May-06
..,
I\) D> -01-Apr-07 o· :::, 01-Mar-08 tn
01-Feb-09 :::,
01-Jan-10 < CD
01 -Dec-10 ca CD -01-Nov-11 D> -01-0ct-12 o· :::,
01-Sep-13 -C 01-Aug-14 0
01-Jul-15 -::::::: " 01-Jun-16 ca -01-May-17 -
01-Apr-18
01-Mar-19
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 2.73E-03
4th '81 20-0ct-81 2.00E-04
2nd '82 15-Apr-82 l.04E-04
3rd '82 OJ-Jul-82 2.00E-05
4th '82 30-Nov-82 2.36E-06
2nd '83 13-Apr-83 8.58E-05
3rd '83 Ol-Jul-83 1.19E-04
4th '83 30-Jan-84 9.78E-05
2nd '84 28-Jun-84 2.08E-04
4th '84 14-Nov-84 6.05E-04
2nd '85 27-Mar-85 l.lOE-04
3rd '85 15-Jul-85 6.IOE-05
4th '85 09-0ct-85 l.07E-04
2nd '86 24-Mar-86 8.86E-04
3rd '86 IO-Jul-86 6.66E-04
4th '86 18-Dec-86 5.20E-04
2nd '87 20-Apr-87 4.JOE-04
3rd '87 05-Jun-87 l.60E-04
4th '87 22-Dec-87 3.60E-04
2nd '88 19-Apr-88 2.60E-04
3rd '88 28-Jul-88 3.IOE-05
2nd '89 07-Apr-89 6.20E-04
3rd '89 06-Jun-89 3.40E-04
4th '89 07-Nov-89 5.IOE-04
!st '90 17-Apr-90 3.60E-04
2nd '90 20-Jun-90 l.70E-04
3rd '90 17-0ct-90 8.80E-05
1st '91 10-Apr-91 3.00E-04
2nd '91 ll-Jun-91 3.IOE-04
3rd '91 20-Nov-91 5.00E-04
1st '92 22-Apr-92 2.00E-05
2nd '92 IO-Jun-92 6.50E-06
3rd '92 IO-Jun-92 l.20E-04
!st '93 13-Apr-93 l.80E-05
2nd '93 26-Jun-93 5.20E-05
3rd '93 12-0ct-93 5.IOE-05
1st '94 ll-May-94 l.20E-04
2nd '94 !9-Jul-94 3.73E-05
3rd '94 28-Nov-94 2.40E-04
1st '95 ll-Apr-95 8.40E-05
2nd '95 06-Jul-95 l.90E-05
3rd '95 15-Nov-95 l.20E-04
!st '96 23-Apr-96 8.30E-05
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96 3.60E-05
!st '97 21-Apr-97 3.30E-05
3rd '97 05-Sep-97 5.40E-06
4th '97 20-Nov-97 8.90E-06
1st '98 23-Mar-98 <9.20E-05
2nd '98 16-Jun-98 < 6.50E-08
4th '98 05-Nov-98 4.20E-05
2nd '99 15-Apr-99 6.20E-05
3rd '99 07-Jul-99 5.45E-05
4th '99 02-Dec-99 I.IOE-04
2nd '00 21-Apr-00 3.70E-05
2nd'OO 22-Jun-OO 2.90E-05
4th '00 21-Dec-OO 2.30E-06
1st '01 30-Apr-01 2.IOE-05
2nd '01 14-Jun-01 l.30E-06
4th '01 17-Dec-01 3.70E-05
!st '02 07-May-02 4.90E-05
2nd '02 07-Jul-02 8.88E-05
Ra-226 MDC¥ Pb-210
ERROR LLD uCi/Kg VALUE
(uCi/Kg) (S.OE-08) (uCi/Kg)
5.00E-05 5.00E-08 7.IOE-03
l.OOE-05 5.00E-08 8.30E-04
9.00E-06 7.00E-06 6.40E-04
1.00E-05 5.00E-08 2.20E-04
9.50E-07 I.OOE-06 8.00E-05
l.36E-05 2.00E-08 3.53E-04
1.IOE-05 5.00E-06 l.58E-04
7.00E-06 2.00E-06 2.16E-03
l.OOE-05 3.00E-09 l.60E-03
l.64E-04 2.00E-07 2.58E-03
8.00E-06 3.00E-06 8.63E-04
6.00E-06 2.00E-06 5.40E-04
6.00E-06 2.00E-06 3.80E-04
l.80E-05 2.00E-06 4.40E-03
l.80E-05 3.00E-06 4.78E-03
I.OOE-04 3.00E-06 1.70E-03
I.OOE-04 5.00E-08 l.60E-03
3.00E-05 5.00E-08 5.50E-04
5.00E-05 5.00E-08 l.80E-03
5.00E-05 5.00E-08 l.90E-03
l.90E-05 5.00E-08 l.60E-04
5.00E-05 *** l.70E-03
3.00E-05 *** 7.40E-04
6.00E-05 7.00E-06 l.OOE-03
3.00E-05 4.00E-06 4.80E-04
2.00E-05 5.00E-08 3.20E-04
l.60E-05 5.00E-08 2.90E-04
3.00E-05 5.00E-06 4.IOE-04
3.00E-05 2.00E-07 4.70E-04
4.00E-05 5.00E-08 1.50E-03
8.00E-06 2.00E-06 9.60E-05
6.00E-06 2.00E-06 l.20E-04
4.00E-05 3.00E-06 l.21E-03
1.70E-05 3.00E-06 2.IOE-04
l.90E-05 3.00E-06 1.70E-05
2.30E-05 3.00E-06 7.IOE-04
l.OOE-05 3.00E-05 9.80E-04
l.60E-06 8.40E-08 7.80E-05
l.50E-05 l.70E-07 2.60E-04
6.IOE-06 l.50E-07 l.20E-04
l.SOE-06 l.40E-07 4.50E-05
6.80E-06 1.40E-07 l.OOE-05
3.30E-06 1.90E-07 6.80E-05
2.50E-06 l.60E-07 8.50E-05
2.306-06 l.70E-07 4.40E-05
3.50E-07 l.56E-07 3.20E-05
7.20E-07 5.40E-07 3.40E-04
9.20E-05 9.20E-05 <4.60E-04
6.50E-08 6.50E-08 <3.20E-07
l.OOE-06 l.lOE-07 l.70E-04
l.OOE-06 I.OOE-07 l.40E-04
l.40E-06 8.30E-08 9.20E-05
3.00E-06 2.206-07 2.80E-05
l.OOE-06 2.40E-07 2.70E-04
l.OOE-06 3.30E-07 2.80E-04
l.40E-06 3.70E-07 3.30E-04
l.OOE-06 l.50E-07 <7.6E-07
4.00E-08 l.20E-07 l.80E-06
7.67E-07 8.30E-08 6.72E-05
2.40E-06 7.60E-07 l.28E-04
4.32E-06 7.60E-07 8.33E-05
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR LLDuCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
3.00E-04 I.OOE-06 NS NA NA NS NA NA
5.00E-05 l.OOE-06 NS NA NA NS NA NA
5.00E-05 4.00E-05 NS NA NA NS NA NA
9.00E-05 l.OOE-07 NS NA NA NS NA NA
I.OOE-05 I.OOE-05 NS NA NA NS NA NA
l.90E-05 1.00E-05 NS NA NA NS NA NA
l.30E-05 l.OOE-05 NS NA NA NS NA NA
3.40E-04 3.00E-04 NS NA NA NS NA NA
7.00E-05 3.00E-08 NS NA NA NS NA NA
l.lOE-04 3.00E-08 NS NA NA NS NA NA
4.20E-05 3.00E-05 NS NA NA NS NA NA
5.00E-05 5.00E-05 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
l.90E-04 3.00E-05 NS NA NA NS NA NA
2.IOE-04 6.00E-05 NS NA NA NS NA NA
I.OOE-04 6.00E-05 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
4.00E-05 1.00E-06 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
4.00E-05 l.OOE-06 NS NA NA NS NA NA
1.00E-04 *** NS NA NA NS NA NA
3.00E-05 *** NS NA NA NS NA NA
7.00E-05 1.40E-05 NS NA NA NS NA NA
2.00E-05 2.20E-05 NS NA NA NS NA NA
2.00E-05 l.OOE-06 NS NA NA NS NA NA
2.00E-05 I.OOE-06 NS NA NA NS NA NA
2.00E-05 1.00E-06 NS NA NA NS NA NA
2.00E-05 2.00E-07 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
l.40E-05 l.OOE-05 NS NA NA NS NA NA
2.00E-05 1.00E-06 NS NA NA NS NA NA
8.00E-05 2.00E-05 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
3.60E-05 2.00E-05 NS NA NA NS NA NA
6.00E-05 2.00E-05 NS NA NA NS NA NA
l.60E-04 2.00E-04 NS NA NA NS NA NA
7.IOE-06 4.20E-07 NS NA NA NS NA NA
l.30E-05 8.30E-07 NS NA NA NS NA NA
I.IOE-05 7.50E-05 NS NA NA NS NA NA
4.30E-06 7.20E-07 NS NA NA NS NA NA
5.80E-06 7.IOE-07 NS NA NA NS NA NA
6.30E-06 l.80E-07 NS NA NA NS NA NA
NS NA NA NS NA NA
5.60E-06 8.40E-07 NS NA NA NS NA NA
4.80E-06 8.40E-07 NS NA NA NS NA NA
9.00E-07 7.83E-07 NS NA NA NS NA NA
6.70E-06 l.lOE-07 NS NA NA NS NA NA
4.60E-04 4.60E-04 NS NA NA NS NA NA
3.20E-07 3.20E-07 NS NA NA NS NA NA
l.OOE-05 5.50E-07 NS NA NA NS NA NA
7.00E-06 l.OOE-07 NS NA NA NS NA NA
4.00E-06 4.20E-07 NS NA NA NS NA NA
1.00E-06 l.lOE-06 NS NA NA NS NA NA
l.OOE-05 1.20E-06 NS NA NA NS NA NA
2.00E-05 l.70E-06 NS NA NA NS NA NA
5.00E-05 l.90E-06 NS NA NA NS NA NA
NIA 7.606-07 NS NA NA NS NA NA
3.00E-08 5.90E-07 NS NA NA NS NA NA
2.62E-06 6.00E-07 NS NA NA NS NA NA
5.61E-06 I.OOE-05 NS NA NA NS NA NA
4.32E-06 I.OOE-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
4th '02 15-Dec-02 l.50E-04
Isl '03 21-Mar-03 5.00E-05
2nd '03 IO-Jun-03 5.60E-05
4th '03 20-Nov-03 3.20E-04
Isl '04 08-Aor-04 6.29E-05
2nd '04 12-Jun-04 6.51E-05
4th '04 30-Nov-04 7.50E-05
1st '05 21-Apr-05 4.90E-05
2nd '05 13-Jun-05 2.30E-05
4th '05 10-Nov-05 7.40E-05
1st '06 03-Apr-06 l.OOE-04
2nd '06 16-Jun-06 9.50E-05
4th '06 28-Nov-06 8.13E-05
Isl '07 30-Mar-07 4.30E-05
2nd '07 l-Jun-07 5.lOE-05
4th '07 23-Nov-07 7.30E-05
!st '08 22-Apr-08 2.80E-06
2nd '08 18-Jun-08 3.20E-06
4th '08 12-Dec-08 7.30E-05
1st '09 28-Apr-09 5.25E-05
2nd '09 l 7-Jun-09 2.30E-05
4th '09 18-Dec-09 5.50E-05
1st '10 13-Mav-10 l.90E-04
2nd '10 18-Jun-JO 2.30E-05
4th '10 20-Dec-LO 8.60E-06
2nd '11 23-Jun-ll 2.lOE-07
3rd '11 28-Jul-l l 4.20E-06
4th 'II 23-Nov-1 I 7.70E-06
2nd '12 ll-Apr-12 l.50E-05
3rd '12 ll-Jun-12 8.30E-06
4th '12 06-Nov-12 2.34E-05
2nd'l3 30-Apr-13 9.04E-05
3rd '13 20-Jun-13 2.58E-06
4th '13 14-Nov-13 l.43E-04
2nd '14 16-Apr-14 2.53E-05
3rd '14 JO-Jun-14 2.53E-05
4th '14 25-Nov-14 7.41E-05
1st '15 21-Apr-15 l.31E-04
2nd '15 15-Jun-15 2.39E-04
4th '15 23-Nov-15 l.03E-04
2nd '16 14-Apr-16 l.28E-04
2nd '16 14-Jun-16 5.91E-05
4th '16 l l-Nov-16 2.66E-04
2nd '17 13-Apr-17 3.84E-05
2nd '17 19-Jun-17 l.56E-04
4th '17 02-Nov-17 2.24E-04
2nd '18 26-Apr-18 2.63E-04
2nd '18 20-Jun-18 2.13E-04
4th '18 02-Nov-18 l.7 IE-04
2nd '19 25-Apr-19 4.15E-05
2nd '19 06-Jun-19 1.12E-05
Ra-226 MDC¥ Pb-210 Pb-210
ERROR LLD uCi/Kg VALUE ERROR
(uCi/Kg) (5.0E-08) (uCi/Kg) (uCi/Kg)
6.20E-06 7.60E-07 3.16E-04 l.07E-05
3.40E-06 2.71E-06 <4.2e-6
2.00E-06 4.lOE-07 J.88E-04 5.14E-06
8.20E-06 l.70E-07 4.89E-04 l .25E-05
4.JOE-06 2.00E-07 l.94E-05 4.00E-06
3.40E-06 l.30E-07 1.87E-05 3.90E-06
4.60E-06 2.00E-08 4.45E-04 l.40E-05
2.70E-06 l.30E-07 l.27E-04 4.80E-06
2.lOE-06 l.50E-07 4.70E-05 5. IOE-06
3.50E-06 l.20E-JO 2.40E-06 8.IOE-08
6.00E-06 5.00E-08 6.54E-04 1.50E-05
5.90E-06 5.00E-08 4.48E-04 l.40E-05
4.lOE-06 2.20E-07 3.25E-04 l.12E-06
2.60E-06 1.70E-07 2.64E-04 7.20E-06
3.20E-06 2.30E-07 5.30E-04 l.40E-06
6.60E-06 5.00E-08 7.00E-04 2.20E-05
2.SOE-06 7.20E-07 4.40E-04 2.00E-05
3.30E-06 l.SOE-06 l.40E-04 3.30E-05
3.20E-06 7.40E-07 4.40E-04 2.50E-05
3.60E-06 1.lOE-06 l.90E-04 l.50E-05
l.60E-05 5.20E-07 4.30E-05 l.OOE-05
3.50E-06 3.00E-04 I.IOE-05
6.lOE-06 9.40E-07 5.IOE-04 2.40E-05
2.00E-06 7.70E-07 8.30E-05 l.80E-05
9.IOE-07 3.90E-07 l.lOE-07 6.80E-07
l.20E-07 l.40E-07 <2.2E-06 l.30E-06
5.40E-07 2.70E-07 2.30E-04 2.50E-06
6.SOE-07 2.30E-07 <5.8E-08 3.40E-07
9.50E-07 2.60E-07 <7.0E-07 6.00E-07
5.40E-07 l.20E-07 l.40E-04 8.30E-06
4.lOE-07 7.71E-08 4.59E-04 3.83E-06
l.68E-06 8.58E-07 2.24E-04 4.46E-06
9.59E-07 8.06E-07 l.06E-04 2.30E-06
3.70E-06 2.17E-06 4.65E-04 l.17E-05
6.29E-07 5.51E-07 5.70E-05 2.21E-06
5.55E-07 5.77E-07 7.68E-05 2.0SE-06
l.90E-06 l.53E-06 2.98E-04 6.48E-06
4.21E-06 5.92E-06 6.33E-04 l.17E-05
4.43E-06 3.45E-06 l.08E-03 2.02E-05
3.95E-06 4.25E-06 4.78E-04 l.06E-05
4.20E-06 5.79E-06 3.56E-04 1.14E-05
3.97E-06 6.94E-06 1.73E-04 2.02E-05
4.22E-06 2.03E-06 l.28E-03 2.57E-05
(5.00E-08)
2.55E-06 4.35E-06 8.85E-04 l.5 LE-05
(5.00E-08)
l.77E-06 8.68E-07 1.15E-04 3.18E-06
(5.00E-08)
4.17E-06 2.0IE-06 9.23E-04 l.34E-05
(5.00E-08)
2.93E-06 7.38E-7 5.85E-04 9.12E-06
(5.00E-08)
4.85E-06 3.93E-06 6.02E-04 l.28E-05
(5.00E-08)
3.84E-06 3.48E-06 5.54E-04 l.06E-05
(5.00E-08)
4.50E-06 6.02E-06 3.18E-04 2.29E-05
(5.00E-08)
l.08E-06 1.79E-06 l.41E-04 !.72E-05
(5.00E-08)
MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(l.OE-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
l.OOE-05 NS NA NA NS NA NA
4.20E-06 NS NA NA NS NA NA
8.20E-08 NS NA NA NS NA NA
8.30E-07 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
6.50E-07 NS NA NA NS NA NA
3.00E-07 NS NA NA NS NA NA
6.50E-07 NS NA NA NS NA NA
7.60E-07 NS NA NA NS NA NA
5.80E-10 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
1.00E-06 NS NA NA NS NA NA
l.OOE-05 NS NA NA NS NA NA
8.60E-07 NS NA NA NS NA NA
l.20E-06 NS NA NA NS NA NA
l.lOE-06 NS NA NA NS NA NA
l .OOE-06 NS NA NA NS NA NA
5.50E-05 NS NA NA NS NA NA
3.20E-05 NS NA NA NS NA NA
2.20E-05 NS NA NA NS NA NA
l.70E-05 NS NA NA NS NA NA
NS NA NA NS NA NA
3.lOE-05 NS NA NA NS NA NA
2.90E-05 NS NA NA NS NA NA
l.lOE-06 NS NA NA NS NA NA
2.20E-06 NS NA NA NS NA NA
2.30E-06 NS NA NA NS NA NA
5.80E-07 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
6.50E-06 NS NA NA NS NA NA
6.ISE-07 NS NA NA NS NA NA
4.68E-06 NS NA NA NS NA NA
3.28E-06 NS NA NA NS NA NA
l.80E-05 NS NA NA NS NA NA
4.52E-06 NS NA NA NS NA NA
3.66E-06 NS NA NA NS NA NA
l.06E-05 NS NA NA NS NA NA
l.45E-05 3.35E-04 2.41E-05 1.17E-05 7.35E-06 8.57E-07 7.82E-07
3.25E-05 5.24E-04 2.41E-05 9.70E-06 2.38E-05 2.12E-06 7.36E-07
l.75E-05 l.51E-04 l.53E-05 7.71E-06 2.30E-05 l.53E-06 4.23E-07
l.86E-05 6.33E-05 8.20E-06 5.95E-06 l.66E-06 4.81E-07 5.40E-07
5.42E-05 3.15E-05 l.90E-06 l.54E-06 2.95E-06 8.26E-07 l.47E-06
4.95E-05 4.33E-04 2.58E-05 8.24E-06 3.87E-06 7.58E-07 1.03E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
2.23E-05 6.97E-04 l.21E-05 3.52E-06 6.IIE-06 9.91E-07 1.15E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
6.0?E-06 3.29E-04 6.61E-06 l.44E-06 l.58E-05 l.37E-06 5.35E-07
(l.OOE-06) (2.00E-07) (2.00E-07)
1.94E-05 3.34E-04 9.09E-06 3.50E-06 l.52E-05 l.35E-06 l.80E-07
(1.00E-06) (2.00E-07) (2.00E-07)
8.17E-6 4.60E-04 7.74E-06 l.56E-06 5.49E-06 2.15E-06 3.47E-6
(l.OOE-06) (2.00E-07) (2.00E-07)
2.33E-05 4.98E-04 9.07E-06 2.43E-06 9.46E-06 l.05E-06 l.07E-6
(l.OOE-06) (2.00E-07) (2.00E-07)
l.55E-05 5.25E-04 l.63E-05 4.23E-06 4. l 7E-07 7.48E-07 l.45E-6
(l.OOE-06) (2.00E-07) (2.00E-07)
3.18E-05 l.55E-04 5.l7E-06 2.42E-06 3.0SE-05 2.51E-06 3.89E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
3.49E-05 4.41E-05 3.41 E-06 2.39E-06 l.65E-05 6.68E-06 l.24E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
4th '19 13-Nov-19 6.09E-04
Ra-226 MDC¥
ERROR LLD uCi/Kg
(uCi/Kg) (5.0E-08)
6.16E-06 2.42E-06
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLD uCi/Kg VALUE ERROR
(uCi/Kg) (uCi/Kg) (1.0E-06) (uCi/Kg) (uCi/Kg)
l.31E-03 l.82E-05 2.46E-05 3.63E-04 6.29E-06
(l.OOE-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected during this period
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
1.43E-06 7.34E-06
(2.00E-07)
t NRC Regulatory Guide does not specify a Lower Limit of Detection (LLD) for Thorium 232 in vegetation (or any matrix). The LLD for Thorium 230 was used.
NS = Not Sampled
NA= Not Applicable
Th-232 MDC¥
ERROR LLD
(uCi/Kg) uCi/Kg
(2.0E-07)t
l.18E-06 2.05E-06
(2.00E-07)
¥ The value in the MDC column is the sample-specific minimum detectable concentration. The MDC is based on the sample moisture, composition and other sample-specific variables. The
value in parantheses is the method-specific lower limit of detection (LLD), which is a limit representing the detection capability of the measurement system. The LLDs in the data package are
referred to as the Reporting limit (RL).
(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 ...... 0) 01 .i:,. c.v I\)
01-Aug-81 :e :::c 01-Jul-82 =i
01-Jun-83 m
01-May-84 3: m
01-Apr-85 en )>
01-Mar-86 3: 01-Feb-87 F
01-Jan-88 r-
01 -Dec-88 z
01-Nov-89 0 lJ
01-0ct-90 -I
t 01-Sep-91 :::c :e
01-Aug-92 m JJ en 'l' I\) 01-Jul-93 -I I\) 0 er, 01-Jun-94 .,,
T 01-May-95 3: 01 -Apr-96 -r--0 r-0-01 -Mar-97 ~ lJ
0 01-Feb-98 I»
01-Jan-99 Q.
t o·
01-Dec-99 ::s C C 01-Nov-OO 2. z )> 01-0ct-01 0.: --t (1)
f 01-Sep-02 0
01-Aug-03 0 ::s
--t 01 -Jul-04 (')
:r: (1)
I\) 01-Jun-05 ::s
(,J -I\) ...
01-May-06 I» -01-Apr-07 s· ::s
01-Mar-08 u,
01-Feb-09 ::s
01-Jan-10 < (1)
01-Dec-10 (Q
(1) -01-Nov-11 I» -01-0ct-12 o· ::s
01-Sep-13 -C 01-Aug-14 0
01-Jul-15 :::::.: " 01-Jun-16 (Q -01-May-17
01-Apr-18
01-Mar-19 -
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 9.SOE-04
4th '81 20-0ct-81 3.00E-05
2nd '82 15-Apr-82 l.37E-05
3rd '82 OI-Jul-82 3.40E-04
4th '82 30-Nov-82 1.75E-05
2nd '83 13-Apr-83 7.13E-04
3rd '83 01-Ju1-83 5.39E-05
4th '83 30-Jan-84 6.40E-05
2nd '84 28-Jun-84 8.27E-05
4th '84 14-Nov-84 2.72E-04
2nd '85 27-Mar-85 4.73E-04
3rd '85 15-Ju1-85 6.60E-05
4th '85 09-0ct-85 2.83E-04
2nd '86 24-Mar-86 l.57E-04
3rd '86 10-Ju1-86 3.78E-04
4th '86 18-Dec-86 2.60E-04
2nd '87 20-Apr-87 4.IOE-04
3rd '87 05-Jun-87 2.90E-04
4th '87 22-Dec-87 l.80E-04
2nd '88 19-Apr-88 2.30E-04
3rd '88 28-Jul-88 J.SOE-04
2nd '89 07-Apr-89 3.IOE-04
3rd '89 06-Jun-89 l.30E-04
4th '89 07-Nov-89 4.30E-04
1st '90 17-Apr-90 2.50E-04
2nd'90 20-Jun-90 l.lOE-04
3rd '90 17-0ct-90 6.IOE-05
1st '91 10-Apr-91 3.40E-05
2nd '91 11-Jun-91 8.00E-05
3rd '91 20-Nov-91 6.50E-05
1st '92 22-Apr-92 l.60E-05
2nd '92 10-Jun-92 l.90E-05
3rd '92 10-Jun-92 l.60E-05
1st '93 13-Apr-93 2.60E-05
2nd '93 26-Jun-93 3.00E-05
3rd '93 12-0ct-93 3.IOE-05
1st '94 11-May-94 2.00E-05
2nd '94 19-Ju1-94 1.75E-05
3rd '94 28-Nov-94 l.OOE-04
1st '95 11-Apr-95 l.70E-05
2nd '95 06-Ju1-95 6.40E-06
3rd '95 15-Nov-95 2.JOE-05
1st '96 23-Apr-96 4.20E-05
2nd '96 * 31-Ju1-96
3rd '96 14-Nov-96 2.IOE-05
1st '97 21-Apr-97 5.50E-06
3rd '97 05-Sep-97 5.30E-06
4th '97 20-Nov-97 2.50E-05
1st '98 23-Mar-98 <7.90E-05
2nd '98 16-Jun-98 3.60E-07
4th '98 05-Nov-98 4.30E-05
2nd '99 15-Apr-99 2.40E-05
3rd '99 07-Jul-99 2.23E-05
4th '99 02-Dec-99 l.SOE-04
2nd '00 21-Apr-00 1.00E-04
2nd '00 22-Jun-00 1.30E-06
4th '00 21-Dec-OO l.20E-06
1st '01 30-Apr-01 l.80E-06
2nd '01 14-Juo-01 2.60E-06
4th 'OJ 17-Dec-01 2.63E-06
1st '02 07-May-02 3.50E-05
2nd '02 07-Jul-02 4.02E-05
4th '02 15-Dec-02 8.IOE-05
Ra-226 MDC¥ Pb-210
ERROR LLD uCi/Kg VALUE
(uCi/Kg) (5.0E-08) (uCi/Kg)
2.00E-05 5.00E-08 l.SOE-04
3.00E-06 5.00E-08 l.SOE-04
3.00E-06 3.00E-06 3.80E-04
2.00E-05 5.00E-08 3.68E-03
3.00E-06 2.00E-06 7.92E-04
7.30E-05 9.00E-08 2.51E-03
4.SOE-06 2.00E-06 6.88E-04
7.00E-06 4.00E-06 J.20E-03
6.30E-06 3.00E-09 l.80E-03
l.48E-04 2.00E-07 4.70E-03
l.60E-07 3.00E-06 7.07E-04
7.00E-06 4.00E-06 4.90E-04
2.00E-05 7.00E-06 l.SOE-03
I.OOE-05 4.00E-06 4.14E-03
I.ODE-OS 2.00E-06 1.65E-02
2.00E-05 2.00E-06 l.70E-03
7.00E-05 5.00E-08 2.20E-03
4.00E-05 5.00E-08 7.SOE-04
3.00E-05 5.00E-08 2.40E-03
5.00E-05 5.00E-08 2.90E-03
3.00E-05 5.00E-08 4.30E-03
4.00E-05 *** 4.20E-03
2.00E-05 ••• J.SOE-03
5.00E-05 l.40E-05 3.50E-03
3.00E-05 5.00E-06 2.39E-03
2.00E-05 5.00E-08 6.60E-04
l.40E-05 5.00E-08 6.IOE-04
l.lOE-05 5.00E-06 2.20E-04
6.00E-06 2.00E-07 1.20E-04
J.40E-05 5.00E-08 9.JOE-04
7.00E-06 2.00E-06 3.20E-04
l.OOE-05 2.00E-07 2.20E-04
1.80E-05 3.00E-06 7.60E-04
2.00E-05 3.00E-06 3.40E-04
l.40E-05 3.00E-06 O.OOEt-00
l.60E-05 3.00E-06 4.20E-04
5.00E-06 3.00E-05 3.90E-04
J.70E-06 7.60E-08 1.30E-04
9.00E-06 1.50E-07 2.60E-04
l.50E-06 l.60E-07 l.60E-04
6.00E-07 l.40E-07 4.40E-05
2.20E-06 l.70E-07 6.60E-05
2.20E-06 l.70E-07 1.00E-04
2.00E-06 l.60E-07 l.90E-04
4.20E-07 l.40E-07 3.30E-05
3.20E-07 1.26E-07 l.90E-05
9.50E-07 5.90E-07 1.30E-04
7.90E-05 7.90E-05 <3.90E-04
l.40E-07 3.30E-08 <l.7E-07
l.OOE-06 7.60E-08 2.50E-04
I.OOE-06 l.20E-07 1.70E-04
8.60E-07 1.20E-07 2.30E-04
3.00E-06 2.00E-07 1.70E-05
2.00E-06 l.20E-07 l.lOE-04
l.OOE-07 2.40E-07 2.00E-04
9.00E-07 2.40E-07 1.20E-04
J.OOE-07 l.70E-07 <8.3E-07
2.00E-07 9.90E-08 l.lOE-06
4.60E-05 1.20E-07 9.40E-05
2.20E-06 7.60E-07 l.36E-04
2.34E-06 7.60E-07 7.04E-05
3.90E-06 7.60E-07 2.87E-04
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(uCi/Kg) (1.0E-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
l.OOE-05 l.OOE-06 NS NA NA NS NA NA
2.00E-05 l.OOE-06 NS NA NA NS NA NA
4.00E-05 4.00E-05 NS NA NA NS NA NA
2.70E-04 l.OOE-07 NS NA NA NS NA NA
4.00E-06 2.00E-05 NS NA NA NS NA NA
3.00E-04 3.00E-04 NS NA NA NS NA NA
4.30E-05 4.00E-05 NS NA NA NS NA NA
I.OOE-04 4.00E-05 NS NA NA NS NA NA
1.00E-04 9.00E-08 NS NA NA NS NA NA
7.20E-04 3.00E-07 NS NA NA NS NA NA
3.60E-05 3.00E-05 NS NA NA NS NA NA
3.00E-05 3.00E-05 NS NA NA NS NA NA
l.OOE-04 7.00E-05 NS NA NA NS NA NA
l.80E-04 3.00E-05 NS NA NA NS NA NA
7.00E-04 l.OOE-04 NS NA NA NS NA NA
I.OOE-04 1.00E-04 NS NA NA NS NA NA
1.00E-04 l.OOE-06 NS NA NA NS NA NA
5.00E-05 l.OOE-06 NS NA NA NS NA NA
1.00E-04 l.OOE-06 NS NA NA NS NA NA
1.00E-04 1.00E-06 NS NA NA NS NA NA
2.00E-04 1.00E-06 NS NA NA NS NA NA
l.OOE-04 *** NS NA NA NS NA NA
l.OOE-04 *** NS NA NA NS NA NA
1.40E-04 2.70E-05 NS NA NA NS NA NA
5.00E-05 2.SOE-05 NS NA NA NS NA NA
3.00E-05 l.OOE-06 NS NA NA NS NA NA
3.00E-05 l.OOE-06 NS NA NA NS NA NA
J.OOE-05 1.00E-06 NS NA NA NS NA NA
l.OOE-05 2.00E-07 NS NA NA NS NA NA
5.00E-05 l.OOE-06 NS NA NA NS NA NA
2.00E-05 l.OOE-05 NS NA NA NS NA NA
2.00E-05 1.00E-06 NS NA NA NS NA NA
6.00E-05 2.00E-05 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
6.00E-05 2.00E-05 NS NA NA NS NA NA
8.00E-05 2.00E-04 NS NA NA NS NA NA
7.80E-06 3.80E-07 NS NA NA NS NA NA
J.20E-05 7.40E-07 NS NA NA NS NA NA
1.SOE-05 8.lOE-07 NS NA NA NS NA NA
4.20E-06 7.00E-07 NS NA NA NS NA NA
9.60E-06 8.30E-07 NS NA NA NS NA NA
6.70E-06 1.80E-07 NS NA NA NS NA NA
NS NA NA NS NA NA
7.30E-06 8.20E-07 NS NA NA NS NA NA
3.90E-06 7.00E-07 NS NA NA NS NA NA
6.90E-07 6.34E-07 NS NA NA NS NA NA
4.?0E-06 l.20E-07 NS NA NA NS NA NA
3.90E-04 3.90E-04 NS NA NA NS NA NA
J.70E-07 1.70E-07 NS NA NA NS NA NA
l.OOE-05 3.80E-07 NS NA NA NS NA NA
8.00E-06 6.20E-07 NS NA NA NS NA NA
7.00E-06 5.90E-07 NS NA NA NS NA NA
l.OOE-06 l.OOE-06 NS NA NA NS NA NA
7.00E-06 6.lOE-07 NS NA NA NS NA NA
l.OOE-05 l.20E-06 NS NA NA NS NA NA
3.00E-05 l.20E-06 NS NA NA NS NA NA
NIA 8.30E-07 NS NA NA NS NA NA
2.00E-08 5.00E-07 NS NA NA NS NA NA
3.72E-06 6.00E-07 NS NA NA NS NA NA
5.61E-06 1.00E-05 NS NA NA NS NA NA
4.llE-06 l.OOE-05 NS NA NA NS NA NA
8.54E-06 1.00E-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
1st '03 21-Mar-03 3.70E-05
2nd '03 lO-Jun-03 1.30E-05
4th '03 20-Nov-03 1.60E-04
1st '04 08-Apr-04 1.40E-04
2nd '04 12-Jun-04 6.51E-05
4th '04 30-Nov-04 8.40E-05
1st '05 21-Apr-05 1.70E-05
2nd '05 13-Jun-05 1.50E-05
4th '05 JO-Nov-05 3.80E-05
1st '06 03-Apr-06 1.00E-04
2nd '06 16-Jun-06 3.40E-05
4th '06 28-Nov-06 7.31E-05
!st '07 30-Mar-07 3.00E-05
2nd'07 1-Jun-07 1.lOE-04
4th '07 23-Nov-07 5.60E-05
!st '08 22-Aor-08 3.20E-05
2nd '08 18-Jun-08 1.25E-05
4th '08 12-Dec-08 9.20E-05
1st '09 28-Apr-09 2.60E-05
2nd '09 17-Jun-09 2.40E-05
4th '09 18-Dec-09 3.JOE-05
1st 'JO 13-May-lO 2.00E-05
2nd 'JO 18-Jun-10 1.IOE-05
4th 'IO 20-Dec-10 6.70E-06
2nd '11 23-Jun-ll <1.7E-07
3rd 'I I 27-Jul-11 1.60E-05
4th '11 23-Nov-11 7.80E-07
2nd '12 11-Apr-12 5.00E-06
3rd '12 ll-Jun-12 1.90E-08
4th '12 06-Nov-12 1.49E-05
2nd '13 30-Apr-13 4.50E-05
3rd '13 20-Jun-13 1.51E-05
4th '13 14-Nov-13 l.18E-04
2nd '14 16-Apr-14 4.65E-05
3rd '14 IO-Jun-14 1.23E-05
4th '14 25-Nov-14 1.16E-04
1st '15 21-Apr-15 2.27E-04
2nd '15 15-Jun-15 3.90E-05
4th '15 23-Nov-15 1.83E-04
2nd '16 14-Apr-16 1.67E-04
2nd '16 14-Jun-16 2.90E-05
4th '16 ll-Nov-16 8.39E-05
2nd '17 13-Apr-17 3.05E-05
2nd '17 19-Jun-17 3.98E-05
4th '17 02-Nov-17 9.70E-05
2nd '18 26-Apr-18 5.16E-05
2nd '18 20-Jun-18 5.14E-05
4th '18 02-Nov-18 1.04E-04
2nd '19 25-Apr-19 7.27E-06
2nd '19 06-Jun-19 3.54E-05
Ra-226 MDC¥ Pb-210 Pb-210
ERROR LLDuCi/Kg VALUE ERROR
(uCi/Kg) (5.0E-08) (uCi/Kg) (uCi/Kg)
2.60E-06 2.41E-06 2.69E-05 2.0JE-06
1.00E-06 5.20E-07 <1.00E-07
1.30E-05 1.20E-07 1.42E-04 6.42E-06
7.70E-06 l.lOE-07 6.JOE-06 2.70E-06
3.20E-06 1.50E-07 5.27E-05 4.90E-06
5.70E-06 3.00E-08 3.39E-04 1.60E-05
1.60E-06 1.30E-07 4.50E-05 3.50E-06
1.60E-06 1.40E-07 7.00E-05 5.JOE-06
2.JOE-06 8.60E-I0 1.20E-06 4.80E-08
6.00E-06 5.00E-08 3.30E-04 1.lOE-05
2.50E-06 5.00E-08 l.37E-04 6.00E-06
3.20E-06 1.60E-07 2.98E-04 8.50E-06
2.20E-06 1.70E-07 3.20E-04 7.90E-06
4.60E-06 2.3-07 3.20E-04 l.lOE-05
5.20E-06 5.00E-08 6.40E-04 l.90E-05
2.30E-06 7.20E-07 2.30E-04 1.50E-05
2.20E-06 1.80E-06 5.00E-05 3.00E-05
4.JOE-06 9.60E-07 4.lOE-04 3.00E-05
2.90E-06 1.40E-06 3.70E-05 1.50E-06
1.40E-06 3.90E-07 3.50E-05 7.90E-06
2.30E-06 2.lOE-04 8.40E-06
2.lOE-06 9.40E-07 5.60E-05 1.50E-05
J.30E-06 6.60E-07 7.80E-05 1.60E-05
9.lOE-07 4.80E-07 8.00E-07 7.90E-07
6.90E-08 1.70E-07 <2.5E-06 l.50E-06
1.00E-06 2.60E-07 9.50E-05 1.60E-06
2.50E-07 2.30E-07 <5.9E-07 3.50E-07
6.00E-07 3.00E-07 <7.0E-07 7.00E-07
6.20E-08 l.lOE-07 <2.5E-07 1.30E-06
3.41E-07 4.25E-08 4.45E-04 4.0lE-06
1.19E-06 5.39E-07 3.62E-04 6.30E-06
1.06E-06 1.96E-06 6.7lE-05 2.93E-06
3.39E-06 2.97E-06 5.92E-04 1.27E-05
1.08E-06 7.35E-07 2.13E-04 5.93E-06
4.97E-07 6.97E-07 2.46E-05 1.84E-06
2.25E-06 1.53E-06 4.43E-04 1.04E-05
5.0lE-06 4.08E-06 5.90E-04 l.16E-05
1.88E-06 2.71E-06 5.29E-04 1.61E-05
6.96E-06 9.64E-06 8.94E-04 1.43E-05
4.lOE-06 3.65E-06 7.99E-04 2.08E-05
1.88E-06 3.85E-06 1.95E-04 2.18E-05
2.71E-06 3.21E-06 1.21E-03 2.15E-05
(5.00E-08)
2.30E-06 4.61E-06 6.14E-04 1.26E-05
(5.00E-08)
l.17E-06 l.04E-06 5.25E-05 2.68E-06
(5.00E-08)
3.12E-06 3.05E-06 6.36E-04 l.14E-05
(5.00E-08)
l.21E-06 8.lOE-07 3.83E-04 8.29E-06
(5.00E-08)
2.70E-06 4.37E-06 9.22E-05 7.25E-06
(5.00E-08)
3.19E-06 3.73E-06 4.03E-04 8.74E-06
(5.00E-08)
1.23E-06 2.84E-06 6.61E-05 l.22E-05
(5.00E-08)
l.58E-06 2.25E-06 2.18E-04 1.90E-05
(5.00E-08)
MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(1.0E-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
3.73E-06 NS NA NA NS NA NA
1.00E-07 NS NA NA NS NA NA
5.90E-07 NS NA NA NS NA NA
5.50E-07 NS NA NA NS NA NA
7.60E-07 NS NA NA NS NA NA
3.00E-07 NS NA NA NS NA NA
6.50E-07 NS NA NA NS NA NA
6.90E-07 NS NA NA NS NA NA
4.30E-JO NS NA NA NS NA NA
1.00E-06 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
8.20E-07 NS NA NA NS NA NA
8.40E-07 NS NA NA NS NA NA
l.lOE-06 NS NA NA NS NA NA
1.00E-06 NS NA NA NS NA NA
l.OOE-06 NS NA NA NS NA NA
4.80E-03 NS NA NA NS NA NA
4.00E-05 NS NA NA NS NA NA
2.50E-05 NS NA NA NS NA NA
1.30E-05 NS NA NA NS NA NA
NS NA NA NS NA NA
2.40E-05 NS NA NA NS NA NA
2.50E-05 NS NA NA NS NA NA
1.30E-06 NS NA NA NS NA NA
2.50E-06 NS NA NA NS NA NA
1.70E-06 NS NA NA NS NA NA
5.90E-07 NS NA NA NS NA NA
1.00E-06 NS NA NA NS NA NA
2.20E-06 NS NA NA NS NA NA
8.57E-07 NS NA NA NS NA NA
9.90E-06 NS NA NA NS NA NA
6.24E-06 NS NA NA NS NA NA
1.62E-05 NS NA NA NS NA NA
1.31E-05 NS NA NA NS NA NA
4.63E-06 NS NA NA NS NA NA
l.94E-05 NS NA NA NS NA NA
1.67E-05 4.33E-04 l.86E-05 5.J4E-06 3.31E-05 2.15E-06 1.14E-06
3.36E-05 7.78E-05 8.47E-06 6.43E-06 1.08E-05 l.28E-06 l.21E-06
2.03E-05 4.88E-04 2.91E-05 9.00E-06 7.92E-06 7.67E-07 3.20E-07
4.12E-05 2.JOE-04 2.24E-05 l.39E-05 5.58E-05 5.42E-06 2.lOE-06
5.93E-05 7.04E-05 3.17E-06 l.92E-06 3.70E-06 8.08E-07 1.04E-06
3.78E-05 l.27E-03 4.84E-05 l.lOE-05 7.71E-06 1.08E-06 l.32E-06
(1.00E-06) (2.00E-07) (2.00E-07)
1.71E-05 8.20E-04 1.28E-05 2.31E-06 2.91E-06 7.40E-07 l.21E-06
(1.00E-06) (2.00E-07) (2.00E-07)
5.93E-06 1.77E-04 4.52E-06 l.32E-06 l.08E-05 l.12E-06 1.07E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
1.72E-05 2.52E-04 7.28E-06 3.25E-06 6.82E-06 l.05E-06 2.l!E-06
(1.00E-06) (2.00E-07) (2.00E-07)
1.5 IE-05 4.02E-04 6.92E-06 l.50E-06 4.93E-06 l.99E-06 3.69E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
2.08E-05 1.49E-04 4.71E-06 2.17E-06 3.18E-06 5.8 lE-07 7.45E-07
(1.00E-06) (2.00E-07) (2.00E-07)
l.33E-05 6.50E-04 1.85E-05 3.65E-06 9.67E-06 l.l9E-06 l.6JE-06
(1.00E-06) (2.00E-07) (2.00E-07)
2.95E-05 1.96E-04 5.58E-06 1.78E-06 9.27E-06 l.29E-06 l.30E-06
(l.OOE-06) (2.00E-07) (2.00E-07)
2.89E-05 7.00E-05 4.74E-06 3.31E-06 2.56E-05 9.31E-06 1.43E-05
(1.00E-06) (2.00E-07) (2.00E-07)
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
4th '19 13-Nov-19 5.12E-05
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (S.OE-08)
l.70E-06 l.69E-06
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLD uCi/Kg VALUE ERROR
(uCi/Kg) (uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg)
4.IOE-04 l.12E-05 2.17E-05 3.48E-05 l.99E-06
(l.OOE-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected durmg this period
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
l.24E-06 4.56E-06
(2.00E-07)
t NRC Regulatory Guide does not specify a Lower Limit of Detection (LLD) for Thorium 232 in vegetation (or any matrix). The LLD for Thorium 230 was used.
NS = Not Sampled
NA= Not Applicable
Th-232 MDC¥
ERROR LLD
(uCi/Kg) uCi/Kg
(2.0E-07)t
8.00E-07 2.00E-05
(2.00E-07)
¥ The· value in the MDC column is the sample-specific minimum detectable concentration. The MDC is based on the sample moisture, composition and other sample-specific variables. The
value in parantheses is the method-specific lower limit of detection (LLD), which is a limit representing the detection capability of the measurement system. The LLDs in the data package are
referred to as the Reporting limit (RL).
(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 6 I 6 I 6 I 6 + 0 0 0 0 0 00 --..J en 01 """ (,.) I\) ...... 0
01-Aug-81 :e :c
01-Jul-82 =i
01-Jun-83 m
01-May-84 s: m
01-Apr-85 CJ)
)>
01-Mar-86 s:
01-Feb-87 -r
01-Jan-88 r
I
01-Dec-88 CJ)
01-Nov-89 0
C
01-0ct-90 -t
t :c 01-Sep-91 :e
01-Aug-92 m JJ CJ) Ill 01-Jul-93 -t I\)
"' 0 0) 01-Jun-94 .,,
T 01-May-95 s:
01-Apr-96 -r "'O r CT 01-Mar-97 I\) :::0 -01-Feb-98 m 0 Q.
t 01-Jan-99 s·
01-Dec-99 -::s C
C 01-Nov-OO (') z a: )> 01-0ct-01 --i Cl)
t 01-Sep-02 0 0 01-Aug-03 ::s
(') --i 01-Jul-04 Cl) I
I\) 01-Jun-05 ::s ... c,J "'I "' m 01-May-06 ...
01-Apr-07 s· ::s
01-Mar-08 en s· 01-Feb-09 < 01-Jan-10 Cl) cg
01-Dec-10 !2.
01-Nov-11 m ...
01-0ct-12 s· ::s
01-Sep-13 -C
01-Aug-14 0
z::::.: 01-Jul-15 " 01-Jun-16
cg -
01-May-17
01-Apr-18
01-Mar-19
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: December 13, 2019
Company:
Address:
Contact:
Project:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis -------------~~
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
North East
496617001
SOLID
13-NOV-19 09:00
15-NOV-19
Client
Parameter Qualifier Result Uncertainty
lad Alpha Spec Analysis
MDC
\lphaspec Th-232, Solid (Limited Volume) "Dry Weight Corrected"
~horium-232 1.01 E-05 +/-1.24E-06 l.68E-06
\.lphaspec U, Solid (Limited Volume) "Dry Weight Corrected"
Jranium-233/234 7.96E-05 +/-l.80E-06 5.87E-07
Jranium-235/236 4.3 IE-06 +/-4. 70E-07 1.50E-07
Jranium-238 8.20E-05 +/-1.83E-06 4.48E-07
lad Gas Flow Proportional Counting
:iFPC, Pb210, Solid (Limited Volume) "Dry Weight Corrected"
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
,ead-210 0.00086 +/-l.SIE-05 2.41E-05 1.00E-06
:iFPC, Total Alpha Radium, solid (Limited Volume) "Dry Weight Corrected"
~otal Radium 0.000491 +/-4.77E-06 l.73E-06 5.00E-08
[he following_ Pr~p Methods were performed:
Project:
Client ID:
DNMI00101
DNMI001
Units PF DF Analyst Date Time Batch Method
uCi/kg HAKB 12/04/19 1404 1940453
uCi/kg HAKB 12/05/19 1728 1940454 2
uCi/kg
uCi/kg
uCi/kg LXB3 12/12/19 1140 1941985 3
uCi/kg LXB3 12/09/19 1938 1941984 4
Date Time \1:ethod Description __ Analyst CXCl _____ _
)ry Soil Prep Dry oil Pr,;p GL-RAD-A-021
Prep Batch
11/19/19 1059 1940341
The following Analytical Methods were performed: ---\llethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 903.0
,urrogate/Tracer Recovery Test
,horium-229 Tracer Alphaspec Th-232, Solid (Limited Volume) "Dry
Weight Corrected"
Jranium-232 Tracer Alphaspec U, Solid (Limited Volume) "Dry Weight
Corrected"
,ead Carrier GFPC, Pb210, Solid (Limited Volume) "Dry
Weight Corrected"
3arium Carrier GFPC, Total Alpha Radium, solid (Limited
Volume) "Dry Weight Corrected"
'tfotes:
=:ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Page 1 7 of 25 SDG: 496617
Analyst Comments
Result Nominal Recovery% Acceptable Limits
62.7 (15%-125%)
85.2 (15%-125%)
107 (25%-125%)
IOI (25%-125%)
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: December 13, 2019
Company :
Address:
Contact:
Project:
Client Sample ID:
Sample ID:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North East
496617001
Parameter Qualifier Result Uncertainty MDC RL ------------------
Column headers are defined as follows:
DF: Dilution Factor
DL: Detection Limit
MDA: Minimum Detectable Activity
MDC: Minimum Detectable Concentration
Page 18 of25 SDG: 496617
Le/LC: Critical Level
PF: Prep Factor
RL: Reporting Limit
SQL: Sample Quantitation Limit
Project:
Client ID:
DNMI00101
DNMIOOI
Units PF DF Analyst Date Time Batch Method
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: December 13, 2019
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
496617002
SOLID
13-NOV-19 08:30
15-NOV-19
Client
Parameter Qualifier Result Uncertainty
lad Alpha Spec Analysis
MDC
\lphaspec Th-232, Solid (Limited Volume) "Dry Weight Corrected"
:horium-232 7.34E-06 +/-1.18E-06 2.05E-06
\lphaspec U, Solid (Limited Volume) "Dry Weight Corrected"
Jranium-233/234 0.000174 +/-2.76E-06 4.80E-07
Jranium-235/236 9.52E-06 +/-7 .25E-07 4. I 4E-07
Jranium-238 0.000179 +/-2.80E-06 5.38E-07
lad Gas Flow Proportional Counting
]FPC, Pb2IO, Solid (Limited Volume) "Dry Weight Corrected"
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
,ead-210 0.00131 +/-1.82£-05 2.46E-05 1.00E-06
]FPC, Total Alpha Radium, solid (Limited Volume) "Dry Weight Corrected"
:otal Radium 0.000609 +/-6.16£-06 2.42E-06 5.00E-08
rhe following Prep Methods were performed:
\1:ethod Description
)ry Soil Prep Dry oil Prep GL-RAD-A-021
The following Analytical Methods were performed: ---\.1ethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 903.0
Analy t ~~-c=·xc1~-
Project:
Client ID:
DNMIOOI01
DNMIOOl
Units PF DF Analyst Date Time Batch Method
uCi/kg HAKB 12/07/19 1400 1940453
uCi/kg HAKB 12/05/19 1728 1940454 2
uCi/kg
uCi/kg
uCi/kg LXB3 12/12/19 1140 1941985 3
uCi/kg LXB3 12/09/19 1938 1941984 4
Date Time Prep Batch
11/19/19 1059 194034_1 __
Anal st Comments
;urrogate/Tracer Recovery Test Result Nominal Recovery% Acceptable Limits
rhorium-229 Tracer Alphaspec Th-232, Solid (Limited Volume) "Dry
Weight Corrected"
Jranium-232 Tracer Alphaspec U, Solid (Limited Volume) "Dry Weight
Corrected"
,ead Carrier GFPC, Pb210, Solid (Limited Volume) "Dry
Weight Corrected"
3arium Carrier GFPC, Total Alpha Radium, solid (Limited
Volume) "Dry Weight Corrected"
~otes:
:ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Page 19 of 25 SDG: 496617
62.9 (15%-125%)
94.6 (15%-125%)
106 (25%-125%)
105 (25%-125%)
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Company :
Address :
Contact:
Project:
Client Sample ID:
Sample ID:
Certificate of Analysis
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North West
496617002
Project:
Client ID:
Report Date: December 13, 2019
DNMIOOlOl
DNMIOOI
Parameter Qualifier Result Uncertainty MDC RL Units PF DF Analyst Date Time Batch Method
Column headers are defined as follows:
OF: Dilution Factor
DL: Detection Limit
MDA: Minimum Detectable Activity
MDC: Minimum Detectable Concentration
Page 20 of 25 SDG: 496617
---------
Le/LC: Critical Level
PF: Prep Factor
RL: Reporting Limit
SQL: Sample Quantitation Limit
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: December 13, 2019
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
496617003
SOLID
13-NOV-19 08:00
15-NOV-19
Client
Project:
Client ID:
DNMIOOlOl
DNMIOOI
Parameter Qualifier Result Uncertainty MDC RL Units PF DF Analyst Date Time Batch Method
lad Alpha Spec Analysis
\lphaspec Th-232, Solid (Limited Volume) "Dry Weight Corrected"
~horium-232 4.56E-06 +/-8.00E-07 l.02E-06
\lphaspec U, Solid (Limited Volume) "Dry Weight Corrected"
Jranium-233/234 l.71E-05 +/-8.49E-07 4.59E-07
Jranium-235/236 I.94E-06 +/-3.31E-07 3.90E-07
Jranium-238 l.58E-05 +/-8.14E-07 3.95E-07
lad Gas Flow Proportional Counting
JFPC, Pb210, Solid (Limited Volume) "Dry Weight Corrected"
2.00E-07
2.00E-07
2.00E-07
2.00E-07
,ead-210 0.00041 +/-1.12E-05 2. I 7E-05 l.OOE-06
JFPC, Total Alpha Radium, solid (Limited Volume) "Dry Weight Corrected"
:otal Radium 5.12E-05 +/-1.70E-06 l.69E-06 5.00E-08
rhe following Prep Methods were performed: -------------vf et hod Description Analyst
---
uCi/kg HAKB 12/04/19
uCi/kg HAKB 12/07/19
uCi/kg
uCi/kg
uCi/kg LXB3 12/12/19
uCi/kg LXB3 12/09/19
Date Time Prep Batch
)ry Soil Prep Dry Soil Prep GL-RAD-A-021 CXCI -----,--~-,---11/19/19 1059 194034 1
The following Analytical Methods were performed:
\1ethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 903.0
Anajyst Comments
1404 1940453
1340 1940454
1140 1941985
1938 1941984
;urrogate/Tracer Recovery,__T_e_s_t-----------------------------~---~ Result Nominal Recovery% Acceptable Limits
fhorium-229 Tracer Alphaspec Th-232, Solid (Limited Volume) "Dry
Weight Corrected"
Jranium-232 Tracer Alphaspec U, Solid (Limited Volume) "Dry Weight
Corrected"
,ead Carrier GFPC, Pb210, Solid (Limited Volume) "Dry
Weight Corrected"
3arium Carrier GFPC, Total Alpha Radium, solid (Limited
Volume) "Dry Weight Corrected"
~otes:
:::ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Page 21 of25 SDG: 496617
72.1 (15%-125%)
82.2 (15%-125%)
107 (25%-125%)
86.9 (25%-125%)
2
3
4
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: December 13, 2019
Company :
Address:
Contact:
Project: ----Client Sample ID:
Sample ID:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
South West
496617003
Parameter Qualifier Result Uncertainty MDC
Column headers are defined as follows:
DF: Dilution Factor
DL: Detection Limit
Le/LC: Critical Level
PF: Prep Factor
RL: Reporting Limit
RL
MDA: Minimum Detectable Activity
MDC: Minimum Detectable Concentration SQL: Sample Quantitation Limit
Page 22 of 25 SDG: 496617
Project:
Client ID:
DNMI00101
DNMI001
Units PF DF Analyst Date Time Batch Method
tel ij • I Laboratories LLC
a member of The GEL Group INC
PO Box :!0712 Cr1arl eston. s C 2!1417
2040 Smoe Road Charleston SC 29407
P 843.556.8171
P 84,760.1178
December 13, 2019
Ms. Kathy Weinel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
Work Order: 496617
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on November 15, 2019. This original data report has been prepared and reviewed in
accordance with GEL's standard operating procedures.
Test results for NELAP or ISO 17025 accredited tests are verified to meet the requirements of those standards,
with any exceptions noted. The results reported relate only to the items tested and to the sample as received by
the laboratory. These results may not be reproduced except as full reports without approval by the laboratory.
Copies ofGEL's accreditations and certifications can be found on our website at www.gel.com.
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. 4289.
