DRC-2018-001806 - 0901a068807bffa9

ENERGYFUELS
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.eneigyfuels.com
February 21, 2018 Div of Waste Management
and Radiation Control
VIA OVERNIGHT DELIVERY FEB 2 6 2018
Mr. Scott Anderson
Director wt-mfrooim?
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84114-4820
Mr. Anderson:
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, 2017
As required by Utah Administrative Code, R 313-24-4 (incorporating by reference 10 CFR 40.65
(subpartl)), and License Condition 11.3A of State of Utah Radioactive Materials License No.
UT 1900479, enclosed is the Semi-Annual Effluent Monitoring Report for the White Mesa Mill
for the period July 1 through December 31, 2017.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Mark Chalmers
David E. Turk
Scott A- Bakken
Logan Shumway
Paul Goranson
4134.
February 21, 2018
VIA OVERNIGHT DELIVERY
Mr. Scott Anderson
Director
Division of Waste Management and Radiation Control
Utah Department of Environmental Quality
195 North 1950 West
P.O. Box 144880
Salt Lake City, UT 84114-4820
Mr. Anderson:
Energy Fuels Resources (USA) Inc.
225 Union Blvd. Suite 600
Lakewood, CO, US, 80228
303 974 2140
www.cnergvfuels.c m
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, 2017
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, 2017.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
;• very
ENERGY FUELS RESOURCES ( SA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Mark Chalmers
David E. Turk
Scott A. Bakken
Logan Shumway
Paul Goranson
White Mesa Uranium Mill
Radioactive Materials License UT900479
Semi-Annual Effluent Monitoring Report
(July through December 2017)
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 21, 2018
TABLE OF CONTENTS
1.0 INTRODUCTION .................................................................................................. 1
1.1 Modifications 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 ........................................................................................... 5
2.4 Site Specific Sampling Data ................................................................................. 5
2.5 Radon-222 ............................................................................................................ 6
3.0 EXTERNAL RADIATION (DIRECT GAMMA) .................................................. 7
4.0 VEGETATION SAMPLES ..................................................................................... 7
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
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
INDEX OF TABS
A High Volume Air Monitoring Stations
B BHV Air Sampling Graphs and Data Tables
Tab 1 BHV-1 Air Sampling Graphs and Data Table
Tab 2 BHV-2 Air Sampling Graphs and Data Table
Tab 3 BHV-3 Air Sampling Graphs and Data Table
Tab 4 BHV-4 Air Sampling Graphs and Data Table
Tab 5 BHV-5 Air Sampling Graphs and Data Table
Tab 6 BHV-6 Air Sampling Graphs and Data Table
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 QNQC
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 QNQC
G Stack Sample Laboratory Results
H Surface Water Graphs and Field Data Sheets
I Soil Sample Graphs, Data Table, Laboratory Results and QNQC
J Radon Monitoring Graphs and Data
K Cell 2 Radon Flux Data
jj
WHITE MESA URANIUM MILL
SEMI-ANNUAL EFFLUENT REPORT, JULY THROUGH DECEMBER 2017
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; and1
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 particulate 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.
A review of the field data collection activities noted that the calibration orifice used for
calibration of the high volume air samplers was not sent offsite to be calibrated by an
independent third party as required by the Environmental Protection Manual, Section 1.1.
It should be noted that the License Part 11.2.E requires calibration at least every two
years and the site-specific requirements are more stringent than the License requires. A
review of the procedures that resulted in the missed calibration prompted a corrective
action for the field procedures used to track equipment calibrations. Field data collection
equipment and meter calibration due dates will now be tracked via spreadsheet by the
Mill Radiation Safety Officer ("RSO"). Previously, Field Personnel tracked calibration
due dates. In addition, a list of calibration due dates will be generated and sent to the QA
Manager in the EFRI Corporate Offices to verify that all calibrations are completed as
needed. Overall, the data are still usable for the intended purpose and there is no adverse
effect on the data or its usability because the pre-and post-calibration orifice calibration
slope and intercept showed minimal changes. The minimal changes indicate that the
orifice was accurate for calibration and did not adversely affect the data collected.
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.
4
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 noteworthy and expected that Pb-210 concentrations are elevated when compared to
the other parent radionuclide concentrations (i.e. U-nat, Th-230 and Ra-226). This
phenomenon is due to the well-established controlling effect experienced worldwide as a
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
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 l.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
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
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).
2.5 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
MILDOS 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
6
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.
3.0 EXTERNAL RADIATION (DIRECT GAMMA)
Gamma exposure rate estimates were measured for the reporting 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 report. 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-1, BHV-2, BHV-4, BHV-5, BHV-6, BHV-7, and BHV-8 are within regulatory
limits. 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.
4.0 VEGETATION SAMPLES
Vegetation samples are collected at three locations around the Mill property. The
sampling locations are: 1) northeast, 2) northwest and 3) southwest of the Mill facility.
The NRC Regulatory Guide 4.14 requires that three samples be collected during the
grazing season, without specifying exact months or times during the season. Two samples
were collected during the January through June reporting period and were reported in the
7
SAER submitted on August 29, 2017. The third sample was collected during the July
through December reporting period. As noted in Section 1.1, the vegetation sampling
program was expanded through the addition of Th-232 and U-Nat.
During the July through December reporting period, samples were collected on
November 2, 2017. The data from the sampling events are included in the 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
2017 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:
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 analytical results of stack sampling conducted in the reporting period, as well as for
the previous two quarters, are provided in Table 8 in the Tables Tab of this report. The
8
actual analytical results reported by the laboratory for the reporting period (third and
fourth quarters 2017) are provided in Attachment G to this report.
The south yellowcake dryer and yellowcake baghouse operated during the third and
fourth quarters of 2017. The grizzly did not operate during the third and fourth quarters
2017. 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 packaging stack did not operate during the reporting period and were
not sampled.
It is also important to note that 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
surface water was not sampled in 2017, because no water was present during this
reporting period. A sediment sample was collected in August 2017. The data from the
sediment sample is included with the soil data in Attachment I. Attempts to collect a
surface water sample from Westwater Canyon continued throughout the third and fourth
quarters of 2017 but were unsuccessful. Documentation of the attempted sample
collection is included in Tab H for the third and fourth quarters of 2017 and in the
previous Semi-Annual Effluent Report for the first and second quarters of 2017.
The Mill's Environmental Protection Manual requires that samples from Cottonwood
Creek be analyzed for TDS and total suspended solids ("TSS") quarterly, and the
License, Part 11.2 B requires that samples from Cottonwood Creek be analyzed for
dissolved and suspended radionuclides including Gross Alpha, U-nat, Ra-226, and Th-
230 semi-annually. Cottonwood Creek surface water was sampled in the third quarter of
2017. Cottonwood Creek surface water was not sampled in the fourth quarter of 2017,
because no water was present during this reporting period. Documentation of the
attempted sample collection is included in Tab H.
9
The field data sheets for the surface water sampling events, along with graphs showing
current and historic results are included as Attachment H. The results of this sampling
indicate that surface water concentrations remain low and within the range of a typical
surface water.
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, surface soils were collected in August 2017. 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 2017 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. The
approved SOP specifies a separate corrective action for duplicate RPDs outside of
acceptance limits. The revised procedure for duplicate results outside of acceptance
limits was implemented for the results outside of the acceptance limits. The corrective
actions that were taken in accordance with the SOP procedure are as follows: the QA
Manager contacted the Analytical Laboratory and requested a review of the raw data to
assure that there were no transcription errors and the data were accurately reported. The
laboratory noted that the data were accurate and reported correctly. Reanalysis was not
completed as the samples were disposed of by the laboratory. 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 July 2017 for the
July through December 2017 reporting period. The July 2017 measurement was 0.9
pCi/(m2-sec). The July 2017 measurement was below the 20.0 pCi/(m2-sec) standard.
The full data report for the July 2017 Cell 2 radon flux sampling is provided in
Attachment K.
The 2017 average radon flux is 0.7 pCi/(m2-sec) which is the arithmetic average of the
March 2017 measurement of 0.5 pCi/(m2-sec) and the July measurement of 0.9 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. on February 21,
2018.
ENERGY FUELS RESOURCES (USA) INC.
By:
Scott A. Balck.en
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
Stde Pb-?H~
I, ·~3 I ueitml
California 600 l.60E-14
Illinois 1500 4.lOE-14
Ohio 300 8.lOE-15
Massachusetts 700 l.90E-14
Table 2 -Air Monitoring Station Results U-Nat (Comparison to Limits) 3rd
and 4th Quarter 2017
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration PercentECL
(uCi/ml) (uCi/ml) Limit (ECL)
BHVl 6.00E-16 2.40E-15 9.00E-14 1.67E+OO
BHV2 2.00E-16 6.00E-16 9.00E-14 4.44E-Ol
BHV4 2.SOE-15 1.00E-14 9.00E-14 6.94E+OO
BHV5 2.70E-15 1.40E-14 9.00E-14 9.28E+OO
BHV6 3.SOE-15 1.40E-14 9.00E-14 9.72E+OO
BHV7 1.20E-15 4.60E-15 9.00E-14 3.22E+OO
BHV8 6.00E-16 2.90E-15 9.00E-14 1.94E+OO
Table 3 -Air Monitoring Station Results Th-230 (Comparison to Limits)
3rd and 4th Quarter 2017
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 6.00E-17 5.00E-17 2.00E-14 2.75E-01
BHV2 2.00E-17 3.00E-17 2.00E-14 l .25E-01
BHV4 3.00E-16 2.00E-16 2.00E-14 1.25E+OO
BHVS 2.00E-16 4.00E-16 2.00E-14 l.50E+OO
BHV6 2.00E-16 4.00E-16 2.00E-14 1.SOE+OO
BHV7 6.00E-17 2.00E-16 2.00E-14 6.SOE-01
BHV8 8.00E-17 5.00E-17 2.00E-14 3.25E-Ol
Table 4 -Air Monitoring Station Results Ra-226 (Comparison to Limits)
3rd and 4th Quarter 2017 Quarter 2017
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 1.00E-16 7.00E-17 9.00E-13 9.44E-03
BHV2 5.00E-17 5.00E-17 9.00E-13 5.56E-03
BHV4 2.00E-16 2.00E-16 9.00E-13 2.22E-02
BHV5 2.00E-16 3.00E-16 9.00E-13 2.78E-02
BHV6 1.00E-16 1.00E-17 9.00E-13 6.l IE-03
BHV7 1.00E-16 1.00E-16 9.00E-13 l.1 IE-02
BHV8 1.00E-16 5.00E-17 9.00E-13 8.33E-03
Table 5 -Air Monitoring Station Results Pb-210 (Comparison to Limits)
3rd and 4th Quarter 2017
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/rnl) I
BHVl 1.20E-14 l.80E-14 6.00E-13 2.50E+OO
BHV2 l.30E-14 2.00E-14 6.00E-13 2.75E+OO
BHV4 l.60E-14 2.20E-14 6.00E-13 3.17E+OO
BHVS l.60E-14 l.60E-14 6.00E-13 2.67E+OO
BHV6 l.90E-14 2.00E-14 6.00E-13 3.25E+OO
BHV7 l.90E-14 2.lOE-14 6.00E-13 3.33E+OO
BHV8 l.20E-14 l.70E-14 6.00E-13 2.42E+OO
Table 6 -Air Monitoring Station Results Th-232 (Comparison to Limits)
3rd and 4th Quarter 2017
Monitoring 3rd 4th Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 8.00E-18 l.OOE-17 4.00E-15 2.25E-01
BHV2 4.00E-18 9.00E-18 4.00E-15 l.63E-01
BHV4 4.00E-18 2.00E-17 4.00E-15 3.00E-01
BHVS 4.00E-18 l.OOE-17 4.00E-15 l.75E-01
BHV6 l.OOE-17 l.OOE-17 4.00E-15 2.SOE-01
BHV7 4.00E-18 l.OOE-17 4.00E-15 1.75E-01
BHV8 2.00E-18 7.00E-18 4.00E-15 1.13E-01
Table 7 -Environmental Optically Stimulated Luminescence Dosimeter
Measurements (Gamma)
3:Ffl tffil1 3i·n 1(1.}nat-C!Wr ~'tit Q:tm~ter ,CUD.lulaiifhie
I .Qaari&\F Q:tiarter tlefflll L'mi &es~tt Turess. Semian11iu.d
M'Dm'too-iitig Re oil aes1t11Ut B.:aek:p0mm [l~~~~lfflltdl E$11imalte
8t.1ti0;ni ~~Jtl/ (mrem) @ilill'ClJI) ~m,ein~ (numlrn)
BHVl 36.8 39.3 1.3 7.9 9.2
BHV2 36.9 34.3 1.4 2.9 4.3
BHV3 35.5 31.4 0 0 0
BHV4 33.4 31.8 0 0.4 0.4
BHV5 35.5 35.4 0 4 4
BHV6 32.7 34.2 0 2.8 2.8
BHV7 36.2 30.7 0.7 0 0.7
BHV8 33.3 33.9 0 2.5 2.5
Table 8 Stack Effluent Concentrations and Release Rates
~ ls{ Qfr.. 2Q_17 -U-Nat U-Nat. ln-LL.:5 1 n-2:Z~ ln-LjV lll-2::lU ln-LjL 1Il-L5L Pb-LIU Pb-LIU Ka-LLO Ka-LLO Ka-U~ Ka-LL~
uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
SYC Dryer
Scrubber 1 3.0SE-09 l.93E-03 O.OOE+OO O.OOE+OO 1.76E-13 l.l lE-07 l.35E-14 8.54E-09 2.57E-1 l 1.62E-05 l.35E-13 8.54E-08 l.35E-13 8.54E-08
SYC Dryer
Scrubber 2 3.31E-09 2.00E-03 5.64E-15 3.41E-09 l.69E-13 l.02E-07 O.OOE+OO O.OOE+OO l.98E-l 1 l.19E-05 8.47E-14 5.12E-08 l.41E-13 8.53E-08
YC Packaging
Baghouse 5.20E-11 5.65E-05 O.OOE+OO O.OOE+OO 9.27E-14 l.OIE-07 O.OOE+OO O.OOE+OO 7.42E-13 8.0SE-07 2.32E-13 2.52E-07 l.76E-12 l.91E-06
2.uil Qtr. 2017
U-Nat U-Nat. lh-LL~ lh-LL~ "lh-LjV 1n-·nu lh-LSL ·1n-nz l'b-:Ll u l'b-:LlU Ka-:L:LD Ka-LLO Ka-LL~ Ka-:L:L~
uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
SYC Dryer
Scrubber I 7.SOE-09 4.07E-03 5.04E-15 2.73E-09 l.21E-12 6.56E-07 3.36E-15 l.82E-09 l.88E-11 l.02E-05 5.04E-15 2.73E-09 l.68E-13 9.llE-08
SYC Dryer
Scrubber 2 5.45E-09 l.97E-03 O.OOE+OO O.OOE+OO 6.71E-13 2.43E-07 O.OOE+OO O.OOE+OO 1.24E-l l 4.SOE-06 4.91E-15 l.78E-09 l.64E-13 5.92E-08
YC Packaging
Baghouse 4.0SE-11 3.77E-05 5.l lE-15 4.75E-09 8.68E-13 8.07E-07 O.OOE+OO O.OOE+OO 2.58E-11 2.40E-05 2.04E-14 l.90E-08 5.llE-13 4.75E-07
3ril Qtr. 2017
U-Nat U-Nat. lll-LL~ Th-U~ Th-LjV Th-LjV Th-LjL Th-nL Pb-:LlU Pb-:LlU Ka-:L:LD Ka-L:LO Ka-LL.:5 Ka-LL~
uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
SYC Dryer
Scrubber 1 l.90E-09 l.60E-03 l.29E-14 l.09E-08 l.OSE-13 9.lOE-08 O.OOE+OO O.OOE+OO 4.31E-12 3.64E-06 2.02E-14 l.71E-08 l .35E-l 3 1.14E-07
SYC Dryer
Scrubber 2 1.28E-09 l.1 lE-03 l.12E-14 9.70E-09 l.62E-13 l.40E-07 7.36E-15 6.36E-09 5.49E-12 4.74E-06 7.llE-14 6.14E-08 l .25E-l 3 l.OSE-07
YC Packaging
Baghouse 6.75E-11 1.28E-04 I.33E-l 3 2.53E-07 8.71E-14 l.65E-07 O.OOE+OO O.OOE+OO 4.46E-12 8.46E-06 9.22E-14 l.75E-07 5.12E-13 9.72E-07
4th Qtr.20]7,
U-Nat U-Nat. l h-:L:L~ Th-Z:L~ rn-:L5U lh-L5U lh-DZ l h-L.)L l'b-:LlU l'b-:LlU Ka-:LZO Ka-LLO Ka-LLO Ka-a~
uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec uCi/cc uCi/sec
SYC Dryer
Scrubber I 8.02E-10 l.SOE-04 2.59E-15 5.SIE-10 2.59E-15 5.SlE-10 O.OOE+OO O.OOE+OO 4.15E-12 9.30E-07 2.59E-15 5.SlE-10 2.59E-13 5.SIE-08
SYC Dryer
Scrubber 2 l.OlE-09 2.67E-04 O.OOE+OO O.OOE+OO 2.56E-15 6.75E-IO l .60E-17 4.22E-12 4.64E-12 I.22E-06 2.88E-15 7.59E-10 l.60E-13 4.22E-08
YC Packaging
Baghouse 7.41E-IO 7.87E-04 8.60E-17 9.13E-11 4.30E-15 4.57E-09 O.OOE+OO O.OOE+OO 3.22E-12 3.42E-06 8.60E-15 9.13E-09 4.30E-13 4.57E-07
ATTACHMENT A
HIGH VOLUME AIR MONITORING STATIONS
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Canyon Rim
Drainage
Coordinate System: NAO
1983 StatePlane Utah
South FIPS 4303 Feet
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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
(
Energy Fuels Resources Inc. White Mesa Mill
High Volume Air Monitoring Stations Coordinates
Air Station Northing Easting Ground Elevation*
BHV-1 10171106.23 2222420.22 5678.37
BHV-2 10180701.63 2223565.12 5789.20
BHV-4 10159480.63 2216380.00 5544.79
BHV-5 10164004.22 2221859.34 5590.50
BHV-6 10160451.77 2221996.62 5578.61
BHV-7 10170920.58 2219311.48 5660.72
BHV-8 10167873.94 2222236.08 5634.74
Coordinate System: Modified Utah State Plane -NAD83 -South Zone -US
Survey Feet
* Using Fisher Survey Vertical Datum
ATTACHMENT B
BHV AIR SAMPLING GRAPHS AND DATA TABLES
TAB 1
BHV-1 AIR SAMPLING GRAPHS AND DATA TABLE
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-1TZ3Z
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= limit= ~imit=
ALARA Goal = . :Z.ZSE-14 uCi/ml -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 ZE-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 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 1.25E-12 7.82E-16 8,00E-14 2.00E-14 1.06E-15 2.00E-12 5.00E-13 2.57E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 1.56E-15 • 5.00E-12 l.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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 2.16E-15 5.00E-12 1.25E-12 2.93E-15 8.00E-14 2.00E-14 1.16E-15 2.00E-12 , 5.00E-13. 2.09E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A...QPlicable
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 r,.iot Analyzed Not Applicable Not Applicable
9/27/1982 4.45E-15 ?-OOE-12 1.25E-12 3.29E-15 8.00E-14 2.00E-14 3.23E-15 2.00E-12 5.00E-13 1.99E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 4.39E-15 5.00E-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 Agplicable
4/4/1983 "7.51E-16 5.00E-12 1.25E-12 2.13E-16 8.00E-14 2.00E-14 3.20E-16 2.00E-12 5.00E-13. 1.88E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable No!_APplicable
6/30/1983 2.68E-16 , 5.00E-12 1.25E-12 6.92E-16 8.00E-14 2.00E-14 7.92E-16 ;1.00E-12 5.00E-13 2.00E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/3/1983 5.00E-12 J..25E-12 8.00E-14 2.00E-14 O.OOE+OO .-2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable _
1/3/1984 2.87E-15 5.00E-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 Not Analyzed Not Applicable Not Applicable
4/2/1984 1.59E-15 ',5.00E-12 1.25E-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 1.00E-12 Not Analyzed Not Applicable Not A_pplicable
10/1/1984 6.42E-16 5.00E-12 1.25E-12 1.39E-16 8.00E-14 2.00E-14 1.94E-16 -2.00E-12 5.00E-13 l,85E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1985 5.06E-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 Applicable
4/1/1985 O.OOE+OO 5.00E-12 1.25E-12 l,23E-15 S.OOE-14 2.00E-14 '4.SSE-16 ;2.00E-12 5.00E-13 8.06E-15 4.00E-12 l.OOE-12 r,.iot Analyzed Not Applicable Not Applicable
7/1/1985 7.17E-16 5.00E-12 1.25E-12 8.00E-14 2.00E-14 1.05E-15 ~.OOE-12 ; 5.00E-1{ 2.15E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 6.13E-16 5.00E-12 1.25E-12 l.18E-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 5.00E-12 1,25E-12 4.74E-16 8.00E-14 2.00E-14 2.00E-12 = 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 3.98E-15 5.00E-12 l.25E-12 9.74E-16 8.00E-14 2.00E-14 1.50E-15 2.00E-12 5.00E-13 1.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 5.51E-17 5.00E-12 1.25E-12 3.52E-16 8.00E-14 2.00E-14 1.37E-15 2.00E-12 5.00E-13 1.23E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 1.99E-15 5.00E-12 l.25E-12 3.06E-16 8.00E-14 2.00E-14 i.25E-15 2.00E-12 5.00E-13 1.08E-14 4.00E-12 1.00E-12 Not Analyzed Not AJ>plicable Not Ap_plicable
12/15/1986 _1.67E-15 5.00E-12 1.25E-12 1.16E-16 8.00E-14 2.00E-14 5.98E-16 2.00E-12 5.00E-13 1.37E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable t,iot Applicable
3/16/1987 '2.33E-15 5.00E-12 1.25E-12 4.30E-16 8.00E-14 2.00E-14 1.92E-16 2.00E-12 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 5.00E-13 1.45E-14 4.00E-12 1.00E-12 Not Analyzed .Not Applicable Not Applicable
9/9/1987 2.27E-15 5.00E-12 l.25E-12 2.44E-15 8.00E-14 2.00E-14 8.51E-16 2.00E-12 5.00E-13 3.14E-14 4.00E-12 1.00E-12 Not Analyzed • Not A_p_plicable Not A_pplicable
11/2/1987 2.75E-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 l.OOE-12 Not Analyzed Not Applicable ,Not Applicable
2/16/1988 1.07E-15 "_5.00E-12 1.25E-12 1.47E-16 8.00E-14 2.00E-14 4.44E-16 2.00E-12 5.00E-13 4.0lE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 l.98E-15 5.00E-12 1.25E-12 l.25E-15 8.00E-14 2.00E-14 6.40E-16 2.00E-12 5.00E-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 1.25E-12 3.41E-15 8.00E-14 2.00E-14 5.08E-16 2.00E-12 5.00E-13 1.62E-14 4.00E-12 1.00E-12 Not Analy~ed _ Not Applicable Not Applicable
11/14/1988 3.94E-15 5.00E-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 1.00E-12 Not Analyzed · Not Applicable Not Applicable
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 Agplicable Not A_pplicable
5/15/1989 1.70E-15 5.00E-12 1.25E-12 6.32E-16 8.00E-14 2.00E-14 5.86E-16 2.00E-12 5.00E-13 6.16E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 2.31E-15 5.00E-12 !,25E-12 2.31E-16 8.00E-14 2.00E-14 1.77E-16 2.00E-12 5.00E-13 7.65E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/13/1989 4.72E-15 5.00E-12 1.25E-12 1. 71E-15 8.00E-14 2.00E-14 1.52E-15 2.00E-12 5.00E-13 l.89E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 3.44E-16 5.00E-12 1.25E-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 1.25E-12 1.47E-15 8.00E-14 2.00E-14 1.04E-15 2.00E-12 5.00E-13 l.79E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.64E-15 5.00E-12 1.25E-12 1.49E-15 8.00E-14 2.00E-14 o.34E-16 2.00E-12 5.00E-13-8.27E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 1.48E-15 5.00E-12 1.25E-12' 7.50E-16 8.00E-14 2.00E-14 5.80E-16 2.00E-12 I 5.00E-13 2.16E-14 4.00E-12 1.00E-12 Not Analyzed _ Not ApJillcable _Not ApQlicable
2/11/1991 1.90E-16 5.00E-12 1.25E-12 3.48E-17 8.00E-14 2.00E-14 7.91E-17 2.00E-12 I 5.00E-13, 3.79E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A_pplicable
5/13/1991 3.42E-16 5.00E-12 1.25E-12 1.34E-15 8.00E-14 2.00E-14 7.39E-16 2.00E-12 5.00E-13 1.46E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 2.77E-16 5.00E-12 1.25E-12 4.17E-17 8.00E-14 2.00E-14 _1.45E-16 2.00E-12 5.00E-13. 1.80E-14 4.00E-12 1.00E-12 Not Analyzed _ Not Applicable _Not Applicable
11/11/1991 6.65E-17 5.00E-12 1.25E-12 9.13E-17 8.00E-14 2.00E-14 2.77E-17 2.00E-12 5.00E-13 l.06E-14 4.00E-12 l.OOE-12 Not Analyzed Not A_pplicable Not Ap.Q!icable
2/10/1992 l.94E-16 5.00E-12 1.25E-12 4.28E-17 8.00E-14 2.00E-14 4.08E-17 2.00E-12 5.00E-13 3.51E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1992 2.54E-16 5.00E-12 1.25E-12 6.49E-16 8.00E-14 2.00E-14 6.86E-17 2.00E-12 5.00E-13 1.38E-14 /I.OOE-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 l.73E-16 5.00E-12 1.25E-12 1.55E-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 1.56E-16 5.00E-12 l.25E-12 3.19E-17 8.00E-14 2.00E-14 4.90E-18 2.00E-12 5.00E-13 l.86E-14 4.00E-12 l.OOE-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 Not Applicable
5/10/1993 1.00E-16 5.00E-12 1.25E-12 4.llE-17 8.00E-14 2.00E-14 6.43E-17 2.00E-12 5.00E-13 l.26E-14 4.00E-12 1.00E-12 Not Analyzed Not ~plicable Not Applicable
8/10/1993 2.30E-16 5.00E-12 l.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 l.OOE-12 Not Analyzed Not Agplicable Not J>,p_plicable
Date Effluent 9E-14 uCi/ml BHV-lU Effluent 2E-14 uCi/ml BHV-lT230 Effluent 9E-13 uCi/ml BHV-1R Effluent 6E-13 uCi/ml BHV-1PB Effluent 4e-15 uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration 'concentration
Limit= Limit= Limit= limit= limit=
ALARAGoal= 2.ZSE-14 uCi{ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= lE-15 uCl/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 1994MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
pre 1994 1.25E-U uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
!:one EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA -
11/8/1993 5.00E-12 l.25E-12 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 1.57E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A_pplicable
2/7/1994 1.82E-16 5.00E-12 'l.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 Ana]yzed Not Applicable Not Applicable
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 Not 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 2.00E-12 5.00E-13 2.00E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 9.18E-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 Analyzed 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 1.50E-13 Not Analyzed Not Applicable Not Applicable
S/9/1995 9.40E-17 9.00E-14 2.25E-14 5.36E-16 2.00E-14 5.00E-15 l.60E-15 9.00E-13 2.25E-13 3.84E-15 6.00E-13 1.50E-13 Not Analyzed 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 1.50E-13 Not Analyzed Not Applicable Not Al!Plicable
11/11/1995 ~.SOE-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 5.34E-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 S.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 1.50E-13 Not Analyzed Not Applicable Not Applicable
8/5/1996 5.99E-16 9.00E-14 2.25e-14· 1.55E-15 2.00E-14 5.00E-15 2.03E-16 9.00E-13 2.25E-13 5.94E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 3.38E-16 9.00E-14 2.25E-14 5.45E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.22E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 l.OOE-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 Analyzed 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 1.50E-13 Not Analyzed Not Applicable Not Applicable
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·l3 4.73E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable ,Not Applicable -
4/28/1998 4.75E-16 9.00E-14 2.25E-14 6.73E-16 2.00E-14 5.00E-15 5.69E-16 9.00E-13 2.25E-13 5.94E-15 6.00E-13 l.50E-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 1.43E-15 9.00E-13 2.25E-13 5.22E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 2.81E-16 9.00E-14 2.25E-14 2.89E-16 2.00E-14 5.00E-15 1.80E-16 '9.00E-13 2.25E-13 4.64E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/28/1998 8.08E-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
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
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.SOE-13 Not Analyzed Not Applicable Not 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.ZSE-13 7.29E-15 6.00E-13 l.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 6.57E-16 9.00E-13 2.25E-13 6.19E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 1.00E-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.SOE-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 S.62E-16 9.00E-13 2.25E-13 4.50E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable · Not Ap11licable
9/26/2000 2.SlE-16 9.00E-14 2.25E-14 l.78E-16 2.00E-14 5.00E-15 3.25E-16 9.00E-13 2.25E-13 8.55E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/26/2000 1.00E-16 9.00E-14 2.25E-14 1.42E-16 2.00E-14 5.00E-15 1.31E-16 9.00E-13 2.25E-13 7.77E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 3.lOE-16 9.00E-14 2.ZSE-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/29/2001 1.52E-16 9.00E-14 2.25E-14 l.44E-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.25E·l3 7.21E-15 6.00E-13 l.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 1.00E-16 9.00E-13 2.25E-13 8.09E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2001 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 1.39E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable i:,Jot Applicable
4/1/2002 2.05E-16 9.00E-14 2.25E-14 2.44E-16 2.00E-14 5.00E-15 2.29E-16 9.00E-13 2.25E-13 8.15E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 3.55E-16 9.00E-14 2.25E-14 4.85E-16 2.00E-14 5.00E-15 1.06E-16 9.00E-13 2.25E-13 7.65E-15 6.00E-13 1.50E·l3 Not Ana]yzed Not Applicable Not Applicable
9/30/2002 l.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 l.50E-13 Not Analyzed 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.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 l.ZOE-16 9.00E-14 2.ZSE-14 l.12E-16 2.00E-14 5.00E-15 l.OOE-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 l.50E-13 Not Analyzed Not Applicable 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 1.50E-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 1.00E-16 9.00E-13 2.25E-13 1.54E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 l.OOE-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 3.04E-15 6.00E-13 l.SOE-13 Not Analyzed Not ARPlicable Not A.11plicable
9/27/2004 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.ZSE-13 1.0SE-14 6.00E-13 l.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 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.59E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 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 7.42E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable 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 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 1.00E-16 9.00E-14 2.25E-14 2.56E-16 2.00E-14 S.OOE-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 l.04E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 3,73E-14 6.00E-13 1.50E-13 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-1TZ3Z
:concentration Concentration <;oncentration Concentration Concentration
limit= Limit= pmit= Limit= Limit=
ALARAGoal = 2.ZSE-14 uCi/ml AlARAGoal = SE-15 uCi/ml ALARAGoal = ,2.ZSE-13 uCi/ml AlARAGoal = 1.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-1Z uCi/ml Pre1994MPC !'lot Applicable
limit= limit= Limit= Limit= Limit= -
pre 1994 1.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
4/3/2006 l.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 l.50E-13 Not Analyzed Not Applicable Not Ap,plicable
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 Applicable
10/2/2006 l.OOE-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 1.30E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 1.00E-16 9.00E-14 2.25E-14 l.47E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.17E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 2.23E-16 9.00E-14 2.25E-14 l.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 l.34E-16 2.00E-14 5.00E-15 1.36E-16 9.00E-13 2.25E-13 1.78E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not A~licable
9/30/2007 1.15E-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 7.68E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 1.00E-16 9.00E-14 2.25E-14 l.93E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2008 1.14E-16 9.00E-14 12.25E-14 1.13E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 l.50E-13 Not Analyzed .Not Applicable Not Applicable
6/30/2008 7.09E-16 9.00E-14 2.25E-14 3.83E-16 2.00E-14 5.00E-15 2.27E-16 9.00E-13 2.25E-13, 6.52E-15 6.00E-13 1.50E-13 Not Analyzed 'Not Applicable Not A_pplicable
9/30/2008 7.69E-16 9.00E-14 , 2.25E-14 2.94E-16 2.00E-14 5.00E-15 1.90E-16 9.00E-13 2.25E-13 7.64E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2008 1.21E-15 9.00E-14 ·~.25E-14 4.76E-16 2.00E-14 S.OOE-15 3.34E-16 9.00E-13 2.25E-13 1.16E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable 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-13 4.44E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 5.97E-17 9.00E-14 l.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 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 9.55E-16 9.00E-14 2.25E-14 1.71E-16 2.00E-14 5.00E-15 9.87E-17 9.00E-13 2.25E-13 9.47E-15 6.00E-13 1.SOE-13 Not Anail,'Zed Not Applicable Not A_p_p_licable
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 1.SOE-13 Not Analyzed Not A11plicable Not A_pplicable
3/31/2010 l.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 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2010 'i.58E-15 9.00E-14 2.25E-14 4.71E-16 2.00E-14 5.00E-15 7.70E-16 . 9.00E-13 2.25E-13 4.07E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable 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 2.25E-13 6.80E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2010 1.27E-15 9.00E-14 2.25E-14 2.32E-16 2.00E-14 5.00E-15 2.30E-16 9.00E-13 2.25E-13 1.27E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 9.0lE-16 9.00E-14 2.25E-14 l.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 9.00E-13 2.25E-13 8.38E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 2.92E-16 9.00E-14 2.25E-14 1.17E-16 2.00E-14 5.00E-15 6.76E-17 9.00E-13 2.25E-13 1.14E-14 6.00E-13 l.SOE-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 5.00E-15 8.58E-17 9.00E-13 2.25E-13 1.73E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Ap_p_licable
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. 1.25E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 1.50E-13 Not Analyzed Not Applicable 'Not Applicable
10/1/2012 1.06E-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 1.13E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not A_pplicable
12/31/2012 6.86E-16 9.00E-14 2.25E-14 l.27E-16 2.00E-14 5.00E-15 1.38E-16 9.00E-13 2.25E-13 L54E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable !';Jot 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 1.82E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A_p_plicable
7/2/2013 1.46E-16 9.00E-14 2.25E-14 3.34E-16 2.00E-14 5.00E-15 ~.91E-16 9.00E-13 2.25E-13 5.78E-15 6.00E-13 1.50E-13 NotAnal'[Zed 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 1,50E-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 1.SOE-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 5.00E-15 ?,69E-16 l').OOE-13 2.25E-13 1.24E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2014 2.24E-15 9.00E-14 2.25E-14 5.14E-16 2.00E-14 5.00E-15 1.09E-15 9.00E-13 ·nse-13 1.23E-14 6.00E-13 1.50E-13 Not Analyzed Not A11plicable Not A_p_p_licable
9/30/2014 l.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 l.OOE-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 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1,50E-13 7.00E-18 4.00E-15 _)..OOE-15
3/30/2015 1.9DE-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 1.50E-13 4.00E-18 4.00E-15 1.00E-15
6/29/2015 6.00E-16 ~.OOE-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 2.2DE-16 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 2.00E-16 iJ.OOE-13 2.25E-13 1.20E-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 1.40E-14 6.00E-13 1.50E-13 2.00E-18 4.00E-15 1.00E-15
6/27/2016 l.lOE-15 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 9.00E-16 9.00E-13 2.25E-13 9,60E-15 6.00E-13 1,SOE-13 3.00E-18 4.00E-15 l.OOE-15
9/27/2016 1.lOE-15 9.00E-14 2.25E-14 8.70E-17 2.00E-14 5.00E-15 1.80E-16 9.00E-13 2.25E-13 1.20E-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 7.80E-17 2.00E-14 5.00E-15 1.30E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.50E-13 4.80E-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' 1.50E-14 6.00E-13 l.50E-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 1.lOE-14 6.00E-13 1.50E-13 8.00E-18 4.00E-15 LOOE-15
9/25/2017 6.00E-16 9.00E-14 2.25E-14 6.00E-17 2.00E-14 5.00E-15 1.00E-16 iJ.OOE-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 8.00E-18 4.00E-15 LOOE-15
12/26/2017 2.40E-15 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 7.00E-17 9.00E-13 2.25E-13 1.80E-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 J..,POE-15
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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-2TZ30 Effluent 9E-15 uCi/ml BHV-2R Effluent 6E-l3 uCi/ml BHV-2PB Effluent 4e-15 uCi/ml BHV-2T232
Concentration Concentration Concentration Concentration Concentration
Limit= limit= Limit= limit= Limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARAGoal = SE-13 uCi/ml AlARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.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=
Pre 1994 ALARA 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable ~
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone _EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 1.39E-15 5.00E-12 1.25E-12 3.69E-16 8.00E-14 2.00E-14 5.92E-16 2.00E-12 5.00E-13 1.67E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Ap_plicable
12/14/1981 4.62E-16 5.00E-12 1.25E-12 8.03E-16 8.00E-14 2.00E-14 3.62E-16 2.00E-12 5.00E-13 l.33E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 7.07E-16 5.00E-12 1.25E-12 1.lOE-15 8.00E-14 2.00E-14 7.27E-16 2.00E-12 5.00E-13 1.52E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 8.84E-16 5.00E-12 l.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 l.OOE-12 Not Analyzed Not Applicable Not Ap11licable
9/27/1982 1.23E-15 5.00E-12 1.25E-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 l.OOE-12 Not Analyzed Not Ap_plicable Not A_p1;1licable
1/3/1983 2.64E-15 5.00E-12 l.25E-12 2.55E-16 8.00E-14 2.00E-14 1.98E-16 2.00E-12 5.00E-13 2.85E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 2.14E-16 5.00E-12 1.25E-12 1.02E-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 S.OOE-13 1.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable~ 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 1.78E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
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 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 4.28E-16 5.00E-12 l.25E-12 1.75E-16 8.00E-14 2.00E-14 4.57E-17 2.00E-12 S.OOE-13 3.SSE-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 2.78E-15 5.00E-12 1.25E-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/1/1984 ?.69E-16 5.00E-12 1.25E-12 2.66E-17 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 5.00E-13 l.77E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1985 2.lSE-16 5.00E-12 l.25E-12 7.55E-16 8.00E-14 2.00E-14 2.87E-16 2.00E-12 5.00E-13 3.19E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 l.OOE-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 1.00E-12 Not Anal~zed Not Ap_plicable Not Applicable
7/1/1985 3.70E-17 S.OOE-12 l.25E-12 9.00E-16 8.00E-14 2.00E-14 4.90E-17 2.00E-12 5.00E-13 1.31E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not AQQlicable
9/30/1985 9.32E-17 S.OOE-12 1.25E-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 1.00E-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.lSE-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 S.OOE-12 1.25E-12 1.SOE-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 2.90E-15 4.00E-12 l ,OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 2.23E-16 5.00E-12 1.25E-12 l.32E-16 8.00E-14 2.00E-14 7.09E-17 2.00E-12 5.00E-13 2.53E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 6.41E-16 5.00E-12 1.25E-12 l.74E-16 8.00E-14 2.00E-14 3.67E-16 2.00E-12 S.OOE-13 1.04E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 3.56E-16 5.00E-12 :l.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.0SE-16 2.00E-12 S.OOE-13 7.BlE-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 5.31E-16 5.00E-12 l .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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/11/1987 4.06E-16 5.00E-12 '1.25E-12 6.63E-17 8.00E-14 2.00E-14 1.34E-16 ' 2.00E-12 5.00E-13 1.lOE-14 4.00E-12 l.OOE-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 5.00E-13 1.04E-14 4.00E-12 l.OOE-12 Not Analyzed Not Ap11licable Not Applicable
11/2/1987 3.73E-16 5.00E-12 l.25E-12 3.llE-16 8.00E-14 2.00E-14 1.83E-16 2.00E-12 S.OOE-13 1.17E-14 4.00E-12 l.OOE-12 Not Analyzed Not A11plicable Not AllJllicable
2/16/1988 '2.78E-15 5.00E-12 1.25E-12 2.31E-17 8.00E-14 2.00E-14 1.20E-16 2.00E-12 5.00E-13 3.SSE-14 4.00E-12 l.OOE-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.lSE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 8.06E-16 5.00E-12 1.25E-12 8.69E-16 8.00E-14 2.00E-14 1.80E-16 2.00E-12 5.00E-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 l.OOE-12 Not Analyzed Not Aplill_cable Not Ap_plicable
2/13/1989 5.BOE-16 5.00E-12 1.25E-12 2.85E-16 8.00E-14 2.00E-14 1.5SE-16 2.00E-12 5.00E-13 2.80E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 5.06£-16 5.00E-12 1.25£-12 2.28E-16 8.00E-14 2.00E-14 l.63E-16 2.00E-12 5.00E-13 6.0SE-15 4.00E-12 1.00E-12 Not Anal-aed Not Applicable Not Applicable
8/14/1989 4.71E-16 5.00E-12 1.25E-12 9.60£-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 5.00E-13 6.65E-15 4.00E-12 l.OOE-12 Not Analyzed Not Ap_plicabie Not Applicable
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 5.00E-13 l.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A.1111licable
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 1.98E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 9.32E-16 5.00E-12 1.25E-12_ 5.27E-16 8.00E-14 2.00E-14 3.97E-16 2.00E-12 5.00E-13 1.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.66E-16 5.00E-12 1.25E-12 S.49E-16 8.00E-14 2.00E-14 4.75E-17 2.00E-12 5.00E-13 1.27E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 6.0SE-16 5.00E-12 1.25E-12 2.64E-16 8.00E-14 2.00E-14 1.93E-16 2.00E-12 5.00E-13 2.25E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/11/1991 8.72E-17 5.00E-12 1.25E-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 l.OOE-12 Not Analyzed Not Applicable Not Ap_plicable
5/13/1991 1.16E-16 5.00E-12 1.25E-12 3.86E-16 8.00E-14 2.00E-14 2.BOE-16 2.00E-12 5.00E-13 l.SOE-14 4.00E-12 l.OOE-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 l.58E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable r,lot Applicable
11/11/1991 4.81E-17 5.00E-12 1.25E-12 3.82E-17 8.00E-14 2.00E-14 2.54E-17 2.00E-12 s.ooe-n l.4SE-14 4.00E-12 l.OOE-12 Not Anal¥zed Not Applicable • Not Applicable
2/10/1992 1.54E-16 5.00E-12 l.25E-12. 6.82E-17 8.00E-14 2.00E-14 1.40E-17 2.00E-12 5.00E-13 3.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not AQQlicable
5/11/1992 2.38E-16 S.OOE-12 1.25E-12 7.63E-17 8.00E-14 2.00E-14 3.07E-17 ~.OOE-12 5.00E-13 l.27E-14 4.00E-12 1.00E-12 ·Not Analyzed Not Applicable Not Applicable
8/10/1992 l.OlE-16 5.00E-12 1.25E-12 7.07E-17 8.00E-14 2.00E-14 2.BOE-17 2.00E-12 5.00E-13 1.41E-14 4.00E-12 1.00E-12 .f'lot Analyzed Not Applicable 'Not Applicable
11/9/1992 5.ZOE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.39E-16 5.00E-12 l.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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/10/1993 l.OOE-16 5.00E-12 1.25E-12 7.llE-17 8.00E-14 2.00E-14 3.19E-17 2.00E-12 5.00E-13 1.34E-14 4.00E-12 1.00E-12 Not Analyzed Not Apl)_licable Not A1111licable
8/10/1993 1.90E-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 1.80E-14 4.00E-12 l.OOE-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
Limit= Limit= Limit= Limit= Limit=
AlARAGoal= 2.25E-14 uCi/ml AlARAGoal = SE-13 uCi/ml ALARAGoal= 2.25E-13 uCi/ml AlARAGoal = 1.SE-13 uCi/ml ALARA Goal = . lE-15 uCi/ml
Pre 1994MPC 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
1
Pre 1994 M PC Not Applicable
Limit= 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=
Cone EFC EFCA Cone EFC EFCA Cone . EFC EFCA Cone EFC EFCA Cone EFC EFCA
11/8/1993 1.00E-16 5.00E-12 1.25E-12 l.OOE-16 8.00E-14 2.00E-14 1.00E-16 i.ooe-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. l.OOE-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 Applicable 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 1.37E-14 4.00E-12 l.OOE-12 Not Analy_zed 'Not Ap_plicable Not ApJ!licable
8/9/1994 9.29E-17 5.00E-12 l..25E-12 2.96E-16 8.00E-14 2.00E-14 3.04E-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 1.00E-12 Not Analyzed :. Not A_p_plicable Not Applicable
11/7/1994 !'1.21E-17 S.OOE-12 1.25E-12 2.35E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 l.OOE-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 5.00E-15 9.70E-17 9.00E-13 2.25E-13 7.42E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 !).40E-17 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 3.SOE-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 Applicable
11/11/1995 2.83E-15 9.00E-14 2.25E-14 4.09E-16 2.00E-14 5.00E-15 5.23E-16 9.00E-13 2.25E-13 6.77E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable 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 l ,50E-13 Not Analyzed Not Applicable Not Applicable
·s/6/1996 1.40E-16 9.00E-14 2.25E-14 1.lSE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE·13· 6.85E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A.l!l!licable
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 l.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 l.19E-14 6.00E-13 l.50E-13 Not A.[1alyzed Not Applicable Not Applicable
2/6/1997 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 5.84E-16 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 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 3.89E-15 6.00E-13 1.50E-13 Not Analyzed Not App_licable Not Ap11licable
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 ~.OOE-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/5/1998 2.55E-16 9.00E-14 2.25E-14. L07E-16 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 5.llE-15 6.00E-13 1.50E-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 S.OOE-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 S.OOE-15 3.39E-16 9.00E-13 2.25E-13 4.80E-15 6.00E-13 1.50E-13 Not Analyzed Not A_p111icable Not A_pJ!!j_cable
9/28/1998 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 4.26E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A1111licable
12/28/1998 2.54E-16 9.00E-14 2.25E-14 2.15E-16 2.00E-14 5.00E-15 1.38E-16 I 9.00E-13 2.25E-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 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.61E-15 6.00E-13 l.50E-13 Not Analyzed Not _;pplicable Not Applicable
7/3/1999 2.46E-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 1.50E-13 Not Analyzed Not ApQlicable Not Applicable
9/27/1999 2.81E-16 9.00E-14 2.25E-14 1.41E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 -2.25E-13 7.35E-15 6.00E-13 l.50E-13 ,Not Analyzed Not Applicable Not Applicable
12/28/1999 5.20E-16 9.00E-14 2.25E-14 2.60E-16 2.00E-14 5.00E-15 2.0lE-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 .1.50E-13 NotAnal\'Zed Not A11J11icable Not AQPlicable
3/27/2000 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 7.12E-15 6.00E-13 l.50E-13 Not Analtzed Not Applicable Not AQPlicable
6/26/2000 1.lOE-16 9.00E-14 2.25E-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 NotAnal'{Zed Not Applicable Not Applicable
9/26/2000 l.OOE-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 5.31E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable _ Not Applicable
12/26/2000 1.26E-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 9.45E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 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 6.95E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 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 6.56E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A_p_111icable
9/24/2001 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 6.16E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A11plicable
12/31/2001 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 2.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable • Not Applicable
4/1/2002 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 9.95E-15 6.00E-13 1.50E-13 NotAnal\'Zed Not A11plicable Not A_p_11licable
7/1/2002 l.25E-16 9.00E-14 2.25E-14 l.43E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.25E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 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 3.69E-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 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.91E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 :p5E-13 6.16E-15 6.00E-13 1.50E-13 Not Analyzed Not A_pplicable Not AQPlicable
6/30/2003 _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 5.27E-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 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.23E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 1.00E-16 9.00E-14 ;t.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.80E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap_11licable
3/29/2004 1.00E-16 9.00E-14 •?.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.04E-14 6.00E-13 1.50E-13 Not Ana.!Y_zed ·' Not Ap_plicable Not~plicable
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 1.50E-13 Not Analyzed Not Applicable 'Not Applicable
9/27/2004 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 1. 73E-14 6.00E-13 1.50E-13 Not AnaJyzed Not Applicable Not Ap11licable
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 1.30E-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 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13' 8.88E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 l.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 8.85E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 1.00E-16 9.00E-14 2.25E-14 1.99E-16 2.00E-14 5.00E-15 1.44E-16 9.00E-13 2.25E-13 3.81E-14 6.00E-13 1.50E-13 Not Analyzed 'Not A_pplicable Not A_~plicable
1/3/2006 1.29E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 4.08E-16 9.00E-13 2.25E-13 6.58E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date ~fftuent 9E-14 uCi/ml BHV-ZU Effluent ZE-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-ZlliZ
Concentration Concentration Concentration Concentration Concentration
Umit= Limit= Limit= Limit= Limit= -
ALARAGoal= 2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARAGoal= 2.ZSE-13 uCifml ALARA Goal= l.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Prel994MPC SE-UuCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Umit: limit= Limit= Limit= Umit=
pre 1994 ALARA 1.ZSE-U uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL= ,
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
4/3/2006 l.OZE-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 1.08E-14 6.00E-13 l .SOE-13 !'lot 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 l.lOE-14 6.00E-13 1.SOE-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 l.SOE-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 1.24E-16 9.00E-14 '2.25E-14 1.00E-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 1.38E-14 6.00E-13 l .SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 1.40E-16 9.00E-14 2.25E-14 1.00E-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 1.63E·l4 6.00E-13 l.SOE-13 Not Analyzed Not l\11Plicable Not Applicable
7/2/2007 l.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 l .36E·l4 6.00E-13 1.SOE-13 Not Analyzed Not AIJ.plicable Not Applicable
9/30/2007 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 8.24E-15 6.00E-13 l .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 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.18E-14 6.00E-13 l.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 1.50E-l3 Not Analyzed Not Applicable Not Applicable
6/30/2008 01.29E-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2008 2.73E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 8.30E-15 6.00E-13 L50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2008 S.71E·16 9.00E-14 2.25E-14 1.GlE-16 2.00E-14 5.00E-15 1.25E-16 9.00E-13 2.25E-13 2.04E-l4 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 3.96E·16 9.00E-14 2.25E-14 1.38E-16 2.00E-14 5.00E-15 1.07E-16 9.00E-13 2.25E-13 4.81E-15 6.00E-13 l.50E-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 5.llE-17 9.00E-13 2.25E-13 4.58E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 2.43E-16 9.00E-14 2.25E-14 S.28E-17 2.00E-14 5.00E-15 4.84E·17 9.00E-13 2.25E-13 l.19E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 5.72E-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-15 6.00E-13 l.50E-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 2.25E-13 8.24E-15 6.00E-13 l.50E-13 Not Analyzed Not {\pplicable Not Applicable
6/30/2010 3.SSE-16 9.00E-14 2.25E-l4 6.64E-17 2.00E-14 5.00E-15 9.90E-17 9.00E-13 2.25E-13 2.0lE-15 6.00E-13 l.50E-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·l7 9.00E-13 2.25E-13 1.08E-15 6.00E-13 1.50E-l3 Not Analyzed Not Applicable Not Applicable
12/31/2010 S.73E-16 9.00E-14 2.25E-14 7.24E-l7 2.00E-14 5.00E-15 6.76E-17 9.00E-13 2.25E-13 l.35E-l4 5.00E-13 l.50E-l3 Not Analyzed Not Applicable r,lot Applicable
4/4/2011 3.79E-16 9.00E-14 2.25E-14 4.0lE-17 2.00E-14 5,00E-15 9.llE-17 9.00E-13 2.25E-13 1.06E-l4 5.00E-13 l .50E-l3 Not Analyzed Not Applicable Not Applicable
7/4/2011 3.07E-l6 9.00E-14 2.25E-14 8.54E-l7 2.00E-14 5.00E-15 9.21E-17 .9.00E-13 2.25E-13 7.21E-15 6.00E-13 1.50E-l3 Not Analyzed Not Applicable Not Applicable
10/3/2011 1.17E-16 9.00E-14 2.25E-14 3.04E-17 2.00E-14 5.00E-15 2.81E-17 9.00E-13 2.25E-13 1.03E-l4 6.00E-13 l.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·l7 9.00E-13 2.25E-13 1.58E-l4 6.00E-13 1.50E-l3 Not Analyzed Not l\pplicable 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 !/.OOE-13 2.25E-13 1.58E-14 6.00E-13 1.50E-13 Not Analyzed Not AQplicable r,lot Applicable
7/2/2012 3.39E-16 9.00E-14 2.25E-14-1.56E-16 2.00E-14 5.00E-15 1.74E·16 9.00E-13 2.25E-13 8.60E-15 6.00E-13 l.50E-13 Not Analyzed Not A_pplicable Not Applicable
10/1/2012 3.13E-16 !!.OOE-14 2.25E-14 4.13E-17 2.00E-14 5.00E-15 ;3.04E-17 9.00E-13 2.25E-13 l.03E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 2.76E-16 g.OOE-14 2.25E-14 5.41E-17 2.00E-14 5.00E-15 7.0SE-17 9.00E-13 2.25E-13 1.48E-14 6.00E-13 l.50E-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 2.25E-13 1.42E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 4.06E-16 9.00E-14 2.25E-14 4.89E-17 2.00E-14 5.00E-15 8.06E-17 9.00E-13 2.25E-13 4.93E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable !'lot Applicable
9/30/2013 1.76E·16 9.00E-14 2.25E-14 2.52E-17 2.00E-14 5.00E-15 6.13E-17 9.00E-13 2.25E-13 4.90E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2013 6.20E-16 9.00E-14 2.25E-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2014 4.63E-16 9.00E-14 2.25E-14 4.97E-17 2.00E-14 5.00E-15 1.15E-16 9.00E-13 2.25E-13 1.49E-14 6_()()E-13 l.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 1.21E-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 1.50E-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-l4 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
3/30/2015 5.00E-16 9.00E-14 2.2SE·l4 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 fl.OOE-15 ,l.OOE-15
6/29/2015 1.00E-16 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.40E-14 6.00E-13 l.50E-13 8.00E-18 4.00E-15 1.00E-15
9/28/2015 5.00E-16 9.00E-14 2.25E-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 l.50E-l3 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·l3· 2.20E-14 6.00E-13 l.50E-13 3.00E-18 4.00E-15 l.OOE-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 1.50E-14 6.00E-13 l.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 2.25E-13 l.30E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-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 2.25E-13 1.00E-14 6.00E-13 l.50E-13 .5.20E-17 4.00E-15 1.00E-15
12/27/2016 4.lOE-16 9.00E-14 2.25E-14 l.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 2.25E-14 4.00E-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 1.50E-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 l.OOE-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-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 l.30E-14 6.00E-13 l.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 5.00E-13 1.50E-13 ~.OOE-18 4.00E-15 l.OOE-15
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Lo-das
go-das
go-das
vo-das
80-das
io-das
~o-das
oo-das
55-das
95-das
L6-das
95-das
95-das
175-das
86-das
i5-das
~5-das
05-das
59-das
99-das
Ls-das
99-das
99-das
179-das
8s-das
is-das
~9-das
Sep-14
Oct-14
Nov-14
Dec-14
Jan-15
Feb-15
Mar-15
Apr-15
May-15
Jun-15
Jul-15
Aug-15
Sep-15
Oct-15
Nov-15
Dec-15
Jan-16
Feb-16
Mar-16
Apr-16
May-16
Jun-16
Jul-16
Aug-16
Sep-16
Oct-16
Nov-16
Dec-16
Jan-17
Feb-17
Mar-17
Apr-17
May-17
Jun-17
Jul-17
Aug-17
Sep-17
Oct-17
Nov-1 7
Dec-17
_.
0 0 m I _.
CXl
_.
0 0 m I _.
-...J
J
4
\
V
_. _. _.
0 0 0 0 0 0 m m m I I I _. _. _.
m en .i:,.
~
~ ~•
_. _. _. .{Log Scale).
0 0 0 o o o 0 0 0 0 0 0 m m m m m m I I I I I I _. _. _. _. 0 0 w I\) _. 0 co CX)
~ ~ ~ ~ ~ ~
_. _. _. _. _. _.
0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m I I I I 6 I 0 0 0 0 0 -...J m en .i:,. w I\)
:
'
~ ~
_. _.
0 0
0 0 m m
I + 0 0 _. 0
'
'
l> m r-:::i: l> i: JJ (I) l> :, -G) (")
0 O Ill :, ii"2 ..... :, . -0 ., m !!l, I -• ..... 0 (11 :,
C: l o -· -· 3 3 ::.
-11
.I>, m I .....
(11
C: C')
~
m J: t
-4 ::::r
0 ~-c
3 I I\) w
I\)
0 0
::::s (')
(I)
::::s -..,
A> = 0
::::s u, -C
0 ~ -
TAB3
BHV-3 AIR SAMPLING GRAPHS AND DATA TABLE
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= 2.ZSE-14 uCi/ml ALARA Goal= SE-15 uCi/ml AlARAGoal= 2.ZSE-13 uCi/ml ALARAGoal = .l.SE-13 uCi/ml
Pre 1994 MPC ·SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-12 uCl/ml Pre 1994 MPC 4E-12 uCi/ml
Limit= Limit= Limit= Limit=
,Pre 1994 ALARA 1.ZSE-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 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 1.54E-14 4.00E-12 1.00E-12
12/14/1981 1.59E-15 5.00E-12 1.2SE-12 5.03E-16 8.00E-14 2.00E-14 1.30E-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 1.2SE-12 5.25E-16 8.00E-14 2.00E-14 4.08E-16 2.00E-12 5.00E-13 l.96E-14 4.00E-12 1.00E-12
6/30/1982 3.83E-16 5.00E-12 1.25E-12 2.16E-16 8.00E-14 2.00E-14 1.41E-15 2.00E-12 S.OOE-13 2.40E-14 4.00E-12 1.00E-12
9/27/1982 S.95E-16 S.OOE-12 1.25E-12 1.44E-15 8.00E-14 2.00E-14 S.36E-16 2.00E-12 5.00E-13 1.43E-14 4.00E-12 1.00E-12
1/3/1983 'l.OSE-16 5.00E-12 1.25E-12 1.23E-16 8.00E-14 2.00E-14 1.lOE-16 2.00E-12 5.00E-13 3.0lE-14 4.00E-12 1.00E-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 l.OOE-12
6/30/1983 3.06E-16 S.OOE-12 1.2SE-12 9.59E-17 8.00E-14 2.00E-14 2.0SE-16 2.00E-12 S.OOE-13 l.70E-14 4.00E-12 l.OOE-12
10/3/1983 1.91E-16 5.00E-12 l.25E-12 3.0SE-16 8.00E-14 2.00E-14 2.79E-16 2.00E-12 5.00E-13 1.76E-14 4,00E-12 'l.OOE-12
1/3/1984 3.0lE-16 5.00E-12 1.25E-12 9.SlE-17 8.00E-14 2.00E-14 1.00E-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 l .25E-12 7.52E-16 8.00E-14 2.00E-14 S.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 , 1.2SE-12 6.18E-16 8.00E-14 2.00E-14 l.40E-16 2.00E-12 5.00E-13 l.32E-14 4.00E-12 l .OOE-12
10/1/1984 1.74E-16 5.00E-12 1.25E-12 7.lOE-17 8.00E-14 2.00E-14 1.00E-16 2.00E-12 S.OOE-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.SOE-17 2.00E-12 S.OOE-13 2.73E-14 4.00E-12 1.00E-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 5.00E-13 l.12E-14 4.00E-12 l .OOE-12
7/1/1985 1.04E-16 5.00E-12 l.25E·12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.64E-14 4.00E-12 1.00E-12
9/30/1985 1.00E-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 1.00E-12
1/2/1986 1.03E-15 5.00E-12 1.25E-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 l .25E-12 1.93E-17 8.00E-14 2.00E-14 1.54E-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 l.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 1.00E-12
10/27/1986 6.45E-16 5.00E-12 l.25E-12 9.89E-17 8.00E-14 2.00E-14 4.16E-15 2.00E-12 5.00E-13 1.64E-14 4.00E-12 1.00E-12
12/15/1986 1.31E-16 5.00E-12 1.25E-12 0.00E+OO 8.00E-14 2.00E-14 4.16E-17 2.00E-12 5.00E-13 4.60E-15 4.00E-12 l.OOE-12
3/16/1987 2.0lE-16 5.00E-12 l.25E-12 l.20E-16 8.00E-14 2.00E-14 5.73E-17 2.00E-12 5.00E-13 1.60E-14 4.00E-12 l .OOE-12
5/11/1987 2.16E-16 5.00E-12 l.25E-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 LOOE-12
9/9/1987 2.41E-16 5.00E-12 , 1.25E-12 2.18E-16 8.00E-14 2.00E-14 3.52E-17 2.00E-12 5.00E-13 1.46E-14 4.00E-12 1.00E-12
11/2/1987 2.44E-16 5.00E-12 l.25E-12 2.32E-16 8.00E-14 2.00E-14 2.37E-17 2.00E-12 5.00E-13 2.48E-14 4.00E-12 1.00E-12
2/16/1988 8.08E-16 ,5.00E-12 1.25E-12 2.55E-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 l.14E-16 5.00E-12 1.25E-12 4.14E-17 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 5.00E-13 l.20E-14 4.00E-12 1.00E-12
8/15/1988 2.08E-16 5.00E-12 1.25E-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 1.25E-12 2.93E-16 8.00E-14 2.00E-14 1.09E-16 2.00E-12 5.00E-13 2.48E-14 4.00E-12 1.00E-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 S.OOE-13 3.34E-14 4.00E-12 l .OOE-12
5/15/1989 1.05E-16 5.00E-12 1.25E-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 l.31E-16 5.00E-12 :1.25E-12 5.85E-17 8.00E-14 2.00E-14 3.97E-17 2.00E-12 5.00E-13 6.75E-15 4.00E-12 1.00E-12
11/13/1989 1.67E-16 5.00E-12 1.2SE-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 1.00E-12
2/12/1990 4.43E-16 S.OOE-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 1.00E-12
5/14/1990 3.84E-16 S.OOE-12 1.25E-12 2.54E-16 8.00E-14 2.00E-14 1.02E-16 2.00E-12 5.00E-13 1.68E-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 l.21E-17 2.00E-12 5.00E-13 7.86E-15 4.00E-12 l.OOE-12
11/12/1990 1.84E-16 5.00E-12 1.25E-12 1.34E-16 8.00E-14 2.00E-14 8.53E-17 2.00E-12 S.OOE-13 2.0lE-14 4.00E-12 1.00E-12
2/11/1991 4.66E-17 5.00E-12 l.25E-12 8.4SE-16 8.00E-14 2.00E-14 1.94E-17 2.00E-12 5.00E-13 3.69E-14 4.00E-12 l.OOE-12
5/13/1991 5.0SE-17 5.00E-12 1.25E-12 7.40E-17 8.00E-14 2.00E-14 7.00E-18 2.00E-12 5.00E-13 LSOE-14 4.00E-12 l .OOE-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 l .OOE-12
11/11/1991 ,l.41E-17 5.00E-12 1.25E-12 2.19E-18 8.00E-14 2.00E-14 2.75E-17 2.00E-12 5.00E-13 l.lBE-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 5.00E-13 1.28E-14 4.00E-12 l.OOE-12
8/10/1992 2.00E-18 S.OOE-12 l.25E-12 4.19E-17 8.00E-14 2.00E-14 2.00E-18 2.00E-12 S.OOE-13 l.59E-14 4.00E-12 1.00E-12
11/9/1992 4.00E-17 5.00E-12 l .25E-12 2.68E-17 8.00E-14 2.00E-14 l.07E-17 2.00E-12 5.00E-13 1.81E-14 4.00E-12 1.00E-12
2/9/1993 7.94E-17 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 1.09E-16 2.00E-12 5.00E-13 2.69E-14 4.00E-12 1.00E-12
5/10/1993 1.60E-17 S.OOE-12 l.25E-12 5.07E-17 8.00E-14 2.00E-14 7.64E-17 2.00E-12 5.00E-13 1.26E-14 4.00E-12 1.00E-12
8/10/1993 6.00E-17 S.OOE-12 1.2SE-12 6.00E-18 8.00E-14 2.00E-14 l.OOE-16 2.00E-12 5.00E-13 l.SOE-14 4.00E-12 l.OOE-12
Date !effluent 9E-14 uCi/ml BHV-3U Effluent 2E-14 uCi/ml BHV-3T230 Effluent 9£-13 uCi/ml BHV-3R Effluent 6£-13 uCi/ml BHV-3PB
Concentration Concentration Concentration Concentration
Umit= Limit= Umit= Limit=
ALARAGoal= 2.25£-14 uCi/ml ALARAGoal = SE-15 uCi/ml ALARAGoal= 2.25£-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml
Pre1994MPC 5E-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
Umit= Limit= Umit= Limit=
Pre 1994 ALARA 1.25£-12 uCi/ml Pre 1994 ALARA 5£-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
11/8/1993 l.OOE-16 5.00E-12 l.25E-12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 S.OOE-13 2.lOE-14 4.00E-12 l.OOE-12
2/7/1994 1.61E-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 l.OOE-12
5/9/1994 2.77E-16 5.00E-12 1.25E-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 l.OOE-16 8.00E-14 2.00E-14 1.14E-16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-12
11/7/1994 9.05E-17 5.00E-12 'l.25E-12 l.OOE-16 8.00E·l4 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 2.2SE-14 9.60E-17 2.00E-14 5.00E-15 9.60E-17 9.00E-13 2.25E-13 9.05E-15 6.00E-13 1.50E-13
5/9/1995 9.40E-17 9.00E-14 2.25E-14 9.80E-17 2.00E-14 5.00E-15 8.60E-17 9.00E-13 2.25E·l3 2.88E-15 6.00E-13 1.50E-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 2.2SE-13 l.96E-15 6.00E-13 1.50E-13
11/11/1995 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
2/5/1996 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 1.50E-13
5/6/1996 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 l.50E-13
8/5/1996 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5,00E-15 3.99E-16 9.00E-13 2.25E-13 l,31E-14 6.00E-13 l.50E-13
11/6/1996 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 1.50E-13
2/6/1997 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
5/5/1997 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 l.53E-14 6.00E-13 l.50E-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 1.31E-14 6.00E-13 l.50E-13
1/5/1998 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 l.50E-13
4/28/1998 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.50E-13
7/31/1998 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 l.SOE-13
9/28/1998 3.00E-16 9.00E-14 2.2SE-14 3.43E-16 2.00E-14 S.OOE-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 l.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 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E·13 1.SOE-13
7/3/1999 l .31E-16 9.00E-14 2.25E-14 l ,39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.2SE-13 1.53E-14 6.00E-13 1.50E-13
9/27/1999 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 1.50E-13
12/28/1999 3.16E-16 9.00E-14 2.25E·14 1.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 l.50E-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 l.50E-13
6/26/2000 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 l.50E-13
9/26/2000 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
12/26/2000 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
3/26/2001 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/2/2001 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
9/24/2001 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 l.SOE-13
12/31/2001 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·l3 l.91E-14 6.00E-13 l.50E-13
4/1/2002 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
7/1/2002 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 l.50E-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 l.31E-14 6.00E-13 1.SOE-13
12/30/2002 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 '2.25E-13 1.91E-14 6.00E-13 l.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 2.25E-13 .2.69E-14 6.00E-13 1.SOE-13
6/30/2003 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.SOE-13
9/29/2003 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 l.31E-14 6.00E-13 1.50E-13
12/29/2003 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 1.50E-13
3/29/2004 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
6/27/2004 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 l.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 jl.()()E-13 2.25E-13 l.31E-14 6.00E-13 l.SOE-13
12/27/2004 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 l.91E-14 6.00E-13 l .SOE-13
3/28/2005 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-13
6/29/2005 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.SOE-13
9/26/2005 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E·16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
1/3/2006 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.50E-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= 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.25E-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml
Pre 1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC 2E-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml
limit= limit= limit= ~imit=
Pre 1994 ALARA 1.ZSE-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 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 '1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
7/3/2006 1.31E-16 9.00E-14 :p5E-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 1.50E-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 1.31E-14 6.00E-13 1.50E·13
1/1/2006 3.16E-16 9.00E-14 2.25E-14· 1.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
4/2/2007 3.41E-16 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 l.50E-13
7/2/2007 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/30/2007 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
12/31/2007 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
3/31/2008 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 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.50E-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 1.31E-14 6.00E-13 l.50E-13
12/31/2008 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.50E-13
3/15/2009 o.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
6/15/2009 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 l.50E-13
9/15/2009 3.00E-16 ~.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 l.50E-13
12/15/2009 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 ,, 2.25E-13 1.91E-14 6.00E-13 l.50E-13
3/31/2010 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
6/30/2010 1.31E-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.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 1.50E-13
12/31/2010 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13. l.91E-14 6.00E-13 1.50E-13
4/4/2011 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 S.OOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/4/2011 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 l.50E-13
10/3/2011 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.50E-13
1/3/2012 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13_ 1.91E-14 6.00E-13 1.50E-13
4/3/2012 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
7/2/2012 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
10/1/2012 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 9.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 l.50E-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 1.50E-13
3/25/2013 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13. 2.69E-14 6.00E-13 1.50E-13
7/2/2013 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/30/2013 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 1.31E-14 6.00E-13 1.50E-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 1.91E-14 6.00E-13 l.50E-13
3/31/2014 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 l.50E-13
6/30/2014 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 -2.25E·13· 1.53E-14 6.00E-13 l.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 1.50E-13
12/29/2014 9.16E-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.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 7.25E-13 2.69E-14 6.00E-13 l.50E-13
6/29/2015 ,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 l .SOE-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 l.31E-14 6.00E-13 1.SOE-13
.12/28/2015 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 l.SOE-13
3/28/2016 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
6/27/2016 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.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 1.31E-14 6.00E-13 l.SOE-13
12/27/2016 3.16E-16 "9.00E-14 2.25E-14 l.31E-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.25E-13 ;l.91E-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.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 l.SOE-13
6/26/2017 i..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 1.53E-14 6.00E-13 l.50E-13
9/25/2017 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
12/26/2017 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 l.50E-13
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£s-das
lB·das
~s-das
TAB4
BHV-4 AIR SAMPLING GRAPHS AND DATA TABLE
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
Umit= limit= limit= limit= limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARAGoal = 5E-15 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARA Goal= 1.5E-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre 1994 MPC 5E-UuCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC ZE-UuCi{ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC Not Applicable
Umit= limit= limit= limit= Umit=
Pre 1994 1.ZSE-U 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 EFCA
9/28/1981 S.20E-15 5.00E-12 1.25E-12 2.93E-15 8.00E-14 2.00E-14 2.74E·l5 2.00E-12 5.00E-13 l.84E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 4.53E·l5 . 5.00E-12 l.2SE·12 l.78E-15 8.00E-14 2.00E-14 2.29E·15 2.00E-12 ,5.00E-13 2.54E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable f'lot Applicable
3/29/1982 l.06E-15 5.00E-12 1.25E-12 1.42E-14 8.00E-14 2.00E-14 1.07E·l5 2.00E-12 S.OOE-13 2.31E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 6.03E·l5 5.00E-12 l.25E-12 l .57E·l4 8.00E-14 2.00E-14 2.62E·l5 2.00E-12 5.00E-13 2.25E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable f'lot Applicable
9/27/1982 1.26E·14 5.00E-12 1.25E-12 7.58E-16 8.00E-14 2.00E-14 S.35E-15 2.00E-12 5.00E-13 2.68E·l4 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 4.33E·15 5.00E-12 l.25E·12 6.52E-16 8.00E-14 2.00E-14 6.04E-16 2.00E-12 5.00E-13 2.57E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 1.25E·15 5.00E-12 1.25E·12 7.17E-16 8.00E-14 2.00E-14 6.76E-16 2.00E-12 5.00E-13 2.00E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 3.73E·16 5.00E-12 1.25E-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 Not Analyzed Not Applicable Not Applicable
10/3/1983 2.54E-16 5.00E-12 1.25E·12 1.51E·l6 8.00E-14 2.00E-14 2.65E-16 2.00E-12 5.00E-13 2.SOE-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1984 2.76E-15 S.OOE-12 1.2SE·12 l.GOE-16 jl.OOE-14 2.00E-14 l.05E-16 2.00E-12 5.00E-13 1.59E-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 4.27E·l6 : S.OOE-12 l.25E-12 2.33E-16 8.00E-14 2.00E-14 6.28E·16 2.00E-12 5.00E-13 3.67E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 2.57E-15 5.00E-12 1.25E-12 l ,36E-16 8.00E-14 2.00E-14 l.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.lBE-16 5.00E-12 1.25E-12 3.54E·16 8.00E-14 2.00E-14 l.lOE-17 2.00E-12 5.00E-13 9.83E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1985 S.30E·17 S.OOE-12 1.25E·12 3.SSE-17 8.00E-14 2.00E-14 7.00E-18 2.00E-12 5.00E-13 2.57E·l4 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 l.OOE-16 5.00E-12 1.2SE·l2 6.00E-16 8.00E-14 2.00E-14 4.3SE·l7 2.00E-12 5.00E-13 5.02E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
7/1/1985 9.36E-16 5.00E-12 l.25E-12 2.33E-16 8.00E-14 2.00E-14 2.36E-16 2.00E-12 S.OOE-13 7.48E·15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 1.46E-15 5.00E-12 1.25E-12 7.69E-16 8.00E-14 2.00E-14 5.38E·16 2.00E-12 5.00E-13 7.86E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 8.40E-15 S.OOE-12 l.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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 S.79E-15 5.00E-12 1.25E-12 5.80E·16 8.00E-14 2.00E-14 1.34E·15 2.00E-12 5.00E-13 l.33E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 5.19E-15 5.00E-12 i.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 l.25E·l2 4.67E-16 8.00E-14 2.00E-14 2.37E-15 2.00E-12 5.00E-13 1.13E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 2.7SE·l5 5.00E-12 l.25E-12 S.90E-16 8.00E-14 2.00E-14 9.39E·16 2.00E-12 S.OOE-13 1.20E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 4.64E·l5 S.OOE-12 l.2SE·12 1.18E-15 8.00E-14 2.00E-14 4.97E-16 2.00E-12 S.OOE-13 5.89E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
5/11/1987 4.3SE·15 5.00E-12 1.25E-12 l.23E-14 8.00E-14 2.00E-14 l.13E·15 2.00E-12 S.OOE-13 2.21E·l4 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/9/1987 6.39E-15 5.00E-12 1.25E-12 1.SOE-14 8.00E-14 2.00E-14 2.26E·15 2.00E-12 5.00E-13 l.57E-14 4.00E-12 l.OOE-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.SSE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 1.91E-15 5.00E-12 1.25E-12 l.3SE·14 8.00E-14 2.00E-14 4.42E·l6 2.00E-12 5.00E-13 4.44E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not l\_pplicable
5/18/1988 1.78E·14 5.00E-12 l.25E-12 4.39E·14 8.00E-14 2.00E-14 4.92E·l6 2.00E-12 5.00E-13 1.38E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 7.56E-15 5.00E-12 1.25E-12 3.31E·14 8.00E-14 2.00E-14 l.51E-15 2.00E-12 5.00E-13 1.97E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 l.47E-14 5.00E-12 1.25E-12 l.56E·15 8.00E-14 2.00E-14 2.57E·15 2.00E-12 5.00E-13 2.12E-14 4.00E-12 l.OOE-12 jllot Analyzed Not Applicable Not Applicable
2/13/1989 2.47E-15 5.00E-12 1.25E-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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 2.SOE-16 5.00E-12 1.25E-12 7.68E-15 8.00E-14 2.00E-14 9.03E-16 2.00E-12 S.OOE-13 8.05E·15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
8/14/1989 6.50E-15 S.OOE-12 1.25E-12 4.72E-15 8.00E-14 2.00E-14 2.35E-15 2.00E-12 5.00E-13 9.9SE·15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/13/1989 9.63E-15 S.OOE-12 1.25E-12 4.0SE-15 8.00E-14 2.00E-14 4.03E-15 2.00E-12 S.OOE-13 l.99E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 8.92E·15 5.00E-12 l.25E-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 5.00E-12 l.25E-12 3.58E·l5 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 1.92E·l5 5.00E-12 1.25E·12 1.87E·15 8.00E-14 2.00E-14 5.06E-16 2.00E-12 5.00E-13 8.86E·15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 2.91E·l5 5.00E-12 1.25E·12 2.25E-17 8.00E-14 2.00E-14 1.08E-15 2.00E-12 5.00E-13 2.19E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/11/1991 1.67E-16 5.00E-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 jllot Applicable Not Applicable
5/13/1991 l.87E-16 S.OOE-12 1.25E-12 2.61E-15 8.00E-14 2.00E-14 3.54E·16 2.00E-12 .· 5.00E-13 l.40E·l4 4.00E-12 l.OOE-12 Not Analyzed Jllot Applicable Not Applicable
8/12/1991 4.8SE-16 5.00E-12 1.25E-12 4.38E-16 8.00E-14 2.00E-14 1.27E·l6 2.00E-12 5.00E-13 2.20E·l4 4.00E-12 1.00E-12 Not Analyzed f'lot Applicable jllot Applicable
11/11/1991 1.77E·l6 5.00E-12 l.25E-12 1.46E-16 8.00E-14 2.00E-14 3.76E-17 2.00E-12 5.00E-13 l.15E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 1.83E·16 5.00E-12 1.25E-12 l.9SE·15 8.00E-14 2.00E-14 l.33E·16 2.00E-12 5.00E-13 3.35E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/11/1992 4.40E-16 5.00E-12 1.25E-12 2.56E-16 8.00E-14 2.00E-14 4.04E-16 2.00E-12 5.00E-13 1.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 9.09E-17 5.00E-12 1.25E-12 l.lSE-16 8.00E-14 2.00E-14 4.50E-17 2.00E-12 S.OOE-13 l.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 2.07E·16 5.00E-12 l.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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 1.73E-16 5.00E-12 l.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 l .OOE-12 Not Analyzed Not Applicable Not Applicable
5/10/1993 2.70E-17 S.OOE-12 1.25E-12 2.SOE-17 8.00E-14 2.00E-14 8.74E·17 2.00E-12 S.OOE-13 l.2SE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 9.00E-17 5.00E-12 1.25E·12 1.76E-16 8.00E-14 2.00E-14 O.OOE+OO 2.00E-12 S.OOE-13 1.SOE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/8/1993 l.OOE-16 -5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 6.00E-17 2.00E-12 5.00E-13 l.75E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable ,Not Apglicable
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
Limit= Limit= limit= ~imit= limit=
~Goal=' 2.2SE-"1.4 uO/ml ALARAGoal = SE-15 uO/ml jlJ.ARA(Goal = 2.2SE'·13'ii0lml ALARAGoal: 1.SE-13 uCi/ml ALARAGoal: 1£-15 uCi/ml
Pre 1994 MPC ;»E-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.ZSE-12 uCi/ml Pre 1994 ALARA 5E·13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
Al.ARA GOAL= GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
2/7/1994 1.lOE-16 5.00E-12 l.25E-12 3.38E-16 8.00E-14 2.00E-14 2.21E-16 .Z.OOE-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 5.00E-12 :l.25E-12 2.82E-16 8.00E-14 2.00E-14 3.46E-16 2.00E-12 5.00E-13 1.73E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/9/1994 3.85E-16 5.00E-12 1.25E-12 3.53E-16 8.00E-14 2.00E-14 l .OOE-16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-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 l.96E·16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.40E-17 g.OOE-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 1.50E-13 Not Analyzed Not Applicable Not Apl)licable
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 2.25E-13 2.70E-15 6.00E-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_ 6.60E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 l.19E-14 9.00E-14 2.25E-14 3.80E-16 2.00E-14 5.00E-15 6.lOE-15 9.00E-13 2.25E-13 6.48E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
5/6/1996 4.55E-16 9.00E-14 2.25E-14 3.57E-15 2.00E-14 5.00E-15 2.84E-16 9.00E-13 2.25E-13 7.68E-15 6.00E-13 1.SOE-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 l.50E-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 1.50E-13 Not Analyzed Not Applicable Nor Applfcable
2/6/1997 1.00E-16 9.00E-14 2.25E-14 1.40E-16 2.00E-14 5.00E-15 l.03E-16 9.00E-13 2.25E-13 6.76E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
5/5/1997 l.OOE-16 9.00E-14 -2.25E-14 4.00E-16 2.00E-14 5.00E-15 2.24E·16 9.00E-13 2.25E-13 4.55E-15 6.00E-13 1.50E-13 Not Analyzed 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 1.50E-13 Not Analyzed Not Ai>pUcabli! 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 AJ>.Plicable
4/28/1998 3.32E-16 9.00E-14 2.25E-14 4.43E-15 2.00E-14 5.00E-15 1.21E-16 9.00E-13 2.25E-13 7.43E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable'
7/31/1998 ~.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.SOE-13 j\Jot 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 1.50E-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 1.50E-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 1.SOE-13 Not Analyzed Not Applicable · Not Applicable
7/3/1999 5.90E-16 9.00E-14 2.25E-14 9.89E-16 2.00E-14 5.00E-15 l.28E-16 ~ 9.00E-13 . 2.25E-13 6.40E-15 6.00E-13 1,50E-13 Not Analyzed Not Applicable Not Applicable
9/27/1999 1.70E·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 A111>licable 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 2.25E-13 6-42E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 1.00E-16 9.00E-14 2.25E-14 2.13E-16 2.00E-14 5.00E-15 2.20E-16 9.00E-13 2.2SE:l3 S.61E-15 6.00E-13 1.50E-l3 NoMnalyzed Not Applicable Not App!lcable
6/26/2000 1.75E-16 9.00E-14 2.25E-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 1.SOE-13 Not Analyzed Not Applicable Nol App,llcable
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 1.SOE-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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 1.45E-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 6.37E-15 6.00E-13 1.SOE-13 Not Analyzed Not Appllcrable Not Applicable
7/2/2001 l.OOE-16 9.00E-14 .2.25E-14 1.0SE-16 -2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.99E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 l.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 l.38E-16 9.00E-14 2.25E-14 2.0SE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l .83E-15 6.00E-13 1.SOE-13 Not Analyzed NotAp))liqible Not Applicable
4/1/2002 2.ZOE-16 9.00E-14 2.25E-14 3.38E·16 2.00E-14 5.00E-15 l.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 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 7.40E-15 6.00E-13 l.SOE-13 Not Analyzed Not Appllcable .. Not A11!l)icable
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 9.00E-14 2.25E-14 1.92E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.42E-15 6.00E-13 1.50E-13 j\Jot Analyzed Not Applicable Not Applicable
3/31/2003 2.SOE-16 9.00E-14 2.25E-14 1.69E-16 2.00E-14 5.00E-15 l.29E-16 9.00E-13 2.25E-13 4.SSE-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.ZOE-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 Not 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 2.25E-13 9.45E·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.26E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.00E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.00E-16 9.00E-14 2.25E-14 2.53E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.23E-15 6.00E-13 LSOE-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-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 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 1.37E-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 2.66E-16 2.00E-14 5.00E-15 3.lSE-16 9.00E-13 2.25E-13 9.22E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 l.47E-16 9.00E-14 , 2.25E-14 1.45E-15 2.00E-14 5.00E-15 1.42E·16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Appllcab_l_e
9/26/2005 2.0lE-16 9.00E-14 2.25E-14 2.06E-16 2.00E-14 5.00E-15 4.BOE-16 9.00E-13 2.25E-13 2.12E-14 6.00E-13 1.SOE-13 Not Analyzed Not APPll~abl_e Not Applicable
1/3/2006 4.54E-16 9.00E-14 2.25E-14 1.24E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 3.60E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/3/2006 l.99E-16 9.00E-14 2.25E-14 l.32E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 8.36E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Appji~;,ble
7/3/2006 2.76E-16 9.00E-14 2.25E-14 2.63E·16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.03E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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=
ALARA Goal= 2.2SE-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.2SE-13 uCi/inl 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 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= limit= Limit= limit= Limit=
i>re 1994 1.2SE-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 EFCA
10/2/2006 4.97E-16 9.00E-14 2.25E-14 2.37E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.60E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
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 A_pplicable
4/2/2007 7.08E-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 l.54E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AJ>plicable
7/2/2007 9.41E-16 9.00E-14 2.25E-14 1.46E-16 2.00E-14 5.00E-15 1.99E-16 9.00E-13 2.25E-13 2.56E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2007 3.30E-16 9.00E-14 2.25E-14 5.50E-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 Applicable Not Applicable
12/31/2007 1.42 E-15 : 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.93E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2008 1.25E-16 9.00E-14 2.25E-14 7.72E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 4.09E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2008 1.28E-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 l.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 1.lOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2008 2.88E-15 9.00E-14 2.25E-14 l.lOE-15 2.00E-14 5.00E-15 6.56E-16 '9.00E-13 2.25E-13 1.38E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 i.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.50E-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 1.51E-16 9.00E-13 2.25E-13 4.47E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable ]'Jot Applicable : 9.00E-13 .2.25E-13 6,00E-13 l.50E-13 Not Analyzed Not Applicable Not AllJ>licable 9/15/2009 4.05E-15 9.00E-14 2.25E-14 l.45E-15 2.00E-14 5.00E-15 2.52E-16 l.24E-14
12/15/2009 6.50E-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 g.OOE-14 2.25E-14 l.26E-16 2.00E-14 5.00E-15 1.34E-16 9.00E-13 2.25E-13 l.19E-14 6.00E-13 l.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 1.50E-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 5.00E-15 8.23E-16 9.00E-13 2.25E-13 5.llE-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable _Not Applicable -
12/31/2010 e3.93E-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 1.13E-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 l.58E-16 9.00E-13 2.25E-13 l.llE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 3.30E-15 ,. 9.00E-14 2.25E-14 5.44E-16 2.00E-14 5.00E-15 4.18E-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 1.32E-15 9.00E-14 i.25E-14 7.89E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 2.25E-13 1.18E-14 6.00E-13 1.50E-13 Not Analyzed _ Not Applicable Not Applicable
1/3/2012 1.04E-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 1.14E-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 5.02E-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 J\p_plicable Not Ap_plicable
7/2/2012 2.62e-:.15 9.00E-14 2.25E-14 1.23E-15 2.00E-14 5.00E-15 2.97E-16 9.00E-13 .2.25E-13 9.27E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 4.05E-15 9.00E-14 2.25E-14 8.33E-16 2.00E-14 5.00E-15 5.43E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 2.32E-15 9.00E-14 _ i.25E-14. 5.89E-16 2.00E-14 5.00E-15 3.75E-16 9.00E-13 2.25E-13 1.56E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 6.04E-15 9.00E-14 2.25E-14 4.99E-16 2.00E-14 5.00E-15 2.79E-16 9.00E-13 2.25E-13 2.13E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not I\J!plicable
7/2/2013 2.50E-15 9.00E-14 '2.25E-14 3.62E-16 2.00E-14 5.00E-15 2.40E-16 9.00E-13 2.25E-13 4.93E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 2.98E-15 9.00E-14 2.25E-14 4.49E-16 2.00E-14 5.00E-15 1.54E-16 9.00E-13 2.25E-13 7.49E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2013 3.88E-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2014 ~.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 l.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 l.77E-15 9.00E-13 2.25E-13 1.06E-14 6.00E-13 l.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 1.llE-14 6.00E-13 l.50E-13 1.0lE-17 4.00E-15 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 l.90E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 1.00E-15
3/30/2015 5.90E-15 ~.OOE-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 . 2.25E-13 2.BOE-14 6.00E-13 l.50E-13 5.00E-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 2.2~E-13 l.20E-14 6.00E-13 l.50E-13 .1.00E-17 -4.00E-15 1.00E-15
9/28/2015 5.00E-15 9.0QE-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 l.50E-13 7.00E-18 4.00E-15 .1.00E-15
12/28/2015 4.50E-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 9.00E-13 2.25E-13 l.70E-14 6.00E-13 1.50E-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 ~-OOE-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 5.00E-15 2.20E-15 9.00E-13 .2.25E-13 3.40E-16 6.00E-13 l.50E-13 7.lOE-18 4.00E-15 1.00E-15
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 1.50E-13 4.50E-18 4.00E-15 i.OOE-15
3/27/2017 2.60E-15 '9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 l,50E-13 'l.OOE-18 4.00E-15 1.00E-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 ?.25E-13 1.lOE-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 1.00E-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 1.00E-15
12/26/2017 1.00E-14 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 j1.25E-13 2.20E-14 6.00E-13 1.50E-13 2.00E-17 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 2E-14 uCi/ml 8HV-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
Limit= Limit= Limit= Limit= Limit=
AlARAGoal = 2.2SE·l4 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-lZ uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre1994MPC 2E-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre1994MPC Not Applicable
Limit= Limit= Limit= Limit= Limit=
Pre 1994 1.25E·U 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 ~FC EFCA
9/28/1981 2.44E-15 5.00E-12 1.25E-12 1.53E-15 8.00E-14 2.00E-14 7.54E-16 2.00E-12 5.00E-13 1.69E-14 4.00E-12 1.00E-12 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-1S 2.00E-12 5.00E-13 1.53E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 1.04E-15 5.00E-12 1.25E-12 2.62E-15 8.00E-14 2.00E-14 1.llE-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-1S 5.00E-12 1.25E-12 7.61E-15 8.00E-14 2.00E-14 1.39E-15 2.00E-12 S.OOE-13 1.80E-1S 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/27/1982 1.71E-14 S.OOE·12 1.2SE-12 9.46E-15 8.00E-14 2.00E-14 3.SOE-15 2.00E-12 5.00E-13 2.35E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 1.90E-14 5.00E-12 1.25E-12 S.77E-15 8.00E-14 2.00E-14 9.34E-17 2.00E-12 5.00E-13 4.32E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/4/1983 5.00E-12 1.2SE-12 2.33E-15 8.00E-14 2.00E-14 5.93E-16 2.00E-12 5.00E-13 3.0lE-14 4.00E-12 1.00E-12 Not Analyzed N9t Appllc:;iti!e Not Applicable
6/30/1983 7.62E-16 5.00E-12 1.25E-12 3.25E-1S 8.00E-14 2.00E-14 6.28E-15 1.00E-12 5.00E-13 2.69E-14 4.00E-12 1.00E-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 S.OOE-13 2.08E-14 4.00E-12 1.00E-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 l.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 3.88E-15 2.00E-12 S.OOE-13 4.67E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 1.12E-15 5.00E-12 ·1.ZSE-12 l.92E-1S 8.00E-14 2.00E-14 3.31E-1S 2.00E-12 5.00E-13 2.21E-14 4.00E-12 1.00E-12 !'Jot Analyzed Not Applicable Not Applicable
10/1/1984 1.llE-15 5.00E-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 S.OOE-12 l.25E-12 6.71E-16 8.00E-14 2.00E-14 4.94E-16 2.00E-12 S.OOE-13 2.42E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
4/1/1985 .2.36E-16 5.00E-12 l.25E-12 5.43E-16 8.00E-14 2.00E-14 2.71E-16 2.00E-12 5.00E-13 1.25E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/1/1985 7.58E-16 5.00E-12 1.25E-12 4.00E-16 B.OOE-14 2,00E-14 6.90E-16 2.00E-12 5.00E-13 2.15E-14 4.00E-12 1.00E-12 Not Analyzed f."lot Applicable Not Applicable
9/30/1985 7.47E-1S 5.00E-12 1.25E-12 1.16E-15 8.00E-14 2.00E-14 2.19E-15 2.00E-12 5.00E-13 9.20E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
1/2/1986 l.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 l .25E-12 7.64E-15 8.00E-14 2.00E-14 l.51E-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 ~.25E-12 5.19E-15 8,00E-14 2.00E-14 l.05E-14 . 2.00E-12 5.00E-13 2.16E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 2.33E·14 5.00E-12 1.25E-12 7.78E-15 8.00E-14 2.00E-14 1.60E-14 2.00E-12 5.00E-13 2.02E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 3.40E-14 5.00E-12 1.25E-12 S.35E-15 8.00E-14 2.00E-.14 l.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 1.25E·12 4.50E-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 Applicable Not Applicable
5/11/1987 2.50E-14 :;.OOE-12 1.25E-12 8.54E-15 8.00E-14 2.00E-14 8.15E-15 2.00E-12 5.00E-13 3.28E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/9/1987 2.65E-14 5.00E-12 1.25E-12 6.62E-15 8.00E-14 2.00E-14 9.34E-15 .2.00E-12 5.00E-13 2.77E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable !'lot Applicable
11/2/1987 1.80E-14 ·s.OOE-12 l.25E-12 7.09E-15 8.00E-14 2.00E-14 7.20E-15 2.00E-12 5.00E-13 1.77E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 1.0lE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 l.78E-14 5.00E-12 1.25E-12 8.14E-15 8.00E-14 2.00E-14 7.43E-15 ;!.OOE-12 5.00E-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not Applica_l~le 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 lliot Analyzed Not Applicable Not l',11pllcable
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 S.OOE-13 3.43E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/13/1989 1.67E-14 5.00E-12 1.25E-12 5.54E-15 8.00E-14 2.00E-14 7.20E-15 2.00E-12 5.00E-13 S.02E·14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 2,03E-14 5:00E-12 1.lSE-12· 7.05E-15 8.00E-14 2.00E-14 9_.56E.-l6, 2.00E-12 S.OOE-13 i.43E·l4 4.00E-12 1.00E-12 Not Analyzed Not Applfcable Not Applicable
8/14/1989 2.81E-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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
U/13/1989 S.38E-14 5.00E-12 1.25E-12 8.0lE-15 8.00E-14 2.00E-14 1.81E-14 2.00E-12 5.00E-13 4.09E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 4.48E-14 S.OOE-12 l.25E-12 l.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 2.18E-14 5.00E-12 1.2SE-12 1.70E-14 8.00E-14 2.00E-14 1.59E-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 1.25E-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 1.00E-12 Not Analyzed Not Applicable Not_ApJJlicable
11/12/1990 1.llE-14 5.00E-12 1.2SE-12 5.27E-15 8.00E-14 2.00E-14 S.38E-15 2.00E-12 5.00E-13 1.56E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/11/1991 6.35E-16 5.00E-12 1.2SE-12 3.13E-16 8.00E-14 2.00E-14 2.31E-16 2.00E-12 5.00E-13 3.89E-14 4.00E-12 l.OOE-12 Not Analyzed Not Ap_plicable Not A11plicable
5/13/1991 l.22E-1S 5.00E-12 1.25E-12 6.14E-15 8.00E-14 2.00E-14 4.41E-15 2.00E-12 S.OOE-13 2.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Appllc"abl_e !'Jot Applicable
8/12/1991 7.84E-16 5.00E-12 1.2SE-12 1.43E-15 8.00E-14 2.00E-14 4.47E-16 2.00E-12 5.00E-13 l .84E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 5.37E-16 5.00E-12 1.25E-12 4.20E-16 8.00E-14 2.00E-14 1.37E-16 2.00E-12 5.00E-13 1.27E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 3.54E-16 S.OOE-12 1.25E·12 1.18E-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 A_pplicable Not Applicable
5/11/1992 4.71E-16 5.00E-12 1.25E-12 9.58E-16 8.00E-14 2.00E-14 8.31E-17 2.00E-12 S.OOE-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 1.6SE-16 2.00E-12 5.00E-13 l.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ~p_plicable
11/9/1992 3.66E-16 5.00E-12 1.25E-12 2.25E-16 8.00E-14 2.00E-14 1.08E-16 2.00E-12 ·s.OOE-13 2.24E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applica61e
2/9/1993 2.05E-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/10/1993 4.SOE-16 5.00E-12 1.25E-12 8.25E-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 S.OOE-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 5.00E-13 1.70E-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-ST230 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
limit= 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
Pre 1994MPC 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= limit=
Pre 1994 1.25E-U 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
11/8/1993 2.70E-16 5.00E-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 l.OOE-12 Not Analyzed Not Applicable l\lot Applicable
2/7/1994 3.18E·16 5.00E-12 l.25E·12 l.OOE-16 8.00E-14 2.00E-14 5.lSE-16 2.00E-12 5.00E-13 3.64E·14 4.00E-12 l.OOE-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 l.lOE-15 2.00E-12 5.00E-13 8.30E·15 4.00E-12 l.OOE-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 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ~plicable
11/7/1994 9.21E-17 5.00E-12 1.25E-12 l.59E·15 8.00E-14 2.00E-14 l.66E·15 2.00E-12 5.00E-13 1.00E-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/7/1995 1.51E·15 9.00E-14 2.25E-14 9.50E-16 2.00E-14 5.00E-15 9.70E·17 9.00E-13 2.25E·l3 9.35E·15 6.00E-13 l.50E-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.50E-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 1.66E·16 9.00E-14 2.25E-14 l.67E-15 2.00E-14 5.00E-15 3.90E-15 9.00E-13 2.25E-13 5.60E·15 6.00E-13 l.50E-13 Not Analyzed Not Applicable l\lot Applicable
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 .l.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.50E-13 Not Analyzed Not Applicable l\lot Applicable
5/6/1996 1.76E-15 9.00E-14 2.25E-14 3.57E-15 2.00E-14 5.00E-15 9.SSE-16 9.00E-13 2.25E-13 7.54E-15 6.00E-13 .l.50E-13 Not Analyzed Not Applicable 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 l.50E·l3 Not Analyzed Not Aru>licable Not Applicable
11/6/1996 3.53E·15 9.00E-14 2.2SE·14 5.31E-15 2.00E-14 5.00E-15 9.39E-16 9.00E-13 2.25E·l3 1.21E-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 l.87E·16 9.00E-13 2.25E-13 6.14E·15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not A_p_plicable
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 l.50E-13 Not Analyzed Not Applicable Not Applicable
8/11/1997 1.21E·15 9.00E-14 2.25E-14 7.39E·16 2.00E-14 5.00E-15 5.0SE-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 1.92E·15 2.00E-14 5.00E-15 6.21E·16 9.00E-13 2.25E-13 4.68E·15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/28/1998 '2.84E·15 9.00E-14 2.25E-14 2.38E·15 2.00E-14 5.00E-15 l.72E·15 9.00E-13 2.25E-13 7.35E·l5 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 7.49E-16 9.00E-14 2.2SE·14 1.49E-15 2.00E-14 5.00E-15 8.34E-16 9.00E-13 2.2SE·l3 7.0lE-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable l\lot 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.50E-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 5.00E-15 4.58E-15 9.00E-13 2.25E-13 l.43E·14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/1999 3.7SE·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 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 l.53E-15 9.00E-14 2.25E-14 8.65E·16 2.00E-14 5.00E-15 6.52E-16 9.00E-13 2.25E-13 7.20E·15 6.00E-13 l.SOE-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.SSE·lS 9.00E-13 2.25E-13 8.22E·15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/28/1999 9.48E·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 l.50E-13 Not Analyzed Not Applicable 'Not Applicable
3/27/2000 2.06E-15 9.00E-14 2.25E-14 l.27E-15 2.00E-14 5.00E-15 1.09E·15 9.00E-13 2.25E-13 7.72E·l5 6.00E-13 'l.50E-13 Not Analyzed Not Applicable Not Applicable
6/26/2000 l.SOE·15 9.00E-14 2.25E-14 l.24E·15 2.00E-14 5.00E-15 l.OlE-15 9.00E-13 2.25E-13 4.36E·l5 6.00E-13 l.SOE-13 Not 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 l.50E-13 Not Analyzed Not Applicable r,Jot Ap_plicable
12/26/2000 1.48E·15 ~.OOE-14 2.25E-14 7.56E·l6 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·l6 2,00E-14 5.00E-15 '1.89E-16 9.00E-13 2.25E-13 6.13E·15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable l\lot Applicable
7/2/2001 4.52E-16 9.00E-14 2.25E-14 4.02E·l6 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E·13 7.48E·15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 4.65E-16 9.00E-14 2.25E-14 2.06E-16 2.00E-14 5.00E-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.SlE-16 2,00E-14 S.OOE-15 3.64E·16 9.00E-13 2.25E-13 4.72E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A_pplicable
4/1/2002 l.26E-15 9.00E-14 2.2SE·14 7.53E-16 2.00E-14 5.00E-15 7.19E·l6 9.00E-13 2.25E-13 9.65E·15 6.00E-13 1.50E-13 Not Analyzed Not Applicable ,-.iot Applicable
7/1/2002 1.02E·15 9.00E-14 2.25E-14 1.03E·l5 2.00E-14 5,00E-15 3.39E-16 9.00E-13 2.25E·l3 7.20E-15 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not Applicable
9/30/2002 5.82E·16 9.00E-14 -2.25E-14 9.28E·16 2.00E-14 5.00E-15 3.14E-16 9.00E-13 2.25E·l3 4.48E-15 6,00E-13 l.50E-13 Not Analyzed Not Applicable i'lot Applicable
12/30/2002 1.00E-16 9.00E-14 2.25E-14 7.67E·l6 2.00E-14 5.00E-15 3.48E-16 9.00E-13 2.25E·l3 9.56E-15 6.00E-13 l.50E-13 ,Not Analyzed Not Applicable i'lot 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 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2003 4.35E-16 9.00E-14 2.25E-14 5.08E·16 2.00E-14 5.00E-15 2.51E-16 9.00E-13 2.25E·l3 l .34E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/29/2003 1.51E·16 9.00E-14 2.25E-14 l.02E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 7.28E·15 6.00E-13 l.50E-13 Not Analyzed Not Applicable tJot Applicable
12/29/2003 l.52E-16 9.00E-14 2.25E-14 l.54E-16 2.00E-14 .5.00E-15 l.SlE-16 9.00E-13 2.25E·l3 7.02E·15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/2004 1.00E·16 9.00E-14 2.25E·l4 l.12E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E·l3 8.82E-15 6.00E-13 1.50E-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 l.25E-16 9.00E-13 2.25E·13 2.47E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.16E·16 9.00E-14 2.25E-14 l.72E-16 2.00E-14 5.00E-15 1.18E·16 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/27/2004 1.14E·l6 9.00E-14 2.25E-14 l.06E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.59E·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 2.04E·16 2.00E-14 5.00E-15 1.83E-16 9.00E-13 2.25E-13 8.57E-15 6.00E-13 1.SOE-13 'Not Analyzed Not Applicable Not Applicable
6/29/2005 1.83E-16 9.00E-14 2.25E·14 3.SlE-16 2.00E-14 S.OOE-15 3.09E-16 9.00E-13 2.25E·l3 1.06E-14 6.00E-13 1.50E-13 Not Ana!Yzed Not Applicable Not Applicable
9/26/2005 2.87E-16 9.00E-14 2.25E-14 8.21E·l6 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 8.74E-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 l.50E-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-SU Effluent 2E-14 uCi/ml BHV-ST230 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
Limit= Limit= Limit= 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-12 uCi/ml Pre 1994 MP( SE-14 uCi/ml Pre 1994 MPC 2E-1Z uCi/ml Pre 1994 MPC 4E-1Z uCi/ml Pre1994MPC Not Applicable
Limit= Limit= Limit= Limit= limit=
Pre 1994 l .25E-1Z 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
4/3/2006 5.22E-16 9.00E-14 2.25E-14 6.66E-16 2.00E-14 S.OOE-15 1.llE-16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 l.50E·l3 Not Anal¥zed Not A~plicable Not Applicable
7/3/2006 3.08E·16 9.00E-14 2.25E-14 1.lOE-16 2.00E-14 5.00E-15 l .OOE-16 9.00E-13 2.25E·l3 l.25E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
10/2/2006 9.14E-16 9.00E-14 2.25E-14 4.95E-16 2.00E-14 5.00E-15 l.86E-16 9.00E-13 2.2SE-13 1.67E-14 6.00E-13 l.50E-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 1.0BE-15 9.00E-14 2.2SE·14 8.22E-16 2.00E-14 5.00E-15 2.26E-16 9.00E-13 2.25E-13 1.64E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 l.54E·15 9.00E-14 2.25E-14 8.16E-16 2.00E-14 S.OOE-15 4.76E-16 9.00E-13 2.25E-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 2.25E-14 2.37E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 6.65E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 .1.46E-15 9.00E-14 2.25E-14 5.67E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.02E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2008 3.16E-16 9.00E-14 2.25E-14 6.17E-16 2.00E-14 5.00E-15 3.71E-16 9.00E-13 2.25E-13 4.82E-15 6.00E-13 l.50E·l3 Not Analyzed Not Applicable Not 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 1.50E-13 Not Analyzed Not ApJ>licable 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 L15E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 l.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 2.25E-13 4.66E-15 6.00E-13 l.50E·l3 Not Analyzed Not Applicable Not Applicable
6/15/2009 2.31E-16 9.00E-14 '2.25E-14 7.79E-16 2.00E-14 S.OOE-15 6.37E-16 9.00E-13 2.25E-13 4.18E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 3.lOE-15 9.00E-14 2.25E-14 9.20E-16 2.00E-14 5.00E-15 6.36E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 l.50E·l3 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 2.25E-13 2.48E-15 6.00E-13 l .50E·l3 Not Analyzed Not Applicable Not Applicable
3/31/2010 4.78E-15 9.00E-14 2.25E-14 3.73E-16 2.00E-14 S.OOE-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 2.25E·14 7.84E-16 2.00E-14 5.00E-15 1.05E-15 9.00E-13 2.25E-13 4.40E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2010 3.57E-15 9.00E-14 2.25E·14 1.14E-15 2.00E-14 5.00E-15 7.97E-16 9.00E-13 2.25E·l3 3.78E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap~licable
12/31/2010 8.52E-15 9.00E-14 2.25E·14 1.4SE-15 2.00E-14 5.00E-15 1.29E-15 9.00E-13 2.25E·l3 1.33E-14 6.00E-13 l .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 .50E-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 6.98E-15 9.00E-14 2.2SE·14 2.03E-15 2.00E-14 5.00E-15 ~.52E-15 9.00E-13 2.25E-13 1.08E-14 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 3.llE-15 9.00E-14 2.25E-14 1.14E-15 2.00E-14 5.00E-15 5.75E-16 9.00E-13 2.25E-13 1.41E·14 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not Applicable
1/3/2012 4.44E-15 9.00E-14 2.25E-14 2.14E-15 2.00E-14 5.00E-15 l.53E-15 9.00E-13 2.25E-13 2.0SE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 S.52E-15 9.00E-14 2.25E-14 3.24E-15 2.00E-14 S.OOE-15 l.79E·15 9.00E-13 2.25E-13 1.SSE-14 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not Applicable
7/2/2012 5.87E-15 9.00E-14 2.25E-14 3.06E-15 2.00E-14 5.00E-15 l.21E-15 9.00E-13 2.25E-13 1.llE-14 6.00E-13 1.50E·l3 Not Analyzed Not Applicable !'lot 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·l3 1.30E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 4.SOE-15 9.00E-14 2.25E·14 1.62E-15 2.00E-14 5.00E-15 1.79E-15 9.00E-13 2.25E·l3 1.74E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 6.66E-15 9.00E-14 2.2SE·l4 1.48E-15 2.00E-14 5.00E-15 1.12E-15 9.00E-13 2.2SE·l3 l.80E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 7.35E-15 9.00E-14 2.25E·l4 l .72E-15 2.00E-14 5.00E-15 2.02E-15 9.00E-13 2.25E·l3 6.67E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 2.78E-15 9.00E-14 2.2SE-14 6.92E-16 2.00E-14 5.00E-15 3.29E-16 9.00E-13 2.25E-13 6.62E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
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·l3 Not Analyzed Not Applicable Not Applicable
3/31/2014 4.74E-15 9.00E-14 2.25E·14 l.42E-15 2.00E-14 5.00E-15 3.48E-15 9.00E-13 2.25E-13 l.50E-14 6.00E-13 l.50E·l3 Not Analyzed Not Applicable Not Applicable
6/30/2014 8.18E-15 9.00E-14 2.25E-14 l.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 !'lot Applicable Not Applicable
9/30/2014 l.32E-14 9.00E-14 2.25E·14 7.76E-16 2.00E-14 5.00E-15 1.04E-15 9.00E-13 2.25E-13 1.23E-14 6.00E-13 1.SOE-13 4,66E-17 4.00E-15 l.OOE-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 2.2SE·l3 2.lOE-14 6.00E-13 1.50E·l3 8.00E-18 4.00E-15 l.OOE-15
3/30/2015 1.00E-14 9.00E-14 2.2SE-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.SOE-13 3.00E-18 4.00E-15 l.OOE-15
6/29/2015 4.60E·15 9.00E-14 2.25E·14 8.00E-16 2.00E-14 5.00E-15 3.70E-15 9.00E-13 2.25E·l3 l.40E-14 6.00E-13 l.50E-13 2.00E-17 4.00E-15 1.00E-15
9/28/2015 1.20E-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 l.SOE-13 l.OOE-17 4.00E-15 1.00E-15
12/28/2015 7.40E·16 9.00E-14 2.25E·14 1.00E-16 2.00E-14 5.00E-15 1,90E·16 9.00E-13 2.25E·l3 2.20E-14 6.00E-13 l.SOE-13 2.00E-17 4.00E-15 1.00E-15
3/28/2016 1.40E-15 9.00E-14 2.25E-14 6.00E-16 2.00E-14 5.00E-15 6.20E-15 9.00E-13 ;2.2SE·l3 2.30E-14 6.00E-13 1.50E·l3 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 S.OOE-15 1.lOE-15 9.00E-13 2.25E·l3 2.90E-16 6.00E-13 1.SOE-13 3.00E-17 4.00E-15 1.00E-15
12/27/2016 5.lOE-15 .9.00E-14 2.25E-14 6.GOE-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 l.30E-17 4.00E-15 l .OOE·lS
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·l3 l.50E-14 6.00E-13 1.SOE-13 2.00E-17 4.00E-15 1.00E-15
6/26/2017 8.00E-16 9.00E-14 2.25E-14 3.00E-16 2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E·l3 1.30E-14 6.00E-13 1.50E-13 6.00E-18 4.00E-15 1.00E-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 l.60E-14 6.00E-13 1.50E·l3 4.00E-18 4.00E-15 1.00E-15
12/26/2017 l.40E-14 9.00E-14 2.25E-14 4.00E-16 2.00E-14 S.OOE-15 3.00E-16 9.00E-13 2.25E·l3 1.60E-14 6.00E-13 1.50E·l3 l.OOE-17 4.00E-15 1.00E-15
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TAB6
BHV-6 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent !IE-14 uCi/ml BHV-6U Effluent ZE-14 uCi/ml BHV-6T230 ~ffluent 9E-13 uCi/ml BHV-6R Effluent 6E-13 uCi/ml BHV-6PB Effluent 4e-15 uCi/ml BHV-6TZ32
Concentration Concentration Concentration Concentration Concentration
Umlt= Limit= Limit= Limit= Limit=
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal= SE-13 uCi/ml ,!'LARA Goal= 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=
Pre 1994 1.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 .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
12/14/1981 5.00E-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
3/29/1982 .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
6/30/1982 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
9/27/1982 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
1/3/1983 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 App_licable
4/4/1983 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
6/30/1983 5.00E-12 l.2SE-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
10/3/1983 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
1/3/1984 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 Ap_plicable Not Applicable
4/2/1984 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
7/2/1984 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
10/1/1984 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
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 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
7/1/1985 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 Apj>licable
9/30/1985 -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
1/2/1986 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 · Nor Applicable
4/1/1986 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
6/30/1986 _5.00E-12 L25E·12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applioal51e Not Apphcable
10/27/1986 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 No.t_Analyzeil Not Applicable Not Applicable
12/15/1986 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 .A,pplicable
3/16/1987 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.Appllcalilj!'
