DRC-2018-009083 - 0901a068808bcfd8

ENERGY FUELS
Energy Fuels Resources (USA) Inc. 225 Union Blvd. Suite 600 Lakewood, CO, US, 80228 303 974 2140
yavw.encrgyfuels.cotll
Div of Waste Management
August 29, 2018 and Radiation Control
AUG 3 1 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:
Dr\c,-zoce)-001O63
Re: State of Utah Radioactive Nlaterial IAcense No. 0T1900479
White Mesa Mill, Blanding, Utah
Semi-Annual Effluent Monitoring Report for Period
January 1 through June 30, 201.8
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 January 1 through June 30, 2018.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
Yours vel trruly,
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Terry Slade
Scott A. Bakken
Logan Shumway
Paul Goranson
drbi
August 29, 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.energyfuels.com
Re: State of Utah Radioactive Material License No. UT1900479
White Mesa Mill, Blanding, Utah
Semi-Annual Effluent Monitoring Report for Period
January 1 through June 30, 2018
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 January 1 through June 30, 2018.
If you have any questions regarding this report, please contact the undersigned at (303) 389-
4134.
;~er~
ENERGY FUELS RESOURCES (USA) INC.
Kathy Weinel
Quality Assurance Manager
cc: David C. Frydenlund
Terry Slade
Scott A. Bakken
Logan Shumway
Paul Goranson
White Mesa Uranium Mill
Radioactive Materials License UT900479
Semi-Annual Effluent Monitoring Report
(January through June 2018)
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
August 29, 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 ........................................................................................... 4
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 ........................................................................................ 10
10.0 SIGNATUREANDCERTIFICATION ................................................................ 11
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
ii
WHITE MESA URANIUM MILL
SEMI-ANNUAL EFFLUENT REPORT, JANUARY THROUGH JUNE 2018
1.0 INTRODUCTION
The White Mesa Mill (the "Mill") has established monitoring programs to evaluate
compliance with effluent limitations and to assess the potential for release of radioactive
material into the local environment. These monitoring programs were developed and
implemented at the time of Mill construction, operated with appropriate adaptation over
time, and are consistent with the Mill's State of Utah Radioactive Materials License No.
UT1900479 (the "License") and guidelines developed by the United States Nuclear
Regulatory Commission ("NRC") (NRC Regulatory Guide 4.14, Radiological Effluent
and Environmental Monitoring at Uranium Mills-Rev. 1, ML003739941), 1980).
1.1 Modifications to the Monitoring Programs
As stated above, the monitoring programs implemented to date are consistent with the
Mill's License and guidelines developed by the NRC and described in Regulatory Guide
4.14. The Mill's License modifies and expands the effluent monitoring programs
implemented at the Mill beyond what is regularly required by NRC Regulatory Guide
4.14. Specific changes to the individual monitoring programs are discussed in the
subsequent sections of this report.
In a letter dated July 23, 2014, DWMRC stated that because "Tailings Cell 2 is no longer
in operation (receiving tailings), the Division of Air Quality and the Division of
Radiation Control agree that Subpart W NESHAPs requirements ( 40 CFR Part 61) no
longer apply; however, at this phase of cell 2 closure activities, the requirements of 10
CFR Part 40, Appendix A, Criterion 6 do apply." The July 23, 2014 letter further
requires that radon flux measurements for Cell 2 be collected semi-annually in
accordance with methodology specified in 40 CFR Part 61, Appendix B, Method 115 and
that the measured results be included in the Semi-Annual Effluent Reports submitted to
DWMRC. As a result of the July 23, 2014 letter, Cell 2 radon flux monitoring data are
reported herein. Additional details regarding the monitoring and data collection activities
for the Cell 2 radon flux are included in Section 9.0.