Purchase Order: DW16138
Enclosures
Sincerely
Julie Robinson
Project Manager
11 11 1111 rn1 11111 111 11 111111111
gel .corn
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 496617
Case Narrative
Page 1 of25 SDG:496617
December 13, 2019
Laboratory Identification:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 496617
Sample receipt: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on November 15,
2019 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
496617001 North East
496617002 North West
496617003 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.
Page 2 of 25 SDG: 496617
Julie Robinson
Project Manager
Chain of Custody and
Supporting
Documentation
Page 3 of25 SDG: 496617
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: _G_e_l _L_ab_o_ra_t_o_rie_s _____ ,--___ Contact: Tanner Holliday
2040 Savage Road Ph: 435 678 2221
Charleston, SC 29407 tholl [e-mail]
Chain of Custody/Sam >ling Analysis Request
Project Samplers N ~me Samplers Signature
Late Fall Vegetation 2019 Tanner Holli ~av I .;-t ~.rlP J( H/L/~ef
(/
Time
Sample ID Date Collected Collected Laboratorv Analysis Requested
North East 11/13/2019 900 Ra 226, U-Nat, Th-232, PB 210
North West 11/13/2019 830 Ra 226, U-Nat, Th-232, PB 21 O
South West 11/13/2019 800 Ra 226, U-Nat, Th-232, PB 210
Wekihts:
North East: 2400 Grams
North West: 1730 Grams
South West: 1700 Grams
* Please use caution when handling samples. Some
plants have thorns.
Comments: Please send report to Kathy Weinel at [e-mail]
Relinquished By:~nat~_} Date/Time Received By:(Signature) Dafi:le 0~ '~ .. 11/13/2019 1 ~ Tanner Hollid~( 1130 11/ii!tl/
Relinquished By:(Signature) Date/Time Receivevgnature) Date/Time
Page 4 of25 SDG: 496617
Client: \\1\..,
Received B ZKW
Carrier and Tracking Number
Suspected Hazurd Information
A)Ship cd as n DOT Hazardous'/
B) Did the client designate the samples arc lo be
received as radioact1vc?
C) Did the RSO classify the samples as
radioactive?
D) Did the client dcsib~latc samples are
hazardous?
E) Did lhe RSO idcntily il0Ssiblc hazards?
Sample lkcei11t Criteria
Shipping containers received intact and
sealed?
2 Chain of custody documents included
with shipment9
3 Samples requiring cold preservation
within (0 :': 6 deg, C)'l*
4 Daily check performed and passed on IR
tcmperalure gun?
5 Sample containers intact and sealed?
6 Samples requiring chemical preservation
at proper pH9
7 Do any samples require Volatile
Analysis?
8 Samples received within holding time'?
9 Sample ID's on COC match !D's on
bottles'?
10 Date & time on COC match date & lime
on bottles?
11 Number or containers rec~ived match
number indicated on COC'?
12 Arc sample containers identifiable as
, I. r vi e 1·1
13 COC form is properly signed in
relinquished/received sections?
Comments (Use Continuation Fonn if needed):
SAMPLE RECEIPT & REVIEW FORM
SDG/AR/COC/Work
FedEx E~press
Cir~bf~
FedEx Ground ~ l'ield Services Courier Other I
I Z. *If Net Counts > IOOcpm on samPilc.~ not marked "radioactivc0
, contact the Radiation Safoly Group for l\1rthcr invcstigalion.
Hazard Class Shipped: j UN/I:
lfUN2910, Is the Radioactive Sl11!>111cn1 SurvcyComplim11? Yes ___ No __
RCRA Asbestos Beryllium Other:
Commcr11s/Quuliiior, (Required for Non-Conforming Items)
Circle Applicabl~: Seals broker~ l)nm11gcJ con In mer l('111d11.s c:umnincr 01hc-r {dc:'icribc)
Circle Applicnbtc: Client co111nc1cd and provitl<d COC
Prcscr"~1io11 kthod: Wet Ice, Ice Pncks Ory ice
•:11i 1cmpera1tires are re orclcd in Celsius
Tem11ernture De,·icc Serini fl: IR3-18
Secondary Temperature Device Seri"I II (If Applicable):
COC created upon r~.:e1p1
101 c Othc .
Circle Applicable: Seals brok1m Damaged container Leaking Cl>nlnincr Other (describe)
S:unplc 10'.s amJ l'ontoi11c.1s ;\ffcclctl:
--,--::, I
TEMP: .:r.;, S, C
Do liquid VOA vials contain ~cid prcscrvotion? Yes_ o_ NA_(lf 1111know11, sel~cl No)
re liquid VOA vials free ofhcadspace'! Yes ____ No __ NA ____ _
ID's and lcsls affected:
ID's and conlaincrs affected:
Circle Applicable: No dates on containers No limes on containers COC missing info Other (dcscril>e)
Circle Applical>le: No contai11cr co11nl on COC Other (describe)
Nol relinquished Other (describe)
I
PM (or PMA) review: lnitials ___ 1_,. ___ _ P:rgc _ (_ of ___ I_
GL-CHL-SR-001 Rev 6
Page 5 of25 SDG: 496617
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 496617
Client SDG: 496617
Late Fall Vegetation 2019
Project Manager:
Project Name:
Purchase Order:
Package Level:
EDD Format:
Julie Robinson
DNMI00101 Vegetation Analysis
DW16138
LEVEL3
EIM_DNMI
GELID Client Sample ID Client Sample Desc.
496617001 North East
496617002 North West
496617003 South West
Client Sample ID Status Tests/Methods
-001 North East REVW GFPC, Pb210, Solid (Limited
Volume)
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
(Limited Volume)
REVW Alphaspec U, Solid (Limited
Volume)
REVW Alphaspec Th-232, Solid
(Limited Volume)
-002 North West REVW GFPC, Pb210, Solid (Limited
Volume)
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
(Limited Volume)
REVW Alphaspec U, Solid (Limited
Volume)
REVW Alphaspec Th-232, Solid
(Limited Volume)
-003 South West REVW GFPC, Pb210, Solid (Limited
Volume)
REVW Laboratory Composite -Dry prep
instructions
REVW GFPC, Total Alpha Radium, solid
(Limited Volume)
REVW Alphaspec U, Solid (Limited
Volume)
REVW Alphaspec Th-232, Solid
(Limited Volume)
Collect
Date & Time
13-NOV-19 09:00
13-NOV-19 08:30
13-NOV-19 08:00
Product
Reference
Ra226
U-Natural
Ra226
U-Natural
Ra226
U-Natural
Work Order Due Date: 15-DEC-19
Package Due Date:
EDD Due Date:
Due Date:
JAR1
Receive Time # of
Date & Time Zone Cont.
15-NOV-19 09:40 -2
15-NOV-19 09:40 -2
15-NOV-19 09:40 -2
Fax Date PM Comments
13-DEC-19
14-DEC-19
15-DEC-19
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Limited Volume. Please run Client Matrix
LCS/LCSD.Use caution when
handling samples. Some plants
have thorns.
Limited Volume. Please run Client Matrix
LCS/LCSD.Use caution when
handling samples. Some plants
have thorns.
Limited Volume. Please run Client Matrix
LCS/LCSD.Use caution when
handling samples. Some plants
have thorns.
Report Date: 13-DEC-19
Work Order: 496617
Page 1 of 3
Collector: C
Prelogin #: 20180673982
Project Workdef ID: 1310529
SDG Status: Closed
Logged by:
Fax Days to
Due Date Process CofC#
Prelog Lab Field
Group QC QC
30
30
30
Aux Data
SOLID
SOLID
SOLID
Receive
Codes
LS
LS
LS
r----\0
\0
O'\
s::t"
0 Cl
V)
N
4-< 0
\0
ll)
~ i:i...
GEL Laboratories LLC -Login Review Report
Product: LABCOMP _S Workdef ID: 1481531
Method:
In Product Group? No
Product Description: Laboratory Composite -Dry prep instructions
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Product: GFC_PBS WorkdeflD: 1481511
Method: DOE RP280 Modified
Product Description: GFPC, Pb210, Solid (Limited Volume)
Samples: 001, 002, 003
Parrnname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS Workdef ID: 1481534
Method: EPA 903.0
In Product Group? No
In Product Group? No
Product Description: GFPC, Total Alpha Radium, solid (Limited Volume)
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Total Radium
Product: ASP_ UUS Workdef ID: 1481535 In Product Group? No
Method: DOE EML HASL-300, U-02-RC Modified
Product Description: Alphaspec U, Solid (Limited Volume)
Samples: 001 , 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
13968-55-3/13966-. Uranium-233/234
15117-96-1/13982-Uranium-235/236
7440-61-1 Uranium-238
Group Name:
Client RDL or
PQL & Unit
Group Name:
Client RDL or
PQL & Unit
.000001
Group Name:
Client RDL or
PQL & Unit
.00000005
Group Name:
Client RDL or
PQL & Unit
.0000002
.0000002
.0000002
Reporting
Units
Reporting
Units
uCi/kg
Reporting
Units
uCi/kg
Reporting
Units
uCi/kg
uCi/kg
uCl/kg
Group Reference:
Report Date: 13-DEC-19
Work Order: 496617
Page 2 of 3
Path: Rad Soil Prep SPRP
Product Reference:
Moisture Correction: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
Group Reference:
Path: Standard (Dry)
Product Reference:
No
Moisture Correction: "Dry Weight Corrected"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y No
Group Reference:
Path: Standard (Dry)
Product Reference: Ra226
Moisture Correction: "Dry Weight Corrected"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y No
Group Reference:
Path: Standard (Dry)
Product Reference: U-Natural r--Moisture Correction: "Dry Weight Corrected" ,..... \0
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y No
REG y y
REG y y
\0 °' s::I"
0 Q
rf).
V)
N
~ 0
r--
(I)
bl.)
ell 0....
GEL Laboratories LLC -Login Review Report
Product: ASP_ THS Workdef ID: 1481536 In Product Group? No
Method: DOE EML HASL-300, Th-01-RC Modified
Product Description: Alphaspec Th-232, Solid (Limited Volume)
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS#
7440-29-1
Contingent
Tests
Parmname
Thorium-232
Action Product Name Description
Login Requirements:
Requirement
LOGIN: Are these vegetation sample?
Login Reminder?
Group Name: Group Reference:
Report Date: 13-DEC-19
Work Order: 496617
Page 3 of 3
Path: Standard (Dry)
Product Reference:
Moisture Correction: "Dry Weight Corrected"
Client RDL or
PQL & Unit Reporting Parm Included Included Custom
Units Function in Sample? in QC? List?
.0000002 uCi/kg REG y y No
Samples
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? _____ _
r:---.....
I.O I.O "" 'tj-
ci Cl r:/).
If)
N
4-+ 0
00
(1)
~ p..
Page 9 of 25 SDG: 496617
Laboratory
Certifications
List of current GEL Certifications as of 13 December 2019
State Certification
Alaska 17-018
Alaska Drinking Water SCOOOl2
Arkansas 88-0651
CLIA 4200904046
California 2940
Colorado SCOOOl2
Connecticut PH-0169
DoD ELA?/ ISO 17025 A2LA 2567.01
Florida NELAP E87156
Foreign Soils Permit P330-15-00283,P330-15-00253
Georgia SC00012
Georgia SOWA 967
Hawaii SC00012
Idaho SC00012
Illinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332
Kentucky SDWA 90129
Kentucky Wastewater 90129
Louisiana Drinking Water LA024
Louisiana NELAP 03046 (AI33904)
Maine 2019020
Maryland 270
Massachusetts M-SCOl2
Massachusetts PF AS Approv Letter
Michigan 9976
Mississippi SC00012
Nebraska NE-OS-26-13
Nevada scooo 122020-1
New Hampshire NELAP 2054
New Jersey NELAP SC002
New Mexico SC00012
New York NELAP 11501
North Carolina 233
North Carolina SDWA 45709
North Dakota R-158
Oklahoma 2019-165
Pennsylvania NELAP 68-00485
Puerto Rico SCOOOl2
S. Carolina Radiochem 10120002
Sanitation Districts of L 9255651
South Carolina Chemistry 10120001
Tennessee TN 02934
TexasNELAP TI04704235-19-15
UtahNELAP SCOOOl22019-29
Vermont VT87156
Virginia NELAP 460202
Washington C780
Page 10 of 25 SDG: 496617
Radiochemistry
Technical Case Narrative
Energy Fuels Resources
SDG #: 496617
Product: Alphaspec Th-232, Solid (Limited Volume)
Analytical Method: DOE EML HASL-300, Th-01-RC Modified
Analytical Procedure: GL-RAD-A-038 REV# 18
Analytical Batch: 1940453
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1940341
The following samples were analyzed using the above methods and analytical procedure(s).
Client Sample Identification
North East
North West
South West
Method Blank (MB)
Laboratory Control Sample (LCS)
GEL Sample ID#
496617001
496617002
496617003
1204435943
1204435944
1204435945 Laboratory Control Sample Duplicate (LCSD)
The samples in this SDG were analyzed on a "dry weight" basis.
Data Summary:
All sample data provided in this report met the acceptance criteria specified in the analytical methods and
procedures for initial calibration, continuing calibration, instrument controls and process controls where
applicable, with the following exceptions.
Oualitv Control (QC) lnformation
RDLMet
The blank (See Below) did not meet the detection limit due to keeping the blank volume consistent with the
other sample aliquots.
Sample Analyte Value
1204435943 (MB) Thorium-232 Result 0.000000338 < MDA 0.000000813 > RDL 0.0000002 uCi/kg
Technical Information
Recounts
Sample 496617002 (North West) was given additional clean-up steps and recounted in order to improve the
resolution. The recount is reported.
Page 11 of 25 SDG: 496617
Product: Alphaspec U, Solid (Limited Volume)
Analytical Method: DOE EML HASL-300, U-02-RC Modified
Analytical Procedure: GL-RAD-A-011 REV# 27
Analytical Batch: 1940454
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1940341
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
496617001
496617002
496617003
1204435946
1204435947
1204435948
Client Sample Identification
North East
North West
South West
Method Blank (MB)
Laboratory Control Sample (LCS)
Laboratory Control Sample Duplicate (LCSD)
The samples in this SDG were analyzed on a "dry weight" basis.
Data Summary:
All sample data provided in this report met the acceptance criteria specified in the analytical methods and
procedures for initial calibration, continuing calibration, instrument controls and process controls where
applicable, with the following exceptions.
Quality Control (OC) Information
RDLMet
The blank (See Below) did not meet the detection limit due to keeping the blank volume consistent with the
other sample aliquots.
Sample Analyte Value
1204435946 Uranium-233/234 Result -0.000000129 < MDA 0.000000489 > RDL 0.0000002 uCi/kg (MB)
Uranium-235/236 Result -0.0000000000000323 < MDA 0.000000596 > RDL 0.0000002
uCi/kg
Uranium-238 Result -0.000000235 < MDA 0.000000722 > RDL 0.0000002 uCi/kg
Technical Information
Recounts
Samples 1204435947 (LCS) and 1204435948 (LCSD) were recounted due to high recovery. The recounts are
reported. Sample 496617003 (South West) was recounted due to high MDC. The recount is reported.
Product: Dry Weight
Page 12 of25 SDG: 496617
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1940341
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
496617001
496617002
496617003
Client Sample Identification
North East
North West
South West
The samples in this SDG were analyzed on an "as received" basis.
Data Summary:
There are no exceptions, anomalies or deviations from the specified methods. All sample data provided in this
report met the acceptance criteria specified in the analytical methods and procedures for initial calibration,
continuing calibration, instrument controls and process controls where applicable.
Product: GFPC, Total Alpha Radium, solid (Limited Volume)
Analytical Method: EPA 903.0
Analytical Procedure: GL-RAD-A-010 REV# 18
Analytical Batch: 1941984
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1940341
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
496617001
496617002
496617003
1204439542
)204439545
1204439546
Client Sample Identification
North East
North West
South West
Method Blank (MB)
Laboratory Control Sample (LCS)
Laboratory Control Sample Duplicate (LCSD)
The samples in this SDG were analyzed on a "dry weight" basis.
Data Summary:
All sample data provided in this report met the acceptance criteria specified in the analytical methods and
procedures for initial calibration, continuing calibration, instrument controls and process controls where
applicable, with the following exceptions.
Quality Control (OC} Information
RDLMet
The blank (See Below) did not meet the detection limit due to keeping the blank volume consistent with the
other sample aliquots.
Page 13 of25 SDG: 496617
Sample Analyte Value
1204439542 (MB) Total Radium Result 0.00000153 < MDA 0.00000155 > RDL 0.00000005 uCi/kg
Product: GFPC, Pb2IO, Solid (Limited Volume)
Analytical Method: DOE RP280 Modified
Analytical Procedure: GL-RAD-A-018 REV# 15
Analytical Batch: 1941985
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1940341
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
496617001
496617002
496617003
1204439547
1204439548
1204439549
Client Sample Identification
North East
North West
South West
Method Blank (MB)
Laboratory Control Sample (LCS)
Laboratory Control Sample Duplicate (LCSD)
The samples in this SDG were analyzed on a "dry weight" basis.
Data Summary:
All sample data provided in this report met the acceptance criteria specified in the analytical methods and
procedures for initial calibration, continuing calibration, instrument controls and process controls where
applicable, with the following exceptions.
Quality Control (QC) Information
RDLMet
The blank (See Below) did not meet the detection limit due to keeping the blank volume consistent with the
other sample aliquots.
Sample Analyte Value
1204439547 (MB) Lead-210 Result 0.0000021 < MDA 0.0000239 > RDL 0.000001 uCi/kg
Technical Information
Recounts
Samples 496617001 (North East), 496617002 (North West) and 496617003 (South West) were recounted to
verify sample results. Recounts are reported. Sample 1204439547 (MB) was recounted due to a suspected blank
false positive. The recount is reported.
Page 14 of 25 SDG: 496617
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.
Page 15 of 25 SDG: 496617
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Qualifier Definition Report
for
DNMI001 Energy Fuels Resources (USA), Inc.
Client SDG: 496617 GEL Work Order: 496617
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 N 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: jA.-1:J-~ Name: Theresa Austin
Date: 13 DEC 2019 Title: Group Leader
Page 16 of 25 SDG: 49661 7
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary Reoort Date: December 13, 2019
Energy Fuels Resources (USA), Inc. Page 1 of
225 Union Boulevard
Suite 600
Lakewood, Colorado
Contact: Ms. Kathy Weinel
Workorder: 496617
Parmname NOM Sample Q_ual C Units RPO% REC% Range Anlst Date Time
Rad Alpha Spec
3atch 1940453
QC1204435944 LCS
Thorium-232 0.000132 0.000129 uCi/kg 98.2 (75%-125%) HAKB 12/04/19 14:0
Uncertainty +/-3.70E-06
QC1204435945 LCSD
Thorium-232 0.000132 0.000135 uCi/kg 4.63 103 (0%-20%) 12/04/1914:0
Uncertainty +/-4.54E-06
QC1204435943 MB
Thorium-232 u 3.38E-07 uCi/kg 12/04/19 14:0
Uncertainty +/-2. 78E-07
3atch 1940454 ----
QC1204435947 LCS
Uranium-233/234 8.42E-05 uCi/kg HAKB 12/07/19 13:41
Uncertainty +/-1 .82E-06
Uranium-235/236 3.46E-06 uCi/kg
Uncertainty +/-4.16E-07
Uranium-238 6.78E-05 8.36E-05 uCi/kg 123 (75%-125%)
Uncertainty +/-l .82E-06
QC1204435948 LCSD
Uranium-233/234 8.32E-05 uCi/kg 1.17 12/07/19 13:41
Uncertainty +/-1.91 E-06
Uranium-235/236 4.60E-06 uCi/kg 28.3
Uncertainty +/-5.lOE-07
Uranium-238 6.78E-05 8.06E-05 uCi/kg 3.64 119 (0%-20%)
Uncertainty +/-1.88E-06
QC1204435946 MB
Uranium-233/234 u -l.29E-07 uCi/kg 12/05/19 17:2
Uncertainty +/-l .04E-07
Uranium-235/236 u -3.23E-14 uCi/kg
Uncertainty +/-1.53E-07
Page 23 of 25 SDG: 496617
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary
Workorder: 496617
Parmname
Rad Alpha Spec
NOM Sam le Qual Q~ Units RPD%
3atch 1940454
Uranium-238 U -2.35E-07
Uncertainty
Rad Gas Flow
3atch 1941984
QC1204439545 LCS
Total Radium 0.00448
Uncertainty
QC1204439546 LCSD
Total Radium 0.00448
Uncertainty
QCl204439542 MB
Total Radium u
Uncertainty
3atch 1941985
QC1204439548 LCS
Lead-210 0.00861
Uncertainty
QC 1204439549 LCSD
Lead-210 0.00861
Uncertainty
QC1204439547 MB
Lead-210 u
Uncertainty
Notes:
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 a1dol-condensation product
+/-1 .66E-07
0.00378
+/-4.11 E-05
0.00376
+/-4.15E-05
l.53E-06
+/-5.08£-07
0.00857
+/-0.000123
0.00839
+/-0.000121
2.JOE-06
+/-7.12£-06
uCi/kg
uCi/kg
uCi/kg 0.394
uCi/kg
uCi/kg
uCi/kg 2.07
uCi/kg
A
B
BD
C
D
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
Page 24 of25 SDG: 496617
REC%
Page 2 of
Date Time
HAKB 12/05/19 17:2
84.4 (75%-125%) LXB3 12/09/19 13:41
84 (0%-20%) 12/09/19 13 :41
12/09/19 19:3
99.6 (75%-125%) LXB3 12/11/1910:5
97.5 (0%-20%) 12/11/19 10:5
12/12/19 11:2'
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
Workorder:
f>armname
496617
F Estimated Value
NOM
H Analytical holding time was exceeded
QC Summary
QC Units
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
NIA RPD or %Recovery limits do not apply.
See case narrative
Analyte concentration is not detected above the detection limit
RPO%
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 or DER.
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
NI
ND
NJ
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
I\
h
QC Samples were not spiked with this compound
RPD of sample and duplicate evaluated using +I-RL. Concentrations are <5X the RL. Qualifier Not Applicable for Radiochemistry.
Preparation or preservation holding time was exceeded
Page 3 of
Date Time
NI 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.
/\ 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 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.
Page 25 of 25 SDG: 49661 7
ATTACHMENT G
STACK SAMPLE LABORATORY RESULTS
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
October 17, 2019
THIRD QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
VANADIUM DRYER STACK
VANADIUM PACKAGING STACK
BLANDING, UTAH
August 20-21, 2019
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 con:i,ply with procedures set forth in the Federal Register.
Mike McNamara .
Reviewer: ~ ~ -------'-----------
Date: /(} /;.; ); J: ------'---,7----7+---'-.__ ___ _
Dean Kitchen
Reviewer: R~:£.--
nate: ______ _;_;;_~__L_2-l-1_ ....... ....,_;__,7_;_
ii ,•:·
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 ................................................................................................................... I
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 Isokinetic Sampling ................................................................................................ 3
Source Operation
Process Control Devices Operation ..................................................................................... 5
Process Representativeness .................................................................................................. 5
Sampling and Analytical Procedures
Sampling Port Location ....................................................................................................... 6
Sampling Point Location ...................................................................................................... 6
Sampling Train Description ................................................................................................. 6
Sampling and Analytical Procedures ................................................................................... 7
Quality Assurance ................................................................................................................ 7
111
Table
I
II
III
IV
V
Figure
LIST OF TABLES
PAGE
Measured Radionuclide Emissions ...................................................................................... 3
Percent Isokinetic Sampling ................................................................................................ 4
Sampling Point Location ...................................................................................................... 6
Complete Results, Vanadium Dryer .................................................................. Appendix A
Complete Results, Vanadium Packaging .......................................................... Appendix A
LIST OF FIGURES
1 Facility Schematic Representation Vanadium Dryer ......................................... Appendix D
2 Facility Schematic Representation Vanadium Packaging ................................ Appendix D
3 Schematic of Method 5/114 Sampling Train ..................................................... Appendix E
lV
INTRODUCTION
Test Purpose
This test project was conducted to determine the total radionuclide emissions from the Vanadium
Dryer and the Vanadium Packaging exhaust stacks. Emissions are calculated in terms of pico
curies per dry standard cubic foot (pCi/dscf) and pico curies per hour (pCi/hr).
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Vanadium containing
material is processed and packed into barrels which are shipped to other facilities for additional
processing. A scrubber serves as the main emission control device for the vanadium dryer. A
baghouse serves as the control device for the vanadium packaging area.
Stack schematics are shown as Figures 1 and 2 in Appendix D.
Test Dates
Run 1 on the Vanadium Dryer and run 1 on the Vanadium Packaging exhausts were completed
August 20, 2019. The second test runs were completed August 21, 2019.
Pollutants Tested and Methods Applied
These tests were a determination of radionuclide emissions in accordance with EPA Method
5/114.
Test run filters and front wash residues were sent to Inter-Mountain Labs in Sheridan, Wyoming.
Test Participants
Energy Fuels
TETCO
Logan Shumway
Mike McNamara
Reed Kitchen
1
Steve Snyder
Doug Olsen
Deviations from EPA Methods
None.
Quality Assurance
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 RESU LTS
Emission Results
Table I presents the findings of the test in Curies per dry standard cubic foot. Tables IV and Vin
Appendix A have more detailed information.
Table I. Measured Radionuclide Emissions
Run# Vanadium Dryer Vanadium Packaging
pCi/dscf pCi/hr pCi/dscf pCi/hr
1 0.998 4.417E+5 0.317 4.802E+4
2 0.165 7.358E+04 0.324 5.229E+04
AVE 0.576 2.5765E+5 0.320 5.015E+04
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Production data was retained by Energy Fuels
Resources.
Description of Collected Samples
The test filters for the Vanadium Dryer were heavily covered with a dull, lime green colored
particulate. The front washes were clear in appearance.
The test filters for the Vanadium Packaging exhaust were moderately covered with Dark Brown
colored particulate matter. The front washes were brown in appearance.
Discussion of Errors or Irregularities
None
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.
3
T bl II P a e . ercen ti ki f s so ne 1c amp lin lt!
Run# Vanadium Dryer Vanadium Packaging
1 101 101
2 101 101
4
SOURCE OPERATION
Process Control Devices Operation
All process control devices were operated normally. Recorded scrubber pressure drop and water
flow rate readings are found in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND ANALYTICAL PROCEDURES
Sampling Port Location
The inside diameter of the Vanadium Dryer exhaust stack was 36 inches. Two, four-inch
diameter sample port were located 9.67 diameters (29 feet) downstream from the last disturbance
and 3.33 diameters (10 feet) upstream from the next disturbance. Figure 1 in Appendix Dis a
schematic of the stack.
The inside diameter of the Vanadium Packaging exhaust stack was 29.5 inches. Two, four-inch
diameter sample ports were located 3.29 diameters (9 inches) downstream from the last
disturbance and more than 6.78 diameters (200 inches) upstream from the last 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 was marked and identified with a wrapping of glass tape and numbered.
These points were determined by measuring the distance from the inside wall.
Sample Distance From the Inside Wall inches
Point Vanadium D er Vanadium Packa
1 1.58 1.00
2 5.26 1.98
3 10.66 3.48
4 25.34 5.22
5 30.74 7.38
6 34.42 10.50
7 19.00
8 22.13
9 24.28
10 26.02
11 27.52
12 28.50
Sampling Train Description
To determine the emission rates for these stacks, 40 CFR 60, Appendix A, Methods 1-5/114 were
followed.
6
All sampling trains were made of inert materials, (Teflon, stainless steel, and glass) to prevent
interference of the sampled gas. The sample consoles used to conduct Methods 1-5/114 were
constructed to meet the specifications outlined in the CPR. The temperature sensors were K-type
thermocouples. Heater, vacuum, and pitot line connections were designed to be interchangeable
with all units used by the tester. A 316 stainless steel probe liner was used for the tests. Figure 3
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 CPR 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
APPENDICES
A: Complete Res~lts 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, Vanadium Dyer
Table V Complete Results, Vanadium Packaging
Nomenclature
Sample Equations
A
TABLE IV
COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UT AH
VANADIUM DRYER
dryer
Symbol DescriEtion Dimensions Run#l Run#2
Date 8/20/19 8/21/19
Filter# 7204 7206
Begin Time Test Began 7:42 7:46
End Time Test Ended 15:45 15:47
Pbm Meter Barometric Pressure In. Hg. Abs 25.50 25.50
11H Orifice Pressure Drop In. H10 1.119 1.103
y Meter Calibration Y Factor dimensionless 1.007 1.007
Vrn Volume Gas Sampled--Meter Conditions cf 322.904 319.689
Tm Avg Meter Temperature "F 94.6 92.4
'V11P Sq Root Velocity Head Root In. H20 0.3677 0.3654
Wtwc Weight Water Collected Grams 359.2 328.5
Tt Duration of Test Minutes 480 480
cp Pitot Tube Coefficient Dimensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.3080 0.3080
CO2 Volume% Carbon Dioxide Percent 0.00 0.00
02 Volume% Oxygen Percent 20.00 20.00
N2&CO Volume% Nitrogen and Carbon Monoxide Percent 80.00 80.00
Vmstd Volume Gas Sampled (Standard) dscf 264.689 263.085
Vw Volume Water Vapor scf 16.936 15.489
Bws (measured) Fraction H20 in Stack Gas (Measured) Fraction 0.0601 0.0556
Bws (saturated) Fraction HP in Stack Gas (Saturated) Fraction 0.0779 0.0767
Bws Fraction H20 in Stack Gas * Fraction 0.0601 0.0556
xd Fraction of Dry Gas Fraction 0.940 0.944
Md Molecular Wt. Dry Gas lb/lbmol 28.80 28.80
Ms Molecular Wt. Stack Gas lb/lbmol 28.15 28.20
%1 Percent lsokinetic Percent 101.1 100.7 AVG
Ts Avg Stack Temperature •F 100.8 100.3 100.6
As Stack Cross Sectional Area Sq. Ft. 7.069 7.069
Pa Stack Static Pressure In. H10 -0.120 -0.120
PbP Sample Port Barometric Pressure In. Hg. Abs 25.43 25.43
Ps Stack Pressure In. Hg. Abs 25.421 25.421
Qs Stack Gas Volumetric Flow Rate (Std) dscfm 7.45E+03 7.44E+03 7.45E+03
Qa Stack Gas Volumetric Flow Rate (Actual) cfm 9.91E+03 9.84E+03 9.88E+o3
Vs Velocity of Stack Gas fpm 1.40E+03 l .39E+03 l.40E+o3
Curies Radionuclides per sample pCi 261.44 43.37
Radionuclides per blank pCi 0.00 0.00
Net Curies Net Radionuclides per sample pCi 261.44 43.37
Crad Concentration of Radionuclides pCi/dscf 0.988 0.165 0.576
ERrad Emission Rate of Radionuclides pCi/hr 4.417£+05 7.358£+04 2.5765E+OS
TABLEV
COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UTAH
V ANDIUM PACKAGING
Symbol DescriEtion Dimensions Run#l Run#2
Date 8/20/19 8/21/19
Filter# 7205 7207
Begin Time Test Began 7:33 7:32
End Time Test Ended 15:42 15:34
Pbm Meter Barometric Pressure In. Hg. Abs 24.50 24.50
L\.H Orifice Pressure Drop In. HiO 0.669 0.767
y Meter Calibration Y Factor dimensionless 0.996 0.996
Vm Volume Gas Sampled--Meter Conditions cf 272.483 289.061
Tm Avg Meter Temperature "F 88.6 87.5
'1L\.P Sq Root Velocity Head Root ln. HP 0.1801 0.1921
Wtwc Weight Water Collected Grams 22.8 34.4
Tt Duration of Test Minutes 480 480
CP Pitot Tube Coefficient Dimensionless 0.84 0.84
Do Nozzle Diameter Inches 0.3900 0.3900
CO2 Volume% Carbon Dioxide Percent 0.00 0.00
02 Volume% Oxygen Percent 20.90 20.90
N 2 &CO Volume% Nitrogen and Carbon Monoxide Percent 79.10 79.10
Vmstd Volume Gas Sampled (Standard) dscf 214.315 227.878
Vw Volume Water Vapor scf 1.075 1.622
Bws (measured) Fraction H,O in Stack Gas (Measured) Fraction 0.005 0.007
Bws (saturated) Fraction H~O in Stack Gas (Saturated) Fraction 0.072 0.076
Bws Fraction H,O in Stack Gas * Fraction 0.005 0.007
xd Fraction of Dry Gas Fraction 0.995 0.993
Md Molecular Wt. Dry Gas lb/lbmol 28.84 28.84
Ms Molecular Wt. Stack Gas lb/lbmol 28.78 28.76
%I Percent Isokinetic Percent 101.1 101.l AVG
Ts Avg Stack Temperature "F 97.0 98.6 97.8
As Stack Cross Sectional Area Sq. Ft. 4.746 4.746
Pa Stack Static Pressure In. H20 -0.020 -0.020
PbP Sample Port Barometric Pressure In. Hg. Abs 24.48 24.48
Ps Stack Pressure ln Hg. Abs 24.479 24.479
Os Stack Gas Volumetric Flow Rate (Std) dscfin 2.53E+03 2.69E+03 2.61E+03
Q. Stack Gas Volumetric Flow Rate (Actual) cfin 3.27E+03 3.50E+03 3.39E+03
vs Velocity of Stack Gas 1pm 6.90E+02 7.37E+02 7.14E+02
Curies Radionuclides per sample pCi 67.87 73.90
Radionuclides per blank pCi 0.00 0.00
Net Curies Net Radionuclides per sample pCi 67.87 73.90
Crad Concentration of Radionuclides pCi/dscf 0.317 0.324 0.320
ERrad Emission Rate of Radionuclides pCi/hr 4.802E+04 5.229E+04 5.0I5E+04
Method 5 Nomenclature
%I = percent isokinetic, percent
As= stack cross-sectional area (ft3)
AS~P = see '1~P
Btu= unit heat value (British thermal unit)
Bws = fraction of water in stack gas
Cr= concentration of particulate matter, front half (gr/dscf,lb/dscf, etc.)
Cmetal = concentration of metals (ppm, µg!ft3, etc.) atomic symbol replaces "metal"
CO2 = percent carbon dioxide in the stack gas
CP = pitot tube coefficient (0.84)
C x (avg) = species symbol replaces x .
C x (corr) = actual gas concentration corrected to required percent 0 2
~H = orifice pressure drop (inches H20)
~@ = orifice pressure (inches H20)
Dn = nozzle diameter (inches)
Dn des= calculated desired nozzle size (inches)
~p = stack flow pressure differential (inches H20)
Ds = diameter of the stack (feet)
EA = percent excess air
ERF = emission rate of front half particulate (lb/hr)
ERmmBtu = emission rate per mmBtu or ton of fuel etc.
ERx = emission rate of compound which replaces x
k-fact = multiplier of test point ~p to determine test point ~H
L = length ofrectangular stack (inches)
mBtu = thousand Btu
Ma = molecular weight of stack gas, dry basis (lb/lb-mol)
MF= mass of particulate on filter (mg)
MFP = mass of particulate matter on filter and probe (mg)
mmBtu = million Btu
Mp = mass of particulate matter in probe (mg)
Ms= molecular weight of stack gas, wet basis (g/gmol)
N2 = percent nitrogen in the stack gas
0 2 = percent oxygen in the stack gas
'1~P = average of the square roots of ~p (may also be referred to as AS~P)
Pbm = absolute barometric pressure at the dry gas meter (inches Hg)
PbP = absolute barometric pressure at the sample location (inches Hg)
PG= stack static pressure (inches H20)
P s = absolute stack pressure (inches Hg)
Pstd = absolute pressure at standard conditions (29.92 inches Hg.)
8 = time of test (minutes)
Oa = stack gas volumetric flow rate (acfm)
Os = stack gas volumetric flow rate ( dscfm)
Ow= wet stack gas std. volumetric flow (ft3/min, wscfm)
Tm = meter temperature (°F)
Ts = stack temperature (°F)
Method 5 Nomenclature
Tstd = absolute temperature at standard conditions (528°R)
Tt = see 0
Vm = sample volume (ft3) at meter conditions
Vffisid = volume standard (dscf), sample volume adjusted to 68°F and 29.92 inches Hg.
V5 = velocity of stack gas (fpm)
V w = volume water vapor (scf) at 68°F and 29.92 inches Hg.
W = Width ofrectangular stack (inches)
Wtwc = weight of the condensed water collected (grams)
Xd = fraction of dry gas
Y = meter calibration Y-factor (dimensionless)
•
Method 5 Sample Equations
%1 = Vlllsta •(Ts+ 460) • 1039 I (8 •Vs• Ps • Xa • D/)
2 As= (Ds / 4) • 7t
Bws = V w / (Vlllstd +V w)
Cr= M1v • 0.01543 I V1I1s1a
Cx (corr)= Cx (avg)• (20.9 -desired %02) I (20.9 -actual %02)
Deq = 2 • L • W / (L + W)
Dnaes = ...f {0.0269 • (Pbm + 0.0735) /[(Tm+ 460) • CP • Xa •,/[(Ts+ 460) •Ms)/ (Ps • LlP)]}
EA= (%02 -0.5 %CO) I [0.264 %N2 -(%02 -0.5 %CO)]
ERF = Cr• Qs • 0.00857
ERmmBtu = ERx I (rnmBtu I hr)
K-fact = 846.72 • Dn4 • LlH@ • c/ • x/ •Ma• PS• (Tm+ 460) /[Ms• (Ts+ 460) • (Pbm + LlH I 13.6)]
Ma = CO2 • 0.44 + 0 2 • 0.32 + N2 •0.28
Ms= (Ma• Xa) + (18 • Bws)
Ps = PbP +(Po/ 13.6)
Qa =Vs• As
Q5 = Qa • Xd • Ps • Tsta I [(Ts+ 460) • Psid]
Qw= Qsl xd
VIngtd = Vm • Y • Tstd • (Pbm + LlH I 13.6) I [Pstd •(Tm+ 460)]
Vs= 85.49 • 60 • Cp • ...ftlP • ...J [(Ts+ 460) I (Ps • Ms)]
Vw = Wtwc • 0.04715
Xd = 1 -Bws
.. . . " .
..
Vanadium o :ryer · ..
Main Stack
'. .
. . . . . . .
. ' . .
.. . . . ..'\ . . . . . .
. ' . ~ .
. .
. . . .
. : ..
Preli~ 6 pts blank
Facility Energy Fuels
Stack Identification Vanadium -Dryer
Date 'b(24,( 1 j
l .
Barometric Pressare
B Pbm -zf_.?O iriHg Pbp "2, S' · <-c 3 . inHg
N 0 Static Pressure (P 0) ... o, 1'2.--inH20
Estimated Moistw-e (Bw,) 5-9 %
Sample Height from Ground 70' feet
A
Comments:
Stack Dia. 36 Reference: 0
Ports are 10' Upstream from next disturbar1ce
Ports are 29' Downstream from last disturbance
traverse Percent Distance From: Ports· ..
Point Diameter ID R,eference A B C D E F
1 4.4 1.58 1.58 11 jl .
2 14.6 5.26 5.26 10 q ..
3 29.6 10.66 10.66 ~ '1
4 70.4 25.34 25.34 5 s
5 85.4 30;74 30.74 i 9
95.6 34.42 34.42 ti' q, .. 6
'
'•
-
'
Averages:
Ts -------LFlow ----
ti.P ../AP ----------
~
' ,
<; l, <"[ Fiold O.b '"'" '1-,tOfTETCO /4--
Fitter 1 Sample Box __ _
Plant: Energy f uelsi ,
Date: ~ ./ z,, c> 11'1
Location: v~
Operator:_l2::5...;;,. __ ...:..... _______ _
Traverse 11 Time
l. Point
DGM AP II AH r~ H,Ol
Desired I Actual
DGM T cmp_(T,.) Temperatures C'I)
4 1
1
.?.
2
~
3 ,z.. 4
4
5 ·, 2
6
6 ~c=
1 II I I:'-{$,
'---i _ I _ ,,· 7~1a .11------'-I ~I .... 1 I IC ·1 -,;:1 -'I ... I
{)..,1 --ll . ·-.,=i ~ .. ,.11 .... , .' -, ll------:--1 -1-,a,----il , ... >J I I , ,. l ... ~ l, ,,. II ~ -l , I
1
2 ~ ---11 I -• ,,II :: A . ;: .. 'r' n--::-;:,::---11 ,· _,,: I , ~ .a! 11--<.-r-11 ; L i t· ~ _,,·1, -1 H ~, ,JI ..--& II -·:.....t: 1., Cl 2
~
3
~ 4
.1
5
5 1--I "-' "' 'I ' I --I • /( II ' ., I r" I I . , ., ,. I < . .,\ " . " < ~I .1 · h ,?=I '>-' II :! I ; ~-""'-,n ~ > • < r .1 -il
6
6
Total
Average l D0·'i
Additional (Extra) Leak Check Information
DGM before-Leak Check Vac ("Hg) Rate (ft3/min) DGM After Leak Check Vac ("Hg)
'
' .
'(. } Page __ · _of~ Run# __
i ·o N
A
Stack Diameter 36" Port Reference __ O_" __
Ports are
Ports are ·
~ Upstream from next disturbance
29' , Down~tream from last disturbance
Assumed Moisture {;, 5-9 %
Probe > ~ . Cp~
Nozzle Calibration y' ~
. ~ 0 r' . ~ o-y -5 i) • 'S 0
Avg D0 • 3, t, Y inches. ---
A:R:lbieot Afr C -C) 5-
Barometric ~~, ~S-Sq)
Pbm ~ (j · ~ ,/~g~ ~ J:;i. iJ Pb,, ··Cb , '1n g
.p,, -,{Z inH20
Leak Check: Pre
ll'tmin O ·90 2-
vac in Hg 20f)
Pitot Rate
InH,O
O•O
941
Post
() ~gt) s
~
t). {)
?z .e(
.3.~ 1. . '2'......
Water Collected t;~j: V'
Time Sampled · r{ ~ 0 g .
Review -~ mm
K= @Tm
K= @).Tm
Rate (ft3/min).
.,
_/ f ' ~ Field Data Sheet·
Plant Energy Fuels r )
Date: Fj-tf ~~ ·
Time Traverse I I
Point II Clock I Min (8)
DGM
(ft')
AP
(iuH:<))
... ,r
Filter 717-IJ wr,,co A --Sample Box
_: ... ~ ::.
,I' ..... -· ;"J '• ... .. .• . . '' .. ~: .. : •• !'-,.,
"' I •. ," ; ~ •
:Page ( of_l Rwi # 2--~---
wcaiion: Vanadi~
Operator: .
f
11 AH ~· H,~l II Vacuum 11 . Tempera.tu= (FJ I DOM Temp (T ml I Probe I Oven I CPM Filter I Elf. Out In Desired I Actual
i ·o
A
N
S1ack Diameter~ Port Reference __ O_"
2
2
3
3
5
6
6
'{ ' . 1
2
7 2
3
3
{I 4 .
4 ,.
5 • II•
« -L1 1 · -11 v -' • ·r1~11 J, '{ ·1 • -,-· 1~1 · -.-c 1 ..., ( u ' .. £.1 "' .... -1 ..... • 11 • :r 1 • -• . ~ -i.JA .• I ,~ ... I , ~ " ·-.. • ~ • -• ,,· -. .,,,, ... E ; .. A .,_.-/! • .A ..., 6
6
Total
Ayeia&,e
Additional· (Extra)· Leak Chee!! Information
DGM before Leak Check _Vac(''Hg) ·Rate (ft3imin) DGM A~; Leak Check Vac ("Hg}
··{·
J'
Ports are
Pons are
!Q'.__ Upstream from_ next disturbance
29' Downstream from last disturbaoc.e
Assumed Moisture 5-9 %
Probe sr ~ cp~
No:qlj: ~oration ·.
• ~ ll'Y ,3i:,r-. ,56 r · . So~
Avg D0 ~ jc) >"• inches
aaifBag . F -:-t"'. ~
Console.;..~..;..-·,__=-
:·Factor f ·, ~_:f--·
6Ho J~ c:f.:l ~20 .
Leak Check:
f\3/min
vacin Hg
Pir.otlub,
lnH2Q
Barometric Pressll{es
.Pbm f'lS° . .Jp · inHg
Pb• 'l §" . l 5 in Hg
Pa...,. 0 ' f Z..-in H20
Pre ·~ · (!)~o5 · a.a o3 .
2=..l_ _,_!-=-Z-
0 · '0 0 , '()
°l -:r '1: $"
. .-/
Water Collected g
~
1'1
Time Sampled min
Review
K= @Tm.
K= @T,.
Rate (~3/min)
~.f ;~
. ... . -
. .
Vanadium Packaging
Baghouse
Prelim 6 pts blank
Facility Energy Fuels
Stack. Identification Vanadium Packaging·Baghouse
Date Blzo l,ci
r ·Barometric Pressure
A Pbm '2.Y,[o in Hg PbP '24,"I~ in Hg
N Bo Static Pressure (P 0) -,!V'l.D inH20
Estimated Moisture (Bw.) 1 %
Sample Height from Ground 25' feet
Comments:
' Stack Dia 29.5 Reference: 0
Ports ate >250" Upstream from next disturbance
Ports ate 97" Downstream from last disturbance .
Traverse Percent Distance From: Ports ;
Point Diameter ID Reference A B C .D E .F
1 2.1 1.00. 1.00
2 6.7 1.98 1.98
3 11.8 3.48 3.48
4 17.7 5.22 5.22 .·
5 25.0 7.38 7.38 .
6 35.6 10.50 10.50
7 64.4 19.00 19.00 .. --•'
8 75.0 22.13 . 22.13 ..
·.
9 82.3 24.28 24.28
10 . 88.2 26.02 26.02
11 93.3 27.52 27.52
12 97.9 28.50 28.50 ..
Averages:
Ts . LFlow --------
&> ___ _ ~& ----
KEY=> ... IT_s ___ Af>=-· _· L_· _Fl_m_..wl
'
5 /{ I 'i Field pata Sheet
A
(). t
Plant: Energy Fuels
Date: 'o / Z-0 ( I Cf
Traveme Time
Poul! Clock Min (8)
1 1'.33 0
2 w
"3 r./0
4 (.,D
6 80
6 /oO
7 2.-0
8 l<(O
9 lC..O
10 1eci
11 2.oO
12 Zzo
Z'f{)
1 1\: '11.. No .
2 i.i,o
3 i~o
4 300
6 320
6 3't0
7 '31o0
8 3~
9 ~oO
10 lf-z.O
11 "11-{o
12' 41,0
'(','"11 '-ilbO
DOM
·ctn
012,l'-U
.s'o2.-3W
1,2. ,ss
L(6$ .ooO
q,~ '04'{
'it.S. l{.f'
·~31.. o'e,o
i.t·\7·. \{'i)
i.\5Qi. 040
"'f'1 O • S'~ f"
'i~7;2YO
L.{~:s. 'i <o
l5oS. C:,t'2-
I. Ji"' 5 . ,;-;t z. ·
51 S -1QO
5"25-'1~0
53(... ,q,...,
~~-1.21°".
55B-57o
"C..'LS2.0
s'oo. "4o
5':i3 l3-~
t..oS.T!>o
~I?> .,1-0 .
b32.. Ct. '=1--
C.'(<{.~'\ '+-
::{
AP AH r .. H,Ol
(i:mff20) Desired Actual
,oi, ,57-·~'2-,oi-r .sz. ,fl,.
,n'3o • (pl , IA(
.030 .(,,\ • {pl
,o~-< .11.. •11-
.030 . "''Z. ,(ol-
,c,)o I(,)_ I C.,2..
10';{ ,11-•12..
.o3:('.' , 17.-112-
,03( ,72-172-
,93.5 •1'2.. ,,2.
,03( •12. ,.., 'l..
• o'Z-?' ·,SI .~,
·~1.'I"' ,fl ,-{ i
,o~o .,, .. (.(
.•o-Z,1°" • 5 l . c I
,030 'fo I .~,
103-o .• C.. I . G, I
,0'30 • lo l . le; • I;,, I
•0'10· ,Al .~ I
: ,.,,c.ln .tt ·Be
,~-t( ,,(( 'i,. ~~1...
,o'-(i ., i-. -qi,.
'. o"{o .~\ '. -il . ..
1 ,z.0.(' TETCO R
Filter Sample Box_V __
Vao1111m
[mil&)
2..
'L
2-
"2..
1.-
2...
z..
'J
l.
1
2.
1-
'2..
)...
1-
--z_
')..
~
1-.
-z.,.
2.
1..
'2..
~
Location: Vanadium Packaging Baghouse
Operator: M , I\::) ~c,la,. r'.'1 o. r c---.
Temperatures m
Stack(TJ Probe ProboOut Filter Effluent
~3 2c:11.{ 2 'itJ 240 ~\
f;t..( 1-'i'Z.. Z<,(3 2'{3 tj l{
B«, 2.tf1 l'h,., Z-'t1 '{ (p
85 1'"10 Z.3~ ZJ~ '5 l
~9 z. '1 Ii> Z1'b ?.'"{~ 5J-
'OCl 2fl 2.ttf" Z.'1'1 5<t
~ I 2.1.!0 ZJ~ 2.3~ 5'i
Cjz. 2{D z.~o Z.'10 .55
Cf5 251 2 '12.. '2..c.rz~ 5@.
91.:. 2<.f+ Z.ol ") (" \ 58'
q~ 'Z.'(Q Z<t+ Z.'i "f scr
qq l91 2.42... z~z..; l,o
., -~ /U PIM.,
101 l'f'i 2 f'I Z!'-f ~o
c.'\8 l. 'f"=1 -Z.3+-Bt-'. 5n
lot '2.L{L. ,,Sc; Z,C::&; ~i.
'\.p1.... '2.'I 't 'l.. 'i l '2."11 51.{
l'~"\ 2{\ 2{? -i1a I.\ 9i
1"'3 2.'l~ 2,.)9, ..Z...38 4i"l .
toe; -z.•-rz.. .2.c.1:z. "2..1.f 'l.. 5'-1
I~'{ Z.'1 Cf '1.1 C, t,~ l{'{
IOI.. .2-'tL 7Jb · tlo ~B
j.,'.(. 1,-(\ .V·~~ ·. :z. tf'::r ~'{
It><.:.· 2;'h '2..4(,, 2-'{ ¥" 'H,
I~ Ip l '1'-i i), t-39 'if'
Total 1.1'1.l{t)J ..;1.\-~t:,o · ... fl,,~l..o ·
. . . ,/ ./ i~~i ·/
., " ,\io\ • ~l,<\1.. C\1;b A~ ·:..:.>·
-----------·-------
DGM before leak Check Vac("Hg) Rate (ft~lmln) DGM After Leak Check
DGMTcmp(T.,)
Out 'in
13--~-
18 ~o eo ~o go oll
lq !lo
1 <t . 12..
So '~· . ao ctD
5·1 q1
~2.. ~3
R'Z q_)
Bi 'lr
St{ ~5
03 C\2..
8fo 95
R~ q~
9B q4-
'e? 'T~
~'? q~
Sq. ·qcy
·'lo 1 ... 1
'\ l ·~o3
ei l /02,
4t /0'2-·
Page _l_or_\_ Run#_\_
A i Bo N
Stack Diameter 29.5" Port R¢ference __Q'.'.
Ports an:. ·> 250" U~stream from next disturba,nce
·-J Potts are . .-97" ;: Downstream from.~ dislmbance
< Assumed Mois(ure , 1'~''-%
Probe J,6 (, -t. Cp 0.84 : -
N07:Zie Calibration
~ '!'lo ,39o .J<reJ
Avg D0 • J C,t> inches
Gas Bag Ambient Air
Console (,. ---Y-Factor ,'fi'Co
AH@_/,5"<.((,, inH20
Barometric Pressures
Pb., 2.c{ 6,0 inHg
Pb, 'Z.4, 'f %° in Hg
Pc. .-• oZO inH20
Leak Check: Pre
c?tmm l>· o0'.2.-
vac inlig zo,0
Piii>ll!Me Q.O
Post
€J·oOl
!2.:.Q
--12..:..2
rna.o ~~ ,vfo
.-z,.(o 2-z.. V Water Collected -_______ g
w-min Time Sampled _J.{~ll
Review ~
•.'. ....
~Z.5S / -9~-<o . K =
K=
@T ..
@T.,
Vac (nHg) Rate (ft3iminl
( ,c.,lo\. 6w(el @
551 Ldj
I I I \
5( ( ( t.(,_ Field Data Sheet
PlllDt: E~ Fuels
Date: · 1.\ l ( <\.
Traveme Time
PJlllll Clock ~it{S)
rs;. t).. 1 1'.'2,'2.. . 0-
2 ·w
3 'le
4 C:iO
5 eo
6 loo
7 120
8 l'-40
9 ,~o
10 1110
11 2,.oO
12 i.z.:o
'i:11.· ZlfO
r, f> 1 ·I\ ',3<-f 2YO
2 2"'0
3 Z.00
4 3&0
5 '31.(\)
6 3'l0
7 '%0
·a J!o
9 '(oO
10 'tz,o
11 'f<W
12 '((.0
'e:;: '.W t.t8D
DGM
rm
f:>L{.f ., 1..0
L> 5 .c:. qi.<
Ioli.. .1~j .
£.ll; S7o
lc,Bq.-z.t<
ifOO.-l'lO
112. 010
"1'Z-'-f. L{t{:(
73, -~00
7'-l't, ~<tO
1 "2 . <,,2-o
11s. sqo ,ee,. ll P.
,S'i'.. IIR
1,cr. ,gi:;-
ai.a. s:30 ea. i-i'O
831.1~0
io'{ s ;. 5oi;
8S;-.~o0
tr<!). 1-1.'t 0
882,501
S"\5~ \,'i'q
q,,~ }~('
ci1. ~. (.13 0
C\..$lrt j~c
t,.P t,.H (~H,O)
(iaH10) Desm"ill . , Actual
,o30 . "z.. • e,; 'Z...
•030 • to7..." . c;-~
.o3o • G.2., ' I (.2..
'03{ •+'L ,·:n-
,o3o .~~ • (., '2-,;
,o3{ :-q'Z.. , "}"2.
,o'-10 .S:3 -. S),
·"'10 .~)· .. ~~-
•e"f,o . 9.i:i . 9i3
• (l"f :( ,q3 .• Cf.7>
. • e<-\{ ·"'3 . • cf2>
'tl)I.{() . ' • ~-·t,:" "'; ~'1 '
,o'!.< ,1-z;.. ,,'2;..
..... ~ ... . c.. 'Z,. r G, Z,...
. 10~0 -:-(..7_ ,"z
.--03-5 YVZ.. t"JZ.
,<!>~5 .. , z. •"TL
,...el{' ' . viz.;. t17
.d() '. • fl;, ,e.3
..-o':t,O . ;,-fo} ,s.:=;
.-e«<> ' .. g~ ~41'?.
.. £)({.{ .. (\~ .-'l)
_rb"t., • '{3 ,cu
-C>~b .• 'o3 -~3
"
TETCO
Filter 12!' '"=,.: Sample Box~
v-
CinHs)
1,.
2.
2-
L-
"2-
2..
j_· .
l
l. ·. z.
.2..
~ 1--
2...
2.
1.;
'l-
2..
·2-
2-
1.
'2-
2
'2-.
"2-..
Loc.ation: Vanadium Packaging Baghouse
Operator: ~\ ·"'1. ~c,.Jc>-
Temperatures ('F)
Stack(T.) Probe Probe Out Filter Effluent
8+ 2'18 Z..3o '2.'31'1 (,;,
se l{I 'Z..31-'2.;'Yr so
90 2'{6 .2.'(~ ":z..<t e, "19
~l "2'{{ zc..13 Z'\j .53
q3 1.'i't 2<i.o Z,4() .si
. "1 "i 2.'1(' 2.,{2.,. Z,{J .5q -
'H 2C( fl z (I') -z.,r, S'i .
q:'.f-. 2ro Z.'-1 L 'Z. <-( l 53 ·
.. q:J,--, 7.•fJ--2~ -z,3~ 5 :f---
~ (? l'iO Z,c;~ Z'f'o s~--
.·ci.~ 2C{( 2.,, 2S"2-1,0
q 'l 2.t.{ Cp ·z.~~ z.39 . (.o
IE>O 2.5 I 25(.j 1,{4 C..o ..
loo Z>fl -4'i'l.. 2.~'2.. 5\
tol 2. 'i °' 'Z.fl 'Z, -{ \ 5l
lo2-2..'i<J 25Q 1.{o 53
102.. 2 'i1>i 1.L{o z.-to 5'-1
lot{ 'Z, '{.,. 2.. '1. t ?41 5(..