5/11/1987 S.OOE-12 1.25E-12 B.OOE-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 S.OOE-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
11/2/1987 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
2/16/1988 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 -
5/18/1988 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
8/15/1988 -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
11/14/1988 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
2/13/1989 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 J'lot Ap_plicable
S/l.S/1989 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 _
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 !'lot Applicable
11/13/1989 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
2/12/1990 5.00E-12 1.25E·12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 .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 Al)plicable
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 Appjlcablg
11/12/1990 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.ooe-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
2/U/1991 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
5/13/1991 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 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
11/11/1991 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-H 4.00E-12 l.OOE-12 Not Analyzed ,Not Applicable Not Applicable
2/10/1992 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
5/11/1992 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
8/10/1992 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 A1111licable Not Applicable
11/9/1992 5.00E-12 l.25E-12 8.00E-14 2.00E-14 -?.OOE-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not App\fcatile. Not Applicable
2/9/1993 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
5/10/1993 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 Applicable Not Applicable
8/10/1993 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 Applicable Not Applicable
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 BHV-6PB Effluent 4e-15 uCi/ml BHV-6T232
Concentration Concentration Concentration Concentration Concentration
limit= Limit= Limit= Limit= Limit= ·-
AlARAGoal= 2.25E-14 uCl/ml ALARA Goal= SE-13 uCi/ml Al.ARA Goal= 2.25E-13 uCi/ml ALARAGoal = 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre1994MPC SE-U uCi/rnl Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC 2E-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
µmlt= Limit= Limit= Limit: Limit=
Pre 1994 :1.2SE-12 uCi/ml pre 1994 SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 l\lot Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
:cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
11/8/1993 S.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1,00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1994 5.00E-12 1.25E-12 8.00E-14 ~.OOE-14 2.00E-12 .5.00E-13 4.00E-12 1.00E-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 .S.OOE-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/9/1994 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
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 J',lot 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.SOE-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.SOE-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AQ!)licable
11/11/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E·13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 ~.OOE-14 2.25E-14 2.00E-14 S.OOE-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 J',lot 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 1.50E-13 Not Analyzed Not Applicable Not Applicable
8/5/1996 -9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 ,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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
2/6/1997 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 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 1.50E-13 Not Analyzed Not Applicable Not Applicable
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 .SOE-13 Not Analyzed Not Applicable )',lot Applicable
7/31/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable J',lot Applicable
9/28/1998 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 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 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/1999 9.00E-14 l.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
7/3/1999 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 A!!plicable
9/27/1999 3.03E-15 9.00E-14 2.25E-14 1.37E-15 2.00E-14 5.00E-15 8.72E-16 9.00E-13 2.25E-13 7.SSE-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable : Not A.ru>licable
12/28/1999 5.0lE-15 9.00E-14 2.25E-14 2.89E-15 2.00E-14 5.00E-15 1.31E-15 9.00E-13 2.25E-13 8.lOE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable 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 1.50E-13 Not 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 1.50E-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 5.00E-15 1.91E-16 9.00E-13 2.25E-13 6.41E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
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 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 1.42E-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.lSE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 1.BlE-16 9.00E-14 2.25E-14 1.66E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.95E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 3.0BE-16 9.00E-14 2.25E-14 l.OlE-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.25E-13 8.59E-15 6.00E-13 1.50E-13 Not Analyzed ~ot Applicable Not Applicable
12/31/2001 3.31E-16 9.00E-14 2.25E-14 1.2SE-16 2.00E-14 5.00E-15 1.09E-16 9.00E-13 2.2SE-13 3.14E-15 6.00E-13 l.50E-13 Not Anal_yzed Not Applicable Not 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 2.25E-13 8.61E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 3.68E-16 9.00E-14 2.25E-14 4.41E-16 2.00E-14 5.00E-15 1.76E-16 9.00E-13 2.25E-13 8.20E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 3.67E-16 9.00E-14 2.25E-14 5.60E-16 2.00E-14 5.00E-15 1.BOE-16 9.00E-13 2.25E-13 5.55E-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 3.43E-16 2.00E-14 5.00E-15 1.67E-16 9.00E-13 2.25E-13 I.3SE-14 6.00E-13 1.SOE-13 Not Analyzed l'lot Applicable Not Applicable
3f31/2003 1.98E-16 9.00E-14 2.25E-14 1.68E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 ~.25E-13 7.77E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2003 1.lBE-16 9.00E-14 2.25E-14 1.lSE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.92E-15 6.00E-13 l.SOE-13 Not Analyzed .l'lot 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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 1.00E-16 9.00E-14 2.25E-14 1.36E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.66E-15 6.00E-13 1.50E-13 Not Analyzed Not Ai:>plicable 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 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 l.OOE-16 9.00E-13 2.25E-13 3.SSE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-16 9.00E-14 2.2SE-14 1.38E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 l.22E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/27/2004 1.0SE-16 9.00E-14 2.25E-14 1.72E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.52E-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 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 9.34E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 l.28E-16 9.00E-14 2.25E-14 1.0lE-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 9.85E-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 5.00E-15 3.SSE-16 9.00E-13 2.25E-13 1.71E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/3/2006 7.67E-16 9.00E-14 2.25E-14 2.88E-16 2.00E-14 5.00E-15 3.60E-15 9.00E-13 2.25E-13 4.SSE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E·14 uCi/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-6TZ32
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
ALARAGoal= 2.2SE·14 uCi/ml AlARA Goal= SE-13 uCi/ml AlARAGoal= 2.2SE-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-UuCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC Not Applicable
limit= Limit= Umit= Limit= Limit= -
Pre1994 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 HC 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 N_<>t ApplTcabie
7/3/2006 3.25E-16 9.00E-14 2.25E-14 2.36E-16 2.00E-14 5.00E-15 1.0SE-16 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
10/2/2006 5.03E-16 9.00E-14 2.25E-14 1.49E-16 2.00E-14 5.00E-15 1.19E-16 9.00E-13 2.25E-13 2.13E-15 6.00E-13 l.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 l.70E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 S.36E-16 9.00E-14 2.25E-14 3.lSE-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.43E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 1.08E-15 9.00E-14 2.25E'14 2.18E-16 2.00E-14 5.00E-15 l.54E-16 , 9.00E-13 2.25E-13 2.04E-14 6.00E-13 l.SOE-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.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 l.92E-15 9.00E-14 2.25E-14 l.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 Applicable Not ~l!Plicable
3/31/2008 4.34E-16 9.00E-14 2.25E-14 a.SlE-16 2.00E-14 5.00E-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 l.SOE-13 Not Analyzed Not Applicable Not Appllcll>le
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 1.00E-14 6.00E-13 1.SOE-13 Not Analyzed Not fillplicable Not.Applicable
12/31/2008 4.SOE-15 9.00E-14 2.25E-14 1.70E-15 2.00E-14 5.00E-15 1.25E-15 9.00E-13 2.25E-13 1.49E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 2.77E-15 9.00E-14 2.25E-14 1.0lE-15 2.00E-14 5.00E-15 7.82E-16 9.00E-13 2.25E-13 6.46E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/15/2009 1.41E-16 9.00E-14 2.25E-14 2.67E-16 2.00E-14 5.00E-15 1.81E-16 9.00E-13 2.25E-13 .S.76E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 4.87E-15 9.00E-14 2.25E-14 4.32E-16 2.00E-14 5.00E-15 2.23E-16 9.00E-13 2.25E-13 8.98E-15 6.00E-13 1.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 2.25E-13 6.44E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2010 9.63E-15 9.00E-14 2.25E-14 l.82E-16 2.00E-14 5.00E-15 2.06E-16 9.00E-13 2.25E-13 1.37E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applica~le Not Applicable
6/30/2010 3.62E-15 9.00E-14 2.25E-14 3.94E-16 2.00E-14 S.OOE-15 4.89E-16 9.00E-13 2.25E-13 4.30E-15 6.00E-13 l.SOE-13 Not Analyzed No_tApplfcable Not Applicable
9/30/2010 S.42E-15 9.00E-14 2.25E-14 1.08E-15 2.00E-14 5.00E-15 S.68E-16 9.00E-13 2.25E-13 3.98E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2010 1.24E-14 9.00E-14 2.25E-14 l.21E-15 2,00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 l.53E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not A)Jpllcable
4/4/2011 2.70E-15 9.00E-14 2.25E-14 4.62E-16 2.00E-14 5.00E-15 6.SlE-16 9.00E-13 2.25E-13 1.29E-14 6.00E-13 1.50E-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 2.25E-13 7.97E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 2.05E-15 9.00E-14 2.25E-14 6.12E-16 2.00E-14 5.00E-15 l.88E-16 9.00E-13 2.25E-13 9.93E-15 6.00E-13 1.SOE-13 NoM'nalyzed Not Applicable Not Applicable
1/3/2012 3.14E-15 9.00E-14 2.25E-14 1.09E-15 2.00E-14 5.00E-15 7.65E-16 9.00E-13 2.25E-13 L89E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 4.41E-15 9.00E-14 2.25E-14 1.82E-15 2.00E-14 5,00E-15 4.00E-16 9.00E-13 2.25E-13 1.50E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2012 6.42E-15 9.00E-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
10/1/2012 6.63E-15 9.00E-14 2.25E-14 1.31E-15 2.00E-14 5.00E-15 1.22E-15 9.00E-13 2.25E-13 1.34E-14 6.00E-13 1.50E-13 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 1.60E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not ApQlicable
3/25/2013 4.52E-15 9.00E-14 2.25E-14 7.93E-16 2.00E-14 S.OOE-15 4.91E-16 9.00E-13 2.25E-13 l.70E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable _Not Applicable
7/2/2013 5.91E-15 9.00E-14 2.25E-14 6.74E-16 2.00E-14 5.00E-15 7.85E-16 9.00E-13 2.25E-13 S.18E-15 6.00E-13 l.50E-13 Not Analyzed Not ApJ!licable Not'AppUcabl!!,
9/30/2013 2.68E-15 9.00E-14 2.25E-14 3.97E-16 2.00E-14 5.00E-15 1.04E-16 9.00E-13 .2.25E-13 6.13E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2013 l.60E-14 9.00E-14 2.25E-14 2.48E-16 2.00E-14 5.00E-15 1.05E-16 9.00E-13 2.25E-13 2.67E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2014 j!.92E-15 9.00E-14 2.25E-14 7.68E-16 2.00E-14 5.00E-15 l.SOE-15 9.00E-13 2.25E-13 1.61E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/30/2014 8.29E-15 9.00E-14 2.25E-14 5.35E-16 2.00E-14 5.00E-15 6.72E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicatile
9/30/2014 1.20E-14 9.00E-14 2.25E-14 5.54E-16 2.00E-14 5.00E-15 p.18E-16 9.00E-13 2.25E-13 1.38E-14 6.00E-13 l.SOE-13 01.00E-16 4.00E-15 l.OOE-15
12/29/2014 5.00_.-16 9.00E•l4 2.25E•14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9:j)O_E-1$" f2SE·l3, 2.30E-14 6.00E-13 1.SOE-13 8.00E-18 4:00E-15 l>;OOE-"15
3/30/2015 2.BOE-14 9.00E-14 2.25E-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.SOE-13 1.00E-18 4.00E-15 1.00E-15
6/29/2015 5.30E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 5.00E-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 ' 1.00E-15
9/28/2015 1.00E-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 1.lOE-14 6.00E-13 l.50E-13 2.00E-18 4.00E-15 1.00E-15
12/28/2015 8.40E-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 2.00E-14 6.00E-13 1.SOE-13 6.00E-18 4.00E-15 1.00E-15
3/28/2016 7.00E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 9.00E-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 1.00E-15
6/27/2016 1.20E-14 9.00E-14 2.25E-14 1.00E-16 2,00E-14 5.00E-15 6.00E-15 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 4.00E-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.50E-13 1.20E-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 1.50E-13 9.SOE-18 4.00E-15 1.00E-15
3/27/2017 8.lOE-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 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 2.25E-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 1.50E-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 l.90E-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 1.00E-15
12/26/2017 'i.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 1.50E-13 1.00E-17 4.00E-15 1.00E-15
9/28/1981
4/4/1983
10/1/1984
4/1/1986
9/9/1987
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iil
g-8/13/1990
3
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~8/10/1993
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TAB7
BHV-7 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-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=
ALARA Goal = . 2.25E-14 uCi/ml AlARAGoal = SE-13 uCi/ml AlARAGoal= 2.25E-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 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
12/29/2014 NS 9.00E-14 2.25E-14 NS 2.00E-14 5.00E-15 NS 9.00E-13 2.25E-13 NS 6.00E-13 1.50E-13 NS 4.00E-15 l.OOE-15
3/30/2015 6.00E-15 9.00E-14 2.2SE-14 8.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.50E-14 6.00E-13 1.SOE-13 7.00E-18 4.00E-15 l.OOE-15
6/29/2015 l.40E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 l.30E-15 9.00E-13 2.25E-13 1.70E-14 6.00E-13 l.50E-13 l.OOE-17 4.00E-15 l.OOE-15
9/28/2015 4.20E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 l.50E-13 6.00E-18 4.00E-15 l.OOE-15
12/28/2015 3.60E-16 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 l.50E-13 3.00E-18 4.00E-15 l.OOE-15
3/28/2016 ~.OOE-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E-13 l.70E-14 6.00E-13 l.50E-13 5.00E-18 4.00E-15 1.00E-15
6/27/2016 1.50E-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 l.50E-14 6.00E-13 l.50E-13 3.00E-18 4.00E-15 1.00E-15
9/27/2016 2.60E-15 9.00E-14 2.25E-14 l.70E-16 2.00E-14 5.00E-15 4.lOE-16 9.00E-13 2.25E-13 2.80E-15 6.00E-13 l.SOE-13 5.50E-18 4.00E-15 1.00E-15
12/27/2016 1.60E-15 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 2.50E-16 9.00E-13 2.25E-13 l.50E-14 6.00E-13 l.SOE-13 4.SOE-18 4.00E-15 1.00E-15
3/27/2017 3.30E-15 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.40E-15 9.00E-13 2.25E-13 l.40E-14 6.00E-13 1.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 1.50E-15 9.00E-13 2.25E-13 l.40E-14 6.00E-13 1.50E-13 2.00E-17 4.00E-15 1.00E-15
9/25/2017 1.20E-15 9.00E-14 2.25E-14 6.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.90E-14 6.00E-13 l.50E-13 4.00E-18 4.00E-15 l.OOE-15
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.SOE-13 l.OOE-17 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-SU Effluent ZE-14 uCi/ml BHV-8T230 Effluent 9E-13 uCi/ml BHV-SR Effluent 6E-13 uCi/ml BHV-8PB Effluent 4e-15 uCi/ml BHV-ST232
Concentration Concentration Concentration Concentration Concentration
limit= Limit= Limit= Limit= Limit= :
ALARAGoal= 2.25E-14 uCi/ml ALARAGoal = SE-13 uCi/ml ALARAGoal= 2.ZSE-13 uCl/ml ALARA Goal= l.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
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 EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
12/29/2014 4.00E-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 7,00E-17 9.00E-13 2.25E-13 9.90E-15 6.00E-13 l.50E-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 l.50E-13 l.OOE-16 4.00E-15 1.00E-15
6/29/2015 5.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 5.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 l.50E-13 7.00E-18 4,00E-15 l.OOE-15
9/28/2015 1.80E-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 l.50E·l3 3.00E-18 4.00E-15 1.00E-15
12/28/2015 2.lOE-16 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5.00E-15 9.00E-16 9.00E-13 7,25E-13 2.00E-14 6.00E-13 l.50E-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 :Z.25E-13 1.60E-14 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 ·1.ooe-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 2.25E-13 1.lOE-14 6.00E-13 l.50E-13 2.00E-18 '4,00E-15 l.OOE-15
9/27/2016 l.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 8.50E-17 9.00E-13 2.25E-13 l.40E-14 6.00E-13 1.50E-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 5.00E-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 1.50E-13 5.00E-19 4.00E-15 LOOE-15
9/25/2017 6.00E-16 9.00E-14 2.25E-14 8.00E-17 2.00E-14 5.00E-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 2.90E-15 9.00E-14 2.25E·14 5.00E-17 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 1.70E-14 6.00E-13 l.SOE-13 7.00E-18 4.00E-15 1.00E-15
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ATTACHMENT C
BHV AIR SAMPLING LABORATORY RESULTS AND QA/QC
EI\ERGY
, , 1l •n, ,I I
Trust our People. Trust our Data.
www.energylab.com
.Ill HIGH VOLUME AIR SAMPLING REPORT ~ I I
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-1 -
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-00 I nalu 6E-16
Third Quarter 2017 230Th 6E-17
Air Volume in mLs 226Ra IE-16
1.21E+l 1 210Pb 1.2E-14
232Tb 8E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
IE-17
2E-I7
4E-15
5E-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
MDCµCi/mL
NIA
IE-17
8E-18
4E-16
6E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
-
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 7E-01
IE-16 3E-14 2E-01
IE-16 9E-13 IE-02
2E-15 6E-13 2.0E+OO
NIA 6E-15 IE-01
Page 5 of 41
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 2017
Lab ID: C17090829-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium 9.5E-10 mg/L
Uranium, Activity 6.4E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.6E-15 uCi/mL
Lead 210 MDC 4.0E-16 uCi/mL
Radium 226 1.1E-16 uCi/mL
Radium 226 precision (±) 2.3E-17 uCi/mL
Radium 226 MDC 7.9E-18 uCi/mL
Thorium 230 6.0E-17 uCi/mL
Thorium 230 precision (±) 1.1E-17 uCi/mL
Thorium 230 MDC 9.9E-18 uCi/mL
Thorium 232 7.7E-18 uCi/mL
Thorium 232 precision (±) 4.8E-18 uCi/mL
Thorium 232 MDC 6.4E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1460 pCi/Filter
Lead 210 precision (±) 437 pCi/Filter
Lead 210 MDC 47.8 pCi/Filter
Radium 226 13.0 pCi/Filter
Radium 226 precision (±) 2.8 pCi/Filter
Radium 226 MDC 0.96 pCi/Filter
Thorium 230 7.2 pCi/Filter
Thorium 230 precision (±) 1.4 pCi/Filter
Thorium 230 MDC 1.2 pCi/Filter
Thorium 232 0.93 pCi/Filter
Thorium 232 precision (±) 0.58 pCi/Filter
Thorium 232 MDC 0.77 pCi/Filter
Uranium, Activity 77.3 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 1.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 2.0E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.3E-01 %
Thorium 232, EFF Year 3.0E-14 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: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date / By
SW6020 10/27/17 15:14 / eli-h
SW6020 10/27/17 15: 14 / eli-h
E909.0 10/05/17 23:27 / meh
E909.0 10/05/17 23:27 I meh
E909.0 10/05/17 23:27 I meh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16: 34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
RADCALC 11/05/1715:05 / sec
RADCALC 11/05/1715:05 / sec
RADCALC 11/05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/1715:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/1715:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/1715:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 3 of41
EN:RGY Trust our People. Trust our Data.
www.encrgylab.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 2017
Lab ID: C17090829-001
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
1.0E-16 uCi/mL
7.1E-01 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
120779600 L
Qualifiers RL
MCU
Report Date: 11 /07 /17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11/05/1715:09 / sec
11 /05/17 15:09 I sec
11 /05/17 15:09 I sec
11 /05/17 15:09 / sec
09/25/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 41
EN:RGY Trust our People. Trust our Data.
www.energylab.com
... • HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc .
t~ PROJECT: Quarterly Air Analysis ... SAMPLE ID: BHV-1
... REPORT DATE: January 25, 2018
Quarterillate Sampled Radionuclide Air Volume
CI8010137-001 na,u
Fourth Quarter 2017 230Th
Air Volume in mLs 226Ra
l.25E+II 210Pb
232Th
+LLD's are from NRC Reg. Guide 4.14
I .......
..
Concentration
µCi/mL
2.4E-15
SE-17
7E-17
1.SE-14
lE-17
II
•
Counting
Precision
µCi/mL
N/A
IE-17
2E-17
6E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thoriurn-232
Week for Radium-226
Day for Lead-210
I J
•
MDCµCi/mL
N/A
2E-17
IE-17
SE-16
2E-17
r I
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
II I. / ', I ..
I ,. •l ... ":•.
. -
s, I_
II
• I
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 2.6E+OO
IE-16 3E-14 2E-01
IE-16 9E-13 SE-03
2E-15 6E-13 3.IE+OO
NIA 6E-15 2E-01
Page 6 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium 3.5E-09 mg/L
Uranium, Activity 2.4E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.8E-14 uCi/mL
Lead 210 precision (±) 5.5E-15 uCi/mL
Lead 210 MDC 4.7E-16 uCi/mL
Radium 226 7.5E-17 uCi/mL
Radium 226 precision (±) 1.8E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 5.3E-17 uCi/mL
Thorium 230 precision (±) 1.0E-17 uCi/mL
Thorium 230 MDC 1.8E-17 uCi/mL
Thorium 232 1.0E-17 uCi/mL
Thorium 232 precision (±) 2.0E-18 uCi/mL
Thorium 232 MDC 1.5E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2300 pCi/Filter
Lead 210 precision (±) 689 pCi/Filter
Lead 210 MDC 58.6 pCi/Filter
Radium 226 9.4 pCi/Filter
Radium 226 precision (±) 2.2 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 6.6 pCi/Filter
Thorium 230 precision (±) 1.2 pCi/Filter
Thorium 230 MDC 2.3 pCi/Filter
Thorium 232 1.3 pCi/Filter
Thorium 232 precision (±) 0.25 pCi/Filter
Thorium 232 MDC 1.9 pCi/Filter
Uranium, Activity 295 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.1E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 8.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.8E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.7E-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
u
u
MCL/
RL QCL
1.1E-14
7.5E-21
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01 /18/18 13:20 / eli-h
SW6020 01 /18/18 13:20 / eli-h
E909.0 01/16/18 13:43 / meh
E909.0 01/16/18 13:43 / meh
E909.0 01/16/18 13:43 / meh
E903.0 01 /22/18 10:48 I arh
E903.0 01 /22/18 10:48 / arh
E903.0 01 /22/18 10:48 I arh
E908.0 01 /18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15: 37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 4 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-001
Client Sample ID: BHV-1
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 2.6E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
124930100
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 5 of 42
EI\ERGY
'' .,,,1, ) '
Trust our People. Trust our Data.
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r I l . 1 J-HIGH VOLUME AIR SAMPLING REPORT
• CU ENT: Energy Fuels Resources (USA) Inc
II>ROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-2
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
C 17090829-002 nalu 2E-16 NIA
Third Quarter 2017 230Th 2E-17 3E-18
Air Volume in rnLs 226Ra 5E-I7 JE-17
l.21E+l l 210Pb J.3E-14 4E-15
232Th 4E-I8 2E-I8
+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
...
' .. . ~
MDC µCi/mL
NIA
4E-18
8E-I8
4E-16
3E-I8
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
...
..
I",
•
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
JE-16 9E-14 2E-01
JE-16 3E-14 6E-02
JE-16 9E-13 5E-03
2E-I5 6E-13 2.2E+OO
NIA 6E-15 7E-02
Page 8 of41
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 ANAL YT I CAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Lab ID: C 17090829-002
Client Sample ID: BHV-2
Analyses Result Units
METALS, IN AIR
Uranium 2.3E-10 mg/L
Uranium, Activity 1.5E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.3E-14 uCi/mL
Lead 210 precision (±) 4.0E-15 uCi/mL
Lead 210 MDC 4.2E-16 uCi/mL
Radium 226 4.6E-17 uCi/mL
Radium 226 precision (±) 1.2E-17 uCi/mL
Radium 226 MDC 8.2E-18 uCi/mL
Thorium 230 1.8E-17 uCi/mL
Thorium 230 precision (±) 3.4E-18 uCi/mL
Thorium 230 MDC 4.2E-18 uCi/mL
Thorium 232 4.4E-18 uCi/mL
Thorium 232 precision (±) 2.3E-18 uCi/mL
Thorium 232 MDC 2.8E-18 uCi/mL
RADIONUCLIDES -lt:,I AIR -PER FILTER
Lead 210 1620 pCi/Filter
Lead 210 precision(±) 486 pCi/Filter
Lead 210 MDC 50.5 pCi/Filter
Radium 226 5.5 pCi/Filter
Radium 226 precision {±) 1.5 pCi/Filter
Radium 226 MDC 0.99 pCi/Filter
Thorium 230 2.1 pCi/Filter
Thorium 230 precision (±) 0.41 pCi/Filter
Thorium 230 MDC 0.50 pCi/Filter
Thorium 232 0.53 pCi/Filter
Thorium 232 precision (±) 0.27 pCi/Filter
Thorium 232 MDC 0.34 pCi/Filter
Uranium, Activity 18.4 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.2E+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 6.0E-02 %
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 3.0E-14 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 /07 /17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date / By
SW6020 10/27 /17 15:22 I eli-h
SW6020 10/27/17 15:22 I eli-h
E909.0 10/06/17 00: 12 / meh
E909.0 10/06/17 00: 12 / meh
E909.0 10/06/17 00:12 / meh
E903.0 10/15/17 12:24 I arh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 I cnh
E908.0 10/24/17 16:34 I cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 I cnh
E908.0 10/24/17 16:34 I cnh
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/1715:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/1715:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/1715:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 41
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 2017
Lab ID: C 17090829-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 1. 7E-01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
120742800
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 11 /07 /17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
FIELD 09/25/17 00:00 I***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 41
EN:RGY
, • ( • I ', 1 , ~ I
Trust our People. Trust our Data.
www.energylab.com
·~ r C: ·.-
HIGH VOLUME AIR SAMPLING REPORT
~ J
.L
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
SAMPLE ID: BHV-2
REPORT DATE: January 25, 2018
Quarterillate Sampled Concentration Radionuclide Air Volume µCi/mL
C!8010137-002 ""U 6E-16
Fourth Quarter 2017 230Th 3E-17
Air Volume in mLs 226Ra SE-17
l.25E+l l 2IOPb 2.0E-14
232Th 9E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
SE-18
IE-17
6E-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
MDCµCi/mL
NIA
IE-17
IE-17
SE-16
8E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
I~ T"
I • i.. I I :1 .
I .· . t. '1t,J ~ .. I '."J ~ ' iii, ·"' ,t •
~...: I ~ -1fi • I ~ • II,, II' I
Ill )-.....
,.. • • IL. --
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 7E-Ol
IE-16 3E-14 9E-02
IE-16 9E-13 6E-03
2E-15 6E-13 3.3E+OO
NIA 6E-15 IE-OJ
Page 9 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-002
Client Sample ID: BHV-2
Analyses Result Units
METALS, IN AIR
Uranium 9.3E-10 mg/L
Uranium, Activity 6.3E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 2.0E-14 uCi/mL
Lead 210 precision (±) 5.8E-15 uCi/mL
Lead 210 MDC 4.7E-16 uCi/mL
Radium 226 5.0E-17 uCi/mL
Radium 226 precision (±) 1.4E-17 uCi/mL
Radium 226 MDC 1.2E-17 uCi/mL
Thorium 230 2.8E-17 uCi/mL
Thorium 230 precision (±) 5.3E-18 uCi/mL
Thorium 230 MDC 1.1E-17 uCi/mL
Thorium 232 8.8E-18 uCi/mL
Thorium 232 precision (±) 1.7E-18 uCi/mL
Thorium 232 MDC 7.9E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2450 pCi/Filter
Lead 210 precision (±) 731 pCi/Filter
Lead 210 MDC 59.1 pCi/Filter
Radium 226 6.3 pCi/Filter
Radium 226 precision (±) 1.7 pCi/Filter
Radium 226 MDC 1.5 pCi/Filter
Thorium 230 3.5 pCi/Filter
Thorium 230 precision (±) 0.67 pCi/Filter
Thorium 230 MDC 1.4 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.21 pCi/Filter
Thorium 232 MDC 0.99 pCi/Filter
Uranium, Activity 78.5 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.3E+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 9.0E-02 %
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
1.1E-14
7.5E-21
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01 /18/18 13:24 / eli-h
SW6020 01 /18/18 13:24 / eli-h
E909.0 01/16/18 13:51 / meh
E909.0 01/16/18 13:51 / meh
E909.0 01/16/18 13:51 / meh
E903.0 01/22/18 10:48 / arh
E903.0 01/22/18 10:48 / arh
E903.0 01/22/18 10:48 / arh
E908.0 01/18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 7.0E-01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
125183000
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 8 of 42
EN:RGY
,.1-, 1111 I I ii' !
Trust our People. Trust our Data.
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-4
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-003 nalu 2.5E-15
Third Quarter 2017 230Th 3E-16
Air Volume in mLs 226Ra 2E-16
I.I IE+! I 210Pb 1.6E-14
232Th 4E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
5E-17
5E-17
5E-15
5E-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
MDCµCi/mL
NIA
9E-18
9E-18
5E-16
9E-18
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 2.8E+OO
IE-16 3E-14 9E-01
IE-16 9E-13 3E-02
2E-15 6E-13 2.6E+OO
NIA 6E-15 6E-02
Page 11 of 41
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 Report Date: 11/07/17
Project: 3rd Quarter Air 2017 Collection Date: 09/25/17
Lab ID: C 17090829-003 Date Received: 09/27/17
Client Sample ID: BHV-4 Matrix: Filter
MCL/
Analyses Result Units Qualifiers RL QCL Method Analysis Date / By
METALS, IN AIR
Uranium 3.7E-09 mg/L 1.5E-10 SW6020 10/27/17 15:24 / eli-h
Uranium, Activity 2.5E-15 uCi/mL 1.0E-16 SW6020 10/27/17 15:24 / eli-h
RADIONUCLIDES -IN AIR
Lead 210 1.6E-14 uCi/mL E909.0 10/06/17 00:24 I meh
Lead 210 precision (±) 4.7E-15 uCi/mL E909.0 10/06/17 00:24 I meh
Lead 210 MDC 4.6E-16 uCi/mL E909.0 10/06/17 00:24 I meh
Radium 226 2.4E-16 uCi/mL E903.0 10/15/17 12:24 / arh
Radium 226 precision (±) 5.0E-17 uCi/mL E903.0 10/15/17 12:24 / arh
Radium 226 MDC 9.1E-18 uCi/mL E903.0 10/15/17 12:24 / arh
Thorium 230 2.6E-16 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 230 precision (±) 4.9E-17 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 230 MDC 8.6E-18 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 232 3.6E-18 uCi/mL u E908.0 10/24/17 16: 34 / cnh
Thorium 232 precision (±) 5.0E-18 uCi/mL E908.0 10/24/17 16: 34 / cnh
Thorium 232 MDC 9.1E-18 uCi/mL E908.0 10/24/17 16:34 / cnh
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1760 pCi/Filter RADCALC 11/05/17 15:05 / sec
Lead 210 precision (±) 528 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Lead 210 MDC 51.6 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Radium 226 26.9 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Radium 226 precision (±) 5.5 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Radium 226 MDC 1.0 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Thorium 230 28.8 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Thorium 230 precision (±) 5.5 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Thorium 230 MDC 0.95 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Thorium 232 0.40 pCi/Filter u RADCALC 11/05/17 15:05 / sec
Thorium 232 precision (±) 0.56 pCi/Filter RADCALC 11/05/17 15:05 / sec
Thorium 232 MDC 1.0 pCi/Filter RADCALC 11/05/17 15:05 / sec
Uranium, Activity 277 pCi/Filter 0.20 RADCALC 11/05/17 15:05 / sec
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.6E+OO % RADCALC 11/05/17 15:09 / sec
Lead 210, EFF Day 6.0E-13 uCi/mL RADCALC 11 /05/17 15:09 / sec
Lead 210, LLD 2.0E-15 uCi/mL RADCALC 11 /05/17 15:09 / sec
Radium 226, % of EFF 3.0E-02 % RADCALC 11 /05/17 15:09 / sec
Radium 226, EFF Week 9.0E-13 uCi/mL RADCALC 11 /05/17 15:09 / sec
Radium 226, LLD 1.0E-16 uCi/mL RADCALC 11 /05/17 15:09 / sec
Thorium 230, % of EFF 8.6E-01 % RADCALC 11 /05/17 15:09 / sec
Thorium 230, EFF Year 3.0E-14 uCi/mL RADCALC 11 /05/17 15:09 / sec
Thorium 230, LLD 1.0E-16 uCi/mL RADCALC 11/05/17 15:09 / sec
Thorium 232, % of EFF 6.0E-02 % RADCALC 11 /05/17 15:09 / sec
Thorium 232, EFF Year 3.0E-14 uCi/mL RADCALC 11 /05/17 15:09 / sec
Report RL -Analyte reporting limit. MCL -Maximum contaminant level.
Definitions: QCL -Quality control limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration U -Not detected at minimum detectable concentration
Page 9 of 41
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 2017
Lab ID: C 17090829-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 2.8E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
111457200
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
FIELD 09/25/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 41
EN:RGY
, t ,,•, , , I,
Trust our People. Trust our Data.
www.energylab.com
HIGH VOLUME AIR SAMPLING REPORT
• 11 CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
'I SAMPLE ID: BHV-4
. .
REPORT DATE: January 25, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C18010137-003 natu 1.0E-14
Fourth Quarter 2017 230111 2E-16
Air Volume in mLs 226Ra 2E-16
I.25E+l l 210pb 2.2E-14
232111 2E-17
+LLD's are from NRC Reg. Guide 4.14
I .
Counting
Precision
µCi/mL
NIA
4E-17
3E-17
6E-15
3E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, 111orium-232
Week for Radium-226
Day for Lead-210
MDCµCi/mL
NIA
lE-17
lE-17
SE-16
lE-17
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
1, I
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
lE-16 9E-14 1.IE+Ol
lE-16 3E-14 7E-OI
lE-16 9E-13 2E-02
2E-15 6E-13 3.6E+OO
NIA 6E-15 3E-01
Page 12 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-003
Client Sample ID: BHV-4
Analyses Result Units
METALS, IN AIR
Uranium 1.5E-08 mg/L
Uranium, Activity 1.0E-14 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 2.2E-14 uCi/mL
Lead 210 precision (±) 6.4E-15 uCi/mL
Lead 210 MDC 5.0E-16 uCi/mL
Radium 226 1.6E-16 uCi/mL
Radium 226 precision (±) 3.4E-17 uCi/mL
Radium 226 MDC 1.3E-17 uCi/mL
Thorium 230 2.1E-16 uCi/mL
Thorium 230 precision (±) 4.0E-17 uCi/mL
Thorium 230 MDC 1.4E-17 uCi/mL
Thorium 232 1.6E-17 uCi/mL
Thorium 232 precision (±) 3.1 E-18 uCi/mL
Thorium 232 MDC 1.2E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2690 pCi/Filter
Lead 210 precision (±) 803 pCi/Filter
Lead 210 MDC 63.0 pCi/Filter
Radium 226 19.6 pCi/Filter
Radium 226 precision (±) 4.2 pCi/Filter
Radium 226 MDC 1.6 pCi/Filter
Thorium 230 26.6 pCi/Filter
Thorium 230 precision (±) 5.1 pCi/Filter
Thorium 230 MDC 1.8 pCi/Filter
Thorium 232 2.0 pCi/Filter
Thorium 232 precision (±) 0.38 pCi/Filter
Thorium 232 MDC 1.5 pCi/Filter
Uranium, Activity 1280 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.6E+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 7.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.7E-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
5.5E-14
3.7E-20
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01 /04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01/18/18 16:38 / eli-h
SW6020 01 /18/18 16:38 / eli-h
E909.0 01 /16/18 13:59 / meh
E909.0 01/16/18 13:59 / meh
E909.0 01/16/18 13:59 / meh
E903.0 01/22/18 10:48 / arh
E903.0 01/22/18 10:48 / arh
E903.0 01/22/18 10:48 / arh
E908.0 01/18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/1815:37 /sec
RADCALC 01/23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 42
EI\ERGY 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
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Lab ID: C 18010137-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 1.1E+01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
124902900
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 11 of 42
EI\ERGY
·. ), ,,1,,1,•
Trust our People. Trust our Data.
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r I HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels'Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-5
REPORT DATE: November 7, 2017
Quarterillate Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-004 natu 2.7E-15
Third Quarter 2017 230Th 2E-16
Air Volume in mLs 226Ra 2E-16
l.21E+l 1 210Pb l.6E-14
232Th 4E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
3E-17
3E-17
SE-15
IE-17
*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
MDCµCi/mL
NIA
2E-17
8E-18
SE-16
2E-17
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
..
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 3.0E+OO
IE-16 3E-14 6E-01
IE-16 9E-13 2E-02
2E-15 6E-13 2.7E+OO
NIA 6E-15 6E-02
Page 14 of 41
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Lab ID: C 17090829-004
Client Sample ID: BHV-5
Analyses Result Units
METALS, IN AIR
Uranium 3.9E-09 mg/L
Uranium, Activity 2.7E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.6E-14 uCi/mL
Lead 210 precision (±) 4.8E-15 uCi/mL
Lead 210 MDC 4.5E-16 uCi/mL
Radium 226 1.6E-16 uCi/mL
Radium 226 precision (±) 3.3E-17 uCi/mL
Radium 226 MDC 8.2E-18 uCi/mL
Thorium 230 1.8E-16 uCi/mL
Thorium 230 precision (±) 3.4E-17 uCi/mL
Thorium 230 MDC 2.2E-17 uCi/mL
Thorium 232 3.5E-18 uCi/mL
Thorium 232 precision (±) 1.0E-17 uCi/mL
Thorium 232 MDC 1.9E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1950 pCi/Filter
Lead 210 precision(±) 584 pCi/Filter
Lead 210 MDC 54.9 pCi/Filter
Radium 226 19.5 pCi/Filter
Radium 226 precision (±) 4.0 pCi/Filter
Radium 226 MDC 0.99 pCi/Filter
Thorium 230 21 .8 pCi/Filter
Thorium 230 precision (±) 4.1 pCi/Filter
Thorium 230 MDC 2.6 pCi/Filter
Thorium 232 0.43 pCi/Filter
Thorium 232 precision (±) 1.2 pCi/Filter
Thorium 232 MDC 2.3 pCi/Filter
Uranium, Activity 322 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.7E+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 6.0E-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 3.0E-14 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
u
u
MCU
RL QCL
1.5E-10
1.0E-16
0.20
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date I By
SW6020 10/27 /17 15:26 / eli-h
SW6020 10/27 /17 15:26 / eli-h
E909.0 10/06/17 00:35 / meh
E909.0 10/06/17 00:35 I meh
E909.0 10/06/17 00:35 I meh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16: 34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16: 34 / cnh
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/1715:09/sec
RADCALC 11/05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/1715:09 / sec
RADCALC 11/05/17 15:09 I sec
RADCALC 11 /05/17 15:09 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 12 of 41
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 2017
Lab ID: C 17090829-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 3.0E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
120795800
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 11/07/17
Collection Date: 09/25/17
Date Received: 09/27 /17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
FIELD 09/25/17 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 13 of 41
EI\ERGY
' ' ' ,< 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
.. ' . HIGH VOLUME AIR SAMPLING REPORT • I I
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
SAMPLE ID: BHV .5 . .
REPORT DATE: January 25, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C18010137-004 ""U 1.4E-14
Fourth Quarter 2017 230Th 4E-16
Air Volume in mLs 226Ra 3E-16
l.24E+ll 210Pb 1.6E-14
232Th IE-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
8E-17
7E-17
SE-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
,-_ .. "
....... 'I
,,, I 1.,:· J r .. lJ
• I ' ,
L.L.D.+ Effluent Cone.* % Effluent MDC µCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 l.5E+OI
SE-17 IE-16 3E-14 IE+OO
IE-17 IE-16 9E-13 4E-02
4E-16 2E-15 6E-13 2.6E+OO
4E-17 NIA 6E-15 2E-01
Page 15 of 42
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 8&&.&86.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 01/25/18
Project: Quarterly Air Analysis Collection Date: 12/26/17
Lab ID: C18010137-004 Date Received: 01 /04/18
Client Sample ID: BHV-5 Matrix: Filter
MCU
Analyses Result Units Qualifiers RL QCL Method Analysis Date / By
METALS, IN AIR
Uranium 2.0E-08 mg/L 5.5E-14 SW6020 01 /18/18 16:42 / eli-h
Uranium, Activity 1.4E-14 uCi/mL 3.8E-20 SW6020 01/18/18 16:42 / eli-h
RADIONUCLIDE$ -IN AIR
Lead 210 1.6E-14 uCi/mL E909.0 01/16/18 14:06 / meh
Lead 210 precision (±) 4.7E-15 uCi/mL E909.0 01 /16/18 14:06 I meh
Lead 210 MDC 4.4E-16 uCi/mL E909.0 01 /16/18 14:06 I meh
Radium 226 3.5E-16 uCi/mL E903.0 01 /22/18 13:51 / arh
Radium 226 precision (±) 7.0E-17 uCi/mL E903.0 01/22/18 13:51 / arh
Radium 226 MDC 1.2E-17 uCi/mL E903.0 01 /22/18 13:51 / arh
Thorium 230 4.0E-16 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 230 precision (±) 7.7E-17 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 230 MDC 5.4E-17 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 232 1.2E-17 uCi/mL u E908.0 01 /18/18 09:36 / cnh
Thorium 232 precision (±) 2.4E-18 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 232 MDC 4.3E-17 uCi/mL E908.0 01/18/18 09:36 / cnh
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1970 pCi/Filter RADCALC 01/23/18 15:08 / sec
Lead 210 precision (±) 589 pCi/Filter RADCALC 01 /23/18 15:08 I sec
Lead 210 MDC 54.3 pCi/Filter RADCALC 01/23/18 15:08 / sec
Radium 226 43.3 pCi/Filter RADCALC 01 /23/18 15:08 I sec
Radium 226 precision (±) 8.7 pCi/Filter RADCALC 01 /23/18 15:08 I sec
Radium 226 MDC 1.5 pCi/Filter RADCALC 01/23/18 15:08 I sec
Thorium 230 50.1 pCi/Filter RADCALC 01/23/18 15:08 / sec
Thorium 230 precision (±) 9.5 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Thorium 230 MDC 6.7 pCi/Filter RADCALC 01/23/18 15:08 / sec
Thorium 232 1.5 pCi/Filter u RADCALC 01 /23/18 15:08 / sec
Thorium 232 precision (±) 0.30 pCi/Filter RADCALC 01/23/18 15:08 / sec
Thorium 232 MDC 5.3 pCi/Filter RADCALC 01 /23/18 15:08 I sec
Uranium, Activity 1700 pCi/Filter 0.20 RADCALC 01 /23/18 15:08 / sec
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.6E+OO % RADCALC 01/23/18 15:37 / sec
Lead 210, EFF Day 6.0E-13 uCi/mL RADCALC 01 /23/18 15:37 / sec
Lead 210, LLD 2.0E-15 uCi/mL RADCALC 01/23/18 15:37 / sec
Radium 226, % of EFF 4.0E-02 % RADCALC 01/23/18 15:37 / sec
Radium 226, EFF Week 9.0E-13 uCi/mL RADCALC 01/23/18 15:37 / sec
Radium 226, LLD 1.0E-16 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 230, % of EFF 1.3E+OO % RADCALC 01 /23/18 15:37 / sec
Thorium 230, EFF Year 3.0E-14 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 230, LLD 1.0E-16 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 232, % of EFF 2.0E-01 % RADCALC 01/23/18 15:37 / sec
Thorium 232, EFF Year 6.0E-15 uCi/mL RADCALC 01 /23/18 15:37 / sec
Report RL -Analyte reporting limit. MCL -Maximum contaminant level.
Definitions: QCL -Quality control limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration U -Not detected at minimum detectable concentration
Page 13 of 42
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: Quarterly Air Analysis
Lab ID: C18010137-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 1.5E+01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
124331800
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date I By
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 I sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 14 of 42
E1'ERGY
• I , ( ! , i, >I~
Trust our People. Trust our Data.
www.energylab.com
HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-6
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-005 nalu 3.5E-15
Third Quarter 2017 230Th 2E-16
Air Volume in mLs 226Ra IE-16
l.16E+l l z10Pb l.9E-14
232Th IE-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
4E-17
2E-17
6E-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
MDCµCi/mL
NIA
2E-17
SE-18
5E-16
2E-17
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 3.9E+OO
IE-16 3E-14 7E-Ol
IE-16 9E-13 IE-02
2E-15 6E-13 3.2E+OO
NIA 6E-15 2E-Ol
Page 17 of 41
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
LA BORA TORY ANAL YT I CAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 11/07/17
Project: 3rd Quarter Air 2017 Collection Date: 09/25/17
Lab ID: C 17090829-005 Date Received: 09/27/17
Client Sample ID: BHV-6 Matrix: Filter
MCU
Analyses Result Units Qualifiers RL QCL Method Analysis Date / By
METALS, IN AIR
Uranium 5.1 E-09 mg/L 1.5E-10 SW6020 10/27 /17 15:28 / eli-h
Uranium, Activity 3.5E-15 uCi/mL 1.0E-16 SW6020 10/27 /17 15:28 / eli-h
RADIONUCLIDES -IN AIR
Lead 210 1.9E-14 uCi/mL E909.0 10/06/17 00:44 I meh
Lead 210 precision (±) 5.7E-15 uCi/mL E909.0 10/06/17 00:44 / meh
Lead 210 MDC 5.1E-16 uCi/mL E909.0 10/06/17 00:44 / meh
Radium 226 1.0E-16 uCi/mL E903.0 10/15/17 12:24 / arh
Radium 226 precision (±) 2.3E-17 uCi/mL E903.0 10/15/17 12:24 / arh
Radium 226 MDC 8.4E-18 uCi/mL E903.0 10/15/17 12:24 / arh
Thorium 230 2.0E-16 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 230 precision (±) 3.BE-17 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 230 MDC 2.3E-17 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 232 1.1 E-17 uCi/mL u E908.0 10/24/17 16:34 / cnh
Thorium 232 precision (±) 2.1 E-18 uCi/mL E908.0 10/24/17 16:34 / cnh
Thorium 232 MDC 1.BE-17 uCi/mL E908.0 10/24/17 16: 34 / cnh
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2190 pCi/Filter RADCALC 11/05/17 15:05 / sec
Lead 210 precision (±) 655 pCi/Filter RADCALC 11/05/1715:05 / sec
Lead 210 MDC 59.1 pCi/Filter RADCALC 11/05/17 15:05 / sec
Radium 226 12.1 pCi/Filter RADCALC 11 /05/17 15:05 I sec
Radium 226 precision (±) 2.7 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Radium 226 MDC 0.97 pCi/Filter RADCALC 11/05/17 15:05 / sec
Thorium 230 23.0 pCi/Filter RADCALC 11/05/17 15:05 / sec
Thorium 230 precision (±) 4.4 pCi/Filter RADCALC 11/05/17 15:05 / sec
Thorium 230 MDC 2.6 pCi/Filter RADCALC 11 /05/17 15:05 / sec
Thorium 232 1.3 pCi/Filter u RADCALC 11 /05/17 15:05 / sec
Thorium 232 precision (±) 0.24 pCi/Filter RADCALC 11/05/1715:05 / sec
Thorium 232 MDC 2.1 pCi/Filter RADCALC 11/05/17 15:05 / sec
Uranium, Activity 402 pCi/Filter 0.20 RADCALC 11 /05/17 15:05 / sec
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.2E+OO % RADCALC 11/05/1715:09/sec
Lead 210, EFF Day 6.0E-13 uCi/mL RADCALC 11/05/17 15:09 / sec
Lead 210, LLD 2.0E-15 uCi/mL RADCALC 11 /05/17 15:09 / sec
Radium 226, % of EFF 1.0E-02 % RADCALC 11 /05/17 15:09 / sec
Radium 226, EFF Week 9.0E-13 uCi/mL RADCALC 11 /05/17 15:09 I sec
Radium 226, LLD 1.0E-16 uCi/mL RADCALC 11/05/1715:09 / sec
Thorium 230, % of EFF 6.6E-01 % RADCALC 11/05/17 15:09 / sec
Thorium 230, EFF Year 3.0E-14 uCi/mL RADCALC 11/05/17 15:09 / sec
Thorium 230, LLD 1.0E-16 uCi/mL RADCALC 11 /05/17 15:09 I sec
Thorium 232, % of EFF 1.BE-01 % RADCALC 11/05/1715:09 / sec
Thorium 232, EFF Year 3.0E-14 uCi/mL RADCALC 11/05/17 15:09 / sec
Report RL -Analyte reporting limit. MCL -Maximum contaminant level.
Definitions: QCL -Quality control limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration U -Not detected at minimum detectable concentration
Page 15 of41
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 2017
Lab ID: C 17090829-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 3.9E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
115857700
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
FIELD 09/25/17 00:00 I•••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 16 of41
EI\ERGY
\ , I > '/\ , ii It
Trust our People. Trust our Data.
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
SAMPLE ID: BHV-6
REPORT DATE: January 25, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl8010137-005 ""'U 1.4E-14
Fourth Quarter 2017 23oTh 4E-16
Air Volume in mLs 226Ra lE-17
l.24E+ll 210Pb 2.0E-14
232Th lE-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
7E-17
3E-18
6E-15
3E-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
MDCµCi/mL
NIA
4E-17
lE-18
5E-16
3E-17
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
•
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
lE-16 9E-14 1.6E+Ol
lE-16 3E-14 lE+OO
lE-16 9E-13 2E-03
2E-15 6E-13 3.3E+OO
NIA 6E-15 2E-01
Page 18 of 42
EN:RGY " Trust our People. Trust our Data.
www energylab com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WV 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Lab ID: C18010137-005
Client Sample ID: BHV-6
Analyses Result Units
METALS, IN AIR
Uranium 2.1 E-08 mg/L
Uranium, Activity 1.4E-14 uCi/ml
RADIONUCLIDE$ -IN AIR
Lead 210 2.0E-14 uCi/mL
Lead 210 precision (±) 5.9E-15 uCi/mL
Lead 210 MDC 4.7E-16 uCi/mL
Radium 226 1.4E-17 uCi/mL
Radium 226 precision (±) 2.9E-18 uCi/mL
Radium 226 MDC 1.1E-18 uCi/mL
Thorium 230 3.9E-16 uCi/mL
Thorium 230 precision (±) 7.5E-17 uCi/mL
Thorium 230 MDC 4.0E-17 uCi/mL
Thorium 232 1.4E-17 uCi/mL
Thorium 232 precision (±) 2.7E-18 uCi/mL
Thorium 232 MDC 3.0E-17 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 2460 pCi/Filter
Lead 210 precision(±) 736 pCi/Filter
Lead 210 MDC 58.1 pCi/Filter
Radium 226 1.7 pCi/Filter
Radium 226 precision (±) 0.36 pCi/Filter
Radium 226 MDC 0.13 pCi/Filter
Thorium 230 48.9 pCi/Filter
Thorium 230 precision (±) 9.3 pCi/Filter
Thorium 230 MDC 5.0 pCi/Filter
Thorium 232 1.7 pCi/Filter
Thorium 232 precision (±) 0.33 pCi/Filter
Thorium 232 MDC 3.7 pCi/Filter
Uranium, Activity 1780 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.3E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 2.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.3E+OO %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.3E-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
u
u
MCL/
RL QCL
5.6E-14
3.8E-20
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01 /18/18 16:45 / eli-h
SW6020 01 /18/18 16:45 / eli-h
E909.0 01/16/18 14:15 / meh
E909.0 01/16/18 14:15 / meh
E909.0 01/16/18 14:15 / meh
E903.0 01/22/18 13:51 / arh
E903.0 01 /22/18 13:51 / arh
E903.0 01 /22/18 13:51 / arh
E908.0 01 /18/18 09: 36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15: 37 I sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 16 of 42
EN:RGY ;
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www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 871.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Lab ID: C18010137-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 1.6E+01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
123936500
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 17 of 42
EN:RGY
,\•11 L" ,•1
Trust our People. Trust our Data.
www.energylab.com
HIGH VOLUME AIR SAMPLING REPORT .,
' ,., CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-7
REPORT DATE: November 7, 2017
Quarterffiate Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-006 ""u 1.2E-15
Third Quarter 2017 230Th 6E-17
Air Volume in mLs 226Ra IE-16
1.21E+l 1 210Pb 1.9E-14
232Th 4E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
IE-17
2E-17
6E-15
3E-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
MDCµCi/mL
NIA
SE-18
8E-18
SE-16
4E-18
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
L.L.D.+ Effluent Cone.* % Eftluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 1.4E+OO
lE-16 3E-14 2E-Ol
IE-16 9E-13 IE-02
2E-15 6E-13 3.IE+OO
NIA 6E-15 7E-02
Page 20 of41
EN:RGY Trust our People. Trust our Data.
www.energylah com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Lab ID: C 17090829-006
Client Sample ID: BHV-7
Analyses Result Units
METALS, IN AIR
Uranium 1.8E-09 mg/L
Uranium, Activity 1.2E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.9E-14 uCi/mL
Lead 210 precision (±) 5.6E-15 uCi/mL
Lead 210 MDC 5.0E-16 uCi/mL
Radium 226 1.1E-16 uCi/mL
Radium 226 precision (±) 2.4E-17 uCi/mL
Radium 226 MDC 7.8E-18 uCi/mL
Thorium 230 5.6E-17 uCi/mL
Thorium 230 precision (±) 1.1E-17 uCi/mL
Thorium 230 MDC 4.8E-18 uCi/mL
Thorium 232 4.4E-18 uCi/mL
Thorium 232 precision (±) 2.7E-18 uCi/mL
Thorium 232 MDC 3.8E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2260 pCi/Filter
Lead 210 precision(±) 675 pCi/Filter
Lead 210 MDC 60.2 pCi/Filter
Radium 226 13.9 pCi/Filter
Radium 226 precision (±) 2.9 pCi/Filter
Radium 226 MDC 0.95 pCi/Filter
Thorium 230 6.8 pCi/Filter
Thorium 230 precision (±) 1.3 pCi/Filter
Thorium 230 MDC 0.58 pCi/Filter
Thorium 232 0.54 pCi/Filter
Thorium 232 precision (±) 0.32 pCi/Filter
Thorium 232 MDC 0.46 pCi/Filter
Uranium, Activity 149 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.1E+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 1.9E-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 3.0E-14 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: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date / By
SW6020 10/27/17 15:30 / eli-h
SW6020 10/27/17 15:30 / eli-h
E909.0 10/06/17 00:53 / meh
E909.0 10/06/17 00:53 / meh
E909.0 10/06/17 00:53 / meh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 / arh
E908.0 10/24/1716:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of 41
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: 3rd Quarter Air 2017
Lab ID: C 17090829-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 1.4E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
121072400
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
FIELD 09/25/17 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of 41
EI\ERGY
, .. r 1 , rm·· 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
, . • ,... I HIGH VOLUME AIR SAMPLING REPORT . ' ._ • ... • J •
I I
~
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis ,.
I, SAMPl'..E ID: BHV-7 ·•
REPORT DATE: January 25, 2018 i "
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl8010137-006 natu 4.6E-15
Fourth Quarter 2017 230Th 2E-16
Air Volume in mLs 226Ra IE-16
l.25E+l I z10Pb 2.lE-14
232Th lE-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
3E-17
3E-17
6E-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
(
t I i . ! T I •
I ... I' T~ . ' . -. •
II "
~ -
I I ... 1
L.L.D.+ Effluent Cone.* % Effluent MDC µCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 5.IE+OO
3E-18 IE-16 3E-14 5E-01
IE-17 lE-16 9E-13 2E-02
5E-16 2E-15 6E-13 3.4E+OO
3E-18 NIA 6E-15 2E-Ol
Page 21 of 42
EI\ERGY
' ' '
Trust our People. Trust our Data.
www.energylab.mm
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Lab ID: C18010137-006
Client Sample ID: BHV-7
Analyses Result Units
METALS, IN AIR
Uranium 6.8E-09 mg/L
Uranium, Activity 4.6E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 2.1E-14 uCi/mL
Lead 210 precision (±) 6.2E-15 uCi/mL
Lead 210 MDC 5.0E-16 uCi/mL
Radium 226 1.4E-16 uCi/mL
Radium 226 precision (±) 3.1 E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.5E-16 uCi/mL
Thorium 230 precision (±) 2.9E-17 uCi/mL
Thorium 230 MDC 3.2E-18 uCi/mL
Thorium 232 1.3E-17 uCi/mL
Thorium 232 precision (±) 2.4E-18 uCi/mL
Thorium 232 MDC 2.9E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2580 pCi/Filter
Lead 210 precision (±) 770 pCi/Filter
Lead 210 MDC 61.9 ,PCi/Filter
Radium 226 17.7 pCi/Filter
Radium 226 precision (±) 3.8 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 19.1 pCi/Filter
Thorium 230 precision (±) 3.6 pCi/Filter
Thorium 230 MDC 0.40 pCi/Filter
Thorium 232 1.6 pCi/Filter
Thorium 232 precision (±) 0.30 pCi/Filter
Thorium 232 MDC 0.36 pCi/Filter
Uranium, Activity 577 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 3.4E+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 5.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.1 E-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
1.1E-14
7.5E-21
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01 /18/18 13:39 / eli-h
SW6020 01 /18/18 13:39 / eli-h
E909.0 01/16/18 14:22 I meh
E909.0 01/16/18 14:22 I meh
E909.0 01/16/18 14:22 I meh
E903.0 01/22/18 13:51 / arh
E903.0 01/22/18 13:51 / arh
E903.0 01/22/18 13:51 / arh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 I cnh
E908.0 01/18/18 09:36 I cnh
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01/23/1815:37 / sec
RADCALC 01 /23/18 15: 37 / sec
RADCALC 01 /23/18 15: 37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 I sec
RADCALC 01/23/18 15:37 I sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of 42
EI\ERGY
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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: Quarterly Air Analysis
Lab ID: C18010137-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 5.1E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
124914400
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
FIELD 12/26/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 20 of 42
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: BHV-8
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 17090829-007 natu 6E-16
Third Quarter 2017 23°'fh 8E-17
Air Volume in mLs 226Ra IE-16
l.21E+l I 21Dpb 1.2E-14
232Th 2E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
IE-17
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
MDCµCi/mL
NIA
2E-18
8E-18
4E-16
2E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 6E-01
IE-16 3E-14 3E-01
IE-16 9E-13 IE-02
2E-15 6E-13 2.0E+OO
NIA 6E-15 4E-02
Page 23 of 41
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: 3rd Quarter Air 2017
Lab ID: C 17090829-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium 8.2E-10 mg/L
Uranium, Activity 5.5E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.6E-15 uCi/mL
Lead 210 MDC 4.0E-16 uCi/mL
Radium 226 1.1E-16 uCi/mL
Radium 226 precision (±) 2.4E-17 uCi/mL
Radium 226 MDC 7.9E-18 uCi/mL
Thorium 230 7.7E-17 uCi/mL
Thorium 230 precision (±) 1.5E-17 uCi/mL
Thorium 230 MDC 2.1 E-18 uCi/mL
Thorium 232 2.2E-18 uCi/mL
Thorium 232 precision (±) 1.3E-18 uCi/mL
Thorium 232 MDC 1.7E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1480 pCi/Filter
Lead 210 precision(±) 442 pCi/Filter
Lead 210 MDC 48.8 pCi/Filter
Radium 226 13.6 pCi/Filter
Radium 226 precision (±) 2.9 pCi/Filter
Radium 226 MDC 0.96 pCi/Filter
Thorium 230 9.3 pCi/Filter
Thorium 230 precision (±) 1.8 pCi/Filter
Thorium 230 MDC 0.26 pCi/Filter
Thorium 232 0.26 pCi/Filter
Thorium 232 precision (±) 0.15 pCi/Filter
Thorium 232 MDC 0.20 pCi/Filter
Uranium, Activity 67.0 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 1.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 2.6E-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 3.0E-14 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 /07 /17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date / By
SW6020 10/27/17 15:32 / eli-h
SW6020 10/27/1715:32 / eli-h
E909.0 10/06/17 01 :02 / meh
E909.0 10/06/17 01 :02 / meh
E909.0 10/06/17 01 :02 / meh
E903.0 10/15/17 12:24 I arh
E903.0 10/15/17 12:24 / arh
E903.0 10/15/17 12:24 I arh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E90B.O 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11/05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/1715:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/1715:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 21 of41
EI\ERGY
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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 2017
Lab ID: C 17090829-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD 1.0E-16
Uranium Natural, % of EFF 6.2E-01
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
120772700
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 11/05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
FIELD 09/25/17 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of41
EN:RGY
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l HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
SAMPLE ID: BHV-8
REPORT DATE: January 25, 2018
Quarterffiate Sampled Concentration Radionuclide Air Volume µCi/mL
Cl8010137-007 natu 2.9E-15
Fourth Quarter 2017 23oTh SE-17
Air Volume in mLs 226Ra SE-17
J.25E+l I 210Pb J.7E-14
232Th 7E-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
9E-18
lE-17
SE-15
3E-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
MDC µCi/mL
NIA
4E-18
lE-17
SE-16
3E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
T
,_
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 3.2E+OO
IE-16 3E-14 2E-01
lE-16 9E-13 SE-03
2E-15 6E-13 2.9E+OO
NIA 6E-15 IE-01
Page 24 of 42
EI\ERGY
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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: Quarterly Air Analysis
Lab ID: C18010137-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium 4.2E-09 mg/L
Uranium, Activity 2.9E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.7E-14 uCi/mL
Lead 210 precision(±) 5.2E-15 uCi/mL
Lead 210 MDC 4.5E-16 uCi/mL
Radium 226 4.6E-17 uCi/mL
Radium 226 precision (±) 1.5E-17 uCi/mL
Radium 226 MDC 1.4E-17 uCi/mL
Thorium 230 4.6E-17 uCi/mL
Thorium 230 precision (±) 8.8E-18 uCi/mL
Thorium 230 MDC 3.6E-18 uCi/mL
Thorium 232 7.1E-18 uCi/mL
Thorium 232 precision (±) 3.1 E-18 uCi/mL
Thorium 232 MDC 3.3E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2180 pCi/Filter
Lead 210 precision(±) 651 pCi/Filter
Lead 210 MDC 56.5 pCi/Filter
Radium 226 5.7 pCi/Filter
Radium 226 precision (±) 1.8 pCi/Filter
Radium 226 MDC 1.8 pCi/Filter
Thorium 230 5.8 pCi/Filter
Thorium 230 precision (±) 1.1 pCi/Filter
Thorium 230 MDC 0.45 pCi/Filter
Thorium 232 0.88 pCi/Filter
Thorium 232 precision (±) 0.39 pCi/Filter
Thorium 232 MDC 0.41 pCi/Filter
Uranium, Activity 358 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.9E+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 1.5E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.2E-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
1.1E-14
7.5E-21
0.20
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01 /04/18
Matrix: Filter
Method Analysis Date / By
SW6020 01/18/18 13:43 / eli-h
SW6020 01/18/18 13:43 / eli-h
E909.0 01 /16/18 14:29 I meh
E909.0 01/16/18 14:29 / meh
E909.0 01/16/18 14:29 / meh
E903.0 01/22/18 13:51 / arh
E903.0 01 /22/18 13:51 / arh
E903.0 01/22/18 13:51 / arh
E908.0 01 /18/18 09:36 I cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01/18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
E908.0 01 /18/18 09:36 / cnh
RADCALC 01 /23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 I sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01 /23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01 /23/18 15:08 I sec
RADCALC 01/23/18 15:08 / sec
RADCALC 01/23/1815:08 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 I sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01 /23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of 42
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Lab ID: C18010137-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 3.2E+OO
Uranium Natural, EFF Year 9.0E-14
Uranium Natural, LLD 1.0E-16
CLIENT PROVIDED FIELD PARAMETERS
Air Filtering Volume
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
124616100
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 01/25/18
Collection Date: 12/26/17
DateReceived: 01 /04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
RADCALC 01/23/18 15:37 / sec
FIELD 12/26/17 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 23 of 42
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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 07, 2017
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C17090829 Quote ID: C4886 -Quarterly Air Analysis
Project Name: 3rd Quarter Air 2017
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 9/27/2017
for analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C17090829-001 BHV-1 09/25/17 00:00 09/27 /17 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
C17090829-002 BHV-2 09/25/17 00:00 09/27/17 Filter Same As Above
C 17090829-003 BHV-4 09/25/17 00:00 09/27/17 Filter Same As Above
C 17090829-004 BHV-5 09/25/17 00:00 09/27/17 Filter Same As Above
C17090829-005 BHV-6 09/25/17 00:00 09/27/17 Filter Same As Above
C17090829-006 BHV-7 09/25/17 00:00 09/27/17 Filter Same As Above
C17090829-007 BHV-8 09/25/17 00:00 09/27 /17 Filter Same As Above
C17090829-008 Blanks 09/25/17 00:00 09/27/17 Filter Same As Above
The results as reported relate only to the item(s) submitted for testing. The analyses presented in this report were
performed at Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601, unless otherwise noted. Any
exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
If you have any questions regarding these test results, please call.
Report Approved By: ~/~
Technical Director -Casper
Digitally signed by
Steve Carlston
Date: 2017.11 .07 19:17:10 -07:00
Page 1 of 41
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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
3rd Quarter Air 2017
C17090829
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 /07 /17
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.
Tests associated with analyst identified as ELI-H were subcontracted to Energy Laboratories, 3161 E.Lyndale Ave., Helena,
MT, EPA Number MT00945.