As specified by the License and the documents described above, the Mill monitors the
following environmental media and conditions:
a) Airborne particulate radionuclide concentrations obtained from the following
sampling stations:
• North, east and south of the Mill Site: BHV-1, BHV-2, and BHV-8
(north), BHV-5 and BHV-7 (east), and BHV-4 (south). BHV-1 and BHV-
8 serve as surrogates for the nearest resident (BHV -1 and BHV-8 are
1
approximately 1.2 miles north of the Mill, but approximately 0.4 miles
closer to the Mill than the nearest resident);
• A background location distant to and west of the Mill (BHV-3) that was
monitored for airborne particulates up until November, 1995 (at which
time background was established), which is no longer monitored for air
particulates; and
• A station specifically requested by the White Mesa Ute Community south
of the Mill Site (BHV-6);
b) External ( direct) gamma radiation measured at air monitoring stations BHV-1,
BHV-2, BHV-3, BHV-4, BHV-5, BHV-6, BHV-7, and BHV-8;
c) Vegetation at three site periphery locations, for uptake of radionuclides;
d) Stack release rates from the Mill's air emissions sources;
e) Surface water at Cottonwood Creek and, when flowing, Westwater Creek, both
located west of the Mill;
f) Soil radionuclide activity during the third quarter of each year;
g) Radon-222 at the air particulate monitoring stations (BHV-1 through BHV-8);
h) Meteorological conditions;
i) Radon flux of the Cell 2 cover as specified by the DWMRC in correspondence
dated July 23, 2014;
j) Groundwater (up and down gradient) of the Mill facility; and 1
k) Seeps and springs in the vicinity of the Mill.1
This semi-annual effluent report provides the results of the specific monitoring and
sampling activities that were undertaken during the subject reporting period.
2.0 ENVIRONMENTAL AIR PARTICULATE SAMPLING
2.1 Program Overview
Prior to 2014, the environmental airborne particulate monitoring program at the Mill
utilized four air sampling stations. Four high-volume continuous air sampling stations
(BHV-1, BHV-2, BHV-4, and BHV-5) were required by the License. In addition to these
1 Groundwater sampling and seeps and springs sampling are reported separately pursuant to the Mill's State
of Utah Ground Water Discharge Permit No. UGW370004, and are not included with this report.
2
four environmental air sampling locations, an additional station (BHV-6) was installed at
the request of the White Mesa Ute Community. This station began operation in July of
1999 and provides airborne particulate information in the southerly direction between the
Mill and the White Mesa Ute Community.
As stated in Section 1.1 above, the air 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 QNQC information) reported
by the laboratory for the reporting period are provided under Attachment C. In addition to
the analyses for radionuclides, particulate loading is determined for each filter and
composited as a quarterly mass-loading estimate for review purposes only. Graphs
showing particulate loading at each station and the underlying data are included as
Attachment D.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. The analytical data are usable for their intended purpose.
Any deviations noted did not affect the quality or usability of the data.
For graphical illustration purposes, values reported at zero, values reported at less than
the pre ·cribed detection limit ( < 1 x 10-16 uCi/rnl), 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/rnl), the detection limit
concentration was utilized for plotting the data point. This graphing convention is not
utilized to formulate station average information, nor is it intended as a precedent for data
treatment. Rather, the intent is to provide a conservative viewable depiction of site
airborne radionuclide information. This is considered to be a conservative approach,
because the actual concentration below the detection limit cannot be determined and, as a
result, the plotted point will be at the same or a higher concentration than the actual
activity concentration of the collected sample.
2.3 General Observations
The results of environmental air monitoring for this semi-annual period indicate that for
all radionuclides at all monitoring stations, airborne radionuclide particulate activity
concentrations were well below regulatory Effluent Concentration Limits ("ECL's") and
the Mill's ALARA goals, which are set at 25% of the ECLs, except as noted below.
It is 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
4
are carried with the air. Pb-210 is the longest lived of these decay products and is the
decay product of the shorter-lived radon progeny. As such, it accumulates as an electrical
attachment on the natural ambient dust in the atmosphere and is generally measured at
elevated activity when compared to local decay-chain parent radionuclide activity,
regardless of uranium milling activity. At the Mill's BHV air monitoring stations, all
dust (ambient natural and mill derived) is collected by the sample filter. Because of the
natural elevation of Pb-210 accumulated as an attachment to the naturally occurring
ambient dust particles collected by the air sampling equipment, Pb-210 is commonly
elevated and in disequilibrium when compared to parent radionuclide activity, regardless
of the Mill's presence. By way of illustration, average ground-level concentrations have
been reported for selected States (NCRP Report 94, 1992) and are summarized in Table 1
in the Tables Tab of this report, demonstrating that elevated Pb-210 activity is present
where no uranium milling operations are located nearby. In April 1977, prior to Mill
construction and Mill operations, air particulate Pb-210 was measured at the Mill site to
be 1. 3 E-14 u Ci/ml ( 13. OE-3 pCi/m3)2.
2.4 Site Specific Sampling Data
The results of airborne particulate monitoring for the period (without background
subtraction) are provided by sampling station and radionuclide in Tables 2 through 6 in
the Tables Tab of this report. Along with these data, the tables present comparative
ECL' s and the ECL percentage measured at each of the monitoring stations sampled
during the period. A review of these data support the conclusion that airborne particulates
are well controlled at the Mill. In all cases, the measured activity concentrations were
well within the ECL, as well as the Mill's ALARA goal (i.e. 25% of the ECL). Lower
Limits of Detection consistent with NRC Regulatory Guide 4.14 were maintained by the
Mill's contract analytical laboratory for this reporting period.