Ca'-l 1'-i·) Z35 -Z,3A Sl
lo~ . 7_50 Z.4-Z.. in 4( ... ,~s )_,{I z:y; Z]'f Li I.{
I<' .c; Z<i1 zt.t9i 'Z.Cf'O L(~
105 '2'-n 2'1-f 2.'i? 4~
lo5 2.,fo Z, ~ €1 z:~e '{~
Total -z. Q;q ,o ~l. "' t.\-. (,lo)./ \'e, l{eO v l.?,~ 1'. /
Aver~ . ,/_ ,\'\1--\ .11o1-98,(o
Additional iE.xir.l Leak Check lnfonnation
'
DGRII before Leak Check Vac("Hg) Rate (trfmin) DGM After Leak Cheek
DGMTemp(T.J
Out In
TZ.. 10
ll.. 1~.
73 8{
1t.( _P;l.
1Co R11
1:r~ . 8'1
.'1 f' . 8-:J-
-~t) : -Sf .· 9-1 ·"\ I
~2 qz.
83 ~.,· .
'o'f q,1_..
8~ cri:.
B-~ q"
?,<., q4i
8-:J--q3
p_(_ CJA
~'8 ~
8'1 ere,·
ero lol
CJ( 103
Cf2,. 103
9" l 103
q{ ,~;
Page_\_or_i_ RUD#~
i A Bo N
:,,
Stack Diameter 29.5" Port Refetince ___.1
Ports are
Ports are
> 250"-::.. Upstream from next disturban~
-S7" Downstream from last distwb~ce
Assumed Moisture 1 % Pr* 30 f, -2, Cp · 0.84
Neitiii~ Calibration ~
, 390 ·3~ ·3~0 ,3<t1'
AvgD. '3<t0 inches
Gas Bag Ambient Air .
Console__.',>~-
Y·F~or .q~t,
Al:!@ l,fL.( I,., inH20
Barometric Pressures
Pb,. 1 t-1,{ 0 in Hg
PbP 24;"10 in.Hg
P -,o-z.O inH20
Leak Check: Pre
113/min O -00? .• :
wcinHg~
PitotRale O• 0
InH,O • ,z_j
-~
E). 00~
1&2.!.Q,0
e-0 ,Vt ..
Water Collected 3 ~ · i · g
Time Sampled 'i g·o . -mm
'''!'_,.:·
i,:
t,14"1· .,/' Review ;~
K=l9.J(ll{@Tm 38
(b1 .5
Vac ("Hg) Rate (tt3/mln}
K=· -'@T,,,
N,J,i.'o.tf 01-eiw<e!
~ SSt 1..\tS
. .u-t1 '
• .. • : & . . . .
I • • '"
. .
. Vanadium Dryer
' .
Main Stack
. . .
'
'
• I
Plant £~11 t\ J (J :..,._/\ Location __________ .a/~_~ __ .,__/_" ____ _
Analytical Method ____________ _
Date O / _;_.·
TestNo.~
Gw R~ No.. €;6§ )-
Ambient Temp ·
Operator ·
Date ~tv{
Test No. --=v---
Gas Bag No. ---=r::--f/-,-,{""-
Ambient Temp __ . flJ!-t-t=-D-. -·-
(?perator __ ~..__,,_ __
Date -----TestNo. -----
Gas Bag No.-----
Ambient Temp ____ _
Operator ____ _
Gas
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Readin ).
N2 (Net is I 00 Minus
Actual 0 2 Reading).
Gas
0 2 (Net is Actual 02
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 02 Reading).
Gas
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading . . .
N2 (Net is 100 Minus
Actual 0 2 Reading).
RUN
1 . . 2
Actual Ner Actual Net
Reading Reading
Actual
Reading
o·u
zo
Actual
Reading
Net
o~o
2 o·o.
Nei
RUN
2
Actual Net
Reading
O,cJ 6·U
RUN
2
Actual. Net
Reading
t 0 2 was determined using a gas analyzer
CO is not rneasurfd, as it has the same rnole.cular w~ight as N2
l
Actual
Reading
Actual
Reading
C) •C)
3
3
3
Net
c), 0
Ne1
C). ()
2o· ()
Ac tu.al Nel
Reading
Average
Net
Volume
Average
Net
Volume
O·O
1-D-,
Average
Net
Volume
. ' ..
. .
, . .
· Vanadium Packag-ing ·
' ..
. . .
Baghouse ... ·
·. . ..
. . . .. . .
' . ' . . . .. . . . .
. . . . .
'! Method 5
Facility: En.ei'Q,>! Fuel·!! I I • I Date;• ·Bfi:o/19.
Stacklde~tifi~~i.Oll= Vnnadluni .Brughom;e Method: S/114 _
1MPINGf'..M
Run: ( Sample Box: B ------
Filter Nwnber:
,.J,,
lminger Number · I ,.,4,,, I · I ,,j.,,
.Ipitial Yoluine oftiquid (H:20) iii impingers, (n:il)
• I -.
. ~
Total (g) 22.~
......
\.. .. 'o /zJ (Jo.j
lW!IN.GUS 7-.i3 Run: Sample Box: . -
Filter Nwnber: llQptnger.Nunaber . -. Initials
) .2 ~ ·4 ...5. \ jj_
T?..0 '.:1-Initial Volume ofli.quid:(H20) in impingers, (ml)
100 -100 . .. SCI . , ' ' ' • .., .
~ Cl\.$ Final (g) ~8,-:z_ -uY',O .: '61q. <,. 9'3 4, l Ai\~
Initial (g) ' raz. 9 &89·, 9 '1,/t.f '+-qo<f. '> .· . .f. \ {S+--Q..vf'\ ,,-
Net(g) .. V·L 1--1.C-/. \ s ,1.. zq .. ti .. : .
I Total (g) 3 'i. (..(
:~:.,.,,
"•:.-;
~
JMPJNGERS
Run: . Sample Box: ·
Filter Number: 1mp1~,ter l'!UD1'1CJ.' Initials
1 . l 3 4 ·'_S 1, ' Initial Volume ~fliquid (H:20) in impingers,·(ml) ..
mo 100 . SG .,'\\,.'J.",.:S
I '' l . ._, -·'
Final (g)
Initial (g)
Net(g)
Total (g)
.
'. :
' -"
nib:
INT£R-MOUMTAIM LASS
l&J ·UPS ·.
00~
0. VSPs°
Q · Hand Carried
IJ· Other ·
Inter-Mountain Labs
Sheridan, VI/Y and Gillette, VI/Y
· Soil
Solid
Fll~r
Other
7:00
7:00 .
7:00 ..
7:00
7:00-
7:00
SL
SD
FT
OT
SAM-PLE ------
IOENTIFICAI IVN
7204 Vanadium $crubber RUN 1
72Q5 Vanadium Baghouse RU.N 1 ..
. 7206 Vanadium $crubber RUN 2
72(!7 Vanactium Baghouse RUN 2
7204 Vanadium Scrubber RUN 1
:;"2Q5 )'anadium Baghouse RUN 1
7206 Vanadium Scrubber" RUN 2
7207 Vanadium Baghouse RUN 2
,r .. ~~ ,-------"~-9 Standard turnaroul}d
RUSH -5 Working Days
URGENT -<: 2 Working Days
Rush & Urgent Sur_charges w/1/ be spplled
-,
Matrix
FT
FT
FT
FT
OT
OT
OT ·
OT
Inter-Mountain Labs, Inc. www.intennountainlabs.com
page 1 1 of 1
(REMARKS
•1~~~~~~~-~~l~ffii~I #of -• . -· "'-~ -~ :. '!:{!":. ...,,:;, -I ' -. :!':::' ~ _ _... . ~ -~ ~ -., ... • ~ :.r..'!!. ~"I;-~ .
1
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X x· X x X X
1 X X X X X X X
.t
~ev4.6Web
An fr,n' ,· Fo~<Jy Jnte,-MouLin Lalxuato,ies e a:,,tca ·
a1Nssc1ENCEamER 1673 Terra Avenue S eridan, WY 82801
:
CLIENT:
Project:
Lab Order:
Energy Fuels (Whit Mesa)
South Yellow Cake Scrubber, Dryer
S1908376
ph: [phone]
Date: 10/15/2019
CASE NARRATIVE
Report ID: S1908376001
Samples 7204 Vanadium Scrubber UN 1 Filter & Beaker, 7205 Vanadium Baghouse RUN 1 Filter & Beaker, 7206
Vanadium Scrubber RUN 2 Filter &leaker and 7207 Vanadium Baghouse RUN 2 Filter & Beaker were received on August
26, 2019.
All samples were received and anal
1
zed within the EPA recommended holding times, except those noted below in this case
narrative. Samples were analyzed sing the methods outlined in the following references:
"Standard Methods For The Examin . tion of Water and Wastewater", approved method versions
Test Methods for Evaluating Solid ste, Physical/Chemical Methods, SW-846, 3rd Edition
40 CFR Parts 136 and 141
40 CFR Part 50, Appendices B, J, L, and O
Methods indicated in the ~ethods U , date Rule published in the Federal Register Friday; May 18, 2012
ASTM approved and recognized sta dards
All Quality Control parameters met t e acceptance criteria defined by EPA and Inter-Mountain Laboratories except as
indicated in this case narrative.
Reviewedby: d/~
Wade Nieuwsma, Assi!>t~nt Laboratory Manager I . Page 1 of 1
1.
I
~ • Formerly Inter-MOL ntain Lab<?ratories ( ~e!~~~:~~~! -16_7_3_T_e_r-ra_A_v_e_n_u_e....,.~h-e-rl-d-an-,-W....:....Y-82_8_0_1 ______ ph_:_(-30_7_)_6_7_2--8-9-45-------------
.
Company:
ProjectName:
Lab ID:
.
Energy Fuels (Whit ~ Mesa)
391 East 620 Soutt
American Fork, UT 84003
Sample Analysis·Report
South Yellow Cak Scrubber, Dryer
S1908376-001
ClientSample ID: 7204 Vanadium S rubber RUN 1 Filter & Beaker
COC: WEB
Comments
Date Reported . 10/1 ~/2019
Report 10 S1908376001
WorkOrder: S1908376
Collettio_nDate: 8/20/2019 7:00:00 AM
DateReceived: · 8/26/2019 9:21 :00 }\M
FieldSampler:
Matrix: Filter
Analyses Result Units Qual RL ' · RROL
µCl/ml Method Date Ana]yzed/lriit
Radionuclides -Filter
Lead 210 2.6iE·4 µCi/Sample
Lead 210 Precision (±) 1.:-5 µCi/Sample
Radium 226 4 -7 µCi/Sample
Radium 226 Precision (±) t µCi/Sample
Radium 228 -6. E-6 µCi/Sample.
Radium 228 Precision (±) ·r µCi/Sample
Thorium 230 4 -7 µCi/Sample.
Thorium-230 Precision (±) 2 -7 µCi/Sample
Thorium 228 0 -6 µCi/Sample
Thorium-228 Precision (±) 2 -7 µCi/Sample
Thorium 232 Off-6 µCi/Sample
Thorium-232 Precision (±) t µCi/Sainple
Uranium 234 3 ·-7 µCi/Sample
Uranium 234 Precision (±) 2 -7 µCi/Sample
Uranium 235 4~-8 µCi/Sample
Uranium 235 Precision (±) 8~-8 µCi/Sample
Uranium 238 3 -7 µCi/Sample
Uranium 238 Precision (±) t µCi/Sample
Metals -Total
Thorium 232 µg/Sample
Uranium D µg/Sample
2
2E-07
1E-06
3E,15
3E-15
3E-15
4E-07
4E-07
45
6E-14
9E-14
2E-13
3E-,1r
3E-1~
3E-15
9E-15
9E-15
9E-15.
3E-15
9E-15
OTW01 09/11/2019 1708
OTW01 09/11/2019 1708
SM 7500RAB 09/25/2019 1134
SM 7500RAB 09/2.5/2019 1134
Ga-Tech 10/01/2019 2147
Ga-Tech 10/01/2019 2147
ACW10 09/05/2019 1508
ACW10. 09/05/20.19 1508
ACW10 • 09/05/2019 1508
ACW10 09/05/2019 1508
ACW10 09i05/2019 1508
ACW10 09/0?/20191508
ACW01 10/02/201.91652
ACW01 10/02/2019 1652
. ACVi/01 10/02/2019 1652' .
ACW01 10/()2/20i 91652
ACW01 10/~212019_· 1652
· ACW-01 1 Oi0.2/2019 1652
EPA 200.8 09/20/2019 1402
EPA 200.8 08/28/2019 1732
These results apply only to the samples t~sted.
Qualifiers: B Analyte detected-in the assobiated Method Blank
RL • Reporting Umit
E Value above quantitation ra~ge .
H Holding times ror preparatloi:t or analysis exceeded
L Analyzed by another laboratbry
ND Not Detected at0the Reporti~g Limit
S Spike Recoveryo(!tslde acct pled recmvery limits
X Matrix Effect
1 ~4-4' .,.-I Reviewed by: -=~'--""''-~-,---...... ___ ,......, ___ _
Wade Nieuw'sma . As~istant Laborcifory Manager
I .
!
j
I
c Calculated Valu~
G Analyzed-atlMt Gfllette laboratory ..
J . Apalyte-dete_ct~ bel!JW quanUtatl_on limits .
M · Value excee(ls lv'lontlily-Ave or MCL or is less than LCI:. o Outside. ihe Range,ofDlluUons ·· . . . .. · ·. · . ·. ·
U Analysis ~port~d Und~r lhe report(ng limit .
page 1 of 4
TWP
TWP
WN
WN
WN
.WN
WN
'1'fN
WN
WN
INN
WN
WN
WN
WN
WN
l(VN
11:VN
,.
IVIS
\'y1S
.
'
~Ana(ytica( Formerly lnter-Mour tain Laboratories
ING SCIENCE BETTER 1673 Terra Avenue S ~eridan, WY 82801 ph: (307) 672,8945
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported . 10/15/2019
391 East 620 South Report ID S1908376001
American Fork, UTE 4003
ProjectName: South Yellow Cake Scrubber, Dryer WorkOrder: Sl908376
Lab ID: S1908376-003 CollectionDate: 8/21/2019 7:00:00 AM
ClientSample ID: 7206 Vanadium Sc ubber RUN 2 Filter & Beaker D!)teRe~eived: 8/26/2019 9:21 :00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments I Analyses Re ,ult · Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210
Lead 210 Precision (±)
Radium 226
Radium 226 Precision (±)
Radium 228
Radium 228 Precision (±)
Thorium 230
Thorium-230 Precision (±)
Thorium 228
Thorium-228 Precision (±)
Thorium 232
Thorium'232 Precision (±)
Uranium 234
Uranium 234 Precision (±)
Uranium 23.5
Uranium 235 Precision (±)
Uranium 238
Uranium 238 Precision (±)
Metals -Total
Thorium 232
Uranium
,.+, 6~:~t
-2.ak-s
1E 5
SE 7
2E 7
OE 6
µCi/Sample 2
µCi/Sample
µCi/Sample 2E-07
µCi/Sample
µCi/Sample 1E-06
µCi/Sample
µCi/Sample 3E-15
µCi/Sample
µCi/Sample 3E-15
µCi/Sample
µCi/Sample 3E-15
µCi/Sample
µCi/Sample 4E-07
µCi/Sample
µCi/Sample 4E-07
µCl/Sample
µCi/Sample 4E-07
µCi/Sample
µg/Sample 45
µg/Sample
6E-14 OTW01 09/11/20191708
OTW01 09/11/2019 1708
9E-14 SM7500RAB 09/25/20191134
SM 7500RAB 09/25/2019 1134
2E-13 Ga-Tech 10/02/2019 353
Ga-Tech 1.0/02/2019 353
3E015 ACW10 09/05/2019 1508
ACW10 09/05/20191508
3E-15 ACW10 09/05/20191508
ACW10 09/05/2019 1508
3E-15 ACW10 09/05/2019 1508
ACW10 09/05/2019 1508
9E-15 ACW01 10/02/2019 1652
ACW01 10/02/2019 1652
9E-.15 ACW01. 10/02/20191652
ACW01 10/0212019 1652
9E-15 ACWOl 10/02/2019 1652
ACW01 10/02/2019 1652
3E-15 · EPA 200.8 09/20/2Q.19 1410
9E-15 EPA 200.8 08/28/2019 1802
These results apply only to the samples tt .sted .. RL , Reporting Limit
Qualifiers: B . Analyte detected In the associated Method Blank
E Value at?ove quantitation ra1ge .
H Holding times for preparatloo or ar.talysis exceeded
L Analyzed by another laboratory·
ND Not Detected at the R0eport1rjg Limit
S Spike Recovery outside acc~ptea recovery limits
X Matrix Effect l
Reviewedby: d./~
Wade Nieuwsma, Assistant Laporatory l\llanfger
C Calculated Value
G Analyzed at IML, Gillette laboratory
cl Analyt.e detected below quantitatlon limits
M Vaiueexcee~s Monthly Ave or MCL or is less than LCL
0 Outside the Range of Dilutions ·
u '.'\nalysis reported under the reporting limit
. Page 3 of4
TyvP
T\NP
WN
WN
WN
WN.
WN
. WN
WN
WN
WN
WN
WN
WN
IJV.N
WN
WN
WN
MS
MS
I
Company:
ProjectName:
Lab ID:
ClientSample ID:
COC:
Comments
I
I'
. ! .
Formerly lnter-Mo~ntain Laboratories
1673 Terra Avenue Jheridan, WY 82801 ph: [phone]
Sample Analysis Report
Energy Fuels (Whit Mesa)
391 East 620 Sout~
American Fork, UT r 4003
South Yellow Cake Scrubber, Dryer
S1908376-002 I
7205 Vanadium Bbghouse RUN 1 Filter & Beaker
WEB
Date Reported
Report ID
WorkOrder:
Collecti.onDate:
c;>ateReceived:
FieldSampler:
Matrix:
1q11 s12019
$1908376001
S1908376
8/20/2019
8/26/2019 9:·21 :00 AM
Filter
Analyses R suit Units Qual RL RRDL
µCi/ml Method Date Analyzed/lnit
Radionuclides • Filter 2.t -5 Lead 210 µCi/Sample
Lead 210 Precision (±) 4 1'6 µCi/Sample
Radium 226 38.-7 µCi/Sample I Radium 226 Precision (±) 111-7 µCi/Sample I
Radium 228 -8.~-6 µCi/Sample
Radium 228 Precision (±) 7.1 -6 µCi/Sample
Thorium 230 4.1E-5 µCi/Sample
Thorium-230 Precision (±) 5.*·6 µCi/Sample
Thorium 228 '38-7 pCi/Filter
Thorium-228 Precision (±) 3~-7 pCi/Filter
Thorium 232 2~-7 pCi/Filter
Thorium-232 Precision (±) 3 -7 pCi/Filter
Uranium 234 36:-6 µCi/Sample I Uranium 234 Precision (±) 66:-7 µCi/Sample
Uranium 235 7g.5 µCi/Sample I Uranium 235 Precision (±) 11:1-1 µCi/Sample
Uranium 238 3l-6 µCi/Sample
Uranium 238 Precision (±) 6 -7 µCi/Sample
Metals -Total I
Thorium 232 NP ·µg/Sample
Uranium µg/Sample
2
2E-07
lE-06
3E-15
3E-15
3E-15
4E-07
4E-07
4E-07 ·
45
1
6E-14
9E-14
2E-13
3E-15
3E-15
3E-15
9E .. 15
9E-15
9E-15
3E-15 ·
9E-15
OTW01 09/11/2019 1708
OTW01 09/11/2019 1708
SM 7500RAB 09/25/2019 1134
SM 7500RAB 09/25/2019 1134
Ga-Tech· · 10/02/2019 050
Ga-Tech . 10/02/?,019. 050
ACW10 10/08/2019 856
. ACW10 10/08/2019 8.56
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/20i 9 856
ACW01 10/02/20191652
ACW01 10/02/2019 i652
ACW01 10/02/20191652.
ACW01 10/02/2019 1652
ACW01 10/Q2/2019 1 ~52
ACW01 10/02/2019 1652
EPA 200.8 09(20/2019 1438
EPA 200.8 0~/28/2019 1756
These results apply only to the samples tt sted. RL -Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blan!t
E Value above quantltaiion ra~ge
H Holding times for preparat!o? or analysis exce.eded
L Analyzed by another laborat~ry
ND Not Detected at the Rep.ortirig Limit
s Spike Recovery outside accepted reco,very limits
X Matrix Effect I
C Calculated Value
·c; . Anal.vzed at IML Giliette laboratory
J Analyte detected bel0\'1 quantltatlon limits.
·M ,Val\Je exce~s Monihly Ave or f'JICL cir is lei s llian· LCL
0 Outside the Range 9(.1;:>llutions . . . ·' , . :
U An11lysis reported_ under-th.e reporting limit ·
~/1--4' <" ! Reviewed by: -~'-"''--~--'----l--________ _
Wade Nieuwsma, Assistant Laboratory Manager Page 2 of 4
TWP
TWP
WN
WN
WN
WN
WN
WN
WN
WN
WN
WN .
WN
WN
WN.
WN
WN ,
WN
MS
MS
Company:
ProjectName:
Lab ID:
ClientSample ID:
COC:
Comments
Formerly lnter-Mo~ntain Laboratories
1673 Terra Avenue , heridan, WY 8'2801 , ph: [phone]
Sample Analysis Report
Energy Fuels (White Mesa)
391 East 620 Sout~
American Fork, UT 84003
South Yellow Cakf Scrubber, Dryer
S1908376-004
7207 Vanadium Br ghouse RUN 2 Filter & Beaker
WEB ·
Date Reported 10/15/2019
Report ID S1908376001
Work.Order: S1908376
CollectionDate: 8/21/2019 7:00:00 AM
Date Received: 8/26/2019 9:21 :00 AM
FieldSampler:
Matrix: Filter
Analyses R~sult Units Qual Rl RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 9.4:E-6 µCi/Sample
Lead 210 Precision (±) 4.1~-6 µCi/Sample
Radium 226 7E-7 µCi/Sample
Radium 226 Precision (±) 2t-7 µCi/Sample
Radium 228 ·4. E-6 µCi/Sample
Radium 228 Precision (±) 9.4-r6 µCi/Sample
Thorium 230 5:5E-5 µCi/Sample
Thorlum-230 Preci~ion (±) I :µCi/Sample 7.3rs
Thorium 228 SE:-7 pCi/Filter I Thorium-228 Precision (±) 56:-7 pCi/Filter
Thorium 232 2~-7 pCi/Filter
Thorium-232 Precision (±) 3Et-7 I pCi/Filter
Uranium 234 4ff-6 µCi/Sample
Uranium 234 Precision (±) 1{1 µCi/Sample
Uranium 235 ,4.7 µCi/Sample
Uranium 235 Precision (±) 11p µCi/Sample
Uranium 238 4~-6 µCi/Sample
Uranium 238 Precision (±) . I µ~i/Sample
Metals O Total
Thorium 232 µg/Sample
Uranium 12 mg/Kg
2
2E-07
1 E-06
3E-15
3E-15
3E-15
4E-07
4E-07
4E-07
45
1
6E-14
9E-14
2E-13
3E-15
3E-15
3Es15
9E-15
9E-15
9E-15
3E-15
9E-15
OTW01 09/11/2019 1708
OTW01 09/11/2019 1708
SM 7500RAB 09/26/2019 1059
SM 7500RAB 09/26/2019 1059
Ga-Tech 1 O/Q2/2019 656
Ga-Tech 10/02/2019 656
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW10 10/08/2019 856
ACW01 10/02/20191652
ACW01 10/02/2019 1652
ACW01 10/02/2019 1652
ACW01 10/02/2019 1652
ACIN01 10/02/2019 1652
ACW01 10/02/2019 1652
EPA 200.8 09/20/2019 1413
EPA 200.8 08/28/2019 1821
I These results apply only to the samples tested.
Qualifiers: B Analyte·detecte~ In the asso~lated Method Blank
RL • Reporting Limit
. i E Value above quantltallon ra~9e
H Holding times for preparaUo~ or analysis exceeded
L Analyzed by anoth~r laboratory ·
ND Not Detected at the Reportirtg Limit
S SplRe Recovery outside accbpted recovery limits
C Calculat.ed Value
G Analyzed at IML Gillette laboratory
J Analyte det_ected below quantitation limits
M Value exceeds Monthly:Ave or MCL or is 'less than LCL
0 Outside the Range ofDilutions .
U Analysis reported unde[ the reporting limit
X Matrix El?ect
Reviewed by: -=M~'--~------_-_--::::i::::;:::: __ _
Wade Nieuwsma, Assis\ant Laboratqry Manager Page 4 of 4
TWP
TWP
WN
l,yN
WN
WN
WN . \iVN
WN
'WN
WN
WN
WN
WN
WN
WN
WN
WN
ryis
MS
~.~s?~/c~'.Crr~•-Fo_r_m_e_r_1y_1_n_te_r_-M_o_u_n-;~-ai_n_L_a_b_o_ra_t_o_ri_es _______________________ _ r~n::.. ~~ ,K ~ 1673 Terra Avenue s ]bFldaA, WY 82801 ph: (307) ~72-8945
ANAL VTICAL QC SUMMARY REPORT
CLIENT: Energy Fuels (White iesa)
Work Order: S1908376
Project: South Yellow Cake Scrubber. Dryer
Lead 210 in Filters I
MB-754 (09/11/1913:04) J
Sample Type MBLK
RunNo: 171551
Date: 10/15/2019
Report ID: S1908376001
Units: µCl/Sample
Analyte I Result RL Spike Ref Samp %REC % Rec Limits Qual
Lead 210
Lead 210 in Filters
LCS-PB (09/11/19 13:04)
Analyte
Lead 21 O in Filters
Lead 210 I
MS (09/11/19 14:37)
Analyte
Lead 210 in Filters Lead 210 '
MSD (09/11/1914:37)
Analyte
Lead 210
. ' Qualiriers: B Analyte detected in the associ~ted. Meihod Blank
G Analyzed at IML Gillette tatjoraiocy
J Analyte detected below tj~~nlitatlon limits
ND No! Detected at the Repott!ng 'Limit
R RPO outside accepted recovery limits
X Matrix Effect
ND
Sample Type LCS
RunNo: 171551
Result
1E-05
Sampl,e Type MS
RunNo: 171551
Result
1 E-05
Sample Type MSD
·2E-Ofr
RL
2E-06
RL
2E-06
Units: µCi/Sample
Spike
1'E-05
Units:
Spike
1E-05
Units:
Ref Samp %REC
114
µCi/Sample
Ref Samp %REC
0.000003 91 .6
µCl/Sample
% Rec Limits Qual
66'-130
% Rec Limits Qual
66-130
RunNo: 171551
Result .RL · Cone %RPO %REC % RPO. Limiis Qual
2E-05 2E006 1E-05 13.4 108· 30
E Value above quantitation range.
H Holding times for preparation or analysis exce.eded
L Anal~d by another laboratory
O Outside the Range or Dilutions
S Spike Recovery ouiside accepted recovery limits
Page 1 of 5
Formerly lnter-Mounfain Laboratories
1673 Terra Avenue Sh;eridan, WY 82801 ph: [phone]
. I ANAL VTICAL QC SUMMARY REPORT I . .
Energy Fuels (White iesa)
S190~376 I
South Yellow Cake Scrubber, Dryer
CLIENT:
Work Order:
Project:
Radium 226 Air Filter Analysis
MB-2052 (09/24/19 15:09)
r
I Analyte
Radium 226 I
MB-2053 (09/26/19 10:59)
Analyte
Radium 226 1
Radium 226 Air Filter Analysis
LCS-2052 (09/24/19 15:09)
Analyte
Radium 226 I
LCS-2053 (09/26/19 10:59)
Analyte
Radium 226 !
Radium 226 Air Filter Analysis I
MS-2052 (09/24/19 15:09) ! Analyte
Radium 226 j
MS-2053 {09/26/19 10:59) I
Analyte !
Radium 226 j
Radium 226 Air Filter Analysis• I
Qualifiers:
MSD-2052 (09/24/1915:09) I
Analyte j
Radiu.m 226 l
MSD-2053 (09/26/1910:59)
Analyte
Radium 226 I
i
B Analyte detected in the associated Method Blank
G Analyzed at IML Gillette laboratory
j Analyte detected below quantitation limits
ND Not Detected at the Reporting Limit
R RPD outside accepted recovery limits
X Matrix Effect :
Sample Type· MBLK
RunNo: 171949
Result
ND
Date: 1 0/15/2019
Report ID: S1908376001
Units: µCi/Sample
PrepDate: 09/16/19 0:00 BatchlD 16551
RL Spike · Ref Samp %REC % Rec Limits
2E-07
RunNo: 172003 PrepDate: 09/19/19 0:00 BatchlD 16567
Result RL Spike Ref Samp %REC % Rec Limits
ND
Sample Type LCS
2E-07
Units: µCi/Sample
RunNo: 171949
Result
PrepDate: 09/16/19 0:00 BatchlD 16551
RL Spike Ref Samp %REC % Rec Limits
6E-06 2E-07 7E-06 92.2 67.1 -122
RunNo: 172003 PrepDate: 09/19/19 0:00 BatchlD 16567
Result RL Spike Ref Samp %REC % Rec Limits
SE-06 2~-07 7E-06 77.9 67.1 • 122
Sample Type MS Units: µCi/~ample
RunNo: 171949 PrepDate: 09/16/19 0:00 BatchlD 16551
Result RL Spike Ref Samp %REC· % Rec Limits
6E-06 2E-07 7E-06 ND 93.1 65 -131
RunNo: 172003 PrepDate: 09/19/19 0:00 BatchlD 16567
Result RL. Spike Ref Samp %REC % Rec Limits
6E-06
Sample Type MSD
2E-07 : 7E-06 NO 86.7
Units: µ<::I/Sample
65 -13i
Qual
Qual
Quaf
Qual
Qual
Qual
RunNo: 171949 PrepDate: 09/16/19 0:00 BatchlD 16551
Resuii: RL C~nc . %RPO %REG % RPD Limits Qual
6E-06 2E-07 6E-06 4.18 89,3 20
RunNo: 172003 PrepDate: 09/19/19 0:00 BatchlD 16567
Result RL Cone %RPO %REC % RPD Limits Qual
6E-06 2E-07 6E-06 3.42 89.7 20
E V.alue above quantitation range
H Holding tlrries for preparation or analysis exceeded
L Analyzed by another laboratory
0 Outsid~ the Range bf DIiutions
S Spike Recovery outsid~ accepted recovery limits
Page 2 of 5
.
• I
~eAna/ytica(_Fo_r_m_e_rl.;..y_ln_te_r_-M_o_u_n.:...1·~a-i_n_L_ab_o_r_ato_rie_s _____________ ___,, _________ _
(~/:~rn.rmmnEJ 1673 Terra Avenue Sh ridan, WY 82801 ph: (307.) 672-8945
ANALYTICAL QC SUMMARY.REPORT
I
Energy Fuels (White Mesa) . . ' CLIENT:
Work Ord~r: S1908376 j
Project: South Yellow Cake Scrubber, Dryer
Thorium Air Filter Analysis !
MB-695 (09/05/19 09:43) I
Analyte I
Thorium-228 I
Thorium-230 1
Thorium-232 ·
MB-699 (10/08/19 08:56)
Analyte
Thorium-228
Thorium-230
Thorium-232 :
Thorium Air Filter Analysis
LCS-695 (09/05/19 09:43)
Arlalyte
I
'
Thorium-230 i
Thorium-232 i
LCS-699 (10/08/19 08:56)
Analyte
Thorium-230 !
Thorium Air Filter Analysis
LCSD-695 (09/05/19 09:43)
Analyte
Thoriurri-230 ;
LCSD-699 (10/08/19 08:56)
Analyte
Thorium-230 ! .
.
Qualifiers: B Analyte detected in tt,e associated Method Blank.
G Analyzed at IML Gillette labbratory. ·
J Analyte detected below quantitation limits
NO Not Detected at the'Reporting Limit
R RPO outside accepted recovery limits
X Matrix Effect
Date: 10/15/2019
Report ID: S1908376001
Sample Type MBLK Units: µCl/Sample ·
RunNo: 171951
Result Rl Spike Ref Samp %REC % Rec Limits
ND 2E-07
ND 2E-07
ND 2E-07
RunNo: 172403
Result RL Spike Ref Samp %REC % Rec Limits
ND 2E-07
ND 2E-07
ND 2E:07
Sample Type LCS Units: µCi/Sa!11ple
RunNo: 171951
Result RL Spike Ref Samp %REC % Rec Limits
1E~05 2E-07 . 1E-05 . 105 68 • .146
1E-05 2£,07 1E-05 ·103 68 • 146
RunNo: 172403
Result .RL Spike RefSamp %REC % Rec Limits
1E·OS 2E-07 1E-05 107 68 -146
Sample Type l,.CSD .Units: µCi/Sample
RunNo: 171951
Result Rl Coric %RPO %REC % RPD Limits
1E-05 2E-07 1E-05 0.229 10·4 20,
RunNo:172403 ..
Result RL Cone %RPO %REC .% RPDUmits
1£-05 '2E-07. 1,E-05 1.'23 1'06, 20
E Value above quantitation range
H Holdil)g limes for: p~paratioh or anaiysis excee/jed
L . Analyzed by another lal:Joratory
o ,outsi.de the Range or Dilutions
S Spike RE!Coi/ery outside accepted recov11ry limits .
Qual
Qual
Qual
Qual
:Ouar
Qual
~ • Formerly Inter-Mountain Laboratorie.s
r~,;~:!!r~~~!-1-67_3_T_e_rr;..·a_A_v_e_n...;u_e_S_h....;.:e-~-id-a-n,-W-Y-8.,..28-0-1------.-p-h:-(-3-07-)-6-7-2--8-9-4-5------------
ANAL YTl,CAL QC .SUMMARY REPORT
CLIENT: ' I
Energy Fuels (White Mesa)
Work Order: $1908376
Project: South Yellow Cake $~rubber, Dryer
Uranium lsot.opic Filters !
MB-R172619 (10/02/1916:52) :
Analyte
Uranium 234 (
Uranium 235. 1
Uranium 238 ;
Uranium Isotopic Filters
LCS (10/02/19 16:52)
Analyte
Uranium 234 :
Uranium 235 .
Uranium 238 •
Uranium Isotopic Filters
Qualifiers:
LCSD (10/02/19 16:52)
Analyte
Uranium 234 :
Urariium 235
Uranium 238
B Analyte detected In the as.sociated Method Bl.ank
G Analyzed at IML Gillette laboratory
J Analyte detected below quantitation limits
ND Not De.tl:!cted at the Reporting Limit
R RPO outside accepted r!;lcoyery limits
X Matrix Effect
Sample Type MBLK
RunNo: 172619
Result RL
ND 4E-07
ND 4E-07
ND 4E-07
Sample Type LCS
RunNo: 172619
Result RL
9E-06 4E,07
4E-07 3E-08
9E-06 4E-07
Sample Type LCSD
RunNo: 172619
Result RL
8E-06 4E-07
4E-07 4E-08
8E-06 4E-07
E Value above quantitation range
Date: 10[1 5/2019
Report ID: S1908376001
Units: µCi/Sar:nple
Spike Ref Samp %REC % Rec Limits
Units: µCl/Sample
Spike RefSamp %REC % Rec Limits
7E-06 134 50 • 150
3E-07 123 50 -150
7E-06 130 50-150
Units: µCi/SampJe
Cone %RPO %REC · % RP[? Limi.ts
9E-06 14.7 116 20
4E-07 6.60 132 . 20
9E,06 13.3 114 20
H Holding times for preparation iir'analysis exceeded ·
L Analyzed by another laboratory .
0 Outside .the: Range of Dilutions
S Spike Recovery outside.accepted re.covery limits
Page 4 of 5
Qual
\
Qual
Qual
12.eAna/ytica/°-F_o_r_m_e_rl_y_ln_t_e_r-_M_o_u_rit_a_in_L_a_b_o_ra_t_or_ie_s ______________________ _
r -/·u:,~~NG SfA!NtUll!U 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa) Date: 10/15/2019
Report ID: S1908376001 Work Order: S1908376
Project: South Yellow Cake Scrubber, Pryer
Total (3050) Metals by EPA 200.8-Soil:
MBLK (08/28/1917:19)
Analyte
Uranium
MBLK (09/20/19 13:55)
Analyte
Thorium
Total (3050) Meti!IS by EPA 200.8-Soil
LCS (08/28/19 17:13)
Analyte
Uranium
LCS (09/20/19 13:52)
Analyte
Thorium
Total (3050) Metals by EPA 200.8-Soil ·
S1908376-001AS (08/28/19 17:44)
Analyte
Uranium
S1908376-004AS (09/20/19 14:27)
Analyte
Thorium
Total (3050) Metals by EPA 200.8-Soil
S1908376-001AMSD (08/28/1917:50)
Analyte
Uranium
S190B376-004AMS0 (09/20/19 14:31)
Analyte
Thorium
Qualifiers: B Analyte detectec_l in the asso(;iated Method Blank
G Analyzed at IML Gillette laboratory
J Ana.lyte detected below quantitatlon limits
ND Not Detected at the Reporting Limit
R RPO outside accepted recovery limits
X Matrix Effect
'·
Sample Type MBLK
RunNo: 171194
Result
ND
RunNo: 171805
RL
Result RL
ND 45
Sample-Type LCS
RunNo: 171194
Result RL
104 1
RunNo: 171805
Result JR
102 45
Sample Type MS
RunNo: 171194
Result RL
Units: µgt.Sample
Spike Ref Samp %REC % Rec Limits Qua!
Spike Ref Samp %REC % Rec Limits Qual
Units: µg/Sample
Spike Ref Samp %REC % Rec Limits Qual
1E02 104 85 -115
Spike Ref Samp %REC % Rec Limits Qual
1E02 102 85 -115
Units: µg/Sample
Spike Ref samp %REC % Rec Limits Qual
10500 1 · 1E04 ND 104 70 -130
RunNo: 171805
Result RL Spike Ref Samp %REC % Rec Limits Qual
1100
Sample Type MSD
45 ·1E03 ND 10~ . 70 -130
RunNo: 171194
Result
10000
RunNo: 171805
Result
1140
RL
RL
45
E Value above quantitation ra·nge
Units: µgfSample
Cone %RPO %REC % RPO 'Limits Qual
10500 4.58 .. 99.1 20
Cone %RPO %REC % RPD Limits Qual
1100 3.55 112 20
H Holding times for preparation or .analysis exceed.ed
L An.al~ed by another laboratory
6 outside it:ie Range of Dilutlo.ns
S Spike Recovery outside accepted recovery limits
Page·s of 5
/UYtt:
·-· ...... --NTER-MOU)hAIN LAtt:;
ClltntName
:81 UPS ~~
J Hand Carried
J Other
Inter-Mountain Labs
Sheridan, WY and Gillette, WY
Soil
Solid
Filter
Other
7:00
7:00
7:00
7:00
7:00
7:00
7:00
SL
SD
FT
OT
..
7204 Vanadium Scrubber RUN 1
7205 Vanadium Baghouse RUN 1
7206 Vanadium Scrubber RUN 2
7207 Vanadium Baghouse RUN 2
7204 Vanadium Scrubber RUN 1
7205 Vanadium Baghouse RUN 1
7206 Vanadium Scrubber RUN 2
7207 Vanadium B~house RUN 2 ·
Inter-Mountain Labs, Inc.
I Matrix
FT
FT
FT
FT
OT
OT
OT
OT
Page 1 of 1
#WEB
REMARKS
#of tt11tg~1,-~-.~-~ns -Y~-··'~'~ ·' '. · · · ?n • ~~---.' ~.?. ,t¥.' ··l~ ~· . ·'t:a ~.! ,! . . &f '~ -,fflJ.l'i-_J :',!lo ... -..... -: .I ];:';( .9".'tffl1! • _)_ ,i .!° .... l•~: ~Ji! . _ ':" • • _Q.,; I !\'ifi.~,_,t , : ~ ... • _
1
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
1 X X X X X X X
Rev4.6Web
APPENDIXD
Vanadium Dryer
Figure 1. Facility Schematic Representation, Vanadium Dyer
Vanadium Packaging
Figure 2. Facility Schematic Representation, Vanadium Packaging
Process Data (Retained by Energy Fuels)
Scrubber Pressure Drop and Water Flow Rates
D
Facility Energy Fuels
t
a
!
y
Stackldentification: Vanadium Dryer
l+-0 ~1
~
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 Temperature, "F
Estimated Velocity, fpm
Control Unit
Type:
Scrubber
Number of Ports
10' ------
29' -
65' -----
36" ------
3-5% --
75-90 ------
1.400 -
2
Figure 1. Facility Schematic Representation, Vanadium Dryer
Process
Type:
Vanadium Dryer
FaciHty Energy Fuels
t
a
!
y
Stack Identification: Vanadium Packaging
l+-0~1
~
a: Distance upstream from next disturbance, inches
~: Distance downstream from last disturbance, inches
y: Distance of Sample Level to Ground, feet
0: Stack Inside Diameter, inches
Estimated Moisture, percent
Estimated Temperature, "F
Estimated Velocity, fpm
Control Unit
Type:
Baghouse
Number of Ports
>200" ------
97" -
20' -----------
29.5" -
0-1% --
60-80 ------
1,400 -
2
Figure 2. Facility Schematic Representation, Vanadium Dryer
Process
Type:
Vanadium Packaging
..
· .. , .
·.•
Facil~y Energy Fuels
Location Vanadr~ Jryer
Date ct'_ z, V _ \ C,
:
East Scrubber
Run# Time ; "H20 gpm
I ¥~ ~ 0 i {z.. \ 3 ';.y .
I Cf• I) D . • i z . ~ 3.'\ .)
'1~ '3 D l'l, ~ 11.t
b \ t) ,' o o: I z.:. t..,. 1' ., . s--
lo.'JD ll. '~ l 61. '-
I f .' ui) I Z,i.. ]i. s-. ..
t 1: 30. 11·} JC,'{
({;JU rz.~ 1~., ,,: 'Q {l."t 1,,t
,, ." 00_ '?, ~ 'J, %.,
l l .. '"'JO \t·) } ,. r>
l"I.·. p.' 't.~ l\, '
.. ,_., ,w.,o I l·~ ,,,b
. · . . ' .. ft-:01> /1 • ../ '"·' . , r: J t, ft·} ,. ,~~ , .i.. ::'~: -
'.! •.• :.·::: .. q ~~ .. •· .. :" •.
, , .. -~~ ft • .., ., CL i,..
'
;
l
.
West Scrubber Fusion Furnace.
"H20 gpm OF
G·i <;-{, .& Is~ D
J '{) q&.r lJ4 D
t 'f r' ·I. 11&/
i-; (,' -~ '-
ll Sr
l, ., ~ "·t' I J , l>
'·1-ti·(,.-:, 11 'Tb (., . c., fr t (,, IJ 1J "' (,
s-, ., J 110 ,.,
"'· q. I Jft> r, . ., ·r,·1 f1Sr-
{.,.; r' .-1--11.tc./
£,·'S ~t,-~ f)~'i
., •t. -r, ·} ,~-~"
" . t. ¥'·9' r J ,.,
I, ' ' f,., I:)~ ll
I,.~ y:.,. v I ~61 .
.
.
.. .
..
..
'
. .
Faciljty Energy Fuels
' .
Location Vanadl~m Dryr
Date S (2: ( f ~
· East Scrubber West Scrubber Fusion Furnace
Run# Time · "H20 "H20 OF •.
gpm gpm
z. 9-: 00 r /.' 11, J ;., f'·"' / l yCJ
I S,.: 1 l) JI. ,. J.,. r 1-~ s-1·r It S ,-
, :o 0 , , ·r J ,.\ l-.' . 4r&. ~, l'3S.~
'i': Jo. " • I, ), ·' t·D c;,t,,l . .., ( .l ' ..,.
10: -~ ". (;
3,e,. t) 1 . ,;;) f'" -~ ,, l ~c;
. t•: Je "·+ J'i . ,; 1,.1 .; ~ 6 ·) , J 'l ~,
.. : o o \' ·(, ~":~ ~., tl :3 , t~../
... lt I ; . Jo · f '· 1'" ) f·') 1, ·'1-s,6, I I JS"+
. ·' tl: 0 Ci> ( r. r, ,...,,b It., ~ 6.z. , ~lf.t;Jf ' . . \·.'
:~';;~ .. rt : Ji, ',. ~ ]~., (,,, ,{;. ~ l~ ., 't
' 'f'" J 9':4i C, ·1-iL , l I '5 iC> ' I J,'00
I 1.'JO It· t) '-//,}, J u,V ~-,., ,_,,,.
1'{:•o 'l.) \.#t),D {,. ~-5-&,f, l'rVS
c '(;Jo f r., _., ",f"' f, :i. . "'·J 1 r.,v
•r: •• ',.} 1 ~·S' ~ .s ·'~"Z. t 1 i'I
' i~tYO ' ? .Q ~1·' t,·t ~' ,'('. /r,;, .
' /l .'00' l t .' C, 'IO.' c., ... , W'~· 'S / J 1-" .. I ..
. ,
. ;?1~\'t .. ~ ' :.· .
: .
. .
' . ,, -
' .•
:-··..;;"
..
.
'
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
' ~Probe
Type S Pitot
Tube
Temperature
Temperature
Sensor
I rqjnger Train Qitional, M~ Be Replaced
By An Equivalent Condimssr
l Temperature
Sensor
Nozzle 1-W Traat
Sensortl Gooseneck j ,--------------
lmpingers
~ Ga&s-!irai
/ A'dle ---
/
Type S Pitot
Tube ~
Stack
Wall
Glass Filter
Holder
Heated Area
Manometer Temperature Water
Sensors-.-
Orifice
Dry Gas
Meter
Empty Silica
Gel
By-pass
Valve
Air-Tight
Pump
Figure 3 Schematic of Method 5/114 Sampling Train
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 Cali_bration 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.
TECHNICIAN: Alex Moore
DATE: 12/1912018
METER PART#: Console 6
K' TESTED
METER SERIAL II:~
CRITICAL ORIFICE SET SERIAL#:~
FACTOR I VACUUM
ORIFICE# I RUN ,ii (AVG) . (In H~)
DGM READINGS (Fr
INITIAL I .. FINAL I 'NET (V,,J
G: 0.8137 9
0.8137 ' ·9
0.8137 • 9
G: 0.6317 11 .
0:5317 11
0.5317 . 11,
G: 0.3301 13
0;3307 13
0.3307 13
90.906
102.766
112.526
119:(00
130.925
137.549
147.401
154.650
160.129
102.765
112,626
·117.949
130.926 .
137.549
146.61)4
154.550
160.129
168.163
11.860
9.761
5.423
11.825
6.624
9.055
7.149
6;679
8.034
INITIAL
BAROMETRIC PRESSURE in H : 25.65
EQUIPMENT 1D 11, Console #6
TEMPERATURES °F
AMBIENT I DGM INLET I DG~ OUTLET I DGM
INITIAL FINAL INrnAL F!NAL AVG
64 75 84
65 82 87
65 86 88
67 82· 87
69 85 87
70 86 87
70 83 8:t
, 69 81 ·82
69 81 · 82
65
69
71
73
77
77
77
n
77 .
69
71
72
77
77
77
17
n
76
73.3
77.3
79.3
79.8
81.5
81.8
79.5
79.3
7'9.0
USING THE C~ICAL ORIACES AS CALIBRATION STANDARDS: _
!9••u
FINAL
25.65
ELAPSED
TIME(MI.N)
8
11.00
9.00
5.00
17.00
9.50
13.00
16.00
12.50
18.00
AVG (Pbar)
25.65
DGM b.H
(lnltzO)
§ 0
90
1.10
1.10
1.10
§ 43
3
(1)
Vm(STD)
j!,jill
Ylli
4.5907
~
5.5555
7.5909
6.0065
4.6896
6.7564
«~·-4
2019 Pre-Calibration
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
Vcx(STD)
10.0372
~
!,5559
AVG=
10.1072
5.6374
7.7071
AVG=
5.8998
4.6114
~
AVG=
(3)
y
~
~
~
~
~
.1.lli.
j,.ill
.1.lli.
.Yll
g,m
~
~
l
y
VARIATION(%)
:!!:§!!
1.93
:!.ll
j,fil
~
1.663
.1:fil.
~
j.fil
!,ill
~
.1:lli
• The follov.ing equatiollli .re used to calculate the standard volumes of air p.issed through the OGM, v. (std), and tile critical orifice,
V., (std); a_nd the OGM 113libiation factor, Y. These equations are airtoma~cally ~alculated in the spreadsheet above. AVERAGE ORY GAS METER CALIBRATION FACTOR, Y = I 0.996 I
(1)
(2)
(3)
V111i:,,,,, = K, "'Vin* Pbar+(lllf /13.o)
Im ,
= Net volume Of gas sarnpie passed through DGM, corrected to standard conditions
· 'K1 = 17.64 "R/1n.Hg (English), 0 •. 38$8 "Kimm Hg (Metric)
T~ = Absolute DGT\! avg. temperature ("R-English, "K -Metric)
Pbar •El
·vci-l''"l = K,. .JTamb
Vcr,~,'O Y= ----Vm<,,.,
= Volume of gas sample passed t_hrough ttie critical orifice, oorrected to standard conditions
T amb = AbsoJute"arilbient temperawre (°R -Eng0sh, .~K • Metric)
K' = Average K' factor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE AH@ =1 1.546
b.H@ = ( !!:Z§..8 )2 AH (V.,(std))
Vc,{std) v., .
TEMPERATURE Sc.NSORS °F
REFERENCE IN OUT
32 33 33
69 69 70
204 205 205
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three critical orifices to calibrate the dry gas meter· which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure.
hS 'J,,,dtrJ · ·"'"" -~elmMtt~, Mi
3) Run at tested vacuum (from Orifice .Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information In the GREEN cens, YELLOW cells are calculated.
TECHNICIAN:1---~------' M.McNamara
METER SERIAL#:~
CRITICAL ORIFICE SET SERIAL II:~
DATE: 12/18/2018
METER PART II: Con&0le 7
K' TESTED
FACTOR I VACUUM
ORIFICE# I RUN# (AVG) (In Hg)
G: 0.8137 10
0:8137 10
0.8137 10
G: 0.5317 13
0.5317 13
0.5317 13
G: 0.3307 12
0.3307 12
0.3.307 . 12
DGM READINGS!Fr
INIT,IAL I FINAL I NET (VJ
204.661
212.750
219.784
187.2&1
192.411
197.585
228.300
233.545
238.823
212,750
219.784
227.366
192,411
197.585
204.150
233.545
238.823
244.115
8.099
7.034
7.582
5.160
5.174
6.565
5.245
U78
5.292
USING THE CRITICAL ORIACES AS CALIBRATION STANDARDS: .
INITIAL
BAROMETRIC PRESSURE In H ); 25.55
EQUIPMENT ID#: Console #7
TEMPERATURES "F
AMBIENT I DGM INLET I DGM OUTLET DGM
AVG
68
68
68
72
TO
69
72
n
n
INITIAL FINAL I INITIAl FINAL
85 90 76 77
90 90 77 77
90 91 77 78
81 84 69 72
84 84 T3 74
84 86 74 75
87 " n ~
" " n ~
M ~ ~ ~
82.0
83.5
84.0
76.5
78.8
79.8
82.5
83.0
83.8
FINAL
2$.55
ELAPSED
TIME(MIN)
e
AVG(Pb.,.)
25.55
§§ §§.25
us
1.25
§ 5
5
12.00
12.00
12.00
(1)
Vm (STD)
6.8007.
5.8901
6.3431
4.3529
4.3465
5.5048
4.3656
4,3890
~
2019 Pre-Calibration
IF YVARIATION EXCEEDS 2.00%,
ORIACE SHOULD. BE RECALIBRATED
(2)
V.,(STD)
rnZ!
5.8827
~
AVG=
4.4186
4.4270
5.6128
AVG=
4.3972
4.3~72
.Yfil
AVG=
(3)
y
~
~
0.999
0:99s
.1:lli.
!,ill.
~
1,fil!
j,9QZ.
!:ill.
1.001
~
!
y
VARIATION ('Yo)
:!ill
-1,ll
~
The ioHD\\ing equations are 4sed to calculate lhe standard volumes of air passed through the DGM, Vm (sld), and the critical orifice,
V" (std), and 1he DGM calibration ·fac!O{, Y. These equations are aulomatically calculated in lhe spreadsheet above. · AVERAG0E DRY GAS METER CALIBRATION FACTOR, y = I 1.007
(1).
(2)
(3)
V.m1,,,d) = K, •Vm~ Pbar+(Ml /13.6) Tm
= Net volume of gas sample pass11d through DGM,.corrected to standard conditions
K, = 17.64 "R/in. Hg (En~fish), 0.3858 "Kimm Hg (Metric)
. Vcri,tdl = K'*.Pbar • 0
· .JTamb
VcJi,,dJ Y= _. -
· Vm<,,JJ
Tm = Absolute DGM avg. temperah/re ("R -English, "K-Metric)
= Volume of gas sample passed U,rough the critical.orlnce, corrected ·to standard conditions
. T...., = AbSOlule ambl!!nl l1!111per;nure ("R-English, "K-Metric)
K' = Average K' faci?"·from Critical Orifice Calibration
= DGM calibration factor
AVERAGE AH@ =1 1.702
4H@ = ( 0.75 8 )2 t,H /,Vm(std))
Vcr(std) \ .Vm
TEMPERATURE SENSORS °F
REFERENCE IN OUT
32 33 32
70 71 71
204 204 203
~
1&4!!
Lill
Ll2!
1.695
ll!!!
Yll
·1.568
1m.
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 iilformaticm in the GREEN cells, YELLOW cells are calculated.
TECHNICIAN: R Kitchen ,.._--~----~
DA TE: 08/22/19 METER SERIAL#;
METER PART#; Console 6 CRITICAL ORIFICE SET SERIAL #:
K' TESTED
~~~~~~--1 FACTOR VACUUM I ORIFICE# I RUN# [ (AVG) (in Hg)
DGM READINGS {F_TJ
INITIAL FINAL
..
0,42.38 13
0.4238 13
0.4238 13
42.236 48.199
48.199 53.998
53.998 61.299 G:
D:~~
D:~~
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
NET (V,.)
5.963
5.799
7.301
INITIAL
BAROMETRIC PRESSURE (in H : 25.2.5
eou1mENT10 11: Console #6
TEMPERATl.lRES 'F
AMBIENT I DGM INLET I DGM OUTLET I DGM
INITIAL FINAL INITIAL FINAL AVG
80 86 95 78 82 85.3
82 91 99 82 86 89.5
83 95 102 86 89 93.0
I I I' I I I
I I II II
FINAL
25.25
ELAPSED
TIME(MIN)
8
10.35
9.97
12.46
§
§
SMAY
AVG (P .. ,)
25.25
DGMAH
fin H,OJ
0.72
0.72
0.72
§
§
™W C4
(1)
V.,(S11>)
4.8841
4.7130
~
Post Calibration
Energy Fuel
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALi BRA TED
(2)
V"(STD)
4.7675
4.5840
5.7235
AVG=
AVG=
AVG=
(3)
y
0.976
0.973
~
0.973
l
y
VARIATION(%)
0.00
1,ill.
!ill
.1,lli
The following equations are used to calculale the standard volumes of air JlilSSed through the OGM, Vm (std), and the critical orifice,
V" (std), and the OGM calibration factor, Y. These equations are aulomalically calculated in the spreadslieetabove. AVERAGE DRY GAS METER CALIBRATION FACTOR, y = I 0.973
(1)
(2)
(3)
Vm(,,d) =K1 •Vm •.Pbar+(llH'/13.6)
Tm.