BRANCH LABORATORY LOCATIONS
eli-b -Energy Laboratories, Inc. -Billings, MT
eli-g -Energy Laboratories, Inc. -Gillette, WY
eli-h -Energy Laboratories, Inc. -Helena, MT
CERTIFICATIONS:
USEPA: WY00002; FL-DOH NELAC: E87641; Oregon: WY200001; Utah: WY00002; Washington: C1012
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER.WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELi's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of41
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
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Lab ID: C 17090829-008
Client Sample ID: Blanks
Analyses Result Units Qualifiers
METALS, IN AIR
Uranium 0.0029 mg/L D
Uranium, Activity 2.0E-09 uCi/mL D
RADIONUCLIDES -IN AIR
Lead 210 1.4E-09 uCi/mL u
Lead 210 precision(±) 7.7E-09 uCi/mL
Lead 210 MDC 1.3E-08 uCi/mL
Radium 226 8.0E-10 uCi/mL u
Radium 226 precision (±) 6.5E-10 uCi/mL
Radium 226 MDC 9.7E-10 uCi/mL
Thorium 230 3.7E-10 uCi/mL
Thorium 230 precision (±) 2.4E-10 uCi/mL
Thorium 230 MDC 3.6E-10 uCi/mL
Thorium 232 1.7E-11 uCi/mL u
Thorium 232 precision (±) 1.1E-10 uCi/mL
Thorium 232 MDC 2.4E-10 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1.4 pCi/Filter u
Lead 210 precision(±) 7.7 pCi/Filter
Lead 210 MDC 12.8 pCi/Filter
Radium 226 0.80 pCi/Filter u
Radium 226 precision (±) 0.65 pCi/Filter
Radium 226 MDC 0.97 pCi/Filter
Thorium 230 0.37 pCi/Filter
Thorium 230 precision (±) 0.24 pCi/Filter
Thorium 230 MDC 0.36 pCi/Filter
Thorium 232 0.017 pCi/Filter u
Thorium 232 precision (±) 0.11 pCi/Filter
Thorium 232 MDC 0.24 pCi/Filter
Uranium, Activity 2.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.4E+05 %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 8.9E+04 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.2E+06 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.8E+05 %
Thorium 232, EFF Year 3.0E-14 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
MCU
RL QCL
1.4E-06
9.3E-13
0.20
Report Date: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
Method Analysis Date / By
SW6020 10/27/17 15:34 / eli-h
SW6020 10/27/17 15:34 / eli-h
E909.0 10/06/17 01:15 / meh
E909.0 10/06/17 01:15 / meh
E909.0 10/06/1701 :15 / meh
E903.0 10/15/17 12:24 I arh
E903.0 10/15/17 12:24 I arh
E903.0 10/15/17 12:24 I arh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 / cnh
E908.0 10/24/17 16:34 I cnh
E908.0 10/24/17 16:34 / cnh
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/1715:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11/05/1715:05 / sec
RADCALC 11 /05/17 15:05 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11/05/17 15:09 / sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
RADCALC 11 /05/17 15:09 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
D -RL increased due to sample matrix.
Page 24 of41
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: 3rd Quarter Air 2017
Lab ID: C 17090829-008
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
••• Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
1.0E-16 uCi/mL
2.2E+06 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1 L
Qualifiers RL
MCL/
ReportDate: 11/07/17
Collection Date: 09/25/17
DateReceived: 09/27/17
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
11/05/1715:09 / sec
11/05/1715:09 / sec
11 /05/17 15:09 I sec
11 /05/17 15:09 I sec
09/25/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 25 of 41
EI\ERGY
, , , , n 11 11
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I ) 4 HIGH VOLUME AIR SAMPLING REPORT
~· CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 3rd Quarter Air 2017
SAMPLE ID: Blanks
REPORT DATE: November 7, 2017
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
CJ 7090829-008 nalu IE-17
Third Quarter 2017 230Th 3E-18
Air Volume in mLs 226Ra 6E-18
l.36E+l 1 210Pb IE-17
232Th IE-19
Counting
Precision MDCµCi/mL
µCi/mL
NIA NIA
2E-18 3E-18
5E-18 7E-18
6E-17 9E-17
8E-19 2E-18
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 2E-02
IE-16 3E-14 9E-03
IE-16 9E-13 7E-04
2E-15 6E-13 2E-03
NIA 6E-15 2E-03
NOTE: This report uses 136,000,000 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
1.36E+l 1
Page 26 of 41
EN:RGY Trust our People. Trust our Data.
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QA/QC Summary Report
Prepared by Helena, MT Branch
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
Client: Energy Fuels Resources (USA) Inc Report Date: 11 /03/17
Work Order: C17090829 Project: 3rd Quarter Air 2017
Analyte Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: E200.8 Analytical Run: ICPMS205-H_171027A
Lab ID: ICV Initial Calibration Verification Standard 10/27/17 09:03
Uranium 0.0555 mg/L 0.0010 92 90 110
Lab ID: ICSA Interference Check Sample A 10/27/17 09:05
Uranium 2.84E-05 mg/L 0.0010
Lab ID: ICSAB Interference Check Sample AB 10/27/17 09:07
Uranium 8.75E-06 mg/L 0.0010 0 0
Lab ID: ICV Initial Calibration Verification Standard 10/27/17 17:43
Uranium 0.0576 mg/L 0.0010 96 90 110
Lab ID: ICSA Interference Check Sample A 10/27 /17 17:45
Uranium 3.01E-05 mg/L 0.0010
Lab ID: ICSAB Interference Check Sample AB 10/27/1717:47
Uranium 1.02E-05 mg/L 0.0010 0 0
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
Page 27 of41
E~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, MT877.472.0711
QA/QC Summary Report
Prepared by Helena, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 11/03/17
Project: 3rd Quarter Air 2017 Work Order: C17090829
Analyte Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Method: SW6020 Batch: 39228
Lab ID: C17090829-001AMS Sample Matrix Spike Run: ICPMS205-H_171019B 10/19/17 19:22
Uranium 4.35E-09 mg/L 1.5E-10 97 75 125
Lab ID: C17090829-001 AMSD Sample Matrix Spike Duplicate Run: ICPMS205-H_171019B 10/19/17 19:24
Uranium 4.39E-09 mg/L 1.5E-10 98 75 125 0.9 20
Method: SW6020 Batch: 39228
Lab ID: MB-50498 Method Blank Run: ICPMS205-H_171027A 10/27/1715:10
Uranium 4E-05 mg/L 1E-06
Lab ID: LCS2-50498 Laboratory Control Sample Run: ICPMS205-H_ 171027 A 10/27/1715:12
Uranium 0.0955 mg/L 1.4E-06 91 85 115
Lab ID: C17090829-001ADIL Serial Dilution Run: ICPMS205-H_ 171027 A 10/27/17 15: 16
Uranium 8.97E-10 mg/L 1.5E-10 0 0 5.3 20
Lab ID: C17090829-001AMS Sample Matrix Spike Run: ICPMS205-H_ 171027A 10/27/1715:18
Uranium 1.29E-09 mg/L 1.5E-10 85 75 125
Lab ID: C17090829-001 AMSD Sample Matrix Spike Duplicate Run: ICPMS205-H_ 171027 A 10/27 /17 15:20
Uranium 1.30E-09 mg/L 1.5E-10 89 75 125 1.3 20
Lab ID: H17100289-001 ADIL Serial Dilution Run: ICPMS205-H_ 171027A 10/27/17 15:47
Uranium 4.54E-09 mg/L 1.5E-10 0 0 2.2 20
Lab ID: H17100289-001 AMS Sample Matrix Spike Run: ICPMS205-H_171027A 10/27/17 15:49
Uranium 2.00E-08 mg/L 1.5E-10 103 75 125
Lab ID: H17100289-001 AMSD Sample Matrix Spike Duplicate Run: ICPMS205-H_ 171027A 10/27/17 15:51
Uranium 2.08E-08 mg/L 1.5E-10 108 75 125 4.0 20
Qualifiers:
RL -Analyte reporting limit. ND -Not detected at the reporting limit.
Page 28 of 41
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
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Analyte Count Result Units
Method: E903.0
Lab ID: C17090829-008AMS
Radium 226
Lab ID: C17090829-00BAMSD
Radium 226
Lab ID: LCS-50498
Radium 226
Lab ID: MB-50498
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Sample Matrix Spike
90.2 pCi/L
Sample Matrix Spike Duplicate
86.8 pCi/L
Laboratory Control Sample
89.8 pCi/L
Method Blank
0.1 pCi/L
0.1 pCi/L
0.2 pCi/L
Report Date: 11/07/17
Work Order: C17090829
RL %REC Low Limit High Limit
Run: G542M_ 171006A
92 70 130
Run: G542M_171006A
87 70 130
Run: G542M_171006A
95 80 120
Rvn: G542M_171006A
ND -Not detected at the reporting limit.
RPD RPDLimit Qual
3.8
Batch: 50498
10/15/17 12:24
10/15/17 12:24
20
10/15/17 12:24
10/15/17 12:24
u
U -Not detected at minimum detectable concentration
Page 29 of 41
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
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
I Analyte Count Result Units
Method: E908.0
Lab ID: LCS-50498
Thorium 230
lab ID: C 17090829-00SAMS
Thorium 230
Lab ID: C17090829-00SAMSD
Thorium 230
Lab ID: MB-50498
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
6
MDC -Minimum detectable concentration
Laboratory Control Sample
24.9 pCi/L
Sample Matrix Spike
4.85E-07 pCi/L
Sample Matrix Spike Duplicate
4.75E-07 pCi/L
Method Blank
0.4 pCi/L
0.2 pCi/L
0.2 pCi/L
-0.01 pCi/L
0.09 pCi/L
0.2 pCi/L
RL
ReportDate: 11/07/17
Work Order: C17090829
%REC Low Limit High Limit RPO RPDLimit Qual
Batch: 50498
Run: EGG-ORTEC_171011B 10/24/17 16:34
105 80 120
Run: EGG-ORTEC_171011B 10/24/17 16:34
104 70 130
Run: EGG-ORTEC_171011B 10/24/17 16:34
104 70 130 2.2 20
Run: EGG-ORTEC_171011B 10/24/17 16:34
u
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 30 of 41
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
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 3rd Quarter Air 2017
Analyte
Method: E909.0
Lab ID: LCS-50498
Lead 210
Lab ID: MB-50498
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Lab ID: C17090829-001AMS
Lead 210
Count Result Units
Laboratory Control Sample
192 pCi/L
3 Method Blank
-3 pCi/L
7
10
pCi/L
pCi/L
Sample Matrix Spike
1. 70E-05 pCi/L
Report Date: 11 /07 /17
Work Order: C17090829
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: PACKARD 31 OOTR_ 171004A
113 70 130
Run: PACKARD 3100TR_171004A
Run: PACKARD 31 OOTR_ 171004A
173 70 130
Batch: 50498
10/05/17 16:20
10/05/17 17:25
u
10/05/17 23:40
s
-Sample activity for this radionuclide is much larger than the spike activity added therefore the matrix spike recovery could not be calculated accurately.
Lab ID: C17090829-001AMSD Sample Matrix Spike Duplicate Run: PACKARD 31 OOTR_ 171004A 10/05/17 23:58
Lead 210 2.02E-05 pCi/L 289 70 130 17 20 S
-Sample activity for this radionuclide is much larger than the spike activity added therefore the matrix spike recovery could not be calculated accurately.
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 31 of41
EN:RGY Trust our People. Trust our Data.
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Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Tessa Parke
Reviewed by: Kasey Vidick
Reviewed Date: 10/2/2017
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
C17090829
Date Received: 9/27/2017
Received by: kak
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: Next Day Air
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 ate dried
and ground prior to sample analysis.
Contact and Corrective Action Comments:
None
Page 32 of 41
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: Energy Laboraties Contact: Garrin Palmer
..::2;.;.;.39;:;.;3..i.S~a:;.;;lt;;.;;;C~re;.;:;e.;.;.;k:.:H~wy-.-------Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samclers Name Samolers Signature
3rd Quarter Air 2017 Garrin Palmer I /::,'.'!,A~-·· ;Y-l,{.,(_;.._ -
Time
Samele ID Date Collected Collected Laboratorv Analvsis Reauested
BHV-1 6/26/17 -9/25/17 NA U-NAT. TH-230, Ra-226, Pb-210, TH-232
BHV-2 6/26/17 -9/25/17 NA U-NAT. TH-230, Ra-226, Pb-210, TH-232
BHV-4 6/26/17 -9/25/17 NA U-NAT, TH-230, Ra-226 Pb-210, TH-232
BHV-5 6/26/17 -9/25/17 NA U-NAT, TH-230 Ra-226, Pb-210, TH-232
BHV-6 6/26/17 -9/25/17 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-7 6/26/17 -9/25/17 NA U-NAT, TH-230. Ra-226, Pb-210, TH-232
BHV-8 6/26/17 -9/25/17 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
Blanks 6/26/17 -9/25/17 NA U-NAT, TH-230 Ra-226, Pb-210, TH-232
Comments: Please send reoort to Kathv Weinel at kweinelta>eneravfuels.com
Date/Time Re ·ved By:(Signature) Date/Time
qf,z-'/17 °/'/J l 7 /cJ :.
Date/Time
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2015
BHV-1 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
Ml Ml 4H~ Ts t ~a:-, ~Ii :Qa . . ~-;.~~ . Tai:l\l" 1.-::·· -.-c .~ I .,..r --1:V-. . • • h, •. ,
Week Filter Start Stop Start Stop Toial Starting Stopping A-. Wkl.y. A.II$, 'Mly;Avg. Wl;fy,Avg. ,AGL'flow,. :~Flow: "Std. Tam-'. Gema · -'i&ii:.:--illii..::.:a:.:. -~ f" .. ·· ··-.
# Number Daie Date Time Time Tlille Manometer Manomete, ~ Te"'I'. T:ii#, -~ni (~ .Yohliill! --· \tlfliH.it, ~-,:. -.~-rC.~
IIIIUI) (in.H20) (in. H20) •(111,]fJ)) (°C) n<r tmmHg)_ .. (m'/IIIID) . , (IIF/aih,), .~dii) (~,--·(ll. ' '{II cll!Al •. i~-1· .:Bl,.
1 9472583 6/26/2017 7/3/2017 82653.76 82820.38 9997.2 4.0 4.0 4.0 25.1 298.3 618.7 1.13 0.92 32.38 9166.6 4.9168 5.1575 240.7 0.0263 99.2
2 9472580 7/3/2017 7/10/2017 82820.38 82989.17 10127.4 4.0 4.0 4.0 27.1 300.2 622.0 1.13 0.92 32.36 9280.8 4.9263 5.1907 264.4 0.0285 100.5
3 9472567 7/10/2017 7/17/2017 82989.17 83161.5 10339.8 4.0 4.0 4.0 24.6 297.8 621.0 1.12 0.92 32.47 9506.8 4.8616 5.0299 168.3 0.0177 102.6
4 9472564 7/17/2017 7/24/2017 83161.5 83325.52 9841.2 4.0 4.0 4.0 24.4 297.6 621.3 1.12 0.92 32.49 9053.4 4.8647 5.0042 139.5 0.0154 97.6
5 9472556 7/24/2017 7/31/2017 83325.52 83492.86 10040.4 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9266.6 4.8818 4.9886 106.8 0.0115 99.6
6 9472543 7/31/2017 8/7/2017 83492.86 83661.8 10136.4 4.0 4.0 4.0 21.7 294.8 632.20 I.II 0.93 32.93 9451.9 4.8825 5.0132 130.7 0.0138 100.6
7 9472535 8/7/2017 8/14/2017 83661.8 83829.07 10036.2 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 9265.3 4.8911 5.0215 130.4 0.0141 99.6
8 9472532 8/14/2017 8/21/2017 83829.07 83997.94 10132.2 4,0 4.0 4.0 22.l 295.3 620.01 1.12 0.92 32.58 9347.7 4.8781 5.0274 149.3 0.0160 100.5
9 9472519 8/21/2017 8/28/2017 83997.94 84164.8 10011.6 4.0 3.5 3.8 23.2 296.4 621.79 1.09 0.89 31.55 8943.7 4.8915 5.0540 162.5 0.0182 99.3
10 9472511 8/28/2017 9/5/2017 84164.8 84358.91 11646.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10714.9 4.9022 5.1923 290.1 0.0271 115.5
11 9472508 9/5/2017 9/11/2017 84358.91 84500.96 8523.0 4,0 4.0 4.0 22.2 295.3 621.79 1,12 0.92 32,63 7874.1 4.6303 4.8424 212.l 0.0269 84.6
12 9415394 9/11/2017 9/18/2017 84500.96 84670.03 10144.2 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9402.2 4.8304 4.9735 143.1 0.0152 100.6
13 9415386 9/18/2017 9/25/2017 84670.03 84840.6 10234.2 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9505.7 4.8208 5.1806 359.8 0.0379 101.5
Totals 131210.4 14.53 ll.97 422.61 120779.6 63.178 65.676 2497.7 0.2685
-----. Averages 10093.1 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.51 9290.7 4.860 5.052 192.1 0.0207 100.1
Comments:
Insert \1/eekJy flow check values in yellow columns. ~~---~ . . . --':] ~.. . ----. --' -Gn:£n,columnswc.'Calcut:11ed ~ fro1n-the met stfrtion, j
riis4irir:we!i!i5wlllesJa~·!llli~--.,
Energy Fuels Resources -White Mesa Mill Calibration Date: 7/7/2016 First Monitoring Quarter 2014
B.HV 2 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
-Orifice SIN: 8091779
Ml Ml Aff· . T~ Tli Pi! • :Qa . QI ' ~ . ; 'f'Qdl L ;-~· ,-.. -.,
Week Filter Start Stop Start Stop TOlal Starting Stopping Aveago Wl<ly. A.vg. wtly~ AV&: Wkly. A,•g.. Ailf;.flOW ,$if.flow' 'S1~Ao!r, _ --~-'I'la I Gross ~~".° '.:'.' ... ~-
# Number Date Date Time Time ~ Manometer Manometer Manometcl T~np. '(c:mp, l'Jessun: , . (~\ "Voloall!I Wiilallt Wcil!llt ,.-~,. 1 . "~-;" . ~
(mm) (in. H,O) (in. H20) liP. ~> ("C) (K> (~) (111'/mln). _ lrii'/Jnlll) <JffaiaJ; '. ,~, , r.)' I ~ .. '(niaj: , 1 ~'.T, , ·t•>!' -. ' ' ' ' .
1 9472584 6/26/2017 7/3/2017 93261.9 93428.01 9966.6 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9138.5 4.8962 5.2398 343.6 0.0376 98.9
2 9472579 7/3/2017 7/10/2017 93428.01 93596.76 10125 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9278.6 4.9066 5.2718 365.2 0.0394 100.4
3 9472568 7110/2017 7117/2017 93596.76 93769.65 10373.4 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9537.6 4.8633 5.1259 262.6 0.0275 102.9
4 9472563 7/1712017 7124/2017 93769.65 93933.12 9808.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9023.1 4.8854 5.0599 174.5 0.0193 97.3
5 9472555 7/24/2017 7131/2017 93933.12 94101.11 10079.4 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9302.6 4.8709 5.0410 170.1 0.0183 100.0
6 9472544 7/31/2017 8nt2017 94101.11 94269.94 10129.8 4.0 4.0 4.0 21.7 294.8 632.20 I.I I 0.93 32.93 9445.7 4.8980 5.0752 177.2 0.0188 100.5
7 9472536 8nt2017 8114/2017 94269.94 94436.43 9989.4 4.0 3.5 3.8 22.2 295.4 621.03 1.08 0.89 31.58 8933.5 4.9018 5.1281 226.3 0.0253 99.1
8 9472531 8/14/2017 8121/2017 94436.43 94605.52 10145.4 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9359.9 4.8914 5.2397 348.3 0.0372 100.6
9 9472520 8121/2017 8/28/2017 94605.52 94772.23 10002.6 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9224.3 4.8934 5.1229 229.5 0.0249 99.2
10 9472512 8/28/2017 9/5/2017 94772.23 94966.23 ll640 4.0 4.0 4.0 24,7 297.9 622.04 1.12 0.92 32.49 10708.8 4.8736 5.2174 343.8 0.0321 115.5
11 9472507 9/5/2017 9/11/2017 94966.23 95109 8566.2 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7914.0 4.6235 4.8615 238.0 0.0301 85.0
12 9415395 9/\\/2017 9/18/2017 95109 95278.17 10150.2 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9407.7 4.8462 5.0341 187.9 0.0200 100.7
13 9415387 9/18/2017 9/25/2017 95278.17 95448.07 10194 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9468.4 4.8792 5.1926 313.4 0.0331 LOI.I -Totals 131170.2 14.53 11.97 422.60 120742.8 63.230 66.610 3380.4 0.3635
.. ·, _' -!.. Averages 10090.0 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.51 9287.9 4.864 5.124 260.0 0.0280 100.1
Comments:
lnsen weekly flow check values in yellow columns. ------_ • ~~~-ii~ -. -. :J
Oteen'COIUJl)Jls-al'ecQllcolated avernges-fl:!>m the met"-sta.tion :
lipt&liiij!l@llllp:tatoC!JllfiCcllu11111$. ----,
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-4 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
dH dH -m : Tca Ta p,, Qa Qs-' Q5 1'aw I . : \ -~ .!.. -• ; ' '
Week Filter Start Stop Stan Stop TOjll Starting Stopping AICQIIS WI;!}> Asg, Wkly.A~ WIU)' ,\vg. ~ l'low Sl!L~ ·~lilo,,r' : :$ad, T.-GR,-~·-. :~~ ~-·
# Number Date Date Time Time Time Manometer Manometer 'M4ftllllleW' Temp. Tulip. Pre.sun,. =·· ,Volume Wd&ht Wd;llt ' 'Wiogfi& . ; -:---• ~ (nllil} (in.H20) (in. H20) (111.lljOJ (·C) (I() {mmHg) (11t.7ininl (lll"hnill.) lilfJ CS> -~ ·*·-· d~( .;_~
1 9472585 6/26/2017 7/3/2017 68446.83 68614.13 10038 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9204.0 4.9105 5.1278 217.3 0.0236 99.6
2 9472578 7/3/2017 7/10/2017 68614.13 68781.9 10066.2 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9224.7 4.9066 5.1683 261.7 0.0284 99.9
3 9472569 7/10/2017 7/17/2017 68781.9 68954.42 10351.2 4.0 4.0 4.0 24.6 297.8 621.03 Lt2 0.92 32.47 9517.2 4.8767 5.0984 221.7 0.0233 102.7
4 9472562 7/17/2017 7/24/2017 68954.42 69118.56 9848.4 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9060.0 4.8586 5.0250 166.4 0.0184 97.7
5 9472554 7/24/2017 7/31/2017 69118.56 69283.92 9921.6 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9157.0 4.8649 4.9803 115.4 0.0126 98.4
6 9472545 7/31/2017 8n12011 69283.92 69451.32 10044 4.0 4.0 4.0 21.7 294.8 632.20 I.I l 0.93 32.93 9365.7 4.8842 5.0262 142.0 0.0152 99.6
7 9472537 8n12011 8/14/2017 69451.32 69451.32 0 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 0.0 4.8749 5.0091 134.2 #DIV/0! 0.0
8 9472530 8/14/2017 8/21/2017 0 167.23 10033.8 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9256.9 4.8916 5.0250 133.4 0.0144 99.5
9 9472521 8/21/2017 8/28/2017 167.23 335.12 10073.4 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9289.6 4.8944 5.0735 179.1 0.0193 99.9
10 9472513 8/28/2017 9/5/2017 335.12 530.2 11704.8 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10768.5 4.8750 5.1159 240.9 0.0224 116.1
II 9472506 9/5/2017 9/11/2017 530.2 671.3 8466 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7821.5 4.6408 4.8224 181.6 0.0232 84.0
12 9415396 9/11/2017 9/1812017 671.3 839.03 10063.8 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9327.7 4.8591 4.9935 134.4 0.0144 99.8
13 9415388 9/18/2017 9/25/2017 839.03 1008.86 10189.8 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9464.5 4.8280 4.9906 162.6 0.0172 IOI.I . -· Totals 120801.0 14.57 12.00 423.62 111457.2 63.165 65.456 2290.7 #DIV/0! -
-Averages 9292.4 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 8573.6 4.859 5.035 176.2 #DIV/0! 92.2
Comments:
Insert weekly flow check values in yellow columns.
~WIIII?-~--___J
Gitto .:olumll,f are caJcl\1llced a..,,..g# fnini 1fie.n~.station. I
~-.wefallf~hno0181111,tc:olaams: ::J
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-5 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
Ml Ml '• .Alt -. T:1. Ta. I'll Qa '.~; ~ .-.~-·:~i , ~-.:.._ ·._. ·.,-;,.. ...
Week M,ly,A'I, Acf)to-.,, :_s.,,~flli)w ,Sl4,80',f. 'Silr .' I Tme 0.0. ·:.· ,...,,, " .. -~ ..... "'I
Filter Start Stop Start Stop Total Starting Stopping Average Willy. Avg. Wkly. A.vg. "·. ~·· # Number Date Date Time Time 1'°11118 Manometer Manometer ~ Temp. jq.· P~t . ·I I : ~·--:J. '-(~· .~-Wdifn· ·'W#t, I\, ~ '/1 ,,~ ~s. -~
. (111'[,nm}: >ii@~~ ~ {min) (in.H20) (in.H20) •. liia. lM>) 1•t) (K)~ (mmHg) '(Jif ljj!ia} (W/,mlil~ ;CJ:) (i) .. I , ... m,.
I 9472586 6/26/2017 7/3/2017 91914.97 92082.58 10056.6 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9221.0 4.9007 5.1293 228.6 0.0248 99.8
2 9472577 7/3/2017 7/10/2017 92082.58 92250.43 10071 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9229.1 4.9196 5.1821 262.5 0.0284 99.9
3 9472570 7/10/2017 7/17/2017 92250.43 92422.93 10350 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9516.1 4.9108 5.0837 172.9 0.0182 102.7
4 9472561 7/17/2017 7/24/2017 92422.93 92587.05 9847.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9058.9 4.8683 5.0259 157.6 0.0174 97.7
5 9472553 7/24/2017 7/31/2017 92587.05 92752.06 9900.6 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9137.6 4.8926 5.0343 141.7 0.0155 98.2
6 9472546 7/31/2017 8/7/2017 92752.06 92919.47 10044.6 4.0 4.0 4.0 21.7 294.8 632.20 1.11 0.93 32.93 9366.3 4.8807 5.0239 143.2 0.0153 99.6
7 9472538 8/7/2017 8/14/2017 92919.47 93088.03 10113.6 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 9336.7 4.8924 5.0321 139.7 0.0150 100.3
8 9472529 8/14/2017 8/21/2017 93088.03 93255.7 10060.2 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9281.3 4.8820 5.0454 163.4 0.0176 99.8
9 9472522 8/21/2017 8/28/2017 93255.7 93423.24 10052.4 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9270.2 4.8890 5.0594 170.4 0.0184 99.7
10 9472514 8/28/2017 9/5/2017 93423.24 93618.65 11724.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10786.7 4.8787 5.1413 262.6 0.0243 116.3
11 9472502 9/5/2017 9/11/2017 93618.65 93759.73 8464.8 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7820.4 4.6351 4.8039 168.8 0.0216 84.0
12 9415397 9/11/2017 9/18/2017 93759.73 93927.48 10065 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9328.8 4.8413 4.9805 139.2 0.0149 99.9
13 9415389 9/18/2017 9/25/2017 93927.48 94096.92 10166.4 4.0 4.0 4.0 16.2 289.4 615.69 I.I I 0.93 32.80 9442.7 4.8372 5.0004 163.2 0.0173 100.9 -Totals 130917.0 14.57 12.00 423.62 120795.8 63.228 65.542 2313.8 0.2487
... _ --~ Averages 10070.5 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 9292.0 4.864 5.042 178.0 0.0191 99.9
Comments:
lnsen weekly flow check values in yellow-colunms. _G-J '!ii,cilii¥'-·~.!lie,~tit.:. -
~ columns 1111:.calCUhlled average from lhe met St:Uion.
. .filier~ .i.es·• gta!column,. :J
BHV-6
Energy Fuels Resources -White Mesa Mill
Period: June 26, 2017 -September 25, 2017
Calibration Date: 1n12016
Calibration Slope & Intercept: m= 1.25008 b= -0.0206
Week
#
2
3
4
5
6
7
8
9
10
II
12
13
Filter
Number
Stan
Date
Stop
Date
Start
Time
9472587 I 6/2612011 I 7/312017 8384.94
9472576 I 7/3/2017 111012011 I 8552.23
9472571 I 111012017 I 1m12011 I 8720.05
9472560 I 7117/2017 I 112412011 I 8797.98
Stop
Time
8552.23
8720.05
8797.98
8962.ll
9472552 I 112412011 I 7/3112017 I 8962.11 I 9127.48
9472547 I 7/31/2017 I 8n/2017 I 9127.48 I 9294.86
9472539 I 8ni20!7 I 8/14/2017 I 9294.86 I 9463.02
9472528 I 8/14/2017 I 8/21/2017 I 9463.02 I 9630.77
9472523 I 812112017 I 8/28/2017 I 9630.77 I 9798.64
9472515 I 8/28/2011 I 915/2017 I 9798.64 I 9993.73
9472505 I 9/5/2017 I 911112017 I 9993.73 I 10134.84
9415398 I 911112011 I 9118/2017 I 10134.84 I 10302.57
9415390 I 9/18/2017 I 912512011 I 10302.57 I 10472.39
Totals
'total
Time
(nun)
10037.4
10069.2
4675.8
9847.8
9922.2
10042.8
10089.6
10065
10072.2
11705.4
8466.6
10063.8
10189.2
125247.0
Averaies I 9634.4
Comments: Replaced Elapsed time indicator on 7/11/2016
Insert weekly flow check values in yellow columns.
11!-~~-!!~ -
C"ne,:n @lumoi11re Clllcula!ed !l'1'1'all~ from the f11ll,t 1Mio.o, ,
tiilleft;&ltet~•oraii·colwilaL --,
Orifice SIN: 8091779
.<lH llli. AH Tu Ti P~ l: ·Qs
Staning Stopping Mer~ Wl\ly. A,ig, \\'kly,·A"a, Wkly. A'llg. Mr.fl.ow ~ Flo .. !Y'.
Manometer Manomelel -~ Temp. T~. Pressure · .
(in. H.20) (in. H20) (!_n.. H:Q)· ("C) (K) (111mRg) . lm'lmln) (m•lmin)'
4.0 I 4.0 I 4.o I 25. 1 I 298.3 I 618.74 1.13 0.92
4.0 I 4.0 I 4.0 I 27 .1 I 300.2 I 622.04 1.13 0.92
4.0 40 4.0 24.6 297.8 621.03 1.12 0.92
4.0 4.5 4.3 24.4 297.6 621.28 1.16 0.95
4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92
4.0 4.0 4.0 21.7 294.8 632.20 I.II 0.93
4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92
4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92
4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92
4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92
4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92
4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93
4.0 4.0 4,0 16.2 289.4 615.69 I.I I 0.93
14.60 12.02
4.0 4.0 4.0 22.7 295.9 I 621.43692 1.12 0.92
Qr. :_ Tiifal
-Slit Row: ' Slil. ·: . Vol =-., ... er
32.38 9203.4
32.36 9227.5
32.47 4299.1
33.47 9334.2
32.59 9157.5
32.93 9364.6
32.60 9314.6
32.58 9285.7
32.57 9288.5
32.49 10769.0
32.63 7822.0
32.73 9327.7
32.80 9463.9
Tl!'II
~
(I,)
4.9233
4.8850
4.9029
4.8395
4.9017
4.8656
4.8655
4.9013
4.8950
4.8954
4.6265
4.8146
4.8344
424.61 I 115857.7 I 63.151
32.66 8912.1 4.858
First Monitoring Quarter 2014
Updated: 7/30/14
:Grosa
W411pi
,(lj
5.1483
5.1389
5.0185
4.9857
5.0201
5.0059
4.9921
5.0595
5.0719
5.1396
4.8329
4.9585
4.9894
1
.....
I .-~~ :,;..~.· -·~ . --. . ~·~~·er .. -.t ...,,. ,,...,.~·r ._ · !ii11U.! •
225.o I 0.0244 I 99.6
253.9 I 0.0215 I 99.9
115.6 I 0.0269 I 46.4
146.2 I 0.0157 I 97.7
118.4 0.0129 98.4
140.3 0.0150 99.6
126.6 0.0136 100.l
158.2 0.0170 99.9
176.9 0.0190 99.9
244.2 0.0227 116.1
206.4 0.0264 84.0
143.9 0.0154 99.8
155.0 0.0164 IOI.I
65.361 I 2210.6 I o.2530
5.028 170.0 0.0195 95.6
Energy Fuels Resources -White Mesa Mill Calibration Date: 1n12016 First Monitoring Quarter 2014
BHV-7 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
6H fill All T~ r, p3 Qa Q$. 'QI ·, TOOi
Week Filler Stan Stop Start Stop TOUII Starting Stopping Averase Wkly. A ,,g; Wkly.A~ Wl<ly.AYg.. ~Row· ·~-~ .:$ui..aow $11' 1""11 ~ I Nol. : i:i ~-;~:._'.· c.:p~ ::·-i-, # Number Date Date Time Time Ti• Manometer Manometer Ma$!~ T,einp. Temp. P~re ··.~) . Vohim!: Wdpf-Wlijllt Wcipir :~i flJ'lin) (jg.H20) (in. H20)_ ,m.°'HP) ("C) (~ (mm!jg) (cjf°fmfll) ll!i'(mla}' . (lt'/nifa) •(in')' (a) (I) -(iv&) : .·-::c~t
I 9472588 6/26/2017 7/3/2017 476.06 642.67 9996.6 4,0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9166.0 4.9296 5.2029 273.3 0.0298 99.2
2 9472575 7/3/2017 7/10/2017 642.67 811.44 10126.2 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9279.7 4.9170 5.2397 322.7 0.0348 100.5
3 9472572 7/10/2017 7/17/2017 811.44 983.79 10341 4.0 4_0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9507.9 4.9085 5.1476 239.1 0.0251 102.6
4 9472559 7117/2017 7/24/2017 983.79 1147.81 9841.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9053.4 4.8487 5.0018 153.1 0.0169 97.6
5 9472551 7/24/2017 7/31/2017 1147.81 1315.16 10041 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9267.2 4.8932 5.0465 153.3 0.0165 99.6
6 9472548 7/31/2017 8n/2017 1315.16 1484.1 10136.4 4.0 4.0 4.0 21.7 294.8 632.20 I.I I 0.93 32.93 9451.9 4.8789 5,0318 152.9 0.0162 100.6
7 9472540 8/7/2017 8/14/2017 1484.1 1651.27 10030.2 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 9259.7 4.9065 5.0482 141.7 0.0153 99.5
8 9472527 8/14/2017 8/21/2017 1651.27 1820.26 10139.4 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9354.3 4.8747 5.0128 138.1 0.0148 100.6
9 9472524 8/21/2017 8/28/2017 1820.26 1987.39 10027.8 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9247.5 4.8779 5.1019 224.0 0.0242 99.5
10 9472516 8/28/2017 9/5/2017 1987.39 2181.15 11625.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10695.6 4.8979 5.2209 323.0 0.0302 115.3
11 9472504 9/5/2017 9/11/2017 2181.15 2323.32 8530.2 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7880.8 4.6225 4.8737 251.2 0.0319 84.6
12 9415399 9/11/2017 9/18/2017 2323.32 2492.46 10148.4 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9406.1 4.6362 4.8059 169.7 0.0180 100.7
13 9415391 9/18/2017 9/25/2017 2492.46 2662.97 10230.6 4.0 4.0 4.0 16.2 289.4 615.69 111 0.93 32.80 9502.4 4.8506 5.1081 257.5 0.0271 101.5
Totals 131214.6 ' 14.57 12.00 423.62 121072.4 63.042 65.842 2799.6 0.3009
Averages 10093.4 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 9313.3 4.849 5.065 215.4 0.0231 JOO.I
Comments: Time Indicator was found broken on 4/10/2017. Replaced Time Indicator on 4/10/2017.
Insert weekly flow check values in yellow columns.
iileii!llll!lf~-,~ :J Green columns-oalt"Utn11,d a~ rrom tht: met station. I
!I-,'"iilcer~,!!S-J!l!IISCQ!llirii. :J
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-8 Period: June 26, 2017 -9/25/17 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
llli Ml All Tn Ta Pn Qa Q$ -~ TOI.II -.. ;.-.~"' ·-
Week Filter Start Stop Start Stop fOlal Starting Stopping A'/ClffC Wkly. A.vg, Wlcly. Avg. Wkly. Avg. Act. Row-Sid. Flnw:; '51.d; FIQ'IP, -Su(. Tme 6-s-* ~~~. ~
# Number Date Date Time Time lllllCI Manometer Manometer ~·!Cler Temp. Tein,.. Press!re 1~> v~. Wcigtil Weialll ~-·. . 4-~ ....
(rnlll) (in.H20) (in. H,O) (m. H;()) (PO) (K) (mniHg) (m''IIIWI) (tll~fmlll,)· .(ft"l~ (111') (a) (I} ~: -~~), ·:·:~r·· -
I 9472589 6/26/2017 7/3/2017 6937.1 7103.71 9996.6 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9166.0 4.9128 5.0762 163.4 0.0178 99.2
2 9472574 7/3/2017 7/10/2017 7103.71 7272.5 10127.4 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9280.8 4.9086 5.1570 248.4 0.0268 100.5
3 9472573 7/10/2017 7/17/2017 7272.5 7444.84 10340.4 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9507.3 4.9174 5.0449 127.5 0.0134 102.6
4 9472558 7/17/2017 7/24/2017 7444.84 7608.86 9841.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9053.4 4.8678 4.9603 92.5 0.0102 97.6
5 9472550 7/24/2017 7/31/2017 7608.86 7776.2 10040.4 3.5 4.0 3.8 22.8 295.9 621.8 1.09 0.89 31.57 8976.7 4.8916 4.9439 52.3 0.0058 99.6
6 9472549 7/31/2017 8/7/2017 7776.2 7945.14 10136.4 3.5 4.0 3.8 21.7 294.8 632.20 1.07 0.90 31.90 9156.2 4.8763 4.9406 64.3 0.0070 100.6
7 9472541 8/7/2017 8/14/2017 7945.14 8112.42 10036.8 4.5 4.0 4.3 22.2 295.4 621.03 1.15 0.95 33.59 9546.8 4.8835 4.9506 67.1 0.0070 99.6
8 9472526 8/14/2017 8/21/2017 8II2.42 8281.37 10137 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9352.1 4.8818 5.0371 155.3 0.0166 100.6
9 9472525 8/21/2017 8/28/2017 8281.37 8448.08 10002.6 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9224.3 4.8786 4.9812 102.6 0.011 I 99.2
10 9472517 8/28/2017 9/5/2017 8448.08 8642.26 11650.8 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10718.8 4.8709 5.0957 224.8 0.0210 115.6
11 9472503 9/5/2017 9/11/2017 8642.26 8784.42 8529.6 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7880.2 4.6475 4.8383 190.8 0.0242 84.6
12 9415400 9111/2017 9/18/2017 8784.42 8953.6 10150.8 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9408.3 4.8320 4.8571 25.1 0.0027 100.7
13 9415392 9/18/2017 9/25/2017 8953.6 9124.1 10230 4.0 4.0 4.0 16.2 289.4 615.69 I.I I 0.93 32.80 9501.8 4.8355 4.9830 147.5 0.0155 101.5
Totals 131220.0 14.53 I l.97 422.56 120772.7 63.204 64.866 1661.6 0.1792
-. -. ~---Averages 10093.8 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.50 9290.2 4.862 4.990 127.8 0.0138 JOO.I
Comments:
Insert weekly flow check values io yellow columns. ....,....v-•
~~--~~ ~ --=i Green columns are c:alculatcd avernges,from the 1ne<>stati()!I,
biseft lillilf ?!§!!I wl!IC$ into Cll'IQlUoklllll!S. ::J
Blanks Period: June 26, 2017 -September
25 2017
Week Filter Start Stop Net # Number Date Date
1 9472581 26-Jun-17 03-Jul-17 4.9220
2 9472566 03-Jul-17 10-Jul-17 4.8670
3 9472565 10-Jul-17 17-Jul-17 4.8563
4 8472557 17-Jul-17 24-Jul-17 4.8583
5 9472542 24-Jul-17 31-Jul-17 4.8870
6 9472534 31-Jul-17 07-Aug-17 4.8722
7 9472533 07-Aug-17 14-Aug-17 4.8972
8 9472518 14-Aug-17 21-Aug-17 4.8801
9 9472510 21-Aug-17 28-Aug-17 4.8952
10 9472509 28-Auq-17 05-Sep-17 4.6300
11 9472501 05-Sep-17 11-Sep-17 4.6224
12 9415393 11-Sep-17 18-Sep-17 4.8199
13 9415378 18-Sep-17 25-Sep-17 4.7980
Totals
EN:RGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 866.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
January 25, 2018
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C18010137
Project Name: Quarterly Air Analysis
Quote ID: C4886
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 1/4/2018 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix
C18010137-001 BHV-1 12/26/17 00:00 01 /04/18 Filter
C18010137-002 BHV-2 12/26/17 00:00 01 /04/18 Filter
C18010137-003 BHV-4 12/26/17 00:00 01/04/18 Filter
C18010137-004 BHV-5 12/26/17 00:00 01 /04/18 Filter
C18010137-005 BHV-6 12/26/17 00:00 01/04/18 Filter
C18010137-006 BHV-7 12/26/17 00:00 01/04/18 Filter
C18010137-007 BHV-8 12/26/17 00:00 01 /04/18 Filter
C18010137-008 Blanks 12/26/17 00:00 01/04/18 Filter
Test
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
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
Same As Above
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
The results as reported relate only to the item(s) submitted for testing. The analyses presented in this report were
performed at Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601 , unless otherwise noted. Any
exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
If you have any questions regarding these test results, please call.
Page 1 of 42
EN:RGY
Report Approved By:
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
GIiiette, WY 888.888.7175 • Helena, MT 811.472.071
ANALYTICAL SUMMARY REPORT
Digitally signed by
Steve Carlston
Date: 2018.01.25 19:03:58 -07:00
Page 2 of 42
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886. 7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
Quarterly Air Analysis
C18010137
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (±2°C)
Report Date: 01/25/18
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
CERTIFICATIONS:
USEPA: WY00002; FL-DOH NELAC: E87641; Oregon: WY200001; Utah: WY00002; Washington: C1012
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-H were subcontracted to Energy Laboratories, 3161 E.Lyndale Ave., Helena,
MT, EPA Number MT00945.
Page 3 of 42
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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 Report Date: 01/25/18
Project: Quarterly Air Analysis Collection Date: 12/26/17
Lab ID: C18010137-008 DateReceived: 01/04/18
Client Sample ID: Blanks Matrix: Filter
MCU
Analyses Result Units Qualifiers RL QCL Method Analysis Date / By
METALS, IN AIR
Uranium 0.0036 mg/L 1.5E-06 SW6020 01/18/18 16:30 / eli-h
Uranium, Activity 2.5E-09 uCi/mL 9.8E-13 SW6020 01 /18/18 16:30 / eli-h
RADIONUCLIDES -IN AIR
Lead 210 9.9E-09 uCi/mL E909.0 01 /18/18 03:08 / meh
Lead 21 O precision (±) 3.8E-09 uCi/mL E909.0 01/18/18 03:08 / meh
Lead 210 MDC 4.0E-09 uCi/mL E909.0 01/18/18 03:08 / meh
Radium 226 1.3E-09 uCi/mL u E903.0 01/22/18 13:51 / arh
Radium 226 precision (±) 1.0E-09 uCi/mL E903.0 01/22/18 13:51 / arh
Radium 226 MDC 1.5E-09 uCi/mL E903.0 01 /22/18 13:51 / arh
Thorium 230 1.4E-09 uCi/mL E908.0 01 /18/18 09:36 / cnh
Thorium 230 precision (±) 2.6E-10 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 230 MDC 9.4E-10 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 232 1.2E-10 uCi/mL u E908.0 01/18/18 09:36 / cnh
Thorium 232 precision (±) 3.2E-10 uCi/mL E908.0 01/18/18 09:36 / cnh
Thorium 232 MDC 6.3E-10 uCi/mL E908.0 01/18/18 09:36 / cnh
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 9.4 pCi/Filter RADCALC 01/23/18 15:08 / sec
Lead 210 precision (±) 3.6 pCi/Filter RADCALC 01/23/1815:08 / sec
Lead 210 MDC 3.8 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Radium 226 1.3 pCi/Filter u RADCALC 01 /23/18 15:08 / sec
Radium 226 precision (±) 0.99 pCi/Filter RADCALC 01/23/18 15:08 / sec
Radium 226 MDC 1.4 pCi/Filter RADCALC 01/23/18 15:08 / sec
Thorium 230 1.3 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Thorium 230 precision (±) 0.25 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Thorium 230 MDC 0.90 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Thorium 232 0.12 pCi/Filter u RADCALC 01 /23/18 15:08 / sec
Thorium 232 precision (±) 0.30 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Thorium 232 MDC 0.59 pCi/Filter RADCALC 01 /23/18 15:08 / sec
Uranium, Activity 2.3 pCi/Filter 0.20 RADCALC 01/23/1815:08 / sec
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.6E+06 % RADCALC 01/23/18 15:37 / sec
Lead 210, EFF Day 6.0E-13 uCi/mL RADCALC 01/23/18 15:37 / sec
Lead 210, LLD 2.0E-15 uCi/mL RADCALC 01/23/18 15:37 / sec
Radium 226, % of EFF 1.5E+05 % RADCALC 01/23/18 15:37 / sec
Radium 226, EFF Week 9.0E-13 uCi/mL RADCALC 01/23/18 15:37 / sec
Radium 226, LLD 1.0E-16 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 230, % of EFF 4.6E+06 % RADCALC 01/23/18 15:37 / sec
Thorium 230, EFF Year 3.0E-14 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 230, LLD 1.0E-16 uCi/mL RADCALC 01/23/18 15:37 / sec
Thorium 232, % of EFF 2.1E+06 % RADCALC 01/23/18 15:37 / sec
Thorium 232, EFF Year 6.0E-15 uCi/mL RADCALC 01/23/18 15:37 / sec
Report RL -Analyte reporting limit. MCL -Maximum contaminant level.
Definitions: QCL -Quality control limit. ND -Not detected at the reporting limit.
MDC -Minimum detectable concentration U -Not detected at minimum detectable concentration
Page 25 of42
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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: Quarterly Air Analysis
Lab ID: C 18010137-008
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
*** Field data provided by client
Report
Definitions:
RL -Analyte reporting limit.
QCL -Quality control limit.
N/A uCi/mL
2.7E+06 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1 L
Qualifiers RL
MCU
Report Date: 01 /25/18
Collection Date: 12/26/17
DateReceived: 01/04/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
01 /23/18 15:37 / sec
01 /23/18 15:37 / sec
01 /23/18 15:37 / sec
01 /23/18 15:37 / sec
12/26/17 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 26 of 42
EN:RGY
I ' '
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' '. .r I
...... HIGH VOLUME AIR SAMPLING REPORT
-r ' . CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: Quarterly Air Analysis
•• l SAMPLE ID: Blanks
REPORT DATE: January 25, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl 8010137-008 natu 2E-17
Fourth Quarter 2017 230Th IE-17
Air Volume in mLs 226Ra 9E-18
l.36E+l l 2i0Pb 7E-17
232Th 9E-19
..
•• I
"i. • '
Counting
Precision MDCµCi/mL
µCi/mL
NIA NIA
2E-18 7E-18
7E-18 IE-17
3E-17 3E-17
2E-18 4E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
. 4 ... -rl • ..
• I
I I • . ' ~
.,., , t ,-. • •1
L.L.D.+ Effluent Cone.* % EfOuent
µCi/mL µCi/mL Concentration
IE-16 9E-14 2E-02
IE-16 3E-14 3E-02
IE-16 9E-13 IE-03
2E-15 6E-13 IE-02
NIA 6E-15 IE-02
NOTE: This report uses 136,000,000 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
Page 27 of 42
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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 Helena, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 01/23/18
Work Order: C18010137 Project: Quarterly Air Analysis
Analyte
Method: SW6020
Lab ID: ICV
Uranium
Lab ID: ICV
Uranium
Method: SW6020
Lab ID: MB-50967
Uranium
Lab ID: LCS2-50967
Uranium
Lab ID: LFB-50967
Uranium
Lab ID: H18010234-001AMS
Uranium
Lab ID: H18010234-001AMSD
Uranium
Qualifiers:
RL -Analyte reporting limit.
Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Initial Calibration Verification Standard
0.0572 mg/L 0.00030
Initial Calibration Verification Standard
0.0572 mg/L 0.00030
Method Blank
2E-05 mg/L 1E-06
Laboratory Control Sample
0.0944 mg/L 1.4E-06
Laboratory Fortified Blank
0.0457 mg/L 1.4E-06
Sample Matrix Spike
3.40E-05 mg/L 1.0E-09
Sample Matrix Spike Duplicate
3.45E-05 mg/L 1.0E-09
95
95
90
96
97
90
90
Analytical Run: ICPMS205-H_ 180118A
01/18/18 11 :47
110
01/18/1818:04
110
Run: ICPMS205-H_ 180118A
Batch: 40252
01 /18/18 12:38
Run: ICPMS205-H_ 180118A 01/18/18 12:49
85 115
Run: ICPMS205-H_ 180118A 01 /18/18 12:53
75 125
Run: ICPMS205-H_180118A 01 /18/18 13:01
75 125
Run: ICPMS205-H_ 180118A
~ ~ 1~ 1.5
01/18/1813:05
20
ND -Not detected at the reporting limit.
Page 28 of 42
EI\ERGY •' Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.68&.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Quarterly Air Analysis
Analyte Count Result Units
Method: E903.0
Lab ID: LCS-50967
Radium 226
Lab ID: MB-50967
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C18010131-005AMS
Radium 226
Lab ID: C18010131-005AMSD
Radium 226
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Laboratory Control Sample
78.5 pCi/L
Method Blank
0.2 pCi/L
0.2 pCi/L
0.3 pCi/L
Sample Matrix Spike
101 pCi/L
Sample Matrix Spike Duplicate
120 pCi/L
Report Date: 01/25/18
Work Order: C18010137
RL %REC Low Limit High Limit
Run : G5000W_ 180112A
83 80 120
Run: G5000W_180112A
Run: G5000W_180112A
100 70 130
Run: G5000W_ 180112A
121 70 130
ND -Not detected at the reporting limit.
RPO RPDLimit Qual
17
Batch: 50967
01/22/18 10:48
01/22/18 10:48
u
01/22/18 10:48
01/22/18 10:48
20
U -Not detected at minimum detectable concentration
Page 29 of 42
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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
Project: Quarterly Air Analysis
Analyte Count Result Units
Method: E908.0
Lab ID: LCS-50967
Thorium 230
Lab ID: C18010025-002AMS
Thorium 230
Lab ID: C18010025-002AMSD
Thorium 230
Lab ID: MB-50967
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
6
MDC -Minimum detectable concentration
Laboratory Control Sample
27.6 pCi/L
Sample Matrix Spike
50.2 pCi/L
Sample Matrix Spike Duplicate
52.4 pCi/L
Method Blank
0.6 pCi/L
0.4 pCi/L
0.6 pCi/L
0.07 pCi/L
0.2 pCi/L
0.5 pCi/L
Report Date: 01/25/18
Work Order: C18010137
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_ 180116A
116 80 120
Run: EGG-ORTEC_180116A
97 70 130
Run: EGG-ORTEC_ 180116A
102 70 130 4.3
Run: EGG-ORTEC_180116A
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 50967
01/18/18 09:36
01/18/18 09:36
01/18/18 09:36
20
01 /18/18 09:36
u
u
Page 30 of 42
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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
Project: Quarterly Air Analysis
Analyte Count Result Units
Method:
Lab ID:
Lead 210
E909.0
C18010131-001AMS
Lab ID: C18010131-001AMSD
Lead 210
Method: E909.0
Lab ID: LCS-50967
Lead 210
Lab ID: MB-50967
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Sample Matrix Spike
0.000130 pCi/L
Sample Matrix Spike Duplicate
0.000147 pCi/L
Laboratory Control Sample
184 pCi/L
Method Blank
-5 pCi/L
6 pCi/L
10 pCi/L
Report Date: 01/25/18
Work Order: C18010137
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: TRICARB LSC_ 180111A
100 70 130
Run: TRICARB LSC_ 180111A
122 70 130 12
Run: TRICARB LSC_180111 B
102 80 120
Run: TRICARB LSC_ 180111B
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 50967
01/16/18 03:48
01/16/18 04:44
20
Batch: 50967
01/23/18 12:04
01/23/18 15:42
u
Page 31 of 42
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Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: Kasey Vidick
Reviewed Date: 1/7/2018
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 D
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
n/a°C
Yes D
Yes D
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
C18010137
Date Received: 1/4/2018
Received by: kak
Carrier name: NOA
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
Not Present D
Not Present 0
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 32 of 42
Sheet 1 of 1
CHAIN OF CUSTODY·
Samples Shipped to: ~E~n~er~g!-y~La;;;.b~o;.;..;ra;;,,;;ti;.;;,e~s ________ Contact: Garrin Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samplers Name Samplers Slt;anature
4th Quarter Air 2017 Garrin Palmer '
~"'" J _,, -~, II ?/A,,
Time
SamolelD Date Collected Collected Laboratorv Analvsis Requested
BHV-1 9/25/17 -12/26/17 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
SHV-2 9/25/17 -12/26/17 NA U-NAT TH-230, Ra-226, Pb-210, TH-232
SHV-4 9/25/17 • 12/26/17 NA U-NAT TH-230 Ra-226. Pb-210, TH-232
BHV-5 9/25/17 -12/26/17 NA U-NAT TH-230, Ra-226, Pb-210, TH-232
BHV-6 9/25/17 -12/26/17 NA U-NAT, TH-230, Ra-226 Pb-210, TH-232
BHV-7 9/25/17 -12/26/17 NA U-NAT, TH-230. Ra-226, Pb-210, TH-232
BHV-8 9/25/17 -12/26/17 NA U-NAT. TH-230, Ra-226 Pb-210 TH-232
Blanks 9/25/17 -12/26/17 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
('_ \~\ r'"J\~t
Comments: Please send report to Kathy Welnel at kweinelta:!eneravfuels.com
Relinquished By:(Slgnat
&~
Dat7mme Received By:(Signature) ,tJ,,,1 li-uo
Date/Time
Date ime
I .o
--
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2015
BHV~l Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
AH
Sto:ng II
~-To T:, . fa ::·-~. ·--~-~ . ~-·,~ r •· ~; .: ~-,j J.."' --~a,· -;.;:. .. ·: · 1 [, ..
Week Filter Start Stop Start Stop T~ Starting ,.~ .. : Wllly.'A~ ,Ml)!.!\_~ Wkly.Mg.. -~How; ~; ~~: ~. ; .:'fiai, l -~= l.~;:-:.:c· .... • ;~ .
# Number Date Date Time Time T!ffll!: Manometer Manomete~ T"!'JP,• ',·,r. Pre:;sure. "5. . •, --~· . ._.,
1;.,. ··-•,, ~\ _fniin) (in. H20) (in.H20) (m..1¥»·. <'10 -lmmfl&) '-.~~-~ f(fd~ (M .·· !M ~ :lit)' l ~···M_.·. •-' -· -.• t• . .1 ·,
1 9415385 9/25/2017 10/2/2017 84840.6 85006.23 9937.8 4.0 4.0 4.0 13.7 286.9 618.7 1.10 0.93 32.85 9244.0 4.8055 4.9167 111.2 0.0120 98.6
2 9415376 10/2/2017 10/9/2017 85006.23 85172.75 9991.2 4.0 4.0 4.0 13.5 286.7 618.0 l.lO 0.93 32.84 9290.5 4.7987 4.8701 71.4 0.0077 99.l
3 9415362 10/9/2017 10/16/2017 85172.75 85345.6 10371.0 4.0 4.0 4.0 10.3 283.5 622.3 1.09 0,94 33.14 9732.5 4.8053 4.9366 131.3 0.0135 102.9
4 9415359 10/16/2017 10/23/2017 85345.6 85510.2 9876.0 4.0 4.0 4.0 11.9 285.0 621.3 1.09 0.94 33.02 9234.9 4.8894 5.1956 306.2 0.0332 98.0
5 9415351 10/23/2017 10/30/2017 85510.2 85676.57 9982.2 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9327.2 4.7870 5.0229 235.9 0.0253 99.0
6 9415343 10/30/2017 11/6/2017 85676.57 85846.33 10185.6 4.0 4.0 4.0 11.5 284.6 616.96 l.lO 0.93 32.93 9498.2 4.7684 5.0514 283.0 0.0298 101.0
7 9415335 l 1/6/2017 11/13/2017 85846.33 86015.46 10147.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9556.0 4.7717 4.9977 226.0 0.0237 100.7
8 9415327 11/13/2017 11/20/2017 86015.46 86181.59 9967.8 4.0 4.0 4.0 5.7 278.9 620.77 l.08 0.95 33.37 9419.8 4.7635 5.0803 316.8 0.0336 98.9
9 9415313 11/20/2017 11/27/2017 86181.59 86350.83 10154.4 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9564.7 4.8357 4.9871 151.4 0.0158 100.7
10 9415311 11/27/2017 12/4/2017 86350.83 86519-41 10114.8 4.0 4.0 4.0 6.2 279.4 619.76 I 08 0.94 33.32 9542.8 4.7947 5.2338 439.1 0.0460 100.3
11 9471098 12/4/2017 12/11/2017 86519.14 86686.9 10065.6 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9936.2 4.6193 4.7783 159.0 0.0160 99.9
12 9471089 12/11/2017 12/18/2017 86686.9 86855.83 10135.8 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9659.l 4.6192 4.8249 205.7 0.0213 100.6
13 9471082 12/18/2017 12/26/2017 86855.83 87046.59 11445.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10924.1 4.5836 4.7816 198.0 0.0181 113.5 ..
Totals 132375.6 14.16 12.27 433.21 124930.1 61.842 64.677 2835.0 0.2960
. -Averages 10182.7 4.0 4.0 4.0 7.9 281.1 620.69385 1.09 0.94 33.32 9610.0 4.757 4.975 218.1 0.0228 101.0
Comments:
Insert weelcly flow check values in yellow columns. --~-:----4 _ .. -.., ........ . --.•. _-,c•-.~ -~ •. • . •
Grd!ff coTunuis-lire ealo:ulmed·'livem!lC5 from the .ma;stitiim.. . ..:-.__._ ....... -·---.~~---~"-~ .... -,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV 2 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
-Orifice SIN: 8091779
Ml Ml AH fo · '1'/l . Pa '. ··Q]l ... 1• · ~-· ~.-:Q$; • · 'To(al -1 · •• • ·,. • ... ·,, ,;.-~ c.:~·; .. ;, ' . . .. . . • .. ,. -. . •.. • 'I . -.. c..;. ,,.
Week Filter Start Stop S'.art Stop TCIIIII Starting Stopping ~~-. Wkly, Mg. ~(~~ Wkly. A~~-~.· ;~_-' ., •.. <Sid_·.-~.' ., '. ~-'. ~· · ~-" ; -~~:.', ~-'.~~·. ~-.
# Number Date Date Tune Tune TUii,,, Manometer Manometer MliiolllCUll. TetJI{>, ~-l'J:e;ssur,, • ..•. 11 ., :~ .!6h: ,~-·~ I ~: ~ . {c,.:<, .
(lliie) (in. H20) (!!I. H20) (in., ff.Q}. C"(;) 00: . lnimHgJ J:lil~~; ·Wlll)ll!l1 iJfimi3) . · C!.11,')_ . (g) , {Ill . .Jmilt_ . · • _.. ~ .
I 9415384 9/25/2017 10/2/2017 95448.07 95614.35 9976.8 4.0 4.0 4.0 13.7 286.9 618.74 1.10 0.93 32.85 9280.3 4.8122 4.9658 153.6 0.0166 99,0
2 9415375 10/2/2017 10/9/2017 95614.35 95780.33 9958.8 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9260.4 4.8247 5.0438 219.1 0.0237 98.8
3 9415363 10/9/2017 10/16/2017 95780.33 95953.17 10370.4 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9731.9 4.8415 5.1470 305.5 0.0314 102.9
4 9415358 10/16/2017 10/23/2017 95953.17 96117.67 9870 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9229.3 4.7984 5.2062 407.8 0.0442 97.9
5 9415350 10/23/2017 10/30/2017 96117.67 96284.66 10019.4 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9362.0 4.7780 5.0559 277.9 0.0297 99.4
6 9415342 10/30/2017 11/6/2017 96284.66 96453.69 10141.8 4.0 5.0 4.5 11.5 284.6 616.96 1.16 0.99 34.91 10026.6 4.7826 5.1836 401.0 0.0400 100.6
7 9415334 11/6/2017 11/13/2017 96453.69 96623.48 . 10187.4 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9593.3 4.7850 5.0931 308.1 0.0321 IOI.I
8 9415326 11/13/2017 11/20/017 96623.48 96788.54 9903.6 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9359.2 4.7748 5.1963 421.5 0.0450 98.2
9 9415314 11/20/2017 11/27/2017 96788.54 96958.83 10217.4 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9624.1 4.8291 5.2413 412.2 0.0428 101.4
10 9415310 11/27/2017 12/4/2017 96958.83 97126.02 10031.4 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9464.1 4.8150 5.2559 440.9 0.0466 99.5
11 947199 12/4/2017 12/11/2017 97126.02 97294.17 10089 4.0 4.0 4.0 0.4 273.5 625.34 1.07 0.96 33.83 9664.3 4.6196 4,9716 352.0 0.0364 JOO.I
12 9471090 12/11/2017 12/18/2017 97294.17 97463.88 10182.6 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9703.7 4.6017 5.1184 516.7 0.0532 101.0
13 9471083 12/18/2017 12/26/2017 97463.88 97653.94 11403.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10884.0 4.6233 4.8907 267.4 0.0246 113.1
Totals 132352.2 14.20 12.29 434.16 125183.0 61.886 66.370 4483.7 0.4663
. Averages 10180.9 4.0 4.1 4.0 7.9 281.1 620.69385 1.09 0.95 33.40 9629.5 4.760 5.105 344.9 0.0359 101.0
Comments:
Insert weekly flow check values in yellow columns. ;:I -==
·. ·, -.. . . .~-' .. _,-.,.-_J
Green ro1u,nos 11r1railtsulftted a~ from ttie met sun.ion. ,
-----· -·-· .. --.=i
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-4 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
6H .II.If .Aff .-, Tn ,.. . Pa ·:Qia· ' • :~~ ~ TG.111, . ~~·; ~· • Week Filrer Start Stop Start Stop .Toti! Starting Stopping A~· Wlcly. Avg. ~t.i,... Wl1,b,Avg. (A¢Fkllio .'Aiiw. '$Iii; ' .,_ ' 'Giiiit . . .
·-v.;.· ~ . . . ,. : .. _ '}•
# Number Date Dare Time Time . Tmill Manometer Manomerer ~ Temp. T6'J. l?ressun,
(II(~):
. •' ~ J~\: WqJI&· -~:;j '"""" -r ,\..·t"'·"'-' ·-(inl_al (in.H,Q) (in. H,O) -~~) ("Cl lin lm.mllg) . -' ·.(111'/..ii>_ .--flft"t . (gJ w ~ -. '.(mj)t .~ -:--
I 9415383 9/25/2017 10/2/2017 1008.86 1175.3 9986.4 4.0 3.5 3.8 13.7 286.9 618.74 1.07 0.90 31.81 8996.5 4.8070 4.8918 84.8 0.0094 99.1
2 9415374 10/2/2017 10/9/2017 1175.3 1340.07 9886.2 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9192.9 4.8125 4.9483 135.8 0.0148 98.1
3 9415364 10/9/2017 10/16/2017 1340.07 1513.33 10395.6 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9755.6 4.8356 4.9662 130.6 0.0134 103.1
4 9415357 10/16/2017 10/23/2017 1513.33 1677.86 9871.8 4.0 3.5 3.8 11.9 285.0 621.28 1.06 0.91 31.98 8940.1 4.8121 5.0252 213.1 0.0238 97.9
5 9415349 10/23/2017 10/30/2017 1677.86 1845.57 10062.6 4.0 4.0 4,0 12.7 285.8 622.04 L.09 0.93 33.00 9402.4 4.8046 4.9535 148.9 0.0158 99.8
6 9415341 10/30/2017 11/6/2017 1845.57 2015.18 10176.6 4.0 5.0 4.5 11.5 284.6 616.96 1.16 0.99 34.91 10061.0 4.7898 4.9532 163.4 0.0162 101.0
7 9415333 11/6/2017 11/13/2017 2015,18 2183.16 10078.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9491,0 4.7479 4.8427 94.8 0.0100 100.0
8 9415325 11/13/2017 11/20/2017 2183.16 2347.12 9837.6 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9296.8 4.7818 4.9473 165.5 0.0178 97.6
9 9415315 11/20/2017 11/27/2017 2347.12 2515.55 10105.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9519.0 4.8471 4.9387 91.6 0.0096 100.3
10 9415309 11/27/2017 12/4/2017 2515.55 2684.66 10146.6 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9572.8 4.8074 5.0433 235.9 0.0246 100.7
II 9471100 12/4/2017 12/11/2017 2684.66 2850.15 9929.4 4.0 5.0 4.5 0.4 273.5 625.34 1.13 1.02 35.86 10083.8 4.6233 4.7118 88.5 0.0088 98.5
12 9471091 12/11/2017 12/18/2017 2850.15 3018.97 10129.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9652.8 4.6381 4.7970 158.9 0.0165 100.5
13 9471084 12/18/2017 12/26/2017 3018.97 3209.98 11460.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10938.4 4.6135 4.7691 155.6 0.0142 113.7 -Totals 132067.2 14.19 12.29 434.12 124902.9 61.921 63.788 1867.4 0.1950
Averages 10159.0 4.0 4.1 4.0 7.9 281.1 620.69385 1.09 0.95 33.39 9607.9 4.763 4.907 143.6 0.0150 100.8
Comments:
Insert weekly flow check values ~yellow columns. t --~· ---.·.. --·· ... -.. -_ -::i
Gn;en eolum~ &JC calo,il~(e.11 ~VCf\lSCS fmm 1heme1 SlllliQn. I
=,_.,·-. ... . ~ ·-·, .... ----,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-5 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.0106 Updated: 7/30/14
Orifice SIN: 8091779
AH AH .AH ·Ta .:ta· Au . ~-.!_:o.. ~ ~·: ~--.. ~· I? Week Filter Start Stop Start Stop TOIIII Staning Stopping ,. ... Wkly.A•t ~Al$i Wkly A~ :-'d.~ Slct;FJIN :&IL~-. . Sli1: ;.-r..: . Weit '
# Number Do.te Date Time Time 1-Manometer Manomete, ·= Trb. Te'liiiL Pressu,:e •, ( , -~r Volirio : \Ydd( I Wgli,t" .c!lglif'' . ~]' . ' -· ..
JtlllO)" (in.H20) (in.H20) {IQ . (illnlHg;! Citr'l.migl {M1liniii1.· (~.(11111,· ; (lii'f.. (c) _·qt_ (iitigj 'I ~~
I 9415382 9/25/2017 10/2/2017 94096.92 94263.87 10017 4.0 3.5 3.8 13.7 286.9 618.74 1.07 0.90 31.81 9024.l 4.8041 4.9042 JOO.I 0.0111 99.4
2 9415373 10/2/2017 I0/9/2017 94263.87 94428.46 9875.4 4.0 4.0 4.0 13.5 286.7 617.98 LIO 0.93 32.84 9182.8 4.8218 4.9906 168.8 0.0184 98.0
3 9415365 I0/9/2017 I0/16/2017 94428.46 94601.75 10397.4 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9757.2 4.8132 5.0160 202.8 0.0208 103.1
4 9415356 10/16/2017 I0/23/2017 94601.75 94766.39 9878.4 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9237.1 4.7885 5.0219 233.4 0.0253 98.0
5 9415348 10/23/2017 10/30/2017 94766.39 94934.02 10057.8 3.5 4.0 3.8 12.7 285.8 622.0 1.06 0.90 31.96 9101.8 4.8046 4.9928 188.2 0.0207 99.8
6 9415340 10/30/2017 11/6/2017 94934.02 95103.76 10184.4 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9497.1 4.7912 5.0039 212.7 0.0224 101.0
7 9415332 1116/2017 11/13/2017 95103.76 95271.24 10048.8 4.0 4.5 4.3 7.7 280.9 620.77 1.12 0.97 34.27 9751.7 4.7726 4.9146 142.0 0.0146 99.7
8 9415324 11113/2017 11/20/2017 95271.24 95435.57 9859.8 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9317.8 4.8278 5.0561 228.3 0.0245 97.8
9 9415316 11120/2017 11127/2017 95435.57 95603.65 10084.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9499.2 4.8326 4.9467 114.1 0.0120 100.0
10 9415308 11/27/2017 12/4/2017 95603.65 95773.09 10166.4 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9591.5 4.8107 5.0872 276.5 0.0288 100.9
11 9415301 12/4/2017 12/11/2017 95773.09 95938.18 9905.4 4.0 4.5 4.3 0.4 273.5 625.34 LIO 0.99 34.86 9778.l 4.7668 4.8947 127.9 0.0131 98.3
12 9471092 12/11/2017 12/18/2017 95938.18 96107.05 10132.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9655.7 4.6158 4.7976 181.8 0.0188 100.5
13 9471085 12/18/2017 12/26/2017 96107.05 96298.05 11460 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10937.8 4.6216 4.8109 189.3 0.0173 113.7 ..
Totals 132067.8 14.13 12.24 432.15 124331.8 62.071 64.437 2365.9 0.2477
, Averages 10159.1 4.0 4.0 4.0 7.9 28Ll 620.69385 1.09 0.94 33.24 9564.0 4.775 4.957 182.0 0.0191 100.8 -. -
Comments:
losertiweeldy flow check values-in yellow columns. ;c. :..=t=i: k~-~ -,--"-~ ~ ~ colunms me,call:ilh11od a~ fi'c;mi 11\e·nier'.~111ti11n.
~=-•. , ... -·-·-:.c.~ ~ -Iii . .-a -~ ...,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
B·H_V-6 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
t.H t.H ~ Ta ' ,T.1 . Pa Qii · . . ~Q'.· ; : 9s,-. ·. ~~-~--:: ~ .· . I ;:?;-~~
Week Filter Start Stop Start Stop Tocal Starting Stopping Awraje Wlcl)', A,•g. wtJi.AVl!I, Wlcly. Ayg. .ti:,.'~ Ski/~ -~ ·,·$· T• O,fols·: ••• -~ ~-~ ;.. ~ ".
# Number Date Date Time Time Tuno Manometer Manometer ~ Temp, Tcnp. Pres.sure -(~: -voiu.· Wei# -~ W$.\ ··-.. . -. '
~ (in.H20) (in. H20) ~(ln.!lfP)· (•C) {_K} • (mmHg) (~~ .(iifilllil!)l '(~/~ (~"> Ill) (I), -~~ ... ~. ~. ,'t'1), .......... ,
1 9415381 9/25/2017 10/2/2017 10472.39 10638.91 9991.2 4.0 3.0 3.5 13.7 286.9 618.74 1.03 0.87 30.74 8698.0 4.8187 4.9204 101.7 O.ot 17 99.1
2 9415372 10/2/2017 10/9/2017 10638.91 10803.31 9864 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9172.2 4.8424 4.9918 149.4 0.0163 97.9
3 9415366 10/9/2017 10/16/2017 10803.31 10976.85 10412.4 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9771.3 4.8647 5.0649 200.2 0.0205 103.3
4 9415355 10/16/2017 10/23/2017 10976.85 11141.43 9874.8 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9233.8 4.7685 4.9904 221.9 0.0240 98.0
5 9415347 10/23/2017 10/30/2017 11141.43 11309.12 10061.4 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9401.3 4.7778 4.7972 19.4 0.0021 99.8
6 9415339 10/30/2017 11/6/2017 11309.12 11478.25 10147.8 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9462.9 4.7751 4.9729 197.8 0.0209 100.7
7 9415331 11/6/2017 11/13/2017 11478.25 11646.23 10078.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9491.0 4.7766 4.9225 145.9 0.0154 100.0
8 9415323 11/13/2017 11/20/2017 11646.23 11810.12 9833.4 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9292.8 4.8438 5.0330 189.2 0.0204 97.6
9 9415317 11/20/2017 11/27/2017 11810.12 11977.3 10030.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9448.3 4.8697 4.9942 124.5 0.0132 99.5
10 9415307 11/27/2017 12/4/2017 11977.3 12146.38 10144.8 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9571.1 4.8044 5.0842 279 8 0.0292 100,6
11 9415302 12/4/2017 12/11/2017 12146.38 12311.92 9932.4 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9804.7 4.7814 4.9342 152.8 0.0156 98.5
12 9471093 12/11/2017 12/18/2017 12311.92 12480.68 10125.6 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9649.4 4.6273 4.7499 122.6 0.0127 100.5
13 9471086 12/18/2017 12/26/2017 12480.68 12671.71 11461.8 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10939.6 4.6348 4.7794 144.6 0.0132 113.7
Totals 131959.2 14.09 12.21 431.11 123936.5 62.185 64.235 2049.8 0.2151
Averages 10150.7 4.0 4.0 4.0 7.9 281.J 620.69385 1.08 0.94 33.16 9533.6 4.783 4.941 157.7 0.0165 100.7
Comments: Replaced Elapsed time indicator on 7/11/2016
IOS<:rt weekly now checlr'vnlues in yellow columns.
!iJllicS •.. ..
frrecn columns are calool~ averages from the.~ Sfllllon.
.J
ilitill1itiltllUlllilil;~-,an·a ciiu~ _:J
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-7 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
Ml 6H ' AK . ;r.,. :Ti; Pa -~·-'! '":Qi . .--~-".' <~i. -, 1'-",:,i C ~ •• T .. .... ~ -~ itJ · ... " ~!:..•i:--.., .• ,,
Week A.ve:r.ia! Wki1,~-i Wkly. Av:g. ;~~ ·-·~· ~ ...
:~ ·~ !Sid.' -.~'.. ,·:;~\ . ,.~ .. .-Filter Start Stop Start Stop Tomt Starting Stopping Wkly.Avg, ~·~· ' .... _ . \ .. :ivt~~ 1-">'"• ~ ;. .• -:-J-,\. # Number Date Date Time Time • Manometer Manometec ·~ Te.mp. ,.._: ~1.1: ;·.,·• r :: ui;iml!); :·,v~~; .-~ :,,.~,,
(111111) (in. H20) (!n.H20) an:<(¥» ,("C) .:®· -__Lmmlig) ,Jnf/~) .£iii~: . , :~ .. :00 . ... (IJ ~i ~qfjJkl).1 -~f'I .
1 9415380 9/25/2017 10/2/2017 2662.97 2828.6 9937.8 4.0 4.0 4.0 13.7 286.9 618.74 1.10 0.93 32.85 9244.0 4.7948 4.9359 141.1 0.0153 98.6
2 9415371 l0/2/2017 10/9/2017 2828.6 2995.3 10002 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9300.5 4.8430 5.0400 197.0 0.0212 99.2
3 9415367 10/9/2017 l0/16/2017 2995.3 3168.07 10366.2 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9728.0 4.8343 5.1923 358.0 0.0368 102.8
4 9415354 l0/16/2017 l0/23/2017 3168.07 3332.62 9873 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9232.1 4.8000 5.2016 401.6 0.0435 97.9
5 9415346 l0/23/2017 10/30/2017 3332.62 3498.82 9972 4.0 4.0 4.0 12.7 285.8 617.0 1.10 0.93 32.86 9279.3 4.7843 5.1035 319.2 0.0344 98.9
6 9415338 10/30/2017 11/6/2017 3498.82 3668.73 10194.6 4.0 4.0 4.0 11.5 284.6 622.04 1.09 0.94 33.07 9545.9 4.7867 5.0634 276.7 0.0290 IOI.I
7 9415330 11/6/2017 11/13/2017 3668.73 3837.68 10137 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9545.8 4.7622 4.9692 207.0 0.0217 100.6
8 9415322 11/13/2017 11/20/2017 3837.68 4003.38 9942 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9395.4 4.8478 5.3626 514.8 0.0548 98.6
9 9415318 11/20/2017 11/27/2017 4003.38 4173.23 10191 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9599.2 4.8432 5.0421 198.9 0.0207 101.1
10 9415306 11/27/2017 12/4/2017 4173.23 4341.09 10071.6 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9502.1 4.7784 5.1837 405.3 0.0427 99.9
11 9415303 12/4/2017 12/11/2017 4341.09 4509.3 10092.6 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9962.9 4.7879 5.0429 255.0 0.0256 100.1
12 9471094 12/11/2017 12/18/2017 4509.3 4677.72 10105.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9630.0 4.6022 4.8485 246.3 0.0256 100.3
13 9471087 12/18/2017 12/26/2017 4677.72 4868.92 11472 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10949.3 4.6113 4.8493 238.0 0.0217 113.8
1Totals 132357.0 "" 14.16 12.27 433.21 124914.4 62.076 65.835 3758.9 0.3929
Averages 10181.3 4.0 4.0 4.0 7.9 281.1 620.69385 1.09 0.94 33.32 9608.8 4.775 5.064 289.1 0.0302 101.0
Comments: Time Indicator was found broken on 4/10/2017. Replaced Time Indicator on 4/10/2017.
Insert weekly flow check values in yellow columns._ ~
:J . ' .. . .... ··r::.-,,i .-.........
Oreen colu.oms'al'e c:ileulared averagesm,,n themeni,u1on. !
'~.miiiiia~ -,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-8 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
Ml l1H AH . T• T'ar Pa ' 'J~il: . r ;Qs :: 11.· •!.Q,.:·· ' ,-~-:: ·:it:. p :.;:, , ...., .. > -.r:· ~
A~-· . ''A. l~M' I i~: .~~· Week Filter Start Stop Start Stop T°'81 Slatting Stopping Wl;ly 'AYg. ~,. ·g. Wl{.ly ·Mg. Mrt8oiy, ~~ ,,-. ·•·. !I"•: I: ;C;tail . ... ,.';-~ vJi'•·· ' Wdaiit ~ •• :1 ·····; _...._ :-..· .. ~.
# Number Date Date Time Time The Manometer Manometer ~ TeJtrl?. T~. P.nossore. ,~.,~{ r'~ ' .. ,. ·-~I {milt). (in.H20) (in.H20) (11\:~i()) (":C) . (Kl' (mmllg) (,tl'lnuli). ,i {·1.'t. :.~:.·· .(I) :car ' •(NJ ': :. ' '.1 .,..d'~}-,•
1 9415379 9/25/2017 10/2/2017 9124.1 9289.8 9942 4.0 4.0 4.0 13.7 286.9 618.74 l.10 0.93 32.85 9247.9 4.7819 4.8624 80.5 0.0087 98.6
2 9415370 10/2/2017 10/9/2017 9289.8 9456.72 10015.2 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9312.8 4.8093 4.9349 125.6 0.0135 99.4
3 9415369 10/9/2017 10/16/2017 9456.72 9629.19 10348.2 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 971 l.l 4.8183 4.9659 147.6 0.0152 102.7
4 9415353 10/16/2017 10/23/2017 9629.19 9793.79 9876 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9234.9 4.7737 5.0926 318.9 0.0345 98.0
5 9415345 10/23/2017 10/30/2017 9793.79 9960.00 9972.6 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9318.3 4.8022 4.9766 174.4 0.0187 98.9
6 9415337 10/30/2017 11/6/2017 9960.00 10129.93 10195.8 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9507.7 4.7558 4.9678 212.0 0.0223 10!.l
7 9415329 11/6/2017 11/13/2017 10129.93 10298.93 10140 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9548.6 4.7546 4.8690 114.4 0.0120 100.6
8 9415321 I l/13/2017 11/20/2017 10298.93 10465.22 9977.4 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9428.9 4.8052 5.0604 255.2 0.0271 99.0
9 9415319 11/20/2017 11/27/2017 10465.22 10634.4 10150.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9561.3 4.8279 4.9431 115.2 0.0120 100.7
10 9415305 11/27/2017 12/4/2017 10634.4 10802.75 10101 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9529.8 4.7898 5.0938 304.0 0.0319 100.2
11 9415304 12/4/2017 12/11/2017 10802.75 10970.5 10065 4.0 4.0 4.0 0.4 273.5 625.34 1.07 0.96 33.83 9641.3 4.7702 4.8892 119.0 0.0123 99.9
12 9471095 12/11/2017 12/18/2017 10970.5 11138.87 10102.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9627.1 4.6173 4.7596 142.3 0.0148 100.2
13 9471088 12/18/2017 12/26/2017 11138.87 11330.02 11469 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10946.4 4.6291 4.7516 122.5 0.0112 113.8
Totals 132355.2 14.13 12.24 432.18 124616.1 61.935 64.167 2231.6 0.2342
---Averages 10181.2 4.0 4.0 4.0 7.9 28!.l 620.69385 1.09 0.94 33.24 9585.9 4.764 4.936 171.7 0.0180 101.0
Comments:
Insert weekly flow check values in yellow columns. '""'c"'I !.Lr' ---=~~~-. __ _,__ '-::i
Gretn<:0lum~ = c:11~1.d1ed a"!'1'3,ll,;s' rrom 1~ ~ !n:lition. I .._..,_,_ _____ ai'iiia:" -,
Blanks Period: September 25, 201 7 -
December 26 2017
Week Filter Start Stop Net # Number Date Date
1 9415377 25-Sep-17 02-0ct-17 4.7922
2 9415368 02-0ct-17 09-0ct-17 4.8286
3 9415360 09-0ct-17 16-0ct-17 4.7792
4 9415352 16-0ct-17 23-0ct-17 4.7914
5 9415344 23-0ct-17 30-0ct-17 4.7952
6 9415336 30-0ct-17 06-Nov-17 4.7691
7 9415328 06-Nov-17 13-Nov-17 4.7248
8 9415320 13-Nov-17 20-Nov-17 4.8426
9 9415313 20-Nov-17 27-Nov-17 4.8146
10 9471097 27-Nov-17 04-Dec-17 4.5977
11 9471096 04-Dec-17 11-Dec-17 4.6142
12 9471081 11-Dec-17 18-Dec-17 4.6243
13 9471080 18-Dec-17 25-Dec-17 4.6142
Totals
ATTACHMENT D
AIR PARTICULATE LOADING GRAPHS AND SUPPORTING DATA
0 0 0 !'.=> ....
0 0 0 .... 0 0 0 .... 0 0 0 .... 0 0 0 .... 0 0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
+ 7/5/2010
CIJ 10/5/2010 :I: < I 1/5/2011 ....
+
4/5/2011 )> -· .,
CIJ 7/5/2011 ~
:I: ,...
< 10/5/2011 QJ I N ,... -·
+
1/5/2012 0
4/5/2012 :::::s
CIJ ~
:I: 7/5/2012 QJ < .,
J:,. 10/5/2012
,... -·
+
n
1/5/2013 C -
CIJ 4/5/2013 QJ
:I:
,...
< 7/5/2013 tD I l/1 r-
+
10/5/2013 0 QJ
1/5/2014 Q.
CIJ -· :I: 4/5/2014 :::::s < OQ I C1'l
7/5/2014 -
+ 10/5/2014 3
OQ
CIJ 1/5/2015
........
:I: 3 < I -.J 4/5/2015 w -f 7/5/2015
CIJ 10/5/2015 :I: < 1/5/2016 ' 00
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 !:> 0 0
I-'
I-' 0 0 I-' 0 0 I-' 0 0 0 0 0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
7/5/2010
10/5/2010
1/5/2011
4/5/2011
7/5/2011 J -, • m • ». *• :::c:
10/5/2011 < I
1/5/2012 ~
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7/5/2012 ;::i. -· n
10/5/2012 C -
+ 1/5/2013 Q) ,..
0:, 4/5/2013 tD
:::c: < 7/5/2013
r-
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10/5/2013 a. -· 1/5/2014 :::s OQ
4/5/2014 -
7/5/2014 3 OQ
10/5/2014 .......
3
1/5/2015 w -4/5/2015
7/5/2015
10/5/2015
1/5/2016
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 ~ ....
0 0 .... 0
0 .... 0 0 .... 0 0 0 0
0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
7/5/2010
10/5/2010
1/5/2011
4/5/2011
7/5/2011
a:, :c
10/5/2011 < I
1/5/2012 N
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4/5/2012 Q,)
7/5/2012 ~ -· n
10/5/2012 C -
+ 1/5/2013 Q,) ,..
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10/5/2013 Q. -·
1/5/2014 ::::s
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4/5/2014 -
7/5/2014 3
OQ
10/5/2014 ........
3
1/5/2015 \IJ -4/5/2015
7/5/2015
10/5/2015
1/5/2016
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 0 p I-' b b b I-' b 0 0 I-' 0 0 0 I-' 0 0 0 I-' 0 0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
7/5/2010
10/5/2010
1/5/2011
4/5/2011
7/5/2011 ~ :c
10/5/2011 < I
1/5/2012 .,::a.
-,:,
4/5/2012 OJ
"""l
7/5/2012 " -· n
10/5/2012 C -
+ 1/5/2013 OJ " CJ 4/5/2013 tD
::i: r-< 7/5/2013 0 ~ OJ
10/5/2013 C. -·
1/5/2014 ::::s OQ
4/5/2014 -3 7/5/2014 OQ
10/5/2014 ........
3
1/5/2015 w -4/5/2015
7/5/2015
10/5/2015
1/5/2016
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 !=> 0 0
.... .... 0 0 .... 0 0 .... 0 0 0 0 0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
7/5/2010
10/5/2010
1/5/2011
4/5/2011
7/5/2011 0, :::c
10/5/2011 < I
1/5/2012 u,
"'O
4/5/2012 OJ
7/5/2012 ;:i. -· n
10/5/2012 C -
+ 1/5/2013 OJ ,...
OJ 4/5/2013 tD
:::r: < 7/5/2013
r-
I 0 U"I OJ
10/5/2013 Q. -· 1/5/2014 ::::,
OQ
4/5/2014 -
7/5/2014 3 OQ
10/5/2014 ........
3
1/5/2015 w -4/5/2015
7/5/2015
10/5/2015
1/5/2016
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 !::> 0 0 .... .... 0 0 .... 0 0 .... 0 0 0 0 0 0 0
1/5/2009
4/5/2009
7/5/2009
10/5/2009
1/5/2010
4/5/2010
7/5/2010
10/5/2010
1/5/2011
4/5/2011
7/5/2011
c:,
:I:
10/5/2011 < I
1/5/2012 0\
""C 4/5/2012 DJ
7/5/2012 ;:i. -· n
10/5/2012 C -
+ 1/5/2013 DJ ,...
OJ 4/5/2013 tD
::r: < 7/5/2013
r-
CJ'\ 0 DJ
10/5/2013 Q. -· 1/5/2014 ::::s OQ
4/5/2014 -
7/5/2014 3 OQ
10/5/2014 .......
3
1/5/2015 w -"· 4/5/2015
7/5/2015
10/5/2015
1/5/2016
4/5/2016
7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
0 0 0
0 0 ~
I-' I-' I-' I-'
1/5/2015
2/5/2015
3/5/2015
4/5/2015
5/5/2015
6/5/2015
7/5/2015
8/5/2015
9/5/2015
10/5/2015 -
11/5/2015 0:, ::c
12/5/2015 < I
1/5/2016 .......
2/5/2016
.,,
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3/5/2016 ~ -· n
4/5/2016 C -t 5/5/2016 OJ ~
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8/5/2016 Q. -·
9/5/2016 :::,
OQ
10/5/2016 -3 11/5/2016 OQ
12/5/2016 ........
3
1/5/2017 w -
2/5/2017
3/5/2017
4/5/2017 -
5/5/2017
6/5/2017
7/5/2017
8/5/2017
9/5/2017
10/5/2017
11/5/2017
12/5/2017 -
0 0 0
0 0 0
0 0 0 !:>
1--' 1--' 1--' 1--' 1--'
9/29/2014
10/29/2014
11/29/2014
12/29/2014 l I ~
1/29/2015
2/28/2015
3/31/2015
4/30/2015
5/31/2015
6/30/2015
7/31/2015 a:,
8/31/2015 ::i:
9/30/2015 < I
10/31/2015 00
"'C 11/30/2015 Q,)
12/31/2015 ;:i. -· 1/31/2016 n C -2/29/2016
+
Q,) ,..
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Q.