The data obtained since program inception in 1981 indicates that only one individual
quarterly measurement (Th-230 at BHV-5 for the 2nd Quarter of 1996) has ever exceeded
the ECL at the Mill. While it is important to consider and evaluate an individual
measurement exceeding the ECL, it is the average annual concentration that is of primary
significance for public dose estimation purposes. In that instance, the average annual
concentration of Th-230 for BHV-5 in 1996 was well below the ECL. Data obtained
since program inception in 1981 also indicate that, with very few exceptions, the gross
(background inclusive) measurements do not exceed the site's ALARA goal (i.e. only ten
of the several thousand total gross radionuclide determinations to date exceeded the
Mill's self-imposed 25% ALARA goal).
2 See the Environmental Report, White Mesa Uranium Project, San Juan County, Utah for Energy Fuels
Nuclear, Inc. prepared by Dames & Moore, January 30, 1978, Section 2.9.1.1
5
2.5 Radon-222
With the approval of the NRC, Radon-222 monitoring at BHV stations at the Mill was
discontinued in 1995 due to the unavailability of monitoring equipment to detect the
revised 10 CFR Part 20 standard. Instead, compliance with these limits and the
requirements of R313-15-301 was demonstrated by a calculation, authorized by the NRC
and as contemplated by R313-15-302(2)(a) which states "A licensee or registrant shall
show compliance with the annual dose limit in Section R313-15-301 by: (a)
Demonstrating by measurement or calculation that the total effective dose equivalent to
the individual likely to receive the highest dose from the licensed or registered operation
does not exceed the annual dose limit;". This calculation is performed by use of the
MIT.DOS code for estimating environmental radiation doses for uranium recovery
operations. R313-15-302(2)(a) contemplates demonstrating compliance either through
modeling or measurement.
In order to determine whether or not detection equipment has improved since 1995, EFRI
voluntarily began ambient Radon-222 monitoring at the BHV stations in 2013. The
Radon-222 data collected from 2013 through present are presented in Attachment J. As
stated in Section 1.1 above, the Mill's effluent monitoring programs were expanded in
2014. The expanded monitoring programs require the collection of Radon-222 data at all
of the BHV stations. For the BHV stations EFRI calculated ECLs using methodology
shown in Attachment J. The calculated ECLs for all of the BHV stations are included on
the data table included in Attachment J. The radon-222 results are below the calculated
ECLs and within the range of historic levels as shown in Attachment J.
Radon-222 monitoring is completed using detectors with an effective reporting limit of
0.06 pCi/L. Field blank detectors are collected quarterly and the results (with
background included) are included in Attachment J.
During the reporting period, one field blank was collected during each quarter. Field
blanks are opened at the beginning of the monitoring period and immediately sealed in
the manufacturer supplied packaging. The field blanks are stored in the environmental
office until the end of the monitoring period, when they are packaged with the field
samples and shipped to the laboratory for processing. While relatively low concentrations
were reported for the field blanks, the field blank data show detections which are greater
than the highest detection reported for any of the samples collected at the high volume
stations. The field blank data have been consistently higher than the samples. Despite
the detections reported for the field blanks, there is no indication that the results reflect
contamination during shipping. If the detections on the field blanks indicated
contamination resulting from shipment, then all of the detectors would be affected in the
same manner and the sample data are below the field blank levels. It appears that the
field blanks have been affected by the storage prior to shipping. EFRI is conducting an
investigation into the possible causes of the anomalous field blank detections.
6
3.0 EXTERNAL RADIATION (DIRECT GAMMA)
Gamma exposure rate estimates were measured for the 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
The NRC Regulatory Guide 4.14 requires that three samples be collected during the
grazing season, without specifying exact months or times during the season. Two samples
were collected during the January through June reporting period. The third sample will
be collected during the July through December reporting period. As noted in Section 1.1,
Amendment 7 and the associated RFI expanded the vegetation sampling program through
the addition of Th-232 and U-Nat.
During the January through June reporting period, samples were collected on April 26,
and June 20, 2018. 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
2018 data results are within the variation of previous sampling episodes.
7
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
actual analytical results reported by the laboratory for the reporting period (first and
second quarters 2018) are provided in Attachment G to this report.