= Net volume of gas sample passed through DGM, corrected to standard conditions
K, = 17.64 'Riin. Hg (English), 0.3858 'Kimm Hg (Metric)
Tm = Absolute DGM avg. temperature ('R -English, 'K -Metric)
Pbar•E> -K'• Vcr(,'11 -.,/Tamb = Volume of gas sample passed through the critical orifice, corrected to standard conditions
T,m, = Absolute ambient temperature ('R -English, 'K -Metric)
Vcrc,.,1 Y= --
Vm(.,dl
K' = Aver,me K' factor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE AH@=[ 1.557
aHia, = ( 0.75 9 )2 t.H (Vm(std)\
Ve1(std) Vm /
TEMPERATURESENS0RS°F
REFERENCE IN OUT
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES Es '!., .... ,, ,..... 1.,.""""'-. 2'i'4
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 infonnation in the GREEN cells, YELLOW cells are calculated.
TECHNICIAN: R Kitchen
DATE: 08/22/19 METER SERIAL#: 25144
METER PART#: Console 7 CRITICAL ORIFICE SET SERIAL#: 1453S
K' TESTED
FACTORIVACUUM I ORIFICE# [ RUN# I (AVG) (In Hg)
DGM READINGS (Fr)
INITIAL FINAL
G: 0.5317 13
0.5317 13
0.5317 13
23.155 29.035
29.035 34.269
34.269 39.772
D:ffiEB
D:ffiEB
USING THE CRfflCAL ORIFICES AS CALIBRATION STANDARDS:
NET(Vm)
5.880
5.234
5,503
INITIAL
BAROMETRIC PRESSURE (in Hg): 25.25
EQUIPMENT 1D ,, Console #7
TEMPERATURES °F
AMBIEITTI DGM INLET I DGM OUTLET I DGM
INITlAL FINAL INITIAL FINAL AVG
86 98 98 95 93 96.0
84 97 99 93 92 95.3
84 99 101 92 93 96.3
I I i I I I
I I I I I I
0
FINAL
25.25
ELAPSED
TIME (MlN)
0
8.330
7.420
7.79
AVG{P..,)
25.25
DGMAH
(inH20)
1.20
1.20
1.20
§§
§§
(1)
Vm!STD)
4.7295
4.2156
4.4243
Energy Fuel
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
Va(STD)
4.7874
4.2722
4.4853
AVG=
AVG=
AVG~
(3)
y
1.012
1.013
.LQ1!
.Ll!H
i
y
VARIATION(%)
0.00
The following equations are used lo calculate the standard volumes of air pas.sect through the DGM, Vm (std), and Ille critical orifice,
Va (std), and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 1.013
(1)
(2)
(3)
v,"l•<d) =K, *Vm ,..Phar+(l'l.H 113.6)
1i11
= Net volume of gas sample passed through DGM, corrected to standard conditions
K, = 17.64 °Rlin. Hg (English), 0.3858 'Kimm Hg (Metric)
Tm = Absolute DGM avg. temperature ('R. English, 'K • Metric)
Pbar•0 ·-K'* Vcr(,1.11 -,/Tamb = Volume of gas sample passed through the critical orifice, corrected to standard conditions
T,mb = Absolute ambient temperalure ('R • English, 'K • Metric)
Vcr(,Jdi Y= -. -
Vm(,ta)
K' = Average K: factor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE.AH@=! 1.640
.AHCil! = ( 0.75 8. )
2
Ll.H (Vrn(std)\
Vcr(std) Vm }
TEMPERATURE SENSORS 'F
REFERENCE! IN \ OUT
~
1MQ.
1.637
Type S Pitot Tube Inspection Data
Date: ___ 12_/_20"""/_l _8 __ Pitot Tube Identification: -----------380
Technician: M. McNamara : PA
Pa Dt= 0.375 in. Is PA =Pa? Yes -----""----------------Is 1.05 • Dt :S: PA & P8 :S: 1.50 • D1? ____ Y_e_s __ _
PA= 0.491 in.
Pa= 0.491 in.
U1 < 10° UJ = 3 -----Uz<l00 a2= ___ 2 __ _
P1 < 5° P1= _____ 0
P2 < 5° P2= ___ 0 __ _
Z ::S:0.125 in. Z= 0.051 in. -----
_ ...... ~
~ .. ~ y""--.......,-=.~'-.. -=-"':_-. -~· .... ·-· _,,_. ___ ,_-::_ W s0.03125 in. W= 0.017 in. -----
W> 3 inche;,
Z> 3/4 inch
Y 2: 3 inches
W= 4 in. -----
Z = --'0""'.8'-7_5 __ in.
Y= __ 3-._3/....;.4 __ in.
The pilot tube meets the specifications for a calibration factor of0.84? Yes
Temperature Sensor Calibration
Reference· Omega·GL35l2A·
Continuity Check Yes Probe Heat Check 248 Yes
1emperawre 1. emperamre .Lemperature
Source Keterence ;:;ensor Difference
(Meditun) ("F) ("F) (OF)
Probe . AIR 68 69 1 .
AIR 69 · 71 2
Stack ICE WA1ER 33 33 0
BOIL WATER 205 204 1
SIUCONBOIL
Type S Pitot Tube Inspection Data
Date: ---'12;;;;./"'"20"-/_1"'"8 __ Pitot Tube Identification: _____ 3_8_·G_-_2 ___ _
Technician: M. McNamara
.: :: _D_;_,= ____ 0_.3_7_5 __ in. Js PA =PB ? ____ Y_es ___ _
Is I.OS•D, s PA&Pa s l.50•D,? ____ Y_e_s __ _
0.476 in.
PB;= 0.476 in.
a.1 < 1 o• a.1 = l ------a.2<100 a.2= 3 ------
~,, ~I< 5° ~I = ___ 3 ___ •
~2 < 5•
'.!.. ll, .
Z:,;0.125 in. Z = __ o;;..;.·.c..06c..;6 __ in.
~-=i-w ~-··-··-··-··-W :,; 0.03125 in. w = __ o_.0_3_o __ in.
W>3 inches W= 4.75 in. -----
Z >J/4 inch Z= 0.875 in. -----
~-h ....... ,~ ct>
?:i.lolu1~-, ..... -! LJ....all1..J +--.-' ~---·Y?: 3 inches Y= __ 3_1/"'2-'-_in.
The pitot tube meets the specifications for a calibration factor of 0.84? Yes
Temperature Sensor Calibration
Reference· Omega CL3512A
:j . Continuity Check Yes
Heat Check 248 Yes
iemperaiure· .1.emperamre .1 emperature
Source Reference Sensor Difference
(Medium) ("F) ("F) (°E)
Probe I AIR 69 . 70 I
AIR 69 _71' 2
Stack ICE WATER 33 34 I
BOIL WATER 204 205 I
SILICONE OIL
TETCO
Sample Box Temperature Sensor Calibration
Date: l/2/19 Calibrator: Mike McNamara Reference: Ome~CL3512A
Thermocouple Temperature Tem erature Temperature
Unit ID Location Source Reference Sensor Difference
edium ("F) (°F) ("F)
Oven(3) Water 33 33 0
A Water 204 203 -1
ater 33 33 0 Oven(4) Water 204 203 -1
Oven(3) Water 33 33 0
B Water 204 204 0
Water 33 33 0 Oven(4) Water 204 204 .0
Oven(3) Water 33 33 0
C Water 204 205 l
Water 33 33 Oven(4) Water 204 205 l
Oven(3) Water 34 35
D Water 204 205
Water 34 35 1 Oven{4) Water 205 205 ·O
Oven(3) Wat.er 33 34
E .·water 204 205 I
Water 33 3· 1 Oven (4) Water 204 205 l
F Oven Water 33 33 -·o
Water 204 -205 l
G Oven Water 33 34 I.
Wat.er 205 205 0
H Oven Water 33 32 -J
Water 204 205 I
Impinger Out A Water 34 33 · -1
Water 205 205 0
Impinger Out B Water 33 33 ()
Water 205 205 0
Impinger 9ut C Water 34 34 0
Water 205 205 0
lmpinger Out D Water 33 33 0
Water 205 204 -1
Impinger Out E Water · 33 33 0
Water 205 203 -2
Impinger Out F Water 33 33 0
Water 204 203 -1
Impinger Out G Water 33 33 0
Water 205 203 -2
lmpinger Out H Water 33 33 0
Water 205 204 -1
Impinger Out I Water ·33 33 .·o
Water .205 204 -1
lmpinger Out J Water 33 33 0
Water 205 203 -2
Impinger Out K Water 33 33 0
Water 205 204 -1
APPENDIXF
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
F
Prepared for:
Energy Fuels Resources
6425 SHwy91
Blanding, Utah 84511
Date of Report:
January 3, 2020
FOURTH QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
VANADIUM DRYER STACK
VANADIUM PACKAGING STACK
BLANDING, UT AH
October 28-30, 2019
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.
Reviewer. 4LJ IA Mike McNamara -
Date: _ __,_\/-""3'-'-J_?-_O ______ _
Dean Kitchen
Reviewer: _ ___...,,~'---"---"-~-=--.... ~::;...._____,~-=--r..c.~-----~= ......... ---=
Date: __ ---'--/_--=-G_-__ 2]__..0...___ __ _
ii
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ......................................................................................................................... 1
Test Location and Type of Process ...................................................................................... !
Test Dates ............................................................................................................................. I
Pollutants Tested and Methods Applied ............................................................................. .1
Test Participants ................................................................................................................... I
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 Isokinetic Sampling ................................................................................................ 3
Source Operation
Process Control Devices Operation ..................................................................................... 5
Process Representativeness .................................................................................................. 5
Sampling and Analytical Procedures
Sampling Port Location ....................................................................................................... 6
Sampling Point Location ...................................................................................................... 6
Sampling Train Description ................................................................................................. 6
Sampling and Analytical Procedures ................................................................................... 7
Quality Assurance ................................................................................................................ 7
iii
LIST OF TABLES
PAGE
Table
I Measured Radionuclide Emissions ...................................................................................... 3
II Percent Isokinetic Sampling ................................................................................................ 4
Ill Sampling Point Location ...................................................................................................... 6
IV Complete Results, Vanadium Dryer .................................................................. Appendix A
V Complete Results, Vanadium Packaging .......................................................... Appendix A
LIST OF FIGURES
Figure
1 Facility Schematic Representation Vanadium Dryer ......................................... Appendix D
2 Facility Schematic Representation Vanadium Packaging ................................ 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 Vanadium
Dryer and the Vanadium Packaging exhaust stacks. Emissions are calculated in terms of pico
curies per dry standard cubic foot (pCi/dscf) and pico curies per hour (pCi/hr).
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Vanadium containing
material is processed and packed into barrels which are shipped to other facilities for additional
processing. A scrubber serves as the main emission control device for the vanadium dryer. A
baghouse serves as the control device for the vanadium packaging area.
Stack schematics are shown as Figures I and 2 in Appendix D.
Test Dates
Run I on the V anadiwn Dryer and run I on the Vanadium Packaging exhausts were completed
October 28-29, 2019. The second test runs were completed October 29-30, 2019.
Pollutants Tested and Methods Applied
These tests were a determination of radionuclide emissions in accordance with EPA Method
5/114.
Test run filters and front wash residues were sent to Inter-Mountain Labs in Sheridan, Wyoming.
Test Participants
Energy Fuels
TETCO
Logan Shumway
Mike McNamara
Reed Kitchen
1
Steve Snyder
Doug Olsen
Deviations from EPA Methods
None.
Quality Assurance
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 and Vin
Appendix A have more detailed information.
Table I. Measured Radionuclide Emissions
Run# Vanadium Dryer Vanadium Packalring
oCi/dscf pCi/hr pCi/dscf pCi/hr
1 0.046 l.838E+04 0.316 5.049 E+04
2 0.179 7.363E+04 0.237 3.764E+04
AVE 0.112 4.6021E+04 0 .. 277 4.406E+04
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Production data was retained by Energy Fuels
Resources.
Description of Collected Samples
The test filters for the Vanadium Dryer were heavily covered with a dull, lime green colored
particulate. The front washes were clear in appearance.
The test filters for the Vanadium Packaging exhaust were moderately covered with Dark Brown
colored particulate matter. The front washes were brown in appearance.
Discussion of Errors or Irregularities
None
Percent lsokinetic 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.
3
1 98 101
2 97 99
4
SOURCE OPERATION
Process Control Devices Operation
All process control devices were operated normally. Recorded scrubber pressure drop and water
flow rate readings are found in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND ANALYTICAL PROCEDURES
Sampling Port Location
The inside diameter of the Vanadium Dryer exhaust stack was 36 inches. Two, four-inch
diameter sample port were located 9.67 diameters (29 feet) downstream from the last disturbance
and 3.33 diameters (10 feet) upstream from the next disturbance. Figure 1 in Appendix Dis a
schematic of the stack.
The inside diameter of the Vanadium Packaging exhaust stack was 29.5 inches. Two, four-inch
diameter sample ports were located 3.29 diameters (9 inches) downstream from the last
disturbance and more than 6.78 diameters (200 inches) upstream from the last 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 was marked and identified with a wrapping of glass tape and numbered.
These points were determined by measuring the distance from the inside wall.
Sample Distance From the Inside Wall inches
Point Vanadium D er Vanadium Pack.a in
1 1.58 1.00
2 5.26 1.98
3 10.66 3.48
4 25.34 5.22
5 30.74 7.38
6 34.42 10.50
7 19.00
8 22.13
9 24.28
10 26.02
11 27.52
12 28.50
Sampling Train Description
To determine the emission rates for these stacks, 40 CFR 60, Appendix A, Methods 1-5/114 were
followed.
6
All sampling trains were made of inert materials, (Teflon, stainless steel, and glass) to prevent
interference of the sampled gas. The sample consoles used to conduct Methods 1-5/114 were
constructed to meet the specifications outlined in the CFR. The temperature sensors were K-type
thermocouples. Heater, vacuum, and pitot line connections were designed to be interchangeable
with all units used by the tester. A 316 stainless steel probe liner was used for the tests. Figure 3
in Appendix Eis 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 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
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
8
APPENDIX A
Table IV Complete Results, Vanadium Dyer
Table V Complete Results, Vanadium Packaging
Nomenclature
Sample Equations
A
TABLEN
COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UT AH
VANADIUM DRYER
dryer
Symbol Description Dimensions Rllll #1 Run#2
Date 10/28-29/19 10/29-30/19
Filter# 7270 7223
Begin Time Test Began 16:20 13:53
End Time Test Ended 13:12 12:28
Pbm Meter Barometric Pressure In. Hg. Abs 24.24 24.38
,IB Orifice Pressure Drop In. H20 0.842 0.858
y Metc::r Cahlntion Y Factor dimensionleM 0.978 0.978
Vm Volume Gas Sampled-Meler Conditions cf 305.527 304.444
Tm Avg Meter Temperature °F 83.8 81.9
...JM' Sq Rooe Vclociey H~ RooCln.H10 0.3345 0.3352
Wt_ Weight Wat« Collected Grams 269.5 214.7
T, Duration of Test Minutes 480 480
CP Pilot Tube Coefficient Dimeosionloss 0.84 0.84
Dn Nozzle Diametc::r Inches 0.3100 0.3100
CO2 Volume "• Carbon Dioxide Pen:ent 0.80 0.00
02 Volume% Oxygen Percent 20.20 20.50
N2&CO Volume % Nitrogen and Carbon Moooxide Percent 79.00 79.50
Vffistd Volwne Gas Sampled (Standard) dscf 235.628 237.004
Vw Volwne Wlfk:r Vapor scf 12.707 10.123
Bw. (measured) Fraction H10 in Stack Gas (Measured) Fraction 0.0512 0.0410
Bw • c saturated) Fnictioo H20 in StBcl< Gas (Saturated) Fraction 0.0546 0.0461
Bw. Fraction H10 in Slack Oas * Fr:actioo 0.0512 0.0410
x.i Fraction ofD,y Gas Fraction 0.949 0.959
Md Molecular Wt. Dry Gas lbllbmol 28.94 28.82
M, Molecular Wt. Stack Gas lbllbmol 28.38 28.38
%1 Pen,ent bokinetic Pen:ent 98.4 97.0 AVG
Ts Avg Stack Temperature "F 87.6 82.5 85.1
~ Stack Cross Sectiooa1 Area Sq.Ft. 7.069 7.069
Po Stack Slatic Pressure In. H:,O -0.140 -0.140
PbP Sample Port .Baromelric Pressure m.Hg.Abs 24.17 24.31
P, Stack PRsstire In. Hg. Abs 24.158 24.300
Os Stack Gas Volumetric Flow Rate (Std) dscfin 6.73E+o3 6.86E-t-03 6.80E+o3
Q. Stacie Gas Volumetric Flow Rate (Actual) cfin 9.11E+03 9.06E+o3 9.08E+o3
v. Velocity of Slack Oas lj,m 1.29E+o3 l.28E-t-03 l.28E+o3
Curies Radionuclides per sample pCi 10.75 42.37
Radioouclides per blank pCi 0.00 0.00
Net Curies Net Radionuclides per sample pCi 10.75 42.37
Crad Coocentratioo ofRadionuclidcs pCi/dscf 0.046 0.179 0.112
ERrad Emission Rate of Radionuclides pCilhr l.84IE+04 7.363E+04 4.6021E+o4
TABLEV
COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UT AH
V ANDIUM PACKAGING
Symbol Description Dimensions Run#) Run#2
Date 10/28-29/19 I 0/29-30/19
Filter# 7271 7272
Begin Time Test Began 14:43 12:12
End Time Test Ended 11:20 11:45
Pbm Meter Barometric Pressure In. Hg. Abs 24.28 24.38
AH Orifice Pressure Drop In.H20 0.739 0.723
y Meter Calibration Y Factor dimensionless 0.996 0.996
Vm Volmne Gas Sampled-Mete,-Conditions cf 288.106 278.547
Tm Avg Meter Temperature "F 86.0 83.3
~AP Sq Root Velocity Head Root In. H20 0.1828 0.1800
Wtwc Weight Water Collected Grams 6.5 8.0
T, Duration of Test Minutes 480 480
cp Pilot Tube Coefficient Dimensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.3900 0.3900
CO2 Volume % Carbon Dioxide Percent 0.00 0.00
02 Volume % Oxygen Percent 20.90 20.90
N2&CO Vohnne % Nitrogen and Cmban Monoxide Percent 79.10 79.10
Vlllstd Volmne Gas Sampled (Standard) dscf 225.643 220.177
Vw Volume Water Vapor scf 0.306 0.377
Bw s (measured> Fraction H20 in Stack Gas (Measured) Fraction 0.001 0.002
B w s (saturaledl Fraction H20 in StlK:k Gas (Saturated) Fraction 0.018 O.oI5
Bw1 Fraction H20 in StlK:k Gas * Fraction 0.001 0.002
x.i Fraction of[)cy Gas Fraction 0.999 0.998
Md Molec:ular Wt. DI)' Gas lb/lbmol 28.84 28.84
M. Molecular Wt. Stack Gas lb/lbmol 28.82 28.82
%1 Percent lsokinetic Percent 100.9 99.4 AVG
T. Avg Stack Temperature "F 54.4 49.4 Sl.9
A. Stack Cross Sectional Area Sq. Ft. 4.746 4.746
Po Stack Static Pressure In.H20 -0.090 -0.090
PbP Sample Port Barometric Pressure In.Hg.Abs 24.26 24.36
P. StlK:k Pressure In.Hg.Abs 24.248 24.353
Q, Stack Gas Volumetric Flow Rate (Std) dscfin 2.66E+-03 2.64E+-03 2.6SE+o3
Qa Stack Gas Volmnetric Flow Rate (Actual) cftn 3.21E+o3 3.14E+o3 3.17E+o3
Vs Velocity of Stack Gas lj,m 6.76E+o2 6.61E+-02 6.68E+o2
Curies Radioouclides per sample pCi 71.26 5229
Radioouclides per blank pCi 0.00 0.00
Net Curies Net Radionuclidos per sample pCi 71.26 52.29
Crad Concentmtion of Radionuclides pCi/dscf 0.316 0.237 0.277
ERrad F.mi.ssion Rate of Radionuclides pCi/hr 5.049E+o4 3.764E+o4 4.406E+o4
Method S Sample Equations
%1 = Vlllstd • (Ts+ 460) • 1039 / (8 • V, • Ps • ~ • D/)
As= (Ds2 I 4) • 1t
Bws = Vwl (Vlllstd +Vw)
Cr= M1p • 0.01543 / Vlllstd
C x (corr) = Cx (avg) • (20.9 -desired %02) I (20.9 -actual %02)
Dcq = 2 • L • W / (L + W)
Dndcs = v'{0.0269 • (Pbm + 0.0735) /[(Tm+ 460) • CP • Xd • v'[(Ts + 460) •Ms)/ (Ps • Afl)]}
EA= (%02 -0.5 %CO) I [0.264 %N2 -(%02 -0.5 %CO)]
ERp = Cr• Q5 • 0.00857
ERmmatu = ERx / (mmBtu / hr)
K-fact = 846.72 • Dn4 •Mi@• c/ • X/ •Md• Ps •(Tm+ 460) /£Ms• (Ts+ 460) • (Pbm + ~H / 13.6)]
Md = CO2 • 0.44 + 0 2 • 0.32 + N2 •0.28
Ms= (Md•~)+ (18 • Bws)
Ps = PbP + (P0 / 13.6)
Qa =Vs• As
Q9 = Qa • Xd • Ps • Tstd /[(Ts+ 460) • PstJ
Qw= Qs/Xd
Vmstd = Vm • Y • T std• (Pbm + ~H / 13.6) I [Pstd •(Tm+ 460)]
Vs= 85.49 • 60 • Cp • v'Afl • v' [(Ts+ 460) / (Ps • Ms)]
Vw = Wlwc • 0.04715
Xd= 1 -Bws
Method 5 Nomenclature
Tstd = absolute temperature at standard conditions (528°R)
Tt = see 8
Vm = sample volume (ft3) at meter conditions
Vffistd = volume standard (dscf), sample volume adjusted to 68°F and 29.92 inches Hg.
V1 = velocity of stack gas (fpm)
V w = volume water vapor (scf) at 68°F and 29.92 inches Hg.
W = Width of rectangular stack (inches)
Wf-wc = weight of the condensed water collected (grams)
Xd = fraction of dry gas
Y = meter calibration Y -factor (dimensionless)
Method 5 Nomenclature
%I = percent isokinetic, percent
As= stack cross-sectional area (ft:3)
ASdP = see VdP
Btu = unit heat value (British thermal unit)
Bws = fraction of water in stack gas
Cr= concentration of particulate matter, front half (gr/dscf,lb/dscf, etc.)
Cmcta1 = concentration of metals (ppm. µglft:3, etc.) atomic symbol replaces "metal"
CO2 = percent carbon dioxide in the stack gas
CP = pitot tube coefficient (0.84)
Cx (avg)= species symbol replaces x.
Cx (corr)= actual gas concentration corrected to required percent 0 2
dH = orifice pressure drop (inches H20)
dB@ = orifice pressure (inches H20)
D0 = nozzle diameter (inches)
D0 des = calculated desired nozzle size (inches)
dP = stack flow pressure differential (inches H20)
D5 = diameter of the stack (feet)
EA = percent excess air
E~ = emission rate of front half particulate (lb/hr)
E~1u = emission rate per mmBtu or ton of fuel etc.
ERx = emission rate of compound which replaces x
k-fact = multiplier oftest point dP to determine test point m
L = length of rectangular stack (inches)
rnBtu = thousand Btu
Md = molecular weight of stack gas, dry basis (lb/lb-mol)
MF= mass of particulate on filter (mg)
Mpp = mass of particulate matter on filter and probe (mg)
mrnBtu = million Btu
Mp= mass of particulate matter in probe (mg)
M9 = molecular weight of stack gas, wet basis (g/gmol)
N2 = percent nitrogen in the stack gas
0 2 = percent oxygen in the stack gas
VdP = average of the square roots of dP (may also be referred to as ASdP)
Pbm = absolute barometric pressure at the dry gas meter (inches Hg)
PbP = absolute barometric pressure at the sample location (inches Hg)
PO = stack static pressure (inches H20)
P5 = absolute stack pressure (inches Hg)
Pstd = absolute pressure at standard conditions (29.92 inches Hg.)
0 = time oftest (minutes)
Q8 = stack gas volumetric flow rate (acfm)
Q5 = stack gas volumetric flow rate (dscfm)
Qw = wet stack gas std. volumetric flow (ft3/min, wscfin)
Tm = meter temperature (°F)
Ts = stack temperature (°F)
APPENDIXB
Vanadium Dryer
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
Vanadium Packaging
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
B
Prelim 6 pts blank
Facility Enerl!V Fuels
Stack Identification Vanadium Packaging Baimouse
Date
Barometric Pressure
Pbm in Hg PbP in Hg
Static Pressure (P 0) inH20
Estimated Moisture (Bw,) 1 %
Sample Height from Ground 25' feet
Comments:'---------------------
Stack Dia. 29.5 Reference: 0
Ports are __ >_2_50_'_' _Upstream from next disturbance
Ports are 97" Downstream from last disturbance -----
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
I 2.1
2 6.7
3 11.8
4 17.7
5 25.0
6 35.6
7 64.4
8 75.0
9 82.3
10 88.2
11 93.3
12 97.9
1.00
1.98
3.48
5.22
7.38
10.50
19.00
22.13
24.28
26.02
27.52
28.50
1.00
1.98
3.48
5.22
7.38
10.50
19.00
22.13
24.28
26.02
27.52
28.50
Averages:
Ts ----
Af> __ _
LFlow
"Af> ----
KEY=> ._IT_s ___ Af> __ L_F_lo_w ..... 1
J1'i (" Field Data Sheet 1" l-tLJTETCO ;\
Filter Sample BoJC_v-r __
Plant: Enen F.uels )
Date: t -i..i· l'1f7,.J1 1
Location: Vanareer
Operator: ~
Trawne~ Time r. DGM AP Temperatures rr, AH c»H,Ol
Point -..L
1
£
2
1
3 J
10 \,_ .. I I ' . I~ -ft: ., • · 1:1 ·r ~ D • ' I . I I ~ I p p. I I --., I I I I . !, a Q :;,!I I .1 f\C".....,'l"_M,.J:,... ;> t· CJ ,I -·., ... .J. ,._> 1 ::.,; _ ,. -1 , ~ I...-_...
4
5
1
§
6
J it 5 I V • -I H I -' I .,,, , ti )} I a;:±: I .,? j_ I ., ) ? -I I I I , Ji ~ '.'.12 I ;> I 1 Ha•n 1-... -t;t 1 ... r ·
2
> ~ 1 -1 · ":>. n n • 1 · 11 ~ a 1 -~ 1 --2 1 • 1 1 • v n · 1 o 0
--:ti. /a.,.., I ~-} i --, ,,.. A /' ~ • • f /' ,"I .., , / -,I i J ---~ "' ,--...--3
3
~ 4
4
5
1' 5
6 vi
6 I.ti~ 1)
13'./ 't..,-1 u~ ~o
Page _l_or_f_ Run#_/
i ·o N
A
Slack Diameter 36" Port Reference --..!l.::
Pons arc
Pons are
1£'......_ Upstream from next disturbance
29' Downsrream from last disturbance
Assumed Moisture 5-9 o/o
Probe 39' &7 Cp 0.84
w,;;ibration. ';l O . "; \ O · '?. \ D
.'; ·5-tr:i -~-~
Avg D, ~~ inches •; ( 0
Gas.Bag ~ -cJ J
Console_.2
Y -Factor , 7 ]:-S--
aH0 { -S-s-u11 H,O
Barometric Pressures ,{
Pb,. z y-3.5~ in Hg 7,.f, Z V
Pb0 2 '-l · '--"y in Hg z --/ · I 3
Pc; "" C · I '-J in H20
Leak Che,:k:
ll'lmln
~ 0-00~....,
"""'Hg~
Pitot Rote (),0
lnH,0 'kS
Water Collected
Time Sampled
o-o af
L5:
O·o
q.{
,. ~ '; b '1-_) g
min
Total
Average
~ '6-DL-~"\
J r;.J: ,f"). 7 . ')) '1. 'i .J
-z,o,iV,,,.
-~ .... t,
z.\Q [/ v
B+-~
L/ 9 Z, ~ ..,,,-·
~3-~
Review
'J~~D ~
Kn
K •
@T ..
@T.,
-----·· --------------,,-----
DGM hAfore Leak_ Check Vac;("Hg) Rate (ft3/mln) DGM After Leak Check Vac; f"Ha> Rate {ft3/mln) s '-' '~ ,t j'i' 11--0 •Ou7 s-z. l ·°[ « I t '2-0 · OU + ' r "U
·:t
s r1'\ Field Data Sheet
Plant: Ene~ Fuels
Date: JO L'}, )0 /1 C>\ft I
Tra~ Time DGM
Poil!I Clock Min (9) ,11•, -1
TETCO ,\
Filter 1 J.,::/·} Sample Box_n __
Location: Van~i}lm Dryer
Operator:~
AP I AH ("'H,01 I Vacuum I Ternperarun:s,.,,
'" """ Desired I Actual ,in w,1 Stack (T,) I Probe I Oven I CPM Filter
DGMTrmp(T~l
Out In
Page---f:-.or-f--Run# 'Z_.
i ·o N
A
i 1 Stack. Diameter 36" Port Reference __ O_"
~
s-
f
2
i
i
1
4
5
~
~
6
2
2
3
3
Pons are
Pons are
~ ~I I U 'Y t 1 < f'~ ~ ' I ' 1 -< n----.fr-il ' · I ; I -· ~, I I ~ I ~ 1 U 11 · I 7" ' -, __ , __ .-.ii> A-, 'L?J,S J_P 'ii .. ~ ~z ~>;:,.
4
5
1' ---1....,i I n --· n • -u · · 1 · · R 1 1 1 --1 ---'9 1 • 1 1 , • n 1 1 1 • Li , , n 1 .-. ,,,,,._ I ... , r _ , ~ ~ ---->t I. l ~ . l I I A _ --
6
6
Total
Average )o'I. '-ll/i.f
Addltlonal (Extra) Leak Check lnfo~JJ'JJ..
DGM before Leak Check Vac ("H ~~--¥'
Rate (ft3/mln
o·oos-
1'l1C\ ./
la\ -1
Vac ("H
~
!Q'._ Upstream from next disturbance
29' Downstream from last d isturbancc
~ %
Probe Cp ~
Nozzle Calibration L
· 3tv ~;co _. 3~0 . 3 D
Avg o.~ inches
Gas Bag~
Console ___ _
Y-Factor -"i d"Y
AH0 f ·S-c[Qin H20
Barometric Pressures
Pb., Z, <../, ·Z.. 0
Pb z_,'-f.(J
Po
0 ~ oJ q
in Hg 1,, I-{ .l>5
in Hg 1 . .'\-~(J
Leak Cl,«k;
ft'tmin
voe In Hg
PilDI Rate
lnH,0
inH,O
Pre c:--f2fil 0--6 C),;J d.oc, '::,'
7.,1., _U:.
0 -0 t) ,D
_j~ ~
Water Collected ?.1~·1
Time Sampled '-{*15
Review '®
K= @Tm
K • @T.,
I' r)
g
min
l'relim 6 pts blank
Facility Ener~ Fuels
Stack Identification Vanadium Dryer
Date
l Barometric Pressure
B Pbm in Hg PbP in Hg
N 0 Static Pressure (P 0 ) inH20
Estimated Moisture (Bw.) 5-9 %
I
Sample Height from Ground 70' feet
A
Comments:
Stack Dia 36 Reference: 0
Ports are 10' Upstream from next disturbance
Ports are 29' Downstream from last disturbance
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
1 4.4 1.58 1.58
2 14.6 5.26 526
3 29.6 10.66 10.66
4 70.4 25.34 25.34
5 85.4 30.74 30.74
6 95.6 34.42 34.42
Averages:
Ts LFlow --------
~p .J~ --------
KEY =>1 ... r_s ___ ~_P __ L_F_l_ow ..... l
l \"1 /.s. Field Data Sheet
TETCO
Filter 121 \ Sample Box__fi__
1a/tPf(1
Plant: Energy Fuels
Date: I a /?, II t 'I
T,..,.,... Time
Point Clock Min(0)
Jl.j:'l~ 0
£ II 211
1
.1
5
§
7
~
9
10
.11
12
2
3
4
~
§
7
~
.i
10
11
12 ---u:z.o
DGM 6.P
<n~,
Location: Vanadium Packaging Baghouse
Operator. f/1, ~ ~NU,,)M.~ ( lb,
I 6.H I" H,0) I Vacuum I Temperatures m 1 ! Probe I Probeoud
Total _l_aB.lo~ 8..,_ / v / •.. _ ..J'i.l -rS 11.1Jo ~
Average_ v • 182,.~ ,1'.)'i S'i-'1
DGM before Leak Check Vac ("Hg) Rate (tt3/mln) DGM After Leak Check
t.j 1-z.~
8~-0
Vac ("Ha)
Page _·_I _of_~_ Run# _L
i A Bo N
Stack Diameter 29.5'' Port Reference O"
Ports are
Ports are
/
> 250" Upstream from next disturbance
97" Downstream from last disturbance
Assumed Moisture 1 %
Probe 38 l, ·-2,.. Cp~
• Nozzle Calibration
.3qo .~'IQ .~ ~
Avg D0 • l CO, 0 inches
Gas Bag Ambient Air
Console ____k
Y-Factor -• Cf'1(.o
6.H0 I, (4 lo in H20
Barometric Pressures
Pbm 2. '1, 3-{'
Pb0 'Z. L1. '3 3
in Hg
in Hg
inH20
10/l'fl 't
Z "l,Z.'0
:&.'1· 18
Pa -• o,
Leak Check: Pre
ft'lmin ().OQk
wcinHg~
PitotRate o.o
fQfil
0.002.
,o.o
o·O
InH20 ~ -'i JO'" ~
'l,•'3 "Z-• '3
Water Collected ~.{'
Time Sampled __if O
Review
K~
Ka
~
@Tm
@Tm
g
min
Rate (ft:3/mln)
---6q,{(<3~ JJ.tr I
I 1~/ ,r Field Data Sheet
Plant: En:,; Fuels
Date: \0 'l.j / ti
Tni"""' Time N DGM
TETCO B
Filter 1 Z. .,_Z. Sample Box __
Location: Vanadium Pac~g ~house
Operator: M-. MScl~a...C
Temperatures m DOM Temp <T.}
Page_L_of_L_ Run# 2-
i A sQ . N
Poinl Clock Min (BJI en'>
I AP I AH (h K,0) I Vl<IIUnl
C• a,01 Desired I Actual Probe I Probe Out I Filter Effluentl Out In
1 l~J2.
2
3
4
5
2
7
8 I 9
1Q
11
12 'I.~ I
IC/~,,-1 11: 'f
2
3
4
~
~
I
~
!
10
11
12
Total
Avera~
----
0
zo
"40
(,o
Bo
-
, ,..,o
'2.18. 5~1".J 'i-32ol ./ n.J<.o/ ~/
'11. "i ..; .,eoo _,-rl.:}
-----, -----------
DGM before Leak Check Vac ("Hg) Rate (ft'lmln) DGM After Leak Check
S1aek Diameter 29.5" Port Reference _ ___Q'.'.
Ports are > 250" Upstream from next distwbance
Ports are 97" Downstream from.iast disturbance
Assumed Moisture 1 %
Probe 38 l,'.-2. Cp~
Nozzle Calibration
~ ·?>'Jo .~cto ,3'to
AvgD0 • 390 inches
Oas Bag Ambient Air
Console __.Ip __
Y-Factor~
AH0 ~inH20
Barometric Pressures
Pb,. 2'1·2.0
Pbo 'Z'1 . I a
in Hg t:~ '{J
inHg 'Z,'-t.. S 5
~ '11'-' /
83.3
P0 -. o? inH20
Lealc Check: fu fl!fil
ft'lmin G, 00':f O· 00'2..-
ncinHg '2.Q .o IQ·P
Pik>IRale f>. 0
lnH,O ~
Water Collected
Time Sampled
Review
K~
K=
fH2
J.!..:!'.
'd.O
'18'2
~
~~(fl\~
@T.,
®_T,.
Vac ("Hg) Rate (ft3/mln) .u-tf 111
g
min
APPENDIXC
Vanadium Dryer
Sample Recovery
Gas Analysis Data (ORSAT)
Vanadium Packaging
Sample Recovery
Gas Analysis Data (Ambient Air)
Lab Analysis
Chain of Custody
C
Method 5
Facility: Fnllrgv Fuels Date:
Stack Identification: Vru111dium Dryer Scmbber Method:
IMPJNGERS
Filter Number:
1?'70
JMPlNGERs
Filter Number:
JMPJNGERS
Filter Number:
Run: ----
2 ==
Sample Box:
lm_tger Number
I 4 I ,J.,,
Initial Volume ofliquid (H20) in impingers, (ml)
/'. v---,-----
6
Run:_ ..... 1;_·__ SampleBox: ___ 4 __
Im_tger Number
6 -I 3 I 4 I s ..1. 2
Initial Volume ofliquid (H20) in unpingers. (ml)
100
Run: ----Sample Box: ----
1 2
lminger Number I 3 I 4 I 5 .L
Initial Volum.e ofliquid (H20) in impingers, (ml)
100 lUO I I :'\ti I
Final (g) ___ --+----+-----t-------,1-----+----
Initial (g)------------+------.1---------Net (g) ===============::i!:================
Total (g) ========
5
/(l/),J'";)-7 /1 7
Initials
fU I
Plant t At> <-i ---/ r:,,,..._ ~ ) . _______ .......__--'-----'-11'----L-----
c /.. f /.L--Analytical Method ____________ _
I
Date ru/z 'i
Test No. l
Gas Bag No. l=--r ~
Ambient Temp -=f_ D
Operator th
Date 10 /3 0
Test No. ?-
Gas Bag No. J2 ~ (1 ':l
Ambient Temp~
Operator
Date -----
Test No.-----
Gas Bag No.-----
Ambient Temp ____ _
Operator ____ _
Gas
CO2
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N2 (Net is I 00 Minus
Actual 0 2 Reading).
Gas
CO2
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N1 (Net is 100 Minus
Actual 0 2 Reading).
Gas
01 (Net is Actual 02
Reading Minus Actual
CO2 Reading).
N1 (Net is 100 Minus
Actual 0 2 Reading).
Actual
Readinc
(>}
2 I .o
Aclllal
Readinc
0
ZU-~
Actual
Readinc
I ) s·· I / // Location'---__ v_'--_ .. _~__,,c:...1 _"-V\..,--=::...L...--....:·"'--Ci_1_(/"_0_· _,..,_,..._-__
RUN
2 3 Average
Ner Actual Net Actual Net Net
Readinc Reoinc Volume
Q . o~-Q. O)· {).), CJ.~
2.-+u-~c) 2 /-v
2UL -Z/ ·o 2. UL 2o-c ?.. o_ z..
RUN
2 3 Average
Ner Achlal Net Actual Net Net
Rcadinc Rcadinc Volume
6 u 0 0 C) 0
-z..u.r 2,.0,5 20-) 2-d -)-20.s-Z.cJ . s-
RUN
2 3 Average
Net AcfWII Net Actual Net Net
Readin& Rcadinc Volume
to2 was determined using a gas analyzer
CO is not measured, as it bas the same molecular weight as N2
Method 5
Date: Facility: rncrgv Fuels --------
Stack Identification: V IUlD.dium i)nckag.ing liaghouse Method: ___ ....;•::.....5 ---
WfINGERS
Filter Number:
JMPlNGERS
Filter Number:
Final (g)
Initial (g)
Net (g)
Run:
l
lllO
Run:
..L
lOO
(o 12.. \o
71(,. 'I
-lfJ. '()
----Sample Box:_b __ _ 1t?/;-r-;1 /1t
lmiger Number
6 2 -I .J.. I 5 -Initials
initial Volume of liquid (H20) in impingers, (ml)
l--Sample Box: ----
lyger Number
.J.. I J I .J.. I -L
Initial Volume ofliquid (1-120) in impiogers, (ml)
IUO I I !R1 I
1}q. I (,U.i;> ~t.f3 .L{
? 11.. l/ t,oy_,. !r/1i.C/
t(o,,-1t.1,~ 20.0
---·--------·-
IMPINGERS
Run: ----Sample Box: ___ _
Filter Number: Jm_tger Number
I .!. I + 6 I
Initial Volume of liquid (1-120) in impingcrs, (ml)
((IO lllO I I S{l I
Final (g) ____________ ....,_ __ ---i..-------
Initial (g) ___ --t-----------------1----
Net(g) =========c:::!:===================
Total (g) ========
uitt INTEJI-.MOUIITAltl LASS
!Bl FedEx
CJ USPS
CJ Hand Carried
CJ Other
Inter-Mountain Labs
Sheridan, WY and Gillette, WY
7:00 7270 Vanadium Scrubber RUN 1
7:00 7271 Vanadium Baghouse RUN 1
7:00 7273 Vanadium Scrubber RUN 2
7:00 7272 Vanadium Baghouse RUN 2
7:00 , 7270 Vanadium Scrubber RUN 1
7:00 7271 Vanadium Baghouse RUN 1
7:00 7273 Vanadium Scrubber RUN 2
7:00 7272 Vanadium Baghouse RUN 2
Soil SL Standard turnaround
Solid SD RUSH -5 Working Days
Filter FT URGENT -< 2 Working Days
Other OT Rush & Urgent Surcharges will be applied
I Matrix
FT 1
FT 1 X
FT 1 X
FT 1 X
OT 1 X
OT 1 X
OT 1 X
OT 1 X
I PWSID / Permit # .' >·:
Inter-Mountain Labs, Inc. www.intermountainlabs.com
Page 1 of 1
#WEB
REMARKS
X X X X X X
X X X X X X
X X X X X X
X X X X X X
X X X X X X
X X X X X X
X X X X X X
: ~·: ;~~ .. : . · Contact at Ener
Rev4.6Web
~AnaJytical•_F_o_r_m_e_ny __ ln_te_r-_M_o_u_nt_a_in_L_a_bo_r_at_o_ri_es ________________________________________ ~
( /' """ 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
Project:
Lab Order:
Energy Fuels (White Mesa)
Vanadium Dryer Scrubber Packaging Baghouse
S1911054
Date: 12/27/2019
CASE NARRATIVE
Report ID: S 1911054001
Samples 7270 Vanadium Scrubber RUN 1 Filter & Beaker, 7271 Vanadium Baghouse RUN 1 Filter & Beaker, 7272
Vanadium Baghouse RUN 2 Filter & Beaker and 7273 Vanadium Scrubber RUN 2 Filter & Beaker were received on
November 6, 2019.
All samples were received and analyzed within the EPA recommended holding times, except those noted below in this case
narrative. Samples were analyzed using the methods ouUined in the following references:
"Standard Methods For The Examination of Water and Wastewater", approved method versions
Test Methods for Evaluating Solid Waste, PhysicaUChemical Methods, SW-846, 3rd Edition
40 CFR Parts 136 and 141
40 CFR Part 50, Appendices B, J, L. and 0
Methods indicated in the Methods Update Rule published in the Federal Register Friday, May 18, 2012
ASTM approved and recognized standards
All Quality Control parameters met the acceptance criteria defined by EPA and Pace Analytical (Formerly Inter-Mountain
Laboratories) except as indicated in this case narrative.
The uranium isotopes U234, U235, and U238 ratios are typical for the analysis of natural uranium. The quality checks for
mass balance of both uranium and thorium meet expectations.
The Regulatory Required Detection Limit (RRDL) was not met for thorium species due to procedureal, matrix and expected
air volumes of 6,000,000 ml.
A } /I.--?' <"' Reviewed by: vf/,t:'/ -
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 1
ILceAmMif,a(_F_o_r_m_e_r1.y_1n_te_r_-M_o_u_n_ta_in_La_bo_ra_t_o_rie_s _____________________ _
(/' uu, 1673 Terra Avenue Sheridan, WV 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 12/27/2019
391 East 620 South Report ID S 1911054001
American Fork, UT 84003
ProjectName: Vanadium Dryer Scrubber Packaging Baghouse Work.Order: S1911054
lab ID: S 1911054-001 CollectionDate:
ClientSample ID: 7270 Vanadium Scrubber RUN 1 Filter & Beaker Date Received: 11/6/2019 9:30:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments Sam led 10/28-29 2019
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCl/ml
Radionuclides -Filter
Lead 210 7.9E-6 µCl/Sample 2E-06 6E-14 OTW01 12/20/2019 945 AEF
Lead 210 Precision(±) 2.6E-6 µCi/Sample OTW01 12/20/2019 945 AEF
Radium 226 2E-7 µCl/Sample 2E-07 9E-14 SM 7500RAB 11/20/2019 1108 WN
Radium 226 Precision (±) 1E-7 µCi/Sample SM 7500RAB 11/20/20191108 WN
Radium 228 -2.4E-6 µCi/Sample 1E-06 21;-13 Ga-Tech 12/07/20191853 WN
Radium 228 Precision (±) 2.6E-5 1,1Ci/Sample Ga-Tech 12/07/2019 1853 WN
Thorium 230 4E-7 µCi/Sample JE-15 JE-15 ACWlO 12/1812019 1544 WN
Thorium-230 Precision (±) JE-7 µCi/Sample ACW10 12/1812019 1544 WN
Thorium 228 OE-7 µCi/Sample JE-15 JE-15 ACW10 12/18/2019 1544 WN
Thorium-228 Precision (±) lE-7 µCi/Sample ACW10 12/18/2019 1544 WN
Thorium 232 OE-7 µCi/Sample 3E-15 JE-15 ACW10 12/18/2019 1544 WN
Thorium-232 Precision (±) lE-7 µCi/Sample ACW10 12/18/2019 1544 WN
Uranium 234 1.3E-6 µCl/Sample 4E-07 9E-15 ACWOl 12/20/20191147 WN
Uranium 234 Precision (±) 8E-7 µCi/Sample ACWOl 12/20/20191147 WN
Uranium 235 1.4E-7 µCi/Sample 4£-07 9£-15 ACWOl 12/20/20191147 WN
Uranium 235 Precision (±) 3E-7 µCl/Sample ACWOl 12/20/2019 1147 WN
Uranium 238 8.lE-7 µCi/Sample 4E-07 9E-15 ACWOl 12120/2019 1147 WN
Uranium 238 Precision (±) 6E-7 µCi/Sample ACWOl 12/20/20191147 WN
Metals • Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 11/22/20191251 MS
Uranium 3 µg/Sample 1 9E-15 EPA 200.8 11/22/2019 1251 MS
These results apply only to the samples tested. RL • Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blank C Calculated Value
E Value above quantitation range G Analyzed at IML Gillette laboratory
H Holding times for prepal'lltion or analysis exceeded J Analyte detected below quantitation limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at the Repol1ing Limit o OUtslde the Range or Dilialons
S Spike Recovery OUISide accepted recovery Umits U Analysis reported under the repol1ing limit
X Malrix Effect
Reviewed by: ... eld:......a-~-----------~--------_-_-:_-__ _
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 4
.-------·---------------------------------------~
~Ana1ytir,al·~F_or_m_e_rt_y_1_nt_e_~_M_o_u_n_ta_in __ La_b_o_r_at_o_ri_es ____________________________________________ _
(.../' u"' 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 12/27/2019
391 East 620 South ReponlD S1911054001
American Fork, UT 84003
ProjectName: Vanadium Dryer Scrubber Packaging Baghouse WorkOrder: S1911054
lab ID: S1911054-003 CollectionDate:
ClientSample ID: 7273 Vanadium Scrubber RUN 2 Filter & Beaker Date Received: 11/6/2019 9:30:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments Sam led 10/28-29 2019
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 1.2E-5 µCi/Sample 2E-06 6E-14 OlW01 12/20/2019 945 AEF
Lead 210 Precision (±) 3.lE-6 µCi/Sample OlW01 12/20/2019 945 AEF
Radium 226 2E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 11/20/20191108 WN
Radium 226 Precision (±) 1E-7 µCi/Sample SM 7500RAB 11/20/2019 1108 WN
Radium 228 -4.4E-6 µCi/Sample 1E-06 2E-13 Ga-Tech 12/08/2019 059 WN
Radium 228 Precision (±) 1.7E-5 µCi/Sample Ga-Tech 12/08/2019 059 WN
Thorium 230 1.6E-6 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-230 Precision (±) 6E-7 µCi/Sample ACW10 12/18/2019 1544 WN
Thorium 228 3E-7 µCi/Sample 3E-15 3E-15 ACW10 12/18/20191544 WN
Thorium-228 Precision (±) 2E-7 µCi/Sample ACW10 12/18/2019 1544 WN
Thorium 232 OE-61E-7 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-232 Precision (±) OE-61E-7 µCi/Sample ACW10 12/18/20191544 WN
Uranium 234 1.5E-5 µCi/Sample 4E-07 9E-15 ACWOl 12/20/2019 1147 WN
Uranium 234 Precision (±) 3E-6 µCi/Sample ACW01 12/20/20191147 WN
Uranium 235 1.7E-7 µCi/Sample 4E-07 9E-15 ACW01 12/20/20191147 WN
Uranium 235 Precision (±) 3E-7 µCi/Sample ACW01 12/20/20191147 WN
Uranium 238 1.3E-5 µCi/Sample 4E-07 9E-15 ACW01 12/20/20191147 WN
Uranium 238 Precision (±) 3E-6 µCi/Sample ACW01 12/20/20191147 WN
Metals· Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 11/22/2019 1258 MS
Uranium 69 µg/Sample 1 9E-15 EPA 200.8 11/22/2019 1258 MS
These results apply only to the samples tested. RL -Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blank C Calculated Value
E Value above quantltallon range G Analyzed at IML Gillette laboratory
H HOiding limes for preparation or analysis exceeded J Analyte detected below quantitalion limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at lhe Reporting Limit 0 Outside the Range or DillAions
S Spike Recovery outside accepted rea:Nery Omits U Analysis reported under the reporting limit
X Matrix Effect
~/J.-4" ~
Reviewed by: .. ~i;;..w--~---------------
Wade Nieuwsma, Assistant Laboratory Manager Page 3 of 4
~Ana1ytical·-F_o_r_m_e_~y __ 1n_te_r_-tv1_o_u_n_ta_in __ La_bo __ ra_t_o_rie_s ______________________________ ~----~----~
(./' '"" 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 12/27/2019
391 East 620 South Report ID S1911054001
American Fork, UT 84003
ProjectName: Vanadium Dryer Scrubber Packaging Baghouse Work.Order: S1911054
Lab ID: S1911054-002 CollectionDate:
ClientSample ID: 7271 Vanadium Baghouse RUN 1 Filter & Beaker DateReceived: 11/6/2019 9:30:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments Sam led 10/28-29 2019
Analyses Result Units Qual RL RRDL Method Date Analyzedllnit µCi/ml
Radionuclides -Filter
Lead 210 4.lE-5 µCi/Sample 2E-06 6E-14 OTW01 12/20/2019 945 AEF
Lead 210 Precision (:1:) 4.4E-6 µCi/Sample OTW01 12/20/2019 945 AEF
Radium 226 9E-7 µCi/Sample 2E-07 9E-14 SM7500RAB 11/20/20191108 WN
Radium 226 Precision (:1:) 3E-7 µCi/Sample SM7500RAB 11/20/2019 1108 WN
Radium 228 6E-7 µCi/Sample lE-06 2E-13 Ga-Tech 12/07/2019 2156 WN
Radium 228 Precision (:1:) 4.2E-5 µCi/Sample Ga-Tech 12/07/2019 2156 WN
Thorium 230 2.lE-5 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-230 Precision (:1:) 2.7E-6 µCi/Sample ACW10 12/18/2019 1544 WN
Thorium 228 1.7E-7 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-228 Precision (:1:) lE-7 µCi/Sample ACW10 12/18/20191544 WN
Thorium 232 4E-8 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-232 Precision (:1:) 1E-7 µCi/Sample ACW10 12/18/2019 1544 WN
Uranium 234 2.7E-6 µCi/Sample 4E-07 9E-15 ACW01 12/20/2019 1147 WN
Uranium 234 Precision (:1:) lE-6 µCi/Sample ACW01 12/20/20191147 WN
Uranium 235 2.5E-7 µCi/Sample 4E-07 9E-15 ACW01 12/20/20191147 WN
Uranium 235 Precision (:1:) 4E-7 µCi/Sample ACW01 12/20/2019 1147 WN
Uranium 238 4.6E-6 µCi/Sample 4E-07 9E-15 ACW01 12/20/2019 1147 WN
Uranium 238 Precision (:1:) 1E-6 µCi/Sample ACW01 12/20/2019 1147 WN
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 11/22/2019 1255 MS
Uranium 17 µg/Sample 9E-15 EPA 200.8 11/22/2019 1255 MS
These results apply only to the samples tested. RI. • Reporting Limit
Qualifiers: B Analyl:e detected in the associated Method Blank C Calculated Value
E Value above quantitatlon range G Analyzed at IML Gfflette laboratory
H Hokffng limes ror preparation or analysis exceeded J Analyte detected below quan11tation Hmils
L Analyzed by another laboratoly M Value exceeds Monthly Ave or MCL or is less than LCL
ND NOi Detected at the Reporting Limit 0 Outside the Range of DHWlllS
S Spike Recovery outside accepted recovery limits U Analysis reported under the reporting limit
X Matrix Effect
~/}-, r" Reviewed by: .. ~ ........ '-~---..____ _______ _
Wade Nieuwsma, Assistant Laboratory Manager Page 2 of 4
I ~A1Ja/)1ica( Formerly !mer-Mountain Laboratories
(../' av, 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
Company:
Sample Analysis Report
Energy Fuels (White Mesa)
ProjectName:
lab ID:
391 East 620 South
American Fork, UT 84003
Vanadium Dryer Scrubber Packaging Baghouse
S 1911054-004
ClientSample ID: 7272 Vanadium Baghouse RUN 2 Filter & Beaker
COC: WEB
Comments Sam led 10/28-29 2019
Date Reported 12/27/2019
Report ID $1911054001
Work Order: $1911054
CollectionDate:
DateReceived: 11/6/2019 9:30:00 AM
FieldSampler:
Matrix: Filter
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCl/ml
Radionuclides • FIiter
Lead 210 2.8E-5 µCi/Sample 2E-06 6E-14 OTWOl 12/20/2019 945 AEF
Lead 210 Precision(±) 3.1 E-5 µCi/Sample OTW01 12/20/2019 945 AEF
Radium 226 5E-7 µCi/Sample 2E-07 9E-14 SM7500RAB 11/20/20191108 WN
Radium 226 Precision (±) 2E-7 µCi/Sample SM 7500RAB 11/20/2019 1108 WN
Radium 228 -4. 1 E-6 µCi/Sample lE-06 2E-13 Ga-Tech 12/08/2019 402 WN
Radium 228 Precision (±) 1.BE-5 µCi/Sample Ga-Tech 12/08/2019 402 WN
Thorium 230 1.5E-5 µCi/Sample 3E-15 3E-15 ACWlO 12/18/20191544 WN
Thorium-230 Precision (±) 2.lE-6 µCi/Sample ACW10 12/18/20191544 WN
Thorium 228 4E-8 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-228 Precision (±) lE-7 µCi/Sample ACW10 12/1 B/2019 1544 WN
Thorium 232 BE-8 µCi/Sample 3E-15 3E-15 ACW10 12/18/2019 1544 WN
Thorium-232 Precision (±) 1E-7 µCi/Sample ACW10 12/18/2019 1544 WN
Uranium 234 4.4E-6 µCi/Sample 4E-07 9E-15 ACW01 12/20/20191147 WN
Uranium 234 Precision (±) 2E-6 µCi/Sample ACWOl 12/20/2019 1147 WN
Uranium 235 1.7E-7 µCi/Sample 4E-07 9E-15 ACW01 12/20/2019 1147 WN
Uranium 235 Precision (±) 3E-7 µCi/Sample ACWOl 12/20/2019 1147 WN
Uranium 238 4.lE-6 µCi/Sample 4E-07 9E-15 ACWOl 12/20/20191147 WN
Uranium 238 Precision (±) 2E-6 µCi/Sample ACWOl 12/20/20191147 WN
Metals • Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 11/22/2019 1302 MS
Uranium 13 µg/Sample 9E-15 EPA 200.8 11/22/20191302 MS
These resutts apply only to the samples tested. RL • Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blank C Calculated Value
E Value above quantitation ral'lQe G Analyzed al IML GiHette laboratory
H Holding limes ror preparation or analysis exceeded J Analyle detected below quanlltation Hmils
L Analyzed by anolher laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected al 1he Reporting Limit o OUtside the Range or Dllwons
S Spike Recove,y outside accep(ed recavery limits U Analysis repolted under 1he reponing limit
X Mab'ix Erfect
Reviewed by: .. dd-..-.... ~-----------_-:::===~---
Wade Nieuwsma, Assistant Laboratory Manager Page 4 of 4
~AnaJytical·~F_or_rn_e_r_ly_l_n_te_r_-M_o_u_n_ta __ in_L_a_bo __ ra_t_o_ri_e_s ____________________________________________ ~
(../' u"' 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
ANAL VTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa) Date: 12/27/2019
ReportlD: S1911054001 Work Order: S1911054
Project: Vanadium Dryer Scrubber Packaging Baghouse
Lead 210 in Filters
MB-765 (12/19/19 15:26)
Analyte
Lead 210
Lead 210 in Filters
LCS-PB (12/19/19 15:26)
Analyte
Lead 210
Lead 210 in Filters
MS (12/19/19 15:26)
Analyte
Lead 210
Lead 210 in Filters
MSD (12/19/19 15:26)
Analyte
Lead 210
Radium 226 Air Filter Analysis
MB-2085 (11/20/19 11 :08)
Analyte
Radium 226
Radium 226 Air Filter Analysis
LCS-2085 (11 /20/19 11 :08)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MS-2085(11/20/1911:08)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MSD-2085 (11 /20/19 11 :08)
Analyte
Radium 226
Qualifiers: B Analyte detected in the associated Method Blank
G Analyzed at IML Gillette laboratory
J Analyte detected below quantltation limits
ND Not Detected at the Reporting limit
R RPO outside accepted recovery limits
X MatrixEffect
Units: µCi/Sample Sample Type MBLK
RunNo:174862
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND 2E-06
Sample Type LCS Units: µCi/Sample
RunNo:174862
Result RL Spike Ref Samp %REC % Rec Limits Qual
lE-05 2E-06 lE-05 104 66-130
Sample Type MS Units: µCi/Sample
RunNo:174862
Result RL Spike Ref Samp %REC % Rec Limits Qual
1E-05 2E-06 1E-05 ND 95.1 66-130
Sample Type MSD Units: µCi/Sample
RunNo:174862
Result RL Cone %RPD %REC % RPD Limits Qual
lE-05 2E-06 1E-05 9.83 105 30
Sample Type MBLK Units: µCi/Sample
RunNo: 173910 PrepDate: 11/12/19 0:00 BatchlD 16835
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND
Sample Type LCS
2E-07
Units: µCi/Sample
RunNo: 173910 PrepDate: 11/12/19 0:00 BatchlD 16835
Result RL Spike Ref Samp %REC % Rec Limits Qual
6E-06
Sample Type MS
2E-07 7E-06
Units: µCi/Sample
88.1 67.1 -122
RunNo: 173910 PrepDate: 11/12/190:00 BatchlD 16835
Result RL Spike Ref Samp %REC % Rec Limits Qual
6E-06 2E-07 7E-06 ND 79.3 65 -131
Sample Type MSD Units: µCi/Sample
RunNo: 173910 PrepDate: 11/12/19 0:00 BatchlD 16835
Result RL Cone %RPD %REC % RPD Limits Qual
6E-06 2E-07 6E-06 3.57 82.1 20
E Value above quantitation range
H Holding times for preparation or analysis exceeded
L Analyzed by another laboratory
o Outside the Range or Dilutions
S Spike Recow,y outside accepted recovery limits
Page 1 of 3
~AnaJyticaJ•--Fo_r_rne __ rt_y_l_n_te_r_-M_o_u_n_t_ai_n_L_a_b_o_ra_t_o_rie_s ______________________________________________ _
(_.,,raw; 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
I
CLIENT:
Work Order:
ANAL VTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1911054
Project: Vanadium Dryer Scrubber Packaging Baghouse
Date: 12/27/2019
ReportlD: $1911054001
Thorium Air Filter Analysis Sample Type MBLK Units: µCi/Sample
MB-711 (12/18/1915:44) RunNo: 174858
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium-228
Thorium-230
Thorium-232
Thorium Air Filter Analysis
LCS-711 (12/18/19 15:44)
Analyte
Thorium-230
Thorium-232
Thorium Air Filter Analysis
LCSD-711 (12/18/19 15:44)
Analyte
Thorium-230
Uranium Isotopic Filters
MB-R175002 (12/20/1911:47)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
LCS (12/20/19 11:47)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
Qualifiers:
LCSD (12/20/1911:47)
Analyte
B
G
J
ND
R
X
Uranium 234
Uranium 235
Uranium 238
Analyte detected in the associated Method Blank
Analyzed al IML Gllette laboratay
Analyte detected below quantitation limits
Not Detected at the Reporting Limit
RPD outside accepted recovery limits
Matrix Effect
ND 2E-07
ND 2E-07
ND 2E-07
Sample Type LCS Units: µCi/Sample
RunNo: 174858
Result RL Spike Ref Samp %REC % Rec Limits Qual
lE-05 2E-07 lE-05 110 68-146
lE-05 2E-07 lE-05 105 68-146
Sample Type LCSD Units: µCi/Sample
RunNo: 174858
Result RL Cone %RPO %REC % RPO Limits Qual
lE-05 2E-07 lE-05 8.90 100 20
Sample Type MBLK Units: µCi/Sample
RunNo:175002
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND 4E-07
ND 4E-07
ND 4E-07
Sample Type LCS Units: µCl/Sample
RunNo: 175002
Result RL Spike Ref Samp %REC % Rec Limits Qual
9E-06 4E-07 7E-06 132 50 -150
3E-07 lE-07 3E-07 101 50-150
9E-06 4E-07 7E-06 126 50-150
Sample Type LCSD Units: µCi/Sample
RunNo:175002
Result RL Cone %RPO %REC % RPD Limits Qual
8E-06 4E-07 9E-06 5.24 125 20
4E-07 lE-07 3E-07 7.69 109 20
9E-06 4E-07 9E-06 3.36 130 20
E Value above quantitatlon range
H Holding limes for preparation or analysis exceeded
L Analyzed by another laboratory
0 Outside the Range of DIiutions
s Spike Rec:overy outside accepted recovery limits
Page 2 of 3
~Ana/ytiCa/•--Fo_r_rn_e_rl_y_ln_t_e_r-_lVl_o_u_nt_a_in_L_a_bo __ ra_t_o_ne_s ____________________________________________ ~
(./' u"' 1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
Work Order:
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1911054
Project: Vanadium Dryer Scrubber Packaging Baghouse
Date: 12/27/2019
Report ID: S 191 1054001
Total (3050) Metals by EPA 200.8-Soil Sample Type MBLK Units: µg/Sample
MBLK (11/22/19 12:08) RunNo: 173950
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium
Uranium
Total (3050) Metals by EPA 200.8-Soil
LCS (11 /22/19 12:05)
Analyte
Thorium
Uranium
Total (3050) Metals by EPA 200.8-Soil
S1911054-004AS (11/22/1913:09)
Analyte
Thorium
Uranium
Total (3050) Metals by EPA 200.8-Soil
S1911054-004AMSD (11/22/19 13:12)
Analyte
Thorium
Uranium
Total (3050) Metals by EPA 200.8-Soil
Qualifiers:
S1911054-004AD (11/22/1913:05)
Analyte
B
G
J
ND
R
X
Thorium
Uranium
Analyte detected in the associated Method Blank
Analyzed at IML Gillette laboral<Jly
Analyte detected below quantitation lknlts
Not Detected at the Reporting Limit
RPD outside accepted recoveiy llmits
Matrix Effect
ND
ND
Sample Type LCS
RunNo: 173950
Result
Sample Type MS
101
104
RunNo: 173950
45
RL
45
Result RL
1060 45
1080
Sample Type MSD
RunNo:173950
Result RL
1070 45
1100 1
Sample Type DUP
RunNo: 173950
Units: µg/Sample
Spike Ref Samp
1E02
1E02
Units: µg/Sample
Spike RefSamp
1E03 ND
1E03 13
Units: µg/Sample
Cone %RPO
1060 0.996
1080 1.64
Units: µg/Sample
Result RL Ref Samp %RPO
E
H
L
0
s
ND
13
45
1
Value above quantitallon range
ND
13 2.55
Holding times for preparation or analysis exceeded
Analyzed by another laboralOl)I
Outside the Range ol DIiutions
Spike Recovery outside accepted recovery limits
%REC % Rec Limits Qual
101 85-115
104 85 -115
%REC % Rec Limits Qual
105 70 -130
106 70-130
%REC % RPD Limits Qual
106 20
108 20
%REC % RPD Limits Qual
20
20
Page 3 of 3
APPENDIXD
Vanadium Dryer
Figure 1. Facility Schematic Representation, Vanadium Dyer
Vanadium Packaging
Figure 2. Facility Schematic Representation, Vanadium Packaging
Process Data (Retained by Energy Fuels)
Scrubber Pressure Drop and Water Flow Rates
D
Faciltty, Energy Fuels
t
a
!