6/30/2016 -· :::J
7/31/2016 OQ -8/31/2016 3
9/30/2016 OQ .......
10/31/2016 3
11/30/2016 UJ -12/31/2016
1/31/2017
2/28/2017
3/31/2017
4/30/2017
5/31/2017
6/30/2017
7/31/2017
8/31/2017
9/30/2017
10/31/2017
11/30/2017
Energy Fuels Resources -White Mesa Mill Calibration Date: 7nt2016 First Monitoring Quarter 2015
BHV--} Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= L25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
Ml Ml $ , ta 1"~ . Pa ·~ . Qs : .Q!; TOIIII, . ', • · .-.
Week Filter Start Stop Start Stop TOIIII Starting Stopping A~ Wld~.A1'!!· ,~Y,::A!J, """'.)il)'.Avg. Mt.-fi!,w :·$!1.fklw '~~ 'SIIL -~ ': ~ · ~--"~t!:J:: ~
# Number Date Date Time Time TJ!De Manometer Manometer _ . . T,;_mp. 1°eqli-Pressu.re . • . . ., ~ ·v~ -~ ' W6 Weljlir ·,... ·. ~
Cli!JD) (in.H20) (in.H20) (la.1:12Q) fG) 00' (nimRgJ _ (111~ Jlillialn), ~. __ (If)' .®. '__Jg.._ -·Cii!al . ,'.6.ilafm'>: (*)-
1 9472583 6/26/2017 7/3/2017 82653.76 82820.38 9997.2 4.0 4.0 4.0 25.1 298.3 618.7 1.13 0.92 32.38 9166.6 4.9168 5.1575 240.7 0.0263 99.2
2 9472580 7/3/2017 7/10/2017 82820.38 82989.17 10127.4 4.0 4.0 4.0 27.1 300.2 622.0 1.13 0.92 32.36 9280.8 4.9263 5.1907 264.4 0.0285 100.5
3 9472567 7/10/2017 7/17/2017 82989.17 83161.5 10339.8 4.0 4.0 4.0 24.6 297.8 621.0 1.12 0.92 32.47 9506.8 4.8616 5.0299 168.3 0.0177 102.6
4 9472564 7/17/2017 7/24/2017 83161.5 83325.52 9841.2 4.0 4.0 4.0 24.4 297.6 621.3 1.12 0.92 32.49 9053.4 4.8647 5.0042 139.5 0.0154 97.6
5 9472556 7/24/2017 7/31/2017 83325.52 83492.86 10040.4 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9266.6 4.8818 4.9886 106.8 0.0115 99,6
6 9472543 113112017 8n12017 83492.86 83661.8 10136.4 4.o 4.o 4.0 21.1 294.8 632.20 1.11 o.93 32.93 9451.9 4.8825 5.0132 130.7 0.0138 100.6
7 9472535 8/7/2017 8/14/2017 83661.8 83829.07 10036.2 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 9265.3 4.8911 5.0215 130.4 0.0141 99.6
8 9472532 8/14/2017 8/21/2017 83829.07 83997.94 10132.2 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9347.7 4.8781 5.0274 149.3 0.0160 100.5
9 9472519 8/21/2017 8/28/2017 83997.94 84164.8 10011.6 4.0 3.5 3.8 23.2 296.4 621.79 1.09 0.89 31.55 8943.7 4,8915 5.0540 162.5 0.0182 99.3
10 9472511 8/28/2017 9/5/2017 84164.8 84358.91 11646.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10714.9 4.9022 5.1923 290.1 0.0271 115.5
11 9472508 9/5/2017 9/11/2017 84358.91 84500.96 8523.0 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7874.1 4.6303 4.8424 212.1 0.0269 84.6
12 9415394 9/11/2017 9/18/2017 84500.96 84670.03 10144.2 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9402.2 4.8304 4.9735 143.1 0.0152 100.6
13 9415386 9/18/2017 9/25/2017 84670.03 84840.6 10234.2 4.0 4.0 4.0 16.2 289.4 615.69 I.I I 0.93 32.80 9505.7 4.8208 5.1806 359.8 0.0379 101.5
Totals 131210.4 14.53 11.97 422.61 120779.6 63.178 65.676 2497.7 0.2685
_ _ Averages 10093.1 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.51 9290.7 4.860 5.052 192.1 0.0207 JOO.I
Comments:
Insert weekly flow check values in yellow columns. 1
--~-. -----~-. _J Gi,ee/1 columns '!fe,calcrulalJ!id avecigeS'liom 1he me1 station. I ~-iiier,~-.iiio_;~ -------,
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-2 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779 -Lill Lill .&I· ' To Ta. P,a !)I " ~ . Q$, :t••· .. I
Week Filter Stan Stop Stan Stop ni!il Starting Stopping ~. Wkly. Avg. Wldy:,.vs. Wl.:ly. Avg. !~~-~~ ;5id.eo;,·
1:v~e· :rn :· .filrlla. '"M · t~.~r-~~ .~.
-~ . ~('·. -.. !<o. •• ·w~ ,~ :J...~( .· # Number Date Date Time Time :ra Manometer Manometen T~mp. 'J'.emp. Pressure. :(a?~) (~ 't~' . l(tijT (mia). (in. H20) (in. H20) (ijl;up) rC> (19. (mmHg) (l!fiailn>_, (ft"lmio) I -(m~. W-,--J&{--. (11@· . •. -·-.,
1 9472584 6/26/2017 7/3/2017 93261.9 93428.01 9966.6 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9138.5 4.8962 5.2398 343.6 0.0376 98.9
2 9472579 7/3/2017 7/10/2017 93428.01 93596.76 10125 4.0 4.0 4.0 27.l 300.2 622.04 1.13 0.92 32.36 9278.6 4.9066 5.2718 365.2 0.0394 100.4
3 9472568 7/10/2017 7/17/2017 93596.76 93769.65 10373.4 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9537.6 4.8633 5.1259 262.6 0.0275 102.9
4 9472563 7/17/2017 7/24/2017 93769.65 93933.12 9808.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9023.1 4.8854 5.0599 174.5 0.0193 97.3
5 9472555 7/24/2017 7/31/2017 93933.12 94101.11 10079.4 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9302.6 4.8709 5.0410 170.1 0.0183 100.0
6 9472544 7/31/2017 8n/2017 94101.11 94269.94 10129.8 4.0 4.0 4.0 21.7 294,8 632.20 1.11 0.93 32.93 9445.7 4.8980 5.0752 177.2 0.0188 100.5
7 9472536 8/7/2017 8/14/2017 94269.94 94436.43 9989.4 4.0 3.5 3.8 22.2 295.4 621.03 1.08 0.89 31.58 8933.5 4.9018 5.1281 226.3 0.0253 99.1
8 9472531 8/14/2017 8/21/2017 94436.43 94605.52 10145.4 4.0 4.0 4.0 22.l 295.3 620.01 1.12 0.92 32.58 9359.9 4.8914 5.2397 348.3 0.0372 100.6
9 9472520 8/21/2017 8/28/2017 94605.52 94772.23 10002.6 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9224.3 4.8934 5.1229 229.5 0.0249 99.2
10 9472512 8/28/2017 9/5/2017 94772.23 94966.23 11640 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10708.8 4.8736 5.2174 343.8 0.0321 115.5
11 9472507 9/5/2017 9/11/2017 94966.23 95109 8566.2 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7914.0 4.6235 4.8615 238.0 0.0301 85.0
12 9415395 9/11/2017 9/18/2017 95109 95278.17 10150.2 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9407.7 4.8462 5.0341 187.9 0.0200 100.7
13 9415387 9/18/2017 9/25/2017 95278.17 95448.07 10194 4.0 4.0 4,0 16.2 289.4 615.69 I.I I 0.93 32.80 9468.4 4.8792 5.1926 313.4 0.0331 IOI.I
Totals 131170.2 . '------14.53 11.97 422.60 120742.8 63.230 66.610 3380.4 0.3635
-Averages 10090.0 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.51 9287.9 4.864 5.124 260.0 0,0280 JOO.I
Comments:
Insert weekly flow check values in yellow columns. I
~oapl~~-~ ..J Green•99lu~ * ~culn1_ci! ~~~ from ~=m~~tul911. I
--~·Vifales'1nlo«a181~ =1
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-4 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
fill fill 411; Ta ,.-. 1'll Qa. ~-.QI,-Tocal a .
Week Filter Start Stop Start Stop T~ Starting Stopping -~~ Wkly. Avg. Wkly.A'tZ-Wkly . .:O.,g. Act.Row Sld-Fliiw • Std. i:ro,t' Slit; .Tfi!'e:. '~: ' ~--~: ~-
# Number Date Date Time Time 'l'ililo' Manometer Manometer MIDllilil:ili,r Tdmp. Tciilp; Prcs.<uie ·(S(lfM)· Voflllnc: w-•. Wei&ln· ' . wc(gfil ~ (mfo} (in.H20) (in.H20) (J!iltp) (!C) (IQ (mniTig) (111'/mla) (m'hllln} (ft7alinl l,n7 . (i,' ',---lil :-. {iii&} (ia#la,1. ~)
l 9472585 6/26/2017 7/3/2017 68446.83 68614.13 10038 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9204.0 4.9105 5.1278 217.3 0.0236 99.6
2 9472578 7/3/2017 7/10/2017 68614,13 68781.9 10066.2 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9224.7 4.9066 5.1683 261.7 0.0284 99.9
3 9472569 7/10/2017 7/17/2017 68781.9 68954.42 10351.2 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9517.2 4.8767 5.0984 221.7 0.0233 102.7
4 9472562 7/17/2017 7/24/2017 68954.42 69118.56 9848.4 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9060.0 4.8586 5.0250 166.4 0.0184 97.7
5 9472554 7/24/2017 7/31/2017 69118.56 69283.92 9921.6 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9157.0 4.8649 4.9803 115.4 0.0126 98.4
6 9472545 7/31/2017 8n/2017 69283.92 69451.32 10044 4.0 4.0 4.0 21.7 294.8 632.20 I.I I 0.93 32.93 9365.7 4.8842 5.0262 142.0 0.0152 99.6
7 9472537 8n12011 8/14/2017 69451.32 69451.32 0 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 0.0 4.8749 5.0091 134.2 #DIV/0! 0.0
8 9472530 8/14/2017 8/21/2017 0 167.23 10033.8 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9256.9 4.8916 5.0250 133.4 0.0144 99.5
9 9472521 8/21/2017 8/28/2017 167.23 335.12 10073.4 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9289.6 4.8944 5.0735 179.1 0.0193 99.9
10 9472513 8/28/2017 9/5/2017 335.12 530.2 11704.8 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10768.5 4.8750 5.1159 240.9 0.0224 116.1
11 9472506 9/5/2017 9/11/2017 530.2 671.3 8466 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7821.5 4.6408 4.8224 181.6 0.0232 84.0
12 9415396 9/11/2017 9/18/2017 671.3 839.03 10063.8 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9327.7 4.8591 4.9935 134.4 0.0144 99.8
13 9415388 9/18/2017 9/25/2017 839.03 1008.86 10189.8 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9464.5 4.8280 4.9906 162.6 0.0172 IOI.I
Totals 120801.0 14.57 12.00 423.62 111457.2 63.165 65.456 2290.7 #DIV/0!
-Averages 9292.4 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 8573.6 4.859 5.035 176.2 #DIV/0! 92.2
Comments:
Insert weekly flow checkj¥alues in1yellow colwnns. I
er..aoi-aiaua:Cllcullled. ~ -~ ·----p~ ,oolu~ Im!. c,,k;ulorcd a~gl1S f10m the mc1 j f.l\.Uon,
liml Jilter llll!lt!ht. viiueJhno Mlmcohm!lll. .. --,
Energy Fuels Resources -White Mesa Mill Calibration Date: 1n12016 First Monitoring Quarter 2014
Buv· 5 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
fl -Orifice SIN: 8091779
6H 6H :AH Ta. ' Tm·. l'a ~-• .Q,· ·• T«al', , · 1 '.1 , •', • • •1
Week Filter Start Stop Start Stop 'J'.~· Starting Stopping . 4~·: Wkly. Mg. ~· ~ Wlily. Avg. ~~ .. w: ;S@_:~~~., ~:~ ~ . .~. ~· , ;·. ;~-'_' ~.i t;,
# Number Date Date Time Time _rnne· Manometer Manometer ~ T,imp. 't~.. Pressure ...• ,, •.• ·,. _.. ~ V~c· Weijlt ~ ~1. ~.I'. .. . ~ (in. H20) (in. H20) .Iiil.°¥), ~€) .__119._ (mmH&) "(m,hoilJ)., ~~ (ft"l,iia)~ ,,(ti!.') . ; ,(&l,, • ,. _.(gl Q11Bt._,_ !!!!!"!'"l' , ~.}~ •
I 9472586 6/26/2017 7/3/2017 91914.97 92082.58 10056.6 4.0 4.0 4.0 25.I 298.3 618.74 1.13 0.92 32.38 9221.0 4.9007 5.1293 228.6 0.0248 99.8
2 9472577 7/3/2017 7/10/2017 92082.58 92250.43 10071 4.0 4.0 4.0 27.1 300.2 622,04 1.13 0.92 32.36 9229.1 4.9196 5.1821 262.5 0.0284 99.9
3 9472570 7/10/2017 7/17/2017 92250.43 92422.93 10350 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9516.1 4.9108 5.0837 172.9 0.0182 102.7
4 9472561 7/17/2017 7/24/2017 92422.93 92587.05 9847.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9058.9 4.8683 5.0259 157.6 0.0174 97.7
5 9472553 7/24/2017 7/31/2017 92587.05 92752.06 9900.6 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9137.6 4.8926 5.0343 141.7 0.0155 98.2
6 9472546 7/31/2017 8nt2017 92752.06 92919.47 10044.6 4.0 4.0 4.0 21.7 294.8 632.20 1.11 0.93 32.93 9366.3 4.8807 5.0239 143.2 0.0153 99.6
7 9472538 sn12017 8/1412011 92919.47 93088.03 10113.6 4.o 4.o 4.o 22.2 295.4 621.03 1.12 o.92 32.60 9336.7 4.8924 5.0321 139.7 0.0150 100.3
8 9472529 8/14/2017 8/21/2017 93088.03 93255.7 10060.2 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9281.3 4.8820 5.0454 163.4 0.0176 99.8
9 9472522 8/21/2017 8/28/2017 93255.7 93423.24 10052.4 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9270.2 4.8890 5.0594 170.4 0.0184 99.7
10 9472514 8/28/2017 9/5/2017 93423.24 93618.65 11724.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10786.7 4.8787 5.1413 262.6 0.0243 116.3
11 9472502 9/5/2017 9/11/2017 93618.65 93759.73 8464.8 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7820.4 4.6351 4.8039 168.8 0.0216 84.0
12 9415397 9/11/2017 9/18/2017 93759.73 93927.48 10065 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9328.8 4.8413 4.9805 139.2 0.0149 99.9
13 9415389 9/18/2017 9/25/2017 93927.48 94096.92 10166.4 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9442.7 4.8372 5.0004 163.2 0.0173 100.9
Totals 130917.0 14.57 12.00 423.62 120795.8 63.228 65.542 2313.8 0.2487
_ ~ _ Averages 10070.5 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 9292.0 4.864 5.042 178.0 0.0191 99.9
Commcncs:
Insert weekly flow check values in yellow columns. ~ -,
:'/NICI. ' . . -. _J
~columns~,i'calcubled averages from the ~station. :
lalmiiier:"!!,bl---·ilHomnp--. -..:::J
BHV-6
Energy Fuels Resources -White Mesa Mill
Period: June 26, 2017 -September 25, 2017
Week
#
2
3
4
5
6
7
8
9
10
11
12
13
Filter
Number
Start
Date
9472587 I 6/26/2011
9472576 I 7/312017
Stop
Date
7/3/2017
7/10/2017
Start
Time
8384.94
8552.23
9472571 I 111012017 I m112011 I 8720.05
9472560 I 7117/2017 I 112412011 I 8797.98
9472552 I 112412011 I 113112011 I 8962.11
9472547 I 113112011 I 8/7/2017 I 9127.48
9472539 I 81112011 I 8/1412017 I 9294.86
9472528 I 8tt4t2017 I 812112017 I 9463.02
Stop
Time
8552.23
8720.05
8797.98
8962.11
9127.48
9294.86
9463.02
9630.77
9472523 I 812112017 I 8/28/2017 I 9630.77 I 9798.64
9472515 I 8/28/2017 I 91512017 I 9798.64 I 9993.73
9472505 I 91512011 I 911112011 I 9993.73 I 10134.84
9415398 I 911112011 I 9118/2017 I 10134.84 I 10302.57
9415390 I 9/18/2017 I 9/2512011 I 10302.57 I 10472.39
Totals
Toial
TBll6
(ailll}
10037.4
10069.2
4675.8
9847.8
9922.2
10042.8
10089.6
10065
10072.2
11705.4
8466.6
10063.8
10189.2
125247.0
Averaies J 9634.4
Comments: Replaced Elapsed time indicator on 7/11/2016
Insert weekly flow check values in yellow columns.
---.J :G'rccn,columnf :ue'l:alculatcd a~ from•ilic mei,S111iiQil,.
fflier'MilJ!II vallles illmc,r,ee aolmnnt. :J
MI MI ;AH
Starting Stopping A~·
Manometer Manometer ·~
(in. H20) (in. H20) '(IILHP.)
4.o I 4.o I 4.0
4.0 I 4.0 I 4.0
4.0 4.0 4.0
4.0 4.5 4.3
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
4.0 4.0 4.0
Calibration Date: 7n/2016
Calibration Slope & Intercept: m= 1.25008
Orifice SIN: 8091779
Ta Tac Pa
~y. Avg. Wli!r.Ayt. ~ly. A~.g.
Temp.. Te'llip. Pies.sure
(~) ,(IQ (mm Hg)
25.1 298.3 618.74
27.1 300.2 622.04
24.6 297.8 621.03
24.4 297.6 621.28
22.8 295.9 621.8
21.7 294.8 632.20
22.2 295.4 621.03
22.l 295.3 620.01
23.2 296.4 621.79
24.7 297.9 622.04
22.2 295.3 621.79
19.1 292.3 619.25
16.2 289.4 615.69
Qa :Qi<· .Qs,
:Aci/t'low. 'Siil R~ ~f.low . ,. ' • , .• t. I -:-::. ~ ..
.. ·I:(~
(11('/ml!l) _(rjlf!iin.)'. • Ctr/mm)
1.13 0.92 32.38
1.13 0.92 32.36
1.12 0.92 32.47
1.16 0.95 33.47
1.12 0.92 32.59
I.I I 0.93 32.93
1.12 0.92 32.60
1.12 0.92 32.58
1.12 0.92 32.57
1.12 0.92 32.49
1.12 0.92 32.63
1.12 0.93 32.73
I.I I 0.93 32.80
b= -0.0206
First Monitoring Quarter 2014
Updated: 7/30/14
1'Cllil
~-' ~-j ~')
9203.4
9227.5
4299.1
9334.2
9157.5
9364.6
9314.6
9285.7
9288.5
10769.0
7822.0
9327.7
9463.9
,, ' .
~ J ·~1 ~ 1-, --f.~ .. ·' ·· ...... _'· ~·.1 ~-.'·--,,-..
W'djt . w~ ·w· . )_ . . --.... I·'..,~··, ..... ;-.,~.····--;-. ,Cc), . _ _._; . (nig). . . .. ' .. (lj&,). :
4.9233 5.1483 225.0 0.0244 99.6
4.8850 5.1389 253.9 0.0275 99.9
4.9029 5.0185 115.6 0.0269 46.4
4.8395 4.9857 146.2 0.0157 97.7
4.9017 5.0201 118.4 0.0129 98.4
4.8656 5.0059 140.3 0.0150 99.6
4.8655 4.9921 126.6 0.0136 100.1
4.9013 5.0595 158.2 0.0170 99.9
4.8950 5.0719 176.9 0.0190 99.9
4.8954 5.1396 244.2 0.0227 116.1
4.6265 4.8329 206.4 0.0264 84.0
4.8146 4.9585 143.9 0.0154 99.8
4.8344 4.9894 155.0 0.0164 IOI.I
14.60 12.02 424.61 I 115857.7 I 63.151 65.361 I 2210.6 I o.2530
22.7 295.9 I 62 t.43692 1.12 0.92 32.66 8912.1 4.858 5.028 170.0 0.0195 95.6
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
B·HV-7 Period: June 26, 2017 -September 25, 2017 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
llli llli 4Jl ''tn ·ra· Pa Q.il ·~-~ T~•
~-Week Filter Start Stop Start Stop Tolil Starting Stopping A~ Wkly.Avg. ~,.~~~ Wkly. Avg, ~.Fl4w ,$Iii[~ .SIil~, -~ .Taril: ·~· Net "i~
# Number Date Date Time Time Tlllie Manometer Manometer Manomeer Temp. Temp: Pressure ·~ Volmnls · Welilir:I .. w~ ·.-·,,:: • 1 ~i.;"ri
:(min) (in. H20) (in.H20) r~.t1,or, c·c) (IQ ·lmmHg) (m"'~)· :c~•1_ (ft'Jmin}~ . _(Jja'!) -_{JLJ ·--~-; .. ·tq; ·~ ~-......
1 9472588 6/26/2017 7/3/2017 476.06 642.67 9996.6 4.0 4.0 4.0 25.l 298.3 618.74 1.13 0.92 32.38 9166.0 4.9296 5.2029 273.3 0.0298 99.2
2 9472575 7/3/2017 7/10/2017 642.67 811.44 10126.2 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9279.7 4.9170 5.2397 322.7 0.0348 100.5
3 9472572 7/10/2017 7/17/2017 811.44 983.79 10341 4.0 4.0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9507.9 4.9085 5.1476 239.1 0.0251 102.6
4 9472559 7/17/2017 7/2412017 983.79 1147.81 9841.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9053.4 4.8487 5.0018 153.1 0.0169 97.6
5 9472551 7/24/2017 7/31/2017 1147.81 1315.16 10041 4.0 4.0 4.0 22.8 295.9 621.8 1.12 0.92 32.59 9267.2 4.8932 5.0465 153.3 0.0165 99.6
6 9472548 7/31/2017 8nt2017 1315.16 1484.1 10136.4 4.0 4.0 4.0 21.7 294.8 632.20 1.11 0.93 32.93 9451.9 4.8789 5.0318 152,9 0.0162 100.6
7 9472540 8/7/2017 8/14/2017 1484.1 1651.27 10030.2 4.0 4.0 4.0 22.2 295.4 621.03 1.12 0.92 32.60 9259.7 4.9065 5.0482 141.7 0.0153 99.5
8 9472527 8/14/2017 8/2112017 1651.27 1820.26 10139.4 4.0 4.0 4.0 22.I 295.3 620.01 1.12 0.92 32.58 9354.3 4.8747 5.0128 138.1 0.0148 100.6
9 9472524 8/21/2017 8/2812017 1820.26 1987.39 10027.8 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9247.5 4.8779 5.1019 224.0 0.0242 99.5
10 9472516 8128/2017 9/5/2017 1987.39 2181.15 11625.6 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10695.6 4.8979 5.2209 323.0 0.0302 115.3
11 9472504 9/5/2017 9/11/2017 2181.15 2323.32 8530.2 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7880.8 4.6225 4.8737 251.2 0.0319 84.6
12 9415399 9111/2017 9/1812017 2323.32 2492.46 10148.4 4.0 4.0 4.0 19.l 292.3 619.25 1.12 0.93 32.73 9406.1 4.6362 4.8059 169.7 0.0180 100.7
13 9415391 9118/2017 9/2512017 2492.46 2662.97 10230.6 4.0 4.0 4.0 16.2 289.4 615.69 1.11 0.93 32.80 9502.4 4.8506 5.1081 257.5 0.0271 101.5
Totals 131214.6 14.57 12.00 423.62 121072.4 63.042 65.842 2799.6 0.3009 -
~ Averages 10093.4 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.59 9313.3 4.849 5.065 215.4 0.0231 JOO.I
Comments: Time Indicator was found broken on 4/10/2017. Replaced Time Indicator on 4/10/2017.
Insert weekly.flow check values in yellow columns.
"!""-COlillllll'~ilre . .. __J
Gf1!ell ~lumm;-:ue cilt!illat<'d,av_era_ges from 1he ~ $1DliM;
IIIICL'l·iier !ell!! 'lili!m'1iiio!!.9!~ :::J
Energy Fuels Resources -White Mesa Mill Calibration Date: ?n/2016 First Monitoring Quarter 2014
BHV-8 Period: June 26, 2017 -9/25/17 Calibration Slope & Intercept: m= 1.25008 b= -0.0206 Updated: 7/30/14
Orifice SIN: 8091779
MI MI AH. ,:n T11 Rn -~ ~-.~ !cilll'
Week Filter Start Stop Start Stop Tomi Starting I Stopping A~ Wklj'.Avg. ~·M_Sl W.klr, A'i!,: _Aat;Row sui.FICIW ·Sld.Aow Std. ' ' ,._ 0.-,, NIil, i·~-~-
~ ~l~l vcillnilii. Wdslll : ~: ~ ..:,·=·-·.":· # Number Date Date Time Time TIIIIC Manomete,J Manometer Tern!;> "Temp. .Pn;ssare
(in.H20) . (in:,HD), tt{ 00_ . (mmHg) <m'fllllil) (ntlmillf '. Cft"imni( ·-(pf:) . , • _(J) -' (gt -(ma) -~ I, ,{i)'. ~) (in.H20) ~ ..
I 9472589 6/26/2017 7/3/2017 6937.1 7103.71 9996.6 4.0 4.0 4.0 25.1 298.3 618.74 1.13 0.92 32.38 9166.0 4.9128 5.0762 163.4 0.0178 99.2
2 9472574 7/3/2017 7/10/2017 7103.71 7272.5 10127.4 4.0 4.0 4.0 27.1 300.2 622.04 1.13 0.92 32.36 9280.8 4.9086 5.1570 248.4 0.0268 100.5
3 9472573 7/10/2017 7/17/2017 7272.5 7444.84 10340.4 4.0 4,0 4.0 24.6 297.8 621.03 1.12 0.92 32.47 9507.3 4.9174 5.0449 127.5 0.0134 102.6
4 9472558 7/17/2017 7/24/2017 7444.84 7608.86 9841.2 4.0 4.0 4.0 24.4 297.6 621.28 1.12 0.92 32.49 9053.4 4.8678 4.9603 92.5 0.0102 97.6
5 9472550 7/24/2017 7/31/2017 7608.86 7776.2 10040.4 3.5 4.0 3.8 22.8 295.9 621.8 1.09 0.89 31.57 8976.7 4.8916 4.9439 52.3 0.0058 99.6
6 9472549 7/31/2017 8/7/2017 7776.2 7945.14 10136.4 3.5 4.0 3.8 21.7 294.8 632.20 1.07 0.90 31.90 9156.2 4.8763 4.9406 64.3 0.0070 100.6
7 9472541 8/7/2017 8/14/2017 7945.14 8112.42 10036.8 4.5 4.0 4.3 22.2 295.4 621.03 1.15 0.95 33.59 9546.8 4.8835 4.9506 67.1 0.0070 99.6
8 9472526 8/14/2017 8/21/2017 8112.42 8281.37 10137 4.0 4.0 4.0 22.1 295.3 620.01 1.12 0.92 32.58 9352.1 4.8818 5.0371 155.3 0.0166 100.6
9 9472525 8/21/2017 8/28/2017 8281.37 8448.08 10002.6 4.0 4.0 4.0 23.2 296.4 621.79 1.12 0.92 32.57 9224.3 4.8786 4.9812 102.6 0.0111 99.2
10 9472517 8/28/2017 9/5/2017 8448.08 8642.26 11650.8 4.0 4.0 4.0 24.7 297.9 622.04 1.12 0.92 32.49 10718.8 4.8709 5.0957 224.8 0.0210 115.6
II 9472503 9/5/2017 9/11/2017 8642.26 8784.42 8529.6 4.0 4.0 4.0 22.2 295.3 621.79 1.12 0.92 32.63 7880.2 4.6475 4.8383 190.8 0.0242 84.6
12 9415400 9/11/2017 9/18/2017 8784.42 8953.6 10150.8 4.0 4.0 4.0 19.1 292.3 619.25 1.12 0.93 32.73 9408.3 4.8320 4.8571 25.1 0.0027 100.7
13 9415392 9/18/2017 9/25/2017 8953.6 9124.1 10230 4.0 4.0 4.0 16.2 289.4 615.69 I.I I 0.93 32.80 9501.8 4.8355 4.9830 147.5 0.0155 101.5
Totals 131220.0 14.53 11.97 422.56 120772.7 63.204 64.866 1661.6 0.1792
---Averages 10093.8 4.0 4.0 4.0 22.7 295.9 621.43692 1.12 0.92 32.50 9290.2 4.862 4.990 127.8 0.0138 100.1
Comments:
~nsertiweekly flow check values in yellow columns. ~
!!i,.ijii§jijiiiei!_ejiiciijiii. -_-:;---
Green.columns. nre calculnted ave cases-from the.met stntion.
biat iillerc'Mll!llt va1aes-1!!!!! !!!!!!iao1m1119, :J
B~ Period: June 26, 2017 -September
25 2017
Week Filter Start Stop Net # Number Date Date
1 9472581 26-Jun-17 03-Jul-17 4.9220
2 9472566 03-Jul-17 10-Jul-17 4.8670
3 9472565 10-Jul-17 17-Jul-17 4.8563
4 8472557 17-Jul-17 24-Jul-17 4.8583
5 9472542 24-Jul-17 31-Jul-17 4.8870
6 9472534 31-Jul-17 07-Aug-17 4.8722
7 9472533 07-Aug-17 14-Aug-17 4.8972
8 9472518 14-Aug-17 21-Aug-17 4.8801
9 9472510 21-Auo-17 28-Auo-17 4.8952
10 9472509 28-Auo-17 05-Sep-17 4.6300
11 9472501 05-Sep-17 11-Sep-17 4.6224
12 9415393 11-Sep-17 18-Sep-17 4.8199
13 9415378 18-Sep-17 25-Sep-17 4.7980
Totals
Energy Fuels Resources -White Mesa Mill Calibration Date: I 0/4/2017 First Monitoring Quarter 2015
BHV--1 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
---Orifice SIN: 8091779
6H 6H -:.tm " Ta .-,.,_ l!a . ',Qe. · \~., · 'Qij::., :~·I' -1 • : (-. 1"...· ·---, r. · I
Week Filter Start Stop Start Stop ·.· :a:~-Starting Stopping _ _!;~: Wk:Iy.,A~g. !~;-~ w:kly. A\Og. ::'¥=~; -~~ .~1 ~ .:, :J ~~ ii _ ~~ ---:, •. ~ i~J I!~!
# Number Date Date Time Tune .~_. M_anometer M_anometer . ____ ·._ .. , ., Temp. :!~· _ Pressure .. --_, ... · _ .. I: ~: ~-.•. ,, ~· ~ ~-, . -·._.,.' ,. , -·-. ,(dlJ/ij,• . (m. H20) (m. H20) (fn.lfP) fC) , · .t.10 _ -(mml:fg) . (llt'l.mio)_ ,(ll(Ji!ilo>, ;{k'liill!),: · ; C-O-!j , .,..;fifJ-,_ lj;, _ • ~-,}iJlf/JJ/):. c'{18l · :
1 9415385 9/25/2017 10/2/2017 84840.6 85006.23 9937.8 4.0 4.0 4.0 13.7 286.9 618.7 1.10 0.93 32.85 9244.0 4.8055 4.9167 111.2 0.0120 98.6
2 9415376 10/2/2017 10/9/2017 85006.23 85172.75 9991.2 4.0 4.0 4.0 13.5 286.7 618.0 1.10 0.93 32.84 9290.5 4.7987 4.8701 71.4 0.0077 99.1
3 9415362 10/9/2017 10/16/2017 85172.75 85345.6 10371.0 4.0 4.0 4.0 10.3 283.5 622.3 1.09 0.94 33.14 9732.5 4.8053 4.9366 131.3 0.0135 102.9
4 9415359 10/16/2017 10/23/2017 85345.6 85510.2 9876.0 4.0 4.0 4.0 11.9 285.0 621.3 1.09 0.94 33.02 9234.9 4.8894 5.1956 306.2 0.0332 98.0
5 9415351 10/23/2017 10/30/2017 85510.2 85676.57 9982.2 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9327.2 4.7870 5.0229 235.9 0.0253 99.0
6 9415343 10/30/2017 11/6/2017 85676.57 85846.33 10185.6 4.0 4,0 4.0 11.5 284.6 616.96 I.IO 0.93 32.93 9498.2 4.7684 5.0514 283.0 0.0298 101.0
7 9415335 11/6/2017 11/13/2017 85846.33 86015.46 10147.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9556.0 4,7717 4.9977 226.0 0.0237 100.7
8 9415327 11/13/2017 11/20/2017 86015.46 86181.59 9967.8 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9419.8 4.7635 5.0803 316.8 0.0336 98.9
9 9415313 11/20/2017 11/27/2017 86181.59 86350.83 10154.4 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9564.7 4.8357 4.9871 151.4 0.0158 100.7
10 9415311 11127/2017 12/4/2017 86350.83 86519.41 10114.8 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9542.8 4.7947 5.2338 439.1 0.0460 !00.3
11 9471098 12/4/2017 12/11/2017 86519.14 86686.9 10065.6 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9936.2 4.6193 4.7783 159.0 0.0160 99.9
12 9471089 12/11/2017 12/18/2017 86686.9 86855.83 10135.8 4.0 4.0 4.0 1,3 2744 621.03 1.07 0.95 33.65 9659.1 4.6192 4.8249 205.7 0.0213 100.6
13 9471082 12/18/2017 12/26/2017 86855.83 87046.59 11445.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10924. 1 4.5836 4.7816 198.0 0.0181 113.5
!Totals 132375.6 14.16 12.27 433.21 124930. 1 61.842 64.677 2835.0 0.2960
Averages 10182.7 4.0 4.0 4.0 7.9 281.1 620.69385 1.09 0.94 33.32 9610.0 4.757 4.975 218.1 0.0228 101.0
Comments:
Insert weekl.ylflow check values in yellow columns_. 1
-_ .. -~-c·,_·· -~
G,ieen·C1)1umris'arecca1~1.a1cil averascs-rroJ11'llje,!l\l.ct Sint.ion. I
.. =·· • tllllesim-caiamm; :J
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-2 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
Lili Lili 6H 'fa . 'I): P<J ·~. . (is .: :~ "T'.~. I. ..... -:·;,
·-1 mt: ~ . . ' ...
Week Filter Start Stop Start Stop TOflll Starting Stopping ·~~ Wkly, Avg_ Wily.Al'&, Wkly. Avg. : :Act. Flcil" ~~· .Sid.HoiP' : Slit· ·-.
h:·· ,~, ~-Time ··'r~·· •J· . ts!W> ·v~ ·~ ·~·· .w~.' ~ ·::: :,.~ .... -.·-'.:._;:. # Number Date Date Time Time Manometer Manometer Temp. Pressure ~CafJniiii, I ' ·• .•
~'..c (in. H20) (in.H20) . C!ft.:8i9>: c·G> ·.@ .. (mmHJt) .~itnia) (li'~j: J. r.nj._ -.fi); _; .J ·-~~ I ,(mg) . /ffiJt/ilf.) ;' '00:
1 9415384 9/25/2017 10/2/2017 95448.07 95614.35 9976.8 4.0 4.0 4.0 13.7 286.9 618.74 1.10 0.93 32.85 9280.3 4.8122 4.9658 153.6 0.0166 99.0
2 9415375 10/2/2017 10/9/2017 95614.35 95780.33 9958.8 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9260.4 4.8247 5.0438 219.1 0.0237 98.8
3 9415363 10/9/2017 10/16/2017 95780.33 95953.17 !0370.4 4.0 4.0 4.0 l0.3 283.5 622.30 1.09 0.94 33.14 9731.9 4.8415 5.1470 305.5 0.0314 !02.9
4 9415358 10/16/2017 10/23/2017 95953.17 96117.67 9870 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9229.3 4.7984 5.2062 407.8 0.0442 97.9
5 9415350 10/23/2017 l0/30/2017 96117.67 96284.66 10019.4 4.0 4.0 4,0 12.7 285.8 622.0 1.09 0.93 33.00 9362.0 4.7780 5.0559 277.9 0.0297 99.4
6 9415342 10/30/2017 11/6/2017 96284.66 96453.69 10141.8 4.0 5.0 4.5 11.5 284.6 616.96 1.16 0.99 34.91 10026.6 4.7826 5.1836 401.0 0.0400 100.6
7 9415334 1116/2017 11/13/2017 96453.69 96623.48 10187.4 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9593.3 4.7850 5.0931 308.1 0.0321 IOI.I
8 9415326 11/13/2017 11/20/017 96623.48 96788.54 9903.6 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9359.2 4.7748 5.1963 421.5 0.0450 98.2
9 9415314 11/20/2017 11/27/2017 96788.54 96958.83 10217.4 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9624.1 4.8291 5.2413 412.2 0.0428 101.4
10 9415310 11/27/2017 12/4/2017 96958.83 97126.02 10031.4 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9464.1 4.8150 5.2559 440.9 0.0466 99.5
11 947199 12/4/2017 12/11/2017 97126.02 97294.17 10089 4.0 4.0 4.0 0.4 273.5 625.34 1.07 0.96 33.83 9664.3 4.6196 4.9716 352.0 0.0364 100.1
12 9471090 12/11/2017 12/18/2017 97294.17 97463.88 10182.6 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9703.7 4.6017 5.1184 516.7 0.0532 101.0
13 9471083 12/18/2017 12/26/2017 97463.88 97653.94 11403.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10884.0 4.6233 4.8907 267.4 0.0246 113.1
Totals 132352.2 ' 14.20 12.29 434.16 125183.0 61.886 66.370 4483.7 0.4663
Averages 10180.9 4.0 4.1 4.0 7.9 281.1 620.69385 1.09 0.95 33.40 9629.5 4.760 5.105 344.9 0.0359 lOI.O
Comments:
lnsen weekly flow check values in yellow columns. 1
_._ .... , ......... ,, ---····•·,· ~ -. _J
Green columns·:ue calcoWed a ,·emges from the met smnoo. j
lad!,t"iiit,~ ...... --'°"' .... ----,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-4 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -O.ot058 Updated: 7/30/14
Orifice SIN: 8091779
6H 6H 6H . Ta I "fa P3 Qr . QI· . .·Qi· 'tGlid' ·, . k -<·:: .• . ----
Week Filter Start Stop Start Stop ~' Starting Stopping A~-Wkly. A\/g. -:A~ Wkl_y Asg. ·Act·Roi! ~-$Ill.·· ... ~ 'Taa -~.-~Net· ,:, ''~·, 'r~ , Tei$ :(S<l'M), ·, -.·i . \\'#ft.· I---, 1r-.• -# Number Date Date Time Time . Ta Manometer Manometer -~ Ttmj>. Pressure oa'fmin>· (la,iim!n)
''V.olume· Wi¥t' .i~f ~) (in.H20) (in.H20) , .. ;-1~, r e) .(IQ, .. ,(mmH!Q :Cft'Arila), ·~--@ 1 ' (ii',__ ~, ... i: ::/<,,j,
I 9415383 9/25/2017 10/2/2017 1008.86 1175.3 9986.4 4.0 3.5 3.8 13.7 286.9 618.74 1.07 0.90 31.81 89%.5 4.8070 4.8918 84.8 0.0094 99.1
2 9415374 10/2/2017 10/9/2017 1175.3 1340.07 9886.2 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9192.9 4.8125 4.9483 135.8 0.0148 98.1
3 9415364 10/9/2017 10/16/2017 1340.07 1513.33 10395.6 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9755.6 4.8356 4.9662 130.6 0.0134 103.1
4 9415357 10/16/2017 10/23/2017 1513.33 1677.86 9871.8 4.0 3.5 3.8 11.9 285.0 621.28 1.06 0.91 31.98 8940.1 4.8121 5.0252 213.1 0.0238 97.9
5 9415349 10/23/2017 10/30/2017 1677.86 1845.57 10062.6 4.0 4.0 4.0 12.7 285.8 622.04 1.09 0.93 33.00 9402.4 4.8046 4.9535 148.9 0.0158 99.8
6 9415341 10/30/2017 11/6/2017 1845.57 2015.18 IOI76.6 4.0 5.0 4.5 11.5 284.6 616.96 1.16 0.99 34.91 10061.0 4.7898 4.9532 163.4 0.0162 101.0
7 9415333 11/6/2017 11/13/2017 2015.18 2183.16 10078.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9491.0 4.7479 4.8427 94.8 0.0100 100.0
8 9415325 11/13/2017 11/20/2017 2183.16 2347.12 9837.6 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9296.8 4.7818 4.9473 165.5 0.0178 97.6
9 9415315 11/20/2017 11/27/2017 2347.12 2515.55 10105.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9519.0 4,847] 4,9387 91.6 0.0096 100.3
JO 9415309 11/27/2017 12/4/2017 2515.55 2684.66 I0146.6 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9572.8 4.8074 5.0433 235.9 0.0246 100.7
II 9471100 12/4/2017 12/11/2017 2684.66 2850.15 9929.4 4.0 5.0 4.5 0.4 273.5 625.34 1.13 1.02 35.86 10083.8 4.6233 4.7118 88.5 0.0088 98.5
12 9471091 12/11/2017 12/18/2017 2850.15 3018.97 10129.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 095 33.65 9652.8 4.6381 4.7970 158.9 0.0165 100.5
13 9471084 12/18/2017 12/26/2017 3018.97 3209.98 11460.6 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10938.4 4.6135 4.7691 155.6 0.0142 113.7
Totals 132067.2 . 14.19 12.29 434.12 124902.9 61.921 63.788 1867.4 0.1950
-Averages 10159.0 4.0 4.1 4.0 7.9 281.1 620.69385 1.09 0.95 33.39 9607.9 4.763 4.907 143.6 0.0150 100.8
Comments:
lnsen weekly flow check values in yellow columns. I --.... ~.·.: ... :· ·.,,. . :J
'ii~ c_olwnns.an>~uln!Cll a\'CrllgeS fiym ~ffl!.'L;s:131ii>IL -i llioMIUlet-Vlllles --·mllam!IL
,Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-5 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -O.OI06 Updated: 7/30/14
Orifice SIN: 8091779
,lli ,lli ~; .J -T~ .t .. Pn .Qa .;~, ·.~. '.I"~··: I '· I' i_'.·1
Week Filter Start Stop Start Stop 'J'.c'(l_a_l Starting Stopping I .. ~~Ji?/ Wkly. Avg. -~.,A., iWkl~. ~.v( . Ai=':¥. lsiis:i 1'Tcili ~-~ ' ,5,!!l. I~ /Giw,J i . 'Nc:i . ~: '.= # Number Date Date Time Time . 1imo--Manometer Manometel · Temp. 'rel:gl.'~ 'l'ressuic.
I•;··•,·.-. m; votume 'Wd&M _., "'•· ··. C~L (in.H20) (in. H20) @.:&Pf ra> oo: -· <mml-lg) ~~-·:~) --~(la):.· .. Ji>-~-~~. (~f F ~.
1 9415382 9/25/2017 10/2/2017 94096.92 94263.87 10017 4.0 3.5 3.8 13.7 286.9 618.74 1.07 0.90 31.81 9024.1 4.8041 4.9042 100.1 0.0111 99.4
2 9415373 10/2/2017 10/9/2017 94263.87 94428.46 9875.4 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9182.8 4.8218 4.9906 168.8 0,0184 98.0
3 9415365 10/9/2017 10/16/2017 94428.46 94601.75 10397.4 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9757.2 4.8132 5.0160 202.8 0.0208 103.1
4 9415356 10/16/2017 10/23/2017 94601.75 94766.39 9878.4 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9237.1 4.7885 5.0219 233.4 0.0253 98.0
5 9415348 10/23/2017 10/30/2017 94766.39 94934.02 10057.8 3.5 4.0 3.8 12.7 285.8 622.0 1.06 0.90 31.96 9101.8 4.8046 4.9928 188.2 0.0207 99.8
6 9415340 10/30/2017 11/6/2017 94934.02 95103.76 10184.4 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9497.1 4.7912 5.0039 212.7 0.0224 101.0
7 9415332 11/6/2017 11/13/2017 95103.76 95271.24 10048.8 4.0 4,5 4.3 7.7 280.9 620.77 1.12 0.97 34.27 9751.7 4.7726 4.9146 142.0 0,0146 99.7
8 9415324 11/13/2017 11/20/2017 95271.24 95435.57 9859.8 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9317.8 4.8278 5.0561 228.3 0.0245 97.8
9 9415316 11/20/2017 11/27/2017 95435.57 95603.65 10084.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9499.2 4.8326 4.9467 114.1 0.0120 100.0
10 9415308 11/27/2017 12/4/2017 95603.65 95773.09 10166.4 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9591.5 4.8107 5.0872 276.5 0.0288 100.9
11 9415301 12/4/2017 12/11/2017 95773.09 95938.18 9905.4 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9778.1 4.7668 4.8947 127.9 0.0131 98.3
12 9471092 12/11/2017 12/18/2017 95938.18 96107.05 10132.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9655.7 4.6158 4.7976 181.8 0.0188 100.5
13 9471085 12/18/2017 12/26/2017 96107.05 96298.05 11460 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10937.8 4.6216 4.8109 189.3 0.0173 113.7
Totals 132067.8 14.13 12.24 432.15 124331.8 62.071 64.437 2365.9 0.2477
--Averages 10159.1 4.0 4.0 4.0 7.9 281.1 620.69385 1.09 0.94 33.24 9564.0 4.775 4.957 182.0 0.0191 100.8
Comments:
Insert weekly flow check values in yellow columns. I
-~~;··· -·~ --.._.J
~.c;_olumns'~a lcµl~.a~li'ori:I ~ID@:~~~-
·= ··-.ftlllelfllfo-colamas. ---,
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
BHV-6 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
AH AH •·&:I i:a. Ta: Pa ~ .. -,~ .Qr<, -·'ttiull ·. ·J I . -
Week Filter Start Stop Start Stop TO!ll'. Starting Stopping A~ Wkly.Mg. ~.:A\jg. Wlily.Avg. ~Flaw .Sti:f/.~· S(U.How,! ·•· Tlli'e' Giilll$ ;,'Nil ~I .~·
# Number Date Date Time Time ,._, Manometer Manometer -~ Temp. Temp.: ~ .:e . Nillllsm ;~:, I .• , ·"Weijjllt. 8iislieam
...(~},,_ (in.H20) (in. H20) 5m.'ffi0} t°C l ll'll '(!nmlfg) (.li(lininj ' .Jin.fniii,} (ln'")" -;(j}. .. ·1-~ ~. ~ ~
1 9415381 9/25/2017 10/2/2017 10472.39 10638.91 9991.2 4.0 3.0 3.5 13.7 286.9 618.74 1.03 0.87 30.74 8698.0 4.8187 4.9204 101.7 0.0117 99.1
2 9415372 10/2/2017 10/9/2017 10638.91 10803.31 9864 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9172.2 4.8424 4.9918 149.4 0.0163 97.9
3 9415366 10/9/2017 10/16/2017 10803.31 10976.85 10412.4 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9771.3 4.8647 5.0649 200.2 0.0205 103.3
4 9415355 10/16/2017 10/23/2017 10976.85 11141.43 9874.8 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9233.8 4.7685 4.9904 221.9 0.0240 98.0
5 9415347 10/23/2017 10/30/2017 11141.43 11309.12 10061.4 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9401.3 4.7778 4.7972 19.4 0.0021 99.8
6 9415339 10/30/2017 11/6/2017 11309.12 11478.25 10147.8 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9462.9 4.7751 4.9729 197.8 0.0209 100.7
7 9415331 11/6/2017 11/13/2017 11478.25 11646.23 10078.8 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9491.0 4.7766 4.9225 145.9 0.0154 100.0
8 9415323 11/13/2017 11/20/2017 11646.23 11810.12 9833.4 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9292.8 4.8438 5.0330 189.2 0.0204 97.6
9 9415317 11/20/2017 11/27/2017 11810.12 11977.3 10030.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9448.3 4.8697 4.9942 124.5 0.0132 99.5
10 9415307 11/27/2017 12/4/2017 11977.3 12146,38 10144.8 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9571.1 4.8044 5.0842 279.8 0.0292 100.6
11 9415302 12/4/2017 12/11/2017 12146.38 12311.92 9932.4 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9804.7 4.7814 4.9342 152.8 0.0156 98.5
12 9471093 12/11/2017 12/18/2017 12311.92 12480.68 10125.6 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9649.4 4.6273 4.7499 122.6 0.0127 100.5
13 9471086 12/18/2017 12/26/2017 12480.68 12671.71 11461.8 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10939.6 4.6348 4.7794 144.6 0.0132 113.7
Totals 131959.2 14.09 12.21 431.11 123936.5 62.185 64.235 2049.8 0.2151
Averages 10150.7 4.0 4.0 4.0 7.9 281.1 620.69385 1.08 0.94 33.16 9533.6 4.783 4.941 157.7 0.0165 100.7
Comments: Replaced Elapsed time indicator on 7/11/2016
Insert weekly flow check values in yellow columns.
!. ' . . ....,..,.,..~----.,. -~ i reen rotum_nsann:alcut:il(l(I a~from the,metstn.tion.
L-·~rnmJ.= l
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
EHV-7 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
IUi L\.H •• T:a. :ra: · ·l?a -~l'/lit.--,~· . CJ$:: ~'l'o111f ,: .• • I 1-.... .•• i-Week Filter Start Stop Stan Stop ~ Starting Stopping ·~-: Wkly.Av,g. ~-:'A~ Wkly.,Av,g. ~~1 1.sail=low ;~ °:-Slli: :· Te. '.Uiillis' ··-•· I~ . ... ..,.-. ,, .. ..... '-'"''. , . --••.. !'..:·~-,..,,_., ... J
# Number Date Date Time Time -Timc · Manometer Manometer .:f\;ffip: J>ressu,:e ~-··-YOli11111s' .. ~ ... ;. caft/ill~ ~' (in.H20) (in.H20) ·_(iii;¥), ~C) ~! i1{mniHg),,, (m"Jiiioo :(oi'/ffli9J. .taO'' ... ,(I)~ -•. -bl);_ . :{llm): . ~' · . -.:.~
1 9415380 9/25/2017 10/2/2017 2662.97 2828.6 9937.8 4.0 4.0 4.0 13.7 286.9 618.74 LIO 0.93 32.85 9244.0 4.7948 4.9359 141.1 0.0153 98.6
2 9415371 10/2/2017 10/9/2017 2828.6 2995.3 10002 4.0 4.0 4.0 13.5 286.7 617.98 LIO 0.93 32.84 9300.5 4.8430 5.0400 197.0 0.0212 99.2
3 9415367 10/9/2017 10/16/2017 2995.3 3168.07 10366.2 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9728.0 4.8343 5.1923 358.0 0.0368 102.8
4 9415354 10/16/2017 10/23/2017 3168.07 3332.62 9873 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9232.1 4.8000 5.2016 401.6 0.0435 97.9
5 9415346 10/23/2017 10/30/2017 3332.62 3498.82 9972 4.0 4.0 4.0 12.7 285.8 617.0 1.10 0.93 32.86 9279.3 4.7843 5.1035 319.2 0.0344 98.9
6 9415338 10/30/2017 11/6/2017 3498.82 3668.73 10194.6 4.0 4.0 4.0 11.5 284.6 622.04 1.09 0.94 33.07 9545.9 4.7867 5.0634 276.7 0.0290 IOI.I
7 9415330 11/6/2017 11/13/2017 3668.73 3837.68 10137 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9545.8 4.7622 4.9692 207.0 0.0217 100.6
8 9415322 11/13/2017 11/20/2017 3837.68 4003.38 9942 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9395.4 4.8478 5.3626 514.8 0.0548 98.6
9 9415318 11/20/2017 11/27/2017 4003.38 4173.23 10191 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9599.2 4.8432 5.0421 198.9 0.0207 IOI.I
10 9415306 11/27/2017 12/4/2017 4173.23 4341.09 10071.6 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9502.1 4.7784 5.1837 405.3 0.0427 99.9
11 9415303 12/4/2017 12/11/2017 4341.09 4509.3 10092.6 4.0 4.5 4.3 0.4 273.5 625.34 1.10 0.99 34.86 9962.9 4.7879 5.0429 255.0 0,0256 JOO.I
12 9471094 12/11/2017 12/18/2017 4509.3 4677.72 10105.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9630.0 4.6022 4.8485 246.3 0.0256 100.3
13 9471087 12/18/2017 12/26/2017 4677.72 4868.92 11472 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10949.3 4.6113 4.8493 238.0 0.0217 113.8
Totals 132357.0 14.16 12.27 433.21 124914.4 62.076 65.835 3758.9 0.3929
Averages 10181.3 4.0 4.0 4.0 7.9 281.1 620.69385 1.09 0.94 33.32 9608.8 4.775 5.064 289.1 0.0302 101.0
Comments: Time Indicator was found broken on 4/10/2017. Replaced Time Indicator on 4/10/2017.
Insert, weekly flow check values in r,ellow columns .
...... ••• ,0( L'I• •· ... ·." _-•~._..•'-""-.c,"",.,.,,=""_ O: -• _ _:,• -... . • __.J
Green columt1s,11WoaJ.coJl)[ed,a~'fr,om 1M met slation. I
~ ·~--..,.. -, ,•
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017 First Monitoring Quarter 2014
I BHV-8 Period: September 25, 2017 -December 26, 2017 Calibration Slope & Intercept: m= 1.24782 b= -O.DI058 Updated: 7/30/14
Orifice SIN: 8091779
.. filf filf .AB ' T11 Ti.· . .ea .Qa . . 'Qs-,..,' -Q:l .. ..... . -...-. ; :-: ->, . = T~ '"~· ~,.K,'v,. ~~ I --• I ~'.~: l'. •. I ~··.1 ·,c :-_:~ ,;~-Week Filter Start Stop Start Stop Starting Stopping Wkly.Avg. Wl(ly. Avg. I ~~ __ ,., .. ·;~· ~tt~ # Number Date Date Time Time :rllne' Manometer Manometer ~ Temp. '.[~ Pressure • I I -~ ,tcil&iail,. ... . .... , (in.H20) (in.H20) '(lii;:H§):: '("C)' (IQ:· (mll!Hg) -~l'milij . im~llllnf (tt'i.Dj~; . __ ,(~·.; _;Cl);:i.:: ... _(&;'._ '_<~:'. '= i(J;):
I 9415379 9/25/2017 10/2/2017 9124.1 9289.8 9942 4.0 4.0 4.0 13.7 286.9 618.74 1.10 0.93 32.85 9247.9 4.7819 4.8624 80.5 0.0087 98.6
2 9415370 10/2/2017 10/9/2017 9289.8 9456.72 10015.2 4.0 4.0 4.0 13.5 286.7 617.98 1.10 0.93 32.84 9312.8 4.8093 4.9349 125.6 0.0135 99.4
3 9415369 10/9/2017 10/16/2017 9456.72 9629.19 10348.2 4.0 4.0 4.0 10.3 283.5 622.30 1.09 0.94 33.14 9711.1 4.8183 4.9659 147.6 0.0152 102.7
4 9415353 10/16/2017 10/23/2017 9629.19 9793.79 9876 4.0 4.0 4.0 11.9 285.0 621.28 1.09 0.94 33.02 9234.9 4.7737 5.0926 318.9 0.0345 98.0
5 9415345 10/23/2017 10/30/2017 9793.79 9960.00 9972.6 4.0 4.0 4.0 12.7 285.8 622.0 1.09 0.93 33.00 9318.3 4.8022 4.9766 174.4 0.0187 98.9
6 9415337 10/30/2017 11/6/2017 9960.00 10129.93 10195.8 4.0 4.0 4.0 11.5 284.6 616.96 1.10 0.93 32.93 9507.7 4.7558 4.9678 212.0 0.0223 101.l
7 9415329 11/6/2017 11/13/2017 10129.93 10298.93 10140 4.0 4.0 4.0 7.7 280.9 620.77 1.09 0.94 33.26 9548.6 4.7546 4.8690 114.4 0.0120 100.6
8 9415321 11/13/2017 11/20/2017 10298.93 10465.22 9977.4 4.0 4.0 4.0 5.7 278.9 620.77 1.08 0.95 33.37 9428.9 4.8052 5.0604 255.2 0.0271 99.0
9 9415319 11/20/2017 11/27/2017 10465.22 10634.4 10150.8 4.0 4.0 4.0 8.5 281.6 622.80 1.09 0.94 33.26 9561.3 4.8279 4.9431 115.2 0.0120 100.7
10 9415305 11/27/2017 12/4/2017 10634.4 10802.75 10101 4.0 4.0 4.0 6.2 279.4 619.76 1.08 0.94 33.32 9529.8 4.7898 5.0938 304.0 0.0319 100.2
II 9415304 12/4/2017 12/11/2017 10802.75 10970.5 10065 4.0 4.0 4.0 0.4 273.5 625.34 1.07 0.96 33.83 9641.3 4.7702 4.8892 119.0 0.0123 99.9
12 9471095 12/11/2017 12/18/2017 10970.5 11138.87 10102.2 4.0 4.0 4.0 1.3 274.4 621.03 1.07 0.95 33.65 9627.1 4.6173 4.7596 142.3 0.0148 100.2
13 9471088 12/18/2017 12/26/2017 11138.87 11330.02 11469 4.0 4.0 4.0 -0.4 272.8 619.25 1.07 0.95 33.71 10946.4 4.6291 4.7516 122.5 0.0112 113.8
Totals 132355.2 14.13 12.24 432.18 124616.1 61.935 64.167 2231.6 0.2342
Averages 10181.2 4.0 4.0 4.0 7,9 281.1 620 69385 1.09 0.94 33.24 9585.9 4.764 4.936 171.7 0.0180 101.0
Comments:
Insert weelcly flow check values in yellow columns. I
. ~ -.. _,.._ ---.J
~n 'col\Jm!fS :ire cruc:ula~ avera~ from t~~ S\illioa, I ._fiiiir.,.~oea1111«Jlinlm.·· ·· ::J
Blanks Period: September 25, 2017 -
December 26 2017
Week Filter Start Stop Net # Number Date Date
1 9415377 25-Sep-17 02-0ct-17 4.7922
2 9415368 02-0ct-17 09-0ct-17 4.8286
3 9415360 09-0ct-17 16-0ct-17 4.7792
4 9415352 16-0ct-17 23-0ct-17 4.7914
5 9415344 23-0ct-17 30-0ct-17 4.7952
6 9415336 30-0ct-17 06-Nov-17 4.7691
7 9415328 06-Nov-17 13-Nov-17 4.7248
8 9415320 13-Nov-17 20-Nov-17 4.8426
9 9415313 20-Nov-17 27-Nov-17 4.8146
10 9471097 27-Nov-17 04-Dec-17 4.5977
11 9471096 04-Dec-17 11-Dec-17 4.6142
12 9471081 11-Dec-17 18-Dec-17 4.6243
13 9471080 18-Dec-17 25-Dec-17 4.6142
Totals
ATTACHMENT E
ENVIRONMENT AL GAMMA GRAPHS AND SUPPORTING DATA
!White Mesa Mill Ambient Gamma Levels Over Time BHV-1 !
50.00 ..--------------------------------------------------------------------,
45.00 I
40.00 -----------------------------------------------------------------;
35.00 ---------------------------------------------------------------------,
30.00
...
<1) t ca 25.00 ::::,
CF --E <D a: E 20.00
15.00
10.00
5.oo I • 11 • 11 • I a I / :kl: 11 I 11 ,_ ,' I /I I 1 • .,Ill' JI
0.00 1~¥ i.. -1aiin¥ ... -, I 1 ,VP craa, ......... asm r: 416 ' I .• . I l
9/3011981 9/30/1984 9/30/1987 9/3011990 9/3011993 9/3011996 9/3011999 9/30/20o2 9/30/20os 9/3o/2ao8 9/30/2011 9/30/2014 9/30/2017
Background (BHV-3) Subtracted from BHV-1
.........,_Series!
I White Mesa Mill Ambient Gamma Levels Over Time BHV-2 !
50.00 -r----------------------------------------------------------,
45.00 ---------------------------------------------------------1
40.00 ---------------------------------------------------------1
35.00 ---------------------------------------------------------1
30.00 ....
Q)
t::'. a, ::::,
!! 25.00
E Q) a:
E 20.00
15.00 +------------------------------------------------------------1
10.00 +--------------------------------------------------------------1
s.oo I Jl II I IW e • .n. 1f .-• I
0.00
30-seP-81 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 !
60.00 ~---------------------------------------------------------------------,
50.00 -I -----
40.00
...
Q) t:: ro ::,
O" 30.00 --E Q) a: E
20.00
10.00
0.00 ________ ..___ ...... _____ .._ _____ .._ ______________ ...... ___ __. _____ ...... _______ -,-_ _.__ ...... _-+-_ ...... _..._ ___ ..... _____ ...... _____ +"'
30.seP-ei 30..5eP-&, 30.seP-87 30..sep.90 30..Sep.93 30..Sep.96 30..Sep.99 30..seP-02 30.seP-os 30..sep-o8 30..sep.ll 30.5eP-l4 30..5eP-l7
-BHV-3
I White Mesa Mill Ambient Gamma Levels Over Time BHV-4 !
50.00 -r-----------------------------------------------,
45.00 +----------------------------------------------------~
40.00 -------------------------------------------------------~
35.00 ----------------------------------------------------~
30.00
....
(])
t:: ns 25.oo
::::,
C" -E (]) CI: 20.00
E
15.00
10.00 -------------------------------------------------------~
5.oo I 9 I -'illr • II II • I\ I
0.00
30-seP-Bi 30-seP-84 30-se 30-se 30-se 30-se 30-se 30-se P-87 P-9o P-93 P-95 'P-99 'P-02 30-seP-os 30-seP-os 30-seP-22 30-sep_24 3D-seP-l7
Background (BHV-3) Subtracted from BHV-4
~BHV-4
I White Mesa Mill Ambient Gamma Levels Over Time BHV-s !
50.00 ,---------------------------------------
45.00 +-------------------------------------------------------1
40.00 -l------------------------------------------------------1
35.00 -1---------------------------------------------------------l
30.00 ....
Q)
t:::
ctS ::J
C" -25.00
E
Q) a: E 20.00
15.00 +-----------------------------------------------------1
10.00 -1----------------------------__.-----------------------419+----1
5.00 I f I le &. /JIPa nn... l•llal I • ...a I I ±I l:.L: II 'Ill' I II IJ I ..... ,,., I I I
0.0Q •• ~ "119 I •• , • • • -• ,. • •
30-Sep-Bl 30.sep.84
30-5eP-87 30-Sep.90 30-Sep.93 30.Sep.96 30-Sep.99 30.5eP-02 3o.seP-os 30-seP-oe 30-Sep.ll 30-Sep.14 30-Sep.17
Background (BHV-3) Subtracted from BHV-5
-.-BHV-5
! White Mesa Mill Ambient Gamma Levels Over Time BHV-6 j
50.00
45.00
40.00
35.00
30.00 ..
,_
Q) t:: co 25.00 ::I C" --E Q) a: 20.00 E
15.00
10.00
.. 11
J I" ,,
AJ\.. 0 -~~ LA la ----------
5.00
0.00
30-5eP..82 30-seP-&i 30-sep..s7 30-sep..90 30-Sep..93 30-sep..96 30-Sep..99 30-seP--02 30-seP..os 3o-SeP..os 30-seP..22 30-seP-14 30-5eP-l7
Background (BHV-3) Subtracted from BHV-6
-BHV-6
I White Mesa Mill Ambient Gamma Levels Over Time BHV-7 !
50.00
45.00
40.00
35.00
30.00
...
Q)
t:'. ro 25.00 ::::,
!;!
E Q) a: 20.00 E
15.00
10.00
~
--J ~---~--= -----
5.00
0.00
l-seP-14 l-Dec-14 l-Miir-is l-.Jun-15 l-seP-is l-Dec-15 l-Miir-15 l-Jun-15 l-Sep.l6 l-Dec-15 l-11t7ilr-17 l-Ju,,.17 l-Sep.17 l-Dec.17
Background (BHV-3) Subtracted from BHV-7
-BHV-7
I White Mesa Mill Ambient Gamma Levels Over Time BHV-s !
50.00
45.00
40.00
35.00
30.00
....
Q) t:: co 25.00 ::I O" --E
Q) a: 20.00 E
15.00
~
--: --) ~--: : ~ --------_/
10.00
5.00
0.00
l-Sep.l4 l-Dec-14 l-fvtar-15 1·11tn-1s l-seP·ls l-Dec-is l-fvtar-15 l-.11tn-15 l-Sep.l6 l-Dec-15 l-fvtar-17 l-.11tn-11 l-SeP-17 l-Dec-17
Background (BHV-3) Subtracted from BHV-8
-BHV-8
White Mesa Mill Third Quarter 2017 Environmental Spherical Gamma Monitor Results
Mean
Total Days Ambient
Badge Badge at Dose mRem/ mRem/ mRem/
Number Location Date Issued Date Returned WMM Equivalent hour Day Week
Control Administration Vault 7/6/2017 10/3/2017 89 34.1 0.02 0.383 2.68
1 V205 Control Room 7/6/2017 10/3/2017 89 43.8 0.02 0.492 3.44
2 BHV-6 7/6/2017 10/3/2017 89 32.7 0.02 0.367 2.57
3 Ore Stor. -Barrel Area 7/6/2017 10/3/2017 89 458.2 0.21 5.148 36.04
4 Vanadium Precip.Area 7/6/2017 10/3/2017 89 160.8 0.08 1.807 12.65
5 Yellowcake Drying Area 7/6/2017 10/3/2017 89 399.7 0.19 4.491 31.44
6 Leach 7/6/2017 10/3/2017 89 235.3 0.11 2.644 18.51
7 SAG Mill Control Room 7/6/2017 10/3/2017 89 279.9 0.13 3.145 22.01
8 Yellowcake Precip. 7/6/2017 10/3/2017 89 485 0.23 5.449 38.15
9 Central Control Room 7/6/2017 10/3/2017 89 92.1 0.04 l.G35 7.24
10 Ore pad -decontamination pad 7/6/2017 10/3/2017 89 130 0.06 1.461 10.22
11 North East Comer Ore Pad 7/6/2017 10/3/2017 89 281.1 0.13 3.158 22.11
12 Met. Lab 7/6/2017 10/3/2017 89 103.9 0.05 1.167 8.17
13 Filter Press Room 7/6/2017 10/3/2017 89 183 0.09 2.056 14.39
14 BHV-1 7/6/2017 10/3/2017 89 36.8 0.02 0.413 2.89
15 BHV-2 7/6/2017 10/3/2017 89 36.9 0.02 0.415 2.90
16 BHV-3 7/6/2017 10/3/2017 89 35.5 0.02 0.399 2.79
17 BHV-4 7/6/2017 10/3/2017 89 33.4 0.02 0.375 2.63
18 BHV-5 7/6/2017 10/3/2017 89 35.5 0.02 0.399 2.79
19 SAG Mill 7/6/2017 10/3/2017 89 196.5 0.09 2.208 15.46
20 Tails 7/6/2017 10/3/2017 89 44 0.02 0.494 3.46
21 CCD 7/6/2017 10/3/2017 89 85.3 0.04 0.958 6.71
22 North SX 7/6/2017 10/3/2017 89 92.3 0.04 1.037 7.26
23 Administration Building 7/6/2017 10/3/2017 89 36.8 0.02 0.413 2.89
24 Admin Parking Lot 7/6/2017 10/3/2017 89 75.9 0.04 0.853 5.97
25 Yellowcake Packaging 7/6/2017 10/3/2017 89 514.9 0.24 5.785 40.50
26 Yellowcake Storage 7/6/2017 10/3/2017 89 931.1 0.44 10.462 73.23
27 Bucking Room 7/6/2017 10/3/2017 89 216.9 0.10 2.437 17.06
28 Mill Lunch Room 7/6/2017 10/3/2017 89 49.2 0.02 0.553 3.87
29 South SX 7/6/2017 10/3/2017 89 140.1 0.07 1.574 11.02
30 Mtce. Super.'s Office 7/6/2017 10/3/2017 89 48.1 0.02 0.540 3.78
31 Ore Feed Grizzly 7/6/2017 10/3/2017 89 346.4 0.16 3.892 27.24
32 Scalehouse 7/6/2017 10/3/2017 89 203.9 0.10 2.291 16.04
33 Sample Plant (OBS) 7/6/2017 10/3/2017 89 247.3 0.12 2.779 19.45
34 Front Gate 7/6/2017 10/3/2017 89 197.2 0.09 2.216 15.51
45 AF -Barrel Dump Station 7/6/2017 10/3/2017 89 193.4 0.09 2.173 15.21
46 AF Circuit -South 7/6/2017 10/3/2017 89 111.6 0.05 1.254 8.78
47 AF Circuit -North 7/6/2017 10/3/2017 89 171.3 0.08 1.925 13.47
51 North Control# I 7/6/2017 10/3/2017 89 39.6 0.02 0.445 3.11
52 North Control# 2 7/6/2017 10/3/2017 89 38.9 0.02 0.437 3.06
CaF2 Barrel Dump Station -
53 Operator Station 7/6/2017 10/3/2017 89 223.1 0.10 2.507 17.55
64 KF Barrel Dump Station 7/6/2017 10/3/2017 89 233.2 0.11 2.620 18.34
70 BHV-7 7/6/2017 10/3/2017 89 36.2 0.02 0.407 2.85
71 BHV-8 7/6/2017 10/3/2017 89 33.3 0.02 0.374 2.62
White Mesa Mill Fouth Quarter 2017 Environmental Spherical Gamma Monitor Results
Mean
Total Days Ambient
Badge Date Badge at Dose mRem/
Number Location Date Issued Returned WMM Equivalent mRem / hour mRem / Day Week
Control Administration Vault 10/3/2017 1/3/2018 92 33.8 0.02 0.367 2.57
1 V205 Control Room 10/3/2017 1/3/2018 92 45.7 0.02 0.497 3.48
2 BHV-6 10/3/2017 1/3/2018 92 34.2 0.02 0.372 2.60
3 Ore Stor. -Barrel Area 10/3/2017 1/3/2018 92 410.7 0.19 4.464 31.25
4 Vanadium Precip.Area 10/3/2017 1/3/2018 92 180.8 0.08 1.965 13.76
5 Yellowcake Drying Area 10/3/2017 1/3/2018 92 342.7 0.16 3.725 26.08
6 Leach 10/3/2017 1/3/2018 92 138.5 0.06 1.505 10.54
7 SAG Mill Control Room 10/3/2017 1/3/2018 92 241.7 0.11 2.627 18.39
8 Yellowcake Precip. 10/3/2017 1/3/2018 92 309.8 0.14 3.367 23.57
9 Central Control Room 10/3/2017 1/3/2018 92 85.5 0.04 0.929 6.51
10 Ore pad -decontamination pad 10/3/2017 1/3/2018 92 117.1 0.05 1.273 8.91
11 North East Corner Ore Pad 10/3/2017 1/3/2018 92 321.2 0.15 3.491 24.44
12 Met. Lab 10/3/2017 1/3/2018 92 84.7 0.04 0.921 6.44
13 Filter Press Room 10/3/2017 1/3/2018 92 159.5 0.07 1.734 12.14
14 BHV-1 10/3/2017 1/3/2018 92 39.3 0.02 0.427 2.99
15 BHV-2 10/3/2017 1/3/2018 92 34.3 0.02 0.373 2.61
16 BHV-3 10/3/2017 1/3/2018 92 31.4 0.01 0.341 2.39
17 BHV-4 10/3/2017 1/3/2018 92 31.8 0.01 0.346 2.42
18 BHV-5 10/3/2017 1/3/2018 92 35.4 0.02 0.385 2.69
19 SAG Mill 10/3/2017 1/3/2018 92 171.1 0.08 1.860 13.02
20 Tails 10/3/2017 1/3/2018 92 45.5 0.02 0.495 3.46
21 CCD 10/3/2017 1/3/2018 92 91.6 0.04 0.996 6.97
22 North SX 10/3/2017 1/3/2018 92 55.2 0.03 0.600 4.20
23 Administration Building 10/3/2017 1/3/2018 92 37.2 0.02 0.404 2.83
24 Admin Parking Lot 10/3/2017 1/3/2018 92 76.4 0.03 0.830 5.81
25 Yellowcake Packaging 10/3/2017 1/3/2018 92 460.4 0.21 5.004 35.03
26 Yellowcake Storage 10/3/2017 1/3/2018 92 1025.9 0.46 11.151 78.06
27 Bucking Room 10/3/2017 1/3/2018 92 193.8 0.09 2.107 14.75
28 Mill Lunch Room 10/3/2017 1/3/2018 92 54.7 0.02 0.595 4.16
29 South SX 10/3/2017 1/3/2018 92 123.7 0.06 1.345 9.41
30 Mtce. Super.'s Office 10/3/2017 1/3/2018 92 47.3 0.02 0.514 3.60
31 Ore Feed Grizzly 10/3/2017 1/3/2018 92 306.2 0.14 3.328 23.30
32 Scalehouse 10/3/2017 1/3/2018 92 196.4 0.09 2.135 14.94
33 Sample Plant (OBS) 10/3/2017 1/3/2018 92 236.3 0.11 2.568 17.98
34 Front Gate 10/3/2017 1/3/2018 92 184.5 0.08 2.005 14.04
45 AF -Barrel Dump Station 10/3/2017 1/3/2018 92 169.9 0.08 1.847 12.93
46 AF Circuit -South 10/3/2017 1/3/2018 92 94.2 0.04 1.024 7.17
47 AF Circuit -North 10/3/2017 1/3/2018 92 141.6 0.06 1.539 10.77
51 North Control # 1 10/3/2017 1/3/2018 92 38.3 0.02 0.416 2.91
52 North Control # 2 10/3/2017 1/3/2018 92 33 0.01 0.359 2.51
CaF2 Barrel Dump Station -
53 Operator Station 10/3/2017 1/3/2018 92 169.2 0.08 1.839 12.87
64 KF Barrel Dump Station 10/3/2017 1/3/2018 92 197 0.09 2.141 14.99
70 BHV-7 10/3/2017 1/3/2018 92 30.7 0.01 0.334 2.34
71 BHV-8 10/3/2017 1/3/2018 92 33.9 0.02 0.368 2.58
ATTACHMENT F
VEGETATION GRAPHS, DATA TABLE, LABORATORY RESULTS AND QA/QC
(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
O:> ...... O') 0, .j:s. (,J 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 :JJ
8/27/1990 D)
I I\)
8/27/1991 I\)
0)
8/27/1992 0 0
8/27/1993 ::::s n
8/27/1994 (D
::::s -8/27/1995 "'I D) -
t 8/27/1996 s·
::::s
8/27/1997 0
z 8/27/1998 ::::s m <
8/27/1999 (D
(C
T
(D
8/27/2000 -D) -z 8/27/2001 s· ::E ::::s
8/27/2002 -C t 8/27/2003 0 =::.:
(/) 8/27/2004 ;:iii;;
::E (C -8/27/2005
8/27/2006
8/27/2007
8/27/2008
8/27/2009
8/27/2010
8/27/2011
8/27/2012
8/27/2013
8/27/2014
8/27/2015
8/27/2016
8/27/2017
(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 (X) -....I 0) Ol ~ (,J 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
"CJ
8/27/1990 er I I\)
8/27/1991 ....
0
8/27/1992 0 0
8/27/1993 :::s (')
8/27/1994 (I) .