Stack sampling was not conducted during the first quarter of 2018 because the north
yellowcake dryer, south yellowcake dryer, grizzly and yellowcake baghouse did not
operate in the first quarter. The south yellowcake dryer and yellowcake baghouse
operated during the second quarter of 2018. Stack samples were collected from the south
yellowcake dryer and baghouse in the second quarter. The grizzly operated intermittently
during the second quarter 2018. A grizzly sample was inadve1tently omitted from the
second quarter sampling event because the operations were sporadic and intermittent.
The grizzly only operated to process Sequoyah Fuels materials and operated for very
short times in the second quarter. Each operation of the grizzly throughout the second
quarter was just a few hours and due to the limited operations was omitted. It is
8
important to note that the stack data are not collected as point of compliance
measurements and are not compared to regulatory limits. The stack data are used as
inputs into MIDOS modeling for estimating doses for uranium recovery operations.
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 the first or second quarter of 2018, because no water
was present during this reporting period. Attempts to collect a surface water sample from
Westwater Canyon will continue through the next reporting period. If no surface water is
available, a sediment sample will be collected as required.
The Mill's EPM requires that samples from Cottonwood Creek be analyzed for TDS and
total suspended solids ("TSS") quarterly, and the License, Part 11.2 B requires that
samples from Cottonwood Creek be analyzed for dissolved and suspended radionuclides
including Gross Alpha, U-nat, Ra-226, and Th-230 semi-annually. In accordance with
these requirements, Cottonwood Creek was sampled for TDS and TSS during the first
quarter. Cottonwood Creek was not sampled during the second quarter because no water
was present.
The field data sheets for the surface water sampling events, along with graphs showing
historic results are included as Attachment H.
Analytical data were reviewed against the laboratory established acceptance limits
specified in the data packages. No data issues were noted and the data are usable for the
intended purpose.
9
7.0 SOIL SAMPLING
In accordance with the Mill's EPM and License, surface soils will be collected during the
third quarter of 2018. The sampling results will be discussed in the July through
December Semi-Annual Effluent Report submitted to DWMRC on or before March 1,
2019.
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.
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 CPR Part 61) no longer apply;
however, at this phase of cell 2 closure activities, the requirements of 10 CPR 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 CPR
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 March 2018 for
the January through June 2018 reporting period. The March 2018 measurement was 3.1
pCi/(m2-sec). The March 2018 measurement was below the 20.0 pCi/(m2-sec) standard.
The full data report for the March 2018 Cell 2 radon flux sampling is provided in
Attachment K.
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.
10
10.0 SIGNATURE AND CERTIFICATION
This document was prepared by Energy Fuels Resources (USA) Inc.
Energy Fuels Resources (USA) Inc.
By:
g\zq\ \~
\ \ Date Scott A. Bakken
Senior Director Regulatory Affairs
11
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.
12
TABLES
Table 1-NCRP Report 94-Global Pb-210 Concentration Example
State Pb-210 Concentration
uBq{MJ uCi/ml
California 600 1.60E-14
Illinois 1500 4.lOE-14
Ohio 300 8.lOE-15
Massachusetts 700 1.90E-14
Ii
111
111
Table 2 -Air Monitoring Station Results U-Nat (Comparison to Limits) 1st
and 2nd Quarter 2018