y
Stack Identification: Vanadium Dryer
1.-0 _.,
f3
tt: Distance upstream from next disturbance, feet 10'
f3: Distance downstream from last disturbance, feet 29'
y: Distance of Sample Level to Ground, feet 65'
0: Stack Inside Diameter, inches 36"
Estimated Moisture, percent 3-5%
Estimated Temperature, "F 75-90
Estimated Velocity, fpm 1,400 -~
Control Unit
Type:
Scrubber
Number of Ports 2
Figure 1. Facility Schematic Representation, Vanadium Dryer
Process
Type:
Vanadium Dryer
Faciltty: Energy Fuels
t
a
!
y
Stackldentification: Vanadium Packaging
l+-0-+I
13
a: Distance upstream from next disturbance, inches
jl: Distance downstream from last disturbance, inches
y: Distance of Sample Level to Ground, feet
0: Stack Inside Diameter, inches
Estimated Moisture, percent
Estimated Temperature, "F
Estimated Velocity, fpm _
Control Unit
Type:
Baghouse
Number of Ports 2
>200"
97"
20'
29.5"
0-1%
60-80
1,400
Figure 2. Facility Schematic Representation, Vanadium Dryer
Process
Type:
Vanadium Packaging
Facility Energy Fuels
Location Vanadlur Dryer
Date / O 7f'1tj
East Scrubber
Run# Time "H20 gpm
\ 'f: JC) '\. °l I-Ii· I
\ S:o o 11· °l 4 J·t.
' ,S: JD , 2,., C) '-{ l.·' I f:,: />D I , • 1 "' ,.,
Ir C,: JO r f ·1 l.(3.1
IUft.1' =,:Jo ,z· o Ii 2.r,
f .:o e) I Z· t> yiz_EI
i'.'J() I l•() 'i J./
C\:o o 1 z •d 4'). f
e,:111 r I· 1 t(L·"
/();lie> Ll.•O 'fi·'t
Ju;Jo I z.o ti z..-,..
1f.'pi) i,t. , 'I{,, C,,
' (·.) 0 t I. ' 'fZ· V
f Z,, • fl "1· ' "'2.-:/
ll· JC) I z ·O vz.ct
C3 c)O I Z • b '-fl·~ .
('S·' '30 ((.c, "( 1... L,
West Scrubber Fusion Furnace
"H20 gpm OF ~-, "'·i IJ It
"·Z ~l,-l, 136["
'I· I ~~-J '1s 7
r·/ ,,, .z 11,:1,
Y· f rt .:J I *J f-l . i., T' ·':I ( l ~,
f·T.. )"V•~
'''" 0 s..-~ f{,4 f 'J ro ,..~ ,,.J f "Jlry-e,
f,,z__ y~·Z. (j ,~
"'" .3 "' ·:5 IJ 1,
y•t "" ., / J fc, .
f·t Y'" 'j , 3 ,,
t-, c;.i .e I Jli
"' I
frf,,t./ /1$1 .
tr-"Z, i-f •'I 131'1 -.
):( y11. c::: r Jrr ,
S-·z... r•·-[J"'
Facility Energy Fuels
Location Vanadlpm Dry!
Date l DJ 21 ... 3(> _t 5,
East Scrubber
Run# Time "H20 gpm
"Z.. /1~'1S-f z.f ,.u.·f
2. •'i:tS-I z.. !, '-ll·c/ z. 1'4i't~-'l · '4 qz\,
l 1 ~ . l,S"" I Z • \ Lfz.~
I >:'fG"" I Z.. 1 l./Z .(, ,,:,,~ ,-i,"'{_ '-ll. s-
'": "~ f'( . "f,. c./ z.
,=,.; (~-It• '1 t.(t.,
,-=,. : "S"' I z .~ l(Z•L(
~(°.J 0 IL$"" &.(3.f
'i:Do f"t,•'( I.{ 1·'
°l;U> 1'L .. 'S" c.f}. l.
JU:t,O , l .... , 'fl• J
Jc); J 0 (t .. , t.f ~. 'O
,, : 0 0 It·, '-f)· 0
,, : 3 0 I z... c.f t./ z .~
~
ri: " " -f l·S' li 2' 1
rz_. ,u /1·5 .... '-f ~ ,c)
West Scrubber Fusion Furnace
"H20 gpm OF
i"· C> 'ii'·( 13ft;
f. ( trl.•i l S'i I
f.o "' ·r IJS-:J-
b"'. { r, ,s-( JGY
f'·D ,,. '·r I Jiff
& ·I ,,iy' , -ss 1
~-· J ~t,-s ('J Srf
~.D s,L .v r Jr:J
V,, J g,t.z , 3B1 .
q•f f I·~-l'{t.o
i·f 'ii•~ t'{ tcJ
~·S--c;-z • 3 I '-( , o
1-ei 9Z · ( t'(o u ,.v '-""'-·' l 'I 05
f· -t v-1· c.) f'( rJ}
e-,"' y/.C, I 'lo l,,,
'i, . -, ,,. ' / '(OV
<;· C, <;--z.() IVO: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 ~-
/
TypeSP11Dt
Tube ~
stack
WaH
Temperature
Sensor
l~Trai!Qllimal, ~a,Repaced
~ hi Equvalert·O'mlnssr
l Temperature
Sensor
,-----~~----
Manometer T~atwe Water Sensor$ Empty Siica
Gel
Orifice
By-pass
vaave
Figure 3 Schematic of Method 5/114 Sampling Train
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three atlical or1flces to calbrale the dry ges meter ~lctl bracket the expected operating range.
2) Record barometr1c preAUre befOre and alter calbratlon procedure.
3) Run at tested vacuum (from Orifice Calbratlon Report), for a period of time
nec:aasy to achieve a minimum total VOMl1e of 5 aiblc feet.
4) Record data and Information in the GREEN eels, YELLOW cells are caleulated.
TECHNICIAN:
DATE:
METER PART t:
ORFICU I RUU I
G
G
G
2
3
2
3
1
2
3
M.McNaman
12119/2018
Con80le 3
METER SERIAL#:~
CRITlCAL ORIFICE SET SERIAL I: 1413S
I(' TESTED
FACTOR VACUUM I (AVOI (In Hg)
0.1137 12
0.1137 12
0.8137 12
G.1317 13
0.1317 n
O..IS17 13
0.3307 13
0.3307 13
o.uor 13
DGM READINGS
INfflAL I FtNAL
21.012 31.141
31.841 37.294
37.294 4974
8.204 13..112
1:U1Z 1t.278
11.271 24.IIO
11.100 17.208
17.201 82.708
82.708 81.711
uu
1.1141
UICI
l.70I
u ..
U72
UOt
1.100
I.Ole
USIIG TIE CRl11CAL ORFICES AB CAI..IIRATION STANDARDS:
INmAL
BAROMETRIC PREBSURE In 25.76
EQUIPMENT ID 1: Console #3
TEMPERATURES •F
AMBIENT! DGMINLET I DGMOUTLETI DGII
INITIAL FINAL INl'IW. l'1NAI. AYO
12 .. ti
12 II M
12 84 ...
12 80 11
82 B1 81
82 81 83
12 .. 90
82 IO 90
82 IO 13
••
81 ..
70
74
74
71
80
83
.. ..
"
74
74
78
80
83
81
IO.O
IO.O
I0.8
7U
77.1
78.1
83.0
85.8
87.8
Ir
FINAL
21.71
ELAPSED
TIME (lilN)
8
AVG(P .. )
21.71
§§.00
3.00
3.00
§ 80
80
1.10
1.10
1.10
12.to
12.00
11.00
§ .41
.41
I ,'1,',, ;,,,;!= ~ .. ';;-... ::!.~--. ..
2019 Pre-Calibration
IF YVARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
(1) I ,2,
Ym (STD) V., (STD)
(3)
y
y
VARIATION (Yo)
~
~
~
~
W1I
i.lila
~
MUI
jJUI
~
i8ll
i8ll
AVG•
~
MUI
~
AVG•
~
~
~
AYO•
UZI
Yli
UZI
Uli
UH
UH
UH
2,111
Uli
UZI
UZ1
Ull
~
Ul
:f.11
.1.ll.1
J.IZ1
!.lb
.1&i
.Yl1
~
.1.1.U
WI
jJjJ
The fclowllg equations n osed ID calculale lhe standsd wbne6 ot air passed ~ lhe DGM, V • (Sid), at\d the alllcal orifice,
V,, (s!d), m the DGM cailr8tioll fa::lor, Y. 1"-equations n aukxna5catf ~ In lhe sp'98d8heet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y • i 0.978
(1)
(2)
(3)
rm,.,.,, =K, .,,.,. Pl>ar-lNII IJ.(>)
Tm
• Net voklme of o• sample passed through DGM, correded to standerd conditions
K, • 17.64 "Rlln. Hg (Englsh), 0.3858 "l<lmm Hg (Meltlc)
Pbiar • e
l'cr,~,, = IC• 'Tumb
f£t;;~,-.J'~ J'=, --,. ... _.,,
Tm • Absolute DGM avg. len1l9rature ("R • Engllh, "I( • Metric)
• Voklme of gas sample pasaed Woogh the crttJeaf orifice, COIT8Cted to standard conditions
T -• AmOlute ambient tempetawre ("R • Engllh, "K • Metric)
K' " A'<1918Qe K' lackr trom Ctl1ical Orillce Callbtmion
• DGM calbratiorl factor
AVERAGE l>Ho •j 1.886
L>Ho •
( 2.li.9 )
2
AH (~))
V.,(ltd) V'"
TcMPERATURE SENaORS 'F .. OUT
32 33 32
12 83 83
204 201 20I
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three aitlcal orffices to calibrate the dry gas meter '<Mllch bracl(et the expected operating range.
2) Record ba'ometl1c presaura before and after calbratlon procedure.
3) Run at tested vacuum (from Orifice Calbrallon Report), for a period of time
necet881}1 to achieve a minimum total vollme of 6 cubic feel
4) Record data and Information In Ille GREEN eels, YELLOW eels are calcUlated.
TECHNICIAH:1 ~...._ 1
METER SERIAL#:~
CRfTICAL ORIFICE SET SERIAL#:~
DATE: 1Z/1ll2011
METER PART#: Conaole I
I(' TESTED
FACTOR I VACUUM
ORIFICE t I RUN, I (AYO) (In H11)
G
G
G
2
3
2
3
2
3
0.8137
o.a1n
0.81U
0,5317
0.1317
0.5317
G.3307
0.3307
0.3307
I
9
•
11
11
11
1S
13
13
DOM READINGS
INmAL I FINAL
to.IOI 102.711
102.785 112.129
112.129 117.1141
111.100 130.921
1,G.t21 1S7.141
1S7-"8 14U04
1'7.401 114.AO
114.IIO 1eo.12e
1I0.129 118.113
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
11.BIO
9.711
1.423
11.121
1.824
9.061
7.141
UTII
8.0M
NTlAL
BAROMETRIC PRESSURE H : 26.81
EQUIPMENT io 1: Console #6
TEMPERATURES 'F
AMBIEHTI DON INLET I DGM OUTLET I DOM
Nl1AI. .,_, lilTW. FINM. AVG
84 75 84
II 112 17
" .. 81
87 12 17
81 .. 17
70 .. 17
70 IS 11
It 81 12 .. 81 12
.. ..
71
73
77
77
77
77
77
81
71
72
77
77
77
77
17
71
73.S
77.3
7U
79.8
au
81.1
79.1
71.3
79.0
....
F1HAI. AVG(Pi,.)
2UI I 21.68
ELAPSED I
8 I
§§ 2.IO
2.90
§ so
OD
.hl!
1.10
1.10
18.00
12.IO
18.00 E§ .43
43
Mi¥&--... ~ 1i·'· ;. ;.\;;;~~;
(1)
Vm(STD)
wm
JI.ml
j,IE
um
1.1111
LU!ll
Y!lll
~
LIiii
2019 Pre-Calibration
IF YVARIATION EXCEEDS Z.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V.,(STD)
.1IIJW1
YIM
~
AVG•
il.im
.Lim
LZIZ1
AVG•
.I.UH
M1li
~
AVG•
(3)
y
lWi
lWi
2.111
2.112
.1.211
.L2il
j.R1i
.1.211
uu
!1.111
11.111
!1.111
l
y
VARIATION(%)
:Y2
.1.ll
:1.a
The ~ equations n used to cabAala lhe allrldmd vlllumes d air passed lhrougll Ile OGM, v~ (std), aid Iha criHcal <riice,
V.-(stdl, 811d the DGM calilration fact>r, Y. Theseequa11ons are automaacaly calculated it lhe spr88deheet atxwe. AVERAGE DRY GAS METER CALIBRATION FACTOR, y.. 0.998 I
(1)
(2)
(31
1 .. ,.,,,=K,•1-,,,.rbur"11'\J1 u .i,,
Tm
• Net vollme of gas sample pasNd through OGM, cooeded to st6'ldard condMlons
K1 • 17.64 "R/ln. Hg (Engllh), 0.3858 "Kimm Hg (Metr1c)
Pbor • E0 JC• ra;.,.,, = .Jramh
"~-·ii )"=~-,,~~:'
Tm • Absolute DGM avg. temperature ("R • Engbh, "K-Metric)
• Voklme Of gas sample passed through tile crltlcal orfflce, OOIT8Clad to standard conditions
T-= Abtolut.e ambient t8fll*lllure ("R • Englah, "K • Metric)
K' = Awrege K' factor flOm Cntical Orifice Cafibration
• DGM callbratlon fador
AVERAGEAH0 "j tW
Afio• ( tll.9 )2 AH (V,.(std))
V..(std) Vm
TEMPERATURE SENSORS °F
REFERENCI! IN OUT
32 33 33 .. .. 70
204 208 208
.i.m
.1.111
.1.111
.1.m
.i.m
1.m
JdU
~
1dH.
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three eriticaJ orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record berometrtc pressure before and after calibration procedure.
,&JMMA1ww~f z..-·~-·
~~··'-,;,. ..
3) Run at lelted vacuum (from Orifice CaUbration Report), fOf" a period of llme
necesaary to achieve a minimum total volume of 5 cubic feet
4) Record data 1nd Information in the .GREEN eels, YELLOW ca118 are calculated.
TECHNICIAN: M. ~
DATE: 10/31/2011 METERSERIAL#:~
lll!TER PART /1: Coneole J CRfflCAl ORIFICE SET SERIAL#:~
I(' TESTED
FACTOR I VACUUM DGM READINGS (Fr
ORIFICE# I RUN , I (AVG) . (In lffill INITIAL FINAL
1 ~-42311 I
2 0.42311 I
3 OA2J8 •
71.048 auee
111.IN 17.1192
87.02 13.111 G
D:EBEB
D:EBEB
USING THE CRIT1CAL ORIFICES AS CALIBRATION STAHOARDS:
NET(V.J
1.911
5.821
Utt
INmAL
BAROMETRIC PRESSURE In H : 25.711
eQU1P111ENTio•: Console #3
TEMPERATURES •F
AMBIENT! DGM INLET I DGIII OUTLET I DOM
INmAL FINIIL INl11AL F1NAL AVG
17 11 84 88 17
17 11 82 17 84
87 82 82 84 84
I I I I I I
I I I I I I
88.0
au
83.0
ANAL
21.711
ELAPSED
TIME(MIN)
8
10..eoo
~
10.000
AVG(P .. )
211.75
DGIIIAH
(In H,O)
~ 0
70
§§
§§
(1) I
V.,(STD)
Y4H
~
~
Post Calibration
Energy Fuels
Vanadium Dryer
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
(2) I (3) Iv~~~, V.(STD) y
~ .1&1R
~ Yn
~ .1.2.ll
AVG• 1Jl1Q 2.ti
AVG •
AVG•
The bW1g ~ "" used m calaJlale !he slllndard w1umes o1 ar passed lhrough 111e DGM. v,. (stll, n1 111e crNlcal Ollftce, v~ (Sid), end the DGM calbrallon factJr, Y. TI1esa equations 818 aulDmatlcatly cak:ulaled In 1111 spreadsheet allcM!. AVERAGE DRY GAS METER CALIBRATION FACTOR, y -1 1.010 I
(11
(2)
(3)
v..,(r."' =K, •Ym• Pbar ... (MI 113.6J
Ta,
• Nat volume of gas sample passed through DGM, corrected to standard conditions
K, " 17.64 'Rlln. Hg (English), 0.3858 "Kimm Hg (Metric)
Pb1U•0 lcr ,,,, , =-K"* rf0111l,
Tm= Absolute DGM avg. temperature ('R -Englilh, 'K -Metric)
• Volume of gu sample pea&ed through the aitical orifice, corrected to standard conditions
T-• AbBO!ute ambient temperature ('R-Englilh, 'K -Metric)
l:CTi.:1d) Y---
K' = Average K' factor from Critic:81 Orifice Calibration
• OGM calibration factor
-,. •• t't14)
AVERAGE AHo ·I 1.468
t.H,. • ( l!.Zli )2 4H (V11(•tdJ\
V..(atd) V., /
TEMPERATURE SENSORS "F
ReFeRENCEj IN I OUT
1dH
ldH
1dH
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES ~ lit! ca· l!iSMWIW. =1-;;..a'. • -•• ---. JI ~~~
1) Select three critical orifices to caffbrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after callbraUon procedure.
3) Run at teated vacuum (from Orifice Calibration Report), for a period of time
nacauary to achieve a minimum total volume of 5 cubic feet
4) Raconl data and lnfoonation In Iha GREEN cab, YELLOW calls are calculated.
""""""'I ......... I DATE: 10/31/2011 METER SERIAL I : 88092
METER PART•: Contole ~ CRITICAL ORIFICE SET 8ERIAL #:~
I(' TESTED
FACTOR,VACUUlot I ORIFICE• I RUN , I (AVG) (In Hal
DGM ReAOINGS
INITIAL I FINAL
G: 0.1231 12
D.42311 12
0..4231 12
137.297 1142.124
1142.124 ll4l.30I
S48.30II 1114.042
D:EB§
D:EB§
U8ING T1lE CRlllCAL ORIFICES AS CAUBRAT10N STANOARDS:
8.327
1.181
8.737
INmA1.
BAROMETRIC PRESSURE In H : 21.75
EQUIPMENT 10 ,: Console #6
TEMPERATURES'F
AMBIENT! OGM INLET I 0011 ouner j 0011
INl'l1Al FINAL NIW. FINAL AVG
13 113 11 70 90
13 11 70 90 II
13 70 73 II II
I I I I I I
I I I I I I
II.II
71.1
78.1
FIHA1.
24.71
ELAPSED
TIME~MIN)I
1.10
10.00
10.00
AVG(P ... )
21.71
g§ 72
72
§§
§§
(1)
V,.(STO)
4.11111
~
~
Post Calibration
Energy Fuel
Packaging Baghouaa
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
(2) (3) y
V.,(STO) y VARIATION(%)
~ UH
um !lam
~ UH
AVG• !I.Ill g,gg
AVG"
AVG•
The l?bwlg ~ ani used kl calQllal9 the-slllldard wllMnes of Ilk passed IM>Ugh t11e OGM, V • (Ht), 111d the cr1llcal Oltfic8,
V,. (al), RI the DGM caba11on f&t>r, Y. These equallons are aukJmallca8y calculnJd In the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y • i 0.987
(1)
(21
(3)
Viutr-d) =K, .. ,,-..,.Ph,,, .... (.111:I L\.61
Tm
• Nat volume of gas sample passed through DGM, corracted to standard conditions
K, = 17.64 "Rlln. Hg (Englillh), 0.3858 "Klnvn Hg (Metric)
Tm = Absolute DGM ev~ lemperatUr8 ("R -English, "K -Metric)
Vcrr .. ,., = K._Pbor •0
'Tomb • Volume of g8$ 11o11mple pasaed through the critical orifice, c:orracted to standard conditions
T -" Ablclute ambient tempereture ('R • English, "K -Metric)
ra-,.,.,,
,. = ir ... (;14)
K' = Average K' lactor from Critical Orifice Calibration
• DGM calibration factor
AVERAGE AHo • .. I __ _
AH•• ( lill..ll )2
AH (~J\
V..{etd) V,,. /
TEMPERATURE SENSORS "F
REFERENC~ IN I OUT
.L.W
.1J!!I
.!.m
Types Pitot ~~Dela
Dale: 12/20/JS Pitot Tube ldl:otifi~on: 380
°' Technicia.n: M.McNamara
If I I ~ P,.
Pa o.= 0.375 in. Is PA ""Pi, 'I
I, I.OS • 0i '1; PA & Pe S: 1 .SO• 0i 'I
PA= 0.491 in.
s: Pa"' 0.491 in.
0.1 < 10° U1"" 3 0
a«< 10" «12· 2 •
P1 P1 <5° P1= 0
P2<~ Pz"' 0 0
'-1._ Pa ,-~-Z :$:Q.125 in. z .. 0.051 in.
t c_
i -~~,w W S0.03125 pi, W• 0.017 iJI,
Probe
Probe
Stack
W > 3 incJ1r.:!1
Z> 314 lncb
w .... __ ...;.4 __ in.
Z a ____ 0._87~S __ in.
Y • _...;;3___;;;;314c..;....._ in.
Re.beinco: OmepCL3512A
CODl.inui\y Cheak Y•
Heat Cbeat: 248 Yes
11::mpc:.--v l ffllpa1ffl!IV
Sowoc
-~
Diffilrence
lMNliwn) l"F) t"F)
. AIR 68 69 1 .
AIR 69 71 2 '
ICBWATBR. 33 3J 0
JQll. W.\TBll 205 204 1
IIWCOHBOIL
..
Yes
Yes
Dale: _-=12/l=0/--18........__ Pilot Tube ldentifielllicm: ____ 3_8_·0-_2 ___ _
Tcclinician: M.. MC'.Namla
t :: _l>t..:.."" ___ 0_.3_7_S __ in. la PA<= J'ii ? __ ___,.Y,_es __ _
1-l.QS • Di i PA. & Pa :s: 1.50 • 0. ? __ ---'-Y_cs __ _
0.4'16 in.
P~ ~ 0.476 in,
Q.1 < 10° a1 = I 0
11.2< 10" ciz= 3 0
P1 < s" ~I"' 3 0 ----
Pi"" 3 0 ----
Z $ O. l2S l.n. Z • __ o.....;.~ ........... -in.
..---=-,,,~--__ .. -· -~~ w
y ~--·-"-"-··-w s 0-03 l2S in. w .... __ o __ .o_Jo __ in.
W>3~
Z>3/4 inch
w-____ 4 • .._7s __ in.
Z .. __ 0""'.8:;..;..'1S"'--in.
y.. 3 1/2 in.
Ya Continuity Check J>rvbe 11--............ ----------11-----Heat Choclt..243
PIQbe AIR. 69 '10 l.
AIR '69 71 4'
ICBWA~ 33 34 1 SlaQk:
JJOU,.W4TBI. 204 ios
~OIL
TETCO
Sample Box Temperature Sensor Calibration
DR: 1/2/19 CalilllalD(: Mib PkNilnara ltllinm:: Omgp C1.JSJ2A
. '
'JllehlllNl•pla '11 1,, •• T-,et•lan
UllitlD S..nie ~ 8-r Dilfenace Lecatie• (I') ('r) ('I')
Oven(3) 33 33 0
A -204 203 -I
()yen(4) 20\ 203 -1
Oven()) W&m 33 33 0
B Wm, 204 204 0
Ova,.(4) 204 0
Oveo(3) 33 0
C 104 I
Oveo(4) 204 l
Own(3) 34 3S I
D Watm 204 20S 1 •• Oven(4) Wida' 20S 205 0
Oven(3) w.-33 34 I
E -wata 204 205 I --· ------
Oven(4) Walr:r 204 205 l
F Oven W• -33 -33 . 0 --
W• 204 ·205 t
G w..-33 . 34 1 Oven Water 205 0
H O,ien w.-33 -1 w .. -204 I
1nlpinger 0.. A -1
0
~OlltB Wida' 0
W• 0
~Outc
hnpb:w!J 0u;t D jJ
205
lmpiJt#( Out E 3
205
· 1mi,inp Out F w-33 0
Wala' 203 -1
Iq,iopOutG W'*1t
W•
~OutH
~Outl
lmp11ga Ou;t J
.... OutK
APPENDIXF
The testing followed the same procedures ·as outlined in previous protocols and tests at this
facility.
F
ATTACHMENT H
SURFACE WATER GRAPHS AND FIELD DATA SHEETS
1.00E-05
1.00E-06
1.00E-07
-G)
'i
~.OOE-08
C,
0 ..J -
1.00E-09
1+. -
•• ·-
--
• •
·-
,,. ,,.
~ ~
• -
.. -... --.. -----
1.00E-10 .. ---
1.00E-11
fo'l,
':l."Oj ~"
o.,4' ~" '<}'l;
.
~
·-
Cottonwood Creek Dissolved Radionuclide Concentrations
(uCi/ml)
-
... • ---....
• -
. -. ----. -.. ------~ _ ...
o.,°-''l, ~" ,....iv"
-
•
.... --.... • ... • • • -
-
-------------------
g,'o
~"OJ '<}lo
~~ ~ 1 ""
~
-...
•
-
-
-
--
~<:::,o.,
~~ ~"
• U-Nat. • Th-230 & Ra-226
~
•
&
-----
-•
---.-
--
~..._b< ~~
""
•
A
••
-
-
. ~ -~
.. --------
~ ~~~ ~ ~er;
fv~ ..._(§.
1.00E-06
1.00E-07
1.00E-08
-Cl) ca
~.OOE-09
C)
.9 -
1.00E-10
1.00E-11
1.00E-12
~<o ~"
....
:!!!. -----~
t ~~
Cottonwood Creek Suspended Radionuclide Concentrations (uCi/ml)
...
...
-
... •·
.
. ------
fJ(:':) l~
-
-..
•
.
A --. --.
~n..,
~rfi
:!!!. -
•
--
A • ~ .. ... •
----------
'fJ<o
~"':) ,.....'V
~'o
~"r.::,
•
-
...
.
--
-
~ ... .
~ ·-------~-------------
"f)"
~'o ~ ~'V
~'o 1 ""
"f)°"' ~'V
• U-Nat. •Th-230 • Ra-226 I
A -i ..
·-----A
--. ----
~"'1,
~"Oj
& • --. . -· ·-
--
-
~"<o
~"Oj
-
--...
. . -. ... -
~0
~Oj
"
..
........
. ---7 __ • ·-
~ ~<,j ~~'°'
1.000E+OO
1.000E-01
1.000E-02
1.000E-03
1.000E-04
1.000E-05 -Cl)
joooE-06
"' C'I
jOOOE-07 -
1.000E-08
1.000E-09
1.000E-10
1.000E-11
1.000E-12
1.000E-13
s;'j'o ~~ 'V
s;'jO;, ~~~
Westwater Creek Dissolved Radionuclide Concentrations
(uCi/ml)
--
..._<::) fl,(;) ·,/o ..._1'
~
--
~..._'v
~~~
--
l':)
~~ '8-~
-
-
..._b< ~ ~ ..._'1)
-
..._'o ~ ~..._c::s
• U-Nat. •Th-230 A Ra-226 ]
~ ~ ~'v'V
--
~..._OJ
rf~
...
--
.
I
n,<:;)<6'
..._'8-~
1
0.1
0.01
0.001
0.0001
0.00001 -CII
ff>.000001 en
cffi)ooooo 1 ..J -1E-08
1E-09
1 E-10
1 E-11
1 E-12
1E-13
R> ~Oj rv,~
~'\i /\,.~
Westwater Creek Suspended Radionuclide Concentrations (uCi/ml)
~..._<:::,
\°''tj
""
\°''1, ~"
----__.
._
• ..
,~ ~ ..._'V
":>.. ..... ~
'8-~
I • U-Nat •Th 230 • Ra-226 I
~..._ro
~..._<'J ~t ~f
-
":>..°'°" ~~ ~
<"d'..._<tJ
(
c:
~ ~-
White Mesa Mill -Standard Operating Procedures
Book #II: Environmental Protection Manual, Section 2.1
Date: 04/14 Revision: EFR-3
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURF ACE WATER
WHITE MESA MILL
LOCATION (Circle on~~~onw~od ~Westwater Canyon Other (describe) ____ _
pH BUFFER 7.0 ------
BY: "'11+
(Sampler's initials)
pH BUFFER 4.0 _____ _
SPECIFIC CONDUCTIVITY --------~µ~M=H_O_s
STEAM DEPTH:
pH of WATER __________ _ TEMP ______ _
COND µmhos COND µmh ___ o=s,._ ___ _
pH Units pH units ______ _
Temp°C Temp°C ______ _
COND µmhos COND µmh=o=sa.__ ___ _
pH units pH units ______ _
Temp°C Temp °C ______ _
Comments:
9/J~/ .. :2.0 tq I no 1.,.) "(ter" -to ~l)..mf)le
'i /25/2014 1 no Wo-.±er 1o 5UtM r lc
/30/~Dl'i I no WQ\.+er h .56\mylc
.,
{ /
I
' (
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Pate: 04/14 Revision: EFR-3
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURF ACE WATER
WHITE MESA MILL
estwater Can on Other (describe) ___ _
DATE: f2,/ 5/..Q.Ol j BY: -~----------(Sampler's initials)
pH BUFFER 7.0 __ 7_,_,0 __ _ pH BUFFER 4.0 __ 4_,0 __ _
SPECIFIC CONDUCTIVITY _,,.,,,5.,...· :\..._3=-i..-1 b ____ _.......µWI~O~s
STEAM DEPTH: g11
pHofWATER __ g~·-"-~Y ...... l.__ ____ _
GOND µmhos Sl-\3,)
pH Units 8 · Lj ()
Temp°C 63,3<y
COND µmhos 51.\;>.5
Comments: LOO \DS,t>
--f "'r b ;2.C..2,~
TEMP 3,3g
COND µmhos Si3.~
pH units ___.-<-->=3:...;----
Tem.p°C _·:,~.__.~ ...... Q __ _
COND µmhos 5 tl. ~
pH units ---"'8'-'-, '-\....;.,_I ___ _
Temp°C '3.37
Arci\)CA ep $de o..+ 0 &55 . ..S"-M9le~ c.on~J-etl o.+ D';OO. Gr-~ samples
Q~~ th c. MJb()d lLSea. \eft .S,~ ~+ DqD]
,~~ -CHAIN OF CUSTODY RECORD -Page \ of I Inter-Mountain Labs All shaded fields must be completed. 17982 2 Sheridan, WY.:and Gillette, WY This is a legal document: ·any misrepresentation may be construed as fraud. #
t,-.n:R-.M.()UNT~IN LA.0$
Clien"E~m;fC\._ ~ i:v.elS QY 1s& ~er ;1.0\'t Sampler (Slgnatu~z~;;;f a;e.f Authenticity) Telephone #
~ --~ -'42>5 b78' Yll5 --_:-\,,Atl~v , .-
Report Address
Conta~:i~ \.ueil'\e.1 ANALYSES/ PARAMETERS
!2.:1,5 Ul'\:~J'\ b)vd I s~A-c bC.0 ---~~
~ • ea1nwi1xii Lgt tJ.
Lo..~w~~ c.~ ~o~g _\ Email k\.uelt\19 ]@e1")e ~, ~7.;.~,>, C..Orv') -1:1 HN03-M-12o618-1
'--9 H2S04-4712H86
Invoice Address Phone '2.J': -:z.. Mq 4 l'~ 'i '-,1) -NaOH-Wet-2-72-1
--~ Purchase Order # Quote # -•c ,. ,-lbb
~-
1 i REMARKS -:: LABID DATE I TIME SAMPLE # of w !:: (Lab Use Only) SAMPLED IDENTIFICATION Malrix Containers Q
~\q 12.r o 5 ..o: )10si)'f O'iDC G C +te>fl t .J(\('\d w, ~ '!. Al\ srir~1 i,ra. lyilW , non~ no'l'I ,.,._:;...., ,c •
.• ,l -
I 'i C ' ,•
I \ -,
•' ~' , ' -
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:\ . .
'. ii
: il' . . ,, I!
'·-l
' I ' :}
-. :. ll
I I
,
··=--• --1••• ·••= . "'" -I~. l::.t• ... .. --, -""--. "''" •r,••
"17,..,.,v,,-~));,\J\,\ ..:-\,. ~AA-~'! / ef "rVW'f:4 HOO K n-t1.,\ , ~ ~.Av) t2.q. t q l '3 ~0 S -q "[_; I ~ I I . "-.I ,
' f2-R> \ . ~ -.. ~ -. ~i ---
-i
•J [l::.l•f•1,•1•[::a .. ,1::1eJ:U1J~•1tJtl•••• !r.•••••:,i1tm••I'<-1:11•1• 11 ... ,\~-~•::::1• 1111•,··· e1,1 111: .. ,.,1:,e111~11
• UPS Water WT Check desired service Compliance Monitoring? · N
0 Fed Express Soil SL a Standard turnaround Program (SDWA, NPDES, ... ) . A-11 ~ ......... ~lP.s. t1,e 'i(_A\J1 I
0 US Mail Solid SD a RUSH -s Working Days PWSID / Permit # l\tW\ -tll+er.JA . nl"',() ~.serve.().
0 Hand Carried Filter FT 0 URGENT -< 2 Working Days . Chlorinat~d? YIN1 I .
0 Other Other OT Rush & Urgent Surcharges will be applied Sample Dispo~J Client
Inter-Mountain Labs, Inc. www.1ntermountainlabs.com /:1011 Ll. R
~eAnalytica( Formerly Inter-Mountain Laboratories
(./' uv, 1673 Terra Avenue Sheridan, WY 82801
CLIENT:
Project:
Lab Order:
Energy Fuels (White Mesa)
Q4 Surface Water 2019
S1912105
Sample Cottonwood was received on December 9, 2019.
ph: [phone]
Date: 1/2/2020
CASE NARRATIVE
Report ID: S1912105001
All samples were received and analyzed within the EPA recommended holding times, except those noted below in this case
narrative. Samples were analyzed using the methods outlined in the following references:
"Standard Methods For The Examination of Water and Wastewater", approved method versions
Test Methods for Evaluating Solid Waste, Physical/Chemical Methods, SW-846, 3rd Edition
40 CFR Parts 136 and 141
40 CFR Part 50, Appendices B, J, L, and 0
Methods indicated in the Methods Update Rule published in the Federal Register Friday, May 18, 2012
ASTM approved and recognized standards
All Quality Control parameters met the acceptance criteria defined by EPA and Pace Analytical (Formerly Inter-Mountain
Laboratories) except as indicated in this case narrative.
A ) /j _.;;? <'"
Reviewed by: v{/P" ---
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 1
• Formerly Inter-Mountain Laboratories c1ceAnalytical --------------------------
1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
Company:
ProjectName:
Lab ID:
Energy Fuels (White Mesa)
6425 S. Highway 191
Blanding, UT 84511
Q4 Surface Water 2019
S1912105-001
ClientSample ID: Cottonwood
COC: 179822
PWS ID:
Comments
Sample Analysis Report
Date Reported 1/2/2020
Report ID S1912105001
Work Order: S1912105
CollectionDate: 12/5/2019 9:00:00 AM
DateReceived: 12/9/2019 1 :05:00 PM
FieldSampler: TH
Matrix: Water
Analyses Result Units Qual RL Method Date Analyzed/I nit
General Parameters
Total Dissolved Solids (180) 400 mg/L 10 SM 2540 12/10/2019 1404 IJQ
Total Suspended Solids 262 mg/L 5 SM 2540 12/1012019 839 DAJ
Metals -Dissolved
Uranium 0.0043 mg/L 0.0003 EPA 200.8 1211212019 110 MS
Metals -Suspended
Uranium 0.0004 mg/L 0.0003 EPA 200.8 12113/2019 1041 MS
Radionuclides -Dissolved
Radium 226 0.4 pCi/L 0.2 SM 7500 Ra-8 12/27/2019 1146 WN
Radium 226 Precision (±) 0.1 pCi/L SM 7500 Ra-8 1212712019 1146 WN
Thorium 230 ND pCi/L 0.2 ACW10 12117120191450 WN
Thorium 230 Precision (±) NA pCi/L ACW10 12/17/20191450 WN
Thorium 229 Tracer (30-120) 100 % ACW10 12117/2019 1450 WN
Radionuclides -Suspended
Radium 226 0.5 pCi/L 0.2 SM 7500 Ra-8 12127/2019 1146 WN
Radium 226 (Suspended) Precision (±) 0.1 pCi/L SM 7500 Ra-8 12/27/2019 1146 WN
Thorium 230 0.4 pCi/L 0.2 ACW10 12/19/2019 1435 WN
Thorium 230 Precision (±) 0.1 pCi/L ACW10 1211912019 1435 WN
Thorium 229 Tracer (30-120) 110 % ACW10 12119/2019 1435 WN
Radionuclides -Total
Gross Alpha ND pCi/L 2 SM 71108 12/1912019 1526 AEF
Gross Alpha Precision (±) NA pCi/L SM 71108 1211912019 1526 AEF
These results apply only to the samples tested. RL -Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blank C Calculated Value
E Value above quantitation range G Analyzed at IML Gillette laboratory
H Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at the Reporting Limit 0 Outside the Range of Dilutions
S Spike Recovery outside accepted recovery limits U Analysis reported under the reporting limit
X Matrix Effect
~ /J ..,.-:;, ~
Reviewed by:-=~'-""'-~----------------
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 1
• Formerly Inter-Mountain Laboratories aceAnalytical --------------------------
1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
Work Order:
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1912105
Date: 1/2/2020
Report ID: S1912105001
Project: Q4 Surface Water 2019
Dissolved Metals by ICPMS EPA 200.8 -Water Sample Type MBLK Units: mg/L
MBLK (12/12/19 01 :51) RunNo:174537
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium ND 0.0003
Dissolved Metals by ICPMS EPA 200.8 -Water Sample Type LCS Units: mg/L
LCS (12/12/19 08:56) RunNo: 174537
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium 0.0981 0.0003 0.1 98.1 85 -115
Dissolved Metals by ICPMS EPA 200.8 -Water Sample Type MS Units: mg/L
S1912104-011CS (12/12/19 00:53) RunNo: 174537
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium 1.09 0.001 1.1 ND 99.3 70 -130
Dissolved Metals by ICPMS EPA 200.8 -Water Sample Type MSD Units: mg/L
S1912104-011CMSD (12/12/19 00:58) RunNo: 174537
Analyte Result RL Cone %RPO %REC % RPO Limits
Uranium 1.11 0.001 1.09 1.42 101 20
Gross Alpha, Beta by SM 71108 Sample Type MBLK Units: pCi/L
MBLK-609 (12/19/19 11 :34) RunNo: 174824
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Gross Alpha ND 2
Gross Alpha, Beta by SM 71108 Sample Type LCS Units: pCi/L
LCS A-609 (12/19/19 11 :34) RunNo: 174824
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Gross Alpha 59 2 70.5 83.2 60-124
Gross Alpha, Beta by SM 71108 Sample Type MS Units: pCi/L
S1910428-002AMSA (12/19/1911:34) RunNo: 174824
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Gross Alpha 184 5 141 ND 130 30 -130
Gross Alpha, Beta by SM 711 OB Sample Type DUP Units: pCi/L
S1910428-001ADUP (12/19/1911:34) RunNo: 174824
Analyte Result RL Ref Samp %RPO %REC % RPO Limits
Gross Alpha 5 4 7 26.0 20
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range
G Analyzed at IML Gillette laboratory H Holding times for preparation or analysis exceeded
J Analyte detected below quantitation limits L Analyzed by another laboratory
ND Not Detected at the Reporting Limit 0 Outside the Range of Dilutions
R RPO outside accepted recovery limits s Spike Recovery outside accepted recovery limits
X Matrix Effect
Page 1 of 4
Qual
Qual
Qual
Qual
Qual
Qual
Qual
Qual
• Formerly Inter-Mountain Laboratories . aceAnalyfjca/ --------------------------
CLIENT:
Work Order:
Project:
1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa) Date: 1/2/2020
ReportlD: S1912105001 S1912105
Q4 Surface Water 2019
Sample Type MBLK Units: pCi/L
RunNo: 175080 PrepDate: 12/16/19 0:00 BatchlD 16972
Radium 226 in Water -Dissolved
MB-2103 (12/27/1911:46)
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Radium 226 (Dissolved)
Radium 226 in Water -Dissolved
LCS-2103 (12/27/19 11 :46)
Analyte
Radium 226 (Dissolved)
Radium 226 in Water -Dissolved
MS-2103 (12/27/1911 :46)
Analyte
Radium 226 (Dissolved)
Radium 226 in Water -Dissolved
MSD-2103 (12/27/1911:46)
Analyte
Radium 226 (Dissolved)
Radium 226 in Water -Suspended
MB-2103 (12/27/1911 :46)
Analyte
Radium 226 (Suspended)
Radium 226 in Water -Suspended
LCS-2103 (12/27/1911 :46)
Analyte
Radium 226 (Suspended)
Radium 226 in Water -Suspended
MS-2103 (12/27 /19 11 :46)
Analyte
Radium 226 (Suspended)
Radium 226 in Water -Suspended
MSD-2103 (12/27/1911:46)
Analyte
Radium 226 (Suspended)
Qualifiers: B Analyte detected in the associated Method Blank
G Analyzed at IML Gillette laboratory
J Analyte detected below quantitation limits
ND Not Detected at the Reporting Limit
R RPD outside accepted recovery limits
X Matrix Effect
ND
Sample Type LCS
RunNo: 175080
Result
5.8
Sample Type MS
RunNo: 175080
Result
6.0
Sample Type MSD
RunNo: 175080
Result
5.6
Sample Type MBLK
RunNo: 175080
Result
ND
Sample Type LCS
RunNo: 175080
Result
5.8
Sample Type MS
RunNo: 175080
Result
6.0
Sample Type MSD
RunNo: 175080
Result
5.6
0.2
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Spike Ref Samp
0.2 7
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Spike Ref Samp
0.2 7 ND
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Cone %RPO
0.2 6.0 6.90
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Spike Ref Samp
0.2
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Spike Ref Samp
0.2 7
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Spike Ref Samp
0.2 7 ND
Units: pCi/L
PrepDate: 12/16/19 0:00
RL Cone %RPO
0.2 6.0 6.90
E Value above quantitation range
H Holding times for preparation or analysis exceeded
L Analyzed by another laboratory
0 Outside the Range of Dilutions
s Spike Recovery outside accepted recovery limits
BatchlO 16972
%REC % Rec Limits Qual
83.5 67.1-122
BatchlD 16972
%REC % Rec Limits Qual
85.5 65 -131
BatchlD 16972
%REC % RPD Limits Qual
79.8 20
BatchlD 16971
%REC % Rec Limits Qual
BatchlD 16971
%REC % Rec Limits Qual
83.5 67.1 -122
BatchlD 16971
%REC % Rec Limits Qual
85.5 65 -131
BatchlD 1697.'1
%REC % RPO Limits Qual
79.8 20
Page 2 of 4
pAnal;tica!' Formerly Inter-Mountain Laboratories
1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT: Energy Fuels (White Mesa) Date: 1/2/2020
Work Order: S1912105 Report ID: S1912105001
Project: Q4 Surface Water 2019
Thorium 230 in Water -Dissolved Sample Type MBLK Units: pCi/L
MB-710 (12/16/19 14:19) RunNo: 174856
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium 230 (Dissolved) ND 0.2
Thorium 230 in Water -Dissolved Sample Type LCS Units: pCi/L
LCS-710 (12/16/19 14:19) RunNo: 174856
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium 230 (Dissolved) 13 0.2 12 101 68 -146
Thorium 230 in Water -Dissolved Sample Type LCSD Units: pCi/L
LCSD-710 (12/16/19 14:20) RunNo: 174856
Analyte Result RL Cone %RPO %REC % RPD Limits Qual
Thorium 230 (Dissolved) 12 0.2 13 6.31 94.5 20
Thorium 230 in Water -Suspended Sample Type MBLK Units: pCi/L
MB-711 (12/18/19 15:44) RunNo: 174858
Analyte Result RL Spike RefSamp %REC % Rec Limits Qual
Thorium 230 (Suspended) ND 0.2
Thorium 230 in Water -Suspended Sample Type LCS Units: pCi/L
LCS-710 (12/16/1914:19) RunNo: 174856
Analyte Result RL Spike RefSamp %REC % Rec Limits Qual
Thorium 230 (Suspended) 13 0.2 12 101 68 -146
LCS-711(12/18/1915:44) RunNo: 174858
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium 230 (Suspended) 14 0.2 12 110 68 -146
Thorium 230 in Water -Suspended Sample Type LCSD Units: pCi/L
LCSD-710 (12/16/19 14:20) RunNo: 174856
Analyte Result RL Cone %RPO %REC % RPD Limits Qual
Thorium 230 (Suspended) 12 0.2 13 6.31 94.5 20
LCSD-711 (12/18/19 15:44) RunNo: 174858
Analyte Result RL Cone %RPO %REC % RPD Limits Qual
Thorium 230 (Suspended) 13 0.2 14 8.90 100 20
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range
G Analyzed at IML Gillette laboratory H Holding times for preparation or analysis exceeded
J Analyte detected below quantitation limits L Analyzed by another laboratory
ND Not Detected at the Reporting Limit 0 Outside the Range of Dilutions
R RPD outside accepted recovery limits s Spike Recovery outside accepted recovery limits
X Matrix Effect
Page 3 of 4
• Formerly Inter-Mountain Laboratories aceAnatyticaf --------------------------
1673 Terra Avenue Sheridan, WY 82801 ph: [phone]
CLIENT:
Work Order:
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1912105
Date: 1/2/2020
ReportlD: S1912105001
Project: Q4 Surface Water 2019
Solids By SM 2540 Sample Type MBLK Units: mg/L
DI (12/10/19 08:35) RunNo: 174535
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Total Suspended Solids ND 5
DI (12/10/19 13:27) RunNo: 174628
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Total Dissolved Solids (180) ND 10
Solids By SM 2540 Sample Type LCS Units: mg/L
CONTROL (12/10/19 08:36) RunNo: 174535
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Total Suspended Solids 94 5 100 94.0 80 -110
CONTROL (12/10/19 13:28) RunNo: 174628
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Total Dissolved Solids (180) 220 10 226 96.5 80 -110
Solids By SM 2540 Sample Type DUP Units: mg/L
S1912119-003A (12/10/19 14:10) RunNo: 174628
Analyte Result RL Ref Samp %RPO %REC % RPD Limits
Total Dissolved Solids (180) 5290 10 5320 0.566 20
Suspended Natural Uranium Sample Type MBLK Units: mg/L
MBLK (12/13/1910:35) RunNo: 174604
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium Suspended ND 0.0003
Suspended Natural Uranium Sample Type LCS Units: mg/L
LCS (12/13/19 10:30) RunNo: 174604
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium Suspended 0.0963 0.0003 0.1 96.3 85 -115
Suspended Natural Uranium Sample Type MS Units: mg/L
S1912105-001 CS (12/13/19 10:53) RunNo: 174604
Analyte Result RL Spike Ref Samp %REC % Rec Limits
Uranium Suspended 2.12 0.0003 2.1 0.0004 101 70 -130
Suspended Natural Uranium Sample Type MSD Units: mg/L
S1912105-001CMSD (12/13/19 10:59) RunNo: 174604
Analyte Result RL Cone %RPO %REC % RPD Limits
Uranium Suspended 2.12 0.0003 2.12 0.162 101 20
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range
G Analyzed at IML Gillette laboratory H Holding times for preparation or analysis exceeded
J Analyte detected below quantitation limits L Analyzed by another laboratory
ND Not Detected at the Reporting Limit 0 Outside the Range of Dilutions
R RPD outside accepted recovery limits s Spike Recovery outside accepted recovery limits
X Matrix Effect
Page 4 of 4
Qual
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ATTACHMENT I
SOIL SAMPLE GRAPHS, DATA TABLE, LABORATORY RESULTS AND QA/QC
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SOIL MONITORING LOCATIONS
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OJ Jun-17 ::I -I ""I < m .i,. !:!:. Aug-17 0
+
::I UI
Oct-17 -::I OJ CJ) I < Dec-17 2. 01 -
+
"C
Feb-18 0 ~ Ill -I Apr-18 < 0)
t i Jun-18
Aug-18 OJ I I <
.!.i I Oct-18
f 1 Dec-18
OJ I ~ Feb-19
Apr-19
Jun-19
Aug-19
6~-onv
6 ~-unr
6 ~-JdV
6kqa.::1 C')
0 ch
B~-oaa f
8~-PO
N -0 g s~-onv ch
0 t a. -s~-unr -·o T"" u, 8~-JdV 0
C ch
Cl) 8 ~-qa.::1 + C 0 .: m n-oaa LO I,,, 0 -z C
Cl) n-100 + u
C
0 0 L~-onv
N '<I"
('I) 0 I N n-unr z I
+ .c I-
.c L~-JdV -:::, C') 0 0 u, L ~-qa.::1 z ,,
+ C m g~-oaa
.c t= 0 9~-100 N 0 z z
g~-onv +
g~-unr
T"" 0 I
9 ~-Jd'7' z
+ 9~-qa.::1
g~-oaa
9~-PO
s~-onv
0 0 0 0 0 0 0 0 ,..._ co L!) -.:I" (") C\J T"" 0 0 0 0 0 0 0 0 0
0 0 0 0 9 ..... ..... ..... a rv .i::,. O'l CX) a rv .i::,. 0 0 0 0 0 0 0 0
Aug-15
Oct-15
Dec-15
+I Feb-16
m 6 Apr-16 ....