:::s -8/27/1995 "'I D) -
f
8/27/1996 o·
:::s
8/27/1997 0
z :::s m 8/27/1998 <
8/27/1999 (I) cc t (I)
8/27/2000 -D)
z -::: 8/27/2001 o·
:::s
8/27/2002 -
f
C
8/27/2003 0 =:::.:
(I) 8/27/2004 :;:iili; ::: cc -8/27/2005
8/27/2006
8/27/2007
8/27/2008
8/27/2009
8/27/2010
8/27/2011
8/27/2012
8/27/2013
8/27/2014
8/27/2015
8/27/2016
8/27/2017
(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
(X) -...J 0) C.11 .i::,. w I\)
4/1/2015
5/1/2015
6/1/2015
7/1/2015
8/1/2015
9/1/2015
10/1/2015
11/1/2015 I I I I 1111 t t I I C: I
121112015 I I I I / I I I I z ~
11112016 I I I ~ I I I I 0
21112016 I I I /I I I I I 0 :I (')
3/1/2016 I I I / I II I I CD :I -..,
4/1/2016 I I I •I ~ I I D> -
5/1/2016
5·
t :I tn
z 6/1/2016 :I m < 7/1/2016 CD cc
T 8/1/2016 CD -D> -z 9/1/2016 o· :E :I
10/1/2016 -C t 11/1/2016 0 :::::.: ;;,ii; en 12/1/2016 cc :E -1/1/2017
2/1/2017
3/1/2017
4/1/2017
5/1/2017
6/1/2017
7/1/2017
8/1/2017
9/1/2017
10/1/2017
11/1/2017
{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 (X) --J 0) C.T1 .i,... w I\)
4/1/2015
5/1/2015
6/1/2015
7/1/2015
8/1/2015
9/1/2015
10/1/2015
11/1/2015 i I JI • I -I ::::c
121112015 I I \IV I I N w
11112016 I I ~ \ I N
(')
21112016 I I / I\ \ I 0
::::s
C,
3/1/2016 I I / I \ \ I C'D ::::s -4/1/2016 I I If I ;. > I "'I m -5/1/2016 er
t ::::s en
6/1/2016 ::::s z m < 7/1/2016 C'D cc
T 8/1/2016 C'D -m
9/1/2016 -z er :E ::::s 10/1/2016 -C
t 11/1/2016 (')
:::::.:: ~ en 12/1/2016 cc :E -1/1/2017
2/1/2017
3/1/2017
4/1/2017
5/1/2017
6/1/2017
7/1/2017
8/1/2017
9/1/2017
10/1/2017
11/1/2017
WHITE MESA MILL
FORAGE RADIONUCLIDE DA TA
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.3 IE--04
3rd '82 OI-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.05E-03
3rd '85 15-Jul-85 8.20E-05
4th '85 09-0ct-85 1.15E-04
2nd'86 24-Mar-86 5.72E--04
3rd '86 10-Jul-86 5.0JE-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 4.50E-04
3rd '88 28-Jul-88 3.20E-05
2nd '89 07-Apr-89 5.60E-04
3rd '89 06-Jun-89 l.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 JO-Apr-91 l.20E-04
2nd '91 ll-Jun-91 9.IOE-05
3rd '91 20-Nov-91 4.50E-04
!st '92 22-Apr-92 3.60E-05
2nd '92 IO-Jun-92 l.OOE-05
3rd '92 LO-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 I l-May-94 l.80E-04
2nd '94 19-Jul-94 l.71E-05
3rd '94 28-Nov-94 2.40E-04
!st '95 l l-Apr-95 6.70E-05
2nd '95 06-Jul-95 l.50E-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-Sep-97 l.lOE-05
4th '97 20-Nov-97 8.00E-06
1st '98 23-Mar-98 <9.IOE-05
2nd '98 16-Jun-98 l.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 l.SOE-04
2nd '00 22-Jun-OO l.20E-06
4th '00 21-Dec-00 l.60E-06
1st '01 30-Apr-Ol l.OOE-06
2nd '01 14-Jun-01 2.30E-06
4th '01 17-Dec-Ol 9.IOE-06
1st '02 07-May-02 3.30E-05
2nd '02 07-Jul-02 5.55E-05
4th '02 15-Dec-02 7.75E-05
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (S.OE-08)
1.00E-05 5.00E-08
l.OOE-05 5.00E-08
l.30E-05 1.00E-06
1.00E-05 5.00E-08
1.07E-06 l.OOE-06
6.20E-06 8.00E--09
l.20E-05 6.00E-06
8.00E-06 4.00E-06
1.20E-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
l.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
i.60E-05 2.00E-07
4.00E-05 5.00E--08
1.00E-05 2.00E-06
7.00E-06 2.00E-07
3.50E-05 3.00E-06
2.20E-05 3.00E-06
l.50E-05 3.00E-06
2.70E-05 3.00E-06
4.00E-05 3.00E-05
l.20E-06 9.00E-08
1.50E-05 I.70E-07
5.40E-06 l.60E-07
I.50E--06 l.SOE-07
5.00E-06 J.80E-07
2.50E-06 1.SOE-07
2.50E-06 l.80E-07
4.70E-07 l.21E-07
4.30E-07 l.33E-07
l.20E-06 5.60E-07
9.lOE-05 9.!0E-05
1.20E-06 6.30E-08
1.00E-06 8.20E-08
3.00E-06 l.20E-07
l.40E-06 8.30E-08
l.OOE-06 2.30E-07
3.00E-06 l.20E-07
l.OOE-07 2.80E-07
l.lOE-06 3.70E-07
1.00E-07 2.40E-07
2.00E-07 9.90E-08
2.40E-06 l.20E-07
1.80E-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) (1.0E-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
l.lOE-03 1.00E-04 l.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 1.70E-04 l.OOE-07 NS NA NA NS NA NA
l.OSE-04 9.00E-06 J.OOE-05 NS NA NA NS NA NA
4.97E-04 9.30E-05 l.OOE-04 NS NA NA NS NA NA
l.84E-04 1.20E-05 l.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 1.40E-04 2.00E-05 NS NA NA NS NA NA
7.70E-04 1.30E-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 I.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.50E-03 l.OOE--04 I.OOE--06 NS NA NA NS NA NA
9.50E-04 4.00E-05 l.OOE-06 NS NA NA NS NA NA
I.70E-03 l.OOE-04 l.OOE-06 NS NA NA NS NA NA
1.40E-03 l.OOE-04 l.OOE-06 NS NA NA NS NA NA
l.50E-04 4.40E-04 J.OOE-06 NS NA NA NS NA NA
1.IOE-03 l.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 1.40E-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 l.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.50E-04 2.00E-05 I.OOE-05 NS NA NA NS NA NA
7.50E-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 3.50E-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.IOE-06 4.45E-06 NS NA NA NS NA NA
l.70E-04 l.lOE-05 8.30E-07 NS NA NA NS NA NA
l.40E-04 1.30E-05 7.90E-07 NS NA NA NS NA NA
5.IOE-05 4.50E-06 7.60E-07 NS NA NA NS NA NA
6.70E--05 l.OOE-05 8.80E-07 NS NA NA NS NA NA
3.20E-05 4.50E-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.lOE-07 NS NA NA NS NA NA
2.IOE-05 7.30E-07 6.66E-07 NS NA NA NS NA NA
l.40E-04 4.60E-06 l.lOE-07 NS NA NA NS NA NA
<4.50E-04 4.50E-04 4.50E-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.IOE-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.IOE-05 1.00E-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 I .40E-06 NS NA NA NS NA NA
5.IOE-05 5.00E-06 l.90E-06 NS NA NA NS NA NA
<l.2E-06 l.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 1.00E-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 6.15E-06 l.OOE-05 NS NA NA NS NA NA
SAMPLED SAMPLED Ra-226 Ra-226 MDC¥ Pb-210 Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232
QTR. DATE
VALUE ERROR LLDuCi/Kg VALUE ERROR LLDuCi/Kg VALUE ERROR LLD VALUE
(uCi/Kg) (uCi/Kg) (5.0E-08) (uCi/Kg) (uCi/Kg) (1.0E-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg)
(2.0E-07)
1st '03 21-Mar-03 9.IOE-06 l.30E-06 3.60E-07 l.13E-05 l.61E-06 3.36E-06 NS NA NA NS
2nd '03 10-Jun-03 2.50E-05 l.30E-06 3.60E-07 3.26E-06 2.00E-06 7.38E-08 NS NA NA NS
4th '03 20-Nov-03 5.70E-05 3.50E-06 l.50E-07 4.05E-05 5.82E-06 8.30E-07 NS NA NA NS
1st '04 08-Apr-04 9.38E-05 3.70E-06 l.lOE-07 5.88E-05 3.00E-06 5.50E-07 NS NA NA NS
2nd '04 12-Jun-04 5.63E-05 3.40E-06 l.80E-07 6.42E-05 5.90E-06 9.00E-07 NS NA NA NS
4th '04 30-Nov-04 8.41E-05 5.50E-06 2.00E-08 2.48E-04 l .40E-05 3.00E-07 NS NA NA NS
!st '05 21-Apr-05 5.60E-05 3.00E-06 1.40E-07 5.80E-05 4.00E-06 6.90E-07 NS NA NA NS
2nd '05 13-Jun-05 9.IOE-06 l.50E-06 l.80E-07 l .lOE-05 l.20E-05 9.00E-07 NS NA NA NS
4th '05 JO-Nov-05 6.00E-05 3.00E-06 l.lOE-10 l.70E-06 6.40E-07 5.50E-10 NS NA NA NS
Isl '06 03-Apr-06 8.00E-05 5.00E-06 5.00E-08 3.40E--04 l.20E-05 l.OOE-06 NS NA NA NS
2nd '06 16-Jun-06 4.IOE-05 3.lOE-06 5.00E-08 l.16E--04 6.IOE-06 l .OOE-06 NS NA NA NS
4th '06 28-Nov-06 1.17E-04 4.60E-06 1.90E-07 3.28E-04 9.50E-06 9.50E-07 NS NA NA NS
1st '07 30-Mar-07 9.70E-05 4.40E-06 l.90E-07 3.40E-04 8.70E-06 8.4-07 NS NA NA NS
2nd '07 l-Jun-07 l.30E-05 l.60E-06 l.90E-07 1.20E-04 6.60E-06 9.70E-07 NS NA NA NS
4th '07 23-Nov-07 7.00E-05 8.20E-06 2.00E-07 5.00E-04 2.00E-05 l.20E-06 NS NA NA NS
1st '08 22-Apr-08 3.60E-06 3.00E-06 5.20E-07 2.30E-04 l .40E-05 l.OOE--06 NS NA NA NS
2nd '08 18-Jun-08 3.20E-05 3.20E-06 l.80E-06 6.90E-05 3.50E-05 5.50E-05 NS NA NA NS
4th '08 12-Dec-08 l.50E-04 5.20E-06 9.90E-07 3.60E-04 2.90E-05 3.90E-05 NS NA NA NS
!st '09 28-Apr-09 5.90E-04 l.35E-05 l.50E-06 3.40E-04 l.30E-05 l.50E-06 NS NA NA NS
2nd '09 l 7-Jun-09 l.90E-05 l.45E-06 4.90E-07 3.60E-05 l.lOE-05 l.SOE-05 NS NA NA NS
4th '09 18-Dec-09 l.70E-04 5.90E-06 4.80E-04 l.20E-05 NS NA NA NS
Isl '10 13-May-10 2.20E-04 7.20E-06 l.lOE-06 l.90E-04 l.90E-05 2.90E-05 NS NA NA NS
2nd '10 18-Jun-lO 6.50E-05 3.40E-06 7.60E-07 l .40E-04 J.90E-05 2.90E-05 NS NA NA NS
4th 'IO 20-Dec-IO 2.30E-05 l.70E-06 5.20E-07 l.OOE-05 I.50E-06 2.30E-06 NS NA NA NS
2nd'!! 23-Jun-l l 2.40E-07 l.40E-07 l.80E-07 <2.9E-06 1.70E-06 2.90E-06 NS NA NA NS
3rd '11 27-Jul-11 4.90E-06 6.30E-07 3.20E-07 9.50E-05 2.IOE-06 2.50E-06 NS NA NA NS
4th '11 23-Nov-l l 7.20E-06 7.50E-07 2.90E-07 8.80E-08 4.30E-07 7.20E-07 NS NA NA NS
2nd '12 ll-Apr-12 4.40E-05 l.90E-06 3.60E-07 2.IOE-04 2.00E-06 l.OOE-06 NS NA NA NS
3rd '12 l l-Jun-12 2.20E-05 8.40E-07 l.lOE-07 l.30E-04 7.60E-06 5.90E-06 NS NA NA NS
4th '12 06-Nov-12 3.JOE-05 4.82E-07 4.63E-08 4.26E-04 3.72E--06 6.52E-07 NS NA NA NS
2nd '13 30-Apr-13 l.14E-04 l.74E-06 5.34E-07 2.65E-04 4.41E--06 5.37E-06 NS NA NA NS
3rd '13 20-Jun-13 8.91E-05 2.16E-06 1.42E-06 J.42E-04 3.68E-06 6.17E-06 NS NA NA NS
4th '13 14-Nov-13 l.37E-04 3.87E-06 4.71E-06 5.33E-04 l.45E-05 2.27E-05 NS NA NA NS
2nd '14 16-Aor-14 9.90E-05 1.0lE-06 3.9JE-07 l.99E-04 3.14E-06 3.38E-06 NS NA NA NS
3rd '14 10-Jun-14 2.60E-05 8.46E-07 9.19E--07 5.60E-05 3.08E-06 7.12E-06 NS NA NA NS
4th '14 25-Nov-14 2.98E-05 l.23E-06 l.30E-06 2.46E-04 5.38E-06 7.4JE-06 NS NA NA NS
1st '15 21-Apr-15 7.15E-04 8.0JE-06 3.50E-06 5.85E-04 l.27E-05 2.51E-05 6.36E-04 2.70E-05 8.62E-06 l.OIE-04
2nd '15 15-Jun-15 J.52E-04 3.48E-06 2.60E-06 4.49E-04 l.50E-05 3.33E-05 3.llE-04 I .58E-05 6.45E-06 4.19E-05
4th '15 23-Nov-15 2.34E-04 5.79E-06 3.89E-06 9.34E-04 1.36E-05 l.37E-05 2.73E-04 l.91E-05 6.31E-06 6.67E-06
2nd '16 14-Apr-16 4.0SE-04 7.26E-06 5.42E-06 l.34E-03 2.16E-05 2.93E-05 l.69E-04 l.29E-05 5.76E-06 l.66E-05
2nd '16 14-Jun-16 5.92E-05 2.70E-06 4.00E-06 2.61E-04 2.09E-05 4.92E-05 2.IOE-04 5.52E-06 J.70E-06 4.27E-06
4th '16 11-Nov-16 4.56E-05 2.lOE-06 3.47E-06 2.70E-04 l .43E-05 3.81E-05 3.94E-05 5.94E-06 5.02E-06 2.IOE-06
(5.00E-08) (l.OOE-06) (2.00E-07)
2nd '17 13-Apr-17 l.71E-04 4.59E-06 4.06E-06 6.l!E--04 l.34E-05 2.17E-05 2.38E-04 5.71E-06 2.3JE-06 l.54E-05
(5.00E-08) (l.OOE-06) (2.00E-07)
2nd '17 19-Jun-17 2.40E-05 9.69E-07 l.15E-06 7.52E-06 l.72E-06 5.42E-06 l.31E-04 4.21E-06 l.15E-06 7.ISE-06
(5.00E-08) (l.OOE-06) (2.00E-07)
4th '17 02-Nov-17 8.03E-05 2.l SE-06 2.31E-06 6.13E-04 1.IOE-05 l.58E-05 l.15E-04 3.99E-06 J.74E--06 l.04E-05
(5.00E-08) (l.OOE-06) (2.00E--07)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected during this period
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
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
3.06E-06 4.04E-07
2.67E-06 6.78E-07
7.98E-07 7.06E-07
l.28E-06 7.67E-07
8.JOE-07 9.31E-07
5.45E--07 5.66E-07
(2.00E-07)
l.59E-06 2.09E-06
(2.00E-07)
l.09E-06 6.48E-07
(2.00E-07)
l.02E-06 1.05E-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
parantbeses 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 lo 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 CX> ....... 0) 01 .,:,.. c., I\)
01-Aug-81 :e 01-Jun-82 :::c 01-Apr-83 :::j
01-Feb-84 m
01-Dec-84 s: m 01-0ct-85 en
01-Aug-86 )>
s: 01-Jun-87 F 01-Apr-88 ~ r-
01-Feb-89 z
01-Dec-89 0
01-0ct-90 :::0 -t
t 01-Aug-91 :::c m
01-Jun-92 )>
JJ en Q) 01-Apr-93 -t I\)
I\) 01-Feb-94 0 O>
01-Dec-94
.,,
' 01-0ct-95 s: -r-"O 01 -Aug-96 r O' I\) 01-Jun-97 :::0 -m 0 a. 01-Apr-98 o· t 01-Feb-99 ::,
01-Dec-99 · C
C 2. z 01-0ct-OO a: )> -I 01-Aug-01 (I)
0 f 01-Jun-02 0 ::, 01-Apr-03 0 -I (I) I 01 -Feb-04 ::, I\) -(,J 01-Dec-04 .,
I\) m -01-0ct-05 o·
01-Aug-06 ::,
tn
01-Jun-07 s·
01-Apr-08 ~ 01-Feb-09 cc
01-Dec-09 (I) -m
01-0ct-10 -o·
01-Aug-11 :::, -01-Jun-12 C
01-Apr-13 0 i:::::
01-Feb-14 • " cc
01-Dec-14 -
01-0ct-15
01-Aug-16
01-Jun-17
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 OI-Jul-82 2.00E-05
4th '82 30-Nov-82 2.36E-06
2nd '83 13-Apr-83 8.58E-05
3rd '83 OI-Jul-83 l.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 J.IOE-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 I O-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
1st '90 17-Apr-90 3.60E-04
2nd '90 20-Jun-90 1.70E-04
3rd '90 17-0ct-90 8.80E-05
!st '91 10-Apr-91 3.00E-04
2nd '91 1 l-Jun-91 3.IOE-04
3rd '91 20-Nov-91 5.00E-04
1st '92 22-Aor-92 2.00E-05
2nd'92 10-Jun-92 6.50E-06
3rd '92 JO-Jun-92 1.20E-04
!st '93 13-Apr-93 1.80E-05
2nd '93 26-Jun-93 5.20E-05
3rd '93 12-0ct-93 5.10E-05
1st '94 l l-May-94 1.ZOE-04
2nd '94 19-Jul-94 3.73E-05
3rd '94 28-Nov-94 2.40E-04
!st '95 l l-Apr-95 8.40E-05
2nd '95 06-Jul-95 1.90E-05
3rd '95 15-Nov-95 l.20E-04
1st '96 23-Apr-96 8.30E-05
2nd '96 • 3 I-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.ZOE-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 l.lOE-04
2nd'OO 21-Apr-OO 3.70E-05
2nd ·oo 22-Jun-OO 2.90E-05
4th'(){) 21-Dec-OO 2.30E-06
1st '01 30-Apr-01 2.10E-05
2nd 'Ol 14-Jun-01 l.30E-06
4th 'OJ 17-Dec-01 3.70E-05
1st '02 07-May-02 4.90E-05
2nd '02 07-Jul-02 8.88E-05
Ra-226 MDC¥ Pb-210
ERROR LLDuCi/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
I.OOE-05 5.00E-08 2.20E-04
9.50E-07 1.00E-06 8.00E-05
I.36E-05 2.00E-08 3.53E-04
l.LOE-05 5.00E-06 l.58E-04
7.00E-06 2.00E-06 2.16E-03
1.00E-05 3.00E-09 J.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.SOE-04
l.80E-05 2.00E-06 4.40E-03
l.80E-05 3.00E-06 4.78E-03
1.00E-04 3.00E-06 l.70E-03
l.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
1.90E-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
1.60E-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 l.SOE-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
1.90E-05 3.00E-06 l.70E-05
2.30E-05 3.00E-06 7.IOE-04
1.00E-05 3.00E-05 9.80E-04
1.60E-06 8.40E-08 7.80E-05
l.50E-05 l.70E-07 2.60E-04
6.10E-06 l.50E-07 l.ZOE-04
1.SOE-06 l .40E-07 4.SOE-05
6.80E-06 l .40E-07 l.OOE-05
3.30E-06 1.90E-07 6.80E-05
2.50E-06 1.60E-07 8.SOE-05
2.30E-06 L.70E-07 4.40E-05
3.50E-07 l.56E-07 3.ZOE-05
7.20E-07 5.40E-07 3.40E-04
9.20E-05 9.ZOE-05 <4.60E-04
6.50E-08 6.50E-08 <3.20E-07
1.00E-06 l.lOE-07 1.70E-04
1.00E-06 l.OOE-07 1.40E-04
1.40E-06 8.30E-08 9.20E-05
3.00E-06 2.20E-07 2.80E-05
1.00E-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 1.28E-04
4.32E-06 7.60E-07 8.33E-05
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR 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
3.00E-04 l.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 I.OOE-07 NS NA NA NS NA NA
J.OOE-05 1.00E-05 NS NA NA NS NA NA
1.90E-05 I.OOE-05 NS NA NA NS NA NA
l.30E-05 I.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
J.IOE-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
l.OOE-04 6.00E-05 NS NA NA NS NA NA
l.OOE-04 I.OOE-06 NS NA NA NS NA NA
4.00E-05 1.00E-06 NS NA NA NS NA NA
l.OOE-04 1.00E-06 NS NA NA NS NA NA
l.OOE-04 1.00E-06 NS NA NA NS NA NA
4.00E-05 l.OOE-06 NS NA NA NS NA NA
l.OOE-04 *** NS NA NA NS NA NA
3.00E-05 *** NS NA NA NS NA NA
7.00E-05 l.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 l.OOE-06 NS NA NA NS NA NA
2.00E-05 l.OOE-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 l.OOE-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.JOE-05 8.30E-07 NS NA NA NS NA NA
J.IOE-05 7.SOE-05 NS NA NA NS NA NA
4.30E-06 7.ZOE-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 J.IOE-07 NS NA NA NS NA NA
4.60E-04 4.60E-04 NS NA NA NS NA NA
3.20E-07 3.ZOE-07 NS NA NA NS NA NA
l.OOE-05 5.50E-07 NS NA NA NS NA NA
7.00E-06 1.00E-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 l.20E-06 NS NA NA NS NA NA
2.00E-05 l.70E-06 NS NA NA NS NA NA
5.00E-05 1.90E-06 NS NA NA NS NA NA
NIA 7.60E-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 1.00E-05 NS NA NA NS NA NA
4.32E-06 1.00E-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.SOE-04
1st '03 21-Mar-03 5.00E-05
2nd '03 JO-Jun-03 5.60E-05
4th '03 20-Nov-03 3.20E-04
1st '04 08-Apr-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 IO-Nov-05 7.40E-05
!st '06 03-Apr-06 l.OOE-04
2nd '06 16-Jun-06 9.50E-05
4th '06 28-Nov-06 8.13E-05
!st '07 30-Mar-07 4.30E-05
2nd '07 J-Jun-07 5.IOE-05
4th '07 23-Nov-07 7.30E-05
1st '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 'IO 13-May-10 l.90E-04
2nd '10 18-Jun-10 2.30E-05
4th '10 20-Dec-10 8.60E-06
2nd']! 23-Jun-ll 2.IOE-07
3rd '11 28-Jul-l l 4.20E-06
4th 'I I 23-Nov-l I 7.70E-06
2nd '12 I l-Apr-12 l.50E-05
3rd '12 l l-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 10-Jun-14 2.53E-05
4th '14 25-Nov-14 7.41E-05
1st '15 21-Apr-15 J.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 JJ-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
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
6.20E-06 7.60E-07
3.40E-06 2.71E-06
2.00E-06 4.IOE-07
8.20E-06 J.70E-07
4.IOE-06 2.00E-07
3.40E-06 l.30E-07
4.60E-06 2.00E-08
2.70E-06 J.30E-07
2.IOE-06 J.SOE-07
3.50E-06 1.20E-IO
6.00E-06 5.00E-08
5.90E-06 5.00E-08
4.IOE-06 2.20E-07
2.60E-06 J.70E-07
3.20E-06 2.30E-07
6.60E-06 5.00E-08
2.80E-06 7.20E-07
3.30E-06 l.80E-06
3.20E-06 7.40E-07
3.60E-06 l.lOE-06
l.60E-05 5.20E-07
3.50E-06
6.IOE-06 9.40E-07
2.00E-06 7.?0E-07
9.lOE-07 3.90E-07
l.20E-07 J.40E-07
5.40E-07 2.70E-07
6.80E-07 2.30E-07
9.50E-07 2.60E-07
5.40E-07 l.20E-07
4.IOE-07 7.71E-08
I.68E-06 8.58E-07
9.59E-07 8.06E-07
3.70E-06 2.17E-06
6.29E-07 5.51E-07
5.55E-07 5.77E-07
!.90E-06 l.53E-06
4.21E-06 5.92E-06
4.43E-06 3.45E-06
3.95E-06 4.25E-06
4.20E-06 5.79E-06
3.97E-06 6.94E-06
4.22E-06 2.03E-06
(5.00E-08)
2.55E-06 4.35E-06
(5.00E-08)
1.77E-06 8.68E-07
(5.00E-08)
4.17E-06 2.0IE-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)
3.16E-04 1.07E-05 l.OOE-05 NS NA
<4.2e-6 4.20E-06 NS NA
l.88E-04 5.14E-06 8.20E-08 NS NA
4.89E-04 J.25E-05 8.30E-07 NS NA
J.94E-05 4.00E-06 l.OOE-06 NS NA
J.87E-05 3.90E-06 6.50E-07 NS NA
4.45E-04 l.40E-05 3.00E-07 NS NA
l.27E-04 4.SOE-06 6.50E-07 NS NA
4.70E-05 5.lOE-06 7.60E-07 NS NA
2.40E-06 8.IOE-08 5.80E-10 NS NA
6.54E-04 1.50E-05 l.OOE-06 NS NA
4.48E-04 1.40E-05 !.OOE-06 NS NA
3.25E-04 l.l2E-06 l.OOE-05 NS NA
2.64E-04 7.20E-06 8.60E-07 NS NA
5.30E-04 I.40E-06 l.20E-06 NS NA
7.00E-04 2.20E-05 l.lOE-06 NS NA
4.40E-04 2.00E-05 J.OOE-06 NS NA
l.40E-04 3.30E-05 5.50E-05 NS NA
4.40E-04 2.SOE-05 3.20E-05 NS NA
l.90E-04 l.SOE-05 2.20E-05 NS NA
4.30E-05 l.OOE-05 l.70E-05 NS NA
3.00E-04 l.lOE-05 NS NA
5.IOE-04 2.40E-05 3.IOE-05 NS NA
8.30E-05 1.80E-05 2.90E-05 NS NA
l.lOE-07 6.80E-07 l.lOE-06 NS NA
<2.2E-06 !.30E-06 2.20E-06 NS NA
2.30E-04 2.50E-06 2.30E-06 NS NA
<5.SE-08 3.40E-07 5.80E-07 NS NA
<7.0E-07 6.00E-07 l.OOE-06 NS NA
l.40E-04 8.30E-06 6.50E-06 NS NA
4.59E-04 3.83E-06 6.18E-07 NS NA
2.24E-04 4.46E-06 4.68E-06 NS NA
!.06E-04 2.30E-06 3.28E-06 NS NA
4.65E-04 l.l?E-05 l.80E-05 NS NA
5.70E-05 2.21E-06 4.52E-06 NS NA
7.68E-05 2.08E-06 3.66E-06 NS NA
2.98E-04 6.48E-06 J.06E-05 NS NA
6.33E-04 1.17E-05 l.45E-05 3.35E-04 2.41E-05
l.08E-03 2.02E-05 3.25E-05 5.24E-04 2.4IE-05
4.78E-04 l.06E-05 l.75E-05 l.51E-04 l.53E-05
3.56E-04 l.14E-05 l.86E-05 6.33E-05 8.20E-06
J.73E-04 2.02E-05 5.42E-05 3.ISE-05 l.90E-06
J.28E-03 2.57E-05 4.95E-05 4.33E-04 2.58E-05
(1.00E-06)
8.85E-04 l.SIE-05 2.23E-05 6.97E-04 l.21E-05
(l.OOE-06)
1.15E-04 3.18E-06 6.07E-06 3.29E-04 6.61E-06
(l.OOE-06)
9.23E-04 !.34E-05 1.94E-05 3.34E-04 9.09E-06
(l.OOE-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected dunng this penod
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
l.17E-05 7.35E-06
9.70E-06 2.38E-05
7.71E-06 2.30E-05
5.95E-06 l.66E-06
l.54E-06 2.95E-06
8.24E-06 3.87E-06
(2.00E-07)
3.52E-06 6.l!E-06
(2.00E-07)
l.44E-06 l.58E-05
(2.00E-07)
3.50E-06 l.52E-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
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
8.57E-07 7.82E-07
2.12E-06 7.36E-07
l.53E-06 4.23E-07
4.SIE-07 5.40E-07
8.26E-07 I .47E-06
7.58E-07 l.03E-06
(2.00E-07)
9.91E-07 l.lSE-06
(2.00E-07)
l.37E-06 5.35E-07
(2.00E-07)
l.35E-06 J.SOE-0-67
(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 CX) ...... O') c.n .j:>,. c.:, I\)
01-Aug-81 :e ::c
01 -Jul-82 =i
01-Jun-83 m s:: 01-May-84 m
01-Apr-85 CJ)
l>
01-Mar-86 s:: -01-Feb-87 r-r-
01-Jan-88 I
01-Dec-88 z
0
01-Nov-89 :r, -t
t 01-0ct-90 ::c
01-Sep-91 :e m JJ CJ) 1l' 01-Aug-92 I\) -t I\) 01-Jul-93 0 0)
01-Jun-94 "T1
T s:: 01-May-95 -r-lJ 01-Apr-96 r-C" r{, :r, ~ 01-Mar-97 0 D)
C.
t 01-Feb-98 o·
01-Jan-99 ::::,
C C 01-Dec-99 n z :t> 01-Nov-OO a: -I CD
t 01-0ct-01 0 0 01-Sep-02 ::::,
-I n
I 01-Aug-03 CD
r{, ::::,
"' 01-Jul-04 -I\)
..,
D)
01-Jun-05 -o·
01-May-06 ::::,
0
01-Apr-07 ::::,
01-Mar-08 < CD 01-Feb-09 cc CD
01-Jan-10 -D) -01-Dec-1 O o·
01-Nov-11 ::::, -01-0ct-12 C
0
01-Sep-13 =::: " 01-Aug-14 cc -01-Jul-15
01-Jun-16
01-May-17
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 9.50E-04
4th '81 20-0ct-81 3.00E-05
2nd '82 15-Apr-82 l.37E-05
3rd '82 Ol-Jul-82 3.40E-04
4th '82 30-Nov-82 1.75E-05
2nd '83 13-Apr-83 7.13E-04
3rd '83 Ol-Jul-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-Jul-85 6.60E-05
4th '85 09-0ct-85 2.83E-04
2nd '86 24-Mar-86 l.57E-04
3rd '86 10-Jul-86 3.78E-04
4th '86 18-Dec-86 2.60E-04
2nd '87 20-Apr-87 4.!0E-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 l.50E-04
2nd '89 07-Apr-89 3.lOE-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 1.lOE-04
3rd '90 17-0ct-90 6.!0E-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.lOE-05
1st '94 ll-May-94 2.00E-05
2nd '94 19-Jul-94 1.75E-05
3rd '94 28-Nov-94 l.OOE-04
1st '95 11-Apr-95 l.70E-05
2nd '95 06-Jul-95 6.40E-06
3rd '95 15-Nov-95 2.30E-05
1st '96 23-Apr-96 4.20E-05
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96 2.!0E-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.50E-04
2nd '00 21-Apr-00 1.00E-04
2nd '00 22-Jun-OO 1.30E-06
4th '00 21-Dec-OO l.20E-06
1st '01 30-Apr-01 1.80E-06
2nd '01 14-Jun-01 2.60E-06
4th '01 17-Dec-01 2.63E-06
!st '02 07-May-02 3.50E-05
2nd '02 07-Jul-02 4.02E-05
4th '02 15-Dec-02 8.lOE-05
Ra-226 MDC¥ Pb-210
ERROR LLDuCi/Kg VALUE
(uCi/Kg) (5.0E-08) (uCi/Kg)
2.00E-05 5.00E-08 l.50E-04
3.00E-06 5.00E-08 l.50E-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
4.50E-06 2.00E-06 6.88E-04
7.00E-06 4.00E-06 l.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.50E-03
l.OOE-05 4.00E-06 4.14E-03
1.00E-05 2.00E-06 l.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 7.50E-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 *** 1.50E-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.!0E-04
l.lOE-05 5.00E-06 2.20E-04
6.00E-06 2.00E-07 l.20E-04
l.40E-05 5.00E-08 9.IOE-04
7.00E-06 2.00E-06 3.20E-04
l.OOE-05 2.00E-07 2.20E-04
l.80E-05 3.00E-06 7.60E-04
2.00E-05 3.00E-06 3.40E-04
l.40E-05 3.00E-06 O.OOE+OO
l.60E-05 3.00E-06 4.20E-04
5.00E-06 3.00E-05 3.90E-04
1.70E-06 7.60E-08 l.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 l.OOE-04
2.00E-06 l.60E-07 l.90E-04
4.20E-07 l.40E-07 3.30E-05
3.20E-07 l.26E-07 l.90E-05
9.50E-07 5.90E-07 l.30E-04
7.90E-05 7.90E-05 <3.90E-04
l.40E-07 3.30E-08 <1.7E-07
l.OOE-06 7.60E-08 2.50E-04
1.00E-06 l.20E-07 1.70E-04
8.60E-07 l.20E-07 2.30E-04
3.00E-06 2.00E-07 l.70E-05
2.00E-06 l.20E-07 l.lOE-04
1.00E-07 2.40E-07 2.00E-04
9.00E-07 2.40E-07 1.20E-04
1.00E-07 1.70E-07 <8.3E-07
2.00E-07 9.90E-08 l.lOE-06
4.60E-05 l.20E-07 9.40E-05
2.20E-06 7.60E-07 1.36E-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 LLDuCi/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
1.00E-05 1.00E-06 NS NA NA NS NA NA
2.00E-05 1.00E-06 NS NA NA NS NA NA
4.00E-05 4.00E-05 NS NA NA NS NA NA
2.70E-04 1.00E-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
l.OOE-04 4.00E-05 NS NA NA NS NA NA
l.OOE-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
1.00E-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 1.00E-04 NS NA NA NS NA NA
l.OOE-04 l.OOE-04 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
5.00E-05 l.OOE-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
2.00E-04 l.OOE-06 NS NA NA NS NA NA
l.OOE-04 *** NS NA NA NS NA NA
1.00E-04 *** NS NA NA NS NA NA
l.40E-04 2.70E-05 NS NA NA NS NA NA
5.00E-05 2.50E-05 NS NA NA NS NA NA
3.00E-05 1.00E-06 NS NA NA NS NA NA
3.00E-05 1.00E-06 NS NA NA NS NA NA
l.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 l.OOE-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
l.20E-05 7.40E-07 NS NA NA NS NA NA
l.50E-05 8.!0E-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
4.70E-06 l.20E-07 NS NA NA NS NA NA
3.90E-04 3.90E-04 NS NA NA NS NA NA
1.70E-07 l.70E-07 NS NA NA NS NA NA
1.00E-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.!0E-07 NS NA NA NS NA NA
1.00E-05 1.20E-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.IIE-06 1.00E-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)
Isl '03 21-Mar-03 3.70E-05
2nd '03 JO-Jun-03 l.30E-05
4th '03 20-Nov-03 l.60E-04
!st '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 l.70E-05
2nd '05 13-Jun-05 l.50E-05
4th '05 JO-Nov-05 3.80E-05
!st '06 03-Apr-06 l.OOE-04
2nd '06 16-Jun-06 3.40E-05
4th '06 28-Nov-06 7.31E-05
Isl '07 30-Mar-07 3.00E-05
2nd '07 l-Jun-07 l.lOE-04
4th '07 23-Nov-07 5.60E-05
1st '08 22-Apr-08 3.20E-05
2nd '08 18-Jun-08 l.25E-05
4th '08 12-Dec-08 9.20E-05
!st '09 28-Apr-09 2.60E-05
2nd '09 l 7-Jun-09 2.40E-05
4th '09 18-Dec-09 3.!0E-05
!st 'JO 13-May-JO 2.00E-05
2nd '10 18-Jun-10 I.IOE-05
4th '10 20-Dec-!O 6.70E-06
2nd '11 23-Jun-l l <l.7E-07
3rd 'J l 27-Jul-l 1 l.60E-05
4th 'J l 23-Nov-l 1 7.80E-07
2nd '12 l l-Apr-12 5.00E-06
3rd '12 1 I-Jun-12 l.90E-08
4th '12 06-Nov-12 l.49E-05
2nd '13 30-Apr-13 4.50E-05
3rd '13 20-Jun-13 l.51E-05
4th '13 14-Nov-13 l.18E-04
2nd '14 16-Apr-14 4.65E-05
3rd '14 10-Jun-14 l.23E-05
4th '14 25-Nov-14 l.16E-04
!st '15 21-Apr-15 2.27E-04
2nd '15 15-Jun-15 3.90E-05
4th '15 23-Nov-15 l.83E-04
2nd '16 14-Apr-16 l.67E-04
2nd '16 14-Jun-16 2.90E-05
4th '16 11-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
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
2.60E-06 2.41E-06
1.00E-06 5.20E-07
l.30E-05 l.20E-07
7.70E-06 l.LOE-07
3.20E-06 l.50E-07
5.70E-06 3.00E-08
l.60E-06 l.30E-07
l.60E-06 l.40E-07
2.IOE-06 8.60E-JO
6.00E-06 5.00E-08
2.50E-06 5.00E-08
3.20E-06 l.60E-07
2.20E-06 l.70E-07
4.60E-06 2.3-07
5.20E-06 5.00E-08
2.30E-06 7.20E-07
2.20E-06 l.80E-06
4.!0E-06 9.60E-07
2.90E-06 l.40E-06
l.40E-06 3.90E-07
2.30E-06
2.JOE-06 9.40E-07
l.30E-06 6.60E-07
9.lOE-07 4.80E-07
6.90E-08 1.70E-07
l.OOE-06 2.60E-07
2.50E-07 2.30E-07
6.00E-07 3.00E-07
6.20E-08 l.lOE-07
3.41E-07 4.25E-08
l.19E-06 5.39E-07
l.06E-06 l.96E-06
3.39E-06 2.97E-06
l.08E-06 7.35E-07
4.97E-07 6.97E-07
2.25E-06 l.53E-06
5.0lE-06 4.08E-06
l.88E-06 2.7 LE-06
6.96E-06 9.64E-06
4.IOE-06 3.65E-06
l .88E-06 3.85E-06
2.71E-06 3.21E-06
(5.00E-08)
2.30E-06 4.61E-06
(5.00E-08)
l.l7E-06 1.04E-06
(5.00E-08)
3.12E-06 3.05E-06
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLDuCi/Kg VALUE ERROR
(uCi/Kg) (uCi/Kg) (1.0E-06) (uCi/Kg) (uCi/Kg)
2.69E-05 2.0JE-06 3.73E-06 NS NA
<1.00E-07 I.OOE-07 NS NA
l.42E-04 6.42E-06 5.90E-07 NS NA
6.!0E-06 2.70E-06 5.50E-07 NS NA
5.27E-05 4.90E-06 7.60E-07 NS NA
3.39E-04 l .60E-05 3.00E-07 NS NA
4.50E-05 3.50E-06 6.50E-07 NS NA
7.00E-05 5.IOE-06 6.90E-07 NS NA
l.20E-06 4.80E-08 4.30E-10 NS NA
3.30E-04 1.lOE-05 l.OOE-06 NS NA
l.37E-04 6.00E-06 l.OOE-06 NS NA
2.98E-04 8.50E-06 8.20E-07 NS NA
3.20E-04 7.90E-06 8.40E-07 NS NA
3.20E-04 l.!OE-05 1.lOE-06 NS NA
6.40E-04 l.90E-05 l.OOE-06 NS NA
2.30E-04 l.50E-05 l.OOE-06 NS NA
5.00E-05 3.00E-05 4.80E-03 NS NA
4.!0E-04 3.00E-05 4.00E-05 NS NA
3.70E-05 l.50E-06 2.50E-05 NS NA
3.50E-05 7.90E-06 l.30E-05 NS NA
2.IOE-04 8.40E-06 NS NA
5.60E-05 1.50E-05 2.40E-05 NS NA
7.80E-05 l.60E-05 2.50E-05 NS NA
8.00E-07 7.90E-07 l.30E-06 NS NA
<2.5E-06 l.50E-06 2.50E-06 NS NA
9.50E-05 l.60E-06 l.70E-06 NS NA
<5.9E-07 3.50E-07 5.90E-07 NS NA
<7.0E-07 7.00E-07 I.OOE-06 NS NA
<2.5E-07 l.30E-06 2.20E-06 NS NA
4.45E-04 4.0IE-06 8.57E-07 NS NA
3.62E-04 6.30E-06 9.90E-06 NS NA
6.71E-05 2.93E-06 6.24E-06 NS NA
5.92E-04 1.27E-05 l.62E-05 NS NA
2.13E-04 5.93E-06 l.31E-05 NS NA
2.46E-05 l.84E-06 4.63E-06 NS NA
4.43E-04 l.04E-05 l.94E-05 NS NA
5.90E-04 l.16E-05 l.67E-05 4.33E-04 l.86E-05
5.29E-04 l.61E-05 3.36E-05 7.78E-05 8.47E-06
8.94E-04 l.43E-05 2.03E-05 4.88E-04 2.91E-05
7.99E-04 2.08E-05 4.12E-05 2.lOE-04 2.24E-05
l.95E-04 2.18E-05 5.93E-05 7.04E-05 3.17E-06
1.21E-03 2.15E-05 3.78E-05 l.27E-03 4.84E-05
(l.OOE-06)
6.14E-04 l.26E-05 l.71E-05 8.20E-04 l.28E-05
(l.OOE-06)
5.25E-05 2.68E-06 5.93E-06 l.77E-04 4.52E-06
(l.OOE-06)
6.36E-04 1.14E-05 1.72E-05 2.52E-04 7.28E-06
(1.00E-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected dunng this penod
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
NA NS
5.14E-06 3.31E-05
6.43E-06 l.08E-05
9.00E-06 7.92E-06
1.39E-05 5.58E-05
l.92E-06 3.70E-06
I.IOE-05 7.71E-06
(2.00E-07)
2.31E-06 2.91E-06
(2.00E-07)
l.32E-06 1.08E-05
(2.00E-07)
3.25E-06 6.82E-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
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
NA NA
2.15E-06 1.14E-06
l.28E-06 1.21E-06
7.67E-07 3.20E-07
5.42E-06 2.!0E-06
8.08E-07 1.04E-06
l.08E-06 1.32E-06
(2.00E-07)
7.40E-07 l.21E-06
(2.00E-07)
l.12E-06 1.07E-06
(2.00E-07)
l.05E-06 2.IIE-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 0 0 0 0 m m m m m m m m m
I I 6 I I I I I + 0 0 0 0 0 0 0 0 (X) -...J 0) 01 .i:,. (,.) I\) ...... 0
01-Aug-81 =e :::c
01-Jul-82 =i
01-Jun-83 m
s::: 01-May-84 m
01-Apr-85 en ~
01-Mar-86 s:::
01-Feb-87 r-r-
01-Jan-88 I
01-Dec-88 en 0
01-Nov-89 C -I
t 01-0ct-90 :::c =e 01-Sep-91 m :IJ 01-Aug-92 en 'l' -I I\)
I\) 01-Jul-93 0 0)
01-Jun-94
.,,
' s:::
01-May-95 r-lJ 01-Apr-96 r-CT rl:> JJ ~ 01-Mar-97 D) 0 C.
f 01-Feb-98 o·
01-Jan-99 :::J C:
C (") z 01-Dec-99 a: )> 01-Nov-OO -I (I)
t 01-0ct-01 0 0
01-Sep-02 :::J (") -I (I) I 01-Aug-03 rl:> :::J -(,J 01-Jul-04 ... I\) D)
01-Jun-05 -o·
01-May-06 :::J en
01-Apr-07 :::J
01-Mar-08 < (I)
01-Feb-09 cc (I)
01-Jan-10 -D) -01-Dec-10 o·
:::J 01-Nov-11 -C: 01-0ct-12 0
01-Sep-13 ::::::.: " 01-Aug-14 cc -01-Jul-15
01-Jun-16
01-May-17
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: January 8, 2018
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
North East
437346001
Vegetation
02-NOV-17 09:15
08-NOV-17
Client
MDC
Project:
Client ID:
RL Units PF
DNMI00101
DNMI001
Time Batch Method Parameter Qualifier Result Uncertainty ---------'----------------------'------DF Analyst Date
lad Alpha Spec Analysis
\lphaspec Th-232, Solid "Dry Weight Corrected"
~horium-232 l.04E-05 +/-1.02E-06 l.05E-06
\lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 5.48E-05 +/-1.73E-06 8.21E-07
Jranium-235/236 3.78E-06 +/-5.18E-07 5.07E-07
Jranium-238 5.60E-05 +/-1.74E-06 4. llE-07
lad Gas Flow Proportional Counting
3FPC, Pb210, Solid "Dry Weight Corrected"
,ead-210 0.000613 +/-l.lOE-05 1.58E-05
3FPC, Total Alpha Radium, solid "Dry Weight Corrected"
~otal Radium 8.03E-05 +/-2.18E-06 2.31E-06
[he following Prep Methods were performed:
\1:ethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Description
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Modified
;urrogate/Tracer Recovery Test
rhorium-229 Tracer
Jranium-232 Tracer
,ead Carrier
3arium Carrier
~otes:
Alphaspec Th-232, Solid "Dry Weight Corrected"
Alphaspec U, Solid "Dry Weight Corrected"
GFPC, Pb210, Solid "Dry Weight Corrected"
GFPC, Total Alpha Radium, solid "Dry Weight
Corrected"
2.00E-07
2.00E-07
2.00E-07
2.00E-07
l.OOE-06
5.00E-08
Analyst
CXCI
::'.ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
Date
11/14/17
Result
Time
1018
HAKB 12/05/17 1352 1719852
HAKB 12/23/17 1100 1726355
KSDI 12/28/17 1803 1724034
BXFI 12/04/17 1533 1719505
Prep Batch
1718643
Analyst Comments
Nominal Recovery%
90
81.5
98
94.6
Acceptable Limits
(15%-125%)
(15%-125%)
(25%-125%)
(25%-125%)
2
3
4
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: January 8, 2018
Parameter
Company :
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Contact: Ms. Kathy Weinel
Project: Vegetation Analysis --------Client Sample ID: North East
Sample ID: 437346001
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
Project:
Client ID:
DNMI00101
DNMI001
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: January 8, 2018
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Parameter
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
North West
437346002
Vegetation
02-NOV-17 08:45
08-NOV-17
Client
Qualifier Result Uncertainty
lad Alpha Spec Analysis
\lphaspec Th-232, Solid "Dry Weight Corrected"
:horium-232 1.52E-05 +/-l.35E-06
\lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 0.000163 +/-4.07E-06
Jranium-235/236 6.83E-06 +/-9.54E-07
Jranium-238 0.000164 +/-4.07E-06
lad Gas Flow Proportional Counting
}FPC, Pb2IO, Solid "Dry Weight Corrected"
,ead-210 0.000923 +/-1.34E-05
}FPC, Total Alpha Radium, solid "Dry Weight Corrected"
:otal Radium 0.000224 +/-4. l 7E-06
rhe following Prep Methods were performed:
vtethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
Method DescriQtion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Modified
;;urrogate/Tracer Recovery Test
MDC
l.80E-06
l.78E-06
9.50E-07
7.69E-07
l.94E-05
2.0lE-06
rhorium-229 Tracer
Jranium-232 Tracer
,ead Carrier
3arium Carrier
Alphaspec Th-232, Solid "Dry Weight Corrected"
Alphaspec U, Solid "Dry Weight Corrected"
GFPC, Pb210, Solid "Dry Weight Corrected"
GFPC, Total Alpha Radium, solid "Dry Weight
Corrected"
'fotes:
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
1.00E-06
5.00E-08
Analyst
CXCl
:::ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Project:
Client ID:
DNMI00101
DNMI001
Units PF DF Analyst Date
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
Date
11/14/17
Result
HAKB 12/02/17
HAKB 12/23/17
KSD1 12/28/17
BXFl 12/02/17
Time Prep Batch
1018 1718643
Analyst Comments
Nominal Recovery%
95.4
50.6
91.4
83.6
Time Batch Method
1723 1719852
1100 1726355 2
1803 1724034 3
1943 1719505 4
Acceptable Limits
(15%-125%)
(15%-125%)
(25%-125%)
(25%-125%)
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: January 8, 2018
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 West
437346002
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
Project:
Client ID:
DNMI00101
DNMI001
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: January 8, 2018
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
South West
437346003
Vegetation
02-NOV-17 09:45
08-NOV-17
Client
Parameter Qualifier Result Uncertainty
lad Alpha Spec Analysis
\lphaspec Th-232, Solid "Dry Weight Corrected"
~horium-232 6.82E-06 +/-1.05E-06
\lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 0.000119 +/-3.13E-06
Jranium-235/236 8.54E-06 +/-9.68E-07
Jranium-238 0.000124 +/-3.18E-06
lad Gas Flow Proportional Counting
]FPC, Pb2 l 0, Solid "Dry Weight Corrected"
MDC
2.1 IE-06
l.24E-06
l.1 IE-06
8.98E-07
,ead-210 0.000636 +/-1.14E-05 1.72E-05
]FPC, Total Alpha Radium, solid "Dry Weight Corrected"
~otal Radium 9. 70E-05 +/-3.12E-06 3.05E-06
[he following Prep Methods were performed:
IJethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\tfethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Modified
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
1.00E-06
5.00E-08
Analyst
CXCI
Project:
Client ID:
DNMI00101
DNMI001
Units PF DF Analyst Date Time Batch
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
Date
11/14/17
HAKB 12/02/17 1723 1719852
HAKB 12/23/17 1100 1726355
KSDI 12/28/17 1803 1724034
BXFJ 12/02/17 1943 1719505
Time Prep Batch
1018 1718643
Analyst Comments
Method
2
3
4
_;u_rr_o~g~a_te_/_T_ra_c_e_r_R_e_c_o_v_ery~ __ T_e_s_t _________________ R_es_u_l_t __ N_o_m_in_a_l __ R_e_c_o_v_e~ry~o/i_o __ A_c_c~eptable Limits
fhorium-229 Tracer Alphaspec Th-232, Solid "Dry Weight Corrected" 76 (15%-125%)
Jranium-232 Tracer Alphaspec U, Solid "Dry Weight Corrected" 63 (15%-125%)
,ead Carrier GFPC, Pb210, Solid "Dry Weight Corrected" 90.7 (25%-125%)
3arium Carrier GFPC, Total Alpha Radium, solid "Dry Weight 87.2 (25%-125%)
Corrected"
lfotes:
::::ounting Uncertainty is calculated at the 68% confidence level ( I-sigma).
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: January 8, 2018
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
437346003
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
Project:
Client ID:
DNMIOOIOI
DNMIOOI
Units PF DF Analyst Date Time Batch Method
k!IHI I Laboratories LLc
a member of The GEL Group INC
PD Box 30712 Ctm1eston. SC 29417
2-040 Savage Road Cha~eston SC 29407
P 843.556 8171
F 843,766.1178
January 08, 2018
Ms. Kathy W einel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
Work Order: 437346
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on November 08, 2017. This original data report has been prepared and reviewed in
accordance with GEL's standard operating procedures.
Our policy is to provide high quality, personalized analytical services to enable you to meet your analytical needs
on time every time. We trust that you will find everything in order and to your satisfaction. If you have any
questions, please do not hesitate to call me at [phone], ext. 4289.
Purchase Order: DW16138
Enclosures
Sincerely,
te~tl~or
Julie Robinson
Project Manager
11111111 111 1 11111 11 11111111111111
ge l.com
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 437346
Case Narrative
January 08, 2018
Laboratory ldentification:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 437346
Sample receipt.: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on November 08,
2017 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
437346001 North East
437346002 North West
437346003 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.
it~t~for
Julie Robinson
Project Manager
Chain of Custody and
Supporting
Documentation
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: Gel Laboratories Contact: Garrin Palmer --------------2040 Savage Road Ph: 435 678 2221
Charleston, SC 29407 [e-mail]
Chain of Custody/Sampling Analysis Request
Project s amplers Name Samplers Signature
Late Fall VeQetation 2017 Garrin Palmer I ~.~~ ~ (i)/f A,_ -V'
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
North East 11/2/2017 915 Ra 226, U-Nat, Th-232, PB 210
North West 11/2/2017 845 Ra 226, U-Nat, Th-232, PB 210
South West 11/2/2017 945 Ra 226, U-Nat, Th-232, PB 210
Weiahts:
North East: 4800 Grams
North West: 3919 Grams
South West: 4111 Grams
* Please use caution when handling samples. Some
plants in the North East sample have thorns.
Comments: Please send report to Kathy Weinel at kweinel®enerQyfuels.com
o1tefTime
1t1e/W11
Date/Time
m:D I Laboratories LLG
Client:
Received By: ZKW
Currier and Tracking Number
Suspected I-Iu,.ard lnl'onnalion
Shi ped as a DOT Hazardous'?
COC/Samples marked or clnssifted as
radioactive?
Is ackuge, COC, and/or Samples marked HAZ?
Sample Receipt Criteria
1 Shipping containers received intact and
scaled?
2 Chain of custody documents included
with shipment?
3 Samples requiring cold preservation
within (0 .5 6 deg. C)?*
4 Daily check performed and passed on IR
temperature gun?
5 Sample conlainers intact and sealed?
6 Samples requiring chemical preservation
at proper pH?
7 Do any samples require Volatile
Analysis?
8 Samples received within holding time?
9 Sample !D's on COC match ID's on
bottles?
10 Date & time on COC match date & time
on bottles?
11 Number of containers received match
number indicated on COC?
12 Arc sample containers idcntiliablc as
GEL rovided'l
13 COC form is properly signed in
relinq u ished/recci ved sections?
Comments (Use Contlnuntion Form If needed):
SAMPLE RECEIPT & REVIEW FORM
SDG/AR/COC/Work Order:
Dote Received: -/{
01her
i'.I = •If Net Counts> IOOcpm on samples not marked "radioactive", contact the Radiation Safety Group for further
:>< ;z: investigation.
UNff:
Maximum Net Counts Observed* (Observed.,Countsr .Area Background. Counts): ,V CP 'mR/Hr
Classified as: Rad 1 Rad 2 Rad 3
If yes, select Hazards below, and contact the GEL Safety Group.
0PCB's Flammable Foreign Soil RCRA Asbestos Beryllium Other:
Conunents/Qualiticr.; (Required for Non-Confonnlng llelll'l)
Circle Applicable: Seals broken Damaged container Leaking container Olhcr (describe)
Preserv-Jtion Method: Wet Ice Ice Packs Dry ice
•all temperatures are recorded in Celsius TEMP: Zt c_
Temperature Device Serial #: __ ""IR-'-3;c..--'-1..C.6 __ _
Sccondtuy Tempemture Device Serial I' (If Applic::ible):
Circle Applicable: Seals broken Damaged container Leaking contoiner Other (describe)
Sample !D's and Container> Affec1cd:
If Yes, Are Encores or Soil Kits preselll? Yes_ No_ (If yes, take 10 VOA Freezer)
Do VOA vials contain acid preservation? Yes __ No_ N/ A_ (If unknown, select No)
VOA vials'free of headspace? Yes_'''No_ NIA_
Sample !D's and containers affected:
ID's and tests affec1ed:
San-q,lc ID's and con1::1inl!rs nffcclc<l:
Sample !D's affected:
Snmple !D's affected:
GL-CHL-SR-001 Rev 5
,. -~,-·11\1
,rJ:--'!i'fO
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 437346
Client SDG: 437346
Late Fall Vegetation 2017
Project Manager:
Project Name:
Purchase Order:
Package Level:
EDD Format:
Julie Robinson
DNMI00101 Vegetation Analysis
DW16138
LEVEL3
EIM_DNMI
Collect
GELID Client Sample ID Client Sample Desc. Date & Time
437346001 North East
437346002 North West
437346003 South West
Client Sample ID
-001 North East
-002 North West
-003 South West
Status Tests/Methods
REVW Alphaspec Th-232, Solid
REVW Alphaspec LI, Solid
02-NOV-17 09:15
02-NOV-17 08:45
02-NOV-17 09:45
Product
Reference
LI-Natural
REVW GFPC, Total Alpha Radium, solid Ra226
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW Alphaspec Th-232, Solid
REVW Alphaspec LI, Solid LI-Natural
REVW GFPC, Total Alpha Radium, solid Ra226
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
REVW Alphaspec Th-232, Solid
REVW Alphaspec LI, Solid LI-Natural
REVW GFPC, Total Alpha Radium, solid Ra226
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
Work Order Due Date: 10-JAN-18
Package Due Date:
EDD Due Date:
Due Date:
JAR1
Receive Time # of
Date & Time Zone Cont.
08-NOV-17 09:00 -2
08-NOV-17 09:00 -2
08-NOV-17 09:00 -2
Fax Date PM Comments
08-JAN-18
10-JAN-18
10-JAN-18
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Please use caution when
handling samples. Some plants
in the North East sample have
thorns.
Report Date: 08-JAN-18
Work Order:437346
Page 1 of 3
Collector: C
Prelogin #: 20160443172
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
Receive
Codes
GEL Laboratories LLC -Login Review Report
Product: ASP_ THS
Method:
Workdef ID: 1370540 In Product Group? No
DOE EML HASL-300, Th-01-RC Modified
Product Description: Alphaspec Th-232, Solid
Samples: 001,002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
7440-29-1 Thorium-232
Product: LABCOMP _S Workdef ID: 1310628
Method:
In Product Group? No
Product Description: Laboratory Composite -Dry prep instructions
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Pannname
Product: GFC_ PBS WorkdeflD: 1310600 In Product Group? No
Method: DOE RP280 Modified
Product Description: GFPC, Pb210, Solid
Samples: 001, 002, 003
Pannname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS WorkdeflD: 1310679 In Product Group? No
Method: EPA 900.1 Modified
Product Description: GFPC, Total Alpha Radium, solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
Total Radium
Group Name:
Client RDL or
PQL & Unit
.0000002
Group Name:
Client RDL or
PQL & Unit
Group Name:
Client RDL or
PQL & Unit
.000001
Group Name:
Client RDL or
PQL& Unit
.00000005
Reporting
Units
uCi/kg
Reporting
Units
Reporting
Units
uCi/kg
Reporting
Units
uCi/kg
Report Date: 08-JAN-18
Work Order:437346
Page 2 of 3
Group Reference:
Path: No Ash pCi/g
Product Reference:
Moisture Correction: "Dry Weight Corrected"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
Group Reference:
Path: Rad Prep SPRP
Product Reference:
Moisture Correction: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
0
Group Reference:
Path: Standard
Product Reference:
Moisture Correction: "Dry Weight Corrected"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
Group Reference:
Path: Standard
Product Reference: Ra226
Moisture Correction: "Dry Weight Corrected"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
~
(
'
GEL Laboratories LLC -Login Review Report
Product: ASP _uus Workdef ID: 1370669 In Product Group? No
Method: DOE EML HASL-300, U-02-RC Modified
Product Description: Alphaspec U, Solid
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
Contingent
Tests
Action Product Name
Login Requirements:
Requirement
Are these vegetation sample?
Login Reminder?
Description
Group Name:
Client RDL or
PQL & Unit
.0000002
.0000002
.0000002
Samples
Group Reference:
Path: Standard
Report Date: 08-JAN-18
Work Order: 437346
Page 3 of 3
Product Reference: U-Natural
Moisture Correction: "Dry Weight Corrected"
Reporting Parm Included Included Custom
Units Function in Sample? in QC? List?
uCi/kg
uCi/kg
uCi/kg
REG
REG
REG
y
y
y
y
y
y
Yes
Include? Comments
y
y
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry.
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry. Log
with lab comp.
Peer Review by: ___________ _ Work Order (SDG#), PO# Checked? ____ _ C of C signed in receiver location? _____ _
Laboratory
Certifications
List of current GEL Certifications as of 08 January 2018
State Certification
Alaska UST-0110
Arkansas 88-0651
CLIA 42D0904046
California 2940
Colorado SC000\2
Connecticut PH-0169
Delaware SCOOOl2
DoD ELAP/ ISO 17025 A2LA 2567.01
Florida NELAP E87156
Foreign Soils Pennit P330-15-00283,P330-15-00253
Georgia SCOOOl2
Georgia SDWA 967
Hawaii SC00012
Idaho Chemistry SC00012
Idaho Radiochemistry SC00012
Illinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332
Kentucky SDWA 90129
Kentucky Wastewater 90129
Louisiana NELAP 03046 (AI33904)
Louisiana SDW A LA18001 I
Maryland 270
Massachusetts M-SC012
Michigan 9976
Mississippi SC00012
Nebraska NE-OS-26-13
Nevada SC000122018-I
New Hampshire NELAP 205415
New Jersey NELAP SC002
New Mexico SC00012
New York NELAP 11501
North Carolina 233
North Carolina SDW A 45709
North Dakota R-158
Oklahoma 9904
Pennsylvania NELAP 68-00485
Puerto Rico SC00012
S.Carolina Radchem 10120002
South Carolina Chemistry 10120001
Tennessee TN 02934
TexasNELAP T104704235-17-12
UtahNELAP SC000122017-25
Vennont VT87156
Virginia NELAP 460202
Washington C780
West Virginia 997404
Radiochemistry
Technical Case Narrative
Energy Fuels Resources (DNMI)
SDG #: 437346
Product: Alphaspec Th-232, Solid
Analytical Method: DOE EML HASL-300, Th-01-RC Modified
Analytical Procedure: GL-RAD-A-038 REV# 17
Analytical Batch: 1719852
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1718643
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
437346001
437346002
437346003
1203922099
1203922100
]203922101
Client Sample Identification
North East
North West
South West
Method Blank (MB)
43734600l(North East) Sample Duplicate (DUP)
Laboratory Control Sample (LCS)
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
Duplication Criteria between QC Sample and Duplicate Sample
The QC Sample and the Duplicate, (See Below), did not meet the relative percent difference requirement;
however, they do meet the relative error ratio requirement with the value listed below.
Sample Analyte Value
1203922100 (North EastDUP) Thorium-232 RPD 44.5* (0.00%-20.00%) RER 2.89 (0-3)
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
1203922099 (MB) Thorium-232 Result 0.000000625 < MDA 0.00000158 > RDL 0.0000002 uCi/kg
Technical Information
Recounts
Samples 1203922100 (North EastDUP) and 437346001 (North East) were given additional clean-up steps and
recounted in order to improve the resolution. The recounts are reported.
Product: Alphaspec U, Solid
Analytical Method: DOE EML HASL-300, U-02-RC Modified
Analytical Procedure: GL-RAD-A-011 REV# 26
Analytical .Batch: 1726355
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1718643
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)
GEL Sample ID#
437346001
437346002
437346003
1203938920
1203938921
1203938922
437346003(South West) Sample Duplicate (DUP)
Laboratory Control Sample (LCS)
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
Method Blank Criteria
The blank (See Below) activity is greater than the MDC but is less than five percent of the lowest activity in the
batch.
Sample Analyte Value
1203938920 Uranium-233/234 Result: 1. 73E-06 uCi/kg > MDA: l.59E-06 uCi/kg > RDL: 2.00E-07
(MB) uCi/kg
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
1203938920 (MB) Uranium-235/236 Result 0.000000355 < MDA 0.00000136 > RDL 0.0000002 uCi/kg
Uranium-238 Result 0.000000288 < MDA 0.00000138 > RDL 0.0000002 uCi/kg
Technical Information
Sample Re-prep/Re-analysis
The batch was reprepped twice due to low tracer yields. The third analysis is being reported.
Miscellaneous Information
Additional Comments
The tracer peak centroid for sample 1203938920 (MB) is greater than 50 keV from the expected library energy
value for the tracer; however, the tracer yield requirement was met and the tracer peak is within the tracer region
of interest.
Product: Dry Weight
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1718643
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
437346001
437346002
437346003
Client Sample ldentilication
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
Analytical Method: EPA 900.l Modified
Analytical Procedure: GL-RAD-A-010 REV# 16
Analytical Batch: 1719505
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1718643
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)
GEL Sam pie ID#
437346001
437346002
437346003
1203921283
1203921284
1203921285
1203921286
43734600l(North East) Sample Duplicate (DUP)
43734600l(North East) Matrix Spike (MS)
Laboratory Control Sample (LCS)
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} lnrormation
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
1203921283 (MB) Total Radium Result 0.00000169 < MDA 0.0000044 > RDL 0.00000005 uCi/kg
Technical Information
Recounts
Samples 1203921285 (North EastMS) and 1203921286 (LCS) were recounted due to low recovery. The recounts
are reported.
Miscellaneous Information
Additional Comments
The matrix spike, 1203921285 (North EastMS), aliquot was reduced to conserve sample volume.
Product: GFPC, Pb210, Solid
Analytical Method: DOE RP280 Modified
Analytical 'Procedure: GL-RAD-A-018 REV# 14
Analytical Batch: 1724034
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1718643
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
437346001
437346002
437346003
1203932812
1203932813
1203932814
1203932815
Client Sample Identification
North East
North West
South West
Method Blank (MB)
437346002(North West) Sample Duplicate (DUP)
437346002(North West) Matrix Spike (MS)
Laboratory Control Sample (LCS)
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
1203932812 (MB) Lead-210 Result 0.00000741 < MDA 0.000014 > RDL 0.000001 uCi/kg
Technical Information
Sample Re-prep/Re-analysis
Samples were reprepped due to low recovery. The re-analysis is being reported.
Recounts
Samples 1203932814 (North WestMS) and 1203932815 (LCS) were recounted due to low recovery. The
recounts are reported.
Certification Statement
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless otherwise noted in the analytical case narrative.
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Qualifier Definition Report
for
DNMI001 Energy Fuels Resources (USA), Inc.
Client SDG: 437346 GEL Work Order: 437346
The Qualifiers in this report are defined as follows:
* A quality control analyte recovery is outside of specified acceptance criteria
** Analyte is a surrogate compound
U Analyte was analyzed for, but not detected above the CRDL.
Review/Validation
GEL requires all analytical data to be verified by a qualified data reviewer. In addition, all CLP-like deliverables
receive a third level review of the fractional data package.
The following data validator verified the information presented in this data report:
Signature: C,.l O GlJ.,L, (1::J · /'-{ <... ( le fl lJ
Date: 05 JAN 2018
Name: Heather McCarty
Title: Analyst II
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summarl'. Reoort Date: January 8, 2018 Energy Fuels Resources (USA), Inc. Page I of
225 Union Boulevard
Suite 600
Lakewood, Colorado
Contact: Ms. Kathy Weinel
Workorder: 437346
Parmname NOM Sam le ual QC Units RPD% REC% Ran e Anlst Date Time
Rad Alpha Spec
3atch 1719852
QC1203922100 437346001 DUP
Thorium-232 l.04E-05 I.64E-05 uCi/kg 44.5* (0%-20%) HAKB 12/05/17 13:5
Uncertainty +/-1.02E-06 +/-1.33E-06
QCJ203922101 LCS
Thorium-232 0.000128 0.000111 uCi/kg 86.9 (75%-125%) 12/02/17 17:2
Uncertainty +/-3 . I OE-06
QC1203922099 MB
Thorium-232 u 6.25E-07 uCi/kg 12/02/17 17:2
Uncertainty +/-4.80E-07
3atch 1726355
QCJ203938921 437346003 DUP
Uranium-233/234 0.000119 0.000136 uCi/kg 13.4 (0%-20%) HAKB 12/23/ 17 11 :0
Uncertainty +/-3.13E-06 +/-3 .04E-06
Uranium-235/236 8.54E-06 l .OlE-05 uCi/kg 17.3 (Oo/o-20%)
Uncertainty +/-9.68E-07 +/-9.44E-07
Uranium-238 0.000124 0.000143 uCi/kg 13.9 (0%-20%)
Uncertainty +/-3.18E-06 +/-3.09E-06
QC1203938922 LCS
Uranium-233/234 6.46E-05 uCi/kg 12/23/17 11 :01
Uncertainty +/-1 . 79E-06
Uranium-235/236 5.48E-06 uCi/kg
Uncertainty +/-5.90E-07
Uranium-238 6.66E-05 6.59E-05 uCi/kg 99 (75%-125%)
Uncertainty +/-1.81E-06
QC1203938920 MB
Uranium-233/234 1.73E-06 uCi/kg 12/23/17 11 :3'
Uncertainty +/-6.43E-07
Uranium-235/236 u 3.55E-07 uCi/kg
Uncertainty +/-4.35E-07
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary
Workorder: 437346 Page 2 of
:..;[>a::.:r..::m:..:n:.::a:::m.:..::e:...._ _________ __;N:...c..=O;.;M-=------S::..;a:::m=i::..;lc::.e_.._...::..:::.:___--""-'c=---..:cu=nc..cit=--s _ _cRP=-=-D=---'--0/o=------=R=E=C=-0'--'Yo'--"R;.:;:a::..:n:;n.;:..e__:Ac.::;n:.:..:lc:..;st:..__ Date Time
R.ad Alpha Spec
3atch 1726355
Uranium-238 u
Uncertainty
R.ad Gas Flow
3atch 1719505
QC1203921284 437346001 DUP
Total Radium 8.03E-05
Uncertainty +/-2.18E-06
QC1203921286 LCS
Total Radium 0.00492
Uncertainty
QC1203921283 MB
Total Radium u
Uncertainty
QC1203921285 437346001 MS
Total Radium 0.020 8.03E-05
Uncertainty +/-2. l 8E-06
3atch 1724034
QC1203932813 437346002 DUP
Lead-210 0.000923
Uncertainty +/-l.34E-05
QC1203932815 LCS
Lead-210 0.00812
Uncertainty
QC1203932812 MB
Lead-210 u
Uncertainty
QC 1203932814 43 7346002 MS
Lead-210 0.0363 0.000923
Uncertainty +/-l.34E-05
Notes:
Counting Uncertainty is calculated at the 68% confidence level (I-sigma).
The Qualifiers in this report are defined as follows:
** Analyte is a surrogate compound
< Result is less than value reported
2.88E-07
+/-4.07E-07
8.53E-05
+/-2.41E-06
0.00387
+/-4.13E-05
1.69E-06
+/-1.31 E-06
0.0168
+/-0.000161
0.000884
+/-1.31 E-05
0.00814
+/-0.000113
7.41E-06
+/-4.25E-06
0.0402
+l-0.000555
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
HAKB 12/23/17 11 :3'
5.99 (0%-20%) BXFI 12/04/17 15:3
78.5 (75%-125%) 12/13/17 06:4
12/02/17 19:4
83.6 (75%-125%) 12/13/17 06:4
4.35 (0%-20%) KSD1 12/28/17 18:0
100 (75%-125%) 12/29/17 09: l
12/28/17 18:0
108 (75%-125%) 12/28/17 18 :01
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary
Workorder: 437346
> Result is greater than value reported
A The TIC is a suspected aldol-condensation product
B For General Chemistry and Organic analysis the target analyte was detected in the associated blank.
BD Results are either below the MDC or tracer recovery is low
C Analyte has been confirmed by GCIMS analysis
D Results are reported from a diluted aliquot of the sample
F Estimated Value
H Analytical holding time was exceeded
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
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
Ran e Anlst
Nl
ND
NJ
Q
R
u
Ul
UJ
UL
X
y
Not considered detected. The associated number is the reported concentration, which may be inaccurate due to a low bias.
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
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
NIA 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.
ATTACHMENTG
STACK SAMPLE LABORATORY RESULTS
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
October 12, 2017
THIRD QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
SOUTH YELLOW CAKE SCRUBBER
YELLOW CAKE DRYER BAGHOUSE
BLANDING, UT AH
August 15-16, 2017
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.
Mike McNamara
Reviewer:-'--'4/J'-'-""",__~~----tk--________ _
Date: I o/rz. ... j I~ -----~----------
Alex Moore
~
,
Reviewer: "?'k; -------~--------
Date: _---'!c..=..0_---',--""3'----_)o_l_f ____ _
ii
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ......................................................................................................................... l
Test Location and Type of Process ...................................................................................... I
Test Dates ............................................................................................................................. 1
Pollutants Tested and Methods Applied .............................................................................. 1
Test Participants ................................................................................................................... 2
Deviations from EPA Methods ............................................................................................ 2
Quality Assurance ................................................................................................................ 2
Summary of Results
Emission Results .................................................................................................................. 3
Process Data ......................................................................................................................... 3
Description of Collected Samples ........................................................................................ 3
Discussion of Errors or Irregularities ................................................................................... 3
Percent Isokinetic Sampling ............................................................................................... .4
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
Appendices
A: Complete Results and Sample Calculations
B: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
iii
LIST OF TABLES
PAGE
Table
I Measured Radionuclide Emissions ...................................................................................... 3
II Percent Isokinetic Sampling ................................................................................................ 4
III Sampling Point Location ...................................................................................................... 6
IV Complete Results, South Yellow Cake Scrubber Exhaust.. ............................... Appendix A
V Complete Results, Yellow Cake Dryer Baghouse ............................................. Appendix A
LIST OF FIGURES
Figure
1 Facility Schematic Representation South Yellow Cake Scrubber ..................... Appendix D
2 Facility Schematic Representation Yellow Cake Dryer Baghouse .................... Appendix D
3 Schematic of Method 5/114 Sampling Train ..................................................... Appendix E
IV
INTRODUCTION
Test Purpose
This test project was conducted to determine the total radionuclide emissions from the South
Yellow Cake Scrubber and the Yellow Cake Dryer Baghouse exhausts in terms of Curies per dry
standard cubic foot (Ci/dscf).
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Uranium ore is
processed into yellow cake, which is shipped to other facilities for additional processing. There
are two yellow cake dryers with individual scrubbers. Both dryer enclosures discharge into the
Yellow Cake Dryer Baghouse. The packaging enclosure also discharges into the Yellow Cake
Dryer Baghouse. The South Yellow Cake (SVC) dryer was the only operating dryer at the time
of the test. The North Yellow Cake dryer is currently not operational.
Stack schematics are shown as Figures 1 and 2 in Appendix D.
Test Dates
The first test run on the SVC Scrubber was completed August 15, 2017 and the second run on
August 16, 2017.
One run was completed on the Yellow Cake Dryer Baghouse August 16, 2017.
PoJJutants Tested and Methods Applied
The tests were a determination of radionuclide emissions in accordance with EPA Method 5/ 114.
The tests for the SVC and the Yellowcake Dryer Baghouse were for the following radionuclides:
Th-228, Th-230, Th-232, U-234, U-235, U-238, Pb-210, Ra-226 and Ra-228.
Test run filters and front wash residues were sent to Inter-Mountains Labs located in Sheridan,
Wyoming for radionuclide analysis.
Test Participants
Test Facility
State Agency
TETCO
Deviations from EPA Methods
None.
Quality Assurance
Logan Shumway
None
Jeff Graton
Mike McNamara
Doug Olsen
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 V in
Appendix A have more detailed information.
Table I. Measured Radionuclide Emissions
South Yellow Cake Scrubber Yell ow Cake Dryer
Baghouse
Run#
pCi/dscf pCi/hr pCi/dscf
I 53.845 5.780E+06 2.043
2 36.479 4.004E+06
AVE 45.167 4.892E+06
Test Run I on the Yellow Cake Dryer Baghouse was completed with 4 barrels
being filled.
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Scrubber water flow and pressure drop readings
(6p) were recorded and are found in Appendix D. The Dryer Baghouse pressure drop readings
(6p) were recorded and are found on the test run sheets. Production data will be submitted by
Energy Fuels Resources.
Description of Collected Samples
The test filters for the South Yellow Cake Scrubber were covered with a white colored particulate.
The front washes were clear in appearance.
There was no visible particulate matter on the test filter for the Yellow Cake Dryer Baghouse.
The front wash was clear in appearance.
Discussion of Errors or Irregularities
None
3
Percent Jsokinetic Sampling
Each test run was isokinetic within the± I 0% of I 00% criterion specified in the Federal Register.
Isokinetic values for each test run are presented in Table II.
Table II. Percent Isokinetic Sampling
South Yellow Cake Yellow Cake Dryer
Run# Scrubber Baghouse
98 ....... 100
104 ----------------2
4
SOURCE OPERATION
Process Control Devices Operation
AH process control devices were operated normally. Recorded scrubber water flow, pressure, and
baghouse L1p readings are found on the test run sheets or in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND AN AL YTICAL PROCEDURES
Sampling Port Location
The inside diameter of the South Yellow Cake Scrubber stack was 12.75 inches. The two, four-
inch diameter sample port were located 28.24 diameters (30 feet) downstream from the last
disturbance and 6.59 diameters (7 feet) upstream from the next disturbance. Figure l in Appendix
D is a schematic of the stack.
The inside diameter of the Yell ow Cake Dryer Baghouse stack was 16.0 inches. The two, four-
inch diameter sample ports were located 28.38 diameters (454 inches) downstream from the last
disturbance and 3.56 diameters (57 inches) upstream from the next disturbance. The sample port
locations are depicted in Figure 2 in Appendix D.
Sampling Point Location
Table III shows the distance of each sampling point from the inside wall according to EPA
Method l. Each point was marked with a wrapping of glass tape and numbered. These points
were determined by measuring the distance from the inside wall.
Distance (inches) from Inside Wall
Sample Point SYC Scrubber Dryer Baghouse
J
2
3
4
5
6
Sampling Train Description
0.85
3.19
9.56
11.90
0.70
2.34
4.74
11.26
13.66
15.30
To determine the actual emission rates for this stack, 40 CFR 60, Appendix A, Methods 1-5/114
were followed.
All sampling trains were made of inert materials (Teflon, stainless steel and glass) to prevent
interference of the sampled gas and particulate. The stack analyzers used to conduct Methods 1-
5/1 t 4 are constructed to meet the specifications outlined in the CFR. The temperature sensors
6
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 4 in Appendix E is a sketch of the Methods 5/ l l 4 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 5/1 14.
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, South Yellow Cake Scrubber Exhaust
Table V Complete Results, Yellow Cake Dryer Baghouse
Nomenclature
Sample Equations
A
I .-\HU I\
SVC Scrubber
COMPLETE RESULTS
l:Nl-:R(J Y f·UEl,S CORPORATION, !3U\Nl)ING. l 1T/\l I
SOlJ l H 'rTLL.O\VC,1\(,,:1: SCRl nnrn. FXI !Al IS r
Symbol Descrietion Dimensions Run#] Run #2
Date 8 I:-2017 8 I 6 ·2017
Filter# (1821 6822
Begin Time Test Began 8 15 7 ;018
End Time Test Ended I Ci: I l) I 5:5 I
Pbm Meter Barometric Pressure In. Hg Abs 24.40 25.50
6H Orifice Pressure Drop 111.H,O 0.990 I .OX:-
y Meter Calibration Y Factor di1nensionles~ 1.0 I 0 1.0 I 0
Vm Volume Gas Snmpled--Merer Conditions cf 123.880 33 -UJ2.:I
Tm Avg Merer Temperature "F 78.0 77.8
,fap Sq Root Velocity Head Root In. H20 0.720 I 0 .7162
Wtwc Weight Water Collecred Grams 2.:16.3 2]5.6
Tt Duration of Test Minulcs 480 .:180
cp Pilot Tube Coefficie111 Di111c11sionless 0.84 0.84
Dn Nozzle Diameter Inches 0.2250 0.2250
CO2 Volume% Carbon Dioxide Percent 2.60 2.20
02 Volume % O.,y!(en Percent 17.40 17.80
N2 &CO Volume 0/o NitTogen and Carbon Monoxide Percent 80.00 80 ()()
Vm,,d Volume Gas Sampled (Standard) dscf H12 .:-9 I 281 . 17 1
Vw Volume Water Vapor scf I I .6 I 'l 11.IWI
Bw, (measured) l'rac1ion H20 in Stack Gas (Measured) Frac1ion O 0,12 (1.()3 8
B W s (saturated) Fraction H20 in Stack Gas (Saturated) Fraction 0.119 0.110
Bw, Fraction H20 in Stack Gas • Fraclion 0.042 O.o38
xd Fraction of Dry Gas rraction () l)'i 8 0.%2
Md Molecular WL Dry Gas lb/lbmol 2').11 ~HJ.I){)
M, Molecular Wl. Stack Gas lb/lbmol }8.64 2lU15
%1 Percen1 lsokinetic Percenl l/~.2 I 113 r, AVG
T, Avg Stack Temperanire "F 113.7 112.6 113.2
A, Stack Cross Sectional Area Sq Ft. 0 .887 0.887
PG Stack SIAtic Pressure 111. H,O -0.280 -0.280
PbP Sample Pon Barometric Pressure lu Hg, Abs 24.]3 25.43
P, Stack Pressure In. Hg. Abs 2cl .J01) 2 5. WJ
Q, S1ack Gas Volumetric Flow Rate (Std) dscfiT1 1.791 . · OJ 1831'·03 I.SIEIOJ
Oa Stack Gas Volumetric Flow Rate (Actual) cfin 2.501.·0 3 2 .. n1 ,0:1 2A'1E+OJ
v. Velocity of Stack Gas fpm 2.821. · 03 2.7.ff , 03 2.78E~ OJ
Curies Radio1111clides per sample pCi 1.:11.:11.91 I 0330.02
Radionuclides per blank pC1 0.22 0.22
Net Curies Ner Radiouuclides per sample pCi [41°11 .68 111329.8()
Crad Conce111ra1io11 of Radio1111clides pCi/dscf .;-; 8S'1 3(lA7lJ 4~.167
ERrad Emission Rare of Radionuclides pCi/lu 5.7801 . ()(1 ..J 011.:1 I . Oh .t.892[+06
* If the measured moisture content is grealcr than the saturated rr #
the saturated moisture value will be used in all calculations (40 CFR 60, Method 4,
TABLE V
COMPLETE RES UL TS, PM
ENERGY FUELS CORPORATION, BLANDING, UTAH
YELLOW CAKE DRYER BAGHOUSE
Symbol
Date
Filter#
Begin
End
Pb111
DH
y
Vm
T,,,
Description
Dale
Time Tesl Began
Tune Tesl Ended
Meler Baron1e1ric Pressure
Orifice Pressure Drop
Meier Calibralion Y Faclor
Volume Gas Sampled--Mclcr Coudilions
A'!\ Meler Temperalure
ODP Sq Rool Velocity Head
Wt_"c Weighl Wa1erCollec1ed
T1 Duration of Test
Cp Pilot Tube Coeflicienl
D,, Nozzle Diameler
CO2 Volume% Carbon Dioxide
02 Volume ~'o Oxygen
N2 & CO Volume% Nilrogen and Carbon Monoxide
V m,1d Volume Gas Sampled (Standard)
Vw Volume Water Vapor
Bw5 Fraction H,O in Slack Gas
Xd Fraction of Dry Gas
Md Molecular WI. Dry Gas
Ms Molecular W1 Slack Gas
0/o\ Percenl lsokinetic
Ts A,·g Slack T empernture
A, Stack Cross Sec1ional Area
PG Slack Slallc Pressure
Pbp Sample Port Barometric Pressure
P 5 S1ack Pressure
Os Slack Gas Volumetric Flow Rate (Std)
Oa S1ack Gas Volumelric Flow Rale (Ac111al)
V 5 Velocity of Slack Gas
Curies Radionuclides per sample
Curies Radionuclide, per blank
Net Curies Net Radionuclides per sample
C rad Concentralion of Radionuclides
E Rrad Emission Ra1e of Radionuclides
Dimensions
In. Hg. Abs
In H:O
dime11sionless
cf
"F
Rool In H,O
Grams
Minnles
Di1nensionless
h1ches
Percel\t
Percenl
Percenl
dscf
scf
Fraction
Fraction
lbilbmol
lbllb,nol
Percenl
"F
Sq. Fl
In. H,0
In Hg Abs
In Hg. Abs
dscfin
cfin
fpm
pCi
pCi
pCi
pCiidscf
pCi/1,r
Run #I
8/J 6/2017
6828
8:22
10:24
25.50
1.166
1.013
79.797
69.3
0.9570
10.9
120
0.84
0.1910
0.00
20.90
79.10
68.955
0.514
0.007
0.993
28.84
28.76
100.2
93.2
1.396
-1.20
25.43
25.342
4.02E+03
5.02E+03
3.59E+03
141.11
0.22
140.89
2.043
4.934E+05
Dryer Baghouse 13
Method 5 Nomenclature
%1 = percent isokinetic as a percent
A, = stack cross-sectional area (ft3)
AS~P = see JAf>
Btu = unit heat value (British thermal unit)
Bw, = fraction of water in stack gas
Cr = concentration of front half particulate mailer (gr/dscf, lb/dscf. etc.)
Cmcial = concentration of metals (ppm, µg/ft3, e1c.). Atomic symbol replaces "'metal"
CO2 = percent carbon dioxide in the stack gas
Cp = Pitot tube coefficient
C, iavg> = average concentration of x
C, lcorrl = concentration of x corrected to the required percent 0 2
Dcq = equivalent diameter for rectangular stack
~H =-orifice pressure drop (inches H20)
~H@ = orifice pressure (inches H20)
Dn = nozzle diameter (inches)
Dn de, = calculated desired nozzle size (inches)
~p =-stack Aow pressure differential (inches H20)
D~ = diameter of the stack (feet)
EA = percent excess air
ER1 = emission rate of front half particulate (lb/hr)
ERmml3cu = emission rate per mm Btu or ton of fuel etc.
ERx = emission rate of compound. Specific compound replaces x
K-fact = multiplier of test point ~p 10 determine test point ~H
L = length of rectangular stack (inches)
M0 = molecular weight of stack gas, dry basis (lb/lb-mol)
Mn11cr = mass of particulate on filter (mg)
Mr = mass of particulate matter on filter and in front wash (mg)
mmBtu = million Btu
Mp = mass of particulate mal!er in front wash including probe (mg)
Ms = molecular weight of stock gas, wet basis (g/gmol)
N2 = percent nitrogen in the stack gas
02 = percent oxygen in the stack gas
~ = average of the square roots of 6P (may also be referred 10 as AS~P)
Pbm = absolute barometric pressure at the dry gas meter (inches Hg)
Pbp = absolute barometric pressure at the sample location (inches Hg)
Pc. = stack static pressure (inches H20)
P, = absolute stack pressure (inches Hg)
P,10 = absolute pressure at standard conditions (29.92 inches Hg.)
e = time length of test (minutes)
Q., = stack gas volumetric Aow rate (acfm)
Q, = stack gas volumetric flow rate (dscfm)
Q.,. = wet stack gas std. volumetric flow (ft 3/min. wscfm)
Tm = meter temperature (°F)
T, = stack temperature (°F)
T,id = absolute temperature at standard conditions (528°R)
Tt = see 8
Vm = sample volume (ft3) at meter conditions
Vm,,d = volume standard (dsct), sample volume adjusted to 68°F and 29.92 inches Hg.
Method 5 Nomenclature
Vs = velocity of stack gas ( fpm)
Yw = volume water vapor (scf) al 68°F and 29.92 inches Hg.
W = width of rectangular stack (inches)
Wtwc = weigh! of rhe condensed water collected (grams)
Xd = fraction of dry gas
Y = meter calibration Y-factor (dimensionless)
-4
Yw Bw, = ----
Vm~1d + Yw
Mrp · 0.01543 C,-= --'---V rnsid
Method 5 Sample Equations
20.9 -desired %0,
Cx <corr) -= Cx ,~vgl · 20 9 I ,,, O ~ . -actua -10 2
2 -L -W
Deq =----L +W
D,, des = 0 .0269 · (Pbm + 0.0735). J(T~ + 460) Ms
\ (Tm+460) Cµ-Xd v-P~·6P
%02 -0.5 -%CO
EA = -----------0.264 · %N:, -(%0:, -0.5 · %CO)
ER f = Cr · Q, · 0.00857
ER.,
ERmmllw = B /h mm tu r • <J , , ( 846.72 · Dn · 6H@ · C;i · Xd ·Md · P, · Tm+ 460)
K-fact = .1H M. · (T, +460) (Pbm + 136 )
Md = CO:,· 0.44 + 0:, · 0.32 + N2 · 0.28
M, = Mct · Xd + 18 · Bw,
PG P, = Pbr+-. 13 .6
Oa = V,. A,
Oa ·Xt1 ·P,·T,,d Q,= -----(T, +460) · Ps1d
Q,
Q"' = -xd
Yw = Wtwc · 0.04715
Xd c-: J -Bws
APPENDIX B
South Yellow Cake Scrubber
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
Yellow Cake Dryer Baghouse
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
B
Preliminary
Facility Energy Fuels
A Stack Identification South Yellow Cake Scrubber
A I Date
N
Barometric Pressure
Pbm in Hg Pbp in Hg
B--Static Pressure (P0) inH20
Estimated Moisture (Bw,) 1-3 %
Sample Height from Ground 65 feet
Sample Height from Console feet
Comments:
Stack Diameter 12.75" Reference 0.0"
Ports are 7.0' Upstream from next disturbance
Ports are 30.0' Downstream from last disturbance
Port Diameter Type Particulate
Num. of Ports 2 Num. Points 8
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
I 6.70% 0.85 0.85 oy .AJ -.~ ~
2 25.00% 3.19 3.19 oY.~.
=--' 3 75.00% 9.56 9.56 DI -Scf
4 93.30% l J.90 11.90 '"' . S"'Z..
Averages:
Ts ___ _ L Flow -----
6P 'V6P ---------
KEY=> 1 .... T_s ___ 6_P __ L_F_lo_w....,I
~ 5/ 114 _ Field Dara Sheer
Planl: Energy Fuec I
Dare~ / &= \ Js I
~. Tn,vone Time I DGM
Poin1 Clock Min (9) rn)
" 1
__ 1
.f
2
2
3
2
3 "'7-
4
7 4
' ~
,' 2
·2
2
(, 2
3
3
-t 4
4
4
~fl(
TETCO r
Filter r,(jt:-/: Sample Box__i;;:_
Location: ~=.;_;_.=,;;r-===~'-'
Operator: --...,...,,-....,----1-
6P 6H (in H,0) I Vacuum I Temperatures (~ DGM Temp er .• )
('""'°' Desired Actual cm flt> Stack (T,) Probe Oven Filter Effiuenl Out In
</ --ii --I · --.u i I • I • -11------1 t-------1:1------t----,1----+----t----tt----+---
Total J1.,?5«s'\V. v 11'-~
Average ,J • "'\ 'Z,-0'
Comments:
i:s-1-;y
·'\'1. 0
itt4-
n,-1
31~~
1--~-0
Page _l_of__l_ Run#_f_
r 6 N
Stack Diameter filL__ Port Reference _O"_
_7' __ Upstream from next disturbance
30' Downstream from last distur_'2_ance
Assumed Moisture 3-5 %
Probe 2 'T b Cp __QM,
Nozzle 9iiibration , ;
.-it.) ."ll~ .zn ,zt~
AvgD. ~i~
Gas Bag t,I ( :Z.,
Console~
Y-Facto.r .
6H@ • r H20
Barometric Pressures
Pb,. 7. I.{·</ D in Hg
Pb, ':::Llf::B:: ~n Hg 2 '( , ~ 5
Pc;-C,. Zr in H,O
Leak C~eck: Pre ~
ft1tmi~ () ./)6~ _/2_:_C>O 3
Vo114in Hs z;
Pi1ot Rate ~·6
lnH,O 4/5
Water Collected
Time Sampled
~
~
--:---z..-':'{_!P....:=.· 3:...__ g ff° ~·"I min
~"~ d?".1 :!
7
K= \1~
~
DGM before leak check Vac ("Hg) Rate( ft3/min) DGM after leak check Vac("Hg) Rate( ft3/min)
__ 51114_Field Data Sheet TETCO f£
Filter, B-Z-Z:. Sample Box __ _
Plant: Eneri 'uels 1
Date: J l, / I :i'
Location: South 50w Cake Dryer Scrubber
Operator: ' l
Time II DGM
~
~p Vacuum II Temperatures ("I-) II DGM Te.mp er,.) I I I I I
~~=*tf·-'°VJ™'l''l~I/Vi I ~vvltri~u,T~II '"I~ ~ () :i, ?l J~?: ~.& o . . i: ,-1:: : i, : : : = :~l\ : ~ o_: '? E~ : ~ ~, :: 1. ~,: =---...-o
2
~
3
3
'_4
4
4
,4 ~ 1 111/:5
1
1 r-
S._2
2
2
~ 3
3
3
4-4
4 -
4
Total
Average
Comments:
)3~ .o-t\,. ,J t ll~'ti :i~· oY
,J~~i-f.o~
Additional (Extra) Leak Check Information
Zl-C ~
I\L-.(p
Page _l_of_l _ Run # __ 2-
r 6 N
Stack Diameter 12. 75". Port Reference Q'.'.___
./
_7_' __ Upstream from next disturbance
30' Downstream from last disturbance
Assumed Moisture 3-5 %
Probe ~ Cp__QM
Nozzle Ca].i.bration _. ~ ,;--
. 1-is . -zz..s , z/!5 . u-!,
Avg D0 • -Z,Z,. ~ inches
Gas Bag A--o '1
Console ·iJ
Y-Factor / ·DI 0
~H@ ( · S'°1? 3 in H20
Barometric Pressures
Pbm -z,$: S-0 in Hg
Pb0 -z..S::: '{_5 in Hg
P,7""-/). i..¥ in H20
Leak Check· Pre
ft·',min c, ·ocG
vacinHg~
Pho, Rate
In H10
OD
i·~
Pos1 ----Pf-0 ¥"'
O· c)
t.j, <
Water Collected ·~J 5-0 g
Time Sampled "jf O min
~ 6H@
(2 oflowRl!!'ej cc/min p,.,_,>,,J
K=v ~
IS~--@@ITT:
DGM before leak check Vac ("Hg) Rate( ft3/min) DGM after leak check Vac ("Hg) Rate( ft3/mln)
Preliminary
Facility Energy Fuels
~ Stack Identification Yellow Cake Dryer Baghouse
~ Date
Barometric Pressure
Pbm in Hg Pbp in Hg
I t-B Static Pressure (P0) in H20
Estimated Moisture (Bw.) 1-2 %
,,
Sample Height from Ground 65 feet
Sample Height from Console feet
Comments:
Stack Diameter 16.0" Reference 0.0"
Ports me 4.75' Upstream from next disturbance
Pons are 37.83' Downstream from last disturbance
Pon Diameter Type Particulate
Num. of Pons 2 Num. Points 12
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
l 4.40% 0.70 0.70
2 14.60% 2.34 2.34
3 29.60% 4.74 4.74
4 70.40% 11.26 11.26
5 85.40% 13.66 13.66
6 95.60% 15.30 15.30
Averages:
Ts L Flow ---------
~p ..J~p
KEY=>
t;/11'1, Field Data Sheet
Plant: Energy Fuels
Date: 0l ( '-{ l '1=
Traverse Time DGM AP AH ("H,0)
Point Clock Min (0) en'> Cin11:-l>) Desired Actual
(} 1 8 '. i,t... 0 L.l'-g·S"l •!:!( (. /(o t. l(o
2 10 c.,,!'. 1<., .•n L • 11., l . , (.,
3 z.o to\ 1' l. 8-lo -~z.. l, l + \.1~
4 Jo C( ,e,., 10 • '\ z... l ,·1 ':f-1,11"
5 'iO 'i'i{, lwO . 't3 1,1e \,16
6 So Sol ,folO • 1'!) l. I '0 (,(~
A. 1 IS\ ·.1.~ (o0 508. l-:J, s .~n 1-11 L.1..,..-
2 '7-0 s 1'-t. 8i..;-' ,'b~ Iii~ l,l~
3 -eo 15-i t. 5't '( ·"10 I o1 -5" (, 11'"
4 ",O SZ.B ti{ • 'fo ,. ,-r '" i
5 [OQ .s~~· o~o •'\~ I, ·q ,.~(
6 110 S=4 \.1,.-z,O .q3 l ,1 'o I.IS
10·.z.'{ ,2.0 s·"'~ .3.ta
TETCO r
Fitter e,e,i'b Sample Box_,-__
Vacuum
(inll(:)
.3
~
3
~
3
.3
1
3
3
.J
3
:3
Location: Yellowcake Dryer Bagllouse
Operator: l't'\.&M.:~ ...
Temperatures l'1'>
Stack (T,) Probe Probe OuL Filler
90 2"-{ 270 ?..7o
q_ \ Z.'{ lo z. {(o i.<b
ci-z.. 2.4 C 2!3 Z(~
9.2. ?{l,... '2.'1 '\ l"{Cf
q2.,. Zi'O 2.)£ Z.38
91. Z~\ ?.'40 c!'io
q, 2<..o '2. ,' 2. l{i
9'{ 2"o l{i-Zf~
C\5 2.fi. ~ -i(3 'Z?~
95' z<c.~ ?fz... 'lfi.
~(,, Z3o '2.'{3 Z.'f~
'ffo i,r 7..'10 ?'tv
Effluent
{,,[
5-+
Sl
SI
~ 'f
5 '< ss
5 ?.
S''Z..
53
Sl
5 7...
Total --.:....:....:...~~.J L\, "l'b~t.t./ 13 .C\11\v ./ 1q .1q1-tll~ ,/
4:> :z. .. Averai;e .J ,'l510 \,l~lo
Time Comments: Time Beghouse ~P
St 2.;:, ,;t( ~ f,d.li <.l.S -'6 '.'IQ 'l,') 'j L[
l,}~
Cf '.tOI l. ·~ ~
DGM Tcmp(T.J
Out In
C.f ~3 r..a C-t,{ ,t b')
11. (o~ ., '{ /, '1
i~ b+
1?... ~5
13 ,~
7~ )..8
7</ '78
N loR
71.( "'o
\\,~<..\ ./
,
3
(
Page __ of __ ( Run #_\ _
i B Ao N
Stack Diameter _16"__ Pon Reference _o.o··-
Ports are 4. 75 Upstream from next disturbance
Pons are 37.8' Downstream from last dis1urbance
Assumed Moisture 1 %
Probe l0 & Cp 0.84
Nozzle Calibration
d~l .l~ l ~ _:131_
AvgD. l I~ I inches ·l~l~
Gas Bag Ambient Air
Console_j
Y-Factor~
AHo _\_. ~ in H20
Barometric Pressures
Pbm 2-f. {o
Pb0 1.{' -t):
p(; -l. 2D
Loa.k Check: fu
ft·1/min
in Hg
in Hg
in H,O
fQfil
O·O<l 2.-O· oo'2.----
vac in Hg__l o. 0
Pi1ol Ra1c O, 0
lnH,O a__,Q
Water Collected
Time Sampled
Review
___!b_Q
0-o
~-0
It:>-~
____!_fp
~
K ...
K ~
@T.,
@T
g
min
South Yell ow Cake Scrubber
Sample Recovery
Gas Analysis Data (ORSAT)
Yellow Cake Dryer Baghouse
Sample Recovery
Gas Analysis Data (Ambient)
Chain of Custody
Lab Analysis
APPENDIXC
C
Method 5 SYC 5 imp
Facility: Energy Fuels
Stack Identification: SYC Scrubber
Date:
IMPINGERS
Filter Number
IMPINGERS
Filter Number
IMPINGERS
Filter Number
------------------
Run: _ __,\..__ Sample Box: __.f__, __
2 I 3 I 4 I s
lmpinger Number
6
Initial Volume of liquid (H_20) in impingers, (ml) I Silica Gel
Run: Sample Box: ----f.
2
lminger Number I 4 I s 6
Initial Volume of liqµid (H10) in impingers_ (ml)
drop out 100 I 100 ! MT j Silica Gel
Final (gl lal.f O .11
Initial (g) 5-ft, t./, 5"
Net (g) 5. '\
Total (g) 2:i,S, ~ =::!!!!!!!:::::::::::===:====
Run: Sample Box: ___ _
2 I 3 I 4 I s
lmpioger Number
Initial Volume of liquid (H20) in impingers, (ml)
drop out 100 I 100 I MT I SilicaGel
Final (g) -----------------------1 nit i a I (g) --------1----------------N et (g> ========='====::!====!:::::========
Total (g) ========
8/,c. ( 11-
Location _ _:;S;...__'-{-'--C ___________ _
Analytical Method ____________ _
0a" 'ir) is/, 1
Test No.
Gas Bag No. f\ C -'S
Ambient Temp
Operator l j
DateJ;&
fo,No ~ Gas Bag No. -()
Ambient Temp
Operator
\
Date -----TestNo. -----Gas Bag No. ____ _
Ambient Temp ____ _
Operator ____ _
RUN
2
Actual Nel Actual Ne1
Gas Readin& Readin&
COz z.&6 2-& 2·l 2-/,
0 2 (Net is Actual 0 2
Reading Minus Actual zo D , 1--1 ?o.o rr, I CO2 Reading).