Monitoring 1st 2nd Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl l.90E-l 6 8.00E-16 9.00E-14 5.SOE-01
BHV2 6.70E-17 3.80E-16 9.00E-14 2.48E-01
BHV4 6.80E-16 l .SOE-15 9.00E-14 J.21E+OO
BHVS 7.lOE-16 2.60E-15 9.00E-14 1.84E+OO
BHV6 l.20E-15 3.00E-15 9.00E-14 2.33E+OO
BHV7 4.lOE-16 l.60E-15 9.00E-14 l .l2E+OO
BHV8 2.30E-16 9.40E-16 9.00E-14 6.SOE-01
Table 3 -Air Monitoring Station Results Th-230 (Comparison to Limits)
1st and 2nd Quarter 2018
Monitoring 1st 2nd Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 5.30E-17 l .20E-16 2.00E-14 4.33E-01
BHV2 l .40E-17 4.60E-17 2.00E-14 l.SOE-01
BHV4 1.20E-16 8.20E-17 2.00E-14 5.0SE-01
BHVS l.70E-16 2.40E-16 2.00E-14 1.03E+OO
BHV6 1.1 OE-16 9.70E-17 2.00E-14 5.l 8E-Ol
BHV7 l .20E-16 2.20E-16 2.00E-14 8.SOE-01
BHV8 5.80E-17 l.20E-l 6 2.00E-14 4.45E-Ol
Table 4 -Air Monitoring Station Results Ra-226 (Comparison to Limits)
1st and 2nd Quarter 2018
Monitoring 1st 2nd Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCI/ml)
BHVl 9.20E-17 2.50E-16 9.00E-13 l.90E-02
BHV2 4.00E-17 l.20E-16 9.00E-13 8.89E-03
BHV4 5.70E-l 7 3.70E-17 9.00E-13 5.22E-03
BHVS J .SOE-16 5.90E-16 9.00E-13 4.l lE-02
BHV6 1.IOE-16 l.OOE-16 9.00E-13 l .17E-02
BHV7 2.60E-16 4.30E-16 9.00E-13 3.83E-02
BHV8 8.30E-l 7 3.00E-15 9.00E-13 l.71E-01
I
I
L
Table 5 -Air Monitoring Station Results Pb-210 (Comparison to Limits)
1st and 2nd Quarter 2018
Monitoring 1st 2nd Effluent Average
Station Qtr.Result Qtr.Result Concentration PercentECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCl/ml)
BHVl l.50E-I4 I .20E-I4 6.00E-13 2.25E+OO
BHV2 1.30E-I4 l.20E-14 6.00E-13 2.08E+OO
BHV4 1.40E-14 1. IOE-14 6.00E-13 2.08E+OO
BHV5 1.40E-14 1.20E-14 6.00E-13 2.17E+OO
BHV6 1.50E-I4 l.20E-I4 6.00E-13 2.25E+OO
BHV7 l.80E-14 l .20E-14 6.00E-13 2.50E+OO
BHV8 l.30E-I4 8.80E-I5 6.00E-13 l.82E+OO
Table 6 -Air Monitoring Station Results Th-232 (Comparison to Limits)
1st and 2nd Quarter 2018
Monitoring 1st 2nd Effluent Average
Station Qtr.Result Qtr.Result Concentration Percent ECL
(uCi/ml) (uCi/ml) Limit (ECL)
(uCl/ml) II
BHVI 5.30E-l 8 9.30E-I8 4.00E-15 I .83E-01
BHV2 5.30E-18 l .50E-17 4.00E-15 2.54E-Ol
BHV4 4.00E-18 l.20E-17 4.00E-15 2.00E-01
BHV5 2.00E-17 9.40E-l 8 4.00E-15 3.68E-Ol
BHV6 9.70E-17 9.00E-18 4.00E-15 l.33E+OO
BHV7 8.70E-I8 l.70E-17 4.00E-15 3.21E-0I
BHV8 5.IOE-18 8.50E-18 4.00E-15 1.70E-Ol
I
I
11
Table 7 -Environmental Optically Stimulated Luminescence Dosimeter
l\.1easurements ((;amma)
1st 2nd 1st Quarter ''2nd Quarter, £umulati~e.
Quarter Qua1:ter Result Less Re-Sult Less Semiannual
Monitoring Result Result Background Ba~kground Estimate
Station (mrem) (mrem) (mrem) Cmrem~ ~nirem~
BHVl 35 38.9 1 0 1
BHV2 34.1 41.3 0.1 2.2 2.3
BHV3 34 39.1 0 0 0
BHV4 32 39.8 0 0.7 0.7
BHV5 36 40.3 2 1.2 3.2
BHV6 31.2 37.4 0 0 0
BHV7 30.8 37.1 0 0 0
BHV8 30.1 37.6 0 0 0
Table 8 Stack Effluent Concentrations and Release Rates
-~..i:d Qtr. 2017
U-Nat U-Nat. 1 n-LLl:S 1 n-LL(S Th-2:'IU 1n-.ou I n-LlL I n-2:iL Pb-LIU 1-'b-LJU Ka-Uo Ka-2L() Ka-Ul:5 Ka-Ul:5
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 l.90E-09 l.60E-03 l.29E-14 J.09E-08 l.08E-13 9.lOE-08 O.OOE+OO O.OOE+OO 4.31E-12 3.64E-06 2.02E-14 1.71 E-08 l.35E-13 l.14E-07
SYC Dryer
Scrubber 2 l.28E-09 1.11 E-03 1.12E-14 9.70E-09 1.62E-13 l .40E-07 7.36E-15 6.36E-09 5.49E-l 2 4.74E-06 7.l lE-14 6.14£-08 l.25E-J 3 I .08E-07
YC Packaging
Baghouse 6.75E-l I l.28E-04 l.33E-l 3 2.53E-07 8.71E-l4 I .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
4.ffi Qt:t. 20l7
U-Nat U-Nat. 1 n-LL(S 1n-LL!S ·1 n-2:~U I h-2:iU I n-23L rh-LE t'D-L!U Pb-LIU Ka-LL() Ka-no Ka-2L1S 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 I 8.02E-I 0 l.80E-04 2.59E-15 5.8LE-JO 2.59E-15 5.81E-IO O.OOE+OO O.OOE+OO 4.ISE-12 9.30E-07 2.59E-15 5.81E-IO 2.59E-J 3 5.81E-08
SYC Dryer
Scrubber 2 1.01 E-09 2.67E-04 O.OOE+OO O.OOE+OO 2.56E-15 6.75E-LO l.60E-17 4.22E-12 4.64E-12 I .22E-06 2.88E-15 7.59£-10 l.60E-J 3 4.22E-08