+ Jun-16
m I 0 Aug-16 I\)
+ m Oct-16 1 D)
(/1 m -I -0 Dec-16 m w 6
+
....
Feb-17 m m I ~ Apr-17 0 co -
+ -I
Jun-17 '::J' I N m c..> 6 Aug-17 • N 01 0
+
0
Oct-17 :::s n
m (I)
I :::s ~ Dec-17 -"'I D)
t -Feb-18 s· :::s
m (/1
6 ---..J Apr-18 :::s
t CJ)
Jun-18 9. --m ,,
6 Aug-18 0 <Xl 'l 1 ~ t -Oct-18
m gl Dec-18
Feb-19
Apr-19
Jun-19
Aug-19
6~-Bnv
6~-unr
6 ~-JdV
6 ~-qa.::1
B~-oaa co ,...
UJ
B~-~oo f -C') =:::: 8~-Bnv ,...._
0 ,...
C. UJ -t -B~-unr ·o en
C 8 ~-JdV CD ,...
1/J UJ
C 8 ~-qa.::1 t 0 ; ca ... L~-oaa lO -,... C UJ Cl) u H-PO + C 0
0 L~-Bnv N '<t ,...
C") UJ N
+ I u-unr .s:. 1-. -H-JdV co C') ,.. ,...
I UJ w
+ u-qa.::1
0 ,..
I g~-oaa C\l w ,... -I -LU
1/J 9~-PO + ca w
9~-onv ,... ,...
I LU
g~-unr +
9 ~-JdV 0 ,...
UJ
9~-qa.::1 +
g~-oaa
S~-PO
s~-onv
0 0 0 0 0 0 0 <D I.() "<t" (") C\J ..... 0 0 0 0 0 0 0 0
6 ~ -6ny
6 ~-unr
6 ~ -Jd'v'
6 ~-qa::1
0)
0
8~-oaa ~ -B~-PO t
~ CX)
0 8 ~ -onv 0
C. ~ -1 -·o B~-unr Cl)
C I"-
8 kJdV 0 en ~ C t 0 B~-qa::1 ; cu a.. -CD C L~-oaa 0 Cl) ~ CJ
C H-PO + 0 0
N L ~ -6ny LO C? 0 N ~ I ~ n-unr + I--0)
0 H-Jdy 'SI" 3: 0 ~
,-L ~-qa::1
+ 9 ~ g~-oao C') --0 en ~ Cl) 9~-PO ~ + g ~-6ny
C\I 0
g~-unr ~
+ 9 ~ -Jdy
,-
0
9~-qa::1 ~
g~-oao +
SHOO
g ~ -6ny
0 0 0 0 0 0 0 <O I() «:I" en C\J ,-0
0 0 0 0 0 0 0
6 ~ -5nv
6 ~-unr
6 ~ -Jd'v'
6 ~-qa.:::1
co ,....
8~-oaa ~
-8~-PO f
C) :::::: ,..._
0 s ~ -5nv
,....
C. ~ -1 ·s 8~-unr u,
C: (!)
8 ~ -Jd'v' ,.... ,,, ~ C: t 0 Skqa.:::1 ·.:. ca I--LO C: L~-oaa ,....
G) ~ (.)
C: H-PO + 0
0
C\I L ~ -5nv """ ('I') ,....
C\I ~ I .c:
+ I-n-unr -co
'I"" H-Jd'v' I C')
3: ,....
~
0 n-qa.:::1
+ 'I"" I 3: 9~-oaa C\I --,.... ,,, ~ G) 9kPO 3: + g ~ -5nv ,.... ,....
g~-unr ~
+ 9 ~ -Jd'v'
0 ,...
9 ~-qa.:::1 ~
g~-oaa +
9~-PO
g ~ -5nv
0 0 0 0 0 0 0 (0 lO """ Ct) C\I T""" 0
c:i c:i c:i c:i c:i c:i c:i
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 09:50
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19090037-001
Client Sample ID: BHV-01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
2 mg/kg-dry
1 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
1. 1 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
MCL/
Qualifiers RL QCL Method Analysis Date / By
0.2 D2974 09/06/19 12:27 I kjp
SW6020 09/16/19 07:38 / meh
E909.0 09/28/19 00:44 I ajl
E909.0 09/28/19 00:44 I ajl
E909.0 09/28/19 00:44 I ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 I ajl
E903.0 09/30/19 10:21 / ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 3 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.com
BIiiings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 08:42
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19090037-002
Client Sample ID: BHV-02
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
Rl -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
MCU
Qualifiers RL QCL Method Analysis Date / By
0.2 D2974 09/06/19 12:28 / kjp
SW6020 09/16/19 08:02 / meh
E909.0 09/28/19 02:54 I ajl
E909.0 09/28/19 02:54 I ajl
E909.0 09/28/19 02:54 I ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 / ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.con1
BIiiings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 09:07
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19090037-008
Client Sample ID: Black Mesa
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±}
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
MCU
Qualifiers RL QCL Method Analysis Date I By
0.2 D2974 09/06/19 12:38 / kjp
SW6020 09/16/19 08:41 / meh
E909.0 09/28/19 18:57 I ajl
E909.0 09/28/19 18:57 I ajl
E909.0 09/28/19 18:57 I ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 I ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 18
Er\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 08:20
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 1909003 7 -003
Client Sample ID: BHV-04
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
MCL/
Qualifiers RL QCL Method Analysis Date I By
0.2 D2974 09/06/19 12:29 / kjp
SW6020 09/16/19 08:21 / meh
E909.0 09/28/19 08:03 / ajl
E909.0 09/28/19 08:03 / ajl
E909.0 09/28/19 08:03 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 I ajl
E903.0 09/30/19 10:21 / ajl
u E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Nol detected at minimum detectable concentration
Page 5 of 18
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WV 888.235.0515
Gillette, WV 888.888.7175 • Helena, MT 817.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27 /19 08: 10
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 1909003 7-004
Client Sample ID: BHV-05
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
2 mg/kg-dry
2.4 pCi/g-dry
0. 7 pCi/g-dry
0.3 pCi/g-dry
2.6 pCi/g-dry
0.5 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
MCU
Qualifiers RL QCL Method Analysis Date / By
0.2 D2974 09/06/19 12:29 / kjp
SW6020 09/16/19 08:25 / meh
E909.0 09/28/19 10:29 / ajl
E909.0 09/28/19 10:29 / ajl
E909.0 09/28/19 10:29 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 / ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 18
E~RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 08:30
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19090037-005
Client Sample ID: BHV-06
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
Rl -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
2 mg/kg-dry
1.2 pCi/g-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
1.2 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.05 pCi/g-dry
0.01 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
MCU
Qualifiers RL QCL Method Analysis Date I By
0.2 D2974 09/06/19 12:30 / kjp
SW6020 09/16/19 08:29 I meh
E909.0 09/28/19 11 :53 I ajl
E909.0 09/28/19 11 :53 I ajl
E909.0 09/28/19 11 :53 / ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 I ajl
E903.0 09/30/19 10:21 / ajl
u E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 7 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.com
BIiiings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.886.7175 • Helene, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27/19 09:33
OateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 1909003 7 -006
Client Sample ID: BHV-07
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL • Quality control limit.
Result Units
ND wt%
4 mg/kg-dry
0.9 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
1. 1 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
MCL/
Qualifiers RL QCL Method Analysis Date I By
0.2 02974 09/06/19 12:30 / kjp
1 SW6020 09/16/19 08:33 / meh
E909.0 09/28/19 13:53 / ajl
E909.0 09/28/19 13:53 / ajl
E909.0 09/28/19 13:53 / ajl
E903.0 09/30/1910:21 / ajl
E903.0 09/30/19 10:21 I ajl
E903.0 09/30/19 10:21 / ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL • Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 8 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.com
BIiiings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch Revised Date: 11/21/19
Report Date: 10/08/19
Collection Date: 08/27 /19 09:43
DateReceived: 08/30/19
Matrix: Soil
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19090037-007
Client Sample ID: BHV-08
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
ND wt%
ND mg/kg-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.09 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
MCU
Qualifiers RL QCL Method Analysis Date / By
0.2 D2974 09/06/19 12:36 / kjp
SW6020 09/16/19 08:37 I meh
E909.0 09/28/19 16:06 / ajl
E909.0 09/28/19 16:06 I ajl
E909.0 09/28/19 16:06 I ajl
E903.0 09/30/19 10:21 / ajl
E903.0 09/30/19 10:21 I ajl
E903.0 09/30/19 10:21 / ajl
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
E908.0 10/03/19 17:39 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 9 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-019
Client Sample ID: N 01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.8 wt%
ND mg/kg-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:10
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:32 / kjp
SW6020 09/16/19 08:49 I meh
E909.0 09/14/19 01 :44 / plj
E909.0 09/14/1901 :44 / plj
E909.0 09/14/19 01 :44 / plj
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-020
Client Sample ID: N 02
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
ND mg/kg-dry
1 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
Rl QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:13
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 14:32 / kjp
SW6020 09/16/19 09:28 / meh
E909.0 09/19/19 01 :47 / plj
E909.0 09/19/1901 :47 I plj
E909.0 09/19/19 01 :47 / plj
E903.0 09/16/19 17:02 I trs
E903.0 09/16/19 17:02 I trs
E903.0 09/16/19 17:02 I trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 23 of 60
EJ\ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-021
Client Sample ID: N 03
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.06 pCi/g-dry
0.01 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:16
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 14:37 / kjp
SW6020 09/16/19 09:32 / meh
E909.0 09/19/19 04: 17 / plj
E909.0 09/19/19 04: 17 / plj
E909.0 09/19/19 04: 17 / plj
E903.0 09/16/19 11 :20 / trs
E903.0 09/16/19 11 :20 / trs
E903.0 09/16/19 11 :20 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 24 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-022
Client Sample ID: N 04
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
mg/kg-dry
1.5 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
0.8 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.04 pCi/g-dry
0.009 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:18
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 14:41 / kjp
SW6020 09/16/19 09:36 / meh
E909.0 09/19/19 06:42 I plj
E909.0 09/19/19 06:42 / plj
E909.0 09/19/19 06:42 I plj
E903.0 09/16/19 11:21 /trs
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 25 of 60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-023
Client Sample ID: N 05
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
1.0 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:20
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
02974 08/27/19 14:41 / kjp
SW6020 09/16/19 09:39 / meh
E909.0 09/19/19 11 :26 / plj
E909.0 09/19/19 11 :26 / plj
E909.0 09/19/19 11 :26 / plj
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 I trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 26 of 60
EN:RGY
' .
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-006
Client Sample ID: S 01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOT AL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
ND mg/kg-dry
-0.1 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.06 pCi/g-dry
0.04 pCi/g-dry
0.03 pCi/g-dry
0.007 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
u
RL
0.2
MCU
Report Date: 09/30/19
Collection Date: 08/20/19 09:12
DateReceived: 08/22/19
Matrix: Soil
QCL Method Analysis Date / By
D2974
SW6020
E909.0
E909.0
E909.0
E903.0
E903.0
E903.0
E908.0
E908.0
E908.0
08/27/19 14:15 / kjp
09/16/19 03:27 I meh
09/12/19 12:37 / plj
09/12/19 12:37 I plj
09/12/19 12:37 / plj
09/16/1913:11 /trs
09/16/19 13: 11 / trs
09/16/19 13: 11 / trs
09/12/19 17:21 / nsr
09/12/19 17:21 / nsr
09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 9 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-007
Client Sample ID: S 02
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 21 O
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.7 wt%
ND mg/kg-dry
-0.07 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.06 pCi/g-dry
0.01 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
u
RL
0.2
MCU
Report Date: 09/30/19
Collection Date: 08/20/19 09:25
DateReceived: 08/22/19
Matrix: Soil
QCL Method Analysis Date / By
D2974 08/27/19 14:16 / kjp
SW6020 09/16/19 03:31 / meh
E909.0 09/12/19 16:12 / plj
E909.0 09/12/19 16:12 / plj
E909.0 09/12/1916:12 / plj
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13: 11 / trs
E903.0 09/16/1913:11 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 10 of60
El'J:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-008
Client Sample ID: S 03
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
0.2 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.04 pCi/g-dry
0.005 pCi/g-dry
0.07 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
u
RL
0.2
MCU
Report Date: 09/30/19
Collection Date: 08/20/19 08:32
DateReceived: 08/22/19
Matrix: Soil
QCL Method Analysis Date / By
D2974 08/27/19 14:17 / kjp
SW6020 09/16/19 03:35 / meh
E909.0 09/12/19 19:48 / plj
E909.0 09/12/19 19:48 / plj
E909.0 09/12/19 19:48 / plj
E903.0 09/16/19 13:11 / trs
E903.0 09/16/19 13:11 / trs
E903.0 09/16/19 13:11 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 11 of 60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-024
Client Sample ID: E 01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
3 mg/kg-dry
1.5 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
1.5 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:22
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:41 / kjp
SW6020 09/16/19 09:43 / meh
E909.0 09/19/19 13:54 / plj
E909.0 09/19/19 13:54 / plj
E909.0 09/19/19 13:54 / plj
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 27 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-025
Client Sample ID: E 02
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
mg/kg-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.7 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:24
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 14:41 / kjp
SW6020 09/24/19 05:00 I jcg
E909.0 09/19/19 16:04 I plj
E909.0 09/19/19 16:04 I plj
E909.0 09/19/19 16:04 I plj
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11:21 /trs
E903.0 09/16/19 11:21 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 28 of 60
EI\ERGY
'
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-026
Client Sample ID: E 03
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
3 mg/kg-dry
2.0 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
2.2 pCi/g-dry
0.4 pCi/g-dry
0.05 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:27
Date Received: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27119 14:45 I kjp
SW6020 09/16/19 09:51 I meh
E909.0 09/19/19 18:53 / plj
E909.0 09/19/19 18:53 / plj
E909.0 09/19/19 18:53 / plj
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/19 11 :21 / trs
E903.0 09/16/1911 :21 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 29 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-027
Client Sample ID: E 04
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
3 mg/kg-dry
1.6 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
1.5 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 07:31
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:45 / kjp
SW6020 09/16/19 09:55 / meh
E909.0 09/19/19 20:47 I plj
E909.0 09/19/19 20:47 I plj
E909.0 09/19/19 20:47 I plj
E903.0 09/16/1911 :21 / trs
E903.0 09/16/1911 :21 / trs
E903.0 09/16/19 11 :21 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 30 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-028
Client Sample ID: E 05
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
3 mg/kg-dry
2.0 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
1.4 pCi/g-dry
0.3 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
Rl QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:35
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:45 / kjp
SW6020 09/16/19 10:15 / meh
E909.0 09/19/19 22:53 / plj
E909.0 09/19/19 22:53 / plj
E909.0 09/19/19 22:53 / plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 31 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-029
Client Sample ID: E 06
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
6 mg/kg-dry
2.2 pCi/g-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
2.2 pCi/g-dry
0.4 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:40
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:45 / kjp
SW6020 09/16/19 10:19 / meh
E909.0 09/20/19 00:46 / plj
E909.0 09/20/19 00:46 / plj
E909.0 09/20/19 00:46 / plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 32 of60
EI\ERGY
' ' '
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-030
Client Sample ID: E 07
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
8 mg/kg-dry
2.9 pCi/g-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
3.1 pCi/g-dry
0.6 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:45
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 14:51 / kjp
SW6020 09/16/19 10:22 I meh
E909.0 09/20/19 02:35 I plj
E909.0 09/20/19 02:35 I plj
E909.0 09/20/19 02:35 I plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13: 15 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 33 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-031
Client Sample ID: E 08
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Rad ium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
6 mg/kg-dry
5.3 pCi/g-dry
1.6 pCi/g-dry
0.5 pCi/g-dry
4.8 pCi/g-dry
0.9 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.07 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:00
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:52 / kjp
SW6020 09/16/19 10:26 / meh
E909.0 09/20/19 04:08 I plj
E909.0 09/20/19 04:08 I plj
E909.0 09/20/19 04:08 I plj
E903.0 09/16/1913:15 /trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09: 55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 34 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-032
Client Sample ID: E 09
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
2 mg/kg-dry
1.9 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
1.5 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:02
Date Received: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:52 / kjp
SW6020 09/18/19 07:07 I meh
E909.0 09/20/19 05: 11 / plj
E909.0 09/20119 05: 11 / plj
E909.0 09/20/19 05: 11 / plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 35 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-033
Client Sample ID: E 10
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
2 mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.05 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:04
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:52 I kjp
SW6020 09/16/19 10:35 / meh
E909.0 09/20/19 07:07 / plj
E909.0 09/20/19 07:07 I plj
E909.0 09/20/19 07:07 I plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13: 15 /trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 36 of 60
Er\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-034
Client Sample ID: E 11
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADION UCLI DES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
2 mg/kg-dry
1.8 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
1.3 pCi/g-dry
0.3 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:06
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 18:34 / kjp
SW6020 09/16/19 10:38 / meh
E909.0 09/20/19 09:54 I plj
E909.0 09/20/19 09:54 I plj
E909.0 09/20/19 09:54 I plj
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E903.0 09/16/19 13:15 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 / nsr
E908.0 09/13/19 09:55 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 37 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-035
Client Sample ID: E12
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
mg/kg-dry
1.2 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
1.5 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:08
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27/19 18:35 / kjp
SW6020 09/16/19 10:42 / meh
E909.0 09/20/19 22:49 / ajl
E909.0 09/20/19 22:49 I ajl
E909.0 09/20/19 22:49 I ajl
E903.0 09/16/19 12:00 / trs
E903.0 09/16/19 12:00 / trs
E903.0 09/16/19 12:00 / trs
E908.0 09/16/19 14:46 / nsr
E908.0 09/16/19 14:46 I nsr
E908.0 09/16/19 14:46 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 38 of60
EI\ERGY
' .
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-036
Client Sample ID: E13
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
2 mg/kg-dry
2.2 pCi/g-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
1.5 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:11
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 18:35 / kjp
SW6020 09/16/19 10:46 / meh
E909.0 09/21/19 00:55 / ajl
E909.0 09/21/19 00:55 I ajl
E909.0 09/21 /19 00:55 I ajl
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 I trs
E908.0 09/16/19 14:46 / nsr
E908.0 09/16/19 14:46 / nsr
E908.0 09/16/19 14:46 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 39 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-001
Client Sample ID: E 14
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MOC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
1.8 pCilg-dry
0.6 pCilg-dry
0.3 pCi/g-dry
0.5 pCilg-dry
0.1 pCi/g-dry
0.04 pCilg-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
Rl QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 08:16
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08127119 14:081 kjp
SW6020 09/16/19 02:33 I meh
E909.0 09/11/19 22:29 / plj
E909.0 09/11119 22:29 / plj
E909.0 09/11/19 22:29 / plj
E903.0 09/16119 11: 17 I trs
E903.0 09/16/1911:17 / trs
E903.0 09/1611911:17 ltrs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09112/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877 .472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-002
Client Sample ID: E 15
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
1.9 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.7 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08: 18
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:10 / kjp
SW6020 09/16/19 02:56 / meh
E909.0 09/12/19 00: 14 / plj
E909.0 09/12/19 00:14 / plj
E909.0 09/12/19 00: 14 / plj
E903.0 09/16/1911 :17 /trs
E903.0 09/16/1911 :17 / trs
E903.0 09/16/1911 :17 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 5 of 60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-003
Client Sample ID: E16
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.9 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:21
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27/19 14:12 / kjp
SW6020 09/16/19 03:00 / meh
E909.0 09/12/19 03:56 / plj
E909.0 09/12/19 03:56 / plj
E909.0 09/12/19 03:56 / plj
E903.0 09/16/1911 :17 / trs
E903.0 09/16/19 11 :17 / trs
E903.0 09/16/1911 :17 I trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-004
Client Sample ID: E 17
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.04 pCi/g-dry
0.02 pCi/g-dry
0.06 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:45
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 14: 13 / kjp
SW6020 09/16/19 03:04 / meh
E909.0 09/12/19 06: 14 / plj
E909.0 09/12/19 06: 14 / plj
E909.0 09/12/19 06: 14 / plj
E903.0 09/16/1911:17 /trs
E903.0 09/16/19 11: 17 / trs
E903.0 09/16/19 11:17 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 7 of60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-005
Client Sample ID: E 18
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.9 wt%
ND mg/kg-dry
0.01 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 08:26
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 14:14 / kjp
SW6020 09/16/19 03:08 / meh
E909.0 09/12/19 09:08 I plj
E909.0 09/12/19 09:08 I plj
E909.0 09/12/19 09:08 / plj
E903.0 09/16/19 11: 17 / trs
E903.0 09/16/1911:17 /trs
E903.0 09/16/19 11:17 / trs
E908.0 09/12/19 17:21 I nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 8 of60
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-009
Client Sample ID: W 01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:05
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27 /19 14:23 / kjp
SW6020 09/16/19 03:39 / meh
E909.0 09/12/19 23:01 / plj
E909.0 09/12/19 23:01 / plj
E909.0 09/12/19 23:01 / plj
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13:11 / trs
E903.0 09/16/19 13:11 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 12 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-010
Client Sample ID: W 02
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
1.0 wt%
ND mg/kg-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 07:00
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:24 I kjp
SW6020 09/16/19 03:43 / meh
E909.0 09/13/19 02:03 I plj
E909.0 09/13/19 02:03 / plj
E909.0 09/13/19 02:03 I plj
E903.0 09/16/1913:11 / trs
E903.0 09/16/19 13: 11 /!rs
E903.0 09/16/1913:11 /trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 13 of 60
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-011
Client Sample ID: W03
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.7 wt%
mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.8 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 06:55
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:25 / kjp
SW6020 09/16/19 03:47 I meh
E909.0 09/13/19 05:28 / plj
E909.0 09/13/19 05:28 I plj
E909.0 09/13/19 05:28 / plj
E903.0 09/16/19 13: 11 / trs
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13: 11 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 14 of 60
EN:RGY
I I
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-012
Client Sample ID: W 04
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
1.1 wt%
mg/kg-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.9 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.4 pCi/g-dry
0.07 pCi/g-dry
0.08 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 06:50
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27 /19 14:25 / kjp
SW6020 09/16/19 03:51 / meh
E909.0 09/13/19 08:15 / plj
E909.0 09/13/19 08:15 / plj
E909.0 09/13/19 08: 15 / plj
E903.0 09/16/19 13:11 / trs
E903.0 09/16/19 13:11 / trs
E903.0 09/16/19 13:11 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 15 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-013
Client Sample ID: W05
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.2 pCilg-dry
0.3 pCilg-dry
0.08 pCi/g-dry
0.04 pCilg-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:35
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 14:26 / kjp
SW6020 09/16/19 03:55 / meh
E909.0 09/13/19 11 :20 / plj
E909.0 09/13/19 11 :20 I plj
E909.0 09113/19 11 :20 I plj
E903.0 09116119 13: 11 / trs
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13:11 / trs
E908.0 09/12119 17:21 I nsr
E908.0 09/12119 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 16 of60
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686. 7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-014
Client Sample ID: W06
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:28
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
02974 08/27 /19 14:29 / kjp
SW6020 09/16/19 03:59 / meh
E909.0 09/13/19 13:50 / plj
E909.0 09/13/19 13:50 / plj
E909.0 09/13/19 13:50 / plj
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13:11 / trs
E903.0 09/16/1913:11 /trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 17 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-015
Client Sample ID: W07
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.4 pCi/g-dry
0.08 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 10:26
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:29 / kjp
SW6020 09/16/19 04:03 I meh
E909.0 09/13/19 16:21 / plj
E909.0 09/13/19 16:21 I plj
E909.0 09/13/19 16:21 / plj
E903.0 09/16/1913:11 /trs
E903.0 09/16/19 13:11 / trs
E903.0 09/16/1913:11 / trs
E908.0 09/12/19 17:21 I nsr
E908.0 09/12/19 17:21 I nsr
E908.0 09/12/19 17:21 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of 60
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-016
Client Sample ID: W 08
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
ND mg/kg-dry
1.0 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.08 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:23
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:29 / kjp
SW6020 09/16/19 04:22 / meh
E909.0 09/13/19 18:42 / plj
E909.0 09/13/19 18:42 / plj
E909.0 09/13/19 18:42 / plj
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E908.0 09/12/1917:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT BOO. 735.4489 • Casper, WY BBB.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-017
Client Sample ID: W09
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
1.8 pCi/g-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.08 pCi/g-dry
0.02 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:19
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27/19 14:30 / kjp
SW6020 09/16/19 04:26 / meh
E909.0 09/13/19 20:56 / plj
E909.0 09/13/19 20:56 / plj
E909.0 09/13/19 20:56 / plj
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E903.0 09/16/19 13:12 / trs
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
E908.0 09/12/19 17:21 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 20 of 60
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-018
Client Sample ID: W 10
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
1.3 wt%
ND mg/kg-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:16
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 14:32 / kjp
SW6020 09/16/19 04:30 I meh
E909.0 09/13/19 22:39 / plj
E909.0 09/13/19 22:39 / plj
E909.0 09/13/19 22:39 / plj
E903.0 09/16/19 13:12 / trs
E903.0 09/16/1913:12 /trs
E903.0 09/16/19 13:12 / trs
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 I nsr
E908.0 09/13/19 09:55 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 21 of 60
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-037
Client Sample ID: W 11
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.07 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/1910:12
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 18:35 / kjp
SW6020 09/16/19 05:29 / meh
E909.0 09/21 /19 04:47 I ajl
E909.0 09/21/19 04:47 I ajl
E909.0 09/21/19 04:47 I ajl
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 I trs
E908.0 09/16/19 14:46 I nsr
E908.0 09/16/19 14:46 / nsr
E908.0 09/16/19 14:46 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 40 of60
Er\ERGY Trust our People. Trust our Data.
www_energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-038
Client Sample ID: W 12
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.08 pCi/g-dry
O.D7 pCi/g-dry
0.03 pCi/g-dry
0.006 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:05
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27 /19 18:38 / kjp
SW6020 09/16/19 05:53 / meh
E909.0 09/21/19 07:32 / ajl
E909.0 09/21 /19 07:32 I ajl
E909.0 09/21/19 07:32 / ajl
E903.0 09/16/19 12:00 / trs
E903.0 09/16/19 12:00 / trs
E903.0 09/16/19 12:00 / trs
E908.0 09/16/19 14:46 / nsr
E908.0 09/16/19 14:46 I nsr
E908.0 09/16/19 14:46 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 41 of 60
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-039
Client Sample ID: W13
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
1.0 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.08 pCi/g-dry
0.09 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 09:52
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 18:38 / kjp
SW6020 09/16/19 05:57 I meh
E909.0 09/21/19 10:23 / ajl
E909.0 09/21 /19 10:23 / ajl
E909.0 09/21/19 10:23 I ajl
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 I trs
E903.0 09/16/19 12:00 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 42 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-040
Client Sample ID: W 14
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
ND mg/kg-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.08 pCi/g-dry
0.07 pCi/g-dry
0.01 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 09:45
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 18:40 / kjp
SW6020 09/16/19 06:01 I meh
E909.0 09/21/19 13:16 / ajl
E909.0 09/21/19 13:16 / ajl
E909.0 09/21/19 13:16 / ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 43 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-041
Client Sample ID: W 15
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS,TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.3 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.07 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MOC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 09:35
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date I By
D2974 08/27 /19 18:40 / kjp
SW6020 09/16/19 06:04 / meh
E909.0 09/21/19 16:15 / ajl
E909.0 09/21/1916:15 / ajl
E909.0 09/21/19 16:15 / ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 44 of60
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LA BORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 190810 79-042
Client Sample ID: W16
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.6 wt%
ND mg/kg-dry
1.3 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.07 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
Rl QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 09:30
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27 /19 18:42 / kjp
SW6020 09/16/19 06:24 / meh
E909.0 09/21 /19 18:25 / ajl
E909.0 09/21/19 18:25 / ajl
E909.0 09/21/19 18:25 / ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 45 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABO RA TORY ANAL YT I CAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-043
Client Sample ID: W 17
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDE$
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.7 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.07 pCi/g-dry
0.1 pCi/g-dry
O.o3 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 09:22
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 18:42 / kjp
SW6020 09/16/19 06:28 / meh
E909.0 09/21 /19 20:31 I ajl
E909.0 09/21 /19 20:31 I ajl
E909.0 09/21/19 20:31 / ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 I nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 46 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C19081079-044
Client Sample ID: W 18
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOT AL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.7 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.6 pCi/g-dry
0.1 pCilg-dry
0.07 pCilg-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 09:06
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 18:43 / kjp
SW6020 09/16/19 06:32 / meh
E909.0 09/21119 23:17 / ajl
E909.0 09/21119 23: 17 / ajl
E909.0 09/21/19 23:17 I ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 I nsr
E908.0 09/16/19 14:45 I nsr
E908.0 09/16/19 14:45 I nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 47 of60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-045
Client Sample ID: E 10D
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOT AL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.4 wt%
2 mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.07 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
1
Report Date: 09/30/19
Collection Date: 08/20/19 08:04
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27 /19 18:43 / kjp
SW6020 09/16/19 06:36 / meh
E909.0 09/22/19 02: 10 / ajl
E909.0 09/22/19 02: 10 / ajl
E909.0 09/22/19 02:10 I ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 48 of60
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081079-046
Client Sample ID: W 15D
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
ND mg/kg-dry
1.4 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.08 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 09:35
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
02974 08/27/19 18:45 / kjp
SW6020 09/16/19 06:40 I meh
E909.0 09/22/19 04:57 I ajl
E909.0 09/22/19 04:57 I ajl
E909.0 09/22/19 04:57 I ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
E908.0 09/16/19 14:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 49 of60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Annual Soils 2019
Lab ID: C 19081 079-04 7
Client Sample ID: W05D
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOTAL
Uranium
RADIONUCLIDES
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
Result Units
0.5 wt%
ND mg/kg-dry
0.6 pCi/g-dry
0.2 pCi/g-dry
0.2 pCi/g-dry
0.07 pCi/g-dry
0.07 pCi/g-dry
0.08 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 09/30/19
Collection Date: 08/20/19 10:35
DateReceived: 08/22/19
Matrix: Soil
Method Analysis Date / By
D2974 08/27/19 18:47 I kjp
SW6020 09/16/19 06:44 / meh
E909.0 09/22/19 06:57 I ajl
E909.0 09/22/19 06:57 I ajl
E909.0 09/22/19 06:57 I ajl
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E903.0 09/16/19 13:42 / trs
E908.0 09/16/19 19:45 / nsr
E908.0 09/16/19 19:45 / nsr
E908.0 09/16/19 19:45 / nsr
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 50 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 888.888.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
November 21, 2019
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C19090037
Project Name: Annual Soils 2019
Quote ID: C5645
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 8/30/2019 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C 19090037-001 BHV-01 08/27/19 09:50 08/30/19 Soil Metals by ICP/ICPMS, Total or
Soluble
Moisture
Percent Moisture
Digestion, Total Metals
Digestion For RadioChemistry
ELl_50-169
Drying/Grinding, Radiochemistry
Lead 210
Radium 226
Thorium, Isotopic
C 1909003 7 -002 BHV-02 08/27/19 08:42 08/30/19 Soil Same As Above
C 1909003 7 -003 BHV-04 08/27/19 08:20 08/30/19 Soil Same As Above
C 19090037-004 BHV-05 08/27/19 08:10 08/30/19 Soil Same As Above
C 1909003 7 -005 BHV-06 08/27 /19 08:30 08/30/19 Soil Same As Above
C 1909003 7 -006 BHV-07 08/27/19 09:33 08/30/19 Soil Same As Above
C 19090037-007 BHV-08 08/27/19 09:43 08/30/19 Soil Same As Above
C 1909003 7 -008 Black Mesa 08/27/19 09:07 08/30/19 Soil Same As Above
The analyses presented in this report were performed by Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601, unles
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. Any issues encountered during sample receipt are documented in the Work Order Receipt Checklist.
The results as reported relate only to the item(s) submitted for testing. This report shall be used or copied only in its entirety. Energy
Laboratories, Inc. is not responsible for the consequences arising from the use of a partial report.
If you have any questions regarding these test results, please contact your Project Manager .
Report Approved By:
Digitally signed by
Tracey Archer
Date: 2019.11.21 18:44:34 -07:00
Page 1 of 18
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.886.7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
Annual Soils 2019
C19090037
ORIGINAL SAMPLE SUBMITIAL(S)
All original sample submittals have been returned with the data package.
SOIUSOLID SAMPLES
All samples reported on an as received basis unless otherwise indicated.
SUBCONTRACTING ANALYSIS
Revised Date: 11/21/19
Report Date: 10/08/19
CASE NARRATIVE
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
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER,WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELi's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
REVISED/SUPPLEMENTAL REPORT
Revised 11/21/2019
This report is being issued to correct the Thorium data reported. Th230 was reported on 10/08/2019, Th232 was requested
and is being reported in this revision.
The report has been revised and replaces any previously issued report in its entirety.
Page 2 of 18
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.888.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19090037 Report Date: 09/17/19
Analyte Count Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-55070
Uranium
Lab ID: LCS3-55070
Uranium
Lab ID: C19090037-001 ADIL
Uranium
Lab ID: C 19090037-001 APDS
Uranium
Lab ID: C19090037-001 AMS3
Uranium
Lab ID: C 19090037-001 AMSD
Uranium
Qualifiers:
RL -Analyte reporting limit.
Initial Calibration Verification Standard
0.0192 mg/L 0.00030
Interference Check Sample A
7.50E-06 mg/L 0.00030
Interference Check Sample AB
3.42E-06 mg/L 0.00030
Method Blank
ND mg/kg 0.8
Laboratory Control Sample
93.0 mg/kg 2.0
Serial Dilution
ND mg/kg-dry 4.0
Post Digestion/Distillation Spike
6.83 mg/kg-dry 1.0
Sample Matrix Spike
26.3 mg/kg-dry 1.0
Sample Matrix Spike Duplicate
24.8 mg/kg-dry 1.0
96
101
102
99
98
90
Analytical Run: ICPMS5-C_190915A
09/15/19 14:08
110
Run: ICPMS5-C_190915A
Run: ICPMS5-C_190915A
80 120
Run: ICPMS5-C_190915A
Run: ICPMS5-C_190915A
75 125
Run: ICPMS5-C 190915A -
75 125
Run: ICPMS5-C_ 190915A
75 125
09/15/19 14:39
09/15/19 14:43
Batch: 55070
09/16/19 07:23
09/16/19 07:26
09/16/19 07:42
10
09/16/19 07:46
09/16/19 07:50
09/16/19 07:54
6.0 20
ND -Not detected at the reporting limit.
Page 11 of 18
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19090037
Revised Date: 11/21/19
Report Date: 10/08/19
Analyte Count Result Units
Method: E903.0
Lab ID: LCS1-55092
Radium 226
Lab ID: MB-55092
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C19090037-001BMS1
Radium 226
Lab ID: C19090037-001BMS1
Radium 226
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Laboratory Control Sample
2.3 pCi/g-dry
Method Blank
0.006 pCi/g-dry
0.006 pCi/g-dry
0.010 pCi/g-dry
Sample Matrix Spike
3.3 pCi/g-dry
Sample Matrix Spike Duplicate
3.2 pCi/g-dry
RL %REC Low Limit High Limit
Run: G542M_ 190924A
92 67 120
Run:G542M_190924A
Run: G542M_ 190924A
89 70 130
Run: G542M_ 190924A
85 70 130
ND -Not detected at the reporting limit.
RPD RPDLimit Qual
4.0
Batch: RA226-9435
09/30/19 10:21
09/30/19 10:21
u
09/30/19 10:21
09/30/19 10:21
20
U -Not detected at minimum detectable concentration
Page 12 of 18
E"-ERGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19090037
Revised Date: 11/21/19
Report Date: 10/08/19
Analyte Count Result Units
Method: E908.0
Lab ID: MB-55092
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: LCSS-55092
Thorium 230
Lab ID: C19090037 -003BMS5
Thorium 230
6 Method Blank
-0.0002 pCi/g-dry
0.01 pCi/g-dry
0.02 pCi/g-dry
0.003 pCi/g-dry
0.007 pCi/g-dry
0.01 pCi/g-dry
Laboratory Control Sample
5.3 pCi/g-dry
Sample Matrix Spike
1.7 pCi/g-dry
-Spike response is not in range for this analysis.
Lab ID: C19090037 -003BMSD
Thorium 230
Sample Matrix Spike Duplicate
3.8 pCi/g-dry
RL %REC Low Limit High Limit
Run: EGG-ORTEC_191001A
Run: EGG-ORTEC_1 91001A
113 80 120
Run: EGG-ORTEC_191001A
26 70 130
Run: EGG-ORTEC_191001A
RPO RPDLimit Qual
Batch: R251625
10/03/19 17:39
u
u
10/03/19 17:39
10/03/19 17:39
s
10/03/19 17:39
70 70 130 74 20 R
-The RPO for the MSD is not in range. The MSD recoveryis acceptable, the MB is acceptable, and the LCS is acceptable.
Lab ID: C19090119-001 AMS5
Thorium 230
Lab ID: C19090119-001AMSD
Thorium 230
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Sample Matrix Spike
19 pCi/g-dry
Sample Matrix Spike Duplicate
19 pC i/g-d ry
S -Spike recovery outside of advisory limits.
Run: EGG-ORTEC_191001A
103 70 130
Run: EGG-ORTEC_191001A
98 70 130 0.7
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
U -Not detected at minimum detectable concentration
10/03/19 17:39
10/03/19 17:39
20
Page 13 of 18
El'J:RGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19090037
Revised Date: 11/21/19
Report Date: 10/08/19
Analyte
Method: E909.0
Lab ID: LCS3-55092
Lead 210
Lab ID: MB-55092
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Lab ID: C19090037 -002BMS3
Lead 210
Lab ID: C19090037 -002BMS3
Lead 210
Qualifiers:
RL -Analyte reporting limit.
Count Result Units
Laboratory Control Sample
1.8 pCi/g-dry
3 Method Blank
0.006 pCi/g-dry
0.02 pCi/g-dry
0.04 pCi/g-dry
Sample Matrix Spike
2.6 pCi/g-dry
Sample Matrix Spike Duplicate
2.5 pCi/g-dry
MDC -Minimum detectable concentration
RL %REC Low Limit High Limit RPO RPDLimit Qual
Batch: PB-210-1059
Run: PACKARD 3100TR_190919A 09/27/1916:18
76 70 130
Run: PACKARD 3100TR_190919A
Run: PACKARD 3100TR_190919A
81 70 130
Run: PACKARD 3100TR_190919A
76 70 130 4.6
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
09/27/19 17:59
u
09/28/19 05:19
09/28/19 06:40
20
Page 14 of 18
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: Kasey Vidick
Reviewed Date: 9/4/2019
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 cL1stody 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 D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
"C
Yes D
Yes D
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
C19090037
Date Received: 8/30/2019
Received by: amm
Carrier name: 2Day
No D
No D
No D
No D
No D
No D
No D
No D
No D
No D
No@
No D
No D
Not Present D
Not Present D
Not Present 0
Not Applicable D
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 15 of 18
,··~---Sheet 1 of 1
I
'ERGYFUELS RESOURCES
CHAIN OF CUSTODY
Samples Shipped to: ..,,,E..,,,.n~e~rg~y....,L_ab~o_ra_t .... ie .... s ________ Contact: Tanner Holliday
2393 Salt Creek Hwy. Ph: 435 678 4115
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project SamDlera Name Samplers Signature
Annual Soils 2019 Tanner Holliday I .:JtUVIU(, #~
Time
Sample ID Date Collected Collected Laboratorv Analvsis Reauested
BHV-01 8/27/2019 950 U-NAT, Ra-226, Pb-210, TH-232
BHV-02 8/27/2019 842 U-NAT. Ra-226, Pb-210. TH-232
BHV-04 8/27/2019 820 U-NAT, Ra-226. Pb-210 TH-232
BHV-05 8/27/2019 810 U-NAT, Ra-226, Pb-210, TH-232
BHV-06 6/27/2019 830 U-NAT, Ra-226 Pb-210, TH-232
BHV-07 8/27/2019 933 U-NAT, Ra-226, Pb-210, TH-232
BHV-08 8/27/2019 943 U-NAT Ra-226, Pb-210, TH-232
Black Mesa 8/27/2019 907 U-NAT, Ra-226, Pb-210 TH-232
f' l~OC\c...->-::r-1
Comments: Please send report to Kathy Welnel at [e-mail]
Relinquished By:(Signature) ~ ~ ~r"1r.,-.,~
Rellnqulshed By:{Slgnature)
Date/Time Re
8/28/2019
1130
Page 16 of 18
Dori Quis
From:
Sent:
To:
Subject:
FYI -For C1909003 7
Tessa Parke <[e-mail]>
Tuesday, September 03, 2019 4:33 PM
casper _login
FW: Soil Samples
From: Kathy Welnel [mailto:KWeine!@energyfuels.com]
sent: Tuesday, September 03, 2019 4:06 PM
To: Tessa Parke
Subject: RE: Soil Samples
Tessa,
I had a wonderful holiday-I hope you had a good extended weekend.
No these samples are not lle2 -they are plain old garden variety soils (Pun intended). They are collected at our
perimeter fence surrounding the site or at the high vol air stations.
K
~
~nergy Fuels Resources (USA) Inc.
Kathy Weiner
Quality Assurance Manager
t: 303.389.4134 It: 303.389.4125
225 Union Blvd., Suite 600
Lakewood, CO 80228
http://www.energyfuels.com
This e-mail is intended for the exclusive use of person(s) mentioned as the recipient(s). This message and any attached flies with It are confidential and may
contain privileged or proprietary information. If you are not the intended reclpient(s) please delete this message and notify the sender. You may not use, distribute
print or copy this message If you are not the Intended reclplent(s).
From: Tessa Parke <[e-mail]>
Sent: Tuesday, September 3, 2019 3:03 PM
To: Kathy Weinel <[e-mail]>
Subject: Soil Samples
lllllidt&tn1(IIM:(l11M1l\llwli&ib\MuiiiibdMIHftttiiiili1141iitiM,11lti,id
Hey Kathy,
1
Page 17 of 18
On those soil samples that we just got in are they 11e2? I just need to make sure we mark them correctly. Hope you
had a good Labor Day weekend.
Sincerely,
Tessa
Tessa Parke
Project Manager
Office: 307.995.3249
Fax: [phone]
[e-mail]
This transmission is CONFIDENTIAL. If you have received this in error,
please contact Energy Laboratories, Inc. immediately.
2
Page 18 of 18
EI\ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
ANALYTICAL SUMMARY REPORT
September 30, 2019
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C 19081079
Project Name: Annual Soils 2019
Energy Laboratories, Inc. Casper WY received the following 47 samples for Energy Fuels Resources (USA) Inc on 8/22/2019
for analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C19081079-001 E14 08/20/19 08:16 08/22/19 Soil Metals by ICP/ICPMS, Total or
Soluble
Moisture
Percent Moisture
Digestion, Total Metals
Digestion For RadioChemistry
ELl_50-169
Drying/Grinding, Radiochemistry
Lead 210
Radium 226
Thorium, Isotopic
C 19081079-002 E15 08/20/19 08:18 08/22/19 Soil Same As Above
C 19081 079-003 E16 08/20/19 08:21 08/22/19 Soil Same As Above
C19081079-004 E17 08/20/19 08:45 08/22/19 Soil Same As Above
C 19081079-005 E18 08/20/19 08:26 08/22/19 Soil Same As Above
C 19081079-006 S 01 08/20/19 09: 12 08/22/19 Soil Same As Above
C 19081079-007 S 02 08/20/19 09:25 08/22/19 Soil Same As Above
C 19081079-008 S 03 08/20/19 08:32 08/22/19 Soil Same As Above
C 19081079-009 W01 08/20/19 07:05 08/22/19 Soil Same As Above
C19081079-010 W02 08/20/19 07:00 08/22/19 Soil Same As Above
C 19081079-011 W03 08/20/19 06:55 08/22/19 Soil Same As Above
C 19081079-012 W04 08/20/19 06:50 08/22/19 Soil Same As Above
C19081079-013 W05 08/20/19 10:35 08/22/19 Soil Same As Above
C19081079-014 W06 08/20/19 10:28 08/22/19 Soil Same As Above
C 19081079-015 WO? 08/20/19 10:26 08/22/19 Soil Same As Above
C19081079-016 W08 08/20/19 10:23 08/22/19 Soil Same As Above
C19081079-017 W09 08/20/19 10: 19 08/22/19 Soil Same As Above
C 19081079-018 W 10 08/20/19 10: 16 08/22/19 Soil Same As Above
C 19081079-019 N 01 08/20/19 07: 10 08/22/19 Soil Same As Above
C19081079-020 N 02 08/20/19 07: 13 08/22/19 Soil Same As Above
C 19081079-021 N 03 08/20/19 07:16 08/22/19 Soil Same As Above
Page 1 of 60
EI\ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
ANALYTICAL SUMMARY REPORT
C 19081 079-022 N 04 08/20/19 07:18 08/22/19 Soil Same As Above
C 19081079-023 N 05 08/20/19 07:20 08/22/19 Soil Same As Above
C 19081079-024 E 01 08/20/19 07:22 08/22/19 Soil Same As Above
C 19081079-025 E 02 08/20/19 07:24 08/22/19 Soil Same As Above
C 19081079-026 E 03 08/20/19 07:27 08/22/19 Soil Same As Above
C 19081079-027 E 04 08/20/19 07:31 08/22/19 Soil Same As Above
C 19081079-028 E 05 08/20/19 07:35 08/22/19 Soil Same As Above
C 19081079-029 E 06 08/20/19 07:40 08/22/19 Soil Same As Above
C19081079-030 E 07 08/20/19 07:45 08/22/19 Soil Same As Above
C 19081079-031 E 08 08/20/19 08:00 08/22/19 Soil Same As Above
C 19081079-032 E 09 08/20/19 08:02 08/22/19 Soil Same As Above
C19081079-033 E 10 08/20/19 08:04 08/22/19 Soil Same As Above
C 19081079-034 E 11 08/20/19 08:06 08/22/19 Soil Same As Above
C 19081079-035 E 12 08/20/19 08:08 08/22/19 Soil Same As Above
C 19081079-036 E 13 08/20/19 08: 11 08/22/19 Soil Same As Above
C 19081079-037 W 11 08/20/19 10: 12 08/22/19 Soil Same As Above
C19081079-038 W 12 08/20/19 10:05 08/22/19 Soil Same As Above
C19081079-039 W 13 08/20/19 09:52 08/22/19 Soil Same As Above
C 19081079-040 W 14 08/20/19 09:45 08/22/19 Soil Same As Above
C19081079-041 W 15 08/20/19 09:35 08/22/19 Soil Same As Above
C 19081079-042 W 16 08/20/19 09:30 08/22/19 Soil Same As Above
C 19081079-043 W 17 08/20/19 09:22 08/22/19 Soil Same As Above
C19081079-044 W 18 08/20/19 09:06 08/22/19 Soil Same As Above
C 19081 079-045 E 100 08/20/19 08:04 08/22/19 Soil Same As Above
C 19081079-046 W 150 08/20/19 09:35 08/22/19 Soil Same As Above
C19081079-047 W050 08/20/19 10:35 08/22/19 Soil Same As Above
The analyses presented in this report were performed by Energy Laboratories, Inc., 2393 Salt Creek Hwy., 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. Any issues encountered during sample
receipt are documented in the Work Order Receipt Checklist.
The results as reported relate only to the item(s) submitted for testing. This report shall be used or copied only in its
entirety. Energy Laboratories, Inc. is not responsible for the consequences arising from the use of a partial report.
If you have any questions regarding these test results, please contact your Project Manager .
Report Approved By: rl~~ Project Manager
Digitally signed by
Tessa Parke
Date: 2019.09.30 13:13:03 -06:00
Page 2 of 60
EN:RGY
' '
~-Trust our People. Trust our Data.
~ www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
Annual Soils 2019
C19081079
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (±2°C)
Report Date: 09/30/19
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 ELI 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 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
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER.WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELi's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Tests associated with analyst identified as ELI-B were subcontracted to Energy Laboratories, 1120 S. 27th St., Billings, MT,
EPA Number MT00005.
Page 3 of 60
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc Work Order: C19081079 Report Date: 09/24/19
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: SW6020 Analytical Run: ICPMS5-C_ 190915A
Lab ID: QCS Initial Calibration Verification Standard 09/15/19 14:08
Uranium 0.0192 mg/L 0.00030 96 90 110
Lab ID: ICSA Interference Check Sample A 09/15/19 14:39
Uranium 7.50E-06 mg/L 0.00030
Lab ID: ICSAB Interference Check Sample AB 09/15/19 14:43
Uranium 3.42E-06 mg/L 0.00030
Method: SW6020 Batch: 54931
Lab ID: MB-54931 Method Blank Run: ICPMS5-C_ 190915A 09/16/19 02:29
Uranium ND mg/kg 0.9
Lab ID: C 19081079-001 ADIL Serial Dilution Run: ICPMS5-C_190915A 09/16/19 02: 36
Uranium ND mg/kg-dry 4.1 10
Lab ID: C19081079-001APDS Post Digestion/Distillation Spike Run: ICPMS5-C_190915A 09/16/19 02:40
Uranium 5.54 mg/kg-dry 1.0 101 75 125
Lab ID: C19081079-001 AMS3 Sample Matrix Spike Run : ICPMS5-C_190915A 09/16/19 02:44
Uranium 26.3 mg/kg-dry 1.0 102 75 125
Lab ID: C19081079-001AMSD Sample Matrix Spike Duplicate Run : ICPMS5-C_190915A 09/16/19 02:48
Uranium 26.5 mg/kg-dry 1.0 102 75 125 0.6 20
Method: SW6020 Batch: 54946
Lab ID: MB-54946 Method Blank Run : ICPMS5-C_190915A 09/16/19 08:45
Uranium ND mg/kg 2
Lab ID: C19081079-019ADIL Serial Dilution Run : ICPMS5-C_190915A 09/16/19 08:53
Uranium ND mg/kg-dry 4.1 10
Lab ID: C19081079-019APDS Post Digestion/Distillation Spike Run : ICPMS5-C_ 190915A 09/16/19 08:56
Uranium 5.27 mg/kg-dry 1.0 112 75 125
Lab ID: C19081079-019AMS3 Sample Matrix Spike Run : ICPMS5-C _ 190915A 09/16/19 09: 16
Uranium 26.1 mg/kg-dry 1.0 111 75 125
Lab ID: C19081079-019AMSD Sample Matrix Spike Duplicate Run : ICPMS5-C _ 190915A 09/16/19 09:20
Uranium 27.0 mg/kg-dry 1.0 110 75 125 3.1 20
Method: SW6020 Batch: 54964
Lab ID: MB-54964 Method Blank Run: ICPMS5-C_ 190915A 09/16/19 05:25
Uranium ND mg/kg 0.8
Lab ID: C19081079-037 ADIL Serial Dilution Run : ICPMS5-C _ 190915A 09/16/19 05:33
Uranium ND mg/kg-dry 4.2 10
Lab ID: C19081079-037 APDS Post Digestion/Distillation Spike Run : ICPMS5-C_ 190915A 09/16/19 05:37
Uranium 5.17 mg/kg-dry 1.0 107 75 125
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration
Page 51 of 60
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C 19081079 Report Date: 09/24/19
Analyte Count Result Units RL
Method: SW6020
Lab ID: C19081079-037 AMS3 Sample Matrix Spike
Uranium 26.0 mg/kg-dry 1.0
Lab ID: C19081079-037AMSD Sample Matrix Spike Duplicate
Uranium 14.0 mg/kg-dry 1.0
Method: SW6020
Lab ID: QCS Initial Calibration Verification Standard
Uranium 0.0194 mg/L 0.00030
Lab ID: ICSA Interference Check Sample A
Uranium 1.34E-05 mg/L 0.00030
Lab ID: ICSAB Interference Check Sample AB
Uranium 8.63E-06 mg/L 0.00030
Method: SW6020
Lab ID: MB-54946 Method Blank
Uranium ND mg/kg 2
Method: SW6020
Lab ID: QCS Initial Calibration Verification Standard
Uranium 0.0192 mg/L 0.00030
Lab ID: ICSA Interference Check Sample A
Uranium 7.29E-06 mg/L 0.00030
Lab ID: ICSAB Interference Check Sample AB
Uranium 6.37E-06 mg/L 0.00030
Method: SW6020
Lab ID: MB-54946 Method Blank
Uranium ND mg/kg 2
Qualifiers:
%REC Low Limit High Limit RPD RPDLimit Qual
104
56
97
96
Batch: 54964
Run: ICPMS5-C_190915A 09/16/19 05:41
75 125
Run: ICPMS5-C _ 190915A 09/16/19 05:45
75
90
125 60 20 SR
Analytical Run : ICPMS5-C_190917A
09/18/19 03: 37
110
09/18/19 04:08
09/18/19 04: 12
Run: ICPMS5-C_190917A
Batch: 54946
09/18/19 06:59
90
Analytical Run: ICPMS5-C_ 190924A
09/24/19 03:34
110
09/24/19 04:05
09/24/19 04:09
Run: ICPMS5-C_ 190924A
Batch: 54946
09/24/19 04:56
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
S -Spike recovery outside of advisory limits.
Page 52 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19081079 Report Date: 09/27/19
Analyte
Method: E903.0
Lab ID: C190B1079-021BMS1
Radium 226
Lab ID: C19081079-021BMS1
Radium 226
Lab ID: LCS1-54912
Radium 226
Lab ID: MB-54912
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Method: E903.0
Lab ID: LCS1-5497B
Radium 226
Lab ID: MB-54978
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C19081079-035BMS1
Radium 226
Count Result Units
Sample Matrix Spike
2.5 pCi/g-dry
Sample Matrix Spike Duplicate
2.6 pCi/g-dry
Laboratory Control Sample
2.4 pCi/g-dry
3 Method Blank
0.009 pCi/g-dry
0.007 pCi/g-dry
0.009 pCi/g-dry
Laboratory Control Sample
2.3 pCi/g-dry
3 Method Blank
0.008 pCi/g-dry
0.008 pCi/g-dry
0.01 pCi/g-dry
Sample Matrix Spike
3.4 pCi/g-dry
Lab ID: C19081079-035BMSD Sample Matrix Spike Duplicate
3.6 pCi/g-dry Radium 226
Method: E903.0
Lab ID: C190B1079-001BMS1
Radium 226
Lab ID: LCS1-54911
Radium 226
Lab ID: MB-54911
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C19081079-001 BMS1
Radium 226
Qualifiers:
RL -Analyte reporting limit.