N2 (Net is JOO Minus
Actual 0 2 Reading).
RUN
2
Actual Net Actual Net
Gas Reading Reading
CO2 Z, 'L z. 2.. '2.L ~. 'l...
0 2 (Net is Actual 0 2
Reading Minus Actual 2o. o 17. 8 Zo. o 17.~ CO2 Reading).
N1 (Net is 100 Minus
Actual 0 2 Reading).
RUN
2
Actual
Readine
Net Acrual Net
Gas
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 02 Reading).
Reading
to2 was determined using a gas analyzer
CO is not measured, as it has Lhe same molecular weight as N2
3
Actual Nel
Reading
2.i 7.t.,
20.0 11·1
3
Actual Nee
Reading
2.L '2. 2..
20.0 17,'8
3
Acrual Nee
Reading
Average
Net
Volume
2.6
} 7'
Average
Net
Volume
2. 'L
17~
Average
Net
Volume
Method 5
Facility: Energy Fuels Date: Bf I Y 1-=l-
Stack Identification: Yellow Cake Dryer Baghouse Me1hod: --------5
IMPlNGERS
Filter Number:
IMPINGERS
Filter Number:
IMP!NGERS
Filter Number:
Run: ----Sample Box: ~ ----
Impmger Number
100
Final (g) ___ --+-=---'-+-~-----+-----"---+----+-----
1 nit ial (g) -.:;;;.--,,--"="-+.=.i,c...;::'-'-'"-+-..:;_~_,.,-1-&...a..1......C--f-+----+----
Net (gl =====:=!====:!:::!:=======:::!::::!:!!!!==de:::::!::========
Run: Sample Box:----
lmpinger Number
2 I .l. I .i. I .J...
Initial Volume of liquid (H,0) in impingers, (ml)
100 100 ! [ SG !
Final (gJ ___ --+----+----+-----t----+-----
lnitial (g) ___ ---+-----+-----+-----+----+----
Net (g) ================::::!==============
Total (g) ========
Run: ----Sample Box: ___ _
lmpinger Number
.L I ,1... t .L I .J... 6
Initial Volume ofliqu,d (H10) in impingers. (ml)
100 100 [ [ SG [
Final (gl ____________ --+-----+----+-----
Initial (g) ___ --+----+-----+-----+----+-----
Net (g) ===============:::::!====::::!:::::::=========
Total (g) ========
..c.;._, -UYfa:
INTER-MOUtHAIN LABS
Client Name
En~rgy Fuels
Inter-Mountain Labs
Sheridan, WY and Gillette, WY
Project Identification
All shaded fields must be completed.
This is a legal document; any misrepresentalion may be conslrued as fraud.
Sampler (Signature/Attestation of Authenticity)
SQUth Yeffqw <2~~ §_<;:(!Jbb~H •. OrYe~
Report Address Contact Name ANALYSES/PARAMETERS
391 . East 620 South
Am~fk:~n FP.Hc·i V~IJ .~40Q3
Invoice Address
EfRI C/Oaccouri& Payable
0
Email
Phone
225 ~~ion Bvld.~l;_J;te.600 lak~V.19.0d .. qp.80228
' "rurchase_Order #
LABID I DATE I TIME SAMPLE
SAMPLED IDENTIFICATION
os,15111 I 8:12 6821 SYC Scrubber RUN 1
7:48 6822 SVC Scrubber RUN 2
8:22 6828 Yellow Cake Dryer Baghouse
8:12 6821 SVC Scrubber RUN 1
7:48 6822 SVC Scrubber RUN 2
8:22 6828 Yellow Cake Dryer Bag_house
-· -· ··-· ~w.::i::.:-:
Y, .:;:,,_:~-~ .... ...........
[Rl FedEx Soil SL
Quote#
co ' iii ~ •, # of z .,
I i Matrix Containers ;;:>
FT 1 X X
FT 1 X X
FT 1 X X
OT 1 X X
OT 1 X X
OT 1 X X
Compliance Monitoring ?
Program (SOWA, NPDES, ..
Q
Cl) ~ 0 N ~I "' ~ M N ~ N "C 1 iE ' I'll I .s::. ~ ~, 1-:-
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
'I Page 1 of 1
#WEB
Telephone#
435'678-411,3
I REMARKS
!Conduct /Blanks
D USPS Solid so
D Hand Carried Filter FT
PWSID /Permit# 'IContact at Energy Fuels Blanding: Logan Shumway I
Chlorinated? " • • ···
D Other Other OT Rush & Urgent Surcharges will be applied Lab Client
Inter-Mountain Labs. Inc www.intermountainlabs.com Rev4.6 Web
~ ··1m-1::
1t<Hl!.-M0UMTA1t,l l "8S
Client Name
Enerav Fi;aels
Inter-Mountain Labs
Sheridan. WY and Gillette, WY
Project Identification
... ,GJ~fAtN ·01tcusrooV·' RECORD .; " . ~ ....:. ~ ~ ___, . .-. ,,.: ..
All shaded fields must be completed
Ttiis 1s a legal docun,ent, any m rsittp1t!'St:11t-al1on may be conslruec! as fraud
sampler (Signature/Attestation of Authenticity)
South Yellow ~ke Scrubber, Dryer
Report Address Contact Name ANALYSES/PARAMETERS
391 East 620 South
American,Fork, Utah ~4003 ..
Invoice Address
EFRI C/Oaccounts Payable
mall
Phone
Purchase Orde, #
226 Union Bvld.Suite 600 Lakewood C0.80228 • ~ £.
LAB ID I DATE I TIME
SAMPLED
SAMPLE
IDENTIFICATION
8:12 16821 SVC Scrubber RUN 1
7:48 16822 SVC Scrubber RUN 2
8:22 16828 Yellow Cake Dryer Baghouse
8:12 16821 SVC Scrubber RUN 1
7:48 16822 SVC Scrubber RUN 2
8:22 16828 Yellow Cake Dryer Baghouse
Quote# \ -#of " :.;:
Matrix Conlainers :=>.
FT 1 X
FT X
FT X
OT X
OT 1 I X
OT X
Compliance Monitoring ?
: '. 0
(0 co .co ·~ .N NI N N . N I") ,; N I'll ~ t')I ~ ~ ~ ell J::, :c ~ jl I-I-
I 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
I
Page 1
#WEB
Telephone#
435-1378-4113
of
REMARKS
!Conduct /Blanks
I
1
0 FedEx Soil SL
0 USPS
Standard turnaround
(J RUSH -5 Working Days
Program (SOWA, NPDES, ... j __________ .. __ --_.,,._·_·--------------------1
PWSID /Permit# · Contacl at Ener Solid SD
D Hand Carried Filter FT
0 Other Other OT
Inter-Mountain Labs, Inc
U URGENT -< 2 Working Days
Rush & Urgent Surcharges will be applied
Chlorinated? ':( I N ~'-----~-------------------! Sample Disposai: Lab Client
www interrnountainlabs.corn Rev 46Web
·'~ffl ..... Your Environmental Monitoring Partner L Inter-Mountain Labs----------------------------------
1""1'·MouNu, .. LAes 1673 Terra Avenue. Sheridan, Wyoming 82801 ph: [phone]
Date: 9/19/2017
CLIENT:
Project:
Lab Order:
Energy Fuels (White Mesa)
South Yellow Cake Scrubber. Dryer
51708353
CASE NARRATIVE
Report ID: 51708353001
Samples 6821 SVC Scrubber RUN 1 filter and beaker. 6822 SVC Scrubber RUN 2 filter and beaker, and 6828 Yellow Cake
Dryer Baghouse filter and beaker were received on August 21. 2017.
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 Inter-Mountain Laboratories except as indicated
in this case narrative.
Qualifiers by sample
LCSD-34 -Uranium Isotopic Fillers/Uranium 238 -RPD outside accepted recovery limits
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 .}> /J ,;?" ,r Reviewed by: vt_/.;e.r ..______
Wade Nieuwsma. Assistant Laboratory Manager Page 1 or 1
iiYit lnte,-Mounta;n Labs
Your Environmental Monitoring Partner
UtT(R. .. MOUJ<IIITAIN L°""81i, 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 9/19/2017
391 Ea st 620 South Report ID 51708353001
American Fork, UT 84003
Project Name: South Yellow Cake Scrubber. Dryer Work Order: 51708353
Lab ID: S 1708353-001 Collection Date: 8/15/2017 8: 12:00 AM
ClientSample ID: 6821 SVC Scrubber RUN 1 filter and beaker Date Received: 8/21/2017 9:37:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 3.2E-05 µCi/Sample 2E-06 6E-14 OTW01 09/13/201 7 1650 MB
Lead 210 Precision(±) 3.8E-06 µCi/Sample OTW01 09/13/2017 1650 MB
Radium 226 1.5E-07 µCi/Sample 2E-07 9E-14 SM 7500RAB 09/12/2017 1620 MB
Radium 226 Precision (±) 1 E-07 µCi/Sample SM 7500RAB 09/12/2017 1620 MB
Radium 228 -9.4E-06 µCi/Sample 1E-06 2E-13 Ga-Tech 09/16/2017 640 MB
Radium 228 Precision (±) 5.6E-06 µCi/Sample Ga-Tech 09/16/2017 640 MB
Thorium 230 8E-07 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-230 Precision (±) 4E-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 228 9.6E-08 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-228 Precision (±) 1.3E-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 232 0.0E-07 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-232 Precision (±) O.OE-07 µCi/Sample ACW10 09/07/2017 1222 WN
Uranium 234 6.145E-03 µCi/Sample 4E-07 9E-15 ACW01 09/19/2017 846 MB
Uranium 234 Precision (±) 1.2E-3 µCi/Sample ACW01 09/19/2017 846 MB
Uranium 235 3.1586E-04 µCi/Sample 4E-07 9E-15 ACW01 09/19/2017 846 MB
Uranium 235 Precision (±) 6.2E-05 µCi/Sample ACW01 09/19/2017 846 MB
Uranium 238 7 .648E-03 µCi/Sample 4E-07 9E-15 ACW01 09/19/2017 846 MB
Uranium 238 Precision (±) 1.5E-03 µCi/Sample ACW01 09/19/2017 846 MB
Metals -Total
Thorium 232 NO µg/Sample 45 3E-15 EPA 200.8 08/30/2017 1116 MS
Uranium 16600 µg/Sample 9E-15 EPA 200.8 08/30/2017 1038 MS
These results apply only to the samples tested. RL . Reporting Limit
Qualifiers: B Analyte de1ected in the associated Method Blank C Calculated Value
E Value above quanlitation range G Analyzed at IML Gillette laboratory
H Holding limes for preparation or analysis exceeded J Analyte delected below quantilation limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at the Reponing Limit O Outside lhe Range of Dilutions
S Spike Recovery outside accepted recovery limits X Matrix Effect
Reviewed by: .... M_..'-~----=--:.-:.-:_~-:_:.:::::: __ _
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 3
,Hitt: Your Environmental Monitoring Partner
Inter-Mountain Labs
HffU.-MOUHTAtH l:AII.$ 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 9/19/2017
391 East 620 South Report ID S1708353001
American Fork. UT 84003
ProjectName: South Yellow Cake Scrubber, Dryer Work Order: S1708353
Lab 10: S 1708353-002 Collection Date: 8/16/2017 7 :48:00 AM
ClientSample ID: 6822 SYC Scrubber RUN 2 filter and beaker DateReceived: 8/21/2017 9:37:00 AM
COC: WEB Field Sampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 4.4E -05 µCi/Sample 2E-06 6E-14 OTW01 09/13/2017 1650 MB
Lead 210 Precision(±) 4.0E -06 µCi/Sample OTW01 09/13/2017 1650 MB
Radium 226 5.7E -07 µCi/Sample 2E-07 9E-14 SM 7500RAB 09/12/2017 1620 MB
Radium 226 Precision (±) .2E -07 µCi/Sample SM 7500RAB 09/12/2017 1620 MB
Radium 228 -5.3E-06 µCi/Sample lE-06 2E-13 Ga-Tech 09/16/2017 943 MB
Radium 228 Precision (±) 6.6E -06 µCi/Sample Ga-Tech 09/16/2017 943 MB
Thorium 230 1.3E-06 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-230 Precision (±) 4E-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 228 9.0E-08 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-228 Precision (±) 1.0E-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 232 5.9E-08 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-232 Precision (±) 8.3E-08 µCi/Sample ACW10 09/07/2017 1222 WN
Uranium 234 4.568E-03 µCi/Sample 4E-07 9E-15 ACWOl 08/31/2017 000 MB
Uranium 234 Precision (±) 9.0E-04 µCi/Sample ACW01 08/31/2017 000 MB
Uranium 235 1.57E-04 µCi/Sample 4E-07 9E-15 ACW01 08/31/2017 000 MB
Uranium 235 Precision (±) 3.1 E-05 µCi/Sample ACW01 08/31/2017 000 MB
Uranium 238 5.559E-03 µCi/Sample 4E-07 9E-15 ACWOl 08/31/2017 000 MB
Uranium 238 Precision (±) 1.lE-03 µCi/Sample ACW01 08/31/2017 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 08/30/2017 1119 MS
Uranium 14200 µg/Sample 9E-15 EPA 200.8 08/30/2017 1 150 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 quantila\ion range G Analyzed at IML Gillelle laboralory
H Holding limes 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 Nol Detected al the Reporting Limit 0 Outside the Range of Dilutions
S Spike Recovery outside accepted recovery limits X Matrix Ellecl
~,4,,..-,, ...--
Reviewed by: ... ~a...,,::;.._~---------------
Wade Nieuwsma, Assistant Laboratory Manager Page 2 of 3
.... ~I:: Your Environmental Monitoring Partner
Inter-Mountain Labs----------------------------------------•~n•-,..0""' .. 1" ..... 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 9/19/2017
391 East 620 South Report ID S1708353001
American Fork, UT 84003
ProjectName: South Yellow Cake Scrubber, Dryer Work Order: S1708353
Lab ID: S 1708353-003 CollectionDate: 8/16/2017 8:22:00 AM
ClientSample ID: 6828 Yellow Cake Dryer Baghouse filter and beaker Date Received: 8/21/2017 9:37:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 8.7E -06 µCi/Sample 2E-06 6E-14 OTW01 09/13/2017 1650 MB
Lead 210 Precision (t) 2.6E-06 µCi/Sample OTW01 09/13/2017 1650 MB
Radium 226 1.8E-07 µCi/Sample 2E-07 9E-14 SM 7500RAB 09/12/2017 1620 MB
Radium 226 Precision (±) 1 E-07 µCi/Sample SM 7500RAB 09/12/2017 1620 MB
Radium 228 -1.0E-05 µCi/Sample lE-06 2E-13 Ga-Tech 09/16/2017 1246 MB
Radium 228 Precision (±) 6.6E -06 µCi/Sample Ga-Tech 09/16/2017 1246 MB
Thorium 230 1.7E -07 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-230 Precision (±) 2E-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 228 2.6E-07 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-228 Precision (±) 2.lE-07 µCi/Sample ACW10 09/07/2017 1222 WN
Thorium 232 O.OE-07 µCi/Sample 2E-07 3E-15 ACW10 09/07/2017 1222 WN
Thorium-232 Precision (±) O.OE-07 µCi/Sample ACW10 09/07/2017 1222 WN
Uranium 234 6.19E-05 µCi/Sample 4E-07 9E-15 ACWOl 08/31/201 7 000 MB
Uranium 234 Precision (±) 1.lE-05 µCi/Sample ACWOl 08/31/2017 000 MB
Uranium 235 2.5E-06 µCi/Sample 4E-07 9E-15 ACWOl 08/31/2017 000 MB
Uranium 235 Precision (±) 1. 7E -06 µCi/Sample ACWOl 08/31/2017 000 MB
Uranium 238 6.74E-05 µCi/Sample 4E-07 9E-15 ACWOl 08/31/2017 000 MB
Uranium 238 Precision (±) 1.lE-05 µCi/Sample ACW01 08/31/2017 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 08/30/2017 1122 MS
Uranium 182 µg/Sample 9E-15 EPA 200.8 08/30/201 7 1100 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 quanlitation range G Analyzed at IML Gillette laboratory
H Holding times for preparation or analysis exceeded J Analyte detected below quantitation limits
L Ana lyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at the Reporting Limit O Outside the Range of Dilutions
S Spike Recovery outside accepted recovery limits X Matrix Effect
~/J.-4' r" Reviewed by: .... ~-""'--~--.____ ________ _
Wade Nieuwsma. Assistant Laboratory Manager Page 3 of 3
-~~ Im I::. Your Environmental Monitoring Partner Inter-Mountain Labs-----------------------------------------
a.nut•Mou1-1T•m LAB:$ 1673 Terra Avenue, Sheridan. Wyoming 82801 ph: [phone]
ANAL VTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1708353
Project: South Yellow Cake Scrubber. Dryer
Lead 210 in Filters
MB-639 (09/13/17 16:50)
Analyte
Lead 210
Lead 210 in Filters
LCS-639 (09/13/17 16:50)
Analyte
Lead 210
Lead 210 in Filters
MS-639 (09/13/17 16:50)
Analyte
Lead 210
Lead 210 in Filters
MSD-639 (09/13/17 16:50)
Analyte
Lead 210
Radium 228 by Ga/Tech
MB-1790 (09/1 5/17 21: 29)
Analyte
Radium 228
Radium 228 by GafTech
LCS-1790 (09/15/17 18:26)
Analyte
Radium 228
Radium 228 by Ga/Tech
MS-1790 (09/16/17 00:33)
Analyte
Radium 228
Radium 228 by Ga/Tech
Qualifiers:
MSD-1790 (09/16/17 03:36)
Analyte
Radium 228
B Analyte de1ec1ed in lhe associaled Melhod Blank
G Analyzed al IML Gilleue labora1ory
J Analyte delected below quan1i1a1ion limilS
ND Not De1ec1ed at the Reporting Limit
R RPO oulside accepled recovery limils
X Malrix Effecl
Sample Type MBLK
RunNo: 150016
Result
ND
Sample Type LCS
RunNo: 150016
Result
1 E-05
Sample Type MS
Date: 9/19/2017
Report ID: S1708353001
Units: µCi/Sample
Prep Date: 08/29/17 0:00 Batch ID R150016
RL Spike Ref Samp %REC % Rec Limits
2E-06
Units: µCi/Sample
PrepDate: 08/29/17 0:00 BatchlD R150016
RL Spike Ref Samp %REC % Rec Limits
2E-06 1 E-05 99.7 80 -147
Units: µCi/Sample
RunNo: 150016 Prep Date: 08/29/17 0:00 Batch ID R150016
Qual
Qual
Result RL Spike Ref Samp %REC % Rec Limits Qual
1E-05
Sample Type MSD
2E-06 1E-05 ND
Units: µCi/Sample
101 80 -143
RunNo: 150016 PrepDate: 08/29/17 0:00 BatchlD R150016
Result RL Cone %RPO %REC % RPD Limits Qual
1 E-05 2E-06 1E-05 1.38 99.3 20
Sample Type MBLK Units: µCi/Sample
RunNo: 150094 Prep Date: 09/18/17 8:27 Batch ID 13666
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND 1 E-06
Sample Type LCS Units: µCi/Sample
RunNo: 150094
Result
PrepDate: 09/18/17 8:27
RL Spike Ref Samp
1E-06 4E-05
BatchlD 13666
%REC % Rec Limits
89.7 65.9 -132 4E-05
Sample Type MS Units: µCi/Sample
RunNo: 150094
Result
PrepDate: 09/18/17 8:27
RL Spike Ref Samp
1E-06 4E-05 0.000002c
BatchlD 13666
%REC % Rec Limits
97.8 50 -139 4E-05
Sample Type MSD Units: µCi/Sample
E
H
L
0
s
RunNo: 150094
Result
PrepDate: 09/18/17 8:27
RL Cone %RPO
4E-05 1E-06 4E-05 8.44
Value above quantitation range
Holding limes for prepara1ion or analysis exceeded
Analyzed by ano1her laboratory
Outside 1he Range of Dilutions
Spike Recovery outside accepted recovery limils
BatchlD 13666
%REC % RPD Limits
89.5 20
Page 1 of 4
Qual
Qual
Qual
Your Environmental Monitoring Partner .-.~mt: Inter-Mountain Labs-----------------------------------------'"nfl-Mou,.,,,,., .... LAIIS 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
ANAL VTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1708353
Project: South Yellow Cake Scrubber. Dryer
Radium 226 Air Filter Analysis
MB-1790 (09/12/17 16:20)
Analyte
Radium 226
Radium 226 Air Filter Analysis
LCS-1790 (09/12/17 16:20)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MS-1790 (09/12/17 16:20)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MSD-1790 (09/12/17 16:20)
Analyte
Radium 226
Thorium Air Filter Analysis
MB-565 (09/07/17 12:21)
Analyte
Thorium-228
Thorium-230
Thorium-232
Thorium Air Filter Analysis
LCS-565 (09/07/17 12:21)
Analyte
Thorium-228
Thorium-230
Thorium-232
Thorium Air Filter Analysis
Qualifiers:
LCSD-565 (09/07/17 12:22)
Analyte
Thorium-230
B Analyte delecled in !he associaled Melhod Blank
G Analyzed al /ML Gillette laboratory
J Analyte delecled below quan1i1a1ion limils
ND Nol De1ected at the Reporting Umil
R RPO outside accepted recovery limils
X Malrix Eflecl
Date: 9/19/2017
Report ID: S1708353001
Sample Type MBLK Units: µCi/Sample
RunNo: 149962 PrepDate: 08/25/17 16:30 BatchlD 13649
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND
Sample Type LCS
2E-07
Units: µCi/Sample
RunNo: 149962 PrepDate: 08/25/17 16:30 BatchlD 13649
Result RL Spike Rer Samp %REC % Rec Limits Qual
6E-06
Sample Type MS
2E-07 6E-06
Units: µCi/Sample
96.3 67.1-122
RunNo: 149962
Result
PrepDate: 08/25/17 16:30 BatchlD 13649
6E-06
Sample Type MSD
RL
2E-07
Spike
6E-06
Units:
Rer Samp %REC % Rec Limits
ND 96.7 65 -131
µCi/Sample
RunNo: 149962
Result
PrepDate: 08/25/17 16:30 BatchlD 13649
RL Cone %RPO %REC
7E-06
Sample Type MBLK
2E-07 6E -06 8.94 106
RunNo: 149821
Resull
Sample Type LCS
NO
ND
ND
RunNo: 149821
Result
2E-05
1E-05
2E-05
Sample Type LCSD
RunNo: 149821
Result
lE-05
RL
2E-07
2E-07
2E-07
RL
2E-07
2E-07
2E-07
RL
2E-07
E Value above quantitalion range
Units: µCi/Sample
Spike Ref Samp %REC
Units: µCi/Sample
Spike Rel Samp %REC
2E-05 105
1E-05 87.8
2E-05 106
Units: µCi/Sample
Cone %RPO %REC
1 E-05 16.3 103
H Holding times for p,eparation or analysis exceeded
L Analyzed by anolher laboratory
0 Outside the Range or Dilulions
s Spike Recovery ou1side accepled recovery /imils
% RPD Limits
20
% Rec Limits
% Rec Limits
68 -146
68-146
68 -146
% RPO Limits
20
Page 2 of 4
Qual
Qual
Qual
Qual
Qual
-'~I: Your Environmental Monitoring Partner
: Inter-Mountain Labs-----------------------------------------'"'"l·Mou,.., ... , .. 1.Aes
CLIENT:
Work Order:
Project:
1673 Terra Avenue, Sheridan. Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1708353
South Yellow Cake Scrubber. Dryer
Date: 9/19/2017
Report ID: Sl 708353001
Uranium Isotopic Filters Sample Type MBLK Units: µCi/Sample
Run No: 149608 PrepDate: 08/25/17 0:00 BatchlD Rl 49608 MB-34 (08/31/17 00:00)
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic filters
LCS-34 (08/31/17 00:00)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic fillers
LCS0-34 (09/19/17 08:46)
Analyte
Qualifiers: B
G
J
ND
R
X
Uranium 234
Uranium 235
Uranium 238
Analyte detected in the associated Method Blank
Analyzed al IML Gillelle laboratory
Analyte detected below quantitation limits
Not Detected at the Reponing Limit
RPO outside accepled recovery limits
Matrix Effec1
ND
ND
ND
4E -07
4E-07
4E-07
Sample Type LCS Units: µCi/Sample
RunNo: 149608
Result
lE-05
4E-07
9E-06
PrepDate: 08/25/17 0:00
Rl Spike Rel Samp
4E-07 8E-06
4E-07 4E-07
4E-07 8E-06
BatchlO R149608
%REC % Rec Limits
131 50-150
111 50 · 150
119 50 · 150
Sample Type LCSD Units: µCi/Sample
E
H
L
0
s
RunNo:.149608
Result
PrepDate: 08/25/17 0:00
lE-05
4E-07
lE-05
RL
4E-07
4E-07
4E-07
Value above quanlitation range
Cone %RPO
1 E-05 11.8
4E-07 3.19
9E-06 22.5
Holding times for preparation or analysis exceeded
Analyzed by another laboratory
Oulside lhe Range of Dilulions
Spike Recovery outside accepted recovery limits
BatchlD Rl 49608
%REC % RPO Limits
147 20
114 20
149 20
Page 3 of 4
Qual
Qual
R
·'~II:: Your Environmental Monitoring Partner
Inter-Mountain Labs-----------------------------------------'"n:"" ...... ouNrArN LAIS
CLIENT:
Work Order:
Project:
1673 Terra Avenue, Sheridan. Wyoming 82801 ph: [phone]
ANAL VTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1708353
South Yellow Cake Scrubber. Dryer
Date: 9/19/2017
Report ID: S1708353001
Total (3050) Metals by EPA 200.8 -Soil
MBLK (08/30/17 10: 19)
Units: µg/Sample
Analyte
Sample Type MBLK
RunNo: 149540
Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium
Uranium
Total (3050) Metals by EPA 200.8 -Soil
LCS (08/30/17 10:16)
Analyte
Thorium
Uranium
Total (3050) Metals by EPA 200.8 -Soil
S1708353-001ASS (08/30/17 10:45)
Analyte
Uranium
S1708353-003AS (08/30/17 11:35)
Analyte
Thorium
Total (3050) Metals by EPA 200.8 -Soil
Qualifiers:
S 1708353-001 AMSD (08/30/17 10:54)
Analyte
Uranium
S 1708353-003AMSD (08/30/17 11 :38)
Analyte
Thorium
B Analyte detected in the associated Method Blank
G Analyzed al IML Gillette laboratory
Analyte detected below quan1it.alion limits
ND Not Detected al the Reporting Limit
R RPO outside accepted recovery limits
X Matrix Effect
ND
ND
Sample Type LCS
RunNo: 149540
Result
98
100
Sample Type MS
RunNo: 149540
Result
127000
RunNo: 149540
Result
1170
Sample Type MSD
RunNo: 149540
Result
125000
RunNo: 149540
Result
1080
45
RL
45
RL
RL
45
RL
RL
45
E Value above quanlitation range
Units: µg/Sample
Spike Ref Samp
1 E02
1E02
Units: µg/Sample
Spike Ref Samp
1E05 ND
Spike Ref Samp
1E03 ND
Units: µg/SampJe
Cone %RPO
ND
Cone %RPO
ND
H Holding limes for preparation or analysis exceeded
L Analyzed by another laboratory
0 Outside the Range of Dilutions
s Spike Recovery outside accepted recovery limits
%REC % Rec Limits Qual
98.2 85 · 115
100 85 · 115
%REC % Rec Limits Qual
114 70 · 130
%REC % Rec Limits Qual
106 70 -130
%REC % RPO Limits Qual
112
%REC % RPO Limits Qual
98.3
Page 4 or 4
APPENDIX D
South Yellow Cake Scrubber
Figure I. Facility Schematic Representation
Yell ow Cake Dryer Baghouse
Figure 2. Facility Schematic Representation
Process Data
South Yellow Cake (Scrubber Flow Rates)
Yellow Cake Dryer Baghouse (L'.\p readings on Field Sheet)
D
Facility Energy Fuels
t
a
!
y
Stack Identification: South yell ow Cake Scrubber
1~0~1
p
a: Distance upstream from next disturbance, feet 7' -
10' P: Distance downstream from last disturbance, feet _ -
65' -y: Distance of Sample Level lo Ground, feet -----
0: Stack Inside Diameter, inches 12.75' ------
Estimated Moisture, percent 4-8% -
I 00-120 -Estimated Temperature, °F -----
2.000 Estimated Velocity, fpm _, _
Control Unit
Type:
Scrubber
J\iumber of Ports
-
2
Figure I. Faciliry Schematic Represenra1ion
Process
Type:
Yellow Cake Processing
,,dlhy Energy Fuels
t
a
i
y
Stack Identification: yellow Cake Dryer Baghouse
l+-0-.1
p
a: Distance upstream from next disturbance, feet 4.8' ----------
p: Distance downstream from last disturbance, feet 37.8'
y: Distance of Sample Level to Ground, feet 65.0'
0 : Stack Inside Diameter, inches 16.00"
Estimated Moisture, percent 1-2
Estimated Temperature, °F ---------125
1400 Estimated Velocity, fpm ---------
Control Unit
Type:
Baghouse
Number of Ports 2
Figure I. Facility Schematic Representation
Process
Type:
Yellow Cake Processing
Facility Energy Fuels
Location South Yellow cake
Date lf& 7.--
South South
Demister Humidy Scrubber Scrubber
Run# Time Spray Spray Venturi Inlet Pressure
I . l) & . () L.\. 1-l/~ "( I ~ __., , . 11.J.. G
( 8<30 L-/. l . 1 <~ -; / ., /L./,0
' °l:oo L--\ Ii., 7,v, 31 -, I L.( . (.. .,
1 I '
C1 ~ .) 0 y . L, ·rJ .< 3 I ._( I ',I · .b>
I
10:00 q -z. ~1 .\ ) ( ·;, t, I 'i I G,
}0·30 ~-z '":°+-t 5\ ?, I U. &
\ \ . 0 D '-f' -z -rs ~I '8' I J. c,,
\ ( ·;o \ . J,7, . / ·1. & ~\) L -1,
I Ctr7 D cf, 1.. 1 . j , 3 z z.. t L.{. f
12:31) ·t"f11 l "}<). 7:, z. I 11..1,,r-
[3'. i) D <...( -'1
L, if'-+ ' '3 z. . r f,f f
I ,, 2 l) ,j 'Z_ -1.1 ?, z · I I~,(,,, l · 7 I . ~ I
I~.' o o "-I L 1--0 ~z .1 ( '{. h
I , 5 I} t.f. 'L 1 3 t · I ,--(.:; h :>-•
15 . 0 c) '-f. "?:--1 ·.S s z. -z. I '--I -/
I t s·Jo tf.. L 1-6 3Z· 0 Ii, Y
I & !) D Lj. 't 1 · ft) ?Z . I { <-{ • ., --I
1~·7D ~.v 1.G ,z. I I~ ·'f'
I
Facility Energy Fuels
Location South Yellow cake
Date ¢;/, t, / 1 a .
Demister
Run# Time Spray
1..--{~oo t..{, i..
¥:~D L/ ·Z-
i: 0 l) t.\. (..
q: 3t) <-i • (/
to: 00 L( ·1-
I0~3D L(.,
\ I : Ob Y·Z
I(: JO c..-t • r
l'[:()O Lf.z._
/Z, : 3 D L{. z
1.r ()0 '<· <...
()~ JD 4. -,e_
1l(; /)D L(. z:
1 '1; 3 0 y. ~
t5.' 0 b '--\ , I
( ~ .. 31> L/-t
1&:00 t./, z__
\ V l /; : ;(.)
South South
Humidy Scrubber Scrubber
Spray Venturi Inlet Pressure
'1" -l, ~(. °1 (L{. C,
,f_·& '?) ·4 lt./ ·1
f."',J. 3z -I 1'-{,'1
1·b 3Z · I /Y''7
1.r 3-Z .2-I~. '1
l-.5"' 3/. cf l~·O
r .l, J(•) t'-f.v
1·1 5(. ~ / 'i ·1
1-& '3 \·j I ~~6
-=J..Jo 3r.& l ~'·o
?-~ 3(-1 l c.(.~
-;;. I., 3/ }y ( t/,4
':J.. (., 32.0 I
( ~-6
-;. 1' 32·0 /Cl,;
7.~ '3/., I c1.1 ":J,h 3l, '1-15,0
1·~ ~,. ~ Jf,()
APPENDIX E
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
Ternpera!ure Ser.s:i,
t ·----l
lnwge: l ran ~!!anal, M!t s, Fi Rt f1n. E :;u.\15'En( C:nje~
.... c:00:-,R oro~e
I
Temperature j
Temperature Sensor
Gooseneck Sensortl J. Temperature Nozzle I . ---Ser.sor
Type S Pilot
Tube
n) \ / F'ttt:e l 11 (("\,) .~ --, :1 ,K .
\
""' ! ~r:=~~ 1
-----~pi~g~r; -·---
u ~ -·-:...=.:L t 11 'O' ~ • !1 I
-0
?\. I Glass Filter /\1(*~" I ~t(>~o ~~~ .. j7i"r,--;i vdivc )
. I Holder ; 11 .: 'I '' w'cet .J ,11 · ·,, 1 1 · • a e11 · ,·
TypeSPitot ~1 ! l1il 1
1
1 Bau,(1 :j i1 ; I Tube t Heated Area · ltil 1i~I ,1;1 ::
1
; i ! Stack '---_-:--_ ~ 1
.:.... 11:,
Wall Manometer Temperat~T ---r ·T I I ~Valcuum
S
w t I ine
J ensors .. _ . a er Empty Silica
. ~ Gel ~ (?rtfi:!! g O . (I) Vacuum
L;-I,-=--:: hi)l(p; ~.: Gauge
"-
I ·=w / 1 --_j! I I ,' -,--1 _, ., ~-Cl·-_.)
,,__A --· 1 By-pass Main t ;.,f ) ·· · l i Vatve n Val;e
·..._ f Dry Gas \ ; r;· I j _,, • I I ,:;;----..:. i I \ Meler ! , 7 ~-.:_
[ I \ I ........_ ·~ ___ _/ i (_~ A;r-Tighi
_j~ ~.J/ Pump c.:......./-::.-· L' _ _.
I igurL· ~l·h-:111.11,l 11i '\k1l10d ~·11~ \:l111plinµ T1:1i11
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 or 5 cubic feet.
4) Record data and information in the GREEN cells. YELLOW cells are calculated.
INITIAL
DATE:1 12'0,2016 I METER SERIAL i, 27863 BAROMETRIC PRESSURE (In Hg):G;l
METER PART t: eo.osole-' CRITICAL ORIFICE SET SERIAL J: 1'53$ EQUIPMENT ID t:
K" TESTED TEMPERA TURES ·F
FACTOR VACUUM DG M READINGS FT' AMBIENT DGMINLET DGM OUTLET DGM
ORIFICE I I RUN t I IAVGl (In lig) INITIAL FINAL NET (V,,J INITIAi. flNAL INfflAL AHAL AVG
IS
FINAL
G;J
ru,sm
ME:MIN)
%MM@i&J&NM
AVG (P.,,)
2s.,o
(1)
vm1s101
i1il
2016 Pre-Calibration
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V0 ISTD)
(3)
y
l
y
VARIATIONrt,J
G
G
G
U137
o.em
O.hff
11 M0.120
11 Mt.no
13 ·--Ml.170
AUOf
"2-UO
USO
e.4.111
5.12$
71 7!
71 76
71 71
75 T6 84 .. 75 83
fl 75 ll
77
71.25
79.00
§§.90
2.90
2.90
Lill!
~
~
!.2Z!i
5.3831
4.93'5
Q.lli
~
~
!!.!!!
o.5317 1' ·~ o.8317 12 Ql.873
0.1317 13_
O.U07 1J 8U50
0.3307 13 687.5'6
o..ntf n au.no
USING THE CRITICAL ORIFICES AS CALIBRATION ST ANOARDS:
62UI!
U-2..770
807SI
113.UO
11..US
5.173
u,1
USO
1.396
5.624
6.079
60
so
eo
59
51
u
78 n
711 77
" 79
63 1511,
71 T6
73 77
75
1,
77
71
73
73
T1
79
79
75
77
77
76.25
78.25
77.25
61.75
74.00
75.00
~ .
~
)9.50
13.00
14.00
1.10
1.10
1.10
~ 45
45
4.9256
~
Mill
Llll1
~
5.1007
AVG=
~
Mill
~
AVG=
L1fil
4.71147
5.1635
AVG=
1.022
!.W
1,ill
.1.W
1,009
1,.W
Lill
1.012
The following equations ll"e used to calculate the standll"dvoll.mes of air passed llv-ou9h the DGM v. (std). and the c-oical orifioa.
V0 (std). and the OGM calibration factor, Y. These equations .. e automaticaly cak:ulated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = ~
(1)
(2)
Vm.,,,,, = K, •Vm• /'liur+(lV/113.(i)
Jill
.. Phur • 0
~·er; ... , 1 = A • JTumh
= Net volume of gas sample passed through DGM. corrected to standard conditions
K,:: 17.64 °Rlin. Hg (English), 0.3858 °Kimm Hg (Melric)
Tm:: Absolute DGM avg_ temperature ("R -English. °K -Metric)
= Volume of gas sample passed through the critical orifice. corrected to standard condilions
T .lfflll = Absolute ambient 1empera1ure (°R -English. °K -Metric)
K' = Average K' ractor trom Critical Orifice Calibration
(3) Vu;,,,,, )" = -~
Vm1m,, = DGM cal1bra11on factor
Technician: J. Graton
Ice Balh
Am1>1&n1 A11
Boding Wa1er
AVERAGE 4H~ =~
2 4H,. = ( 0.75 9 ) 4H (Vm(sld)\
V"(std) Vm /
Temperature Sensors
Rererence In Out
OF OF QF
33 33 33
62 62 62
202 203 203
:Ml
w
Q..11
1.Z!!i
1'ill
la!!!
.!.il!
l.!!!
1£§
1.82
~
llil
Pre Test Cal 2017
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES !:S •WMfili/MiMWO 1iji ~
1) Select three critical orifices 10 calibrate the dry gas meter v.hich bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure. ENVIRONMENTAL SUPPLY COMPANY
3) Run at tested vacuum (from Orifice Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information in the GREE'I cells, YELLOW cells are calculated.
DATE:, t/4/20'7 I
METER PART#: ConaoM 9
METER SERIAL#:, ,1297..S2" I
CRITICAL ORIFICE SET SERIAL#: 1"35
K' TESTED
FACTOR I VACUUM I ORIFICE# I RUN# I (AVG) (In Hi)
DGM READINGS (FT~
INITIAL NET (V.J FINAL
G
G
G
2
3
2
3
2
3
U1S1
Q.&131
D.81S7
o.1317'
0.131.7.
• D.531.7
ll.3307
U307
o..uor
1.2 280.IOO
~ 281..403 '
12 212..314
u 324.702
12 32U11
12 334.143
1S 307.0IO
u 312.077
~ 311.117
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
281.4113
:atU:14
218;22&
S29.118 -
S34.M3
340.711
312.077
311.117
323.1134
6.903
5.911
6.911
5.116
5.125
5,808
5.027
6.610
6.047
INITIAL
BAROMETRIC PRESSURE In H : 25.20
EQUIPMENT ID #: Console 9
TEMPERATURES 'F
AMBIENT I DGM INLET I DGM OUTLET I DGM
INITIAL FINAL INITIAL FINAL AVG
&a 80 80
68 80 80
68 H 80
68 76 76
68 75 75
68 76 75
88 70 70
68 70 70
6S ·. 70 70
72
72
72
70
70
70
66
66
67
72
72
72
70
70
71
66
67
69
78.00
76.00
77.26
72.60
72.50
72.76
68.00
68.25
69.00
FINAL
25.20
ELAPSED
TIME(MIN)
0
AVG (P • .,)
25.20
§§00
3.00 ·
3.00
§§.20
1.20
1.20
12,00
15;50
12.00 ~ 44
44
2017 Pre-Calibration Console 9
(1)
Vm (STD)
!.MY
~
~
4.2Ba3
4,2968
~
~
!dfil
~
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V"(STD)
4,9096
4.9096
4,9095
AVG=
~
4.3746
4.9579
AVG=
4.3634
6.6231
~
AVG=
(3)
y
9..!!!
2.!U
.e.m
J!,ffi
1.020
1,ill
J.!!1!
1.019
i,m
.till
.1.m
l
y
VARIATION(%)
:1.n
~
.1.m lli
!,ill
.1oZZ1
.Lill
1.663
.1,fil
1.§li
i,m
1.586
lam
The following equations are used to calculate the standard volumes or air passed through lhe DGM, V m (std). and the critical orifice,
V0 (std). and lhe DGM calibration factor, Y. These equations are automatically calculated in lhe spreadsheet above, AVERAGE DRY GAS METER CALIBRATION FACTOR. y = I 1.013
(1)
(2)
(3)
Vm,_,,., = K, •I'm• Pl>t1r + luff 113.6) rm
!'h<J/ • 0 Va,,.,, = I('• JTamh
= Net volume of gas sample passed through DGM. corrected to standard conditions
K, = 17.~ 'Rftn. Hg (English). 0.3858 "Kimm Hg (Metnc)
T., = Absolute DGM avg. temperature ('R -English, "K. Metric)
= Volume of gas sample passed through lhe critical orifi~. corrected to standard conditions
T...., = Absolute arroient temperature ('R -English. 'K. Metnc)
K' = Average K' factor from C,iticat Orifice Calibration Vc1;~1n, Y= .~
t·n1,,,,n
= DGM calibration factor
AVERAGE 6He =I ~73
6H,t =
(
0.75 8 )2
6H (Vm(Sld)\
v.,(std) vm /
Temperature Senso~
Reference In Out
OF OF OF
32
72
201
33
73
202
33
73
203
Console 9 PRE Calibralion 2017
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range
2) Record barometric pressure before and after calibration procedure.
3) Run at tested vacuum (from Orifice Calibration Report). for a period of time
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and information in the GREEN cells. YELLOW cells are calculated
DATE:
INITIAL
METER SERIAL I: I 27863 I
CRITICAL ORIFICE SET SERIAL t; 1453~ EQUIPMENT ID t; I Console#4
K' TESTED
~~~~~~~-IFACTORIVACUUM OGM READINGS (FT')
ORIFICE t I RUN I I (AVG) (in Hgl INITIAL FINAL NET(Vm) o:rn 1 1 i
.0
.0
.0
G, 0.5317 12
05317 12
0.5317 12
532.90
538.320
543.770
538.320
543.770
549.249
5420
5.450
5.479
AMBIENT
I
77
TT
TT
TEMPERA TURES "F
DGMINLET DGMOUTLET
INITIAL FINAL INITIAL FINAL
I I I I
70 TO TO 72
TO 73 72 TS
73 75 TS TT
I
DGM
AVG
0
0
0.00
TO.SO
72.50
TS.OD
I
g
FINAL
I 25.50 I
ELAPSED
TIME(l,!INI
8
§
8.00
8.00
8,00
---. t;.i&i.ID~-lt1uh() -Stn,u -Rdrab1l•tr ~
-,,~,
AVG (P,,.,)
25.50
§
1.10
1.10
1.10
(1)
Vm (STD)
~
4.6211
~
energy fuels
IF Y VARIATION EXCEEDS 2.00'/,,
ORIFICE SHOULD BE RECALIBRATED
(2)
VQ (STD)
AVG=
~
4.6820
4.6820
AVG=
1
(3) y
y VARIATIONc,1)
~
.1.Qll
~
0.00 o:rn §§ .o
.0
.0 I I I I I I
0.00
0.00
0.00
§§ ll1.!
AVG=
USING llt!: CRITICAL OR/ACES AS CALIBRATION STANDARDS:
The following equa1ions are used to calculate the saandard volumes of ar passed lllfough the DGM. Vm (std). and the critical orifice.
V" (std). and the DGM calibration factor, Y These equations a-e automaticany calculated in tile spreadsheet above. AVERAGE ORY GAS METER CALIBRATION FACTOR, Y = ~
(1) 1·11,,, =K,•V111•P~':_~t.l./l 1361 7m ------= Net volume of gas sample passed through DGM. corrected to standard conditions
K, = 17 64 "R/in Hg (English) 0 3858 "Kimm Hg (Metric)
(2) r·c.' .l
(3) r .
Technician. J. Graton
;.:·• PiJ(1;· • (-)
.,Jf;,mb
1·,,.
I ·,n
Tm = Absolute DGM avg tempera1u<e tR -English. '1< -Metric)
= Volume of gas sample passed through the critical orifice. corrected to standard conditions
T ,mo= Absolule ambienl temperature t'R -English "K -Metric)
K' = Average K' factor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE .\H@! =1 1.531 I
.IHCII=
(
0.75 0 )2 AH (V,..(std))
VQ(sld) vm
LIB
1.532
1.525
Is .....
i&fdMIPIIIIAJM&Wi,4!'~ ~
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1} Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range
2) Record barometric pressure before and after calibration procedure ENVIRONMENTAL SUPPLY COMPANY
3) Run at tested vacuum (from Orifice Calibration Report}. for a period of time
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and information in the GREEN cells. YELLOW cells are calculated
METER SERIAL #: I 1297-3245
----CRITICAL ORIFICE SET SERIAL#:! 1453S !
K' TESTED
~~~~~~~ FACTORJVACUUM DGM READINGS JFr)
ORIFICE# RUN# (AVG) (In Hg) INITIAL FINAL
0.5317 12
0.5317 12
0.5317 12
551.504 556.925
556.925 562.236
562.236 567.668 G: o:rna o:rna
USING THE CRITICAL ORIFICES AS CALIBRATION STANDAROS:
NET (Vm)
5.421
5.311
• 5.432
.o
.0
.0
.o
.o
.0
INITIAL
BAROMETRIC PRESSURE (In Hg):j 25.50
I
EQUIPMENT ID #: Console 9
TEMPERATURES •F
AMBIENT! DGM INLET I DGM OUTLET
JNITIAL FINAL I INITIAL FINAL
78 74 76 72 72
78 76 78 72 74
78 78 80 74 74
I I I I I I
I I I I I I
DGM
AVG
73.50
75.00
76.50
0.00
0.00
0.00
0.00
0.00
0.00
FINAL
25.50
ELAPSED
TIME(MIN)
9
AVG(P..,)
25.50
DGM~H
(in H20)
§§.2
1.2
1.2
§§
§§
(1)
Vm(STD)
4.5892
~
~
Energy Fuels
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
(2) (3) y
V" (STD) y VARIATION (%)
4.6777 1.019
4.590 1.024
4.6777 !,ill
AVG= 1,Qll 0.00
AVG=
AVG=
The following equatioos are used lo calcula!e lhe standard volumes ol air passed through the OGM, Vm (std}. and the critical orifice,
V0 (std), and the OGM calib<alion factor, Y. These equations are automaticaly calculaled in the Sl)(eadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, v = I 1.022
(1)
(2)
I ·111,.,.1, = A." 1 • / •111 •/'bur+ (AH / IJ.6)
Tm
l "c.:r, ""'. =-;.: •• l'har • e -J'/ ·, l~I~,;-
= Net volume of gas sample passed through DGM. corrected to standard conditions
K, = 17.64 "Rtin. Hg (English). O 3B5B 'Kimm Hg (Metric)
Tm = Absolute DGM avg temperature ('R • English, 'K • Metric)
= Volume of gas sample passed through the critical orifice. corrected to standard conditions
T,.,. = Absolule ambient temperature {'R · English 'K · Metric)
K' = Average K' factor from Critical Orifice Calibration
(3) 1 ·t.:r, ... J,
-1·m •. ,.,,
= DGM calibration factor
Tech(lldan:Mike McNamara
AVERAGE dH@ =I ~1.667 !
dH-.=
(
0.75 8 )
2 dH (Vm(std)\
V0,(std) Vm /
Temperature Sensors
Reference In Out
OF
32
72
201
OF
33
73
202
OF
33
73
203
1.671
1,.lli
1.662
Console 9 POST Calibration 2017
Type S Pi101 Tube lnspeclion Da1a
Dale: ---'-'12=--/=--9,--'' l-'-6 __ P1101 Tube lden1ifica1ion: _____ .:..l8:....::G'---------
Technician· K McNamara
: p•
Pe D,= ______ o_.3_7_5 __ in Is P., = P,. • ____ Y_e_s __ _
Is t 05 • D, $ P, & Pn $ t 50 • D, ~ ____ Y_e_s __ _
PA~ 0,452 in
P11 = 0.452 in
a,< 101, a:1
a:< 10" a, F ___ 2 __ _
P," ___ o __ _
~!-: 5'' p,= ____ _
Z $ 0 125 in. Z = __ o:.:·.:..0=--16=---_in.
~-~w ....... ==-=--, --·-W $ 0,03125 in, w = __ o_.c __ oo_,_-__ in
W > 3 inches
fT:11 Z > 3/4 inch
Y::. 3 111ches
W = __ ..;;6:..;. 7..:;5 __ in
Z = 1.75 in ------
Y = --"-3----'l--'12'-----_in
The p11011ube ,neels lhe spec1fica1ions for a cahbra1 on fac1or ofO 84' Yes
Tempera lure Sensor Calibra1 ion
Rererence Omega CL35 I 2A
Continuity Check Yes Probe Heal Check 248 Yes
1 empera1ure 1 empernJurc ·1 emperature
Source Relerence Sensor Di!ference
(Medium) (F) l"Fl !°Fl
Probe AIR 65 66 I
AIR 65 64 1
ICE WATER 33 34 1 Slack
OOU. WATER 204 204 0
SILICONE OIL
TETCO
Sample Box Temperature Sensor Calibration
Dale: 12/12/16 Cal ibralor: Kawai McNamara Reference: Omega CL35 I 2A
Thermocouple Temperature Temperature Temperature
llnit ID Location Source Reference Sensor Difference
(Medium) (''F) (''F) ("F)
Oven (3) Water 34 33 -I
A Water 204 204 0
Water 34 34 ~ Oven (4) Water 204 204
Oven (3) Water 34 34
B Water 204 204
Water 34 34 ~ Oven (4) Water 204 204
Oven (3) Water 34 34
C Water 204 204
Water 34 33 ~ Oven (4) Water 204 203
Oven (3) Water 34 33
D Water 204 204
Water 34 33 ~ Oven (4) Water 204 203
Oven (3) Water 34 33
E Water 204 203
Water 34 33 ~ Oven (4) Water 204 203
Oven (3) Water 34 33
F Water 204 203
Water 34 33 -1 Oven (4) Water 204 203 -I
G Oven Water 34 34 0
Water 204 204 0
H Oven Water 34 34 0
Water 204 204 0
lmpinger Out A Water 34 35 I
Water 204 204 0
lmpinger Out B Water 34 35 I
Water 204 201 -3
lmpinger Out C Water 34 35 I ,_
Water 204 202 -2
lmpinger Out D Water 34 35 I
Water 204 202 -2
1: lmpinger Out E Water 34 35 I
Water 204 201 -3
lmpinger Out F Water 34 35 I
Water 204 202 ·2
lmpinger Out G Water 34 34 0
11 Water 204 202 -2
lmpinger Out H Water 34 34 0
Water 204 203 -I
lmpinger Out I Water 34 35 I
Water 204 202 -2
lmpinger Out J Water 34 35 I
Water 204 202 -2
lmpinger Out K Water 34 33 -1
Water 204 202 -2
APPENDIXF
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
February 14, 2018
FOURTH QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
SOUTH YELLOW CAKE SCRUBBER
YELLOW CAKE DRYER BAGHOUSE
BLANDING, UT AH
November 13-15, 2017
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.
Al ~ Mike McNamara
Reviewer:_ ..... ~._ ___ Aj..; ___ ,_•1....,_-_-_:-_:-_:-_-__ _
Date: __ --z..--L-/ _I~\'--'-) _I~......;:;___ __ _
Doug Olsen
Date: ----------------
ii
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ......................................................................................................................... I
Test Location and Type of Process ...................................................................................... 1
Test Dates ............................................................................................................................. I
Pollutants Tested and Methods Applied .............................................................................. 1
Test Participants ................................................................................................................... 2
Deviations from EPA Methods ........................................................................................... .2
Quality Assurance ................................................................................................................ 2
Summary of Results
Emission Results .................................................................................................................. 3
Process Data ......................................................................................................................... 3
Description of Collected Samples ........................................................................................ 3
Discussion of Errors or Irregularities ................................................................................... 3
Percent Isokinetic Sampling ................................................................................................ 4
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
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
111
LIST OF TABLES
PAGE
Table
I Measured Radionuclide Emissions ...................................................................................... 3
II Percent Isokinetic Sampling ............................................................................................... .4
III Sampling Point Location ...................................................................................................... 6
IV Complete Results, South Yellow Cake Scrubber Exhaust.. ............................... Appendix A
V Complete Results, Yellow Cake Dryer Baghouse ............................................. Appendix A
UST OF FIGURES
Figure
I Facility Schematic Representation South Yellow Cake Scrubber ..................... Appendix D
2 Facility Schematic Representation Yellow Cake Dryer Baghouse .................... Appendix D
3 Schematic of Method 5/114 Sampling Train ..................................................... Appendix E
iv
INTRODUCTION
Test Purpose
This test project was conducted to determine the total radionuclide emissions from the South
Yellow Cake Scrubber and the Yellow Cake Dryer Baghouse exhausts in terms of Curies per dry
standard cubic foot (Ci/dscf).
Test Location and Type of Process
Energy Fuels Resources is located about 5 miles south of Blanding, Utah. Uranium ore is
processed into yellow cake, which is shipped to other facilities for additional processing. There
are two yellow cake dryers with individual scrubbers. Both dryer enclosures discharge into the
Yellow Cake Dryer Baghouse. The packaging enclosure also discharges into the Yellow Cake
Dryer Baghouse. The South Yellow Cake (SYC) dryer was the only operating dryer at the time
of the test. The North Yellow Cake dryer is currently not operational.
Stack schematics are shown as Figures l and 2 in Appendix D.
Test Dates
The first test run on the S YC Scrubber was completed November 13-14, 2017 and the second run
on November 14-15, 2017.
One run was completed on the Yellow Cake Dryer Baghouse November 14, 2017.
Pollutants Tested and Methods Applied
The tests were a determination of radionuclide emissions in accordance with EPA Method 5/114.
The tests for the SYC and the Yellowcake Dryer Baghouse were for the following radionuclides:
Th-228, Th-230, Th-232, U-234, U-235, U-238, Pb-210, Ra-226 and Ra-228.
Test run filters and front wash residues were sent to Inter-Mountains Labs located in Sheridan,
Wyoming for radionuclide analysis.
Test Participants
Test Facility
State Agency
TETCO
Deviations from EPA Methods
None.
Quality Assurance
Logan Shumway
None
Jeff Graton
Mike McNamara
Kawai McNamara
Testing procedures and sample recovery techniques were according to those outlined in the
Federal Register and the Quality Assurance Handbook for Air Pollution Measurement Systems.
2
SUMMARY OF RESULTS
Emission Results
Table I presents the findings of the test in Curies per dry standard cubic foot. Tables IV and V in
Appendix A have more detailed information.
Table I. Measured Radionuclide Emissions
South Yellow Cake Scrubber Yellow Cake Dryer
Baghouse
Run#
pCi/dscf pCi/hr pCi/dscf pCi/hr
22.813 6.504E+05 21.065 2.848E+06
2 28.720 9.641E+05
AVE 25.767 8.072E+OS
Test Run I on the Yellow Cake Dryer Baghouse was completed with 8 barrels
being filled.
Process Data
The process was operated according to standard procedures. All pertinent process data was
available for recording by agency personnel. Scrubber water flow and pressure drop readings
(.1.p) were recorded and are found in Appendix D. The Dryer Baghouse pressure drop readings
(.1.p) were recorded and are found on the test run sheets. Production data will be submitted by
Energy Fuels Resources.
Description of Collected Samples
The test filters for the South Yellow Cake Scrubber were covered with a brownish red particulate.
The front washes were clear in appearance.
There was a slight grey bullseye in particulate matter on the test filter for the Yell ow Cake Dryer
Baghouse. The front wash was clear in appearance.
Discussion of Errors or Irregularities
None
3
Percent Isokinetic Sampling
Each test run was isokinetic within the± I 0% of 100% criterion specified in the Federal Register.
lsokinetic values for each test run are presented in Table II.
Table II. Percent Isokinetic Sampling
South Yellow Cake Yellow Cake Dryer
Run# Scrubber Bag house
---~ _ _.,___ __ 1_907_1 ___ __
4
SOURCE OPERATION
Process Control Devices Operation
All process control devices were operated normally. Recorded scrubber water flow, pressure, and
baghouse L\p readings are found on the test run sheets or in Appendix D.
Process Representativeness
The facility was operated normally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND AN AL YTlCAL PROCEDURES
Sampling Port Location
The inside diameter of the South Yellow Cake Scrubber stack was 12.75 inches. The two, four-
inch diameter sample port were located 28.24 diameters (30 feet) downstream from the last
disturbance and 6.59 diameters (7 feet) upstream from the next disturbance. Figure I in Appendix
D is a schematic of the stack.
The inside diameter of the Yellow Cake Dryer Baghouse stack was 16.0 inches. The two, four-
inch diameter sample ports were located 28.38 diameters (454 inches) downstream from the last
disturbance and 3.56 diameters (57 inches) upstream from the next disturbance. The sample port
locations are depicted in Figure 2 in Appendix D.
Sampling Point Location
Table Ill shows the distance of each sampling point from the inside wall according to EPA
Method 1. Each point was marked with a wrapping of glass tape and numbered. These points
were determined by measuring the distance from the inside wall.
Distance (inches) from Inside Wall
Sample Point SYC Scrubber Dryer Baghouse
1
2
3
4
5
6
Sampling Train Description
0.85
3.19
9.56
11.90
0.70
2.34
4.74
11.26
13.66
15.30
To determine the actual emission rates for this stack, 40 CFR 60, Appendix A, Methods 1-5/114
were followed.
All sampling trains were made of inert materials (Teflon, stainless steel and glass) to prevent
interference of the sampled gas and particulate. The stack analyzers used to conduct Methods 1-
5/114 are constructed to meet the specifications outlined in the CFR. The temperature sensors
6
were K-type thermocouples. Heater, vacuum, and pitot line connections were designed to be
interchangeable with all units used by the tester. A 3 I 6 stainless steel probe liner was used for the
tests. Figure 4 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/or Air Pollution Measurement Systems.
7
APPENDICES
A: Complete Results and Sample Calculations
8: Raw Field Data
C: Laboratory Data and Chain of Custody
D: Raw Production Data
E: Calibration Procedures and Results
F: Related Correspondence
8
APPENDIX A
Table IV Complete Results, South Yellow Cake Scrubber Exhaust
Table V Complete Results, Yellow Cake Dryer Baghouse
Nomenclature
Sample Equations
A
I AfH.I~ IV SVC Scrubber
COMPLETE RES UL TS
LNl:RGY FULLS CORPORA !"ION. [3L/\NDIN(i. U'l All
SOLi l'fl YELL O\VC/d..::E SCRUBl31:I{ l:XI fAL'S J"
Symbol Descrietion Dimensions Run #I Run #2
Date 11 · I J-14 17 11 ·1.cl-15-17
Filter# 6933 (J9],I
Begin Time Tes1 Began 14: 15 l 2:45
End T ,me Test Ended 12:37 12:05
Pb111 Meter Baromelric Pressure In. Hg. Abs ::'..cl.55 24 .55
~H Orifice Pressure Drop ln.H,O 0.312 0.871
y Meler Calibration Y Faclor dimensionless 0.9% 0.996
Vm Volume Gas Sampled--Me1er Condi lions cf 171 .906 279.970
T'" Avg Meler Temperature "F 84.5 88.1
-,/~p Sq Root Velocily Head Root In HP 0.1881 0.2188
Wt_..c Weighl Waler Collec1ed Grams I 30.2 140.2
Tt D11ra1ion of Tesl Minutes 480 480
cp Pitot Tube Coefficient Di1nensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.3110 0.3750
CO2 Volume% Carbon Dioxide Percenl 3 00 3.20
02 Volnme % Oxygen Percenl 16.80 16 00
N2 &CO Volume% Nitrogen and Carbon Monoxide Percenl 80. 20 80.80
Vm,1d Volume Gas Sampled (S1andard) dscf 13(,,\() 220.lJ87
Vw Volume Water Vapor scf (1 I ,9 (di JO
Bw, <mcas11red1 fraction H,O i11 Stack Gas (Measured) Frac1ion 0.04.:i 0.0::!(J
Bw, (satura1cd) Frac1ion H20 in Stack Gas (Sa1ura1ed) Fraction 0.073 0.072
Bws Fraction H,O in Stack Gas * Frac1ion 0 .043 0.029
xd Frac1ion of Dry Gas Frachon 0 .957 ()_971
Md Molecular W1. Dry Gas lb/lbmol 29.1 '> 2 9. I '.\
M, Molecular Wt Stack Gas lbllbmol 2/Ui7 2X.8,
%1 Perccnl lsokinetic Percent l ()(I ~ %.8 AVC
Ts A,·g Slack Temperature "F 97 .2 96.8 417.0
A, Stack Cross Sec1io11al Area Sq. fl. 0 .887 0 .887
PG Stack Static Pressure ln.H,O -0.100 -0.100
PbP Sample Pon Barometric Pressure 111 Hg Abs 2.:.1.48 2'1.48
P, Stack Pressure lo. Hg. Abs 2-1.473 '.:'-1.473
Q, Stack Gas Volumetric Flow Rate (Std) dscfin 4 .751-.·02 5 .591--02 5.17F +02
Q. Slack Gas Volumelric Flow Rale (Actual) cfin (1.'llL ·O'.!. 7."111 02 6. lJl E +02
v. Velocity of Stack Gas fpm 7.22L 02 s :rnr,02 7.80E+02
Curies Radiomoclides per sample pCi .3111.04 6347.03
Radionucl ides per blank pCi n.22 o.n
Net Curies Net Radiom,clides per sample pCi 31 I 0 .81 63c.l6.8 I
Crad Concentralion of Radionuclides pCi/dscf n.811 28 .7:20 25. 767
ERrad Emission Rate of Radionuclides pCilhr 6.5!1cl I:.· ()5 •J.64 11 · 05 !to72E+05
* If the measured moisture content is greater lhan the saturated n #
the saturated moisture value will be used in all calculations (40 CFR 60. Method 4.
TABLE V
COMPLETE RESULTS. PM
ENERGY FUELS CORPORATION, BLANDING, UTAH
YELLOW CAKE DRYER BAGHOUSE
Symbol
Date
Filter#
Begin
End
Pbm
~H
y
Vm
Description
Dale
rime Tes! Began
Time Tes! Ended
Meter Baromelric Pressure
Orifice Pressure Drop
Meler Calihra1ion Y Faclor
Volume Gas Satnpled--Meler Condi1ions
Avg Meler Temperah1re
Sq Rool Vclocily Head
Wt_,., Weig.hi Waler Collecled
T1 Oura1ion of Tes!
C P Pi101 Tube Coetlicicnl
D,, Nozzle Oiamcler
CO2 Volume% Carbon Dioxide
02 Volume 0/o O.xygen
N2 & CO Volume% Ni1rogen and CMbon Monoxide
V m,1d Volume Gas Sampled (S!andard)
Vw Volume Waler Vapor
Bw s craclion HiO in Slack Gas
Xd Fracliou of Ory Gas
Md Molecular W1. Ory Gas
M$ Molecular WI, S1ack Gas
0/ol Percenl lsokinclic
Ts A ,·g Siack T emperah1re
A 5 Slack Cross Seel ion al Area
PG S1ack S1a1ic Pressure
Pbp Sample Pon Baromeiric Pressure
P s Slack Pressure
Os Siack Gas Volnme1ric Flow Rn!e (Sid)
Q. Slack Gas Volumelric Flow Rale (Aclual)
V 5 Velociry ofS1ack Gas
Curies Rad,onuclides per sample
Curies Rad,onuclides per blank
Net Curies Nel Radionuclides per sample
Crad Conccnlralion of Radionuclides
ER rad Emission Rale of Radionuclides
Dimensions
In. Hg. Abs
In H,0
dimen!--ionless
cf
"F
Roo1 In H,0
Grams
Minutes
Dimensionless
Inches
Perce111
Percent
Percenl
dscf
scf
Frac1ion
Frac1ion
lb~bmol
lb/lbmol
Percenl
"F
Sq Fl.
ht-H:0
In. Hie( Abs
In. Hg Abs
dscfin
cfm
pCi
pCi
pCi
pC,!dscf
pCi,1ir
Run #I
11/14/2017
6935
9:06
11:07
24.55
1.609
1.0 IO
100.668
78.5
0.5494
12.7
120
0.84
0.2780
0.00
20.90
79.10
82.194
0.599
0.007
0.993
28.84
28.76
100.7
101.2
1.396
-0.32
24.48
24.456
2.25E+03
2.95E+03
2.I IE+03
1731.60
0.22
1731.38
21.065
2.848E+06
Drvu Baghouie 13
Method 5 Nomenclature
lVrl = percenr 1sok111e1ic as a percem
A, -" s1ack cross -sec11onal area (fl3)
AS~P = see J6P
Btu = uni1 hea1 value ( British thermal unit)
B", = frac1ion of wa1er in stack gas
C1 = concen1ra1ion of fron1 half particula1e mailer (gr/dscf, lb/dscf. e1c.)
Cm,·1at = concentra1ion of metals (ppm, pg/ft). etc .). Atomic symbol replaces '"metal"'
CO! = percent carbon dioxide in 1he s1ack gas
C P = P11ot 1ube coefficien1
C., <.I\·~, = average concentration of x
C, 1,0rr, = concentration of x corrected 10 1he required percent Oc
D.-q = equivalen1 diame1er for reciungular stack
t,.H =-orifice pressure drop (inches H~O)
t,.H(~· :-: orifice pressure (inches 11 20)
Dn = nozzle diame1er ( inc he.-.)
DnJc, = calcula1ed desired no:ule size (inches)
6P -,--~rnck flow pressure differenwil (inches HJO)
0, -= diameter of the qack (feel)
EA = percen1 excess air
ER1 = emission ra1e or front half particulate (lb/hr)
ERmmD1u = emission rate per mm81u or 10n of fuel e1c.
ER, = emission ra1e of compound. Specific compound replaces .,
K-fact multipl1er of 1est point t,.p to determine 1est po1111 t,.H
L -length of rec1angular s1ack (inches)
M0 molecular weigh1 of s1ack gas. dry basis (lb/lb-moll
Mfi11er = mass of panicula1e on filler (mg)
Mr = mass of par1icula1e ma11er on filler and in from wash (mg)
mmB1u million 81u
Mp = ma~s of panicula1e ma[ler in fron1 wash including probe (mg)
M_, molecular weigh1 of ~l!lck gas. we1 basis (g/gmol)
N1 = percenl ni1rogen in the stack ga~
Oc = percent oxygen ·,n lhe s1ack gas
J t,.P = average of 1he ~qua re roots of 6.P ( may also be referred ro as AS6.P)
Pbin = ab~olu1e barome1ric pressure at the dry ga~ me1er (inches Hg)
Pbr = absolute barome1r1c pressure a1 the sample loca1ion (rncht:, Hg)
Pc s1ack siatic pressure (inches H10)
P, = absolu1e stack pressure (inches Hg)
P,,0 = absolu1e pressure at si.indard conditions (29 92 inches Hg l
e = time leng1h of 1es1 (minu1es)
Q,, s1ack gas volumetric Row ra1e (acfm)
Q, stack ga~ volumetric Row rate (dscfm)
Q.. wc1 s1ack gas std volumetric Row (ft1/min. W\Cfrn)
Tn, -. merer temperature (°F)
T, = qack 1empera1ure (°F)
T,,0 ab,olu1e 1empera1ure at s1andard condi11on~ (528°R)
T1 see(}
Vrn
Vm,,<1
~ample volume (flJ) a1 me1er condition~
volume \landard (dsct). sample volume adjusted to 68°F and 29 92 inches Hg
Method 5 Nomenclature
V, = veloc11y ol s1ack ga\ (fpm)
V". = volume water vapor (scf) at 68°F and 29.92 inche~ Hg
W width of rectnngular .<.rack (mche~)
W1...,, = weigh1 of the conden<:ed water collected (gram~)
Xd -== fraction of dry gas
Y = me1er calibration Y-foctor (dimension le~~)
-.:1
8"., = Vm,,d + Vw
Mr,,· 0.0 I S43 C,=----Vm,,u
Method 5 Sample Equations
20.9 --desired %0,
C,"'"''-= C,,.,-~,-209 I o/.0-. -ac1ua " ~
2 -L -W Dc4 =---L-'~_W.;..;.... _______ ----
0.0269 · (Pbm + 0.073S) /(T ~) M,
l),, d~, = \ (T,,, + 460) Cp x;;--. V -P, L'iP -
%0, -0 S· %CO EA =-•
0.2M · %N~ -(%0~ -0.S · %CO)
ER, == Cr· Q, 0.00857
ER,
ERmmlllu ~ B /h mm 1u r
8 . 4 ' ' . __ 46.n · Dn -L'iH@ -C;; · X.; M<1 -P, (T.., + 460) K-facr -611 M, (T, + 460) · (Pbm +-,~I>)
M0 = CO~ 0.44 + 0~ · 0.32 +-N~ · 0.28
M, = Mct · Xct + 18 · Bw,
T,,u ( Pbm +--~6)
Vm,,cJ = Vm , Y
(Tm + 460) · P"<1
V, = 85.49 60·Cr· ~p ~60 V P,~M,
Vw = Wtwc -0.04715
Xo : I -8._,
APPENDIX B
South Yellow Cake Scrubber
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
Yellow Cake Dryer Baghouse
Preliminary Velocity Traverse and Sampling Point Location Data
Particulate Field Data
B
Preliminary
Facility Energy Fuels
~ Stack Identification South Yell ow Cake Scrubber
A Date
N
Barometric Pressure
Pbm in Hg Pbp in Hg
B-Static Pressure (P0) in H20
Estimated Moisture (Bw.) l-3 %
Sample Height from Ground 65 feet
Sample Height from Console feet
Comments:
Stack Diameter 12.75" Reference 0.0"
Pons are 7.0' Upstream from nex1 disturbance
Ports are 30.0' Downstream from last disturbance
Pon Diameter Type Particulate
Num. of Pons 2 Num, Poin1s 8
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
I 6.70% 0.85 0.85
2 25.00% 3.19 3.19
3 75.00% 9.56 9.56
4 93.30% l l .90 11.90
Averages:
Ts L. Flow ---------
~p ,.fop ---------
KEY => I.__T_s ___ ~_P __ L._F_lo_w_,t
__ 511 14_ Field Data Sheet
TETCO
Filler b I\ '3:!, Sample Box_A__ Page~l~of~I-Run#_L
Plant: Energy Fuels
Date: l\/f?,/1..C!>[l
Locarion: South Yellow Cake Dryer Scrubber
Operaror: .lE:.fT-P..J:.'i A.. (-,@-$\Ta~
I A
'2.
DGM
(1)·'1
6P ,I 6Ht"'H,0) II Vacuum II Tempcrarures1'Tl I OOMTcmp(T.,) 1 I I I I Effiuent Out In
~I Traverse II Time
Po1hl {inll:l))
i 0 N
/!-1}~:;'c, __ , __ ,
2
l
2
3
1
3
4
i
4
/---NI? P.. 1
__ 1
_1
2
2
2
3
1
3
4
4
4
Total
Average
Comments:
{ 1(. 01ob · ,iAf. S1So ../ ,.'ict ../ 2.332.. /
C\7. 2., --io.1AS\ <>~2...
DGM before leak check Vac ("Hg) Rate( ft3/min) DGM after leak check
(\~C\.C\\O q,'10, \ \ 0
C\'10. \\ a ll\'(0.4l"f
'1058 ./
_81./.S
Srack Diameter 12.75" .. Pon Reference Q'.__
Pons are
Pons are
_7_' __ Upstream from next disturbance
30' Downstream from last disrurbance
Assumed Moisture 3-5 %
Probe 2.1 C, • 2. Cp___.QM
JI:, Nozzle Calibration
.~\\)(Ii ,:l:2:ie ~ ~ ~
Avg D0 .tt$!s inches , l\ \U'o
GasBag ~
Console ~
Y-Factoro.'f1_b _
6H@t,k1°3 in H20
Barometric Pressures
Pb.,2.\1. '5S
Pb. 4'i. 'i B
Pu-=-.J.
in Hg
in Hg
in H20
Lea~ Check: Pre ~ 0 • 00 J
A'lmin O • 00~ die': I 0
Posl
vacinHg 2.6 ~<i, ~ .l~
Pito1 Rate _a__...Q,
In H,O ;t,:'(f"
0,()
~
0.25
Waler Collected L 3o. L.
Time Sampled ~ a.o ~, __ .......,,51.~ ____ mrn
--Rew-Rate 6H@ <le>JJNJ cc/min
K=
K=
@Tm
@Tm
Vac ("Hg) Rate( ft3/min)
\C o.o~\
20 D.00\
i~;o2. ""°"" S~~ C°"""loJ Q qss.ct,S (s.,-.,~ vJA."TC.'\'\ S;"t,) .>G. -°ilA..:,.,. ~•~"'"-"' S"'-~"° of~.
-(, a; 2'4 P..tf\ s-ra.e...,. \Jf> )
f -N..:,
A
1(-IF-(7
__ 51114_ Field Data Sheel
Plant: 0~ Fuels
Date:\ /\, •
Time
, ,
i
2
2
~
3
3
4
4
4
1
-
1
~
2
2
2
3
~
~
i
4 -
4
DGM t.P
TETCO
Filterb,~~ Sample Box__L_
Location: South Yellow Cake Dryer Scrubber
Operator:.lEFflt.E'J' A. Gf.~iON
l. i ~ "l lo
1j AH ~nH,OJ II Va<:t1um II Te"!peratures :"'
Total 2.,q,,,6.... vS .7.SIJ /20.c..o/ 2.32.;, 142..~ \
Average vo:2.tu.. C-Y.,1 \ ~g 88, \
Comments: Additional (Extra) Leak Check Information
.,
Page_l_of_l_ Run#~
r 6 N
Stack Diameter _ 12.75" __ Pon Reference Q'.__
Pons are
Pons are
_7_' __ Upstream from nexl dismrbance
30' Downslream from last disturbance
Assumed Moisture
Probe 2~
Nozzle Calibration
3-5 %
Cp_QM
."31S -~1 S .~15 .?,1S
Avg D0 :; 1 'SO inches
Gas Bag:C • 03
Console~
Y-FactorO.l\5b
AH@~ inH20
Barometric Pressures
Pbm 2i e 5'5
Pb.'.2, ~ ,'\9)
Pi;~
Leak Check: Pre
fl'imin Q ,ru,,
vacin Hg 2.0
PitotRate~
lnH,O O. 2S
in Hg
in Hg
in H20
Posl
~
19
o.o
o.~s
Water Collected l L/.0 • z..._. g
Time Sampled •-I i?J O min
~ 6H@
?,--'--.J ,e.u.) ccJmin
K=
K=
@T.,
@Tl"
DGM before leak check-JVac ("Hg) !Rate( ft3/min) DGM after leak check Yac("Hg) Rate( ft3/mln)
l_io4 "lOO o.oo
-lro 190 ,5z_o
Preliminary
Facility Energy Fuels
~ Stack Identification Yellow Cake Dryer Baghouse
~ Date
Barometric Pressure
Pbm in Hg Pbp in Hg
-B Static Pressure (PG) in H20
Estimated Moisture (Bw,) 1-2 %
Sample Height from Ground 65 feet
Sample Height from Console feet
Comments:
Slack Diameter 16.0" Reference 0.0"
Pons are 4.75' Upslream from nexl dislurbance
Pons are 37.83' Downstream from las1 disturbance
Pon Diameter Type Particulate
Num, of Pons 2 Num. Points 12
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
I 4.40% 0.70 0.70
2 14.60% 2.34 2.34
3 29.60% 4.74 4.74
4 70.40% 11.26 11.26
5 85.40% 13.66 13.66
6 95.60% 15.30 15.30
Averages:
Ts L.Flow ----------
6P V6P -----
KEY=>
11-4{ S Field Data Sheet
,TETCO
Filter l.83') Sample Box~_
Plant: Energy Fuels
Date: ~\('1-i,{ l':1.-
Trave.rse Time
Point Clock Min (9)
1 1 q":ol 0
2 10
3 '20
4 30
5 'iO
6 so
1 lo· a+-c.o
2 ,o
3 so
4 "iO
5 loO
6 110
I\ ·.01'--12.0
DOM
((l)
-z.~'+; 100
2"1(.-:Jt'O
Z 5 t\· ll.C
"'t w 2... "1SS
l.?l:'.>{O
i.\o, oou u,q. e{o
Z.°r~-Ol 0
Jo{.1.1.:)
3\7 ,({
"\ l,O . S' '-1)
a,i•3z_'t.1SO
T3'+-,,<,,,e
t.P uH <"'"'°' Vacuum
lmll;I)) Desired Actual {iullr.)
•')3 I. 1 lo ,. 7~ L-
I )1_ 1,10 t,1~ 2-
·~l ,. C. .( ,.i. < 2..
·1l I, 'a S"° l,b) 1-
l) l \,(#)/ L. <o { L
13( (. 8Co l. 8 (. t.
1t1-t, "l4 l, <,f l.l 1..-
, 1.":J. I• '4Y. l • 1.t'-' '2,,
''Z. C,p 1,)S 1,)8 i.
't.<i-(. 3'8 l. )'2: 2..
,"3'L, 1,,0 1,10 1.,..
l)'L I, 1a 1-10 7.-
Total I oo . ~~ ~ " ~ . s ~ z.5 I '1 . ") lo.
Average .J > _S'-\C\t-4. ~
Comments: Time Baghouse t.P Time Baqhouse t.P
C,·.11, 1.\. I{~ io'. ~s U,l.{t.,
Cl: l.b 4. 4~ 10 1.zc, Lt. ~i..,,
C{°.~l I.\ ' Y. "l-lo'."l) '-1,,4 ~
"\'.,~ '1 ,t.\......-10 ',('o <..1,~\/
Location: Yellowcake Dryer Baghouse
Operator: M• Ms.Jo...~\v-..
Temperatures '"
Stack(T,) Probe Probe Ou1 Filter
qi' ., t;_{ tc.O 'Z.~O
er(., 71-0 l(L ? ,"'J
~l.o 2,,,1. z.~io 1',{ lo qr 1..'i lo Z3~ 1,".) 't
'H-'t<.,~ l.'t~ l.4~
'1:J. i.5' l (t l{I
to'"{ Z.'( ( Z-'l ~ Z-'-l0
lo) Z'i~ 2::!,~ z...3s
101-z. '-" t">S Z, "}~
lo~ {..70 i.~e z.~8
Lo~ 7,?u l, .ff.a z.~<o
Jo( l,.{ < 2, {-:J z;e,
\1.-l'\
,01.1.,
Effiuenl s~
"( =,.
so
5"
'1 ~
.'i' '6
ste
C. (;
(,'f
'i~
4(
5'2-
'o Cl~•[~l$
DGM Tcmp(T.)
Out ln
S-=t-' '<> (,,1 70
'1-1 r n. ~)
1t °1 l
1 er 9"7
-,q. Pl~
90 81.{
go 85
~o Bf
Bl 8(,,
~[ s-,
1~is
,B .S
Pab,el .. ~of. _t_ Run# I_
i 8
I Ao N
Stack Diameter _16''__ Port Reference _0.0"_
Pons are ~ Upstream from next disturbance
Ports are 37.8' Do,vnstream from last disturtiance
Assumed Moisture 1 %
Probe 10 (; Cp~
Nozzle Calibration ~ ,27e~~ ,z7li>
Avg D0 •-z, (b inches
Gas Bag Ambient Air
Console v{
Y ,factc,, l I G> I M'. () I 0
6H0 l. ~83 in H20
Barome1ric Pressures
Pbm z..c.1. ( f' in Hg
].Q. u~ Pb,, , in Hg
P1; -" 3 2... in H20
l.<alt Check: Pre
A'imin C, •() 0 3
vacinHg lO,O
P1101 Ra<e Q.-0
lnH,O 5,0
~
Q..:.Q.o.Z-
lo• O
Q:Q
~
Water Collected \ "2., ·-=;,-----=-----g
Time Sampled i1.0 min
Review
K=
K-
~
@Tm
@T, -·
South Yellow Cake Scrubber
Sample Recovery
Gas Analysis Data (ORSA T)
Yell ow Cake Dryer Baghouse
Sample Recovery
Gas Analysis Data (Ambient)
Chain of Custody
Lab Analysis
APPENDIX C
C
SYC
Facility: Energy Fuels
Stack Identification: SVC Scrubber
JMPl NGERS
Filter Number:
<e<t33
st ~·~~.l-{'f
1(A.V\; I\
lo to ir
L,\.t.A,11'{ i ~
~a..d-W {) I\
;: tkr.
IMPINGERS
Filter Number:
b'\?>':\
~f ~L._;. 1'\ ~ ,1
l.C \Gr
\~k,, .. "uv \t'v\
~""-~ C{\ (.,,·,-w
IMP!NGERS
Filter Number:
------------------
Run: ----Sample Box: A -~--
lmpinger Number
2 I 3 I 4 I s 6
Initial Volume of liquid (H10) in impingers. {ml)
100
Final (g) , I,,?·~
Initial (g) 1(5. e, ~.:;..:,....:=-----+-~....:...._;_-t-~.a.1..:.1'-L....+-:~L.:..:=-l-----+----
Net (gl . f5
Total (gl \ 30. 2... ========
Run: 2 Sample Box:_& __ _
2
lmpmger Number
I 3 I 4 I s 6
Initial Volume of liquid (Hi0) in impingers, (ml)
100
Total (g) \ "'l O, 2.,
Run: ----Sample Box: ___ _
lmpmger Number
2 I i I 4 I s 6 -Initial Volume of liquid (H20) in impingers, (ml)
100 I 00 I Dropout ! SG !
Final (g) -----t---------1-----i------t-----l nit i a I (g) ----+----t----+----1-----+----N et (gl ================::::!::::::===!::::::========
Total (g) ========
Location __ S___,_-(_C-____________ _
Analytical Method. ___________ _
Date \l(N/1~
Test No. (
Gas Bag No. y,<,
Ambient Temp <.S
Operator ~
Date I\{ I { { ( '}
Test No. 7,,
Gas Bag No. _"t.,,__ ___ o_) __
Ambient Temp ~C:,
Operator Mo-411
C
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 100 Minus
Actual 0 2 Reading).
Gas
CO2
0 2 (Net is Actual 02
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 0 2 Reading).
Gas
02 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 0 2 Reading).
Actual
Reading
·3.0
I ct. 8
Actual
Readine
3, 1..
l'hl ..
Actual
Reading
RUN
2
Net Actual Net
Reading
)hl 3.o 3.0
l"',ei (°'·a Ito .s
RUN
2
Net Actual Net
Ra,dlng
3 ,2.-""3 I 2.-3,Z..
)t..o l°t,t-llo · I.O
RUN
2
Nol Actual Net
Reading
to2 was determined using a gas analyzer
CO is not measured, as it has the same molecular weight as N2
3
Actual Net
Reading
5.0 ),0
l'l .~ ,,., .e,
3
Actual Ntc
Reading
3,2.. 3,2....
\~cl. I(.. o
3
Actual Net
Readini:
Average
Net
Volume
Average
Net
Volume
Average
Net
Volume
Dryer Baghouse
Facility: Energy Fuels Date : l \/ / '-i / J -={--_ _;_ _____ _
Stack Identification: Yellow Cake Dryer Baghouse
IMPINGERS
Filter Number:
toi3s
51:~k+-
bf"---.f
~v\\t-"i~
IMl!l~~f;BS
Filter Number:
IM~l~GERS
Filter Number:
Run :
100
Final (g) S I ,5
Initial (g) (oo.") ·O
Net (gl -Z':l•
Run:
100
Final (g)
Initial (gl
Net (g)
Run:
100
Final (g)
Initial (g)
Net (gl
_ _.__ __ Sample Box: & ----
2 1 3 1 4 1 s 6
Impmger Number
Initial Volume of liquid (H10 ) in impingers. (ml)
100
Total (g) (2.,,...
Sample Box:
Impinger Number
2 I 3 I 4 I 5 6
Initial Volume of liquid (H20) in impingers. (ml)
100 I I SG I
Total (gl
Sample Box:
lmpinger Number
2 I 3 I 4 I 5 6
Initial Volume of liquid (H20) in impingers, (ml)
100 I I SG I
Total (g)
~ ,fivta:
·~---·. --IHT1:R-MOUNlAIN LAU:ii
3'9~ ,!'afH2(fS<>1i1~
Inter-Mountain Labs
Sheridan, WY and Gillette, WY All shaded fields must be completed.
This 1s a legal do(;Ument; an_t_ misre_presentation may be construed as fraud
Proje<:t Identification !Sampler (Signature/Attestation of Authenticity)
$~uttl!!®IQ.w ~ke ~rul;lber; o
Contact Name ANALYSES/PARAMETERS
Page 1 of
#WEB
Telephone#
~~.ra:-41'13
Amsr.i_~~ fo,:k, ilta,11 MqQJ . ·.,,
SAMPLE
IDENTIFICATION
14:15 16933 SYC Scrubber RUN 1
12:45 16934 SYC Scrubber RUN 2
11/14/17 I 9:06 16935 Yellow Cake Dryer Bc!_g_house
14:15 16933 SYC Scrubber RUN 1
12:45 16934 SYC Scrubber RUN 2
11/14/17 I 9:06 16935 Yellow Cake Dryer Baghouse
Soil . SL -J,l}ilfJ Standard turnaround
Quote#
Matrix
FT 1
FT
FT
OT
OT 1
OT
~ ij, I N I ~I REMARKS
.. jE · -~'--.,. .J I r .,I Conduct /Blanks
I I X X X X X X X
X X X X X X X
X X X X X X X
XIX I XIXIXI XIX
XIXIXIXIX I XIX
X I XIXIXIX I X I X
1
FedEx
USPS Solid SD ~ RUSH • 5 Working Days Fuels BlandinQ: Loqan Shumwa
Hand Carried
Other
lnlPr-Mnunt;iin I ;ih,; Inc
Filter FT
Other OT
Cf URGENT·< 2 Working Days
Rush & Urg_ent Surcharges will be applied
www intermountainlahs com
Lab
Rev4 n Weh
• ~HAIN OF CUSTODY RECORD • -nib~ Inter-Mountain Labs
Sheridan, WY and Gillette, WY All shaded fields must be completed.
INTE1t-11tnUH'f"A.IH LA.US This is a legal document any mi$representalion may be coc-strlied as fraud
CllentName
En
Repart Addr&Ss
91 Eaat 820 Sqilth
Ame""'1 Forte,. Utah 84003
Invoice Address
EFRJ C/Oac=counta P•~
Project Identification
S(ll.lth YelloW Cake Scrubber, D.
Contact Name
ean or Paul Kitchen
Email titcoiltik~COffl
Phone
ll5 Union Bvld.Sulte 800 l.qewood C0.80228 I .
LABID I DATE I TIME SAMPLE
SAMPLED IDENTIFICATION
14:15 6933 SYC Scrubber RUN 1
12:45 6934 SYC Scrubber RUN 2
11/14/17 I 9:06 6935 Yellow Cake Dryer Baghouse
14 15 6933 SYC Scrubber RUN 1
12:45 6934 SVC Scrubber RUN 2
9:06 6935 Yellow Cake Dryer Baghouse
Sampler (Signature/Attestation o! Authenticity)
I ' ft ~ ! #of
Matrix Containers ! i , ~.
FT 1 X X X X X
FT 1 X X X X X
FT 1 X X X X X
OT 1 X X X X X
OT 1 X X X X X
OT 1 X X X X X
Compliance Monitoring ?