YC Packaging
Baghou.se 7.41E-IO 7.87E-04 8.60£-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. I 3E-09 4.30E-13 4.57E-07
~t Qtr. J;UJ:3
No stack samolina was conducted as the drvers did not run. No packa!rinn was comoletcd durina the I st Quarter. -2na Qtr. 2018
u-Nat u-r~at. I n-LLl:5 1 n-221:5 l n-LjU 1 n-2:iU l n-LSL l n-2:iL t'D-21U 1-'b-ZIU Ka-no Ka-no Ka-LL1S I{a-Ul:5
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 1.72E-09 I .39E-03 4.82E-15 3.92E-09 2.53E-13 2.06E-07 4.82E-15 3.92E-09 3.22E-l2 2.6lE-06 6.03E-14 4.90E-08 1.21 E-I 3 9.79E-08
SYC Dryer
Scrubber 2 l.73E-09 l .46E-03 1.29E-14 l.09E-08 3.LOE-13 2.62E-07 O.OOE+OO O.OOE+OO 5.86E-12 4.95E-06 l.03E-13 8.72E-08 l.63E-12 l.37E-06
YC Packaging
Baghouse J.03E-ll l.62E-05 1.74E-14 2.72E-08 3.47E-13 5.44E-07 O.OOE+OO O.OOE+OO 6.90E-l2 I .OSE-05 6.95E-l 3 l.09E-06 4.34E-13 6.SOE-07
ATTACHMENT A
HIGH VOLUME AIR MONITORING STATIONS
\
\
)
---1,
l ,\,'1-J '
Legend
+ Air Monitoring Station [:J Township and Range
U U Property Boundary ~ Section
D Tailings Cell Pond
---Road
-----Canyon Rim
Drainage
Coordinate System: NAD
1983 StatePlane Utah
South FIPS 4303 Feet
REVISIONS Project: WHITE MESA MILL
Date: By: County: San Juan State: Utah
Location: -
ATTACHMENT A
PARTICULATE MONITORING STATIONS
Author: rellis Date: 2/20/2017 Drafted By: rellis
ATTACHMENT B
BHV AIR SAMPLING GRAPHS AND DATA TABLES
TAB 1
BHV-1 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 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 llHV-lPB Effluent 4e-15 uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration Concentration
Umit= 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 uCi/ml
Pre 1994 MPC ~E-12 uCi/ml Pre 1994 MPC 8E-14 uCi/ml pre 1994 MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Umlt= 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 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL =>
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA tone EFC EFCA
9/28/1981 2.3SE-15 _5.00E-12 1.25E-12 7.82E-16 8.00E-14 2.00E-14 1.06E-15 2 OOE-12 5.00E-13 2.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/14/1981 1.56E-15 5.00E-12 1.25E-12 1.49E-15 8.00E-14 2.00E-14 1.93E-15 2.00E-12 . S.OOE-13 2.64E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
3/29/1982 2.16E-15 5.00E-12 l.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 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
6/30/1982 4.69E-15 5.00E-12 1.25E-12 3.46E-15 8.00E-14 2.00E-14 2.38E-15 2.00E-12 S.OOE-13 2.14E-14 4.00E-12 1.00E-12 Not Analyzed Not A_11Plicable Not Applicable
9/27/1982 4.45E-15 5.00E-12 1.25E-12 3.29E-15 8.00E-14 2.00E-14 3.23E-15 2.00E-12 5.00E-13 1.99E-14 4.00E-12 1.00E-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 Applicable
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 Not 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 2.00E-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 1.25E-12 8.00E-14 2.00E-14 O.OOE+OO ;1.00E-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 1.79E-16 2.00E-12 5.00E-13 1.06E-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 l.OOE-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 1.00E-15 8,00E-14 2.00E-14 2.09E-15 2.00E-12 5.00E-13J 1.88E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable _Not Applicable
10/1/1984 6.42E-16 5.00E-12 1.25E-12 1.39E-16 8.00E-14 2.00E-14 1.94E-16 l.OOE-12 S.OOE-13 1.85E-14 4,00E-12 1.00E-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 S.OOE-13 3.03E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
4/1/1985 0.00E+OO 5.00E-12 l .25E-12 1.23E·15 8.00E-14 2.00E-14 4.88E-16 2.00E-12 ~ 5.00E-13 8.06E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A11plicable
7/1/1985 7.17E-16 5.00E-12 1.25E-12 8.00E-14 2.00E-14 1.05E-15 2.00E-12 5.00E-13 2.15E-14 4.00E-12 1.00E-12 Not Analyzed Not A(?plicable Not Applicable