Sample Matrix Spike
2. 7 pCi/g-dry
Laboratory Control Sample
2.0 pCi/g-dry
3 Method Blank
0.006 pCi/g-dry
0.005 pCi/g-dry
0.007 pCi/g-dry
Sample Matrix Spike Duplicate
2.5 pCi/g-dry
MDC -Minimum detectable concentration
RL %REC Low Limit High Limit
Run: G5000W_ 190909A
84 70 130
Run:G5000VV_190909A
87 70 130
Run: G5000VV_ 190909A
96 67 120
Run:G5000VV_190909A
Run: G542M_190910A
92 67 120
Run: G542M_ 190910A
Run: G542M_190910A
77 70 130
Run: G542M_ 190910A
84 70 130
Run: G542M-2_ 190909A
91 70 130
Run: G542M-2_ 190909A
82 67 120
Run: G542M-2_ 190909A
Run: G542M-2_190909A
82 70 130
ND -Not detected at the reporting limit.
RPD RPDLimit Qual
3.2
4.9
8.8
Batch: 54912
09/16/19 11 :21
09/16/19 11 :21
20
09/16/19 13:15
09/16/1913:15
u
Batch: R251132
09/16/19 11 :59
09/16/19 11:59
u
09/16/19 12:00
09/16/19 12:00
20
Batch: 54911
09/16/19 11 :17
09/16/19 17:02
09/16/19 17:02
u
09/16/1911:17
20
U -Not detected at minimum detectable concentration
Page 53 of 60
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 871.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19081079 Report Date: 09/27/19
Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: E908.0
Lab ID: LCSS-54911
Thorium 230
Lab ID: MB-54911
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: C19081079-003BMS5
Thorium 230
Laboratory Control Sample
3.9 pCi/g-dry
3 Method Blank
-0.002 pCi/g-dry
0.005 pCi/g-dry
0.01 pCi/g-dry
Sample Matrix Spike
3.1 pCi/g-dry
Run: EGG-ORTEC_2_ 190830B
83 80 120
Run: EGG-ORTEC_2_190830B
Run: EGG-ORTEC_2_ 190830B
62 70 130
-Spike response is not in range for this analysis. Since the LCS and the RPD recoveries are in range, the response is considered to be matrix related.
Lab ID: C19081079-003BMS5
Thorium 230
Sample Matrix Spike Duplicate
3.0 pCi/g-dry
Run: EGG-ORTEC_2_190830B
w m 1~ 1.8
-Spike response is not in range for this analysis. Since the LCS and the RPD recoveries are in range, the response is considered to be matrix related.
Method: E908.0
Lab ID: MB-54911
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: LCSS-54912
Thorium 230
Lab ID: MB-54912
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: C19081079-023BMS5
Thorium 230
3 Method Blank
-0.001 pCi/g-dry
0.009 pCi/g-dry
0.02 pCi/g-dry
Laboratory Control Sample
4.8 pCi/g-dry
3 Method Blank
0.001
0.006
0.01
pCi/g-dry
pCi/g-dry
pCi/g-dry
Sample Matrix Spike
2.4 pCi/g-dry
Run: EGG-ORTEC_2_190910A
Run: EGG-ORTEC_2_ 19091 OA
105 80 120
Run: EGG-ORTEC_2_ 190910A
Run: EGG-ORTEC_2_ 19091 OA
45 70 130
-Spike response is not in range for this analysis. Since the LCS and the RER recoveries are in range, the response is considered to be matrix related.
Lab ID: C19081079-023BMS5
Thorium 230
Sample Matrix Spike Duplicate
3.3 pCi/g-dry
Run: EGG-ORTEC_2_ 190910A
66 70 130 30
-Duplicate RPD is outside of the acceptance range for this analysis. However, the RER is less than the limit of 2.0.
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
S -Spike recovery outside of advisory limits.
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
U -Not detected at minimum detectable concentration
Batch: 54911
09/12/19 17:21
09/12/19 17:21
u
09/12/19 17:21
s
09/12/19 17:21
20 S
Batch: R250920
09/13/19 09:55
u
09/13/19 09:55
09/13/19 09:55
u
09/13/19 09:55
s
09/13/19 09:55
20 SR
Page 54 of 60
EN:RGY
'
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C 19081079 Report Date: 09/27/19
Analyte
Method: E90B.O
Lab ID: LCSS-54978
Thorium 230
Lab ID: MB-54978
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: C19081079-037BMS5
Thorium 230
Count Result Units
Laboratory Control Sample
4.3 pCi/g-dry
3 Method Blank
0.0 pCi/g-dry
0.004 pCi/g-dry
0.01 pCi/g-dry
Sample Matrix Spike
3. 7 pCi/g-dry
Lab ID: C19081079-037BMSD Sample Matrix Spike Duplicate
3.3 pCi/g-dry Thorium 230
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_2_190910C
92 80 120
Run: EGG-ORTEC_2_ 19091 OC
Run: EGG-ORTEC_2_ 19091 OC
73 70 130
Run: EGG-ORTEC_2_ 19091 OC
63 70 130
Batch: 54978
09/16/19 14:45
09/16/19 14:45
u
09/16/19 14:46
09/16/19 14:46
s
-Spike response is not in range for this analysis. Since the LCS and the RPD recoveries are in range, the response is considered to be matrix related.
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration S -Spike recovery outside of advisory limits.
U -Not detected at minimum detectable concentration
Page 55 of 60
E"-1:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Client: Energy Fuels Resources (USA) Inc
Prepared by Casper, WY Branch
Work Order: C19081079 Report Date: 09/27/19
Analyte Count Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: E909.0 Batch: Pb210-1056
Lab ID: LCSJ-54911 Laboratory Control Sample Run: PACKARD 3100TR_190904D 09/11/19 14:07
Lead 210 2.5 pCi/g-dry 110 80 120
Lab ID: MB-54911 3 Method Blank Run: PACKARD 3100TR_ 190904D 09/11 /19 15:34
Lead 210 0.01 pCi/g-dry u
Lead 210 precision(±) 0.02 pCi/g-dry
Lead 210 MDC 0.04 pCi/g-dry
Lab ID: C19081079-002BMS3 Sample Matrix Spike Run: PACKARD 3100TR_ 190904D 09/12/19 01 :57
Lead 210 4.6 pCi/g-dry 120 70 130
Lab ID: C19081079-002BMS3 Sample Matrix Spike Duplicate Run: PACKARD 3100TR_190904D 09/12/19 02:56
Lead 210 4.5 pCi/g-dry 114 70 130 3.6 20
Method: E909.0 Batch: 54912
Lab ID: LCSJ-54912 Laboratory Control Sample Run: TRICARB LSC_190904C 09/18/19 16:25
Lead 210 2.3 pCi/g-dry 100 80 120
Lab ID: MB-54912 3 Method Blank Run: TRICARB LSC_ 190904C 09/18/19 18:14
Lead 210 -0.03 pCi/g-dry u
Lead 210 precision (±) 0.03 pCi/g-dry
Lead 210 MDC 0.05 pCi/g-dry
Lab ID: C19081079-022BMS3 Sample Matrix Spike Run: TRICARB LSC_190904C 09/19/19 08:51
Lead 210 4.0 pCi/g-dry 110 70 130
Lab ID: C19081079-022BMS3 Sample Matrix Spike Duplicate Run: TRICARB LSC_190904C 09/19/19 10:07
Lead 210 3.9 pCi/g-dry 104 70 130 3.3 20
Method: E909.0 Batch: 54978
Lab ID: LCSJ-54978 Laboratory Control Sample Run: TRICARB LSC_190905A 09/20/19 13:45
Lead 210 2.0 pCi/g-dry 88 80 120
Lab ID: MB-54978 3 Method Blank Run: TRICARB LSC_190905A 09/20/19 15:25
Lead 210 -0.007 pCi/g-dry u
Lead 210 precision (±) 0.02 pCi/g-dry
Lead 210 MDC 0.04 pCi/g-dry
Lab ID: C19081079-036BMS3 Sample Matrix Spike Run: TRICARB LSC_ 190905A 09/21/19 02:31
Lead 210 4.9 pCi/g-dry 120 70 130
Lab ID: C19081079-036BMSD Sample Matrix Spike Duplicate Run: TRICARB LSC_190905A 09/21/19 03:27
Lead 210 2.9 pCi/g-dry 32 70 130 51 20 SR
-Spike response is not in range for this analysis. Since the LCS recovery is in range and the RER is <2, the response is considered to be matrix related.
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
S -Spike recovery outside of advisory limits.
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
U -Not detected at minimum detectable concentration
Page 56 of 60
E"1:RGY Trust our People. Trust our Data.
www.encrgylab.com
Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Casie C. Peppersack
Reviewed by: Kasey Vidick
Reviewed Date: 8/26/2019
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)?
ContainerfTemp Blank temperature:
Water -VOA vials have zero headspace?
Water -pH acceptable upon receipt?
Standard Reporting Procedures:
Yes 0
Yes O
Yes O
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
25.3°C
Yes O
Yes O
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
C19081079
Date Received: 8/22/2019
Received by: ens
Carrier name: Hand Del
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
No 0
Not Present D
Not Present 0
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:
Multiple temperatures include 27 .0, 4.0, 0.3 and 0.0. The lower temps were for the aqueous samples. 8/23/19 CP
Page 57 of60
{J /9D8' /tJ 79
Sheet I. of I
CHAIN OF CUSTODY
Samples Shipped to: _E_n_er_..9 ..... Y_L_ab_o_ra_t1_·e_s ________ Contact: Tanner Holliday
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samolers Name Samolers Signaturp
Annual Soils 2019 Tanner Hollidav ,~~-MJ~
Time
Sample ID Date Collected Collected Laboratorv Analvsis Reauested
E14 8/20/2019 816 U-NAT, Ra-226 Pb-210 TH-232
E15 8/20/2019 818 U-NAT, Ra-226, Pb-210, TH-232
E16 8/20/2019 821 U-NAT. Ra-226, Pb-210, TH-232
E 17 8/20/2019 845 U-NAT Ra-226 Pb-210, TH-232
E18 8/20/2019 826 U-NAT, Ra-226, Pb-210 TH-232
S 01 8/20/2019 912 U-NAT, Ra-226, Pb-210, TH-232
S02 8/20/2019 925 U-NAT, Ra-226, Pb-210, TH-232
S 03 8/20/2019 832 U-NAT, Ra-226 Pb-210, TH-232
W01 8/20/2019 705 U-NAT, Ra-226, Pb-210, TH-232
W02 8/20/2019 700 U-NAT, Ra-226, Pb-210, TH-232
W03 8/20/2019 655 U-NAT, Ra-226, Pb-210, TH-232
W04 8/20/2019 650 U-NAT, Ra-226, Pb-210, TH-232
W05 8/20/2019 1035 U-NAT, Ra-226, Pb-210, TH-232
W06 8/20/2019 1028 U-NAT, Ra-226, Pb-210, TH-232
W07 8/20/2019 1026 U-NAT. Ra-226, Pb-210, TH-232
W08 8/20/2019 1023 U-NAT, Ra-226, Pb-210, TH-232
W09 8/20/2019 1019 U-NAT Ra-226, Pb-210, TH-232
W10 8/20/2019 1016 U-NAT, Ra-226, Pb-210 TH-232
Comments: Please send report to Kathv Weinel at [e-mail]
Relinquished By:(Signature)
Date/Time Received By:(Signature)
8/21/2019
1500
Date/Time Re
. '
Date/Time
Date/Time
i/zi/
Page 58 of 60
{!/1[8/0?9
Sheet 1 of S
CHAIN OF CUSTODY
Samples Shipped to: ....;E __ n_er_..g"""y...,.L_ab __ o_ra_,t,-;.ie,....s ________ Contact: Tanner Holliday
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
p . ro1ect s amp ers N ame s amplera SI 1gnature
Annual Soils 2019 Tanner Hollidav I ~u{IN./t-¥~? .,.
Time
Sample ID Date Collected Collected Laboratorv Analvsis Requested
N 01 8/20/2019 710 U-NAT, Ra-226, Pb-210, TH-232
N 02 8/20/2019 713 U-NAT. Ra-226, Pb-210, TH-232
N03 8/20/2019 716 U-NAT, Ra-226, Pb-210, TH-232
N 04 8/20/2019 718 U-NAT, Ra-226, Pb-210 TH-232
N 05 8/20/2019 720 U-NAT Ra-226, Pb-210, TH-232
E 01 8/20/2019 722 U-NAT, Ra-226, Pb-210, TH-232
E 02 8/20/2019 724 U-NAT, Ra-226, Pb-210, TH-232
E03 8/20/2019 727 U-NAT, Ra-226 Pb-210, TH-232
E04 8/20/2019 731 U-NAT Ra-226, Pb-210, TH-232
E05 8/20/2019 735 U-NAT, Ra-226, Pb-210, TH-232
E06 8/20/2019 740 U-NAT, Ra-226, Pb-210, TH-232
E 07 8/20/2019 745 U-NAT, Ra-226 Pb-210, TH-232
E08 8/20/2019 800 U-NAT, Ra-226, Pb-210, TH-232
E 09 8/20/2019 802 U-NAT Ra-226, Pb-210, TH-232
E10 8/20/2019 804 U-NAT, Ra-226, Pb-210, TH-232
E 11 8/20/2019 806 U-NAT, Ra-226, Pb-210, TH-232
E 12 8/20/2019 808 U-NAT, Ra-226, Pb-210, TH-232
E 13 8/20/2019 811 ' U-NAT, Ra-226, Pb-210, TH-232
Comments: Please send report to Kathy Weinel at kweinel®energyfuels.com \
Page 59 of60
Sheet 3 of 3
CHAIN OF CUSTODY
Samples Shipped to: ...,.E...,..n __ er_..g~y_La_b--o_ra_t_.ie __ s ________ Contact: Tanner Holliday
2393 Salt Creek Hwy. Ph: 435 678 4115
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samplers Name Samplers SianaJure
Annual Soils 2019 Tanner Hollldav i-:-~~M~/?
Time
SamDle ID Date Collected Collected Laboratorv Analvsis ReQuested
W 11 8/20/2019 1012 U-NAT, Ra-226, Pb-210, TH-232
W 12 8/20/2019 1005 U-NAT Ra-226, Pb-210, TH-232
W 13 8/20/2019 952 U-NAT, Ra-226, Pb-210, TH-232
W14 8/20/2019 945 U-NAT, Ra-226, Pb-210, TH-232
W15 8/20/2019 935 U-NAT Ra-226, Pb-210, TH-232
W 16 8/20/2019 930 U-NAT, Ra-226, Pb-210, TH-232
W17 8/20/2019 922 U-NAT, Ra-226, Pb-210, TH-232
W18 8/20/2019 906 U-NA T, Ra-226, Pb-210, TH-232
E10D 8/20/2019 804 U-NAT, Ra-226, Pb-210, TH-232
W15D 8/20/2019 935 U-NAT, Ra-226, Pb-210 TH-232
W05D 8/20/2019 1035 U-NAT, Ra-226. Pb-210, TH-232
U-NAT, Ra-226, Pb-210, TH-232
U-NAT, Ra-226, Pb-210, TH-232
U-NAT, Ra-226, Pb-210 TH-232
U-NAT, Ra-226, Pb-210, TH-232
U-NAT, Ra-226, Pb-210, TH-232
U-NAT, Ra-226, Pb-210, TH-232
U-NAT, Ra-226, Pb-210, TH-232
Comments: Please send report to Kathy Weinel at [e-mail]
Datemme Received By:(Slgnature)
8/21/2019
1500
Date/Time Re
Date/Time
Date/Time
f;,Jfr'I
Page 60 of60
BHV-1 BHV-2 BHV-3
Date Ra-226 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pb-210
9/7/1980 0.65 0.42 . . 0.34 0.42 --0.42 0.42 -
9/8/1981 0.4 1.8 -. 0.3 0.6 -. 0.3 0.6 .
12/3/1981 0.79 0.77 . . 0.44 0.56 . . 0.89 0.42 .
6/30/1982 0.423 0.384 . . 0.412 0.18 . . 0.265 0.207 .
5/5/1983 0.471 0.41 . . 0.569 0.55 . -0.461 0.34 .
6/4/1984 0.713 0.866 . . 0.618 0.683 . . 0.489 0.471 .
10/12/1984 2.96 0.886 -. 2.33 0.069 . . 2.88 0.721 .
8/28/1985 1.63 0.8 . . 2.19 0.424 -. 2.27 0.424 .
8/1/1986 0.369 0.654 . . 0.466 0.866 . . 0.382 0.694 -
8/17/1987 0.6 0.8 -. 1.5 0.9 . 0.8 0.6 -
8/28/1988 1.5 1.6 --1.3 0.7 . . 0.6 0.9 .
8/25/1988 1.2 1.6 --1.1 3 . . 0.8 I
8/1/1990 2.9 5.8 . . I 1.4 . . 0.8 1.4 -
8/5/1991 3.9 8.8 . . 1.7 2.6 . . 2.6 5.7 .
8/13/1992 1.2 2.2 . . 0.9 1.4 . . 0.8 1.2 .
8/13/1993 2 1.7 -. 1.4 1.7 . . I. I 1.9 .
8/3/1994 I 1.6 . -0.7 0.8 -. 0.7 0.9 -
8/28/1995 2.81 4.7 . . 0.68 0.2 . . 0.88 0.65 .
8/13/1996 1.7 2.15 . . 0.6 0.46 . . 0.3 0.21 .
8/1/1997 0.54 0.31 -. 0.56 0.16 . . 0.41 0.27 .
7/1/1998 1.6 3.05 . . 0.7 0.58 . . 0.5 0.45 .
8/24/1999 2.27 1.74 . -0.78 0.84 --0.53 0.42 -
12/1/2000 1.51 1.21 . . 0.81 0.53 -* * .
8/23/2001 I 1 . . 0.6 0.3 . . 0.4 0.3 .
8/1/2002 1.3 1.35 . 0.9 0.524 . . 0.5 0.297 .
8/5/2003 0.8 0.99 . . 0.6 0.79 -0.5 0.33 .
8/9/2004 0.6 0.61 . . 0.4 0.25 . . 0.4 0.22 .
8/3/2005 0.9 0.96 . . 0.7 0.34 . -0.6 0.27 .
8/7/2006 0.7 0.76 . . 0.44 0.25 . . 0.41 0.25 .
8/8/2007 1.1 2.37 -. 0.7 0.53 -. 0.2 0.55 .
8/20/2008 0.9 1.23 --0.3 0.43 . . 0,6 0.98 -
8/10/2009 0.8 0.88 -. 0.7 0.54 . . 0.7 1.08 -
8/2/2010 1.3 1.09 . I 1.49 . . 0.8 0.62 .
8/23/2011 0.9 1.32 . -0.4 0.32 . . 0.4 0.4 .
8/20/2012 0.5 1.96 -0.4 0.54 . 0.7 1.09 .
8/21/2013 0.7 1.013 . . 0.3 0.405 -. 0.6 1.35 .
8/25/2014 0.8 0.945 . . 0.4 0.54 . . 0.5 0.675 .
8/18/2015 0.9 1.215 1.2 0.2 0.6 0.608 0.8 0.3 0.3 0.338 0.7
8/9/2016 0.5 0.4725 0.4 0.2 0.4 0.27 0.2 0.4 0.5 0.54 0.9
8/8/2017 1.2 1.35 2.1 0.3 0.5 0 0.9 0.3 0.2 0 0.8
8/23/2018 0.7 0.675 I 0.2 0.4 0 1.5 0.1 0.3 0 1
8/27/2019 I.I 1.35 I 0.2 0.5 0 0.7 0.2 0.4 0 0.9
-Data not available.
Th-232
-
.
-
.
.
.
.
-
-
.
-
.
.
.
-
-
.
.
.
-
.
.
.
.
.
.
.
.
-
.
.
.
.
.
.
0.3
0.2
0.2
0.3
0.2
Table 1-1
WHITE MESA MILL
Soil Sampling Results at BHV Stations 1-8
(pCi/g)
BHV-4 BHV-5
Ra-226 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pb-210
0.41 12.194 --0.23 14.89 -
0.2 3 -. 0.3 0.6 .
0.75 0.63 --0.55 0.42 .
0.478 0.26 . . 0.449 0.216 .
0.643 0.34 . . 0.147 0.14 .
0.124 0.324 . . 0.132 0.31 .
3.49 0.804 -. 2.55 0.817 .
4.33 0.294 . . 1.28 0.577 .
0.396 0.826 . . 0.728 0.836 .
1.2 0.7 . 1.5 1.3 .
I 1.3 -. 3.8 5 .
I.I 1.4 . . 2.9 5.7 .
1.8 1.3 . -3.7 3.2 .
1.8 2.6 . . 2.5 4.4 -
0.9 0.9 . . I.I 1.8 -
0.8 1.6 -. 4.8 3.5 -
0.7 I.I . . 3 3.8 .
0.58 0.24 -. 2.8 1.6 .
0.5 0.52 . . 1.9 2.01 .
0.41 0.26 -1.7 1.5 -
I 1.19 . . 3 2.76 .
0.84 0.77 . . 3.27 3.15 .
0.83 1.22 . 2.81 3.25 .
0.9 1 . -1.2 I.I .
1.2 1.49 -. 2.4 2.81 .
0.6 0.43 . . 0.28 0.42 .
0.6 0.51 . -I 1.4 -
0.6 0.38 -. 0.7 0.41 -
0.52 0.48 . . 1.4 1.3 .
0.5 0.74 . . I.I 1.45 .
0.5 0.79 . . 0.8 1.33 .
0.8 0.61 . . 2.6 2.98 .
1.3 1.69 . . 1.7 1.69 .
0.5 0.58 . . I 1.48 -
0.6 0.81 . . 1.6 2.7 .
0.3 0.54 . . 1.1 1.62 .
0.7 0.743 . . 2.8 3.71 .
0.5 0.54 0.2 0.3 1.2 1.215 1.0
0.5 0.2025 0.09 0.4 1.2 0.54 0.4
0.7 0 1.3 0.2 3.6 3.38 4.2
0.4 0 0.6 0.2 2.2 2.70 3.1
0.6 0 0.7 0 2.6 1.35 2.4
BHV-6 BHV-7 BHV-8
Th-232 Ra-226 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pb-210 Th-232
. ----. .
. -. . . . .
-. . . . -
. . . -. . .
. . -. . . .
. . . ---.
. . . . . -.
. . . . . . .
. . --. . .
-. . --. .
. . . . . .
. . . . . . .
. . . . --.
. . . -. . .
. . -. . . .
. . . . . .
. . . . . . -
. . . . -. .
. . . -. . -
. . . . . . .
. . -. . . .
. . ---. .
. -. -. . .
. . . . . . -
. . . . . .
. 0.6 0.53 . -. --.
. 0.9 1.4 -. --. -
. I 1.2 . . . . .
. 0.78 0.65 . . . . . .
. 0.8 0.93 . . . . . .
. 0.5 0.67 . . . . .
0.5 0.81 . -. . .
. 0.8 0.87 . . . -. -
. 0.6 0.86 . -. . . .
-0.8 1.37 . . . . . .
. 0.5 0.743 -. . . -.
. 0.4 0.81 . . . . . .
0.3 0.4 1.418 o.~ 0.3 0.7 1.76 0.5 0.09 1.0 0.338 0.8 0.05
0.4 0.8 0.88 0.3 0.2 0.8 0.54 0.2 0.5 0.5 0.135 0.08 0.3
0.2 0.6 0.68 0.6 0.2 0.7 1.35 0.8 0.2 0.6 0 0.4 0.08
0.2 0.7 2.03 1.2 0.2 0.7 2.03 0.8 0.3 0.5 0 0.5 0.2
0.1 1.2 1.35 1.2 0 I. I 2.70 0.9 0.3 0.3 0 0.3 0.2
I N-01 N-02 11 .. N-03
St!mple <Jate _'Ra~226 U-Nat P!c;2JO Tli-232 Ra-2'26 U-Nat Pb-210 Th-2'32, ;Ra-226 T:J-Nat Ph-210
Aug-15 0.30 0.47 0.80 0.30 0.50 0.41 0.30 0.30 0.60 0.61 0.90
Aug-16 0.50 0.20 0.60 0.20 0.60 0.20 0.40 0.50 0.50 0.20 0.60
Aug-17 0.7 0 1.8 0.4 0.7 0 I.I 0.3 0.9 0.7 l.3
Aug-18 0.5 0 1.0 0.4 0.5 0 1.l 0.2 0.8 0.7 2.0
Aug-19 0.4 0 0.3 0.1 0.4 0 1.0 0.2 0.4 0 1.1
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
N-04 N-05
Th-232: Rn-226 U-Nat Ph-210 TH-232 Ra-?26 U;,Nat Pb-210 Th-2~2
0.40 0.60 0.41 0.20 0.20 0.80 0.95 1.00 0.30
0.40 0.70 0.14 0.60 0.40 0.90 0.34 0.50 0.40
0.3 1.0 0.7 1.4 0.3 0.6 0 0.6 0.4
0.2 1.2 0.7 1.3 0.l I.I 1.4 2.4 0.2
0.06 0.8 0.7 1.5 0.04 0.6 0 0.4 0.2
II
Ra-226
0.30
0.40
0.7
0.1
0.2
S-01 11 S-02 S-03
U-Nat. Pb-210 Th-232 Ra-226 U-Nat Pb-210 1'h-2J2 Ra-226 U-Nat Pb-210 Tb-232
0.20 1.10 0.30 0.60 0.54 0.50 0.60 0.30 0.34 1.10 0.06
0.14 0.30 0.08 0.20 0.05 0.70 0.20 0.20 0.07 0.80 0.30
0 1.0 0.4 0.8 1.4 0.8 0.6 0.4 0 1.0 0.07
0 0.8 0.02 0.2 0 I.I 0.05 0.3 0 1.8 0.03
0 0 O.D3 0.4 0 0 0.06 0.3 0 0.2 0.005
i .Jll.t) l E-0'.2 !I rill&~ /
Sa1u1)J', 1, I 11
itf(t) ]I~..,,2.26 l1W,~tf Pb-2ili0 '.lDI1-232 Ga~. 111.!Nnt, Pb,~lllO'. i1f1:1.,2,3~ Ila 2!'26, ll-Nn1 (L'rh-l:J!!), 1'Th,.-l~~ /U.1~6
Aug-15 2.60 3.11 2.40 0.20 1.30 1.69 1.00 0.20 1.20 2.70 0.70 0.30 0.90
Aug-16 1.40 0.61 0.50 0.30 l.70 0.47 0.40 0.20 1.60 0.61 0.30 0.30 1.30
Aug-17 3.2 2.70 2.7 0.3 1.9 2.03 1.6 0.2 1.6 1.35 1.6 0.2 1.5
Aug-18 2.2 2.70 4.1 0.1 1.4 1.35 1.7 0.1 1.3 1.35 1.4 0.2 1.7
Aug-19 1.5 2.03 1.5 0.0 0.7 0.68 0.6 0.3 2.2 2.03 2.0 0.3 1.5
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
IJ!I4JJ,J li.«T5 ,1 B-'06
I •:
·.P·!'llat ~1)"2!.l!O.
c~ lFJl,-231 iR:3·2'26 . iil-Nnt J?ib.~O r1•.l) •. ,!'Q Rtt1-lr1o, lii-Na t Pb-210,
1.69 0.70 0.20 4.90 9.11 3.70 0.20 2.60 3.11 2.10
0.74 0.40 0.20 4.00 2.16 0.30 0.30 4.00 2.90 0.40
2.03 1.5 0.07 2.3 2.70 2.3 0.3 3.0 2.70 2.4
2.03 2.0 0.10 3.0 4.73 4.0 0.1 3.3 4.05 3.0
2.03 '1.6 0.20 1.4 2.03 2.0 0.2 2.2 4.05 2.2
I
Tb-2~2
0.20
0.20
0.10
0.08
0.10
E:-67 EJ.Ol! ~ill). ~ II
Ra-226 l1-Nat P-b-210 Th-232 [Ra-~16J 1U.$1:a1 P,li-!0/0l 1Jilh;-!a2 itu-2~6 lll-,Na1,1 Pl1...2ll.(0 .1'1i-~!
0.50 0.74 0.30 0.10 3.50 4.79 3.20 0.20 2.00 3.51 2.10 0.20
1.20 0.34 0.06 0.08 3.50 1.62 0.50 0.20 2.50 1.35 0.30 0.20
2.7 2.03 2.9 0.1 4.7 4.05 2.7 0.09 4.4 3.38 2.4 1.3
0.4 0.68 0.4 0.1 3.3 4.05 4.7 0.20 0.7 2.03 0.8 0.1
3.1 5.40 2.9 0.2 4.8 4.05 5.3 0.20 1.5 1.35 1.9 0.2
E-JO E-11 E-12
Ra-2-26 C!J-INat Pb-2J.O Th,232 Ra-22(i U-Nat Pb-21~ Tb-232 Ra-v26 U•Nat Pb-ZlO Th-232 Ra-2'26.
1.80 3.51 2.80 0.40 1.30 2.09 1.60 0.10 0.60 0.74 0.60 0.20 0.60
2.00 1.08 0.40 0.30 0.80 0.41 0.20 0.20 0.50 O.D7 0.50 0.30 1.00
3.0 3.38 2.2 0.3 1.9 1.35 1.4 0.2 1.7 0 1.0 0.4 1.9
0.8 1.35 1.0 0.08 1.3 2.03 2.0 0.2 0.6 0 0.8 om 0.9
0.6 1.35 0.7 0.30 1.3 1.35 1.8 0.2 1.5 0.68 1.2 0.20 1.5
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
E-13 E~IIJ E-J'S
U-Nat Pb-210 Th-232 Ra-226 l1-Nat Pb-.21.0 Th-232 Ra-2U 10-Nat Pb-.210
0.41 0.70 0.20 0.40 0.54 1.10 0.20 0.40 0.47 1.10
0.07 0.20 0.10 0.40 0.07 0.08 0.20 0.40 O.D7 1.10
0 1.7 0.1 1.9 0 1.1 0.5 1.6 0 1.5
0 1.9 0.1 0.4 0 1.2 0.4 0.4 0 1.9
1.35 2.2 0 0.5 0 1.8 0.2 0.7 0 1.9
Th-232
0.20
0.20
0.3
0.3
0.2
E-16 I E-17 E-18
Ra-226 U-Nat Pb-210 Th432 Ra-226 C!J-N'at Pb-210 l•Th-232 Ra-226 U-Nat Pb-210 Th-232
0.50 0.34 0.80 0.30 0.50 0.41 1.30 0.30 0.60 0.34 0.90 0.30
0.40 0.20 0.70 0.30 0.30 0.07 0.70 0.20 0.30 0.14 0.40 0.20
1.4 0 0.9 0.5 0.8 0 1.1 0.2 0.7 0 0.8 0.20
0.4 0 1.1 0.02 0.2 0 0.5 0.08 0.3 0 0.8 0.05
0.4 0 0.9 0.20 0.3 0 0.4 0 0.3 0 0 0.10
'Sample W4m ~JOl?! ~OJ
date llf:t~W:. ~Na't l?'b,~01 l:"Efu.i$f.l ~~ _,ilJ~~ ,OCl•'ial~ l.~22!:_ ·-ii-.. !~, ~ 1·.ai-...!,,~-.-,,.1 --.
Aug-15 0.50 0.41 0.20 0.30 0.60 0.68 0.60 0.20 0.90 0.81 1.30 0.20
Aug-16 0.60 0.20 0.60 0.50 1.00 0.20 0.80 0.30 0.80 0.27 1.10 0.20
Aug-17 0.6 0 1.1 0.1 0.6 0 0.9 0.1 0.7 0.68 1.1 0.2
Aug-18 0.7 0 0.6 0.3 0.6 0 0.4 0.2 1.0 0.68 1.7 0.4
Aug-19 0.5 0 0.3 0.3 0.4 0 0.04 0.2 0.8 0.68 0.5 0.2
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
W~OJJ \W,.·05 w~,o,6
a~ i1'ill-'},ra-t ~b'--210 '1~32 :;&a..Z.'!Tu ~a~ II>~ ~Z32 Let-226 .iw--~ ·~~w
0.90 1.08 1.00 0.30 0.50 0.81 0.80 0.40 0.40 0.34 0.50
0.60 0.27 2.00 0.20 0.40 0.20 2.50 0.50 0.40 O.Q7 0.80
0.9 0.68 1.6 0.08 0.4 0 0.9 0.1 0.3 0 0.9
1.8 1.35 3.5 0.20 0.3 0 0.7 0.2 0.3 0 0.6
0.9 0.68 0.2 0.40 0.3 0 0.7 0.1 0.5 0 0.7
111llh-232
0.30
0.10
0.1
0.2
0.2
W•.ffi W-.Ufi~ w.ro9
Ra><-, 'w-ar,.uJ ~j~ ~-lf3l ~
~, l~b~· -ro-Kll'j w.~ 1a,,h.RIJ ''lib--
0.40 0.34 0.60 0.20 0.40 0.61 0.90 0.20 0.20 0.41 0.70 0.09
0.30 O.Q7 1.60 0.30 0.40 0.14 1.50 0.20 0.20 0.05 1.20 0.20
0.4 0 0.7 0.4 0.3 0 0.8 0.2 0.3 0 0.9 0.03
0.4 0 0.6 0.1 0.3 0 0.6 0.1 0.2 0 0.9 0.02
0.4 0 0.9 0.4 0.3 0 1.0 0.1 0.4 0 1.8 0.08
W-10. ~-11 W-12
Ra-226 U-Nat Pb~210 Th:-232, Ra-2-26 U-Nat Pb-210 Th-232 Ra-226 U-Nat Pl):.:210 Th-232 Ra-226
0.40 0.34 0.30 0.30 0.50 0.20 0.50 0.40 0.20 0.14 1.10 0.10 0.40
0.40 0.o7 0.40 0.40 0.30 0.14 0.30 0.20 0.20 0.05 0.70 0.09 0.30
0.3 0 0.4 0.1 0.3 0 1.1 0.1 0.2 0 0.6 0.1 0.4
0.3 0 0.4 0.1 0.4 0 0.9 0.1 0.1 0 0.9 0.1 0.2
0.4 0 0.3 0.2 0.5 0 0.5 0.2 0.2 0 0.5 O.o3 0.4
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
VV-13 W-1~ W-1$
0-Nat Pb-2110 Th-232 Ra-226 0-Nat Pb-210 Th-232 Ra-226 U•Nat 1Pb-210
0.27 1.20 0.20 0.40 0.27 1.10 0.20 0.40 0.34 0.60
0.14 0.50 0.10 0.002 0.27 0.40 0.40 0.20 0.27 0.30
0 0.6 0.3 0.2 0 0.7 0.10 0.3 0 1.3
0 0.7 0.09 0.2 0 0.8 0.o7 0.3 0 1.7
0 0.5 0.09 0.2 0 0.4 0.01 0.5 0 1.1
Th-232
0.20
0.00
0.1
0.1
0.2
W-16 W-17 W-18
Ra-226 0-Nat Pb-Z.10 'th-232 Ra-226, U•.Nnt. Pb•2<10 Tb-232 Ra-226 U-Nat Pb-210 Th-~2
0.60 0.34 0.70 0.40 0.50 0.34 1.20 0.40 0.50 0.34 0.90 0.20
0.30 0.41 0.30 0.00 0.40 0.34 0.60 0.20 0.50 0.34 0.80 0.50
0.4 0 1.2 0.4 0.5 0 0.5 0.30 0.5 0 1.2 0.20
0.3 0 1.1 0.1 0.3 0 1.2 0.02 0.3 0 0.7 0.02
0.5 0 1.3 0.3 0.5 0 0.5 0.10 0.6 0 0.5 0.20
Table 1-3
WHITE MESA MILL
Soil Sampling Results
Duplicate Sample Results
(pCi/g)
E-10
2
0.7
0.6
0.3
Constituent W-15
Uranium (mg/kg) <1
Lead 210 (pCi/g) 1.1
Radium 226 (pCi/g) 0.5
Thorium 232 (pCi/g) 0.2
Constituent W-05
Uranium (mg/kg) <1
Lead 210 (pCi/g) 0.7
Radium 226 (pCi/g) 0.3
Thorium 232 (pCi/g) 0.1
E-10D
2
0.5
0.6
0.2
W-150
<1
1.4
0.4
0.2
W-050
<1
0.6
<0.08
0.2
Duplicate RPD results are outside of the 35% RPD limit.
%RPO
0.0
%RPO
NC
24.0
22.2
0.0
%RPO
NC
15.4
ATTACHMENT J
RADON MONITORING GRAPHS AND DATA
White Mesa Mill Radon Sampling Results*
BHV-1 BHV-2 BHV-4 BHV-5
BHV-1 Calculated BHV-2 Calculated BHV-3 BHV-4 Calculated BHV-5 Calculated
Date (pCi/L) ECL (pCi/L) ECL (pCi/L) (pCi/L) ECL (pCi/L) ECL
01/02/13 0.1 0.71 0 0.34 0.6 0.4 0.5 0 1.43
03/29/13 0.1 0.71 0 0.34 0.7 0.3 0.5 0.5 1.43
07/01/13 0 0.71 0 0.34 0.06 0 0.5 0 1.43
10/01/13 0.1 0.71 0 0.34 O.Q7 0 0.5 NA 1.43
12/24/13 0.4 0.71 0 0.34 0.07 0.33 0.5 0.43 1.43
04/02/14 0.2 0.71 0 0.34 0.06 0.04 0.5 0.54 1.43
06/27/14 0.1 0.71 0 0.34 O.Q7 0 0.5 0.03 1.43
09/30/14 0.2 0.71 0.1 0.34 0.1 0.2 0.5 0.3 1.43
01/07/15 0.1 0.71 0 0.34 0.2 0.3 0.5 0.6 1.43
04/02/15 0.23 0.71 0 0.34 0.07 0.23 0.5 0.43 1.43
06/29/15 0.2 0.71 0.2 0.34 0.2 0.4 0.5 0.4 1.43
09/28/15 0.2 0.71 0.1 0.34 0.3 0.2 0.5 0.6 1.43
01/04/16 0 0.71 0 0.34 0.2 0.4 0.5 0.7 1.43
04/04/16 0 0.71 0.1 0.34 0.2 0 0.5 0.7 1.43
07/05/16 0.1 0.71 0 0.34 0.07 0 0.5 0.23 1.43
10/10/16 0.06 0.71 0 0.34 0.35 0.30 0.5 0.38 1.43
01/05/17 0.14 0.71 0.09 0.34 0.32 0.25 0.5 0.38 1.43
03/29/17 0.05 0.71 0.27 0.34 0.11 0.21 0.5 0.51 1.43
07/05/17 0.06 0.71 0 0.34 0.16 0.14 0.5 0.25 1.43
09/29/17 0.06 0.71 0 0.34 0.24 0 0.5 0.08 1.43
01/02/18 0.17 0.71 0.06 0.34 0.32 0.30 0.5 0.54 1.43
04/02/18 0.08 0.71 0 0.34 0.24 0.25 0.5 0.41 1.43
07/05/18 0.05 0.71 0 0.34 0.11 0.03 0.5 0.24 1.43
10/05/18 0.13 0.71 0.05 0.34 0.19 0.27 0.5 0.27 1.43
01/10/19 0.13 0.71 0.05 0.34 0.30 0.40 0.5 0.59 1.43
04/05/19 0.00 0.71 0 0.34 0.43 0.11 0.5 0.27 1.43
07/02/19 0.05 0.71 0 0.34 0.19 0.03 0.5 0.19 1.43
10/01/19 0.27 0.71 0.14 0.34 0.16 0.43 0.5 0.49 1.43
01/07/20 0.08 0.71 0 0.34 0.30 0.16 0.5 0.32 1.43
* -Measurements obtained from BHV-3 have been designated as background due to BHV-3's remoteness from the Mill site. The
results in the table above are the above-background results with background (BHV-3) subtracted. Any negative values are
reported as zero for graphical purposes.
NA -Not Available -the canister was damaged. No data reported.
NS -Not Sampled -EFRI installed and began radon sampling at BHV-7 and BHV-8 in the fourth quarter of 2014.
BHV-6
BHV-6 Calculated
(pCi/L) ECL
0.4 0.83
0.1 0.83
0 0.83
0 0.83
0.73 0.83
0.24 0.83
0.03 0.83
0.2 0.83
0.2 0.83
0.23 0.83
0.3 0.83
0.3 0.83
0.1 0.83
0.1 0.83
0 0.83
0.08 0.83
0.19 0.83
0.35 0.83
0.19 0.83
0 0.83
0.27 0.83
0.14 0.83
0.08 0.83
0.22 0.83
0.21 0.83
0 0.83
0.11 0.83
0.22 0.83
0.21 0.83
BHV-7 BHV-8
BHV-7 Calculated BHV-8 Calculated
(pCi/L) ECL (pCi/L) ECL
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
0.2 1.12 0.1 0.71
0.33 1.12 0.03 0.71
0.2 1.12 0.2 0.71
0 1.12 0.1 0.71
0.2 1.12 0.1 0.71
0 1.12 0 0.71
0 1.12 0 0.71
0.03 1.12 0 0.71
0 1.12 0.14 0.71
0.13 1.12 0.16 0.71
0.11 1.12 0.11 0.71
0.06 1.12 0 0.71
0.11 1.12 0.25 0.71
0.14 1.12 0.17 0.71
0.08 1.12 0 0.71
0.13 1.12 0.16 0.71
0.19 1.12 0.21 0.71
0 1.12 0 0.71
0 1.12 0 0.71
0.43 1.12 0.33 0.71
0.13 1.12 0.16 0.71
pCi\L
0 0 0 0 0 0 0 0
0 _._ i\, (,) ~ 0, 0) " CX)
1/2/2013
+ 3/29/2013
OJ 7/1/201 I < I 10/1/2013 u.) -C" 12/24/2013 Ill 0 " cc 4/2/2014 .... 0 C: ::::, 6/27/2014 a. -
9/30/2014
1/7/2015
+ 4/2/2015
OJ 6/29/2015 m I < :c I 9/28/2015 _._ < ~ I ;:;: 1/4/201 ...... ::::r
OJ 4/4/201 ~ Ill 0 m " cc 7/5/2016 C. .... 0
C: 0 ::::, 10/10/2016 a. :s CJ) I C: 1/5/2017 I\) C" ..... I\) .... Ill 0 3/29/2017 I\) ..... (t) a. 7/5/2017
9/29/2017
+ 1/2/2018
4/2/2018 OJ I < I 7/5/2018 _._
0 10/5/2018 Ill
0 C: 1/10/2019
!! (t) 4/5/201 a.
m 0 r
10/1/2019
1/7/2020
pCi\L
9 0 0 0 9 0 0 0
0 ...... i--, w :i:,.. 0, CJ) ....... co
1/2/201
+ 3/29/201
lD I 7/1/201 < I w 10/1/201 -0-Ill 12/24/201 0 ca a 4/2/201 C ::, a. 6/27/201 -
9/30/2014
+
1/7/201
4/2/201 lD I < _, __ , __ ·-
I m I\)
~ 9/28/2015 :c ;::;.: :;;r -:=: OJ 1/4/201 Ill I\) 0 "" co ::c -,
0 C 7/5/201 m ::, a. C. en 10/10/201 . 0 C
0-::::, -iil I
0 I\) -(D 3/29/2017 I\) 0. I\)
t 9/29/201
OJ I 4/2/201 < I I\)
(') 7/5/201 ll> 0 C
Ill -(D a.
m (') 4/5/201 r
7/2/201
pCi\L
0 0 0 0 0 p p p
0 ...... i\> (,) ~ 0, 0) """ (X)
1/2/2013
3/29/2013
7/1/2013
10/1/2013
12/24/2013
4/2/2014
6/27/2014
9/30/2014
1/7/2015
4/2/2015
6/29/2015
9/28/2015 m :c
+ 1/4/2016 ~
OJ 4/4/2016 (,J
:r: < :IJ I 7/5/2016 (,) Q)
10/10/2016 I I I I I I I I C.
0
1/5/2017 I I I __.I.II I I I I ~ I
3/29/2017 I .---I I I I I I I
I\)
I\)
I\)
7/5/2017
9/29/2017
1/2/2018
4/2/2018
7/5/2018
10/5/2018
1/10/2019
4/5/2019
7/2/2019
10/1/2019
1/7/2020
t
Cl)
::I: < I u) -O" I» C')
" (Cl .... 0 C: :::, a. -
+ Cl)
::I: < I .Jl,.
::E ;:.: :::r
Cl)
I» C')
" (Cl .... 0 C: :::, a.
en C: C" -.... I» C') -CD a.
+ Cl)
::I: < I
.Jl,.
()
I»
C')
C:
Q) -CD a.
m () r-
0 0
0 ...... i\:>
1/2/2013
3/29/2013
7/1/201
10/1/201
6/27/201
9/30/2014
1/7/2015
4/2/2015
6/29/2015
9/28/2015
1/4/2016
4/4/201
7/5/201
10/10/2016
1/5/2017
3/29/2017
7/5/2017 1 ~
9/29/201
10/5/2018
1/10/2019
4/5/2019
10/1/2019
1/7/2020
pCi\L
0 0 0 0 0 0
(,J :i:,. 01 O> :..i co
a, :c ~ ~
:D
D)
C.
0
::l
I N
I I f I I I N N
+ OJ I < I u)
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White Mesa Mill Radon
Sampling
Quarterly Field Blank Results
Field Blank
Date (pCi/L)
1/2/2013 2.4
3/29/2013 1.4
7/1/2013 0.7
10/1/2013 0.3
12/24/2013 0.7
4/2/2014 1.6
6/27/2014 1.1
9/30/2014 0.8
1/7/2015 1.4
4/2/2015 1.0
6/29/2015 1.7
9/28/2015 1.5
1/4/2016 1.8
4/4/2016 2.0
7/5/2016 1.1
10/10/2016 1.6
1/5/2017 1.6
3/29/2017 1.1
7/5/2017 0.7
9/29/2017 0.84
1/2/2018 1.6
4/2/2018 1.9
7/5/2018 0.8
10/5/2018 1.0
1/10/2019 1.5
4/5/2019 1.6
7/2/2019 1.1
10/1/2019 1.1
1/7/2020 1.7
radonova
lhe global leader in radon measurement
Test results
RADON MONITORING REPORT
Issued by an Accredited Laboratory
REPORT NUMBER
5494949:1
REPORT DATE
10/14/2019
REPORT PAGE 2 ( 4 )
PRINT DATE
10/14/2019
Detector Start date Stop date Location Detector comment Location type Avg Radon
Conc.pCi/1
Total Radon
Exp pCi-days/1
984639-5 07/02/2019 10/01/2019 BHV-1-1
233199-9 07/02/2019 10/01/2019 BHV-2-1
264030-8 07/02/2019 10/01/2019 BHV-4-1
548030-6 07/02/2019 10/01/2019 BHV-5-1
245159-9 07/02/2019 10/01/2019 BHV-6-1
346217-3 07/02/2019 10/01/2019 BHV-7-1
775425-2 07/02/2019 10/0l/2019 BHV-8-1
539351-7 07/02/2019 10/01/2019 BHV-2A-l
222769-2 07/02/2019 10/01/2019 Bl.ackMesa 1
965062-3 07/02/2019 10/01/2019 Office MM '/
Comment to the results
Tryggve Ronnqvist (Electronically signed)
Signature Radonova Laboratories AB Laboratory Measurement Specialist
This report may only be reproduced In full, unless the issuing laboratory has given
prior written approval.
I Out-door 0.43 ± 0.11 38± II
Out-door 0.30 ± 0.11 28± II
'
Out-door 0.59 :1: 0.14 55± 14
Out-door 0.65 ± 0.17 60± 16
Out-door 0.38 ± 0.11 34± II
Out-door 0.59 ±0.14 55± 14
Out-door 0.49 ±0.14 44± 14
Out-door 0.32 ± 0.11 30± II
Out-door 0.16 ± 0.09 16±9
In-door I.I ± 0.17 IOI± 18
Radonova Inc.
900 Oakmont Lane Suite 207,Westmont IL 60559
Telephone: [phone] E-mail: [e-mail]
DISCLAIMER -Radonova Inc. makes no warranty of any kind, express or implied, as regard to the use, operation or analysls of any Radonova Inc. monitor. Radonova Inc. specifically disclaims Implied warranties of
merchantability and fitness ror a particu'1r purpose. Radonova Inc. is not responsible for any damage, Including consequential damages, to persons or property resulting from the use or the monitor or the resulting data.
4511 us
0 .....
radonova
The gbbal leader in radon measurement
Energy Fuels
6425 S HWY 191
Blanding UT 84511
United States
RADON MONITORING REPORT
Issued by an Accredited Laboratory
107831-AL, 107830-RT, NRSB ARL1904
REPORT NUMBER REPORT PAGE 3 ( 4 )
5494949: 1
REPORT DATE
10/14/2019
MEASUREMENT PERFORMED FOR
6425 S HWY 191
Blanding UT 84511
REPORT RECEIVER(S)
PRINT DATE
10/14/2019
The analysis results are located on page 2 of this document.
Description of the measurement
The measurement was performed with a closed high-sensitivity alpha-track detector.
The detector(s) arrived to Radonova Laboratories AB 10/07/2019. They were measured 10/11/2019
Property data and address
6425 S HWY 191
Blanding UT 84511 Transit Detector 1:
Transit Detector 2:
Transit Detector 3:
Measurement method: closed alpha-track high sensitivity detector
725312
128122
The radon measurement was performed with a closed alpha-track detector following the quality assurance guidance given In EPA 402-R-95-012.
14111 ,~rlflr.<: rnm
The detector container is manufactured from electrically conducting plastic.Through a small slit (filter), radon gas enters the detector.The crack-detectfng
material (film) Inside the detector Is hit by alpha particles generated by the radon eNering the container and the decay products formed from it. On the film, the
alpha particles make small cracks which are enlarged through chemical etching and later counted in a microscope in order to determine the radon exposure.
Transit detectors are used for the rewrn delivery of the high-sensitivity detectors in order to make a more accurate background subtraction.
Radonova Laboratories AB is accredited (no. 1489) by SWEDAC to conduct radon-gas measurements using the closed alpha-track detector method. The analysis
equipment is checked daily and the detectors are calibrated at regular intervals.
NRPP Licenses: I 0783 I AL, I 07830 RT
Measured radon concentrations
For each detector, the measured value of the radon concentration is given. For each value an uncertainty associated with the measurement to a 95% confidence
level also given. For example a measurement result of 4.0 ± 0.5 pCl/1 means tha.t the radon concentration is most likely contained in the range 3.5-4.5 pCi/1 .
If the start or end dace of the measurement has not been provided, the radon concentration cannot be calculated. In such cases, the total exposure in pCi*days/1
will be reported.
More information about radon measurements and mitigation can be found in the AARST and EPA publications:
ANSI/AARST Protocol for Conducting Measurements of Radon and Radon-Decay Products in Schools and Large Buildings
ANSI/AARST Protocol for Conducting Radon and Radon Decay Product Measurements in Multifamily Buildings.
ANSI/AARST Radon Mitigation Standards for Schools and Large Buildings.
ANSI/AARST Radon Mitigation Standards for Multifamily Buildings.
EPA Radon Measurements in Schools, EPA 402-R-92-014, July 1993.
A Citizen's Guide to Radon
Home Buyer's and Seller's Gudie to Radon
Consumer's Gudie to Radon Reduction
For more information about the interpretation of your test results or about other radon related issues we suggest contacting your state radon office.
Signature on the report
With the signature on the report, the person responsible for the radon analysis at Radonova Laboratories AB hereby certifies that the measurement procedures
follows the guidance in accordance with EPA 402-R-95-012 and that the demands from SWEDAC are fulfilled.
DISCLAIMER -Radonova Inc. makes no warranty of any kind, express or implied, as regard to the use, operation or analysis of any Radonova Inc. monitor. Radonova Inc. specifically disclaims implied warranties of
merchantability and fitness for a particular purpose. Radonova Inc. is not responsible for any damage, including consequential damages, to persons or property resulting from the use of the monitor or the resulting data.
"' .J
0 ......
radonova RADON MONITORING REPORT
Issued by an Accredited Laboratory 1he gk:Jbal leader in radon measurement
REPORT NUMBER REPORT PAGE 2 (2 )
5588686:l
REPORT DATE PRINT DATE
01/21/2020 01/21/2020
Test results
,;tiBD,t('
~v~
~801-r't~ ,..,
IS(Um::l'lfTH
Detector Start date Stop date Location Detector comment Location type Avg Radon
Conc.pCi/1
Total Radon
Exp pCi-days/1
483784-5 10/01/2019 01/07/2020 BHV-1-1
180877-3 10/01/2019 01/07/2020 BHV-2-1
774956-7 10/01/2019 01/07/2020 BHV-4-1
351381-9 10/01/2019 01/07/2020 BHV-5-1
938901-6 10/01/2019 01/07/2020 BHV-6-1
452727-1 10/01/2019 01/07/2020 BHV-7-1
119287-1 10/01/2019 01/07/2020 BHV-8-1
566226-7 10/01/2019 01/07/2020 BHV-2A-l
585072-2 10/01/2019 01/07/2020 Office-I
364556-1 10/01/2019 01/07/2020 Black Mesa 1
Comment to the results
Tryggve Ronnqvist (Electronically signed)
Signature Radonova Laboratories AB Laboratory Measurement Specialist
This report may only be reproduced in full, unless the issuing laboratory has given
prior written approval.
Out-door 0.38 ± 0.11 38± 11
Out-door 0.22 ± 0.09 21 ±9
Out-door 0.46 ± 0.11 45 ± II
Out-door 0.62 ± 0.14 62± 14
Out-door 0.51 ± 0.14 50± 14
Out-door 0.43 ± 0.11 42± 11
Out-door 0.46 ± 0.11 44± 11
Out-door 0.46 ± 0.11 46± 11
In-door 1.7 ±0.25 164±25
Out-door 0.30 ± 0.09 30±9
Radonova Inc.
900 Oakmont Lane Suite 207, Westmont IL 60559
Telephone: [phone] E-mail: [e-mail]
DISCLAIMER-Radonova Inc. makes no warranty of any kind, express or Implied, as regard to the use, operation or analysis of any Radonova Inc. monitor. Radonova Inc. specifically disclaims lmplled warranties of
merchantability and fitness for a particular purpose. R.adonova Inc. is not responsible for any damage, including consequential damages, to persons or property resulting from the use of the monitor or the resulting data.
4511 us
radonova
The gbbal leader in radon measurement
Energy Fuels Resouces
Garrin Palmer
6425 S. Highway 191
PO Box 809
Blanding UT 84511
United States
17121
RADON MONITORING REPORT
Issued by an Accredited Laboratory
107831-AL, 107830-RT, NRSB ARL1904
REPORT NUMBER REPORT PAGE 1 ( 2 )
5588686: 1
REPORT DATE
01/21/2020
MEASUREMENT PERFORMED FOR
6425 S Hwy 191
Blanding UT 84511
REPORT RECEIVER{S)
Energy Fuels Resouces
PRINT DATE
01/21/2020
The analysis results are located on page 2 of this document.
Description of the measurement
The measurement was performed with a closed high-sensitivity alpha-track detector.
The detector(s) arrived to Radonova Laboratories AB 01/13/2020. They were measured 01/20/2020
Property data and address
6425 S Hwy 191
Blanding UT 84511
Measurement method: closed alpha-track high sensitivity detector
Transit Detector 1:
Transit Detector 2:
Transit Detector 3:
657648
The radon measurement was performed with a closed alpha-track detector following the quality assurance guidance given in EPA 402-R-95-012.