I
X
X
X
X
X
X
0 .,. I '1 I ~ -,:t
Page 1
#WEB
Telephone ti
435-678-4113
of
REMARKS
~I :• I Conduct /Blanks
I I X
X
X
X
X
X
1
~ FedEx Soil SL
'.J USPS
Program (SDWA, NPDES .... ) ----~--~------~----,-------t
PWSID /Permit# Contact at Ener Fuels Blandin : Lo an Shumwa Solid
0 Hand Carried Filter
0 ~ Other
inter-Mountain Labs. Inc
SD
FT
OT
URGENT -< 2 Working D~ys
Rush & Urgent Surch.trges will be applied
www intermountainlabs.com
Lab
Rev 4 6 Wet
~ .... MI:: Your Environmental Monitoring Partner Inter-Mountain Labs ----------------------------------
,,. ... _.,ou .. u,,. •A•• 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
Date: 2/12/2018
CLIENT:
Project:
Lab Order:
Energy Fuels (White Mesa)
South Yellow Cake Scrubber, Dryer
S1711276
CASE NARRATIVE
Report ID: S1711276001
Samples 6933 SVC Scrubber RUN 1 filter & beaker, 6934 SVC Scrubber RUN 2 filter & beaker and 6935 SVC Yellowcake
Dryer Baghouse filter & beaker were received on November 20, 2017.
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 Inter-Mountain Laboratories except as indicated
in this case narrative.
Qualifiers by sample
LCSD-36 -Uranium Isotopic Filters/Uranium 234 -RPO outside accepted recovery limits
LCSD-36 · Uranium Isotopic Filters/Uranium 235 -RPO outside accepted recovery limits
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 } /J ,,.-7' ...--
Reviewed by: vt.,/.,K/ -
Wade Nieuwsma. Assistant Laboratory Manager Page 1 or 1
-~ lntec-Mouatain Labs Your Environmental Monitoring Partner
ll'TC:llll~MOUHTAIH' L.Aa.S 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 2112/2018
391 East 620 South Report ID S1711276001
American Fork. UT 84003
ProjectName: South Yellow Cake Scrubber, Dryer Work Order: S1711276
Lab ID: S1711276-001 Collection Date: 11/14/2017 2:15:00 PM
ClientSample ID: 6933 SYC Scrubber RUN 1 filter & beaker Date Received: 1112012017 10:37:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCl/ml
Radionuclides -Filter
Lead 21 O 1.6E·5 µCi/Sample 2E-06 6E-14 OTW01 12/12/20171351 MB
Lead 210 Precision (±) 2.9E-6 µCi/Sample OTW01 12/12/2017 1351 MB
Radium 226 0.16E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 12/12/2017 1039 MB
Radium 226 Precision (±) 0.1 E-7 µCi/Sample SM 7500RAB 12/12/2017 1039 MB
Radium 228 -2.0E-6 µCi/Sample 1E-06 2E-13 Ga-Tech 01/16/2018 141 MB
Radium 228 Precision(±) 2.6E-5 µCi/Sample Ga-Tech 01/16/2018 141 MB
Thorium 230 0.1E-7 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-230 Precision (±) 0.1 E-7 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 228 0.1E -7 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-228 Precision (±) 0.3E-7 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 232 0.0E-8 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-232 Precision (±) O.OE-8 µCi/Sample ACW10 01/10/2018 000 MB
Uranium 234 1.526E-03 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 234 Precision (±) 5.68E-04 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 235 O.OE-07 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 235 Precision (±) O.OE-07 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 238 1.569E-03 µCi/Sample 4E-07 9E·15 ACW01 02/09/2018 000 MB
Uranium 238 Precision (±) 5.7BE·04 µCi/Sample ACW01 02/09/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 01/23/2018 1323 MS
Uranium 7880 µg/Sample 1 9E-15 EPA 200.8 01/23/2018 1352 MS
These results apply only to the samples tested. RL -Reporting Limit
Qualifiers: B Analyte detected in lhe 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 quantilation 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 or Dilutions
S SpiKe Recovery outside accepted recovery limits U Analysis reported under the reporting limit
x Matrix meet
~ )~--' ~ Reviewed by: ..,~ ..... ;;_...{;e/ __ "----________ _
Wade Nieuwsma. Assistant Laboratory Manager Page 1 of 3
1~ lnle<-Mounta;n Labs
Your Environmental Monitoring Partner
l~Tlll-MOUHTAl'4 I.Aas 1673 Terra Avenue, Sheridan. Wyoming 82801 ph: [phone]
Sample Analysis Repon
Company: Energy Fuels (White Mesa) Dale Reported 2/12/2018
391 East 620 South Report ID S1711276001
American Fork. UT 84003
ProjectName: South Yellow Cake Scrubber. Dryer Work Order: S1711276
Lab ID: S1711276-002 Collection Date: 11/15/2017 12:45:00 PM
ClientSample ID: 6934 SVC Scrubber RUN 2 filter & beaker DateReceived: 11/20/2017 10:37:00 AM
COC: WEB Field Sampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 2.9E-5 µCi/Sample 2E-06 6E-14 OTW01 12/12/2017 1351 MB
Lead 210 Precision (:t) 3.4E-6 µCi/Sample OTW01 12/12/2017 1351 MB
Radium 226 0.18E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 12/12/2017 1039 MB
Radium 226 Precision (:t) 0.1 E-7 µCi/Sample SM 7500RAB 12/12/2017 1039 MB
Radium 228 -4.6E-6 µCi/Sample 1E-06 2E-13 Ga-Tech 01/16/2018 646 MB
Radium 228 Precision (±) 2.8E-5 µCi/Sample Ga-Tech 01/16/2018 646 MB
Thorium 230 0.16E-7 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-230 Precision (:t) 0.1E-7 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 228 0.01E-8 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-228 Precision (:t) 0.02E-8 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 232 0.01 E-8 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-232 Precision (:t) 0.02E-8 µCi/Sample ACW10 01/10/2018000 MB
Uranium 234 3.492E-03 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 234 Precision (±) 7.61E-04 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 235 1.40E-04 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 235 Precision (±) 1.38E-04 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 238 2 686E-03 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 238 Precision (±) 6.39E-04 µCi/Sample ACW01 02/09/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 01/23/2018 1327 MS
Uranium 12700 µg/Sample 9E-15 EPA 200.8 01/23/2018 1355 MS
These results apply only to the samples tested. Rl -Reporting Limit
Qualifiers: B Analyte delected in lhe associaled Melhod Blank C Calculaled Value
E Value above quantitation range G Analyzed al IML Gilleue laboratory
H Holding times for preparation or analysis exceeded J Analyte detecled below quanlilalion limils
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less lhan LCL
ND Nol Detecled at lhe Reporting Limil O Oulside the Range or Dilulions
S Spike Recovery outside accepted recovery limits U Analysis reponed under the reponing limil
X Matrix Elf eel
~ } /J ./7" ~
Reviewed by: ..,0,'-""_'../""--""(;e/ __ --------------
Wade Nieuwsma. Assistant Laboratory Manager Page 2 of 3
--~ Your Environmental Monitoring Partner
Inter-Mountain Labs----------------------------------------
'"n•-Mou .. r .. , ... ,... 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 2/12/2018
391 East 620 South Report ID S1711276001
American Fork. UT 84003
ProjectName: South Yellow Cake Scrubber, Dryer Work Order: S1711276
Lab ID: S1711276-003 Collection Date: 11/14/2017 9:06:00 AM
ClientSample ID: 6935 SYC Yellowcake Dryer Baghouse filter & beaker Date Received: 11/20/2017 10:37:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 7.5E-6 µCi/Sample 2E-06 6E-14 OTW01 12/12/2017 1351 MB
Lead 210 Precision (±) 2.5E-6 µCi/Sample OTW01 12/12/2017 1351 MB
Radium 226 0.2E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 12/12/2017 1039 MB
Radium 226 Precision (±) 0.1 E-7 µCi/Sample SM 7500RAB 12/12/2017 1039 MB
Radium 228 -9.5E6 µCi/Sample 1E-06 2E-13 Ga-Tech 01/17/2018 1116 MB
Radium 228 Precision (±) 2.9E-5 µCi/Sample Ga-Tech 01/17/2018 1116 MB
Thorium 230 0.1E-7 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-230 Precision (±) 0.1E-7 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 228 0.02E-8 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-228 Precision (±) 0.03E-8 µCi/Sample ACW10 01/10/2018 000 MB
Thorium 232 O.OE-8 µCi/Sample 2E-07 3E-15 ACW10 01/10/2018 000 MB
Thorium-232 Precision (±) O.OE-8 µCi/Sample ACW10 01/10/2018 000 MB
Uranium 234 8.37E-04 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 234 Precision (±) 1.25E-04 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 235 3.81 E-05 µCi/Sample 4E-07 9E-15 ACWOl 02/09/2018 000 MB
Uranium 235 Precision(±) 1 .54E-05 µCi/Sample ACW01 02/09/2018 000 MB
Uranium 238 8.49E·04 µCi/Sample 4E-07 9E-15 ACW01 02/09/2018 000 MB
Uranium 238 Precision (±) 1.26E-04 µCi/Sample ACW01 02/09/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 01/23/2018 1330 MS
Uranium 2470 µg/Sample 9E-15 EPA 200.8 01/23/2018 1358 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 Gillelle laboratory
H Holding times for preparation or analysis exceeded J Analyte detected below quantilation 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 O Outside the Range or Dilutions
S Spike Recovery outside accepted recovery limits U Analysis reported under the reporting limit
X Matrix Effect
Reviewed by: ... M"'"""'-~-----~----_-:.-:::::: __
Wade Nieuwsma, Assistant Laboratory Manager Page 3 of 3
~ ...... m I: Your Environmental Monitoring Partner
-Inter-Mountain Labs-----------------------------------------'",r:"'4""ou .. , •• _ .. 1..Aes 1673 Terra Avenue. Sheridan, Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1711276
Project: South Yellow Cake Scrubber, Dryer
Radium 228 by Ga/Tech
MB-477 (01/15/18 00:14)
Analyte
Radium 228
Radium 228 by Ga/Tech
LCS-477 (01/15/18 05:19)
Analyte
Radium 228
Radium 228 by Ga/Tech
MS-4 77 (01 /15/18 15: 29)
Analyte
Radium 228
Radium 228 by Ga/Tech
MSD-477 (01/15/18 20:35)
Analyte
Radium 228
Radium 226 Air Filter Analysis
MB-1821 (12/12/17 10:39)
Analyte
Radium 226
Radium 226 Air Filter Analysis
LCS-1821(12/12/1710:39)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MS-1821(12/12/1710:39)
Analyte
Radium 226
Radium 226 Air Filter Analysis
Qualifiers:
MSD-1821 (12/12/1710:39)
Analyte
Radium 226
B Analyte detecled in the associated Method Blank
G Analyzed at IML Gillel1e laboratory
J Analyte detected below quantitalion limits
ND Not Detected at the Reponing Limit
R RPO outside accepted recovery limits
X Matrix Effect
Sample Type MBLK
RunNo: 153883
Result
ND
Sample Type LCS
RunNo: 153883
Result
4E-05
Sample Type MS
Date: 2/12/2018
Report ID: S1711276001
Units: µ.Ci/Sample
PrepDate: 12/21 /17 14 :00 Batch ID 14113
RL Spike Rel Samp %REC % Rec Limits
1E-06
Units: µCi/Sample
PrepDate: 12/21/17 14:00 BatchlD 14113
RL Spike Rel Samp %REC % Rec Limits
1 E-06 4E-05 108 65.9 -132
Units: µCi/Sample
RunNo: 153883 PrepDate: 12/21/17 14:00 BatchlD 14113
Qual
Qual
Result RL Spike Rel Samp %REC % Rec Limits Qual
4E-05
Sample Type MSD
RunNo: 153883
Result
4E-05
lE-06 4E-05 ND 108 50 · 139
Units: µCi/Sample
PrepDate: 12/21/17 14:00 BatchlD 14113
RL Cone %RPO %REC % RPD Limits
1E-06 4E-05 0 108 20
Sample Type MBLK Units: µCi/Sample
RunNo: 153100 PrepDate: 11/29/17 0:00 BatchlD 14024
Qual
Result RL Spike Rel Samp %REC % Rec Limits Qual
ND 2E-07
Sample Type LCS Units: µCi/Sample
RunNo: 153100 PrepDate: 11 /29/17 0:00 Batch1D 14024
Result RL Spike Rel Samp %REC % Rec Limits Qual
7E-06 2E-07 7E-06 108 67.1 -122
Sample Type MS Units: µCi/Sample
RunNo: 153100 PrepDate: 11 /29/17 0:00 BatchlD 14024
Result RL Spike Rel Samp %REC % Rec Limits Qual
7E-06
Sample Type MSD
2E-07 7E-06 ND
Units: µCi/Sample
101 65 -131
RunNo: 153100 PrepDate: 11/29/17 0:00 BatchlD 14024
Result RL Cone %RPO %REC % RPD Limits Qual
7E-06 2E-07 7E-06 3.93 105 20
E Value above quanlilalion range
H Holding limes for preparation or analysis exceeded
L Analyzed by another laboratory
0 Outside the Range or Dilutions
s Spike Recovery outside accepted recovery limits
Page 1 of 3
,,,,~m· .... L Your Environmental Monitoring Partner lnter-Mountainlabs-----------------------------------------
•HnR-Mou,..,A.N LA8S 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
ANAL VTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1711276
Project: South Yellow Cake Scrubber, Dryer
Thorium Air Filter Analysis
MB-577 (01/10/18 00:00)
Analyte
Thorium-228
Thorium-230
Thorium-232
Thorium Air Filter Analysis
LCS-577 (01/10/18 00:00)
Analyte
Thorium-230
LCS-232 (01/10/18 00:00)
Analyte
Thorium-232
Thorium Air Filter Analysis
LCSD-577 (01/10/18 00:00)
Analyte
Thorium-230
Uranium Isotopic Filters
MB-35 (01/22118 16:38)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
LCS-36 (02109118 00:00)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
LCSD-36 (02109118 00:00)
Analyte
Qualifiers: B
G
J
ND
R
X
Uranium 234
Uranium 235
Uranium 238
Analyte detected in the associated Method Blank
Analyzed at IML Gillelle laboratory
Analyte detected below quanlitation limilS
Nol Detected at the Reponing Limit
RPO outside accepted recovery limits
Matrix Effect
Date: 2/12/2018
Report ID: S1711276001
Sample Type MBLK Units: µCi/Sample
RunNo: 153683 PrepDate: 12/11 /17 0:00 BatchlD R153683
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND
ND
ND
2E-07
2E-07
2E-07
Sample Type LCS Units: µCi/Sample
RunNo: 153683 PrepDate: 12/11/17 0:00 BatchlD R153683
Result RL Spike Ref Samp %REC % Rec Limits Qual
1E-05 2E-07 1E-05 107 68 -146
RunNo: 153683 PrepDate: 12/11/17 0:00 BatchlD Rl 53683
Result RL Spike Ref Samp %REC % Rec Limits Qual
2E-05 2E-07 2E-05 103 50 -150
Sample Type LCSD Units: µCi/Sample
RunNo: 153683 PrepDate: 12/11/17 0:00 BatchlD R153683
Result RL Cone %RPD %REC % RPD Limits Qual
1 E-05
Sample Type MBLK
2E-07 1 E-05 13.8
Units: pCi/L
92.8 20
RunNo: 153889 PrepDate: 01108/18 0:00 BatchlD R153889
Result RL Spike Ref Samp %REC % Rec Limits Qual
ND
ND
ND
4E-01
4E-01
4E-01
Sample Type LCS Units: µCi/Sample
RunNo: 154409 PrepDate: 02102118 0:00 BatchlD R154409
Result RL Spike Ref Samp %REC % Rec Limits Qual
8E-06
5E-07
9E-06
4E-07
3E-07
4E-07
8E-06
4E-07
8E-06
108
137
110
50 -150
50 -150
50 -150
Sample Type LCSD Units: µCi/Sample
E
H
L
0
s
RunNo: 154409 PrepDate: 02102118 0:00 BatchlD R154409
Result RL Cone %RPO %REC % RPD Limits Qual
lE-05
3E-07
lE-05
4E-07
3E-07
4E-07
Value above quanlitation range
8E-06
5E-07
9E-06
20.3
42.6
10.7
Holding times for preparation or analysis exceeded
Analyzed by another laboratory
Outside the Range of Dilutions
Spike Recovery outside accepted recovery limits
133
88.7
122
20
20
20
Page 2 of 3
R
R
... ~I: Your Environmental Monitoring Partner
lnter-MountainLabs-----------------------------------------,w,rR-""ou"T·'" LAIS 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT: Energy Fuels (White Mesa) Date: 2/12/2018
Work Order: S1711276 Report ID: S1711276001
Project: South Yellow Cake Scrubber. Dryer
Total (3050) Metals by EPA 200.8 • Soil Sample Type MBLK Units: mg/Kg
MBLK (11/28/17 13:07) RunNo: 152321
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium ND 1
Uranium ND 3E-01
Total (3050) Metals by EPA 200.8. Soil Sample Type LCS Units: µg/Sample
LCS (01/23/18 13:08) RunNo: 153908
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium 112 45 1E02 112 85 -115
Uranium 115 1E02 115 85 -115
Total (3050) Metals by EPA 200.8 -Soil Sample Type MS Units: µg/Sample
S1711276-003AS (01/23/18 13:36) RunNo: 153908
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Thorium 22400 45 2E04 ND 111 70-130
Uranium 26300 2E04 2470 118 70 -130
Total (3050) Metals by EPA 200.8 . Soil Sample Type MSD Units: µg/Sample
Sl 711276-003AMSD (01/23/18 13:46) RunNo: 153908
Analyte Result RL Cone %RPO %REC % RPO Limits Qual
Thorium 22800 45 22400 1.82 113 20
Uranium 25400 26300 3.82 113 20
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantilalion range
G Analyzed at IML Gillette laboratory H Holding limes ror preparalion or analysis exceeded
J Analyte detected below quantitation limits L Analyzed by another laboratory
ND Not Detected at the Reponing Limit 0 Outside the Range or Dilutions
R RPO outside accepted recove<y limits s Spike Recovery outside accepted recovery limits
X Matrix Effect
Page 3 or 3
APPENDIX D
South Yellow Cake Scrubber
Figure 1. Facility Schematic Representation
Yellow Cake Dryer Bag house
Figure 2. Facility Schematic Representation
Process Data
South Yellow Cake (Scrubber Flow Rates)
Yellow Cake Dryer Baghouse (~p readings on Field Sheet)
D
'";"'' Energy Fuels
t
a
'
'(
Stack ldentiticalion: South yellow Cake Scrubber
1 .......... 0~1
p
a: Dis1ance upstream from next disturbance, feet T ------
10' P: Distance downstream from last disiurbance. feet _ -
65' -y: Distance of Sample Level to Ground, feet-----
0 : Stack Inside Diameter. inches I 2.75 ' ------
Estimated Moisture. percent 4-8% -
I 00-120 Estima1ed Temperawre, °F . __ -
2 000 -Estimated Velocity. fpm ----'''-·----
Control Unir
Type:
Scrubber
J-.;umber of Ports 2
Figure I facility Schematic Represen1a1,on
Process
Type:
Yellow Cake Processing
Facm,y Energy Fuels
t
a
!
y
Stack ldentificalion: yellow Cake Dryer Baghouse
1.._0~1
13
a : Distance upsrrea,n from next disrurbance, feer 4.8' ----------
~: Distance downstream from last disturbance, feet 37.8'
y: Distance of Sample Level to Ground, feet 65.0'
0 : Stack Inside Diameter. inches 16.00" ---------
Esrimated Moisture, percent l-2
Estimated Temperature, °F 125 ----------
Esrimared Velocity, fpm 1400
Control Unit
Type:
Baghouse
Number of Ports 2
Figure I. Facility Schematic Representation
Process
Type:
Yellow Cake Processing
uf,~
Facility Energy Fuels
Location South Yellow cake
Date ll/ 1'3 • 14 f I +--
Demister
Run# Time Spray
I \t.t '. i.o '3. "1-
11-4',)1 '3 . 'l--
15 '. 27.. 3·8
15:53 3.~
II..,: 1B 1-8
''° ' 'i 1-3.g
17 ·. ,< l."~
e·.w 3, ":1-
8.'51 1,.S
41 : 1 B 5-~
1 ~ I ::J.-·1.~
10 '. 20 '3' ii
I a : '-I~ J.t
11 :·vt ~-8
IL :-f O 3 ·r
IZ. '. 1-i, 3-1,-
South South
Humidy Scrubber Scrubber
Spray Venturi Inlet Pressure ,, 1.) 12.. o z{. 2
f'') >l·' 2.~.1-,, ,., ~z...o l{. J
1.~ 32,. O 2.t. 3
/ 1-> 12.1 l {, ') ,,
-,. J 3z_.o 2{, I
'1,t.\ 3 ,.9 2 ), ,
1.{ 31.~ 2.4. °r
7,-{ l) .cf. l,.'
I"' 7,? 21.~ l.{. I ,,
t{,2-7.) 2{ .J ,,,.. 7., ZI. ~ ls. '"Z...
....,, ') z.'0 .3 2[. 3
1, 'f 28-~ tJ,)
l,'f 31, °' is.a,
'·<t 32.. j 2(.~
Facility Energy Fuels
Location South Yellow cake
Date \, I • '1-I, / I l-
South South
Demister Humidy Scrubber Scrubber
Run# Time Spray Spray Venturi Inlet Pressure ,,,,~ 2-r~:oo 3-~ 1.~
,~:30 3. 'l-1. t.(
f'\'.0'3 3. ':1-l . "'
14 :'t< s.r l·ll
15.(1,.. ~ .1-,.~
I S:'i3 ) ,"l-1, "t
It,~ 2 '1--3.:J-( I t.l
l\fri ~'.10 3.'\ lo.+-
0:yf 1-'t c:,' ~
9 ·. l,.:J 3.°t "'' :\. 9 '.41-?,.~ c., . -=,.
to: \'t.. 3-! ~. :,..-
to: 52. 1-C, '° . ::J.
II: n .. '). C, C, . -:J.
I\'. 60 3.~ (,. 1-
APPENDIX E
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
TefT'r~ra:vre Scr,:r
.J
u. o 'W"i" ; .:>ro:,e '""'lll!'liar.~~-M~B,.C"!:.~J ~--1-
1
Htl>~_,,-.,.,n1C.nj. :s •.
Type S
1
Pi1oi Temperature I
T ut:e Sensor i Temperature
Ser.sor
GooseneckTes;~~~~(Jre! lf~ ~-r--···--,Ju----.. ~~i~g-~r; -
Nozzle I t-sr r~ i , . Ill , " I G.wrill'Bl I , I . -°Ir', '· ~ -" ", JL l"tt.C:e I ".., I \.
{r::I, \__'. -' .L t ;; • I f \
U ~--=· l1 ,. 1 , Va:ve )
-==>-~J.i-,~. ,J L,*~o 4il~~. ;";;~~• P )\! Glass Filter ,· •:,: '.1,.1
1
1 Ice 1,,1 .:,1 i ! ~ .C-· 11 • .I Water1 • ··1 · . ; .,. '. H::ilder '. ,:I rq BaU1 / I •.! I I ~rt A J: j1,i ~ !'.11 j,:, I . Vacuum
/
Type S P1tot
Tube Stack
Wall
·. ' !l' IJ1 .,; ·!' I
1 Heated rea -• -__ -+-. , \ Line -. ".'t..,.=--.......---F . _ __.,
'-------"'~ ' ',
Manomete: Temperature Water Empty Silica '"'-.
Sensors Gel ,
{(} ~ (n.lj Vacuu~ ) f g O ~~ 1 · G3L'ge ,t
Orifice Jl / t ...J',.1/. .-, i'-..l./h -,;'"'':_,_ ,"'1! __ __.,/ L.,.l.'" -·-·· u J __ • ;:.q~ ~L-..L •. ~ \ . ~-~-----~\ r !) By-pass ~,H Ma.,n , . -·1 ·v I ! I Val ,e -·-· , . a ve • 1 -··"' I • j 0 r, I ' 71 -,..,_ I ' f Dry Gas 1 ; r------::::· , t. I ' I/ \'\-, "-., · Meler . r .-... )\
+ : \ / i: l_) , Air-T:gh;
r 1 • , ~, )I Pump
J'':'----71 ;-. ;r--..::. '·· . ~~·--~
I i!..:t1 r" "-,·lic'11:.,11l 1d \l1.1l,nd..; l 1-l ,:1111pli11!.l ·1,;1111
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES g-i&-i41 z;
1) Select three critical onrices to calibra1e lhe dry gas mete, wtuch bracket lhe expecle<J operating range.
2) Racord barometric pressure before and after calibration procedure
3) Run at tested vacuum (from Orifice Calibra!lon Repori). fo< a penod or lime
necessary to achieve a minimum total volume of 5 cubic feet
4) Record data and inforrna1ion ,n the GREEN cells YELLOW cells are calculated.
METER SERIAL &:~
CRITICAL ORIFICE SET SERIAL I'~ EQUIPMENT ID t:
K' TESTED TEMPERATURES 'F
INITIAL
FACTOR I VACUUM I ORIFICE. I RUIU I ~LAVG) '"' Mgl
OGM REAOINGS (FT1
INITIAL I FINAL I NET (V~I
AMSENTI DGM INLET I DGM OUTLET I DGM
INITIAL FINAL INITIAL FINAL AVG
G
G
G
0.1137
0.1137
G.8137
0.5317
0.5317
0.5317
• Q.1307
0.3307
0.3307
13 149.120
13 en.no
13 158.%05
13 820.0
13 625.873
13 UZ.770
13 599.150
13 807.50
13 613.170
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
'49.770
cse.zos
56%.130
625.873
632.770
639.3%0
107.5"
113.170
819.249
9.650
&.435
5.925
5.173
6.197
8.550
8.398
5.6%4
6.079
71 7J 75
71 7S 10
71 75 u
60 76 77
10 75 77
60 74 79
59 63 61
59 71 75
59 7) 77
75
7S
75
75
74
77
71
73
73
IC
13
13
77
79
79
75
77
77
77
78.25
79.00
71.25
78.%5
77.25
61.7S
74.00
75.00
FINAL
G;J
ELAPSED
TIME (MIN)
8
AVG (P."i
Z5.CO
§§90
uo
2.IU
E§ 00
50
19.50
13.00
14.00
1:!!
~
1.10
§ .A9
M
(1)
Vm (STD)
!.1fil
~
~
~
~
Mm
7,1281
QZZl
5.1007
2016 Pre-Calibration
FY VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V"(STD)
~
~
4.9345
AVG=
~
~
5.6%80
AVG:,
7.1920
•,19-'1
~
AVG=
(3)
y
l!.!li
!!,ill
0.99)
Q.lli
1.ill
.Yil
~
!,lli
~
1,lli
~
l
V
V,\RtATION ('II)
:1,Il
~
!,ill 0.17
The fcllowingeqoaoo,,s,e used lo oat:ulale lh~ Slatl(l•d YOlJmesol ao passed lhrough lh• DGM. v. (std), ao>d lhe cmcalorfice
V,, (std), and the DGM caibration fat10r. Y. The.e ~n, ,re automaticaly ca~ulated in lhe spreadsheet above AVERAGE ORY GAS METER CALIBRATION FACTOR, Y = ~
(1)
(2)
131
Tedmician
Vm,,,,11 = K , .. flm• J~hu,•+U,';.H 13.6) rm
Vc..•r, .. 111, = J.:'• Phur • 0 Jramh
= Net volume or gas sample passed through DGM. corrected to s1andard conditions
K, = 17 64 °Rlin? Hg (Engfisn), O 3858 °Kimm Hg (Metric)
T"' = Absolute DGM avg. temperature (0R . English. °K. Me1nc)
= Volume ot gas sample passed through the cnt1cal orifice. corrected ro standard conditions
T ...t1 :a; Ab~lule ambient 1empera1ure ('R . English. °K . Metric)
K' 2 Average K' factor from Cntical Orifice Calibration Ver,,,.,, )' = --
Vm,,,dJ
= DGM calibration !actor
J. Gralon
lc:e&lh
A.mbllffl\A1r
~Wafltf
AVERAGE AH@=~
2
AH,.= ( 0.75 9 ) AH (Vrn(std))
V«(std) V~
Temperature Sensors
Reference In Olli
OF
33
62
202
OF
33
62
203
oF
33
62
203
!all!
!,!ll
11.22
.Lil!
1£!
Ml!
1M2
~
1.561
Pre Tesl Cal 2017
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES ~ -™-:vo I :I! '
1) Select three critical orifices to calibrate the dry gas meter v.tiich bracket the expected operating range
2) Record barometric pressure before and after calibration procedure. ENVIRONMENTAL SUPPLY COMPANY
3) Run at tested vacuum (from Orifice Calibration Report). for a period of time
necessary to achieve a minimum total volume of 5 cubic feet. 2017 Pre-Calibration Console 7
4) Record data and information in the : "'::.: • cells, YELLOW cells are calculated.
METER PART #:!Console
K' TESTED
METER SERIAL #:G;J
CRITICAL ORIFICE SET SERIAL #: ~
~~~~~~---1 FACTOR I VACUUM DGM READINGS (F'f')
ORIFICE#
G
G
G
RUN#
2
3
2
3
2
3
(AVG)
0.8137
0.8137
0.8137
0.5317
Q.5317
0.5317
0.3307
0.3307
0.3307
(in Hg)
12
12
12
12
12
12
12
12
1%
INITIAL I FINAL I NET (Vm)
38.030
44.570
50.040
225.972
231.884
237.640
262.105
267.514
272.936
44.570
50.040
11.800
nt.Dt
237.840
243.580
267.514
272.936
278.316
6.540
5.470
8.760
6.912
5.756
5.940
5.409
5.422
5.380
USING THE CRrTICAL ORIFICES AS CALIBRATION STANDARDS:
INITIAL
BAROMETRIC PRE,SSURE (In Hg):J 25.10
EQUIPMENT ID#: Console#7
TEMPERATURES'F
AMBIENT I DGM INLET I OOM OUTLET
INITIAL FINAL { INITIAL i=INAL
68 76 77 81 IO
68 77 71 90 91
S8 71 79 91 93
62 81 83 83 85
62 83 92 85 93
62 92 84 93 91
62 82 84 94 92
&2 84 85 92 92
62 86 86 92 94
DGM
AVG
12.71
84
85.26
83.00
88.25
90.00
88.00
88.25
89.25
FINAL
25.60
ELAPSED
TIME (MIN)
e
AVG(P,,,)
25.60
§~.zo :
3.20
3.20
8.25 1..%6
a.oo 1.20
8,25 1.20
12.00 0.47
12.00 0.47
12.00 0.47
(1)
Vm (STD)
~
4.5851
~
Mm
4.7601
4,8967
~
~
~
IF YVARIATION EXCEEDS 2.00'!,,
ORIFICE SHOULD BE RECALIBRATED
(2)
V"(STD)
yg
~
7.2545
AVG=
~
Ulli
4.9115
AVG=
~
~
4.4478
AVG=
(3)
y
M!2
Y!!
~
~
~
~
~
J..2Q2
l!.!!i
~
1.004
Yll
l
y
VARIATION {'~I
~
~
!J!
The foUowing equations are used to calculate the siandard volumes ol air passed through the DGM. v. (sld). and the cntical orifice.
V0 (std), and the DGM calibra~on factor. Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 0.996
(1)
(2)
(3)
1 ·m, .,,, = K, • Vm • l'l>ur + lJ.l./ / 13.6
1i11
., J>hur • E)
I ~,:r,.,1r1 > ~ A -J7'anrh
= Net volume of gas sample passed through DGM. corrected to standard cond~ions
K, = 17.64 "R/in. Hg (English), 0.3858 "Kimm Hg (Metric)
Tm= Absolute DGM avg, temperature ("R -English. "K -Metric)
= Volume of gas sample passed through the critical orifice. corrected to standard conditions
T..., = Absolute ambient temperature ("R • English, "K -Metric)
K' = Average K' factor from Critical Orifice Calibration
f'1-·r,,"11 l'= .~
~111:mti
= DGM calibration factor
AVERAGE ~H@ =1 1.673
:,H@=
(
0.75 0 )2 &H (Vm(Std))
V"(Std) Vm
Temperature Sensors
Reference In Out
OF
32
72
201
•F
33
73
202
OF
33
73
203
WI
1.835
!.ill
Lill
1,lli
1.fil
1.Hl
~
1.585
10 -~ METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES ~ ~~ 1,11/it)" \a11u• · R4·/1H1nlf!l "-t ~-1i ,
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure
3) Run at tested vacuum (from Orifice Calibration Report). for a period of time
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information in the GREEN cells. YELLOW cells are calculated.
TECHNICIAN: K.McNamara I----~------' INITIAL
DATE: 11/16/2017 METER SERIAL II: 27863
METER PART#: Console 4 CRITICAL ORIFICE SET SERIAL#: 1453S
BAROMETRIC PRESSURE In H : 25.30
EQUIPMENTID#: Console #4
K' I TESTED
.....------,------i FACTOR I VACUUM DGM READINGS (Fr}
ORIFICE# RUN II (AVG) (in Hg) INITIAL FINAL
D:ffi§
G: 0.6BOB 12
0.6808 12
0.6808 12
378.755 385.158
385.158 397.989
397.989 404.630
D:ffi§
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
NET(Vm)
6.403
12.831
6.641
TEMPERATURES 'F
AMBIENT! DGM INLET I DGM OUTLET
INITIAL FINAL INITIAL FINAL
I 111 H
66 67 68 75 74
68 68 69 74 75
70 69 68 75 75
I I I I I I
DGM
AVG
71.0
71.5
71.8
FINAL
25.30
ELAPSED
TIME(MIN)
8
AVG (P .. ,)
25.30
DGM~H
(in H20)
§§
7.15
14.50
7.50
§ 0
0
§§
(1)
Vm (STD)
5.4144
10.8398
5.6078
Post-Calibration
Energy Fuels
Yellow Cake Dryer Baghouse
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V"(STD)
AVG=
5.3713
1Mm
5.6129
AVGs
AVG=
(3)
y
~
~
jJ!Q1
0.999
l
y
VARIATION(%)
Q,22
The following equations are used to calculate the standard volumes of air passed through the DGM, Vm (sill), and the critical orifice,
V0 (std), and the DGM calibration factor, Y These equations are automatically calculaled in (he spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 0.999
(1)
(2)
(3)
Vi11_,.,., ~ K, .. v,11 ,.Pbar+(}l/{ '13.6)
Tm
= Net volume of gas sample passed through DGM. correded to standard conditions
K, = 17.64 vR/in. Hg (English), 0.3858 vK/mm Hg (Metric)
Vcr,::.ri
l'c,·,:rr
J" ::-:: Vm1~:r..,
Tm = Absolute DGM avg temperature ("R -English. "K -Metric)
= Volume of gas sample passed through the critical orifice, corrected to standard conditions
T0.,,. = Absolute ambient temperature ("R -English. "K -Metric)
~ = Average K' faclor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE ~HC! =1 1.606 I
~HC! =
(
0.76 0 )2 ~H (V.,{sld))
V"(std) Vm
TEMPERATURE SENSORS °F
REFERENCE! IN I OUT
1.601
1.606
1.611
-~ METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES • ~-~~ '1ur/i1.-.. \allU' -Rdmh1/1r, ~ ~,,~,
1) Select three critical orifices to calibrate the dry gas meter which bracket the expected operating range.
2) Record barometric pressure before and after calibration procedure.
3) Run at tested vacuum (from Orifice Calibration Report), for a period of time
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information in the GREEN cells, YELLOW cells are calculated.
TECHNICIAN:! K.~cNamara I
METER SERIAL #: G;:;::J
CRITICAL ORIFICE SET SERIAL#;~
DATE: 11116/2017
METER PART#: Console 7 -
K' TESTED
~~~~-.-~----1 FACTOR I VACUUM DGM READINGS (Fr!
ORIFICE# I RUN# I (AVG) fin Hg) INITIAL FINAL
0.4238 12
0.4238 12
0.4238 12
321.651 331.965
331.985 341.165
341.165 348.459 G: o:rnEB o:rnEB
USING THE CRITICAL ORIACES AS CALIBRATION STANDARDS:
NET (Vm)
10.314
9.200
7.294
INITIAL
BAROMETRIC PRESSURE In H : 25.30
Eou1PMENTJD •= Console #7
, TEMPERATURES 'F
AMBlENTI DGM INLET I DGM OUTLET I DGM
INITIAL FINAL I INITIAL FINAL AVG
65 61 68 62 73 66.0
68 68 74 73 81 74.0
69 74 77 81 83 78.8
I I I I I I
I I I I I I
FINAL
25.30
ELAPSED
TIME(MIN)
0
18.75
16.50
13.00
AVG(P.,,)
25.30
DGM6H
(in H,O)
0.75
0.75
0.75
§§
§§
(1)
Vm(STD)
Uill
7.7102
Ylli
2017 Post-Calibration
Energy Fuel
South Yellow Cake Dryer Scrubber
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V«(STD)
8.7767
7.7015
6.0621
AVG=
AVG=
AVG=
(3)
y
W.l!
~
1.001
1,222
1
y
VARIATION (%)
0.00
The following equations are used lo calculate the standard volumes of air passed through the DG M. Vm (std), and the critical orifice,
V0 (std), and the DGM calibration factor, Y. These equations aie automatically calculated in lhe spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 1.000
(1)
(2)
(3)
Viu,,.,., ·= K, .... v,,,,. Pbnr >-(~ )3.6)
'Jiu
= 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)
., Pbnr "le)
Ve,-".·'' = K ,, ifn;;;b = Volume of gas sample passed through the critical orifice. corrected to standard conditions
T-= Allso(uta amt,ient temperature ('R -English, 'K . Metric)
V('I' :ra
1· : J",11,,,.,;,
K' = Average I(' factor from Critical Orifice Calibration
= DGM calibration factor
AVERAGE 6H@ =I 1.624
6Hto1=
( 0.76 8 )
2
6H (Vm(std))
V0,(std) Vm
TEMPERATURE SENSORS °F
REFERENCE I IN I OUT
!,.ill
1.623
Lill
' ~
Type S Pilot Tube I nspec1ion Da1a
Dale: 12/9.'16
o,
t --? " ~ r 8
8"'
-........!.. .,
'-----
P, '
I
~-~"' --==-·--
0
p•
Pe D,"'
f\=
1'11 ~
a, ~-IO"
<l;...: 10"
p, ,• 5"
P, --5"
Z .SO 1~5 in,
W .s 0.03125 in
W ~-3 inches
Z > 3/4 inch
--.-. ____ Y c:: 3 inches
Pilot Tube ldentiticalion 18 G
Technician: K_ McNamara
0_375 in ls P" ~ P11 °
ts I 05 • D, S PA & Po .S I ~O • D,?
0 452 Ill
0 452 in.
a,.:..
a," 2
P,= 0 ------
P, = ------
Z = __ 0_0_10 __ 111.
W = 0_005 in ------
W = 6 75 m ------
Z = I 75 in ------
Y = 3 li2 in ------
The p1101 tube meets 1he spec1licat1ons for a calibration factor ofO 84° Yes
T ~mp<:ra1ure Sensor Calibr3lion
Rell:rtnre· Omega CLJ512A
Conlinuity Check Yes Probe
Heal Check 248 Yes
Temperature T~mpcratur~ -1 emper31ure
Source Keterence Sensor Difference
(Medium) (Fl (Fl ('F)
Probe AIR 65 66 l
AIR 65 64 I
ICE \\iATER 33 34 1 Slack
BOIL WATER 204 20.t 0
SILICONE OIL
Yes
Yes
Dale. 12/27,16 -------
D,
~ j PA
• Pe
8::
Type S Pi101 Tube lnspec1ion Dala
PIiot Tube ldcntificat1on: ____ _;,2_7-'G'---2 ____ _
Technician: K. McNamara
D, 0 375 in. Is P,, ~ P11 ° Yes -----------------I$ I 05 • D, s P, & P11 5 I 50 • D, ~ ____ Y_e_s __ _
P,-0 451 111
l'n -0 451 m.
u, < 10" Ct,= 0 ------
U; ', 10" O.; -
II," 5"
P: < s"
l 5 0.115 in
W 5 0.03125 in
W ;, 3 inches
Z ,. 314 inch
------
Z = ----'0-'0..:;;2_9 __ in
W = 0.031 m. ------
W = __ ..;.(>.:..;. 7..;.5 __ in
l = J.:i IU ------
~ t, -· ·-0 F--:1]-.... .._,___ Y::: 3 inches Y = __ 4_1_!2 __ in,
The pi101 lube meels 1he specificaiions for a calibration faclor ofO 84° ~
Temperature Sensor Calihra11on
Reterence· Omega CL3512A
Coniinuity Check Yes Probe Heal Check 248 Yes
I cmperature ·1 cmoeralure ·1 cmperarnrc
Source Relerence Sensor Oi rrcrcnct
(Medium) ('Fl ('Fl (Fl
Probe AIR 66 66 0
AIR 66 66 0
ICE v.:ATER 33 33 0 Siad
BOIL WATER 204 203 1
SILl('ONE Oil
Type S Pilol Tube lnspeclion Dara
Dare-12/27!16 Pi101 Tuhe ldentificalion 27 G-J ------------------
D, Tc ch n i c i an: K McNamara
F t P.
Pe D,=
p = A
_____ o_3_7 __ s __ in I~ PA= P11 ° ____ Y_e_s __ _
Is 1.05 • D, 5 P-' & P,. 5 uo • D, 0 ____ Y_e_s __ _
0-452 in
s:: P,, = 0 452 in
01 "-10" 01
a:<lif a:· _____ _
0
,./\P,
-~---fy 1\1 . 5''
ir----.:::___.,-:.._ P: ·: S"' p,= ___ _
Z 5 0.1 ~5 m Z = __ o_o_,_7 __ m.
f ~~-~-" W s O.QJ 125 in W= 0 001 in
W -, J inches W= 6 75 Ill
Z > J/4 inch z= m
0 ~ I ••• ra~----.-____ v ,: J inches Y = 4 I '2 in. ------
The pi1011uhc meels 1he specifications for a cahbralion ractor of0.84° ~
Temperature Sensor Calibration
Reference· Omega CL35 I 2A
Con1inuily Check Yes Probe Heat Check 248 Yes
I emperature I cmoerature-·1 cmperature
Source Kelerence .Sensor Difference
(Medium) ("F\ (Fl ("F)
Probe AIR 66 b6 0
AIR 66 66 0
ICE WATER D 34 I
Stack BOQ WATER 204 204 0
SILICONE OIL
TETCO
Sample Box Temperature Sensor Calibration
Date: 9/JJ/17 Calibrator: Kawai McNamara. Alex Moore Reference: OmegaCL3512A
Thermocouple Temperature Temperature Temperature
Unit ID Location Source Reference Sensor Difference
(M~dium) ("F) ('F) f'F)
Oven (3) Water 33 33 0
A Water 204 203 -I
Water 33 33 ~ Oven (4) Water 204 203
Oven (3) Water 33 33
B Water 204 204
Water 33 33 ~ Oven (4) Water 204 204
Oven (3) Water 33 33
C Water 204 205
Water 33 33 ~ Oven (4) Water 204 205
Oven (3) Water 33 35
D Water 204 205
Water 33 35 ~ Oven (4) Water 204 205
Oven (3) Water 33 35
E Water 204 205
Water 33 33 0 Oven (4) Water 204 205 I
F Oven Water 33 33 0
Water 204 205 I
G Oven Water 33 34 I
Water 204 205 I
H Oven Water 33 32 -1
Water 204 204 0
lmpinger Out A Water 33 32 -I
Water 204 204 0
lmpinger Out 0 Water 33 33 0
Water 204 205 I
lmpinger Out C Water 33 33 0
Water 204 203 -I
lmpingcr Out D Water 33 33 0
Water 204 202 -2
lmpinger Out E Water 33 33 0
Water 204 202 -2
lmpinger Out F Water 33 33 0
Water 204 203 -1
Im pinger Out G Water 33 33 0
Water 204 202 -2
lmpinger Out H Water 33 33 0
Water 204 202 -2
lmpinger Out I Water 33 33 0
Water 204 202 -2
lmpinger Out J Water 33 33 0
Water 204 202 -2
lmpinger Out K Water 33 33 0
Water 204 202 -2
APPENDIX F
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
ATTACHMENTH
SURFACE WATER GRAPHS AND FIELD DATA SHEETS
1.00E-05
1.00E-06
1.00E-07
-G)
l.oOE-08 i. • -• •
C)
0 I:• • ..J • -•
1.00E-09 , • • ia· •• ... • • ... ....
1.00E-10 L ---
Cottonwood Creek Dissolved Radionuclide Concentrations
(uCi/ml)
• • ..
-
• • ~ --
• • • • .. • • ---• • • • •• • •• .i -----------------..____.________ _________ -----------------·---,.______ ----
----
•
• • • • ••
• •• • .-
-
1.00E-11 -i------..-------,-------,.-------.-------.-----1a-----.------~
o.,'b'l, ~" ~
~ ).,~Oj ~~
o.,°-''1, ~" ~rv"'
R,'b
~~Oj
~'o
~<:;)n:,
(\..{P
~'1, ~
• U-Nat. • Th-230 A Ra-226
r::,°-' '[l.,G
<,}.~Oj
~
~rf' ~"'
~
<,}.~'1,<:;)
1.00E-06
1.00E-07
1.00E-08
a>' ca
~.OOE-09
C,
0 ..J -
1.00E-10
1.00E-11
1.00E-12
RJ~
":-."OJ ~"'
....... •
= -----
~ .
Ri' "OJ n,,q} ~
Cottonwood Creek Suspended Radionuclide Concentrations (uCi/ml)
•
-... • --A • • -----..
• -~ -... .... • • . .... .... • •
.... . -~-= . --: --. ---------------------_... __
---------wai----------~-----.... •
---
2)~ 2)0;, 2)~ R>'o !::)" ~ !::)ro !::)o., ..... -,, Oj #"Oj '/\"-<,j<"Oj ~"Oj ~ ~ ~ ~ r:::, ~~ r<}.ro ~ro A.~ r}"O ~ro
~'V "<:S ~ ~ ~ti; q}.'l; 4' n;, ..... rv ~ "
• U-Nat. • Th-230 • Ra-226 j
..
-... -
.. • -• .... -~ .... .... -----A ---
-
~ ~ r:::,~ r:::, r:::, ~ro ~ro ~ro ~" ..... ~ ~
1.000E+OO
1.000E-01
1.000E-02
1.000E-03
1.000E-04
1.000E-05 -Cl)
joooE-06
Cl)
C)
jOOOE-07 -
1.000E-08
1.000E-09
1.000E-10 I • •
1.000E-11
1.000E-12
1.000E-13
1;:>°-> ~ ~'l, '\~
Westwater Creek Dissolved Radionuclide Concentrations
(uCi/ml)
~ -
..
"~ "O;, ~ '>-"'o ""'
r::::i""' ~~'l, ~ cs-"~
• U-Nat. • Th-230 4 Ra-226 l
~ ef' ~ "'V
-
"ro ~ <,}."<::)
-Q)
1
0.1
0.01
0.001
0.0001
0.00001
ffl.000001 en
<mJ000001
..J -
--
Westwater Creek Suspended Radionuclide Concentrations (uCi/ml)
--
-•
-
...
1E-08
1E-09
1 E-10
1 E-11
1 E-12 ~ ... "Y
1E-13 ~1 ------:;~======~;~~~~~~~!~~~~~~~~~~~~~~ii
"f,O;,
/\.~
~~<:.::,
\~'o ~~
\~'1, '*~ '::..{':,
'8-~
\~ ~ ~'V
~{o
<,j-~c:j
j • U-Nat • Th 230 _. Ra-226 I
(
White Mesa Mill -Standard Operating Procedures
Book #11: 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 onQ_Co:Onwood C ~Westwater Canyon Other (describe) ____ _
DATE: 7/?.7/Zor1
pH BUFFER 7.0 --'-'--'·'-'-o __ _
BY: G·c,rri',, PAlm:cr
(Sampler's initials)
pH BUFFER 4.0 _ _.'-l.,..,,,0'----
SPECIFIC CONDUCTIVITY --'~o_o_· _o ______ u~MH~O~s
STEAM DEPTH: "
pH of WATER _---=6:;.._·• __ 3_'1~-----
COND bunhos Z.Z 4
pH Units __,(;.te..·=~:....::O=------
Temp °C Jg,53>
COND µrnhos Z:30
pH units --~"""'._4_"2. ___ _
Temp °C -~18"-.~g_D ___ _
Comments:
,".,.rb 3000 1'
orp ,;os
TEMP IS . ~z..
COND µmhos ·z.25
pH units -'-~·':l=O"----
Temp °C I f{.~Z.
COND µrnhos zzg'
pH units -'-'·-4_5 ___ _
Temp°C _l8_._~~'----
I
I
Cottonwood Creek
7/27/2017
(
Li "
White Mesa Mill -Standard Operating Procedures
Book #11: Environmental Protection Manual, Section 2.1
Date: 04/14 Revision: EFR-3
Page 5 of5
Attachment A
FIELD WATER ANALYSIS SURFACE WATER
WHITE MESA MILL
LOCATION (Circle one):Cottonwood Cree~twater Canv~ Other (describe) ____ _
DATE: _ _____.7C-1--/-=2-=-7 ......_/ .......... 1 ]'------BY: _ __-=.(;....;._ .. ...,__P =--. -----
(Sampler's initials)
pH BUFFER 7.0 _ __,7i.....;;."""D'----pH BUFFER 4.0 -----!'-{~. =() __ _
SPECIFIC CONDUCTIVITY ___ ,;_..:::oc....;o:;___o ____ ...,::µ=MH=O~s
STEAM DEPTH:
pH of WATER __________ _
COND=bcmh===o~s ____ _
pH Units -------
Temp °C ______ _
CONDµ=mh=-=-o~s ____ _
pH units ______ _
Temp °C -------
Comments:
TEMP ______ _
COND µmh=o=s;;__ ___ _
pH units -------
Temp 0C ______ _
CONDµ=mh==os~----
pH units -------
Temp °C ______ _
7 /21(,:z A r(""~&JG.d--o ...... s,'f t:. 12= f-o~z.o ... Gp..rrl ...... 4,,A-(A, rc;,~"'-U"" f\l'c~,·-A+-i,1 rc,c.lL 1,..4,)"Z),.~
r}.t-'{ 't/11.,/17 .. A ,.t-,v,J.. °"'"' sd, °'t lto'--1. C-r"-e..t. w,., 1 al~y
( Westwater Creek
7/27/2017
Westwater Creek
9/29/2017
White Mesa Mill-Standard Operating Procedures
Book #11 : 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 one€!inwood Cr"' Westwater Canyon Other (describe) ____ _
BY: &:f __ .__-=----------
(Sampler's initials)
pH BUFFER 7.o __ 7....:......o..;. u ____ _ pH BUFFER 4.0 __ L.{~. 0~--
SPECIFIC CONDUCTIVITY __ 1_0_0_0=-------=µ"""-MH'---0'"---s
STEAM DEPTH:
pH ofWATER ___________ _
COND =µmh===o~s ____ _
pH Units ______ _
Temp °C -------
COND µ_mh_o_s ____ _
pH units ______ _
Temp°C ~------
Comments:
TEMP --------
COND µmh=o=s'------
pH units ______ _
Temp°C ______ _
CONDµ_mh_o_s ____ _
pH units -------
Temp°C ______ _
Cottonwood Creek
12/13/2017
(
t'.
\JI:._
White Mesa Mill -Standard Operating Procedures
Book #11: 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 one):Cottonwood Creek ~ Ca~ Other (describe) ____ _
DATE: io I 1.1 f 11 BY:_....J,G..:...,; .. ,,_,ec....:,.. ____ _
(Sampler's initials)
pH BUFFER 7 .0 _ _,_7 -=-~ o_· ... '-----pH BUFFER 4.0 --'---=--1 _,_O.:;__ __
SPECIFIC CONDUCTNITY ---'-'I O'-O~D _____ ...cµ=MH=O::..:cs
STEAM DEPTH:
pH of WATER __________ _
COND _µmh==~os _____ _
pH Units -------
Temp 0C ______ _
CONDµ=mh==o=s ____ _
pH units -------
Temp °C -------
Comments:
TEMP ______ _
COND µ=mh=os~----
pH units ______ _
Temp°C ______ _
CONDµ.;mh==.;os=-----
pH units ______ _
Temp °C -------
~
INTf.A•""OUH 11\,,. loAV~
Inter-Mountain Labs
Sheridan, WY and Gillette, WY
• CHAIN OF CUSTODY RECORD •
All shaded fields must be completed.
This is a legal document: any misrepresentation may be construed as fraud.
Client Name Sampler (Slgnatu~e/Attest~oryof Authenticity)
W t""tc:.r J7
ANALYSES/ PARAMETERS
-z-zs v"',o~ Sl11d\...) Sv~t,
c,,..~c."6)00~,
Invoice Address
\t ~o ~1 e LABID SAMPLE # of
ghecJL desired service Compliance Monitoring?
Fed Express Soil SL )*'Standard turnaround Program (SOWA, NPDES, ... )
0 US Mail Solid SD D RUSH -5 Working Days PWSID / Permit #
D Hand Carried Filter FT 0 ' URGENT -< 2 Working Days Chlorinated? YI
0 Other Other OT Rush & Urgent Surcharges will be applied Sample Disposal: Client
Inter-Mountain Labs, Inc. www.intermountainlabs.com
Page I of
# 17207 0
Telephone#
'tlS' 67
REMARKS
-,A.!_o,._ £ll t e. ~
Rev4.6
""l~m-.... L Your Environmental Monitoring Partner
, ... ,.,!ii1i,~ioii_.,•oriiiu,.""',•Al,. .. L• .. aiii, Inter-Mountain Labs -1-6-73_T_e-rr_a_A-ve_n_u_e.-S-he-r-id-an-, -W-y-om-i-ng_8_2_8_01--ph-: -(3-0-7)_6_7-2--89_4_5 ___________ _
CLIENT:
Project:
Lab Order:
Energy Fuels (White Mesa)
3rd Q. Surface Water-17
S1707426
Sample Cottonwood Creek was received on July 28, 2017.
Date: 8/15/2017
CASE NARRATIVE
Report ID: S1707426001
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 Inter-Mountain Laboratories except as indicated
in this case narrative.
Reviewed by: 4/~--<"----
Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 1
,,,1~m--,•~ L Your Environmental Monitoring Partner
"',"'!ii'"i!-~--M~o•u"~'A-.,Hi:-L!iiAiii!es Inter-Mountain Labs _1_6_7_3_T_e_r-ra_A_v_e_n_u_e_, _S_h_e_r-id-a-n,-W-yo-m-in_g_8_2_8_0_1 _p_h_: -(3_0_7_) _6-72---8-94_5 ______________ _
Sample Analysis Report
CLIENT: Energy Fuels (White Mesa)
6425 S. Highway 191
Blanding, UT 84511
Project:
Lab ID:
3rd Q . Surface Water-17
S1707426-001
Client Sample ID: Cottonwood Creek
Analyses
General Parameters
Total Dissolved Solids (180)
Total Suspended Solids
Result
200
11300
RL Qual
10
5
Date Reported: 8/15/2017
ReportlD: S1707426001
Work Order: S1707426
Collection Date: 7/27/2017 8:00:00 AM
Date Received: 7/28/2017 10:07:00 AM
Sampler: GP
Units
mg/L
mg/L
Matrix: Water
COC: 172070
Date Analyzed/lnit
07/28/2017 1117 NLG
07/28/20171100 IBS
Method
SM 2540
SM 2540
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 O Outside the Range of Dilutions
S Spike Recovery outside accepted recovery limits X Matrix Effect
A ] _,1,.,...? <"' Reviewed by: vf./P" '---Page 1 of 1 Wade Nieuwsma, Assistant Laboratory Manager
Your Environmental Monitoring Partner ,,,l~M--..::,1::
· Inter-Mountain Labs----------------------------------------
lHTrn .. MaUHTAIH LAD5 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT: Energy Fuels (White Mesa) Date: 8/15/2017
Work Order: S1707426 Report ID: S1707426001
Project: 3rd Q. Surface Water-17
Solids By SM 2540 Sample Type MBLK Units: mg/L
DI 1(07/28/1710:52) RunNo: 148593
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Suspended Solids ND 5
DI (07/28/17 10:54) RunNo: 148766
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Dissolved Solids (180) ND 10
Solids By SM 2540 Sample Type LCS Units: mg/L
LCS (07/28/17 10:50) RunNo: 148593
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Suspended Solids 106 5 100 106 90 -110
CONTROL (07/28/17 10:55) RunNo: 148766
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Dissolved Solids (180) 230 10 226 101 90 -110
Solids By SM 2540 Sample Type DUP Units: mg/L
S1707426-001A (07/28/17 11:02) RunNo: 148593
Analyte Result RL Ref Samp %RPO %REC % RPO Limits Qual
Total Suspended Solids 12400 5 11300 9.68 20
S1707424-007A (07/28/17 11 :16) RunNo: 148766
Analyte Result RL Ref Samp %RPO %REC % RPO Limits Qual
Total Dissolved Solids (180) 440 10 430 1.37 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 1
ATTACHMENT I
SOIL SAMPLE GRAPHS, DATA TABLE, LABORATORY RESULTS AND QA/QC
·e 0 !
11 12 07 oa DU BHV-2 10 11 •
13 18 17 16 15 14
14
w w .... N N-~ 0::
N01 NO> N03 N04 NI 15
24 19 20 ~ \. \ 21 \ jsHV-1 22 23
23 E01 • j
W01 "' irv. n , -., ' E02
BH -8 ;, --::EO.>
W02 "u ,.--
W03 ~ BHV-il ' E04 fl"' E05
25 30 2$ 1n ,. 17 2G
26 E06 W04 .
~ E07
BHV:' E08 -
v\(05 " ~ E09
W,06-E10
BHV. 35 36 31 W07 32 33 ... E11 35
W09 wor ~ BHV-6 ~~ E12
" "' • BHV-4 T37S
,... ,.. T38S E13 .,.; .. . .---
W10
01 on us 04 ~~ 02
oa 14 ,....,, Enengy Fuels Resources (USA) Inc. ,
W11 '
~ :/ ~ W12 I I
W13 W14 11
11 12 07 W15-oa ""/ •
09 ,f--
6
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/~ • .::::=E17 '\
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17 ---
16 ~~ 15 N
W18 E18
1 l~r -MILEc --
I T \ ~
1 0.5 1 S01 S02 S03
I 2J I ,,,
Legend
Proposed Soil Monitoring Location * 1,000 Feet * 2,500 Feet + Air Monitoring Station
=Property Boundary
--Road
0 Township and Range
D section
rv iles 19
Coordinate System: NAO
1983 StatePlane Utah
South FIPS 4303 Feet
20 21 22 2/
'{!'J,I!
"-~NERGYFUELS
REVISIONS Project: WHITE MESA MILL
Date: By: County: San Juan Staie: Utah
Location:.
FIGURE 1-1
SOIL MONITORING LOCATIONS
Author: rellis Date: 2/20/2017 Drafted By: rellis
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...... Oct-16
:::,
(J1 --,i m
t -Nov-16 o· :::,
r;n U)
...... Dec-16 0) :::,
l en
Jan-17 0 -r;n "'C ...... Feb-17 0 ...... ~ f Mar-17 -
m ~ Apr-17
May-17
Jun-17
Jul-17
Aug-17
L~-6ny
n-1nr
n-unr
H-Aelfll
0) 0 I
H-Jdy 3: f -L~-Jelfll ~ 0 co 0 I a. L ~-qa.:J 3: --{ ·s L~-uer en
C I'--0
1/) g~-oaa I
C 3:
0 t ·..::; g~-AON m ~ ~ <D C 9~-PO 0 G) I
(.) 3:
C g~-das + 0 0
0 g~-5ny l() ,.. 0 N I
I 3: J:l C. 9~-1nr + -a,
0 g~-unr "<t' I 3: 0 I
9 ~-ABll'J 3: ,.. + 0 I 3: 9 ~-Jdy -C")
~ 0 I 1/) g ~-Jelfll 3: G)
3: + g~-qa.:J
C\J 0 I g~-uer 3:
s~-oaa + ....
S~-AON 0 I 3:
S~-PO +
g~-das
s~-5ny
0 0 0 0 0 0 0 0 I.{) 0 ~ ~ I.{) 0
Ct) C\J C\i .... .... ci ci
L~-onv
n-1nr
n-unr
H-A'BV\I
CX) ,....
I
L ~-JdV ~
f -L ~ -JBV\I ~ 0 r---,....
C. n-qa.::1 ~ -f ·5 L~-uer en
C co
g~-oaa ,....
,n I ~ C t 0 ·.;::; g~-AON cu ... -LO C 9~-PO ,....
G) ~ (.)
C g~-das + 0 0
0 g~-onv """ ,.... ,.... N I
I ~ Jl 9 ~-1nr + CL. -co ,.... 9~-unr (') I 3= ,....
~
0 9 ~-ABV\I
+ ,....
I 3= 9 ~-JdV -C\I -,....
,n 9 ~-JBV\I ~ G)
3= + 9~-qa.::1 ,.... ,....
I g~-uer ~
s~-oaa +
0 ,.... S~-AON I ~
S~-PO +
s~-das
s~-onv
0 0 0 0 0 0 0 0 ~ "! ~ a:> co """ C\I 0 ,.... ,.... ,.... c:i c:i c:i c:i c:i
9 0 0 0 0 0
0 _. i\:, w :i:,... (J'1 O>
t Aug-15
Sep-15
Oct-15
~ Nov-15
~I Dec-15 -;:: _.
+I Jan-16
Feb-16 CD I
Mar-16 1 I \l I I"\ I I I m < I\) ::::c <
+ Apr-16 -I :::r I
CD I\)
I w
< May-16 I\)
I (") (,)
0 Jun-16
+
::::,
()
C1)
CD Jul-16 ::::, -I ..,
< D)
I !:!". .i,.. Aug-16
I
0
+
::::,
UI
Sep-16 ::::,
CD en I < Oct-16 2. I 01 -
+ Nov-16 i
I I y I I I V I I
"C
(")
(ff
CD -I Dec-16 < 0)
I Jan-17
t i CD Feb-17
I
t 1 Mar-17
l 1 Apr-17
CD !I May-17
Jun-17
Jul-17
Aug-17
0 9 0 9 0 0 0 0 0 ...... i\, c.:, ~ 01 C7) :....i 0 0 0 0 0 0 0 0
Aug-15
Sep-15
Oct-15
+I Nov-15
?I Dec-15
0 .....
I Jan-16
+ Feb-16 z
Mar-161 I /~ I I\ V I\ I I I z 6 I\) 0 ::s. ':S'
+ Apr-16 I» :,
Q. z May-16 en ' 0 0 w C -Jun-16 ':S'
+ -I ':S'
z Jul-16 a{,
~ c,.)
~ Aug-16 0
+
0
Sep-16
:::, n C1I z :,
6 Oct-16 -""I (JI ~
Nov-16 0
+
:, u, -en Dec-16 :,
6 en ..... 2. Jan-17 -
t -"C
Feb-17 0 i::::.: en cc ' 0 -I\) Mar-17
t Apr-17
en
21 May-17
Jun-17
Jul-17
Aug-17
0 0 0 0 ~ ...... ...... ......
0 i\J :i:,. 0) 0) 0 i\J :i:,.
0 0 0 0 0 0 0 0
Aug-15
Sep-15
Oct-15
+; Nov-15 m I 0
...... 1 Dec-15
+1 Jan-16 m 6 I\) Feb-16
+
\
m
Mar-16 1 D> Ch m -I -0 m (.u Apr-16 I 0
+
....
May-16 m m I 6 Jun-16 0 .j:>. U) -
+
-I
Jul-16 :::T I N m w I 0 Aug-16 N 01 0
+
0
Sep-16 :::I
(')
m C'D
I :::I 0 Oct-16 -0) ""I D>
t ::::!':.
Nov-16 0 :::I
m Ch
I -0 Dec-16 :::I -..J
t en
Jan-17 0 -m "C 6 Feb-17 0 00 (if
f -Mar-17
m !J Apr-17
May-17
Jun-17
Jul-17
Aug-17
0 ? 0 0 0 ? 0
0 _.. i-1:> Cl.) :i::,. (11 0)
0 0 0 0 0 0 0
Aug-15
Sep-15
Oct-15
+; Nov-15 r;n _.. 01 Dec-15
+1 Jan-16
m I ...... ...... Feb-16
+ I\ I\ I m
Mar-16 1 m en r;n -...... -I\) Apr-16 m
I .....
+
0
May-16 m r;n I ...... .....
w Jun-16 Q) -
+
-I
Jul-16 :::r I I\) r;n w ...... Aug-16 I\)
.I>, 0
+
0
Sep-16 :::, n
r;n (1)
...... Oct-16
:::,
01 -"'I m
t ::::!'.
Nov-16 0 :::,
r;n en
...... Dec-16 :::, 0)
t
CJ)
Jan-17 2. -r;n "C ...... Feb-17 0 --.J :ti t Mar-17 -
m ~ Apr-17
May-17
Jun-17
Jul-17
Aug-17
L~-5nv
u-1nr
u-unr
H-A"eV'J 0) 0
L ~-JdV 3:
-H-JBV'J .E:> i:3 Q. L ~-qa.:1 -·s L ~-uer C/'J
C ,....
9~-oaa 0
,n 3: C: t 0 ·..= 9~-AON cu lo. -<D C 9~-PO 0
Cl) I
(,) ~
C: 9~-das + 0 0
C\I g~-5nv IO CW) 0 C\I .
I ~ s:. 9~-1nr + I--a,
0 9~-unr '<t I ;:: 0 I
I 9 ~-ABV'J ~ ,... + 9 ;:: 9 ~-JdV -C') -0 ' ,n 9 ~ -JBV',J ~ Cl) ;:: + 9~-qa.:1
C\I 0 I g ~-uer ~
g~-oaa + ....
g ~-AON 0 3:
g~-PO +
g~-das
g~-5nv
0 0 0 0 0 0 0
<D I.() -.:I" C') C\J ~ 0
0 ci 0 ci ci ci ci
L ~ -Bnv
H-1nr
H-unr
L ~-ABl,I\J
CX) ,....
H-Jd'v' ~
f -L ~-JBl,I\J ~ f',.. 0 ,....
I
C. H-qa.:1 s -f 0 L~-uer en
C co
g~-:)ao ,....
en ~ C t 0 ; g~-/\ON
C'CS ... -l{) C 9~-PO ,....
CL) I
(.) s
C g~-das + 0 0
N g ~ -Bnv '<I" C") ,....
N ~ I .c 9~-1nr + I--co ,.... g~-unr I (')
==
,....
I
9 ~-ABl,I\J s
0 + ,....
I
==
9 ~ -Jd'v' -C\J -,....
en 9 ~-JBl,I\J ~ CL)
== + g ~-qa.:1
,.... ,....
g~-uer ~
s ~-:)ao +
0
9~-AON ,....
~
9~-PO +
s~-das
s ~ -Bnv
0 0 0 0 0 0 0 co l!) '<I" Cl) "! ,.... 0
ci ci ci ci 0 ci ci
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 866.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
October 16, 2017
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C17080550
Project Name: Not Indicated
Energy Laboratories, Inc. Casper WY received the following 56 samples for Energy Fuels Resources (USA) Inc on 8/14/2017
for analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C 17080550-001 N01 08/08/17 08:20 08/14/17 Soil Metals by ICP/ICPMS, Total
Moisture
Percent Moisture
Digestion, Total Metals
Digestion For RadioChemistry
Lead 210
Radium 226
Thorium, Isotopic
C 17080550-002 N02 08/08/17 09:01 08/14/17 Soil Same As Above
C17080550-003 N03 08/08/17 09:08 08/14/17 Soil Same As Above
C 17080550-004 N04 08/08/17 09:22 08/14/17 Soil Same As Above
C 17080550-005 N05 08/08/17 09:26 08/14/17 Soil Same As Above
C 17080550-006 E01 08/08/17 09:35 08/14/17 Soil Same As Above
C 17080550-007 E02 08/08/17 09:42 08/14/17 Soil Same As Above
C 17080550-008 E03 08/08/17 09:4 7 08/14/17 Soil Same As Above
C 17080550-009 E04 08/08/17 09:51 08/14/17 Soil Same As Above
C17080550-010 E05 08/08/17 10:01 08/14/17 Soil Same As Above
C 17080550-011 E06 08/08/17 10:06 08/14/17 Soil Same As Above
C 17080550-012 E07 08/08/17 10: 11 08/14/17 Soil Same As Above
C 17080550-013 E08 08/08/17 10:27 08/14/17 Soil Same As Above
C 17080550-014 E09 08/08/17 10:43 08/14/17 Soil Same As Above
C 17080550-015 E10 08/08/17 10:37 08/14/17 Soil Same As Above
C 17080550-016 E11 08/08/17 10:49 08/14/17 Soil Same As Above
C17080550-017 E12 08/08/17 10:59 08/14/17 Soil Same As Above
C 17080550-018 E13 08/08/17 14:26 08/14/17 Soil Same As Above
C17080550-019 E14 08/08/17 14:46 08/14/17 Soil Same As Above
C 17080550-020 E15 08/08/1714:38 08/14/17 Soil Same As Above
C17080550-021 E16 08/09/17 08:26 08/14/17 Soil Same As Above
C 17080550-022 E17 08/09/17 08:35 08/14/17 Soil Same As Above
C 17080550-023 E18 08/09/17 08:39 08/14/17 Soil Same As Above
Page 1 of 77
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 866.686.7175 • Helena, MT 877.472.07 1
ANALYTICAL SUMMARY REPORT
C 17080550-024 S01 08/09/17 09:29 08/14/17 Soil Same As Above
C 17080550-025 S02 08/09/17 09:40 08/14/17 Soil Same As Above
C 17080550-026 S03 08/09/17 08:47 08/14/17 Soil Same As Above
C17080550-027 W01 08/08/17 08:28 08/14/17 Soil Same As Above
C 17080550-028 W02 08/08/17 08:35 08/14/17 Soil Same As Above
C 17080550-029 W03 08/08/17 08:45 08/14/17 Soil Same As Above
C 17080550-030 W04 08/08/17 08:50 08/14/17 Soil Same As Above
C 17080550-031 W05 08/09/17 12:36 08/14/17 Soil Same As Above
C 17080550-032 W06 08/09/17 12:29 08/14/17 Soil Same As Above
C 17080550-033 WO? 08/09/17 12:42 08/14/17 Soil Same As Above
C 17080550-034 W08 08/09/17 12:45 08/14/17 Soil Same As Above
C 17080550-035 W09 08/09/17 12 :49 08/14/17 Soil Same As Above
C 17080550-036 W10 08/09/17 12:53 08/14/17 Soil Same As Above
C 17080550-037 W11 08/09/17 12:56 08/14/17 Soil Same As Above
C 17080550-038 W12 08/09/17 13:00 08/14/17 Soil Same As Above
C 17080550-039 W13 08/09/17 13:09 08/14/17 Soil Same As Above
C 17080550-040 W14 08/09/17 13:22 08/14/17 Soil Same As Above
C 17080550-041 W15 08/09/17 10:01 08/14/17 Soil Same As Above
C 17080550-042 W16 08/09/17 19: 10 08/14/17 Soil Same As Above
C17080550-043 W17 08/09/17 19: 16 08/14/17 Soil Same As Above
C 17080550-044 W18 08/09/17 09:22 08/14/17 Soil Same As Above
C 17080550-045 E65 08/08/17 14:26 08/14/17 Soil Same As Above
C 17080550-046 W70 08/09/17 09: 10 08/14/17 Soil Same As Above
C 17080550-04 7 S75 08/09/17 09:40 08/14/17 Soil Same As Above
C 17080550-048 West Water Creek 08/09/17 12: 19 08/14/17 Soil Same As Above
C 17080550-049 BHV-1 08/08/17 09:30 08/14/17 Soil Same As Above
C17080550-050 BHV-2 08/08/17 13:55 08/14/17 Soil Same As Above
C17080550-051 BHV-3 08/08/17 12:40 08/14/17 Soil Same As Above
C 17080550-052 BHV-4 08/08/17 14: 10 08/14/17 Soil Same As Above
C 17080550-053 BHV-5 08/08/1710:31 08/14/17 Soil Same As Above
C 17080550-054 BHV-6 08/08/17 10:53 08/14/17 Soil Same As Above
C 17080550-055 BHV-7 08/08/17 09:56 08/14/17 Soil Same As Above
C 17080550-056 BHV-8 08/08/17 09: 15 08/14/17 Soil Same As Above
The results as reported relate only to the item(s) submitted for testing. The analyses presented in this report were
performed at Energy Laboratories, Inc., 2393 Salt Creek Hwy., Casper, WY 82601, unless otherwise noted. Any
exceptions or problems with the analyses are noted in the Laboratory Analytical Report, the QA/QC Summary
Report, or the Case Narrative.
Page 2 of 77
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Blllln1s, MT 800.735.4489 • Casper, WY 888.235.051
GIiiette, WY 888.888. 7175 • Helena, MT 871.472.071
ANALYTICAL SUMMARY REPORT
If you have any questions regarding these test results, please call.
Report Approved By: rl~~ Project Manager
Digitally signed by
Tessa Parke
Date: 2017.10.17 12:55:13 -06:00
Page 3 of 77
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WV 866.686.7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
Not Indicated
C17080550
ORIGINAL SAMPLE SUBMITIAL(S)
All original sample submittals have been returned with the data package.
SAMPLE TEMPERATURE COMPLIANCE: 4°C (±2°C)
Report Date: 10/16/17
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
CERTIFICATIONS:
USEPA: WY00002; FL-DOH NELAC: E87641; Oregon: WY200001 ; Utah: WY00002; Washington: C1012
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 4 of77
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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: Not Indicated
Lab ID: C17080550-001
Client Sample ID: N01
Analyses
PHYSICAL CHARACTERISTICS
Moisture
METALS,TOTAL
Uranium
RADIONUCLIDE$
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
5.0 wt%
ND mg/kg-dry
1.8 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
0.4 pCi/g-dry
0.07 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 08:20
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:16 / eli-b
E909.0 09/13/17 05:42 / plj
E909.0 09/13/17 05:42 / plj
E909.0 09/13/17 05:42 I plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/1715:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 5 of 77
EN:RGY
I •
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: Not Indicated
Lab ID: C 17080550-002
Client Sample ID: N02
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 -Anaiyte reporting limit.
QCL -Quality control limit.
Result Units
5.3 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.7 pCi/g-dry
0.2 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: 10/16/17
Collection Date: 08/08/17 09:01
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05: 19 / eli-b
E909.0 09/13/17 07:16 / plj
E909.0 09/13/17 07: 16 / plj
E909.0 09/13/17 07: 16 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15: 55 / dmf
E908.0 09/18/17 15: 55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 77
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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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-003
N03
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
5.0 wt%
mg/kg-dry
1.3 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.9 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 09:08
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:22 I eli-b
E909.0 09/13/17 11 :35 / plj
E909.0 09/13/17 11 :35 / plj
E909.0 09/13/17 11 :35 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 I dmf
E908.0 09/18/17 15:55 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 77
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-004
Client Sample ID: N04
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
5.1 wt%
mg/kg-dry
1.4 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
pCi/g-dry
0.2 pCi/g-dry
0.04 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: 10/16/17
Collection Date: 08/08/17 09:22
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:24 / eli-b
E909.0 09/13/17 13:22 / plj
E909.0 09/13/17 13:22 / plj
E909.0 09/13/17 13:22 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 8 of 77
EN:RGY ;
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: Not Indicated
Lab ID: C17080550-005
Client Sample ID: NOS
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
5.3 wt%
ND mg/kg-dry
0.6 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.4 pCi/g-dry
0.07 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 09:26
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:27 I eli-b
E909.0 09/13/17 15:07 / plj
E909.0 09/13/17 15:07 / plj
E909.0 09/13/17 15:07 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 9 of 77
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: Not Indicated
Lab ID: C 17080550-006
Client Sample ID: E01
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
5.3 wt%
4 mg/kg-dry
2.7 pCi/g-dry
0.8 pCi/g-dry
0.4 pCi/g-dry
3.2 pCi/g-dry
0.6 pCi/g-dry
0.04 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: 10/16/17
Collection Date: 08/08/17 09:35
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/26/17 05:37 I eli-b
E909.0 09/13/17 17:21 / plj
E909.0 09/13/17 17:21 / plj
E909.0 09/13/17 17:21 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E9080 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15: 55 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 77
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
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-007
Client Sample ID: E02
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
5.3 wt%
3 mg/kg-dry
1.6 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
1.9 pCi/g-dry
0.4 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
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 09:42
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:40 I eli-b
E909.0 09/13/17 18:38 / plj
E909.0 09/13/17 18:38 / plj
E909.0 09/13/17 18:38 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 11 of 77
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-008
Client Sample ID: E03
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
3.7 wt%
2 mg/kg-dry
1.6 pCi/g-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
1.6 pCi/g-dry
0.3 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 09:4 7
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:43 / eli-b
E909.0 09/13/17 20: 18 / plj
E909.0 09/13/17 20: 18 / plj
E909.0 09/13/17 20: 18 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 12 of 77
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: Not Indicated
Lab ID: C 17080550-009
Client Sample ID: E04
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
4.2 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
0.04 pCi/g-dry
0.07 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: 10/16/17
Collection Date: 08/08/17 09:51
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:45 / eli-b
E909.0 09/13/17 21 :59 / plj
E909.0 09/13/17 21:59 / plj
E909.0 09/13/17 21:59 / plj
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E903.0 09/05/17 08:33 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 13 of 77
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 877.4 72.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-010
Client Sample ID: E05
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
5.2 wt%
4 mg/kg-dry
2.3 pCi/g-dry
0.7 pCi/g-dry
0.4 pCi/g-dry
2.3 pCi/g-dry
0.5 pCi/g-dry
0.04 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: 10/16/17
Collection Date: 08/08/17 10:01
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:48 / eli-b
E909.0 09/13/17 23:38 / plj
E909.0 09/13/17 23:38 / plj
E909.0 09/13/17 23:38 / plj
E903.0 09/05/17 08:34 / dmf
E903.0 09/05/17 08:34 / dmf
E903.0 09/05/17 08:34 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15: 55 I dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 14 of 77
EI\ERG Y •' 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: Not Indicated
Lab ID: C17080550-011
Client Sample ID: E06
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
3.3 wt%
4 mg/kg-dry
2.4 pCi/g-dry
0.8 pCi/g-dry
0.4 pCi/g-dry
3.0 pCi/g-dry
0.6 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: 10/16/17
Collection Date: 08/08/17 10:06
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:50 I eli-b
E909.0 09/14/17 01:01 / plj
E909.0 09/14/17 01 :01 / plj
E909.0 09/14/1701 :01 / plj
E903.0 09/05/17 08:34 / dmf
E903.0 09/05/17 08:34 / dmf
E903.0 09/05/17 08:34 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15: 55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 15 of 77
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: Not Indicated
Lab ID: C17080550-012
Client Sample ID: E07
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
5.6 wt%
3 mg/kg-dry
2.9 pCi/g-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
2.7 pCi/g-dry
0.6 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/08/17 10: 11
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:53 / eli-b
E909.0 09/14/17 15:30 / plj
E909.0 09/14/17 15:30 / plj
E909.0 09/14/17 15:30 / plj
E903.0 10/11/17 12:30 / trs
E903.0 10/11 /17 12:30 / trs
E903.0 10/11/1712:30/trs
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 16 of 77
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-013
E08
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
3.9 wt%
6 mg/kg-dry
2.7 pCi/g-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
4.7 pCi/g-dry
0.9 pCi/g-dry
0.1 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
Report Date: 10/16/17
Collection Date: 08/08/17 10:27
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/26/17 05:56 I eli-b
E909.0 09/14/17 16:46 / plj
E909.0 09/14/17 16:46 / plj
E909.0 09/14/17 16:46 / plj
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 17 of 77
EI\ERGY r 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: Not Indicated
Lab ID: C 17080550-014
Client Sample ID: E09
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
4.0 wt%
5 mg/kg-dry
2.4 pCi/g-dry
0.8 pCi/g-dry
0.4 pCi/g-dry
4.4 pCi/g-dry
0.9 pCi/g-dry
0.1 pCi/g-dry
1.3 pCi/g-dry
0.3 pCi/g-dry
0.8 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 10:43
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 05:58 / eli-b
E909.0 09/14/17 19:49 / plj
E909.0 09/14/17 19:49 / plj
E909.0 09/14/17 19:49 / plj
E903.0 10/11/1712:16/trs
E903.0 10/11/1712:16/trs
E903.0 10/11/1712:16 /trs
E908.0 09/18/17 15: 55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15: 55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of 77
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: Not Indicated
Lab ID: C17080550-015
Client Sample ID: E10
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
4.3 wt%
5 mg/kg-dry
2.2 pCi/g-dry
0.7 pCi/g-dry
0.4 pCi/g-dry
3.0 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.3 pCi/g-dry
0.05 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 10:37
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/26/17 06:01 / eli-b
E909.0 09/14/17 21:10 / plj
E909.0 09/14/1721:10 / plj
E909.0 09/14/17 21:10 / plj
E903.0 10/11/17 12:16 / trs
E903.0 10/11 /17 12: 16 / trs
E903.0 10/11 /17 12: 16 / trs
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15: 55 I dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of 77
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: Not Indicated
Lab ID: C 17080550-016
Client Sample ID: E11
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
4.3 wt%
2 mg/kg-dry
1.4 pCi/g-dry
0.5 pCi/g-dry
0.4 pCi/g-dry
1.9 pCi/g-dry
0.4 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/08/17 10:49
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 19:52 / eli-b
E909.0 09/14/17 22:39 / plj
E909.0 09/14/17 22:39 / plj
E909.0 09/14/17 22:39 / plj
E903.0 10/11/1712:16 /trs
E903.0 10/11/1712:16 / trs
E903.0 10/11/17 12:16 / trs
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 20 of 77
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C17080550-017
Client Sample ID: E12
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
3.9 wt%
ND mg/kg-dry
pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
1.7 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.4 pCi/g-dry
0.08 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 10:59
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 19:54 / eli-b
E909.0 09/15/17 00:24 / plj
E909.0 09/15/17 00:24 / plj
E909.0 09/15/17 00:24 I plj
E903.0 10/11/1712:16/trs
E903.0 10/11/1712:16/trs
E903.0 10/11/17 12:16 / trs
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
E908.0 09/18/17 15:55 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 21 of77
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: Not Indicated
Lab ID: C 17080550-018
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
5.4 wt%
ND mg/kg-dry
1.7 pCi/g-dry
0.6 pCi/g-dry
0.4 pCi/g-dry
1.9 pCi/g-dry
0.4 pCi/g-dry
0.1 pCilg-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: 10/16/17
Collection Date: 08/08/17 14:26
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08125117 11 :46 I eli-b
SW6020 08/29/17 19:57 / eli-b
E909.0 09/15/17 02:22 I plj
E909.0 09/15/17 02:22 I plj
E909.0 09115/17 02:22 I plj
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E903.0 10111/17 12:16 / trs
E908.0 09119117 18:53 / cng
E908.0 09/19117 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of 77
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: Not Indicated
Lab ID: C 17080550-019
Client Sample ID: E14
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
4.3 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
1.9 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.5 pCi/g-dry
0.09 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
1
Report Date: 10/16/17
Collection Date: 08/08/17 14:46
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 19:59 / eli-b
E909.0 09/15/17 03:59 / plj
E909.0 09/15/17 03:59 / plj
E909.0 09/15/17 03:59 / plj
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E903.0 10/11 /17 12: 16 / trs
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 23 of 77
EI\ERGY Trust our People. Trust our Data.
www.energylab.mm
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-020
Client Sample ID: E15
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
1.7 wt%
ND mg/kg-dry
1.5 pCi/g-dry
0.5 pCi/g-dry
0.4 pCi/g-dry
1.6 pCi/g-dry
0.4 pCi/g-dry
0.1 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 14:38
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:02 I eli-b
E909.0 09/15/17 05:51 / plj
E909.0 09/15/17 05:51 / plj
E909.0 09/15/17 05:51 / plj
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E903.0 10/11/17 12:16 / trs
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 24 of 77
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-021
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
1.5 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
1.4 pCi/g-dry
0.3 pCi/g-dry
0. 1 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 08:26
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 20:05 I eli-b
E909.0 09/15/17 07:33 / plj
E909.0 09/15/17 07:33 / plj
E909.0 09/15/17 07:33 / plj
E903.0 10/11/1712:16/trs
E903.0 10/11/1712:16 / trs
E903.0 10/11/17 12:16 / trs
E908.0 09/19/17 18: 53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 25 of 77
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: Not Indicated
Lab ID: C 17080550-022
Client Sample ID: E17
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
3.0 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.8 pCi/g-dry
0.2 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 08:35
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 20:07 I eli-b
E909.0 09/15/17 09:32 I plj
E909.0 09/15/17 09:32 I plj
E909.0 09/15/17 09:32 I plj
E903.0 10/11 /17 15:34 / trs
E903.0 10/11/1715:34/trs
E903.0 10/11/17 15:34 / trs
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18: 53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 26 of 77
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: Not Indicated
Lab ID: C 17080550-023
Client Sample ID: E18
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
2.6 wt%
ND mg/kg-dry
0.8 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.7 pCi/g-dry
0.2 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/09/17 08:39
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:10 I eli-b
E909.0 09/15/17 11 :26 I plj
E909.0 09/15/17 11 :26 / plj
E909.0 09/15/17 11 :26 / plj
E903.0 10/11/17 15:34 / trs
E903.0 10/11/17 15:34 / trs
E903.0 10/11/17 15:34 / trs
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 27 of 77
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-024
S01
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
1.0 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.7 pCi/g-dry
0.2 pCi/g-dry
0.1 pCi/g-dry
0.4 pCi/g-dry
0.07 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 09:29
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20: 13 / eli-b
E909.0 09/15/17 13:32 / plj
E909.0 09/15/17 13:32 / plj
E909.0 09/15/17 13:32 / plj
E903.0 10/11/17 15:34 / trs
E903.0 10/11/17 15:34 / trs
E903.0 10/11/17 15:34 / trs
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 28 of 77
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: Not Indicated
Lab ID: C 17080550-025
Client Sample ID: S02
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
4.4 wt%
2 mg/kg-dry
0.8 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.8 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 09:40
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 20:23 / eli-b
E909.0 10/12/17 00:46 / meh
E909.0 10/12/17 00:46 / meh
E909.0 10/12/17 00:46 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 I dmf
E903.0 09/18/17 09:35 I dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 29 of 77
EI\ERGY Tn.ist 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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-026
S03
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
3.8 wt%
ND mg/kg-dry
1.0 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.03 pCi/g-dry
0.07 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: 10/16/17
Collection Date: 08/09/17 08:47
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:26 I eli-b
E909.0 10/12/17 05:28 I meh
E909.0 10/12/17 05:28 I meh
E909.0 10/12/17 05:28 / meh
E903.0 09/18/17 09:35 I dmf
E903.0 09/18/17 09: 35 / dmf
E903.0 09/18/17 09:35 I dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 30 of 77
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: Not Indicated
Lab ID: C 17080550-027
Client Sample ID: W01
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
5.4 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/08/17 08:28
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:28 I eli-b
E909.0 10/12/17 07:32 / meh
E909.0 10/12/17 07:32 / meh
E909.0 10/12/17 07:32 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09: 35 / dmf
E903.0 09/18/17 09: 35 / dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 31 of 77
EN:RGY Trust our People. Trust our Data.
www.energylah.mm
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-028
W02
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
5.8 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
1
Report Date: 10/16/17
Collection Date: 08/08/17 08:35
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:31 / eli-b
E909.0 10/12/17 09:32 I meh
E909.0 10/12/17 09:32 I meh
E909.0 10/12/17 09:32 I meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 32 of 77
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: Not Indicated
Lab ID: C 17080550-029
Client Sample ID: W03
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
5.8 wt%
mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.7 pCi/g-dry
0.2 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/08/17 08:45
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:34 I eli-b
E909.0 10/12/17 11:38 / meh
E909.0 10/12/17 11:38 / meh
E909.0 10/12/1711 :38 / meh
E903.0 09/18/17 09:35 I dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 33 of 77
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: Not Indicated
Lab ID: C 17080550-030
Client Sample ID: W04
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
7.1 wt%
mg/kg-dry
1.6 pCi/g-dry
0.5 pCi/g-dry
0.4 pCi/g-dry
0.9 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.08 pCi/g-dry
0.02 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 08:50
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 20:36 / eli-b
E909.0 10/12/17 13:39 / meh
E909.0 10/12/17 13:39 / meh
E909.0 10/12/17 13:39 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09: 35 / dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 34 of 77
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: Not Indicated
Lab ID: C 17080550-031
Client Sample ID: W05
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
6.4 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.03 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/09/17 12:36
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:39 I eli-b
E909.0 10/12/17 15:26 / meh
E909.0 10/12/17 15:26 / meh
E909.0 10/12/17 15:26 / meh
E903.0 09/18/17 09:35 I dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/19/17 18: 53 I cng
E908.0 09/19/17 18: 53 I cng
E908.0 09/19/17 18: 53 I cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 35 of 77
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
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-032
W06
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
2.5 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.08 pCi/g-dry
0.03 pCi/g-dry
0.08 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: 10/16/17
Collection Date: 08/09/17 12:29
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:41 I eli-b
E909.0 10/12/17 17:32 I meh
E909.0 10/12/17 17:32 / meh
E909.0 10/12/17 17:32 I meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18:53 / cng
E908.0 09/19/17 18: 53 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 36 of 77
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
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-033
Client Sample ID: WO?