9/30/1985 6.13E-16 , 5.00E-12 1.25E-12 1.18E-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 3.64E-15 4.00E-12 1.00E-12 Not Analyzed Not ApQlicable 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 A_pplicable Not Applicable
4/1/1986 3.98E-15 __ 5.00E-12 1.25E-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 l.OOE-12 Not Analyzed Not Applicable Not A_pplicable
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 l.23E-14 4.00E-12 l.OOE-12 Not Analyzed Not A_p_plicable }Jot Applicable
10/27/1986 1.99E-15 5.00E-12 l.25E-12 3.06E-16 8.00E-14 2.00E-14 l.25~-15 2.00E-12 5.00E-13 1.08E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
12/15/1986 1.67E-15 5.00E-12 1.25E-12 1.16E-16 8.00E-14 2.00E-14 S.98E-16 2.00E-12 5.00E-13 1.37E-l4 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
3/16/1987 2.33E-15 5.00E-12 1.25E-12 4.30E-16 8.00E-14 2.00E-14 l.92E-16 2.00E-12 5.00E-13 5,59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Agplicable
5/11/1987 2.36E-15 S.OOE-12 i.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 Ac.!!plicable 'Not Applicable
9/9/1987 l!.27E-15 '. 5,00E-12 1.25E-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 Al?l?licable Not Applicable
11/2/1987 2.75E-15 5.00E-12 i.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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 1.98E-15 5.00E-12 ,l.25E-12 l.25E-15 8.00E-14 2.00E-14 6.40E-16 2.00E-12 5.00E-13 1.0?E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 '2.06E-15 5.00E-12 l.25E-12 3.41E-15 8.00E-14 2.00E-14 5.08E-16 2.00E-12 5.00E-13 1.62E-14 4.00E-12 1.00E-12 Not Analyzed 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 1.0lE-15 2.00E-12 5.00E-13 2.47E-14 4.00E-12 1.00E-12 Not Analyzed _Not AJ2lilicable Not Applicable
2/13/1989 1.99E-l5 5.00E-12 l.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 Ap_plicable Not Applicable
5/15/1989 1.70E-15 5.00E-12 p5E-12 6.32E-16 8.00E-14 2.00E-14 5.86E-16 2.00E-12 S.OOE-13_ 6.16E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 2.31E-15 5.00E-12 1.25E-12 2.31E-16 8.00E-14 2.00E-14 1.77E-16 2.00E-12 5.00E-13, 7.65E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not fil!plicable
11/13/1989 4.72E-15 5.00E-12 1.25E-12 l.71E-15 8.00E-14 2.00E-14 1.52E-15 2.00E-12 5.00E-13 1.89E-14 4.00E-12 1.00E-12 Not Analyzed Not ~plicable 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 S.OOE-13 2.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 3.03E-15 5.00E-12 l.25E-12 1.47E-15 8,00E-14 2.00E-14 1.04E-15 2.00E-12 5.00E-13 1.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.64E-15 5.00E-12 l.25E-12 1.49E·15 8.00E-14 2.00E-14 3.34E-16 2.00E-12 S.OOE-13 8.27E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 1.48E-15 5.00E-12 1.25E-12 7,50E-16 8.00E-14 2.00E-14 5.80E-16 2.00E-12 5.00E-13 2.16E-14 4.00E-12 l.OOE-12 INot Analyzed Not Applicable Not Applicable
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 5.00E-13 3.79E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 3.42E-16 5.00E-12 1.25E-12 1.34E-15 8.00E-14 2.00E-14 7.39E-16 :i.OOE-12 5.00E-13 1.46E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 2.77E-16 5.00E-12 1.25E-12 4.l?E-17 8.00E-14 2.00E-14 1.45E-16 2.00E-12 5.00E-13 1.80E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 6.65E-17 5.00E-12 l.25E-12 9.13E-17 8.00E-14 2.00E-14 2.77E-17 2.00E-12 5.00E-13 1.06E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 1.94E-16 S.OOE-12 1.25E-12 4.28E-17 8.00E-14 2.00E-14 4.08E-17 2.00E-12 5.00E-13 3.SlE-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 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 1.73E-16 5.00E-12 1,25E-12 1.SSE-16 8.00E-14 2.00E-14 1.20E-16 2.00E-12 5.00E-13 1.53E-14 4.00E-12 l.OOE-12 Not Analyzed Not ~_plicable Not Applicable