The detector container is manufactured from electrically conducting plastic.Through a small slit (filter), radon gas enters the detector.The track-detecting
material (film) inside the detector is hit by alpha particles generated by the radon entering the container and the decay products formed from it. On the film, the
alpha particles make small tracks which are enlarged through chemical etching and later counted in a microscope in order to determine the radon exposure.
Transit detectors are used for the return delivery of the high-sensitivity detectors in order to make a more accurate background subtraction.
Radonova Laboratories AB is accredited (no. 1489) by SWEDAC to conduct radon-gas measurements using the closed alpha-track detector method. The analysis
equipment is checked daily and the detectors are calibrated at regular intervals.
NRPP Licenses: 107831 AL, 107830 RT
Measured radon concentrations
For each detector, the measured value of the radon concentration is given. For each value an uncertainty associated with the measurement to a 95% confidence
level also given. For example a measurement result of 4.0 ± 0.5 pCi/1 means that the radon concentration is most likely contained in the range 3.5-4.S pCi/1 .
If the start or end date of the measurement has not been provided, the radon concentration cannot be calculated. In such cases, the total exposure in pCi*days/1
will be reported.
More information about radon measurements and mitigation can be found in the AARST and EPA publications:
ANSI/AARST Protocol for Conducting Measurements of Radon and Radon-Decay Products in Schools and Large Buildings
ANSI/AARST Protocol for Conducting Radon and Radon Decay Product Measurements in Multifamily Buildings.
ANSI/AARST R.rdon Mitigation Standards for Schools and Large Buildings.
ANSI/AARST Radon Mitigation Standards for Multifamily Buildings.
EPA Radon Measurements in Schools, EPA 402-R-92-014, July 1993.
A Citizen's Guide to Radon
Home Buyer's and Seller's Gudie to Radon
Consumer's Gudie to Radon Reduction
For more information about the interpretation of your test results or about other radon related issues we suggest contacting your state radon office.
Signature on the report
With the signature on the report, the person responsible for the radon analysis at Radonova Laboratories AB hereby certifies that the measurement procedures
follows the guidance in accordance with EPA 402-R-95-012 and that the demands from SWEDAC are fulfilled.
DISCLAIMER-Radonova Inc. makes no warn.nty of any kind, e,cpress or implied, as regard to the use, operation or analysis of any Radonova Inc. monitor: Radonova Inc. specifically disclaims implied warranties of
merchantabillty and fitness for a. particular purpose. Ra.donova. Inc. is not responsible for any damage, including consequential damages, to persons or property resulting from the use of the monitor or the resultJng data.
Calculation of Location-Specific Effluent Concentration Limits for Radon Track Etch
Monitoring Stations at White Mesa Mill
Calculation Methodology
For the purpose of evaluating alpha track data and compliance with the effluent concentration
limit for radon, two referenced limits are listed in the regulations (10 CFR Pait 20 Appendix B,
Table 2, which are incorporated by reference into R313-15-302(2)(b)(i)). One limit (lx 10-10
uCi/ml or 0.1 pCi/1) is applicable in instances where radon daughters are present with the radon,
and are in 100% equilibrium with the parent Rn-222. The other listed concentration limit (1 x
10-8 uCi/ml or 10 pCi/1) is applicable when radon daughters are not present. Both limits
represent the concentration at which a member of the public would receive a 50 mrem dose
assuming 100% (8760 hours) occupancy.
At the White Mesa Mill, the assumption of 100% equilibrium of radon progeny with parent Rn-
222 is unrealistic given the short half-lives of the nuclides considered and the short travel time to
the monitoring locations. Radon emanates from the ground ( or mill tailings) without daughters
present, and the daughters grow in over time. It is therefore necessary to evaluate radon daughter
equilibrium at each air monitoring station utilizing site-specific wind speed and distance
information to derive site-specific Effluent Concentration Limits (ECLs) for each station.
Such disequilibrium situations and alternative calculations are anticipated by the regulations and,
in particular, R313-15-302(3) provides a means by which the licensee may adjust the effluent
concentration values in 10 CFR Part 20 Appendix B, Table 2, which are incorporated by
reference into R313-15-302(2)(b)(i), to account for disequilibrium. The regulatory purpose of
such an adjustment is to appropriately take into account the actual characteristics of the measured
effluents, including radioactive decay equilibrium.
An established (EPA, 1986) outdoor equilibrium formula to determine the appropriate
Equilibrium Factor for use in calculating the ECL for disequilibrium conditions was used. The
EPA expression of the outdoor Equilibrium Factor (EF) is derived by the following equation:
EF = 1.0-0.0479exp(-,t4·39> _ 2.1963exp<-1138·6> + l.2442exp<-1128A>
[Where: tis the travel time in minutes (distance/wind speed)]
Once the Equilibrium Factor has been determined, the ECL for each air monitoring station is
determined by dividing the 0.1 pCi/1 limit (for situations when daughters are present) by the
Equilibrium Factor (EF).
Results
By utilizing the above formula, the appropriate (equilibrium adjusted) ECLs for the location was
calculated. In developing the ECLs, distances and corresponding travel times have been
determined by:
• assuming a nominal centroid located approximately at the vanadium dryer stack,
• calculating average wind speeds appropriate for each direction from the centroid to each
monitoring station location, and
• using Google Earth to develop the distances.
Meteorological data collected at the Mill's Met Station were utilized to compute the average
wind speed for different directions. These data are applicable and sufficient for the purpose of
these calculations.
It should be noted when comparing actual measurement values to the derived ECLs that the
derived ECL provides ample protection for members of the public. More specifically, if dose
calculations had been performed utilizing current ICRP 65 dose conversion conventions, the
ECLs established here would represent approximately 25 mrem for continuous exposure at the
monitoring stations. Therefore these values can serve as appropriate ALARA goals, since they
yield doses well below the 100 mrem standard for individual members of the public.
References
United States Environmental Protection Agency (EPA). (1986). Final rule for radon-222
emissions from licensed uranium mill tailings. Washington, D.C.: Office of Radiation Programs,
U.S. Environmental Protection Agency.
ATTACHMENT K
CELL 2 RADON FLUX DATA
Cell2
2019 Radon Flux Measurement Program
Second Half 2019 Sampling Results
White Mesa Mill
6425 South ffighway 191
Blanding, Utah 84511
Prepared for: Energy Fuels Resources, (USA) Inc.
6425 S. Highway 191
P.O. Box809
Blanding, Utah 84511
Prepared by: Tellco Environmental
P.O. Box 3987
Grand Junction, Colorado 81502 .
TABLE OF CONTENTS
Page
1. INTRODUCTION ........................................................................................................................... 1
2. SITE HISTORY AND DESCRIPTION .......................................................................................... 1
3. REGULATORY REQUIREMENTS FOR THE SITE .................................................................... 1
4. SAMPLING METHODOLOGY ..................................................................................................... 1
5. FIELD OPERA TIO NS .................................................................................................................... 2
5 .1 Equipment Preparation ....................................................................................................... 2
5.2 Sample Locations, Identification, and Placement.. ........................................................... 2
5.3 Sample Retrieval ............................................................................................................... 3
5.4 Environmental Conditions ................................................................................................ 3
6. SAMPLE ANALYSIS ..................................................................................................................... 3
6.1 Apparatus ........................................................................................................................... 3
6.2 Sample Inspection and Documentation ............................................................................. 4
6.3 Background and Sample Counting .................................................................................... 4
7. QUALITY CONTROL (QC) AND DATA VALIDATION ........................................................... 4
7.1 Sensitivity .......................................................................................................................... 5
7 .2 Precision ............................................................................................................................. 5
7 .3 Accuracy ............................................................................................................................ 5
7 .4 Completeness ..................................................................................................................... 5
8. CALCULATIONS ........................................................................................................................... 5
9. RESULTS ........................................................................................................................................ 6
9 .1 Mean Radon Flux ............................................................................................................... 6
9 .2 Site Results ......................................................................................................................... 7
References ............................................................................................................................................ 8
Figure 1 ................................................................................................................................................ 9
Appendix A. Charcoal Canister Analyses Support Documents
Appendix B. Recount Data Analyses
Appendix C. Radon Flux Sample Laboratory Data, Including Blanks
Appendix D. Sample Locations Map (Figure 2)
i
1. INTRODUCTION
During October 9-10, 2019 Tellco Environmental, LLC (Tellco) of Grand Junction, Colorado,
provided support to Energy Fuels Resources (USA) Inc. (Energy Fuels) to conduct radon flux·
measurements on Cell 2 at its White Mesa Mill site.
Pursuant to Utah Department of Environmental Quality (UDEQ) requirements, Energy Fuels conducts
radon flux measurements on a semiannual basis. This report presents the radon flux measurements
results for Cell 2 that represent the second half of the year 2019.
Tellco was contracted to provide radon canisters, equipment, and canister-placement personnel as well
as lab analysis of samples collected. Energy Fuels personnel provided support for loading and
unloading charcoal from the canisters. This report details the procedures employed by Energy Fuels
and Tellco to obtain the results presented in Section 9.0 of this report.
2. SITE DESCRIPTION
The White Mesa Mill facility is located in San Juan County in southeastern Utah, six miles south of
Blanding, Utah. The mill began operations in 1980 for the purpose of extracting uranium and
vanadium from feed stocks.
Cell 2, which has a total area of approximately 270,624 m2, has been filled and covered. This cell is
comprised of one region, a soil cover of varying thickness. There was no standing liquid and were no
exposed tailings within Cell 2 during this sampling.
3. REGULATORY REQUIREMENTS FOR CELL 2
Radon emissions from the uranium mill tailings for Cell 2 at this site are regulated by the State of
Utah's Division of Waste Management and Radiation Control (DWMRC). In accordance with
DWMRC requirements specified in correspondence dated July 23, 2014, Energy Fuels must measure
the radon flux on Cell 2 in accordance with 40 CFR 61, Appendix B, Method 115, "Monitoring for
Radon-222 Emissions" semiannually. The average annual measured radon flux for Cell 2 shall not
exceed a value of20 picoCuries per meter squared per second (pCi/m2-s):
4. SAMPLING METHODOLOGY
Radon emissions were measured using Large Area Activated Charcoal Canisters (canisters) in
conformance with 40 CFR, Part 61, Appendix B, Method 115, Restrictions to Radon Flux
Measurements, (EPA, 2019). These are passive gas adsorption sampling devices used to determine
the flux rate of radon-222 gas from a surface. The canisters were constructed using a 10-inch
diameter PVC end cap containing a bed of 180 grams of activated, granular charcoal. The prepared
charcoal was placed in the canisters on a support grid on top of a Yi inch thick layer of foam and
secured with a retaining ring under 1 Yi inches of foam (see Figure 1, page 9).
One hundred sampling locations were distributed throughout Cell 2 ( consisting of one region) as
depicted on the Sample Locations Map (see Figure 2; Appendix D). Each charged canister was placed
1
directly onto the surface (open face down) and exposed to the surface for 24 hours. Radon gas
adsorbed onto the charcoal and the subsequent radioactive decay of the entrained radon resulted in
radioactive lead-214 and bismuth-214. These radon ·progeny isotopes emit characteristic gamma
photons that can be detected through gamma spectroscopy. The original total activity of the
adsorbed radon was calculated from these gamma ray measurements using calibration factors
derived from cross-calibration of standard sources containing known total activities of radium-226
with geometry identical to the counted samples and from the principles of radioactive decay.
After approximately 24 hours, the exposed charcoal was transferred to a sealed plastic sample
container (to prevent sample loss and/or further exposure during transport), identified and labeled, and
transported to the Tellco laboratory in Grand Junction, Colorado for analysis. Tellco personnel
maintained custody of the samples from collection through lab analysis.
Upon completion of on-site activities, the field equipment was alpha and beta-gamma scanned by
Energy Fuels Radiation Safety personnel for possible contamination resulting from fieldwork
activities. All of the field equipment used was subsequently released for unrestricted use.
5. FIELD OPERATIONS
5.1 Equipment Preparation
All charcoal was dried at 110°C before use in the field. Unused charcoal and recycled charcoal were
treated the same. 180-gram aliquots of dried charcoal were weighed and placed in sample containers.
Proper balance operation was verified daily by checking a standard weight. The balance readout
agreed with the known standard weight to within± 0.1 percent.
After acceptable balance check, empty containers were individually placed on the balance and the
scale was re-zeroed with the container on the balance. Unexposed and dried charcoal was carefully
added to the container until the readout registered 180 grams. The lid was immediately placed on the
container and sealed with plastic tape. The balance was checked for readout drift between readings.
Sealed containers with unexposed charcoal were placed individually in the shielded counting well,
with the bottom of the container centered over the detector, and the background count rate was
documented. Three five-minute background counts were conducted on ten percent of the containers,
selected at random to represent the "batch". If the background counts were too high to achieve an
acceptable lower limit of detection (LLD), the entire charcoal batch was labeled non-conforming and
recycled through the heating/drying process.
5.2 Sample Locations, Identification, and Placement
On October 9, 2019, 100 sampling locations were spread out throughout the Cell 2 covered region.
The approximate sampling locations that were established for previous samplings of Cell 2 were used
for · the placement of the canisters, although the actual sample identification numbers (IDs) are
different. An individual ID was assigned to each sample point, using a sequential alphanumeric
system indicating the charcoal batch and physical location within the region ( e.g., FO 1 ... F 100). This
ID was written on an adhesive label and affixed to the top of the canister. The sample ID, date, and
2
time of placement were recorded on the radon flux measurements data sheets for the set of one
hundred measurements.
Prior to placing a canister at each sample location, the retaining ring, screen, and foam pad of each
canister were removed to expose the charcoal support grid. A pre-measured charcoal charge was
selected from a batch, opened and distributed evenly across the support grid. The canister was then
reassembled and placed face down on the surface at each sampling location. Care was exercised not
to push the device into the soil surface. The canister rim was "sealed" to the swJace using a berm of
local borrow material.
Five canisters (blanks) were similarly processed and these canisters were kept inside an airtight plastic
bag during the 24-hour testing period.
5.3 Sample Retrieval
On October 10, 2019 at the end of the 24-hour testing period, all canisters were retrieved,
disassembled and each charcoal sample was individually poured through a funnel into a container.
Identification numbers were transferred to the appropriate container, which was sealed and placed in a
box for transpo1t. Retrieval date and time were recorded on the same data sheets as the sample
placement information. The blank samples were similarly processed.
All 100 of the charcoal samples from the Cell 2 covered region were successfully retrieved and
containerized during the retrieval and unloading process. Upon completion of on-site activities, the
field equipment was alpha and beta-gamma scanned by Energy Fuels Radiation Safety personnel and
released for unrestricted use.
5.4 Environmental Conditions
A rain gauge was placed at Cell 2 to monitor rainfall during sampling; additionally, Energy Fuels
maintains an onsite rain gauge.
In accordance with 40 CPR, Part 61, Appendix B, Method 115:
• Measurements were not initiated within 24 hours of rainfall at the site.
• No rainfall occurred during the 24-hour sampling period after the canisters had been
deployed.
• All canister seals remained intact during the 24-hour sampling period and none of the
canisters were surrounded by water.
6. SAMPLE ANALYSIS
6.1 Apparatus
Apparatus used for the analysis:
• Single-or multi-channel pulse height analysis system, Ludlum Model 2200 with a
Teledyne 3" x 3" sodium iodide, thallium-activated (Nal(Tl)) detector.
3
• Lead shielded counting well approximately 40 cm deep with 5-cm t~ick lead walls and a 7-
cm thick base and 5 cm thick top.
• National Institute of Standards and Technology (NIST) traceable aqueous solution radium-
226 absorbed onto 180 grams of activated charcoal.
• Ohaus Port-0-Gram balance with 0.1-gram sensitivity.
6.2 Sample Inspection and Documentation
Once in the laboratory, the integrity of each charcoal container was verified by visual inspection of the
plastic container. Laboratory personnel checked for damaged or unsealed containers and also checked
that the data sheet was complete. ·
All 100 of the sample containers and 5 blank containers inspected at the Tellco analytical laboratory
were ultimately verified as valid with no damaged or unsealed containers observed.
6.3 Background and Sample Counting
The gamma ray counting system was checked daily, including background and radiwn-226 source
measurements prior · to and after each counting session. Based on calibration statistics, using two
sources with known radium-226 content, background and source control limits were established for
each Ludlum/Teledyne system with shielded counting well (see Appendix A).
Gamma ray counting of exposed charcoal samples included the following steps:
• The length of count time was determined by tbe activity of the sample being analyzed,
according to a data quality objective of a minimum of 1,000 accrued counts for any given
sample.
• The sample container was centered on the Nal gamma detector and the shielded well door
was closed.
• The sample was counted over a determined count length and then the mid-sample count
time, date, and gross counts were documented on the radon flux measurements data sheet
and used in the calculations.
• The above steps were repeated for each exposed charcoal sample.
• Approximately 10 percent of the containers counted were selected for recow1ting. These
containers were promptly recounted within a few days following the original count.
7. QUALITY CONTROL (QC) AND DATA VALIDATION
Charcoal flux measurement QC samples included the following intra-laboratory analytical frequency
objectives:
• Blanks, 5 percent, and
• Recounts, 10 percent
4
All sample data were subjected to validation protocols that included assessments of sensitivity,
precision, accuracy, and completeness. As described below, all Method 115-required data quality
objectives (EPA, 2019) were attained.
7.1 Sensitivity
A total of five blanks were analyzed by measuring the radon progeny activity in samples subjected to
all aspects of the measurement process, excepting exposure to the source region. These blank sample
measurements comprised approximately 5 percent of the field measurements. Analysis· of the five
blank samples measured radon flux rates ranging from less than 0.03 to 0.09 pCi/m2-s, with an
aritlunetic average of approximately 0.05 pCi/m2-s. The lower limit of detection (LLD) for the field
blanks was approximately 0.04 pCi/m2-s.
7 .2 Precision
Ten recount measurements, distributed throughout the sample set, were perfo1med by replicating
analyses of individual field samples (see Appendix B). These recount measurements comprised
approximately 10 percent of the total number of samples analyzed. The precision of recount
measurements, expressed as relative percent difference (RPD), for sample result values that were
above 1 pCi/m2-sec ranged from less than 0.1 percent to approximately 8.7 percent, with an average
of approximately 4.5 percent. This complies with the precision objective of+/-10 percent.
7.3 Accuracy
Accuracy of field measurements was assessed daily by counting two laboratory control samples with
known Ra-226 content. Accuracy of these lab control sample measurements, expressed as percent
bias, ranged from approximately -1.3 percent to +0.9 percent. The arithmetic average bias of the lab
control sample measurements was approximately -0.1 percent (see Appendix A). This complies with
the accuracy objective of+/-10 percent bias.
7.4 Completeness
All 100 samples from the Cell 2 cover region were verified as valid, representing 100 percent
completeness, which complies with the completeness objective of 85 percent.
8. CALCULATIONS
Radon flux rates were calculated for charcoal collection samples using calibration factors derived
from cross-calibration to sources with known total activity with identical geometry as the charcoal
containers. A yield efficiency factor was used to calculate the total activity of the sample charcoal
containers. Individual field sample result values presented were not reduced by the results of the field
blank analyses.
5
In practice, radon flux rates were calculated by a database computer program. The algorithms utilized
by the data base program were ~s follows:
Equation 8.1:
pCi Rn-222/m2sec = [rs* A *b~.sCll/9l.7S)]
where: N = net sample count rate, cpm under 220-662 keV peak
Ts = sample duration, seconds
b = instrument calibration factor, cpm per pCi; values used:
0.16895, forM-01/D-21 and
0.16975, for M-02/D-20
d = decay time, elapsed hours between sample mid-time and count mid-time
A = area of the canister, m2
Equation 8.2:
Gross Sample, cpm Background Sample, cpm ,--------+---------
SampleCount,t,min Background Count,t,min Error,2c, = 2X -'-------------------x Sample Concentration
Equation 8.3:
_ 2.71+(4.65){S~
LLD -[Ts* A *b*O.s<cll9 .1s1
where: 2.71 = constant
4.65 = confidence interval factor
Net,cpm
Sb = standard deviation of the background count rate
Ts = sample duration, seconds
b = instrument calibration factor, cpm per pCi; values used:
0.16895, forM-01/D-21 and
0.16975, for M-02/D-20
d = decay time, elapsed hours between sample mid-time and count mid-time
A = area of the canister, m2
9. RESULTS
9.1 Mean Radon Flux
Referencing 40 CFR, Part 61, Subpart W, Appendix B, Method 115 -Monitoring for Radon-222
Emissions, Subsection 2.1. 7 -Calculations, "the mean radon flux for each region of the pile and for
the total pile shall be calculated and reported as follows:
(a) The individual radon flux calculations shall be made as provided in Appendix A EPA
86(1). The mean radon flux for each region of the pile shall be calculated by summing all
individual flux measurements for the region and dividing by the total number of flux
measurements for the region.
6
(b) The mean radon flux for the total uranium mill tailings pile shall be calculated as follows:
At
Where: J5 = Mean flux for the total pile (pCi/m2-s)
Ji = Mean flux measured in region i (pCi/m2-s)
· Ai = Area of region i (m2)
At = Total area of the pile (m2)"
40 CFR 61, Subpart W, Appendix B Method 115, Subsection 2.1.8, Reporting states "The results of
individual flux measurements, the approximate locations on the pile, and the mean radon flux for each
region and the mean radon flux for the total stack [pile] shall be included in the emission test report. Any
condition or unusual event that occurred during the measurements that could significantly affect the results
should be reported."
9.2 Site Results
Site Specific Sample Results (reference Appendix C)
(a) The mean radon flux for the Cell 2 region at the site is as follows:
Cell 2 -Cover Region = 2.3 pCi/m2-s (based on 270,624 m2 area)
Note: Reference Appendix C of this report for the entire summary of individual measurement results.
(b) Using the data presented above, the calculated mean radon flux for Cell 2 is as follows:
Cell 2 = 2.3 pCi/m2-s
(2.3)(270,624) = 2.3
270,624
As shown above, the arithmetic mean of the radon flux rate measurements representing the second
half of the year 2019 for Cell 2 at Energy Fuels' White Mesa milling facility is well below the U.S.
Nuclear Regulatory Commission and EPA regulatory standard of 20 pCi/m2-s. No condition or
unusual events were observed during the measurements that could significantly affect the results.
Appendix C presents the summary of individual measurement results, including blank sample
analysis. Sample locations are depicted on Figure 2, which is included in Appendix D. The map was
produced by Tellco.
7
References
U. S. Environmental Protection Agency, Radon Flux Measurements on Gardinier and Royster
Phosphogypsum Piles Near Tampa and Mulberry, Florida, EPA 520/5-85-029, NTIS #PB86-
161874, January 1986.
U.S. Environmental Protection Agency, Title 40, Code of Federal Regulations, July 2019.
U. S. Nuclear Regulatory Commission, Radiological Effluent and Environmental Monitoring at
Uranium Mills, Regulatory Guide 4.14, April 1980.
U.S. Nuclear Regulatory Commission, Title 10, Code of Federal Regulations, Part 40, Appendix A,
January 2019.
8
Figure 1
Large Area Activated Charcoal Canisters Diagram
FIG ,q{
I. -on T••c~
Sc.ru~b•• Pj.J
,..,2~,,.. r1t,,l
S..:.rut:r&!f Pal
I f2·ut Tl11,:1t. C11,orcu.::a,
Sup,.,u,,1 0:r4
R,naln,11
Sp11n9
10-111 ~·a
PYC Eo,j C.op
Appendix A
Charcoal Canister Analyses Support Documents
A
ENERGY FUELS RESOURCES
WHITE MESA MILL, BLANDING, UTAH
2019 RADON FLUX MEASUREMENTS
COVER REGION
SAMPLING DATES: 10/09/19-10/10/19
ANALYSIS DATES: 10/13/19-10/14/19
SYSTEM COUNT Bkg Counts. (1 min. each)
1.0. DATE #1 #2
M-01/D-21 10/13/2019 115 128
M-01/D-21 10/13/2019 131 127
M-01/0-21 10/14/2019 126 153
M-01/0-21 10/14/2019 114 120
M-01/0-21 10/13/2019 115 128
M-01/D-21 10/13/2019 131 127
M-01/0-21 10/14/2019 126 153
M-01/0-21 10/14/2019 114 120
M-02/0-20 10/13/2019 118 116
M-02/D-20 10/13/2019 131 107
M-02/0-20 10/14/2019 123 147
M-02/D-20 10/14/2019 106 129
M-02/0-20 10/13/2019 118 116
M-02/0-20 10/13/2019 131 107
M-02/0-20 10/14/2019 123 147
M-02/0-20 10/14/2019 106 129
#3
122
136
141
130
122
136
141
130
142
110
105
115
142
110
105
115
ACCURACY APPRAISAL TABLE
CELL 2 SAMPLES
Source Counts (1 min. each)
#1 #2 #3
9986 10124 10312
10160 10113 10224
10136 10149 10240
10411 10052 10094
10263 10198 10231
10055 10193 10234
10178 10104 10251
10126 10234 10263
10195 10147 10036
10136 10197 10203
10054 10009 10147
10150 10107 10203
10147 10122 10395
9977 10039 10377
10013 10268 10136
9963 10092 10116
AVG NET YIELD FOUND SOURCE
cpm cpm/pCi pCi ID
10019 0.1690 59302 GS-04
10034 0.1690 59392 GS-04
10035 0.1690 59396 GS-04
10064 0.1690 59570 GS-04
10109 0.1690 59834 GS-05
10029 0.1690 59363 GS-05
10038 0.1690 59412 GS-05
10086 0.1690 59700 GS-05
10001 0.1698 58914 GS-04
10063 0.1698 59279 GS-04
9945 0.1698 58586 GS-04
10037 0.1698 59126 GS-04
10096 0.1698 59476 GS-05
10015 0.1698 58999 GS-05
10014 0.1698 58993 GS-05
9940 0.1698 58559 GS-05
AVERAGE PERCENT BIAS FOR ALL ANALYTICAL SESSIONS:
KNOWN %BIAS
pCI
59300 0.0%
59300 0.2%
59300 0.2%
59300 0.5%
59300 0.9%
59300 0.1%
59300 0.2%
59300 0.7%
59300 -0.7%
59300 0.0%
59300 -1 .2%
59300 -0.3%
59300 0.3%
59300 -0.5%
59300 -0.5%
59300 -1.3%
-0.1%
MIN -1.3%
MAX 0.9%
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: \!J~\ \-l. tv'\~~~ t,/\ ~ \ \ 1 °B )~ n J 'l ?1 l lA ::I:-,. b
cLrnNT: En .e ~"'Ji l="u,e \s 4$t01A-i'U s ( u. ,s A) l.., , .
Calibration Check Log
System ID: JV\ -D 7-/ D · "2.-0 Calibration Date: ( () / 1 / 1 ~ Due Date: i O / 7 / ,-o
Scaler SIN: t':j I S-(;? High Voltage: Cl<.> 3 Window: 4.42 Thrshld: 2.20
Detector SIN: 0 LL I 5 3 :i._ Source ID/SN: R "I 2. '2. V /& S .. 05' Source Activity: s'l · 7> j,t-f L.;
9• -Blank Canister Bkgd. Range, cpm: 2 a= ___ ..,, __ to 1 c;-0 3 a= B2 to 1&3
Gross Source Range, cpm: 2 a= _~_e_q_i;--__ to ID~t!,L.J 3 a= q771 to i os-o 7
)) £ .le'~-"-Technician: --------w-~2.£ ...
All counts times are one minute.
Date By Backg ound Counts (1 min. each) Source Counts ( 1 min. each ok?
#1 #2 #3 Avg. #I #2 #3 Average YIN
l0/ 1"'3/ 1.:., IJt-'(. 1\6 I l L,, I 4-z.. t "'2-5 i u i4 i I O I "'],... "2-t o-.,,o,c; 10P"'p,I y
t0/ 1"?;/ 1 P) iJi,.-<. ,~, I 07 110 I\ l, •10,-,-, too~9· I v ·~-7 I i01'3/ 'i
10/ILf-,0) 1)~-l"l-~ \ 't-7 to s-I -z-5"' I 001 '3 i0'~8 101";L, \ O 13~ V
iD/J,.. I 1"> en<. l O (11 l'J... ~ II~ 117 ~<,)/,'~ 1 oe,0i·L to 11 ll \ ooc:;, 'v
tcyl'? , , 0) 'bk " ") \ "2-<, l ~?, l '"2.~ l Oly, °' 0e~ '2-\ OCO~O\ ,oo <.,~ /,
1,o/15j I.:, Vt~ !0°1 \·2...~ l It; 111, 1 oo·J.....'f, 1011&1 too 14-1 Oo-7<...J, r"
I
YIN: Y = average background and source cpm falls within the control limits.
N = average background and source cpm does not fall within the control limits.
The acceptable ranges were detennined from prior background and source check data.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: \N~,+~ jV\.e,~ ~, ff\';\\ 1 )5 \nv, d.t-·"i~)) Li.Jo. b,
CLIENT: £n e'(()J/ t=\,\.,~ \ ~ ~So~> Cu s&) \ V\ c...
System ID: _N_'\_~_0_2-_/_D __ -_-z-_o __
Calibration Check Log
Calibration Date: I O / 7 / I 0 Due Date: I D / ·7) 2 0
'
6-/S"(p 3 9 / _ Scaler SIN:----------High Voltage: I.I) 3 Window: 4.42 Thrshld: 2.20
Detector SIN: 0 Lt \ ':5 3 2 Source ID/SN: Rot -:Z 2 (, / 6 S ·04 Source Activity: • ~9 .3 Jt.# L.'
Blank Canister Bkgd. Range, cpm: 2 CJ = __ g_~--to __ I_S-_O __ 3 CJ= __ B_2 __ to __ I _4'_3 __
Gross Source Range, cpm: 2 CJ= _~_B_'f_ll'_ to I O t, t..f Y: 3 CJ= -~-l.P_0_v __ to I D 5 q 4
Technician: ___ V~_/-__ f _·~ ....... o/'::----
All counts times are one minute.
Date By Background Counts (1 min. each) Source Counts ( l min. each) ok?
#1 #2 #3 Avg. #1 #2 #3 Average YIN
ll!J/1?/ P; ~ l l5 tL\# 14-"2-l"'"Z? JU l17JS-IO I '-ii 1003~ J D/--z._i:.,, 'y
;0/1~/JO) ln-{.. i "3 I \0, I \n J( l, 10,~<F tDl">, 1c1v·~ iOI/~ 'v
,o/; q.J JO) l)U., n .. :1. \4-, IOS"-I--,_,:;;;;-/t)v~t-t I Ol?O"'I I Cl 4'7 10070 y
io/11.fhOJ l>i-L l O l, I "Z..''\ l.l C: I \-1 IO I c:;-o lOI07 102c ·~ 101~3 y
i0/1~·, ,o, lal.,-l, l \ 0, 1~(,o l93'"3 i-, L, l C "2...::;;J 101·2..o \Otc;-J {0/7~ i
I~ i5/ I~ DU I 00,, L-i.... 3 \.\, I J /.., I 0"2 l1-· I 0111 /0~ -i...Lf /0'2.IY y
' '
YIN: Y = average background and source cpm falls within the control limits.
N = average background and source cpm does not fall within the control limits.
The acceptable ranges were detennined from prior background and source check data.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: 'JJ hit-e.. ---=----'---'--.L.-C'4-4--....U.::....L.:...a...=:_e__-=--=+-+-----"'---
C LI ENT: E Vl < lV\. C..
Calibration Check Log
System ID: __ W\_. ~--O .......... / /_D __ -_2 __ 1 _ Calibration Date: I CJ/ "7 / I ~ Due Date: 1 O /7 / 7-0
~, s7-i-I\ .:::: Scaler SIN:----------High Voltage: 7 J Window: __ 4...,..4.._.2.___ Thrshld: 2.20
Detector SIN: _o __ L\_1 _s_3_3 ___ Source ID/SN: fl.."'). 2. i:., I &-s -0 6 Source Activity: 5"1·3~fC
Blank Canister Bkgd. Range, cpm: 2 O' =--+1--'{)~0 __ to -~' _.c;;_7a.__ 3 O' = __ e_<., ___ to __ 1_,_I __
0 C, I L, to I O ~ 57 3 cr = OJ I B I to I OS 9 1-
Technician: __ )_/ __ ;;_c_~-r--~--~--·-
Gross Source Range, cpm: 2 cr=
All counts times are one minute.
Date By Background Counts (1 min. each) Source Counts (1 min. each) ok?
#1 #2 #3 Avg. #1 #2 #3 Average YIN
f 0/1''1 ·~ ~Y"" .\I~ l-i..~ l-rl., I "2-:-Z.. t 0~"3 1010) 0 I 07..~ I j 0"2. ~ I " 10/f") ,,,,, 'Jn,-!.-I) l l "'2,' I~ l,p I ~I J,:;Oc;,, I 01~3 I 0~2.. 3~ \ Ol ~ l 't
\0/ !'i 1·:1! 't)JA.., \'? L, '~" I\.\: I 14-0 \0 ;,e, 10 I OLf· 1 o-i s ·I ,01-;te;> 'I
10/i'-f ,"> t,J,-!, 1 I U. \J..O t,o 17.-I ) .? \L " 102..~ I 0"2.A .• ,3 I o-z..os , '/
ro / ,i; l'-'l lJU,, l I Llj II~ 11'7 11 '5 102'58 i 0~00\ lr-,\0)0 I o ''2.-.;-'-I ''i
;i/6 )C, i)t.,.,v t--i.~ , £;""0 \ "7, ~ 1?J'1 101~ lO 14-1 \ 0·2.6'2. 1€>1 8~ y .
YIN: Y = average background and source cpm falls within the control limits.
N = average background and source cpm does not fall within the control limits.
The acceptable ranges were determined from prior background and source check data.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: V\;l,\~ k . \\'\ ese'\ ~: ll, B l(,1111 J' v!f) I 4 hi k.
CLIENT: E..{1-f.vj 1 ~e., ~ '\2-.~SO\A.V'C..e~ C_u ~It) \ "'c .
Calibration Check Log
System ID: Y"v'l -0 \ / _['-?-' Calibration Date: I O / ·7 / 1 C, Due Date: / O /, ) '2-O ----+---=------.
Scaler SIN: ___ 5"_/_5_7_?-____ High Voltage: l \ / 5" Window: 4.42 Thrshld: 2.20
Detector SIN: __ o __ Li_t ':,_-_3_. _3 ___ Source ID/SN: f::l12 2.<,; /GS -O ~ Source Activity: ,;--q '~ ,~ f (_;
Blank Canister Bkgd. Range, cpm: 2 cr = 100 to IS7 3 cr= 8 (.p to 1-11
Gross Source Range, cpm: 2cr= q9·-i..6 to I OL/7 lf_ 3 cr= g,<12. to l 04,1 3
Technician: Pl t.,.()~ ~·k ,
All counts times are one minute
Date By Backl?round Counts (I min. each) Source Counts (l min. each) ok?
#1 #2 #3 Avg. #1 #2 #3 Average YIN
1()/1·3 I'-') 1) t,t., I t t.;' t-.z. e, 1 ·.i. P'" I 2,. -z, q~ P>b l O I -i..L.\-l tr~ l -i. JOl~I 'I ,o ,·~. ,0 Vt,..t., \ '3 \ l'"l-1 '?,v I "?JI \O\vo to ll "'°'l \ 0"'2.-~q IO I t..,L y
( 0 / 4-/ /OJ 'l?,-Z./ \ "J-v \ Ci?, I '-t I 14-0 \Ul"3L, \0\49 10~0 101·,~ ...J
ID t; ~ '°' t,U I \ L\ ,..,_o i~O 12-\ lOY. II \ 00;-2. LOOO)Lt lOf~{.;, 'y
IC iS" I~ tJ'l,b l i 0 .. I 10\ I /1 I \c; , o, .;;-o l 0'2"'5""\ /00 2-2 i D/4 I v
1,0 ts--,,.,, j)~ l:l..5 (S-0 1·-s~ I "'1, \ O'\ ).."? \ D"J-l\ot. lu,._Ov) I 0--z~O 'Y
\QJ--'oJ'\ lO·~ \Cl !7\'Pi ' I'"> 'z.. s-~ )('
YIN: Y = average background and source cpm falls within the control limits.
N = average background and source cpm does not fall within the control limits.
The acceptable ranges were determined from prior background and source check data.
BALANCE OPERATION DAILY CHECK
Balance Model: Olt\C(V\~ ?0,-\--0-5...-z,.vYJ
Standa~d Weight (g): --=~c...:.......-0_0_. 0~~-----------
Date Pre-check (g) Post-check (g) O.K.±0.1 %? By
l0/1""3)1~ ·""2-O O. 0 200.0 Y~~ ~~
lO / 1 "l /'10J
.. PL/;..~' I I 0)9 .0 """2-00. 0 ...;e5 ' ·r
l .
ID j IC::. j \.9 '20 o.o ;;2.00. 0 '{.;<; DJ.. Gq?.<A-
l
AppendixB
Recount Data Analyses
B
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: N/A
AREA: COVER DEPLOYED: 10 9 19 RETRIEVED: 10 10 19 CHARCOAL BKG: 148
FIELD TECHNICIANS: CE, DLC, JD, TE COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM 1.D.: M01/D21, M02/D20 CAL. DUE: 10/07/20
RECOUNT CANISTER ANALYSIS:
PROJECT NO.: 19004.03
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
g.
g.
GRID sAMPtE RETRtv· ANALYsts· ·Mrn -=irtME" dfr · GRoss · ·c;Ross RAboN ± LLD -PREcisroN
LOCATION I. D. HR .M_IN HR MIN MO DA YR HR . MIN (MIN) COUNTS WT, IN pCi/m·; s . pCi/m" s pCi/m7 s % RPD
FlO FlO 8 18 8 24 10 13 19 14 20 3 1381 214.4 0.8 0.1 0.05
FlO FlO 8 18 8 24 10 14 19 14 25 4 1604 214.4 0.8 0.1 0.06 0.0%
F20 F20 8 39 8 30 10 13 19 14 35 1 4254 211.2 10.6 1.1 0.05
F20 F20 8 39 8 30 10 14 19 14 24 1 3679 211. 2 10.9 1.1 0.06 2.8%
F30 F30 8 18 8 24 10 13 19 15 11 5 1100 209.7 0.2 0.0 0.05
F30 F30 8 18 8 24 10 14 19 14 31 5 1094 209.7 0.2 0.0 0.06 0.0%
F40 F40 8 39 8 30 10 13 19 15 30 1 1190 210.8 2 .7 0.3 0.05
F40 F40 8 39 8 30 10 14 19 14 30 1 1022 210.8 2.7 0.3 0.06 0.0%
F50 F50 8 18 8 24 10 13 19 15 59 4 1091 214.2 0.3 0.0 0.05
F50 F50 8 18 8 24 10 14 19 14 37 5 1219 214.2 0.3 0.1 0.06 0.0%
F60 F60 8 39 8 30 10 13 19 16 25 1 1421 211. 5 3.3 0.3 0.05
F60 F60 8 39 8 30 10 14 19 14 35 1 1181 211. 5 3.2 0.3 0.06 3.1%
F7 0 F70 8 8 8 22 10 13 19 16 40 2 1225 213.3 1.2 0.1 0.05
F70 F70 8 8 8 22 10 14 19 14 42 2 1137 213.3 1.3 0.1 0.06 8.0%
F80 F80 8 48 8 36 10 13 19 17 5 2 1195 211. 6 1.2 0.1 0.05
F80 F80 8 48 8 36 10 14 19 14 42 2 1018 211. 6 1.1 0.1 0 .06 8.7%
F90 F90 8 44 8 35 10 13 19 17 33 5 1056 211.4 0.2 0.1 0.05
F90 F90 8 44 8 35 10 14 19 14 46 5 1155 211. 4 0.3 0.1 0.06 40.0%
FlOO FlOO 8 49 8 39 10 13 19 17 53 4 1144 2 13.1 0.4 0.1 0.05
FlOO FlOO 8 49 8 39 10 14 19 14 46 5 1194 213.1 0.3 0.1 0.06 28.6%
OVERALL AVERAGE PERCENT PRECISION FOR THE CELL 2 COVER REGION: 9.1%
Page 1 of 1
Appendix C
Radon Flux Sample Laboratory Data (including Blanks)
C
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: N/A
AREA: COVER DEPLOYED: 10 9 19 RETRIEVED: 10 10 19 CHARCOAL BKG: 148
FIELD TECHNICIANS: CE, DLC, JD, TE COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 10/07/20
PROJECT NO.: 19004.03
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV ANALYSIS' MID-T.IME CNT GROSS GROSS ' RADON . . ±. LLD
g.
g.
LOCATIO~ I. D. HR MIN HR MIN MO DA .YR HR MIN .(MIN) .. COUNTS WT IN pCi/m2 s _pCi/m"s pCi/m2 s COMMENTS:
FOl FOl 8 0 8 20 10 13 19 14 5 4 1003 212.0 0.3 0.0 0.05
F02 F02 8 2 8 20 10 13 19 14 5 3 1133 212.6 0.6 0.1 0.05
F03 F03 8 4 8 21 10 13 19 14 9 4 1001 212.2 0.3 0.0 0.05
F04 F04 8 6 8 21 10 13 19 14 9 4 1076 214.0 0.3 0.0 0.05
F05 F05 8 8 8 22 10 13 19 14 13 3 1414 214.4 0.8 0.1 0.05
F06 F06 8 10 8 22 10 13 19 14 13 3 llll 210.4 0.6 0.1 0.05
F07 F07 8 12 8 23 10 13 19 14 17 3 1004 213.1 0.5 0.1 0.05
F08 F08 8 14 8 23 10 13 19 14 16 1 1370 212.7 3.1 0.3 0.05
F09 F09 8 16 8 24 10 13 19 14 20 3 1125 213.2 0.6 0.1 0.05
FlO FlO 8 18 8 24 10 13 19 14 20 3 1381 214.4 0.8 0.1 0.05
Fll Fll 8 20 8 25 10 13 19 14 23 2 1267 212.4 1.2 0.1 0.05
F12 Fl2 8 22 8 25 10 13 19 14 24 3 1185 212.6 0.6 0.1 0.05
Fl3 Fl3 8 24 8 26 10 13 19 14 27 2 1577 211. 4 1. 6 0.2 0.05
Fl4 Fl4 8 26 8 26 10 13 19 14 28 3 1199 213. 0 0.6 0.1 0.05
F15 F15 8 28 8 27 10 13 19 14 30 2 1054 2ll. 7 1. 0 0.1 0.05
Fl6 F16 8 31 8 28 10 13 19 14 31 3 1243 212.5 0.7 0.1 0.05
F17 F17 8 33 8 29 10 13 19 14 34 1 1812 210.8 4.3 0.4 0.05
Fl8 Fl8 8 35 8 29 10 13 19 14 34 1 4413 210.3 11. 0 1.1 0.05
Fl9 Fl9 8 37 8 30 10 13 19 14 35 1 5364 212.2 13.5 1. 3 0.05
F20 F20 8 39 8 30 10 13 19 14 35 1 4254 211. 2 10.6 1.1 0.05
F21 F21 8 0 8 20 10 13 19 14 39 4 1008 211.1 0.3 0.0 0.05
F22 F22 8 2 8 20 10 13 19 14 38 3 1005 210.7 0.5 0.1 0.05
F23 F23 8 4 8 21 10 13 19 14 50 7 1144 208.0 0.0 0.0 0.05
F24 F24 8 6 8 21 10 13 19 14 50 7 1001 210.5 0.0 0.0 0.05
F25 F25 8 8 8 22 10 13 19 14 58 7 1035 208.5 0.0 o.o 0.05
F26 F26 8 10 8 22 10 13 19 14 57 5 1143 213.2 0.2 0.0 0.05
F27 F27 8 12 8 23 10 13 19 15 5 5 1084 210.7 0.2 0.0 0.05
F28 F28 8 14 8 23 10 13 19 15 5 5 1216 209.8 0.2 0.0 0.05
F29 F29 8 16 8 24 10 13 19 15 11 6 1132 208.2 0.1 0.0 0.05
F30 F30 8 18 8 24 10 13 19 15 11 5 1100 209.7 0.2 0.0 0.05
F31 F31 8 20 8 25 10 13 19 15 19 1 1023 210.1 2.3 0.2 0.05
F32 F32 8 22 8 25 10 13 19 15 19 2 lll6 213.4 1.1 0.1 0.05
Page 1 of 4
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: N/A
AREA: COVER DEPLOYED: 10 9 19 RETRIEVED: 10 10 19 CHARCOAL 8KG: 148
FIELD TECHNICIANS": CE, DLC, JD, TE COUNTED BY: DLC DAT A ENTRY BY: DLC
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 10/07/20
PROJECT NO.: 19004.03
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
. GRID SAMPLE DEPLOY RETRIV ANALYSIS MID-TIME CNT .. GROSS GROSS RADON ± . . LLD
g.
g.
LOCATION I. D . HR MIN HR MIN MO DA YR HR MIN (~IN} COUNTS WT IN pCi/m's pCi/m2 s pCi /m 2 s COMMENTS :
F33 F33 8 24 8 26 10 13 19 15 23 5 1134 210.8 0.2 0.0 O. O'S
F34 F34 8 26 8 26 10 13 19 15 22 3 1051 210.9 0.5 0.1 0.05
F35 F35 8 29 8 28 10 13 19 15 27 1 1161 211. 5 2.6 0.3 0.05
F36 F36 8 31 8 28 10 13 19 15 27 1 5582 208.0 14.0 1. 4 0.05
F37 F37 8 33 8 29 10 13 19 15 28 1 23733 208.7 61.2 6.1 0.05
F38 F38 8 35 8 29 10 13 19 15 28 1 5617 209.9 14.2 1. 4 0.05
F39 F39 8 37 8 30 10 13 19 15 31 3 1105 208.5 0.6 0.1 6.05
F40 F40 8 39 8 30 10 13 19 15 30 1 1190 210.8 2.7 0.3 0.05
F41 F41 8 0 8 20 10 13 19 15 36 5 1147 212.8 0.2 0.0 0.05
F42 F42 8 2 8 20 10 13 19 15 36 5 1029 212.9 0.1 0.0 0.05
F43 F43 8 4 8 21 10 13 19 15 42 6 1126 217.1 0.1 0.0 0.05
F44 F44 8 6 8 21 10 13 19 15 41 3 1104 217.1 0.6 0.1 0.05
F45 F45 8 8 8 22 10 13 19 15 48 5 1043 217.3 0.2 0.0 0.05
F46 F46 8 10 8 22 10 13 19 15 48 5 1155 214.2 0.2 0.0 0.05
F47 F47 8 12 8 23 10 13 19 15 54 5 1006 210.9 0.1 0.0 0.05
F48 F48 8 14 8 43 10 13 19 15 54 5 1199 213.7 0.2 0.0 0.05
F49 F49 8 16 8 24 10 13 19 15 59 4 1147 212.7 0.4 0.1 0.05
F50 F50 8 18 8 24 10 13 19 15 59 4 1091 214.2 0.3 0.1 0.05
F51 F51 8 20 8 25 10 13 19 16 5 4 1035 213. 9 0.3 0.1 0.05
F52 F52 8 22 8 25 10 13 19 16 5 4 1093 213.4 0.3 0.1 0.05
F53 FS3 8 24 8 26 10 13 19 16 11 6 1001 211. 8 0.0 0.0 0.05
F54 FS4 8 27 8 26 10 13 19 16 11 5 1069 212.8 0.2 0.0 0.05
F55 F55 8 29 8 28 10 13 19 16 17 5 1027 209.6 0.1 0.0 0.05
F56 F56 8 31 8 28 10 13 19 16 15 1 4710 209.6 11. 9 1. 2 0.05
F57 F57 8 33 8 29 10 13 19 16 21 1 1621 211.2 3.8 0.4 0.05
F58 F58 8 35 8 29 10 13 19 16 22 4 1096 209.3 0.3 0.1 0.05
F59 F59 8 37 8 30 10 13 19 16 25 1 1605 212.3 3.8 0.4 0.05
F60 F60 8 39 8 30 10 13 19 16 25 1 1421 211. 5 3.3 0.3 0.05
F61 F61 8 42 8 35 10 13 19 16 28 4 1111 210.8 0.3 0.1 0.05
F62 F62 8 44 8 35 10 13 19 16 28 3 1127 209.8 0.6 0.1 0.05
F63 F63 8 46 8 36 10 13 19 16 32 3 1001 209.6 0.5 0.1 0.05
F64 F64 8 48 8 36 10 13 19 16 32 2 1643 213.5 1. 8 0.2 0.05
Page 2 of 4
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: N/A
AREA: COVER DEPLOYED: 10 9 19 RETRIEVED: 10 10 19 CHARCOAL BKG: 148
FIELD TECHNICIANS: CE, DLC, JD, TE COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 10/07/20
PROJECT NO.: 19004.03
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV .ANALYSIS MID-TIME CNT GROSS GROSS RADON . ± LLD .
g.
g.
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) CO~TS WT IN pCi/rn's pCi/rn"s pCi/rn2 s .COMMENTS :
F65 F65 8 so 8 37 10 13 19 16 35 1 1564 208.6 3.7 0.4 0.05
F66 F66 8 52 8 37 10 13 19 16 35 1 2107 213.5 5.1 0.5 0.05
F67 F67 8 54 8 38 10 13 19 16 36 1 1717 212.2 4.1 0.4 0.05
F68 F68 8 4 8 56 10 13 19 16 37 2 1110 215.8 1. 0 0.1 0.05 Black Pipes
F69 F69 8 6 8 21 10 13 19 16 40 2 1184 211. 9 1.2 0.1 0.05
F70 F70 8 8 8 22 10 13 19 16 40 2 1225 213.3 1.2 -0.1 0.05
F71 F71 8 10 8 22 10 13 19 16 43 2 1202 218.3 1.2 0.1 0.05
F72 F72 8 12 8 23 10 13 19 16 44 4 1088 217.1 0.3 0.1 0.05
F73 F73 8 14 8 24 10 13 19 16 49 4 1059 218.4 0.3 0.1 0.05
F74 F74 8 16 8 25 10 13 19 16 49 3 1361 215.0 0.8 0.1 0.05
F75 F75 8 18 8 25 10 13 19 16 54 4 1124 218.3 0.3 0.1 0.05
F76 F76 8 20 8 26 10 13 19 16 54 4 1023 217.9 0.3 0.1 0.05
F77 F77 8 42 8 35 10 13 19 16 57 1 1706 210.2 4.1 0.4 0.05
F78 F78 8 44 8 35 10 13 19 17 0 6 1007 209.6 0.1 0.0 0.05
F79 F79 8 46 8 36 10 13 19 17 6 4 1077 210.4 0.3 0.1 0.05
F80 F80 8 48 8 36 10 13 19 17 5 2 1195 211. 6 1.2 0.1 0.05
F81 F81 8 50 8 37 10 13 19 17 12 5 1002 209.9 0.1 0.0 0.05
F82 F82 8 52 8 37 10 13 19 17 12 3 1089 212.3 0.6 0.1 0.05
F83 F83 8 54 8 38 10 13 19 17 16 2 1004 210.4 0.9 0.1 0.05
F84 F84 8 56 8 38 10 13 19 17 18 5 1005 210.5 0.1 0.0 0.05
F85 F85 8 23 8 27 10 13 19 17 24 5 1078 211.1 0.2 0.0 0.05
F86 F86 8 25 8 28 10 13 19 17 23 2 1244 213. 8 1.2 0.1 0.05
F87 F87 8 27 8 28 10 13 19 17 28 3 1003 214.6 0.5 0.1 0.05
F88 F88 8 29 8 29 10 13 19 17 28 3 1202 217.6 0.7 0.1 0.05
F89 F89 8 42 8 35 10 13 19 17 33 5 1271 209.9 0.3 o.o 0.05
F90 F90 8 44 8 35 10 13 19 17 33 5 1056 211. 4 0.2 0.0 0.05
F91 F91 8 46 8 36 10 13 19 17 37 3 1300 213.5 0.8 0.1 0.05
F92 F92 8 48 8 36 10 13 19 17 37 3 1285 211. 9 0.7 0.1 0.05
F93 F93 8 50 8 37 10 13 19 17 40 1 1485 214.0 3.5 0.4 0.05
F94 F94 8 52 8 37 10 13 19 17 42 4 1197 211.2 0.4 0.1 0.05
F95 F95 8 54 8 38 10 13 19 17 45 1 1334 212.7 3.2 0.3 0.05
F96 F96 8 56 8 38 10 13 19 17 46 2 1756 212.8 1. 9 0.2 0.05
Page 3 of 4
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: N/A
AREA: COVER DEPLOYED: 10 9 19 RETRIEVED: 10 10 19 CHARCOAL BKG: 148
FIELD TECHNICIANS: CE, DLC, JD, TE COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM 1.D.: M01/D21, M02/D20 CAL. DUE: 10/07/20
PROJECT NO.: 19004.03
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV ANALYSIS MID-TIME CNT GROSS GROSS RADON ± LLD
g.
g.
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m's pCi/m 2 s pCi/m2 s COMMENTS :
F97 F97 8 58 8 39 10 13 19 17 48 1 1119 209.7 2.6 0 .3 0.05
F9.8 F98 8 45 8 37 10 13 19 17 49 2 1029 212.5 1.0 0.1 0.05
F99 F99 8 47 8 3 8 10 13 19 17 52 3 1005 213.0 0.5 0.1 0.05
FlOO FlOO 8 49 8 39 10 13 19 1 7 53 4 1144 213.1 0.4 0.1 0.05
AVERAGE RADON FLUX RATE FOR THE CELL 2 COVER REGION: 2.3 pCi/m2 s
0.0 MIN
BLANK CANISTER ANALYSIS: 61.2 MAX
GRID SAMPLE RETRIV ANALYSIS MID-TIME CNT GROSS GROSS RADON ± LLD '
LOCATION I . D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi /m z s pCi/rn' s pCi /m 2 s COMMENTS :
F BLANK 1 F BLANK 1 7 45 8 20 10 13 19 10 55 10 1713 208.2 0.06 0.03 0.04 CONTROL
F BLANK 2 F BLANK 2 7 45 8 20 10 13 19 10 55 10 1687 209.2 0.05 0.03 0.04 CONTROL
F BLANK 3 F BLANK 3 7 45 8 20 10 13 19 11 8 10 1828 209.3 0.09 0.03 0.04 CONTROL
F BLANK 4 F BLANK 4 7 45 8 20 10 13 19 11 8 10 1633 209.1 0.04 0.03 0.04 CONTROL
F BLANK 5 F BLANK 5 7 45 8 20 10 13 19 11 21 10 1589 208.7 0.03 0.03 0.04 CONTROL
AVERAGE BLANK CANISTER ANALYSIS FOR THE CELL 2 COVER REGION: 0.05 pCi/m2 s
Page 4 of 4
AppendixD
Sample Locations Map (Figure 2)
D
-CELL 1-111 1 1-. ---=--" W!::JITE MESA MILL
BLANR!NG, UTAH
RADO~ FLUX
ll~ II .. I 0 0 0 0 0 0 0 0 0 0 0 0 0 0 FOi FD2 f03 .... f-05 . .. f07 FOB FD9 f10 f11 "' "' f14 t 1\ I I I CELL2 0 0 0 0 0 0 0 0 0 0 0 0 0 0 f21 f22 f2l f24 f2S FU f27 f28 F29 F30 F31 F32 F33 F34
0 0 0 0 0 0 0 0 0 0 0 0 " 0 0 0 0 0 -I I SECOND HALF 2019 , ... f44 F4S , .. F47 ... , .. FSO F51 m FS3 FS4 FSS FS6 F57 FS8 FS9 f60 10/09/19-10/10/19 ....CEU.2-
" 0 0 0 0 0 0 0 0 " 0 0 0 0 0 F75 f74 f73 f72 f71 '"' '" , .. F67 F66 F65 F64 F63 F62 F61 I I . \\ • PREPARED FOR 0 0 0 0 0 0 0 0 0 ENERGY FUELS RESOURCES F8S F84 F83 F82 f81 FBD F79 F7B F77
0 0 0 0 0 0 0 0 f96 F9S , .. f93 f92 '" f90 F89
0 II J I Willlll.
F01 0 ~ SAMPlELOCATIONON COVERED AREAS
filillRU
N
t
liiiiiiil ~~~
2CO 100 0 200 ... ,,,,ro
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