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
4.7 wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.03 pCi/g-dry
0.4 pCi/g-dry
0.08 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 12:42
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:44 I eli-b
E909.0 10/12/17 19:41 / meh
E909.0 10/12/17 19:41 / meh
E909.0 10/12/17 19:41 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 I dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/20/17 10:23 / cng
E908.0 09/20/17 10:23 / cng
E908.0 09/20/17 10:23 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 37 of 77
Er\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 ANAL YT I CAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-034
woa
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
2.8 wt%
ND mg/kg-dry
0.8 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
O.D7 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/09/17 12:45
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 20:47 / eli-b
E909.0 10/12/17 21 :55 / meh
E909.0 10/12/17 21 :55 / meh
E909.0 10/12/17 21 :55 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/1 B/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/20/17 10:23 / cng
E90B.O 09/20/17 10:23 / cng
E908.0 09/20/17 10:23 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 38 of 77
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-035
W09
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
4.0 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/09/17 12:49
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 20:57 I eli-b
E909.0 10/13/17 00:06 I meh
E909.0 10/13/17 00:06 / meh
E909.0 10/13/17 00:06 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/21/1711:41 / cng
E908.0 09/21 /17 11 :41 / cng
E908.0 09/21/1711:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 39 of 77
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: Not Indicated
Lab ID: C 17080550-036
Client Sample ID: W10
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
4.6 wt%
ND mg/kg-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/09/17 12:53
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 21 :20 I eli-b
E909.0 10/13/17 02:12 / meh
E909.0 10/13/17 02:12 / meh
E909.0 10/13/17 02:12 / meh
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E903.0 09/18/17 09:35 / dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 40 of 77
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: Not Indicated
Lab ID: C 17080550-037
Client Sample ID: W11
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
1.9 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.06 pCi/g-dry
0.03 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/09/17 12:56
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 I eli-b
SW6020 08/29/17 21 :31 / eli-b
E909.0 10/13/17 04:38 / meh
E909.0 10/13/17 04:38 / meh
E909.0 10/13/17 04:38 I meh
E903.0 09/18/1711 :18 / dmf
E903.0 09/18/1711:18 / dmf
E903.0 09/18/1711:18 /dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711:41 / cng
E908.0 09/21/17 11 :41 I cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 41 of 77
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-038
W12
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
2.5 wt%
ND mg/kg-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
0.05 pCi/g-dry
0.03 pCi/g-dry
0.05 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: 10/16/17
Collection Date: 08/09/17 13:00
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 21 :34 / eli-b
E909.0 10/13/17 06:38 / meh
E909.0 10/13/17 06:38 / meh
E909.0 10/13/17 06:38 / meh
E903.0 09/18/1711:18/dmf
E903.0 09/18/17 11 : 18 / dmf
E903.0 09/18/1711 :18/dmf
E908.0 09/21/17 11 :41 / cng
E908.0 09/21/17 11 :41 / cng
E908.0 09/21/1711:41 /cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 42 of 77
El'l: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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-039
W13
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
2.2 wt%
ND mg/kg-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/09/17 13:09
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/1721 :36 / eli-b
E909.0 10/13/17 08:58 I meh
E909.0 10/13/17 08:58 / meh
E909.0 10/13/17 08:58 / meh
E903.0 09/18/17 11 : 18 / dmf
E903.0 09/18/1711 :18 / dmf
E903.0 09/18/17 11 :18 / dmf
E908.0 09/21/17 11 :41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 43 of 77
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: Not Indicated
Lab ID: C 17080550-040
Client Sample ID: W14
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
2.4 wt%
ND mg/kg-dry
0.7 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.06 pCi/g-dry
O.Q3 pCi/g-dry
0.1 pCi/g-dry
0.02 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 13:22
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date I By
02974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 21:39 / eli-b
E909.0 09/19/17 04:28 I meh
E909.0 09/19/17 04:28 I meh
E909.0 09/19/17 04:28 / meh
E903.0 09/18/17 11:18 / dmf
E903.0 09/18/17 11 :18 / dmf
E903.0 09/18/1711:18 /dmf
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 44 of 77
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-041
Client Sample ID: W15
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
1.1 wt%
ND mg/kg-dry
1.3 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.07 pCi/g-dry
0.04 pCi/g-dry
0.1 pCi/g-dry
O.Q3 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 10:01
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/1721 :41 / eli-b
E909.0 09/19/17 06:44 I meh
E909.0 09/19/17 06:44 / meh
E909.0 09/19/17 06:44 I meh
E903.0 09/18/17 11: 18 / dmf
E903.0 09/18/17 11: 18 / dmf
E903.0 09/18/17 11:18 / dmf
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/17 11 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 45 of 77
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-042
W16
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
3.0 wt%
ND mg/kg-dry
1.2 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.09 pCi/g-dry
0.03 pCi/g-dry
0.4 pCi/g-dry
0.08 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 19: 10
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 21 :44 I eli-b
E909.0 09/19/17 11 :35 / meh
E909.0 09/19/17 11 :35 / meh
E909.0 09/19/17 11 :35 / meh
E903.0 09/18/17 11 :18 / dmf
E903.0 09/18/17 11 :18 / dmf
E903.0 09/18/17 11 :18 / dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/17 11 :41 / cng
E908.0 09/21/17 11 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 46 of 77
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: Not Indicated
Lab ID: C 17080550-043
Client Sample ID: W17
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
2.6 wt%
ND mg/kg-dry
0.5 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.03 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: 10/16/17
Collection Date: 08/09/1719:16
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/1721 :47 / eli-b
E909.0 09/19/17 13:31 / meh
E909.0 09/19/1713:31 / meh
E909.0 09/19/17 13:31 / meh
E903.0 09/18/17 11 : 18 / dmf
E903.0 09/18/17 11: 18 / dmf
E903.0 09/18/17 11 : 18 / dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711:41 /cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 47 of 77
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: Not Indicated
Lab ID: C17080550-044
Client Sample ID: W18
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%
ND mg/kg-dry
1.2 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.5 pCi/g-dry
0.1 pCi/g-dry
0.03 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 09:22
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/1721 :49 I eli-b
E909.0 09/19/17 15:59 / meh
E909.0 09/19/17 15:59 / meh
E909.0 09/19/17 15:59 / meh
E903.0 09/18/17 11 : 18 / dmf
E903.0 09/18/17 11: 1 B / dmf
E903.0 09/18/17 11:18 / dmf
E908.0 09/21/17 11 :41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/17 11:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 48 of 77
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
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-045
E65
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
5.4 wt%
ND mg/kg-dry
1.9 pCi/g-dry
0.6 pCi/g-dry
0,3 pCi/g-dry
1.0 pCi/g-dry
0.2 pCi/g-dry
0.03 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
1
Report Date: 10/16/17
Collection Date: 08/08/17 14:26
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/1721 :52 / eli-b
E909.0 09/19/17 17:55 / meh
E909.0 09/19/17 17:55 / meh
E909.0 09/19/17 17:55 / meh
E903.0 09/18/17 11: 18 / dmf
E903.0 09/18/17 11:18 / dmf
E903.0 09/18/1711:18 / dmf
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711:41 /cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 49 of 77
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: Not Indicated
Lab ID: C 17080550-046
Client Sample ID: W70
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
4.1 wt%
ND mg/kg-dry
1.1 pCi/g-dry
0.4 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.08 pCi/g-dry
O.Q3 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
Report Date: 10/16/17
Collection Date: 08/09/17 09: 10
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
02974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 21 :55 / eli-b
E909.0 09/19/17 19:31 / meh
E909.0 09/19/17 19:31 / meh
E909.0 09/19/17 19:31 / meh
E903.0 09/18/1711:18 /dmf
E903.0 09/18/17 11 : 18 / dmf
E903.0 09/18/17 11 : 18 / dmf
E908.0 09/21/1711:41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 50 of 77
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: Not Indicated
Lab ID: C 17080550-04 7
Client Sample ID: S75
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
4.1 wt%
2 mg/kg-dry
0.5 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.9 pCi/g-dry
0.2 pCi/g-dry
0.03 pCi/g-dry
0.6 pCit9-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/09/17 09:40
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 22:05 I eli-b
E909.0 09/20/17 22:36 / meh
E909.0 09/20/17 22:36 / meh
E909.0 09/20/17 22:36 I meh
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 / dmf
E908.0 09/21/17 11:41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 51 of 77
EI\ERG Y 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: Not Indicated
Lab ID: C 17080550-048
Client Sample ID: West Water Creek
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
2.6 wt%
ND mg/kg-dry
0.09 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.04 pCi/g-dry
-0.003 pCi/g-dry
0.06 pCi/g-dry
0.1 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
u
u
RL
0.2
MCU
Report Date: 10/16/17
Collection Date: 08/09/17 12:19
Date Received: 08/14/17
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
08/25/17 11 :46 / eli-b
08/29/17 22:08 I eli-b
09/21 /17 00:42 I meh
09/21 /17 00:42 I meh
09/21/17 00:42 / meh
09/18/17 08:49 / dmf
09/18/17 08:49 / dmf
09/18/17 08:49 I dmf
09/21/1711:41 / cng
09/21/1711:41 / cng
09/21/1711:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 52 of77
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-049
BHV-1
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
4.5 wt%
2 mg/kg-dry
2.1 pCi/g-dry
0.7 pCi/g-dry
0.4 pCi/g-dry
1.2 pCi/g-dry
0.2 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: 10/16/17
Collection Date: 08/08/17 09:30
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 22: 10 / eli-b
E909.0 09/21/17 05:55 / meh
E909.0 09/21/17 05:55 / meh
E909.0 09/21/17 05:55 / meh
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/17 11:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 53 of 77
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: Not Indicated
Lab ID: C 17080550-050
Client Sample ID: BHV-2
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
5.2 wt%
ND mg/kg-dry
0.9 pCi/g-dry
0.3 pCi/g-dry
0.4 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
0.2 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 13:55
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :46 / eli-b
SW6020 08/29/17 22: 13 / eli-b
E909.0 09/21/17 07:18 / meh
E909.0 09/21/17 07:18 / meh
E909.0 09/21 /17 07: 18 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/17 11:41 / cng
E908.0 09/21 /17 11 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 54 of 77
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: Not Indicated
Lab ID: C 17080550-051
Client Sample ID: BHV-3
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
3.0 wt%
ND mg/kg-dry
0.8 pCi/g-dry
0.3 pCi/g-dry
0.3 pCi/g-dry
0.2 pCi/g-dry
0.06 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: 10/16/17
Collection Date: 08/08/17 12:40
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/29/17 22: 16 / eli-b
E909.0 09/21/17 09:14 / meh
E909.0 09/21/17 09:14 / meh
E909.0 09/21/17 09:14 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711:41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 55 of 77
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: Not Indicated
Lab ID: C 17080550-052
Client Sample ID: BHV-4
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
2.5 wt%
ND mg/kg-dry
1.3 pCi/g-dry
0.5 pCi/g-dry
0.4 pCi/g-dry
0.7 pCi/g-dry
0.2 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: 10/16/17
Collection Date: 08/08/17 14:10
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/29/17 22: 18 / eli-b
E909.0 09/21/1711 :09 / meh
E909.0 09/21/17 11 :09 / meh
E909.0 09/21/1711 :09 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
E908.0 09/21/1711 :41 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 56 of 77
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:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-053
BHV-5
PHYSICAL CHARACTERISTICS
Moisture
METALS, TOT AL
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
3.8 wt%
5 mg/kg-dry
4.2 pCi/g-dry
1.3 pCi/g-dry
0.5 pCi/g-dry
3.6 pCi/g-dry
0.7 pCi/g-dry
0.04 pCi/g-dry
0.2 pCi/g-dry
0.04 pCi/g-dry
0.09 pCi/g-dry
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 10:31
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/29/17 22:21 I eli-b
E909.0 09/21/17 12:53 / meh
E909.0 09/21/17 12:53 / meh
E909.0 09/21/17 12:53 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 / dmf
E908.0 09/22/17 10:21 I cng
E908.0 09/22/17 10:21 I cng
E908.0 09/22/17 10:21 I cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 57 of 77
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 871.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project:
Lab ID:
Client Sample ID:
Analyses
Not Indicated
C 17080550-054
BHV-6
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
6.9 wt%
mg/kg-dry
0.6 pCi/g-dry
0.3 pCi/g-dry
0.4 pCi/g-dry
0.6 pCi/g-dry
0.1 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: 10/16/17
Collection Date: 08/08/17 10:53
Date Received: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/29/17 22:23 I eli-b
E909.0 09/21/17 13:52 / meh
E909.0 09/21/17 13:52 / meh
E909.0 09/21/17 13:52 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/25/17 09:51 I cng
E908.0 09/25/17 09:51 I cng
E908.0 09/25/17 09:51 / cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 58 of 77
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LAB ORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Lab ID: C 17080550-055
Client Sample ID: BHV-7
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
5.9 wt%
2 mg/kg-dry
0.8 pCi/g-dry
0.3 pCi/g-dry
0.4 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
MCL/
RL QCL
0.2
Report Date: 10/16/17
Collection Date: 08/08/17 09:56
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date I By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/29/17 22:26 I eli-b
E909.0 09/21/17 15:56 / meh
E909.0 09/21/17 15:56 / meh
E909.0 09/21 /17 15:56 / meh
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/25/17 09:51 I cng
E908.0 09/25/17 09:51 I cng
E908.0 09/25/17 09:51 I cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 59 of 77
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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: Not Indicated
Lab ID: C 17080550-056
Client Sample ID: BHV-8
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
5.8 wt%
ND mg/kg-dry
0.4 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
0.6 pCi/g-dry
0.1 pCi/g-dry
0.04 pCi/g-dry
0.08 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: 10/16/17
Collection Date: 08/08/17 09: 15
DateReceived: 08/14/17
Matrix: Soil
Method Analysis Date / By
D2974 08/25/17 11 :45 / eli-b
SW6020 08/30/17 18:41 / eli-b
E909.0 09/21/1717:54 / meh
E909.0 09/21 /17 17:54 I meh
E909.0 09/21 /17 17:54 I meh
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 / dmf
E903.0 09/18/17 08:49 I dmf
E908.0 09/25/17 09:51 / cng
E908.0 09/25/17 09:51 I cng
E908.0 09/25/17 09:51 I cng
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 60 of 77
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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 Billings, MT Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte Result Units
Method: D2974
Lab ID: C17080550-01 OBDUP Sample Duplicate
Moisture 5.12 wt%
Lab ID: C17080550-020BDUP Sample Duplicate
Moisture 1.69 wt%
Lab ID: C17080550-030BDUP Sample Duplicate
Moisture 6.99 wt%
Lab ID: C17080550-040BDUP Sample Duplicate
Moisture 2.43 wt%
Lab ID: C17080550-050BDUP Sample Duplicate
Moisture 5.23 wt%
Qualifiers:
RL -Anaiyte reporting limit.
Report Date:
Work Order:
RL %REC Low Limit High Limit RPD
Run: BAL HZW1_170825A
0.20 1.0
Run: BAL HZW1_170825A
0.20 1.2
Run: BAL HZW1_170825A
0.20 2.0
Run: BAL HZW1_ 170825A
0.20 0.0
Run: BAL HZW1 _170825A
0.20 0.2
ND -Not detected at the reporting limit.
08/31/17
C17080550
RPDLimit Qual
Batch: R285646
08/25/17 11 :46
30
08/25/17 11 :46
30
08/25/17 11 :46
30
08/25/17 11 :46
30
08/25/17 11 :46
30
Page 61 of 77
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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 Billings, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 08/31/17
Work Order: C 17080550 Project: Not Indicated
Analyte
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-112992
Uranium
Lab ID: C17080550-01 SBDIL
Uranium
Lab ID: C17080550-015BPDS1
Uranium
Lab ID: SRM3-112992
Uranium
Lab ID: C17080550-015BMS3
Uranium
Lab ID: C17080550-015BMSD3
Uranium
Qualifiers:
RL -Analyte reporting limit.
Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Initial Calibration Verification Standard
0.0217 mg/L 0.00030
Interference Check Sample A
0.0000200 mg/L 0.00030
Interference Check Sample AB
ND mg/L 0.00030
Method Blank
ND mg/kg 0.001
Serial Dilution
4.44 mg/kg-dry 1.0
Post Digestion/Distillation Spike
18.1 mg/kg-dry 1.0
Standard Reference Material
96.7 mg/kg 1.0
Sample Matrix Spike
57.7 mg/kg-dry 1.0
Sample Matrix Spike Duplicate
57.8 mg/kg-dry 1.0
108
102
97
103
103
90
Analytical Run: ICPMS202-B_ 170825A
08/25/17 11 :42
110
Run: ICPMS202-B_ 170825A
Run: ICPMS202-B_ 170825A
Run: ICPMS202-B_ 170825A
75 125
Run: ICPMS202-B_ 170825A
80 120
Run: ICPMS202-B_ 170825A
75 125
Run: ICPMS202-B_ 170825A
75 125
5.0
0.2
08/25/17 12:03
08/25/17 12:05
Batch: 112992
08/26/17 05: 14
08/26/17 06: 11
10
08/26/17 06:14
08/26/17 06: 17
08/26/17 06: 19
08/26/17 06:22
20
ND -Not detected at the reporting limit.
Page 62 of 77
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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 Billings, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 08/31/17
Work Order: C 17080550 Project: Not Indicated
Analyte
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-113038
Uranium
Lab ID: C17080550-035BDIL
Uranium
Lab ID: C17080550-035BPDS1
Uranium
Lab ID: SRM3-11303S
Uranium
Lab ID: C17080550-035BMS3
Uranium
Lab ID: C170S0550-035BMSD3
Uranium
Method: SW6020
Lab ID: MB-113039
Uranium
Lab ID: C170S0550-055BDIL
Uranium
Lab ID: C17080550-055BPDS1
Uranium
Lab ID: SRM3-113039
Uranium
Lab ID: C17080550-055BMS3
Uranium
Lab ID: C170S0550-055BMSD3
Uranium
Qualifiers:
RL -Analyte reporting limit.
Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Initial Calibration Verification Standard
0.0196 mg/L 0.00030
Interference Check Sample A
-0.000510 mg/L O 00030
Interference Check Sample AB
-0.000520 mg/L 0.00030
Method Blank
0.02 mg/kg 0.001
Serial Dilution
0.373 mg/kg-dry 1.0
Post Digestion/Distillation Spike
13.7 mg/kg-dry 1.0
Standard Reference Material
103 mg/kg 1.0
Sample Matrix Spike
55.4 mg/kg-dry 1.0
Sample Matrix Spike Duplicate
55.4 mg/kg-dry 1.0
Method Blank
0.01 mg/kg 0.001
Serial Dilution
1.57 mg/kg-dry 1.0
Post Digestion/Distillation Spike
15.4 mg/kg-dry 1.0
Standard Reference Material
102 mg/kg 1.0
Sample Matrix Spike
55.0 mg/kg-dry 1.0
Sample Matrix Spike Duplicate
56.0 mg/kg-dry 1.0
98
102
103
106
106
107
102
102
104
90
Analytical Run: ICPMS202-B_ 170829A
08/29/17 12:25
110
08/29/17 12:46
08/29/17 12:48
Batch: 113038
Run: ICPMS202-B_ 170S29A 08/29/17 19:36
Run: ICPMS202-B_170829A 08/29/17 21 :00
10
Run: ICPMS202-B_ 170829A 08/29/1721 :02
75 125
Run: ICPMS202-B_ 170829A 08/29/17 21 :05
80 120
Run: ICPMS202-B_ 170829A 08/29/17 21 :07
75 125
Run: ICPMS202-B _ 170829A 08/29/17 21 : 10
75 125 0.0 20
Batch: 113039
Run: ICPMS202-B_ 170829A 08/29/17 21 :18
Run: ICPMS202-B_ 170829A 08/29/17 22:29
4.4 10
Run: ICPMS202-B_170829A 08/29/17 22:39
75 125
Run: ICPMS202-B_170829A 08/29/17 22:42
80 120
Run: ICPMS202-B_ 170829A 08/29/17 22:44
75 125
Run: ICPMS202-B_ 170829A 08/29/17 22:47
75 125 1.7 20
ND -Not detected at the reporting limit.
Page 63 of 77
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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 Billings, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 08/31/17
Work Order: C17080550 Project: Not Indicated
Analyte
Method: SW6020
Lab ID: QCS
Uranium
Lab ID: ICSA
Uranium
Lab ID: ICSAB
Uranium
Method: SW6020
Lab ID: MB-113122
Uranium
Lab ID: B17082516-004BD1L
Uranium
Lab ID: B17082516-004BPDS1
Uranium
Lab ID: SRM3-113122
Uranium
Lab ID: 817082516-004BMS3
Uranium
Lab ID: B17082516-004BMSD3
Uranium
Qualifiers:
RL -Analyte reporting limit.
Result Units RL %REC Low Limit High Limit RPD RPDLimit Qual
Initial Calibration Verification Standard
0.0201 mg/L 0.00030
Interference Check Sample A
-0.000300 mg/L 0.00030
Interference Check Sample AB
-0.000320 mg/L 0.00030
Method Blank
0.006 mg/kg 0.001
Serial Dilution
5.91 mg/kg-dry 1.0
Post Digestion/Distillation Spike
21.2 mg/kg-dry 1.0
Standard Reference Material
102 mg/kg 1.0
Sample Matrix Spike
64.0 mg/kg-dry 1.0
Sample Matrix Spike Duplicate
65.5 mg/kg-dry 1.0
101
108
102
105
104
90
Analytical Run: ICPMS202-B_ 170830A
08/30/17 11 :07
110
08/30/17 11 :35
08/30/17 11 :37
Batch: 113122
Run: ICPMS202-B_ 170830A 08/30/17 18:36
Run: ICPMS202-B _ 170830A 08/30/17 19:00
7.2 10
Run: ICPMS202-B_ 170830A 08/30/17 19: 10
75 125
Run: ICPMS202-B_ 170830A 08/30/17 19:13
80 120
Run: ICPMS202-B_ 170830A 08/30/17 19: 15
75 125
Run: ICPMS202-B_ 170830A 08/30/17 19:18
75 125 2.4 20
ND -Not detected at the reporting limit.
Page 64 of 77
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY B&&.&8&. 7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte Count Result Units
Method: E903.0
Lab ID: C17080550-04 7 AMS1 Sample Matrix Spike
Radium 226 2.9 pCi/g-dry
lab ID: C17080550-047 AMS1 Sample Matrix Spike Duplicate
Radium 226 3.6 pCi/g-dry
Lab ID: LCS1-50343 Laboratory Control Sample
Radium 226 2.1 pCi/g-dry
Lab ID: MB-50343 3 Method Blank
Radium 226 0.06 pCi/g-dry
Radium 226 precision (±) 0.03 pCi/g-dry
Radium 226 MDC 0.04 pCi/g-dry
Method: E903.0
Lab ID: C17080550-001AMS1 Sample Matrix Spike
Radium 226 3.3 pCi/g-dry
Lab ID: C17080550-001AMS1 Sample Matrix Spike Duplicate
Radium 226 2.8 pCi/g-dry
Lab ID: LCS1-50256 Laboratory Control Sample
Radium 226 2.3 pCi/g-dry
Lab ID: MB-50256 3 Method Blank
Radium 226 0.009 pCi/g-dry
Radium 226 precision (±) 0.006 pCi/g-dry
Radium 226 MDC 0.009 pCi/g-dry
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
RL
Report Date: 10/16/17
Work Order: C17080550
%REC Low Limit High Limit RPO RPDLimit Qual
Batch: 50343
Run:G542M_170911B 09/18/17 08:49
82 70 130
Run: G542M_ 1709118 09/18/17 08:49
107 70 130 19 20
Run: G542M_ 170911 B 09/18/17 10:32
81 67 120
Run: G542M_ 170911 B 09/18/17 10:32
Batch: 50256
Run: G542M-2_170829A 09/05/17 08:33
104 70 130
Run: G542M-2_170829A 09/05/17 08:33
84 70 130 16 20
Run: G542M-2_170829A 09/05/17 10: 10
90 67 120
Run: G542M-2_ 170829A 09/05/17 1O:10
ND -Not detected at the reporting limit.
Page 65 of77
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 8&&.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte
Method: E903.0
Lab ID: C17080550-025AMS1
Radium 226
Lab ID: LCS1-50322
Radium 226
Lab ID: MB-50322
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C17080550-025AMS1
Radium 226
Method: E903.0
Lab ID: C17080550-040AMS1
Radium 226
Lab ID : LCS1-50323
Radium 226
Lab ID : MB-50323
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C17080550-040AMS1
Radium 226
Method: E903.0
Lab ID: MB-50470
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: LCS1-50470
Radium 226
Count Result Units
Sample Matrix Spike
2.9 pCi/g-dry
Laboratory Control Sample
1.9 pCi/g-dry
3 Method Blank
0.003 pCi/g-dry
0.004 pCi/g-dry
0.007 pCi/g-dry
Sample Matrix Spike Duplicate
2.6 pCi/g-dry
Sample Matrix Spike
2.1 pCi/g-dry
Laboratory Control Sample
2.1 pCi/g-dry
3 Method Blank
0.001 pCi/g-dry
0.004 pCi/g-dry
0.006 pCi/g-dry
Sample Matrix Spike Duplicate
2.1 pCi/g-dry
3 Method Blank
0.008 pCi/g-dry
0.02 pCi/g-dry
0.02 pCi/g-dry
Laboratory Control Sample
3.2 pCi/g-dry
Report Date: 10/16/17
Work Order: C 17080550
RL %REC Low Limit High Limit
Run: G542M-2_170910A
86 70 130
Run: G542M-2_ 17091 OA
77 67 120
Run: G542M-2_170910A
Run: G542M-2_170910A
76 70 130
Run: G542M-2_170910A
76 70 130
Run : G542M-2_ 17091 QA
84 67 120
Run: G542M-2_170910A
Run: G542M-2_ 17091 QA
76 70 130
Run: G542M-2_ 171009A
Run : G542M-2_ 171009A
127 67 120
RPD RPDLimit Qual
7.7
0.4
Batch: 50322
09/18/17 09:35
09/18/17 11 :18
09/18/17 11 :18
u
09/18/17 09:35
20
Batch: 50323
09/18/17 11 : 18
09/18/17 11: 18
09/18/17 12:53
u
09/18/1711:18
20
Batch: 50470
10/11/17 12:30
u
10/11/1712:30
s
-LCS response is outside of the acceptance range for this analysis. Since the MB, MS, and MSD are acceptable the batch is approved.
Lab ID: C17080550-012AMS1
Radium 226
Lab ID: C 17080550-012AMS 1
Radium 226
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
Sample Matrix Spike
5.4 pCi/g-dry
Sample Matrix Spike Duplicate
5.6 pCi/g-dry
U -Not detected at minimum detectable concentration
Run: G542M-2_ 171009A
108 70 130
Run: G542M-2_171009A
116 70 130
ND -Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
3.9
10/11/1712:16
10/11/1712:16
20
Page 66 of 77
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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
Project: Not Indicated
Analyte
Method: E908.0
Lab ID: LCSS-50256
Thorium 230
Lab ID: C17080550-003AMS5
Thorium 230
Lab ID: C17080550-003AMS5
Thorium 230
Count Result Units
Laboratory Control Sample
4.7 pCi/g-dry
Sample Matrix Spike
7.0 pCi/g-dry
Sample Matrix Spike Duplicate
4.7 pCi/g-dry
RL
Report Date: 10/16/17
Work Order: C17080550
%REC Low Limit High Limit RPD RPDLimit Qual
Batch: R227372
Run: EGG-ORTEC _ 170905C 09/18/17 15:55
96 80 120
Run: EGG-ORTEC_ 170905C 09/18/17 15:55
112 70 130
Run: EGG-ORTEC_ 170905C 09/18/17 15:55
65 70 130 40 20 SR
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RER recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: MB-50256 6 Method Blank
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Lab ID: MB-50257
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
6
MDC -Minimum detectable concentration
0.009 pCi/g-dry
0.009 pCi/g-dry
0.01 pCi/g-dry
-0.0004 pCi/g-dry
0.004 pCi/g-dry
0.01 pCi/g-dry
Method Blank
0.06 pCi/g-dry
0.01 pCi/g-dry
0.03 pCi/g-dry
-0.003 pCi/g-dry
0.008 pCi/g-dry
0.02 pCi/g-dry
S -Spike recovery outside of advisory limits.
Run: EGG-ORTEC_ 170905C
Run: EGG-ORTEC_ 170905C
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
U -Not detected at minimum detectable concentration
09/18/17 15:55
u
u
09/18/17 15:55
u
Page 67 of 77
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
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte
Method: E908.0
Lab ID: LCS5-50257
Thorium 230
Lab ID: MB-50257
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Method: E908.0
Lab ID: C17080550-027 AMS5
Thorium 230
Lab ID: C17080550-027 AMS5
Thorium 230
Count Result Units
6
Laboratory Control Sample
5.0 pCi/g-dry
Method Blank
0.006 pCi/g-dry
0.01 pCi/g-dry
0.02 pCi/g-dry
0.002 pCi/g-dry
0.006 pCi/g-dry
0.01 pCi/g-dry
Sample Matrix Spike
4.4 pCi/g-dry
Sample Matrix Spike Duplicate
3.8 pCi/g-dry
Report Date: 10/16/17
Work Order: C 17080550
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_170914A
101 80 120
Run: EGG-ORTEC_ 170914A
Run: EGG-ORTEC_170914A
78 70 130
Run: EGG-ORTEC_ 170914A
M m 1~ 13
Batch: 50257
09/19/17 18:53
09/19/17 18:53
u
u
Batch: 50322
09/19/17 18:53
09/19/17 18:53
20 S
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RPD recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: MB-50322
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
6 Method Blank
0.001 pCi/g-dry
0.009 pCi/g-dry
0.02 pCi/g-dry
0.002 pCi/g-dry
0.006 pCi/g-dry
0.01 pCi/g-dry
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Run: EGG-ORTEC_ 170914A
ND -Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
09/20/17 10:23
u
u
Page 68 of 77
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
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte
Method: E908.0
Lab ID: LCS5-50322
Thorium 230
Lab ID : MB-50322
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Method: E908.0
Lab ID: C17080550-042AMS5
Thorium 230
Count Result Units
Laboratory Control Sample
4.5 pCi/g-dry
6 Method Blank
0.001 pCi/g-dry
0.009 pCi/g-dry
0.02 pCi/g-dry
-0.001 pCi/g-dry
0.005 pCi/g-dry
0.01 pCi/g-dry
Sample Matrix Spike
3.6 pCi/g-dry
Report Date: 10/16/17
Work Order: C17080550
RL %REC Low Limit High Limit
Run: EGG-ORTEC_170915A
91 80 120
Run: EGG-ORTEC_170915A
Run: EGG-ORTEC_170915A
68 70 130
RPD RPDLimit Qual
Batch: 50322
09/21/1711 :41
09/21/17 11 :41
u
u
Batch: 50323
09/21/17 11 :41
s
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RPO recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: C17080550-042AMS5
Thorium 230
Lab ID : MB-50323
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Method: E908.0
Lab ID: MB-50343
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
Sample Matrix Spike Duplicate
3.8 pCi/g-dry
6 Method Blank
0.004 pCi/g-dry
0.009 pCi/g-dry
0.02 pCi/g-dry
-0.0008 pCi/g-dry
0.004 pCi/g-dry
0.01 pCi/g-dry
6 Method Blank
0.01 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
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Run: EGG-ORTEC_170915A
70 70 130 3.0
Run: EGG-ORTEC_ 17091 SA
Run: EGG-ORTEC_ 170915A
ND -Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
09/21/1711:41
20
09/21 /17 11 :41
u
u
Batch: 50343
09/22/17 10:21
u
u
Page 69 of 77
EN:RGY Trust our People. Trust our Data.
www energylab.rnm
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
Project: Not Indicated
Analyte
Method: E908.0
Lab ID: LCSS-50343
Thorium 230
Lab ID: C17080550-050AMS5
Thorium 230
Count Result Units
Laboratory Control Sample
4.3 pCi/g-dry
Sample Matrix Spike
1.6 pCi/g-dry
Report Date: 10/16/17
Work Order: C 17080550
RL %REC Low Limit High Limit
Run: EGG-ORTEC_ 170918A
86 80 120
Run : EGG-ORTEC_170918A
24 70 130
RPO RPDLimit Qual
Batch: 50343
09/25/17 09:50
09/25/17 09:51
s
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RER recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: C17080550-050AMS5
Thorium 230
Sample Matrix Spike Duplicate
2.2 pCi/g-dry 37
Run: EGG-ORTEC_170918A 09/25/17 09:51
70 130 35 20 SR
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RER recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: MB-50343 6 Method Blank
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
S -Spike recovery outside of advisory limits.
0.007 pCi/g-dry
0.008 pCi/g-dry
0.01 pCi/g-dry
-0.0007 pCi/g-dry
0.004 pCi/g-dry
0.01 pCi/g-dry
Run : EGG-ORTEC_ 170918A
ND -Not detected at the reporting limit.
R -RPO exceeds advisory limit.
U -Not detected at minimum detectable concentration
09/25/17 09:51
u
u
Page 70 of 77
EN:RGY Trust our People. Trust our Data.
www.energylab.mm
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
Project: Not Indicated
Analyte
Method: E909.0
Lab ID: LCS3-50323
Lead 210
Lab ID: MB-50323
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Lab ID: C17080550-041AMS3
Lead 210
Count Result Units
Laboratory Control Sample
1.9 pCi/g-dry
3 Method Blank
-0.1 pCi/g-dry
0.1 pCi/g-dry
0.2 pCi/g-dry
Sample Matrix Spike
2.4 pCi/g-dry
Report Date: 10/16/17
Work Order: C 17080550
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: PACKARD 3100TR_170914A
85 80 120
Run: PACKARD 3100TR_170914A
Run: PACKARD 3100TR_170914A
46 70 130
Batch: 50323
09/18/17 20:43
09/18/17 22: 18
u
09/19/17 08:38
s
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RPD recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Lab ID: C17080550-041AMS3
Lead 210
Sample Matrix Spike Duplicate
2.1 pCi/g-dry 33
Run: PACKARD 3100TR_170914A 09/19/17 10:03
70 130 15 20 S
-Spike response is outside of the acceptance range for this analysis. Since the LCS and the RPD recoveries are acceptable, the response is considered to be matrix
related. The batch is approved.
Method : E909.0 Batch: 50256
Lab ID: C17080550-002AMS3 Sample Matrix Spike
Lead 210 3.1 pCi/g-dry
Lab ID: C17080550-002AMS3 Sample Matrix Spike Duplicate
Lead 210 3.0 pCi/g-dry
Lab ID: LCS3-50256 Laboratory Control Sample
Lead 210 2.3 pCi/g-dry
Lab ID: MB-50256 3 Method Blank
Lead 210 0.09 pCi/g-dry
Lead 210 precision (±)
Lead 210 MDC
Method: E909.0
Lab ID: LCS3-50257
Lead 210
0.2 pCi/g-dry
0.3 pCi/g-dry
Laboratory Control Sample
1.6 pCi/g-dry
Run: TRICARB LSC_ 170905A
92 70 130
Run: TRICARB LSC_170905A
93 70 130 2.3
Run: TRICARB LSC_170905A
103 80 120
Run: TRICARB LSC_170905A
Run: TRICARB LSC_ 170905B
75 80 120
-LCS response is outside of the acceptance range for this analysis. Since the MB, MS, and MSD are acceptable the batch is approved.
Lab ID : MB-50257
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Lab ID: C17080550-013AMS3
Lead 210
Lab ID: C17080550-013AMS3
Lead 210
Qualifiers:
RL -Analyte reporting limit.
3 Method Blank
0.03 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
Sample Matrix Spike
5.4 pCi/g-dry
Sample Matrix Spike Duplicate
5.0 pCi/g-dry
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Run: TRICARB LSC_170905B
Run: TRICARB LSC_170905B
125 70 130
Run: TRICARB LSC_ 170905B
107 70 130 7.8
ND -Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
09/13/17 09: 12
09/13/17 10:24
20
09/14/17 02:23
09/14/17 03:46
u
Batch : 50257
09/14/17 08:23
s
09/14/17 10:01
u
09/14/17 18:03
09/14/17 18:54
20
Page 71 of 77
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
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: Not Indicated
Analyte
Method: E909.0
Lab ID: LCS3-50343
Lead 210
Lab ID: MB-50343
Lead 210
Lead 210 precision(±)
Lead 210 MDC
Lab ID: C170B0550-04BAMS3
Lead 210
Lab ID: C17080550-048AMS3
Lead 210
Method: E909.0
Lab ID: LCSJ-50471
Lead 210
Lab ID: MB-50471
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Lab ID: C17080550-025AMS3
Lead 210
Lab ID: C17080550-025AMS3
Lead 210
Qualifiers:
RL -Analy1e reporting limit.
Count Result Units
Laboratory Control Sample
1 . 8 pCi/g-dry
3 Method Blank
-0.2 pCi/g-dry
0.2 pCi/g-dry
0.3 pCi/g-dry
Sample Matrix Spike
2.3 pCi/g-dry
Sample Matrix Spike Duplicate
2.1 pCilg-dry
Laboratory Control Sample
2.9 pCi/g-dry
3 Method Blank
0.07 pCi/g-dry
0.2 pCi/g-dry
0.4 pCi/g-dry
Sample Matrix Spike
3.8 pCi/g-dry
Sample Matrix Spike Duplicate
3.7 pCi/g-dry
MDC -Minimum detectable concentration
Report Date: 10/16/17
Work Order: C 17080550
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: TRICARB LSC_170918A
80 80 120
Run: TRICARB LSC_170918A
Run: TRICARB LSC_170918A
90 70 130
Run: TRICARB LSC_170918A
84 70 130 8.1
Run: TRICARB LSC_171010A
113 80 120
Run: TRICARB LSC_171010A
Run: TRICARB LSC_171010A
125 70 130
Run: TRICARB LSC_171010A
116 70 130 3.5
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 50343
09/20/17 15:49
09/20/17 17:21
u
09/21117 03:09
09/21/17 04:31
20
Batch: 50471
10/11/1717:54
10/11/17 19:22
u
10112/17 02:56
10/12/17 04:10
20
Page 72 of 77
E"-ERGY 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: 8/15/2017
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 No Ice
Yes D
Yes D
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
C17080550
Date Received: 8/14/2017
Received by: rso
Carrier name: Ground
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
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 73 of 77
Sheet 1 of 4
CHAIN OF CUSTODY
Samples Shipped to: ~E~n~er~g'.!'.--y~La_b~o_ra_,t,.....ie~s ________ Contact: Garrin Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
ProJect Samplers Name Samplers Slanature
Annual Soils 2017 Garrin Palmer ,~~ (Jj,,(A_-
Time
Sample ID Date Collected Collected Laboratory Analysis Reauested ..... N01 8/8/2017 820 Ra-226, U-Net, Pb-210, Th-232
-.;;:---'~. N02 8/8/2017 901 Ra-226, U-Nat Pb-210 Th-232 ... ';, N03 8/8/2017 908 Ra-226, U-Nat, Pb-210 Th-232
N04 8/8/2017 --N05 8/8/2017
E01 8/8/2017
E02 8/8/2017
E03 8/8/2017
E04 8'/8/2017
E05 8/8/2017
E06 8/8/2017
E07 8/8/2017
E08 8/8/2017
E09 8/8/2017
E10 8/8/2017
E11 8/8/2017
E12 8/8/2017
E13 8/8/2017
Relinquished By:{Signa~e) / 6 ~ 6-" cA..A--·
,.,.,.. f'o.l-cr-
Relinquished By:(Sfgnature)
I
922 Ra-226 U-Nat, Pb-210, Th-232
926 Ra-226, U-Nat, Pb-210 Th-232
935 Ra-226, U-Nat, Pb-210, Th-232
942 Ra-226, U-Nat, Pb-210, Th-232
947 Ra-226, U-Nat, Pb-210, Th-232
951 Ra-226, U-Nat, Pb-210. Th-232
1001 Ra-226, U-Nat, Pb-210, Th-232
1006 Ra-226 U-Nat Pb-210, Th-232
1011 Ra-226, U-Nat, Pb-210, Th-232
1027 Ra-226, U-Nat, Pb-210, Th-232
1043 Ra-226, U-Nat, Pb-210, Th-232
1037 Ra-226. U-Nat Pb-210. Th-232
1049 Ra-226, U-Nat, Pb-210, Th-232
1059 Ra-226, U-Nat, Pb-210, Th-232
1426 Ra-226, U-Nat, Pb-210, Th-232
e.,,~r-£00
Datemme Received By:(Signature} Datemme
"''"'~ Datemme ,,_.
-I, ~
Sheet 2 of 4 ,-~---/
( V
ENERGYFUEI.S RESOURCES
CHAIN OF CUSTODY
Samples Shipped to: ..,,.E"'"'n,....er_..g-!-y_La_b"""'o_ra....,ti,...e,....,s ________ Contact: Garrin Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samplers Name Samplers Signature
Annual Soils 2017 Garrin Palmer I ~/',.~ ~':3-~,,;( A f-
Time
Sample ID Date Collected Collected Laboratory Analysts ReQuesled
E14 8/8/2017 1446 Ra-226, U-Nat. Pb-210, Th-232
E15 8/8/2017 1438 Ra-226, U-Nal, Pb-210, Th-232
E16 8/9/2017 826 Ra-226, U-Nat, Pb-210, Th-232
E17 8/9/2017 835 Ra-226 U-Nat, Pb-210, Th-232 -i-E18 8/9/2017 839 Ra-226, U-Nat, Pb-210, Th-232
501 8/9/2017 929 Ra-226 U-Nat, Pb-210 Th-232
502 8/9/2017 940 Ra-226, U-Nat, Pb-210, Th-232
-r--S03 8/9/2017 847 Ra-226 U-Nat, Pb-210, Th-232
W01 8/8/2017 828 Ra-226 U-Nat Pb-210, Th-232
W02 8/8/2017 835 Ra-226, U-Nat, Pb-210, Th-232
W03 8/8/2017 845 Ra-226, U-Nat, Pb-210, Th-232
W04 8/8/2017 850 Ra-226, U-Nat, Pb-210 Th-232
W05 8/9/2017 1236 Ra-226 U-Nat Pb-210, Th-232
W06 8/9/2017 1229 Ra-226, U-Nat, Pb-210, Th-232
W07 8/9/2017 1242 Ra-226, U-Nat, Pb-210 Th-232 woe 8/9/2017 1245 Ra-226, U-Nat Pb-210, Th-232
W09 8/9/2017 1249 Ra-226, U-Nat, Pb-210 Th-232
W10 8/9/2017 1253 Ra-226, U-Nat, Pb-210, Th-232
Comments: Please send report to Kathy Weinel at kweinel(@.eneravfuels.com C. \""'\C1nO~~
Relinquished By:(Signature) Date/Time Recelved By:(Signature)
">HJ•...__• g/,c,/,7
Relinquished By:(Signature)
Datemme
Date/Time
f-1&{-r>
/1.s-
Sheet 3 of 4
CHAIN OF CUSTODY
Samples Shipped to: _E_n __ er_9 .... Y..,.La_b __ o_ra_tl_e_s ________ Contact: Ganin Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samolers Name Samplers Signature
Annual Soils 2017 Garrin Palmer I r;r-~ ,,'";-pk_A -
Time
Sample ID Date Collected Collected Laboratorv Analvsis Reauested
W11 8/9/2017 1256 Ra-226. U-Nat, Pb-210, Th-232
W12 8/9/2017 1300 Ra-226, U-Nat, Pb-210, Th-232
W13 8/9/2017 1309 Ra-226 U-Nat, Pb-210 Th-232
W14 8/9/2017 1322 Ra-226, U-Nat Pb-210, Th-232
W15 8/9/2017 1001 Ra-226, U-Nat, Pb-210, Th-232
W16 8/9/2017 1910 Ra-226, U-Nat, Pb-210, Th-232
W17 8/9/2017 1916 Ra-226, U-Nat, Pb-210, Th-232 -~ W18 8/9/2017 922 Ra-226. U-Nat, Pb-210, Th-232
"' r-E65 8/8/2017 1426 Ra-226, U-Nat, Pb-210 Th-232
.......... " W70 8/9/2017 910 Ra-226, U-Nat, Pb-210, Th-232 ,, S75 8/9/2017 940 Ra-226, U·Nat, Pb-210, Th-232
Westwater Creek 8/9/2017 1219 Ra-226, U-Nat, Pb-210 Th-232
BHV-1 8/8/2017 930 Ra-226, U-Nat, Pb-210, Th-232
BHV-2 8/8/2017 1355 Ra-226, U-Nat Pb-210, Th-232
BHV-3 8/8/2017 1240 Ra-226, U-Nat, Pb-210, Th-232
BHV-4 8/8/2017 1410 Ra-226 U-Nat, Pb-210, Th-232
BHV-5 8/8/2017 1031 Ra-226 U-Nat, Pb-210 Th-232
BHV-6 8/8/2017 1053 Ra-226, U-Nat, Pb-210, Th-232
Comments: Please send report to Kathy Weinel at [e-mail] r ''"'~~
Relinquished By:(Signature) G~
Relinquished By:(Signature) By:(Signature)
Date/Time
Datemme .,,_,..,_,7
/ 5; 5',A
Sheet 4 of 4
CHAIN OF CUSTODY
Samples Shipped to: _E...,.n_e.,.rgy~L_a_bo-ra..;.;.;;.tie_s.,...... _______ Contact: Garrin Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY. 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Prolact SamDlers Name Samplers Slanature
Annual Soils 2017 Ganin Palmer I 6A~ r-R} A ~
Time
Sample ID Date Collected Collected Laboratory Analysis ReQuested
BHV-7 8/8/2017 956 Ra-226 U-Nat, Pb-210, Th-232
BHV-8 8/8/107 915 Ra-226, U-Nat, Pb-210, Th-232
Comments: Please send report to Kathy Weinel at kweinell@.energyfuels.com C\~~C~i'>
Relinquished By:(Signature) ~ R
Relinquished By:(Signature)
Dateffime
Datemme
ff-J'(-1
II 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 Th-232
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 --I.I 3 . -0.8 I .
8/1/1990 2.9 5.8 . -I 1.4 . -0.8 l.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 1 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 I. I 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 0.3
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 0.2
8/8/2017 1.2 1.35 2.1 0.3 0.5 0 0.9 0.3 0.2 0 0.8 0.2
-Data not available.
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 .
1 1.3 . -3.8 5 .
I.I l.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 l.6 .
0.5 0.52 --1.9 2.01 .
0.41 0.26 . . 1.7 l.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 . . 1 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 l.69 . . 1.7 1.69 -
0.5 0.58 . . I 1.48 .
0.6 0.81 . . 1.6 2.7 .
0.3 0.54 . . I.I 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
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 Tb-232
. . . . . . .
. . . . . . .
-. . -. --
--. --. -
. . . . . .
. . -. . . .
. . . . . -.
. . . -. -
---. . .
-. . . . . .
-. -. . . .
. --. --.
-. . --. -
--. . . --
. . . -. . .
. . . -. -.
-. . -. --
--. . . . -
. . -. . -.
. --. -. -
. . . . . -.
-. . --.
-. . . . . -
. -. . . . .
. . -. . --
-0.6 0.53 ---. --
-0.9 1.4 . . --.
. I l.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 0.3 0.3 0.7 1.755 0.5 0.09 l.O 0.338 0.8 0.05
0.4 0.8 0.8775 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
' Ni,011 I ~.l.0! I
'ompfo I :,c
Ii d 11tl' 1' 'Ra-i!o rrtl'~~11 i'Pb-210 li'f'h-392 Sa~ ,,tJ-;Nat Ph, ... lil)i ':fb.,.1at ~-&16
Aug-15 0.30 0.47 0.80 0.30 0.50 0.41 0.30 0.30 0.60
Aug-16 0.50 0.20 0.60 0.20 0.60 0.20 0.40 0.50 0.50
Aug-17 0.7 0 1.8 0.4 0.7 0 1.1 0.3 0.9
Nr1l~
U-:r.s:'111 Pb-,HO
0.61 0.90
0.20 0.60
0.7 l.3
Tablel-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
I N .. OIJ Nr.Oi
I
'Fb-E3it )nne,2J;26 ti!I-Na.t ,Prh!l!O ~23.f; Jla-~u ~~t ""'h~~\O r'iVh-~
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
S·Oi S•fm J S·OJ
i I I> I
R:a~2'.2t1 'IJ.1~n1, Pl,)-210 Ii 'f1b•2"3'~ )Ra-~(j 'l7-~~tt 1:Pri-11HI 1.)lli":l'.\i R1\-:zl61 "'U-Nat P~-21lt01 Tf\-2-321
0.30 0.20 l.10 0.30 0.60 0.54 0.50 0.60 0.30 0.34 1.10 0.06
0.40 0.14 0.30 0.08 0.20 0.05 0.70 0.20 0.20 O.Q7 0.80 0.30
0.7 0 1.0 0.4 0.8 1.4 0.8 0.6 0.4 0 1.0 O.Q7
l!}..l}Jl :tiH),.. ill-OS I
~ '
•$ampfo
d:itc. Ra-2-26 P-Nat Pb-210 Th-23~ Ra-226 U-Nat Pb-210 Th-232 Ra-226 U.Nat Pb-210 Fb-2:-'l~ ~in,.,212:6
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 1.70 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
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
llJ'.0'4 RJ .E,06
'
tf..N'at ~J;J-i1110 ':li'Jt~-3~ ~lit-22(, .~X1it Iti'"U!O ·"Jrih~) ;R'll-2-2ti u~~:i,~ 1Pb-2.a.O
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
'il'li-~'21
0.20
0.20
0.1
ll}.(01 I< Ii!,..((8 :B-i.09 1, -I
R:n-22(i U-Nnt PJl-21,0 'ffil-l/U B:a-tiG, ~~t Pl:1-llli.O 'li'h•JJ!!' rRa-226 ~t· •1Pb-llO Th-232
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
E-ll(j I l.U:1tl E-ill! 11
..
I
mi,vl'26; ,TI-J°"(at .PlJ.,210 'llli-2:121 )l'H•Mli .:m.Mn'l Pl,-2'll0 'Ph..a.32 !.8.flr2Zli u~I'!lut 1-m.11lII01 ':ITih-2,32 ·:Il-a4:im
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.Q7 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
Table 1-2
WHITE MESA l\flLL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g) -.E-:L3 E-14 E-1,S
1fil-N~1 Pb•l!l(OJ 'Jfu,.!MJ Ua~(), ~Ng( 1Pb':~101 1"'JJl1-2-~ l{:.it.2 ... 6 .e:..Nnt Pb·2Ja)i
0.41 0.70 0.20 0.40 0.54 uo 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.Q7 1.10
0 1.7 0.1 1.9 0 1.1 0.5 1.6 0 1.5
'J1h-2'32
0.20
0.20
0.3
) il?'·il6 ·E!,]7 ..Ql•Ni
Jttu..,i.211 llH~ac P.b-!illO Tb-& Ra-226 U-Nat Pb,2/JiO, 'fh'-'.l!~ .Ra...Z26 U.,Nat Pl>-2'10 TJi-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 O.Q7 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 0.2
Sample W-01 W-.02 WsOJ
date Ra-226" 0-N@t Pb-210 Th-232 ,Ra-2:26 U..Nat Pb-210 Tk-232 Ra-226 U-Nnt Pb-210
Aug-15 0.50 0.41 0.20 0.30 0.60 0.68 0.60 0.20 0.90 0.81 1.30
Aug-16 0.60 0.20 0.60 0.50 1.00 0.20 0.80 0.30 0.80 0.27 1.10
Aug-17 0.6 0 1.1 0.1 0.6 0 0.9 0.1 0.7 0.68 1.1
Th-232
0.20
0.20
0.2
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
W-04 W-05 W-06
Ra-226 0-Nat Pb-21'0 Tb-232· Ra4 26 U-Nat, Pb-2:W 11h-232· Ra-ZU l}1.Nat .Pb-210
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 0.07 0.80
0.9 0.68 1.6 0.08 0.4 0 0.9 0.1 0.3 0 0.9
-VV-07 W-08 W-09
'Fh-232 Ra~Z.26 U-Nat Pb~210 'J1h~232 Ra-226 UJ-Na~ Bb-210 Th-23· Ra-2'26. U-Nat Pb-210 111-232,
0.30 0.40 0.34 0.60 0.20 0.40 0.61 0.90 0.20 0.20 0.41 0.70 0.09
0.10 0.30 0.07 1.60 0.30 0.40 0.14 1.50 0.20 0.20 0.05 1.20 0.20
0.1 0.4 0 0.7 0.4 0.3 0 0.8 0.2 0.3 0 0.9 0.03
W-10 W·:11 W-12
Ra-2'26 0-Nat Pb-21~ Th-232 Ra-zi6 U•Nat Pb-210 Th-232 ~a-226 u ~Nat Pb-210 Th-232 Ra-2"26
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 0.07 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
Table 1-2
WHITE MESA MILL
Soil Sampling Results in the Four Cardinal Directions
(pCi/g)
Wil3 W-14 W-15
'C!J-Nat Pb-210 Th!232 Ra-226 lJ.-Nat Fb-210 Th-232 Ra-2'26 lJ-Na( Pb-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 0.1 0.3 0 1.3
Th-232
0.20
0.00
0.1
W-16 V\H7 W-18
Ra-Z.~6 U•Nat Pb-2.10 lll-232 IRa-226 "CJ-Nat, Pb-210 Th-232 l{a-226 U-Nat Pb'.:210 Tb-232
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 0.3 0.5 0 1.2 0.2
Table 1-3
WHITE MESA MILL
Soil Sampling Results
Duplicate Sample Results
(pCi/g)
E13
<I
1.7
1.9
0.1
Constituent W16
Uranium (mg/kg) <1
Lead 210 (pCi/g) 1.2
Radium 226 (pCi/g) 0.4
Thorium 232 (pCi/g) 0.4
Constituent S02
Uranium (mg/kg) 1.35
Lead 210 (pCi/g) 0.8
Radium 226 (pCi/g) 0.8
Thorium 232 (pCi/g) 0.6
E65
<l
1.9
1.0
0.3
W70
<1
I.I
0.3
0.4
S75
1.35
0.5
0.9
0.6
Duplicate RPD results are outside of the 35% RPD limit.
%RPO
NC
11.1
62.1
%RPO
NC
8.7
28.6
0.0
%RPO
0.0
ATTACHMENT J
RADON MONITORING GRAPHS AND DATA
pCi\L
0 0 0 0 0 0 0 0
0 ...... i\, w :i:,.. i:n 0) :....i CX>
1/2/2013
+ 3/29/2013
CD I < 7/1/201 I (,) -C" Q) 10/1/2013 (")
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+
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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
1/2/2013 0.1 0.71 0 0.34 0.6 0.4 0.5 0 1.43
3/29/2013 0.1 0.71 0 0.34 0.7 0.3 0.5 0.5 1.43
7/1/2013 0 0.71 0 0.34 0.06 0 0.5 0 1.43
10/1/2013 0.1 0.71 0 0.34 om 0 0.5 NA 1.43
12/24/2013 0.4 0.71 0 0.34 0.07 0.33 0.5 0.43 1.43
4/2/2014 0.2 0.71 0 0.34 0.06 0.04 0.5 0.54 1.43
6/27/2014 0.1 0.71 0 0.34 0.07 0 0.5 O.Q3 1.43
9/30/2014 0.2 0.71 0.1 0.34 0.1 0.2 0.5 0.3 1.43
1/7/2015 0.1 0.71 0 0.34 0.2 0.3 0.5 0.6 1.43
4/2/2015 0.23 0.71 0 0.34 0.07 0.23 0.5 0.43 1.43
6/29/2015 0.2 0.71 0.2 0.34 0.2 0.4 0.5 0.4 1.43
9/28/2015 0.2 0.71 0.1 0.34 0.3 0.2 0.5 0.6 1.43
1/4/2016 0.0 0.71 0.0 0.34 0.2 0.4 0.5 0.7 1.43
4/4/2016 0.0 0.71 0.1 0.34 0.2 0 0.5 0.7 1.43
7/5/2016 0.1 0.71 0.0 0.34 0.07 0 0.5 0.23 1.43
10/10/2016 0.06 0.71 0.0 0.34 0.35 0.30 0.5 0.38 1.43
1/5/2017 0.14 0.71 0.09 0.34 0.32 0.25 0.5 0.38 1.43
3/29/2017 0.05 0.71 0.27 0.34 0.11 0.21 0.5 0.51 1.43
7/5/2017 0.06 0.71 0.0 0.34 0.16 0.14 0.5 0.25 1.43
9/29/2017 0.06 0.71 0.0 0.34 0.24 0.00 0.5 0.08 1.43
1/2/2018 0.17 0.71 0.06 0.34 0.32 0.30 0.5 0.54 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
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 O.Q3 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
O.Q3 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
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
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 Part 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 = l.0-0.0479expc-,t4·39> _ 2.1963exp<-r 138·6> + l.2442exp<-1128·4>
[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 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
2017 Radon Flux Measurement Program
Second Half 2017 Sampling Results
White Mesa Mill
6425 South Highway 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 OPERATIONS .......................... ii ................................................ ., ........ , ..................................... 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 ..................................................................................................................... 4
6.1 Apparatus ........................................................................................................................... 4
6.2 Sample Inspection and Documentation ............................................. , ............................... 4
6.3 Background and Sample Counting ... : ................................................................................ 4
7. QUALITY CONTROL (QC) AND DATA VALIDATION ........................................................... 5
7.1 Sensitivity ............................... ,a-............................................................................. , •• 11, •••••••••• 5
7 .2 Precision ............................................................................................................................. 5
7 .3 Accuracy ............................................................................................................................ 5
7 .4 Completeness ..................................................................................................................... 5
8. CALCULATIONS ........................................................................................................................... 6
9. RESULTS ........................................................................................................................................ 7
9.1 Mean Radon Flux ............................................................................................................... 7
9.2 Site Results ......................................................................................................................... 8
References ............................................................................................................................................ 9
Figure 1 ............................................... ,, ....... -. ........................ il •••••••••••••••••••••••••••• , ........... ,., .... _ .................. 10
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 July 15-16, 2017 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 2017. 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 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 CPR 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
of 20 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, 2017). 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 Y:z inch thick layer of foam and
secured with a retaining ring under 1 Y:z inches of foam (see Figure 1, page 10).
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 July 15, 2017, 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., FOL. .FIOO). This ID was
written on an adhesive label and affixed to the top of the canister. The sample ID, date, and time of
2
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 surface 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 July 16, 2017 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
transport. Retrieval date and time were recorded on the same data sheets as the sample placement
information. The blank samples were similarly processed.
All of the charcoal samples from the Cell 2 covered region were successfully retrieved and
containerized during the retrieval and unloading process.
5.4 Environmental Conditions
A rain gauge and thermometer were placed at Cell 2 to monitor rainfall and air temperatures during
sampling; additionally, Energy Fuels maintains an onsite rain gauge.
In accordance with 40 CFR, Part 61, Appendix B, Method 115:
• Measurements were not initiated within 24 hours of rainfall at the site.
• There was no rainfall during the 24-hour sampling period.
• All canister seals remained intact during the 24-hour sampling period.
• The criteria regarding 3 5 degree F minimum ambient air temperature and unfrozen ground
do not apply when performing sampling at multiple times throughout the year; however,
the minimum air temperature during the 24-hour sampling period was 62 degrees F, and
the ground was not frozen.
3
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 (NaI(Tl)) detector.
• Lead shielded counting well approximately 40 cm deep with 5-cm thick 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 radium-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 the 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 NaI 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 recounting. These
containers were recounted on the next day following the original count.
4
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
All sample data were subjected to validation protocols that included assessments of sensitivity,
precision, accuracy, and completeness. All method-required data quality objectives (EPA, 2017) 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 approximately 0.02 to 0.04 pCi/m2-s, with an
average of approximately 0.03 pCi/m2-s. The lower limit of detection (LLD) was approximately 0.04
pCi/m2-s.
7.2 Precision
Ten recount measurements, distributed throughout the sample set, were performed by replicating
analyses of individual field samples (see Appendix B). These recount measurements comprised
approximately l O percent of the total number of samples analyzed. The precision values of recount
measurements that were above 1 pCi/m2 -sec, expressed as relative percent difference (RPD), ranged
from 3.2 to 5.1 percent RPD with an average RPO of approximately 4.2 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 -1.7 percent to +0.7 percent. The arithmetic average bias of the lab
control sample measurements was approximately -0.7 percent (see Appendix A).
7.4 Completeness
One hundred samples from the Cell 2 cover region were verified, representing 100 percent
completeness.
5
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.
In practice, radon flux rates were calculated by a database computer program. The algorithms utilized
by the data base program were as follows:
Equation 8.1:
pCi Rn-222/m2sec = [Ts• A •b•~.5(.l.AJl.13)
where: N = net sample count rate, cpm under 220-662 ke V peak
Ts = sample duration, seconds
b = instrument calibration factor, cpm per pCi; values used:
0.1698, forM-01/D-21 and
0.1701, 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, 2u = 2 X -'--------------------X Sample Concentration
Net,cpm
Equation 8.3:
LLD -2.71 + {4.65){S~
-[Ts* A •b•o.s(tl/'J ·7s>1
where: 2. 71 = constant
4.65 = confidence interval factor
Sb = standard deviation of the background count rate
Ts = sample duration, seconds
b = instrument calibration factor, cpm per pCi; values used:
0.1698, forM-01/D-21 and
0.1701, for M-02/D-20
d = decay time, elapsed hours between sample mid-time and count mid-time
A = area of the canister, m2
6
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.
(b) The mean radon flux for the total uranium mill tailings pile shall be calculated as follows:
J.i.A1 + · · · J,AJ. [+] · · · JAi
A,
Where: J9 = 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."
7
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 = 0.9 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 = 0.9 pCi/m2-s
(0.9)(270,624) = 0.9
270,624
As shown above, the arithmetic mean of the radon flux rate measurements representing the second
half of the year 2017 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.
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.
8
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 2017.
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 2017.
9
Figure 1
Large Area Activated Charcoal Canisters Diagram
fHlUil[
10
I .in fn·c~
9crubtlw, P•J
\/2,,•. ,~.,~
S:,uh~• Pu
I '2•i11 Tin..:::c CJ1~rcUa•
.S1.Jp.'°'o,1lf;r..J
il•1.1o1ner
Sp11n9
I 0-111 "'" PYC E,,-, C.:tfl
Appendix A
Charcoal Canister Analyses Support Documents
A
ENERGY FUELS RESOURCES
WHITE MESA MILL, BLANDING, UTAH
2017 NESHAPs RADON FLUX MEASUREMENTS
CELL2
SAMPLING DATES: 07/15/17-07/16/17
ANALYSIS DATES: 07/18/17-07/19/17
SYSTEM COUNT 8kg Counts (1 min. each)
1.0. DATE #1 #2
M-01/0-21 7/18/2017 132 132
M-01/D-21 7/18/2017 122 131
M-01/0-21 7/19/2017 124 110
M-01/D-21 7/19/2017 120 119
M-01/0-21 7/18/2017 132 132
M-01/D-21 7/18/2017 122 131
M-01/D-21 7/19/2017 124 110
M-01/D-21 7/19/2017 120 119
M-02/D-20 7/18/2017 128 132
M-02/D-20 7/18/2017 116 154
M-02/0-20 7/19/2017 149 118
M-02/D-20 7/19/2017 119 140
M-02/D-20 7/18/2017 128 132
M-02/0-20 7/18/2017 116 154
M-02/0-20 7/19/2017 149 118
M-02/0-20 7/19/2017 119 140
#3
121
118
141
144
121
118
141
144
151
131
156
112
151
131
156
112
ACCURACY APPRAISAL TABLE
SECOND HALF 2017
Source Counts (1 min. each)
#1 #2 #3
10140 10270 10334
10399 10183 10170
10124 10173 9978
10132 10122 10136
9995 10172 9977
9988 10266 10189
10059 10109 9950
9954 10123 10152
10157 . 10112 10169
10107 10353 10074
10139 10073 9954
9969 10230 10022
10137 10199 10156
10192 10122 10338
10215 10120 10235
10289 10151 10152
AVG NET YIELD FOUND SOURCE
cpm cpm/pCi pCi ID
10120 0.1698 59598 GS-04
10127 0.1698 59641 GS-04
9967 0.1698 58697 GS-04
10002 0.1698 58907 GS-04
9920 0.1698 58420 GS-05
10024 0.1698 59034 GS-05
9914 0.1698 58388 GS-05
9949 0.1698 58590 GS-05
10009 0.1701 58842 GS-04
10044 0.1701 59050 GS-04
9914 0.1701 58285 GS-04
9950 0.1701 58495 GS-04
10027 0.1701 58948 GS-05
10084 0.1701 59281 GS-05
10049 0.1701 59077 GS-05
10074 0.1701 59222 GS-05
AVERAGE PERCENT BIAS FOR ALL ANALYTICAL SESSIONS:
KNOWN %BIAS
pCi
59300 0.5%
59300 0.6%
59300 -1.0%
59300 -0.7%
59300 -1 .5%
59300 -0.4%
59300 -1.5%
59300 -1.2%
59300 -0.8%
59300 -0.4%
59300 -1.7%
59300 -1.4%
59300 -0.6%
59300 0.0%
59300 -0.4%
59300 -0.1%
-0.7%
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: w ~' 4--< M-Lz'\ ;V\ ~ \ I ) '"BI din ch w'l..::J) Y. :Mb
CLIENT: E n-e. ,r j ~ \-Vv{. \ s & So u.,-.r C.f ~ (_ l,\ s A~
Calibration Check Log
System ID: tv\. -o \ / J) -2-\ Calibration Date: "1 ) 11 / t J Due Date: l} l 1 / L'3
Scaler S/N: .':, l S 12. High Voltage: I l ~) Window: ---'4 .... .4..._2_ Thrshld: 2.20
Detector SIN: _ _,C,,c__'i:~l .... S"'--3_"3=-----Source ID/SN: 'Rrl~~~-0 4 Source Activity: 59 '3 "'-f C,j
Blank Canister Bkgd. Range, cpm: 2 o = --=--1 _0_(,--'-----to __ l-'5""--'\.____ 3 o = CJ 5" to l l./2..
Gross Source Range, cpm: 2o= 0)~5"\ to lOL\S"B to ros~s
Technician: ::9:t Ce,.g, c,,., I
All counts times are one minute.
Date By Background Counts (1 min. each) Source Counts (1 min. each• ok?
#1 #2 #3 Av2. #1 #2 #3 Average YIN
"1 1€,J n i,,-7~ 1~"2-1--z,--z_ 11.1 I 2-'B 10,ut"1 t-n"2 -,n (0°2, ~lf 102-48 'i -, li\3 / V'] l~.-J-)'"l... "'l-,~ \ llto \ ""2..'t I Q "":a,. 0)0\ lnl ~.-,_ ID1-iO 10251 y -, JO) j Ii ~ I '1..L\-"0 / 4' \2 c;-l O l'L'-t tC'\l-J~ Qq'""'J~ to~·-z... "I
7 ',q I 1'7 ~ '-in r '°' ,LJc+ 1 "2.PJ lfll~f2-1012.."2,., IOI~(., t0130 ..t./
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, \rJ~,~ M-e-~ M: H :?i [., nd"l > ;th
CLIENT, Ev--e.01:Jy t"'e.\s R-LS::.Mt~ _ 4~_
Calibration Check Log
System ID: _M ___ -_0_\_/ ............. 1).._·_-_2. ___ \ __ Calibration Date: '/ I 1 / I 7 Due Date: 1 / 17 / I 8
Scaler S/N: ___ ~5_\_5_1_"'1.... ____ High Voltage: \ l (,3 Window: _ ...... 4 ..... .4 ..... 2_ Thrshld: __...2 ..... 2-0 __
Detector SIN: _Q __ '::\..,._....t 5_3_?~---Source ID/SN: '.R,q"'l.U/c,.s-o.$ Source Activity: So> ,3 ~ p C..i_
Blank Canister Bkgd. Range, cpm: 2 cr = __ l_O~lp~-to __ l 5_)~-3 cr = q~ to l(,,1-
Gross Source Range, cpm: 2a= 90)£...\6 to 10435 3 a= 0€,2.7 to
Technician: # k ~,..._ )?U..
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
,IL8 r1 ~. u \ ') '"2-\ °2,L-\ ..,_, l i--t? OiOA, lO l1"'2-o.~-,...., ( .:;c)L--1 '0 y
'1 J t0 I If 7, ~ l "7-'1.,, l-?, \ \ f? l r l.>"f '1\0) ~P, 1f'T> ,.,~ 10\ ~O) 1014-B ''I
1 , l~ Ii, ~ L \ '1--4' 11u IY\ \ 7->5 I or>c:;-q lnLOO\ qo,~D (00"3~ " -, I c,i /n D !..<.. \ r /.,,0 \IQ I 't'-1 \~ qoic;-u· 1~1"7"°'1 ' D \ c::;-J_. 1007~ "' I
YIN: Y = average background and source cpm falls within the control limits.
N = average background and source cpm does not fall witltin the control limits.
The acceptable ranges were determined from prior background and source check data.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: W"'.~.\-e M-t.'A M~\\,:B lta.V\d ~ ~) \.A, k ~
cLIENT: ·E.vl-e_"~'t F\A..e.( s R-eScM-V'c..t s (u S4)
Calibration Check Log
System ID: _tv\.___;_ ... _0_"2..~,,_/_j) ___ -_2.._0 ___ Calibration Date: 7 / (:J / /7 _ Due Date: , / t1 / a 'S
Scaler SIN: __ ...;:S:;;..._l _S_t.o_""3 ____ High Voltage: 8 e 0 Window: 4.42 Thrshld: 2.20
DetectorSIN:_O_L\.,..:_l =~-:>_L-_____ Source ID/SN:~ -Ui&s-oy Source Activity: S),3K1>C:
Blank Canister Bkgd. Range, cpm: 2 a = l 10 to lS:J 3cr= 9 8 to LCo 8
Gross Source Range, cpm: 2 cr = gv) 52,. to / 0 1± S 8 3 o = ____:.q ___;_S_l ...,,,.'3:...__ to l O (., "2 .. L..
Technician: __ )22..ei;;.,""--~--_.&e~;µ~~f':--:::"'.=--.....1~=~=-
All counts times are one minute.
Date By Bacbround Counts ( l min. each) Source Counts (l min. each ok?
#1 #2 #3 An. #1 #2 #3 Average YIN
7{t0Jt, VJ_./) 1·2.6 \ 7>'2. 151 ,-~7 tDLS'-7 I 0\.\-Z-10 ILP'-1 iOtY.l.P 'I
11 i '8117 PU I l lA I 5"4-\ 31 1~4 t0l0"'7 l rv:;r,.:::::~ 1t~o,c. 101~9) ·v
,/ A J ,-, bU.-1 l..f-0 \ '~ IS'l" I ....a..\ lO L 7.0l trrn~ aQt<c.J 100~-5 1../
--f) 10\ / ,1 I~ t I°' 140 \ ' '1-l""J....~ qo,vO) I ,c-,""7_ -:z.n 11~0""2"'2 i007Lf-" '
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.
CHAR.COAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: \JJ k ::\::e: M e5t'\ M ~ \ \ ,1s1~~ d\ via ) Lt+'\ ~
CLIENT: C\/\-ev~'f h-A.-e.. \s ~esou.ru, (_ \..l. SA')
Caljbratjon Check Log
Calibration Date: 1 / L 1 / t ] System ID: -~~--0_"'2..___,}..._"D __ -2_0 __ _,
Scaler SIN:---~--..;;..\ _5..__,,l,..._3~--High Voltage: 008 Window: 4.42 Thrshld: 2.20
Due Date: '1 / 1 1 / t 13
Detector SIN: __,O_'::\...__t 5:_3 ___ 1 ____ Source ID/SN: ~t>,'2:21., /cs ~~ource Activity: ~. "> K..p G"
Blank Canister Bkgd. Range, cpm: 2 a = \LO to l5'] 3a= '7B to 1~8
Gross Source Range, cpm: 2a= OJ0,1 I to 101...\<,0 3a= Glt?Y.v) to [05"°S"2
Technician: Pt-~ ~
All counts times are one minute
Date By Backe•ound Counts (I min. each) Source Counts ( 1 min. each) ok?
#1 #2 #3 Avl!.. #1 #2 #3 Averal?e YIN
1 L1' /17 blJ l"2~ ,~-z.. IS" l 1"3-, fnl.a.., u~, 0\ 0\ U''I\ Ct., 1n1 ldJ V
11 J ,a J ,, t,L.,e. ll t. tc:4 l?,' r?>~ L In IQ\...,_ I r11 -z..'1-10"::l.<.0. fl") '21"7 ....;
7 I ioj /l 1 ~ l~O) ,-, ,;>, IC,(_ I LJ 1&2..\~ lO\ '"2.0 f.0~"3C ,o ,o,n ..:1
7J lg/i, .l>Lt!-llt!J l '-10 \1-'2-12.l.. lt>~O"'\ l0l5 I ,-t~1 IOI~, "' , 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 determined from prior background and source check data.
BALANCE OPERATION DAILY CHECK
Balance Model: 0 h.OL IA. s ? or+-'i),.. ~ VZ>J M s N : / 2.. "307
Standard Weight (g): __ =>_O_O_r_O_~.J.----------
Date Pre-check (g) Post-check (g) O.K. :t 0.1 % ? By
7 /, e/ ,, 300,0 ·2-qq .O) 'I~ ~L,-.
-,J,q/1, I ~L_ ·300_0 300.0 v-es
' 7
Appendix B
Recount Data Analyses
B
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: 62°F
AREA: COVER DEPLOYED: 7 15 17 RETRIEVED: 7 16 17 CHARCOAL BKG:
FIELD TECHNICIANS: CE,DLC, WC,TE,CS COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM 1.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
RECOUNT CANISTER ANAL YSlS:
149
PROJECT NO.: 17004.03
WEATHER: CLEAR, NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
g.
g.
GRID SAMPLE RETRIV ANALYSIS MID-TIME CNT GROSS GROSS RADON ± LLD PRECISION
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m's pCi/m's pCi/rn's % RFD
FlO FlO 6 52 6 51 7 18 17 14 50 3 1172 228.2 0.5 0.1 0.04
RECOUNT FlO 6 52 6 51 7 19 17 ll 29 3 1123 228.2 0.6 0.1 0.05 8.6%
F20 F20 7 6 6 57 7 18 17 15 6 2 1489 226 .1 1.3 0.1 0.04
RECOUNT F20 7 6 6 57 7 19 17 11 6 2 1290 226.1 1.3 0.1 0.05 3.2%
F30 F30 6 52 6 51 7 18 17 15 28 3 1238 228.8 0.6 0.1 0.04
RECOUNT F30 6 52 6 51 7 19 17 11 28 3 1158 228.8 0.6 0.1 0.05 4.4%
F40 F40 7 6 6 57 7 18 17 15 43 1 1444 229.3 2.8 0.3 0.04
RECOUNT F40 7 6 6 57 7 19 17 11 43 1 1207 229 .3 2.7 0.3 0.05 5.1%
F50 F50 6 52 6 51 7 18 17 16 3 3 1011 226.4 0.4 0.1 0.04
RECOUNT F50 6 52 6 51 7 19 17 11 3 4 1256 226.4 0.4 0.1 0.05 1.3%
F60 F60 7 6 6 57 7 18 17 16 22 1 1004 228 .7 1.9 0 .2 0 .04
RECOUNT F60 7 6 6 57 7 19 17 11 22 2 1717 228.7 1. 8 0.2 0.05 4.3%
F70 F70 6 48 7 50 7 18 17 16 44 3 1215 231.4 0.5 0.1 0.04
RECOUNT F70 6 48 7 50 7 19 17 11 44 3 1223 231.4 0.6 0.1 0.04 15.4%
F80 F80 7 12 7 0 7 18 17 17 11 6 1127 218.7 0.1 0.0 0.04
RECOUNT F80 7 12 7 0 7 19 17 11 11 6 1188 218.7 0.1 0.0 0.05 36.4%
F90 F90 7 9 6 59 7 18 17 17 34 3 1377 225.4 0.7 0.1 0.04
RECOUNT F90 7 9 6 59 7 19 17 11 34 3 1299 225.4 0.7 0.1 0 .05 4.8%
FlOO FlOO 7 10 7 0 7 18 17 18 0 4 1136 220.3 0 .3 0 .0 0 .04
RECOUNT FlOO 7 10 7 0 7 19 17 11 0 4 1008 220.3 0.3 0.0 0.04 0.0%
AVERAGE PERCENT PRECISION FOR THE CELL 2 COVER REGION: 8.4%
Paae 1 of 1
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: 62°F
AREA: COVER DEPLOYED: 7 15 17 RETRIEVED: 7 16 17 CHARCOAL BKG:
FIELD TECHNICIANS: CE,DLC, WC,TE,CS COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM 1.0.: M01/D21, M02/D20 CAL. DUE: 7/17/18
149
PROJECT NO.: 17004.03
WEATHER: CLEAR, NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV Al-r"ALYSIS 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/m2 s pCi/m' s pCi/m' s COMMENTS:
FOl FOl 6 40 6 47 7 18 17 14 30 4 1091 225.8 0.3 0.04 0.04
F02 F02 6 41 6 47 7 18 17 14 30 4 1246 229.9 0.3 0.04 0.04
F03 F03 6 42 6 48 7 18 17 14 35 5 1138 227.4 0.2 0.04 0.04
F04 F04 6 44 6 48 7 18 17 14 35 5 1197 225.6 0.2 0.04 0.04
F05 F05 6 45 6 49 7 18 17 14 40 4 1148 229.9 0.3 0.04 0.04
F06 F06 6 46 6 49 7 18 17 14 40 4 1105 229.3 0.3 0.04 0.04
F07 F07 6 48 6 50 7 18 17 14 45 4 1166 229.2 0.3 0.04 0.04
FOB FOB 6 49 6 50 7 18 17 14 45 4 1144 228.3 0.3 0.04 0.04
F09 F09 6 50 6 51 7 18 17 14 50 4 1228 228.0 0.3 0.04 0.04
FlO FlO 6 52 6 51 7 18 17 14 50 3 1172 228.2 0.5 0.05 0.04
Fll Fll 6 53 6 52 7 18 17 14 54 2 1153 228.1 0.9 0.09 0.04
Fl2 Fl2 6 54 6 52 7 18 17 14 54 2 1048 228.4 0.8 0.08 0.04
Fl3 Fl3 6 56 6 53 7 18 17 14 57 2 1087 229.0 0.9 0.09 0.04
Fl4 Fl4 6 57 6 53 7 18 17 14 57 2 1096 230.3 0.9 0.09 0.04
Fl5 F15 6 59 6 55 7 18 17 15 1 3 1011 230.7 0.4 0.05 0.04
F16 Fl6 7 1 6 55 7 18 17 15 1 3 1002 230.2 0.4 0.05 D.04
F17 F17 7 2 6 56 7 18 17 15 4 1 1036 230.4 1.9 0.19 0.04
F18 Fl8 7 3 6 56 7 18 17 15 4 l 1805 229.4 3.6 0.36 0.04
F19 Fl9 7 5 6 57 7 18 17 15 6 1 3776 229.3 7.9 0.79 0.04
F20 F20 7 6 6 57 7 18 17 15 6 2 1489 226.1 1.3 0.13 0.04
F21 F21 6 40 6 47 7 18 17 15 9 3 1016 226.8 0.4 0.05 0.04
F22 F22 6 41 6 47 7 18 17 15 8 1 1352 229.3 2.6 0.26 0 .04
F23 F23 6 42 6 48 7 18 17 15 13 4 1001 227.2 0.2 0.04 0.04
F24 F24 6 44 6 48 7 18 17 15 l3 3 1004 226.0 0.4 0.05 0.04
F25 F25 6 45 6 49 7 18 17 15 18 4 1116 228.7 0.3 0.04 0.04
F26 F26 6 46 6 49 7 18 17 15 18 3 1003 227.5 0.4 0.05 0.04
F27 F27 6 48 6 50 7 18 17 15 23 5 1092 231.5 0.2 0.04 0.04
F28 F28 6 49 6 50 7 18 17 15 23 4 1201 232.1 0.3 0.04 0.04
F29 F29 6 50 6 51 7 18 17 15 28 3 1160 233.8 0.5 0.05 0.04
F30 F30 6 52 6 51 7 18 17 15 28 3 1238 228.8 0.6 0.06 0.04
F31 F31 6 53 6 52 7 18 17 15 31 2 1779 229.8 1. 6 0.16 0.04
F32 F32 6 54 6 52 7 18 17 15 31 2 1294 230.9 1.1 0.11 0.04
F33 F33 6 56 6 53 7 18 17 15 35 4 1165 230.5 0.3 0.04 0.04
F34 F34 6 57 6 53 7 18 17 15 35 3 1223 229.6 0.6 0.06 0.04
F35 F35 6 59 6 55 7 18 17 15 39 3 1228 228.8 0.6 0.06 0.04
F36 F36 7 1 6 55 7 18 17 15 39 2 1002 227.3 0.8 0.08 0.04
F37 F37 7 2 6 56 7 18 17 15 42 1 1004 232.6 1. 9 0.19 0.04
Paqe 1 of 3
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: F SURFACE: SOIL AIR TEMP MIN: 62°F
AREA: COVER DEPLOYED: 7 15 17 RETRIEVED: 7 16 17 CHARCOAL BKG:
FIELD TECHNICIANS: CE,DLC, WC,TE,CS COUNTED BY: DLC DATA ENTRY BY: DLC
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
149
PROJECT NO.: 17004.03
WEATHER: CLEAR, NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV ANALYSIS MID-TIME ciIT GROSS GROSS RADON ± LLD
g.
g.
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m2 s pCi/m' s pCi/m' s COMMENTS:
F75 F75 6 41 6 47 7 18 17 16 58 3 1072 228.5 0.5 0.05 0.04
F76 F76 6 40 6 47 7 18 17 16 59 5 1091 231. 8 0.2 0.04 0.04
F77 F77 7 8 6 59 7 18 17 17 4 3 1126 222.7 0.5 0.06 0.04
F78 F78 7 9 6 59 7 18 17 17 5 5 1104 218.3 0.2 0.04 0.04
F79 F79 7 10 7 0 7 18 17 17 10 3 1045 225.6 0.4 0.05 0.04
F80 F80 7 12 7 0 7 18 17 17 11 6 1127 218.7 0.1 0.03 0.04
F81 F81 7 13 7 1 7 18 17 17 17 5 1154 224.0 0.2 0.04 0.04
F82 F82 7 14 7 1 7 18 17 17 17 5 1171 217.1 0.2 0.04 0.04
F83 F83 7 16 7 2 7 18 17 17 21 3 1156 218.7 0.5 0.06 0.04
F84 F84 7 16 7 2 7 18 17 17 22 5 1095 231.6 0.2 0.04 0.04
F85 F85 6 52 6 52 7 18 17 17 27 3 1003 228.3 0.4 0.05 0.04
F86 F86 6 53 6 52 7 18 17 17 27 3 1151 229.3 0.5 0.06 0.04
F87 F87 6 54 6 53 7 18 17 17 31 3 1258 231.2 0.6 0.06 0.04
F88 F88 6 56 6 53 7 18 17 17 31 3 1399 232.1 0.7 0.07 0.04
F89 F89 7 8 6 59 7 18 17 17 35 5 1001 216.0 0.1 0.04 0.04
F90 F90 7 9 6 59 7 18 17 17 34 3 1377 225 .4 0.7 0.07 0.04
F91 F91 7 10 7 0 7 18 17 17 41 5 1193 215.9 0.2 0.04 0.04
F92 F92 7 12 7 0 7 18 17 17 41 5 1162 225.5 0.2 0.04 0.04
F93 F93 7 13 7 1 7 18 17 17 47 5 1000 221.8 0.1 0.04 0.04
F94 F94 7 12 7 0 7 18 17 17 47 5 1001 219.0 0.1 0.04 0.04
F95 F95 7 13 7 1 7 18 17 17 52 4 1053 218.9 0.3 0 .04 0.04
F96 F96 7 14 7 1 7 18 17 17 52 4 1047 218.8 0.3 0.04 0.04
F97 F97 6 58 6 55 7 18 17 17 55 1 1945 227.4 4.0 0.40 0.04
F98 F98 7 8 6 59 7 18 17 17 56 3 1303 233.0 0.6 0.06 0.04
F99 F99 7 9 6 59 7 18 17 18 1 6 1039 222.3 0.1 0.03 0.04
FlOO FlOO 7 10 7 0 7 18 17 18 0 4 1136 220.3 0.3 0.04 0.04
AVERAGE RADON FLUX RATE FOR THE CELL 2 COVER REGION: 0.9 pCi/m2 s
0.1 MIN
BLANK CANISTER ANALYSIS: 7.9 MAX
GRID Si\MPLE RETRIV ANALYSIS MID-TIME CNT GROSS GROSS RADON :t LLD
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m' s pCi/m' s pCi/m' s COMMENTS:
F BLANK 1 F BLANK 1 6 30 6 40 7 18 17 11 5 10 1649 209.0 0.03 0.03 0.04 CONTROL
F BLANK 2 F BLANK 2 6 30 6 40 7 18 17 11 5 10 1575 209.3 0.02 0.03 0.04 CONTROL
F BLANK 3 F BLANK 3 6 30 6 40 7 18 17 11 16 10 1625 212.0 0.03 0.03 0.04 CONTROL
F BLANK 4 F BLANK 4 6 30 6 40 7 18 17 11 16 10 1569 209.6 0.02 0.03 0.04 CONTROL
F BLANK 5 F BLANK 5 6 30 6 40 7 18 17 11 27 10 1699 209.1 0.04 0.03 0.04 CONTROL
AVERAGE BLANK CANISTER ANALYSIS FOR THE CELL 2 COVER REGION: 0.03 pCi/m2 s
Page 3 of 3
Appendix D
Sample Locations Map (Figure 2)
D
-CELL 1-
\ I 0 0 0 0 0 0 0 0 0 0 0 0 0 I F01 F02 F03 F04 F05 F06 F07 FOB F09 F10 F11 F12 F13
0 0 0 0 0 0 0 0 0 0 0 0 0 F21 F22 F23 F24 F25 F26 F27 F28 F29 F30 F31 F32 F33
0 0 0 0 0 0 0 0 0 0 F44 F45 F46 F47 F48 F49 FSO F51 F52 F53
-CELL2-F76 o 0 0 0 0 0 0 0 F74 F73 F72 F71 F70 F69 F68
0 0 0 F86 F85 FB4
-CELL3-
-CELL4B-
-CELL4A-
0 0 0 0 F14 F16 F17 FlB
0 0 0 0 0 F34 F35 F36 F37 F38
0 0 0 0 0 F54 FSS FS6 F57 F58
0 0 0 0 0 F67 F66 F65 F64 F63
0 0 0 0 0 F83 F82 FBl FBO F79
0 0 0 0 F94 F93 F92 F91
0 0
F19 F20
0 0 F39 F40
0 0 F59 F60
0 0 \ F62 F61
0 0 • F78 F77
0 0 F90 F89
WHITE MESA MILL
BLANDING. UTAH
NESHAPS 2017
CELL2
SECOND HALF 2017
07/15/17-07/16/17
PREPARED FOR
ENERGY FUELS RESOURCES
lliillID.
F01 0 -SAMPLE LOCATION ON
COVERED AREAS
FIGURE 2
N
t
SCALE IN FEET ---200 100 0 200 400 ,,,,,o
ENVIRONMENTAL, LLC
THIS DRAWING IS THE PROPERTY OF TELLCO
ENVIRONMENTAL, LLC, AND IS NOTTO BE
REPRODUCED, MODIFIED OR USED FOR ANY
OTHER PROJECTOR EXTENSION OF THIS PROJECT
EXCEPT BY AGREEMENT WITH TELLCO.