11/9/1992 1.56E-16 ; 5.00E-12 ·1.2se-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.lOE-16 .5.00E-12 l.25E-12 8.00E-14 2.00E-14 3.89E-17 2.00E-12 5.00E-13 2.52E-14 4.00E-12 l,OOE-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 Applicable Not Applicable
Date Effluent 9E·14 uCi/ml BHV·lU Effluent 2E·l4 uCi/ml BHV·1T230 Effluent 9E·l3 uCi/ml BHV·lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-1S uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARA Goal= 5E·l5 uCi/ml ALARAGoal = 2.ZSE-13 uCi/ml ALARA Goal= l.SE·l3 uCi/ml AlARAGoal = lE-15 uCi/ml
Prel994MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994MPC 2E·12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= limit= limit=
pre 1994 1.ZSE-12 uCi/ml Pre 1994 5E·l3 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
Cone EFC J:FCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
8/10/1993 2.30E-16 5.00E-12 1.25E-12 6.00E-17 8.00E-14 2.00E-14 6.43E-17 2.00E-12 5.00E-13 1.60E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Amilicable
11/8/1993 5.00E-12 l.25E·l2 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 Applicable
2/7/1994 1.82E-16 5.00E-12 1.2SE-12 5.00E-18 8.00E-14 2.00E-14 4.30E-17 '.2.00E-12 5.00E-13 2.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/9/1994 3.60E-16 5.00E-12 l.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 ApRlicable Not Applicable
8/9/1994 4.04E-16 : S.OOE-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 l ,OOE-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 9.lBE-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.DOE-12 Not Analyzed Not Applicable Not Applicable -2/7/1995 1.77E-16 9.00E-14 2.25E-14 9.70E-17 2.00E-14 5.00E-15 jl.70E-17 9.00E-13 2.25E-13 8.GOE-15 6.00E-13 l,SOE-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.40E-17 9.00E-14 2.25E-14 S.36E-16 2.00E-14 5.00E-15 1.60E-15 9.00E-13 2.25E-13 3.84E-15 6.00E-13 LSOE-13 Not Analyzed Not~ltcable 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.SOE-13 Not Analyzed No:tApplic:ablil Not Applicable
11/11/1995 4.80E-15 9.00E-14 2.25E-14. 6.41E-16 2.00E-14 5.00E-15 8.93E-16 9.00E-13 2.25E-13 5.20E-15 6.00E-13 1.50E-13 Not Ana jyzed 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 5.llE-16 9.00E-14 2.25E-14' 3.06E-16 2.00E-14 5.DOE-15 1.40E-16 9.00E-13 2.25E-13 7.03E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not AQlllicable
8/5/1996 5.99E-16 9.00E-14 2.25E-14 l.SSE-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 Analy_zed 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.SOE-13 Not Analyzed Not Ap_plicable Not App,flcfj!~e
2/6/1997 1.00E-16 9.00E-14 2.25E-14 1.25E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 ;2.25E-13 5.68E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap_plicable 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.SOE-13 Not Analyzed Not Applicable Not Applicable
8/11/1997 2.88E-16 9.00E-14 2.2SE·14 3.83E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 S.29E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/5/1998 3.24E-16 9.00E-14 2.2SE·14 3.47E-16 2.00E-14 5.00E-15 1.19E-16 9.00E-13 2.25E·13 4.73E-15 6.00E-13 1.SOE-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,SOE-13 Not Analyzed Not Applicable Not Applicable -
7/31/1998 8.84E-16 9.00E-14 2.25E-14 1.93E-15 2.00E-14 5.00E-15 1.43E-15 9.00E-13 2.25E-13 5.22E-15 6.00E-13 l.SOE-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 l.80E-16 9.00E-13 2.25E-13 4.64E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not AJ111licable
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 1.SOE-13 Not Analyzed Not Applicable : Not APPiicabie
3/29/1999 2.06E-16 9.00E-14 2.2SE·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 l\lot Applicable Not Applicable
7/3/1999 ?.31E-16 9.00E-14 2.25E-14 2.47E-16 2.0DE-14 5.00E-15 '.2.23E-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 1.SOE-13 Not Analyzed Not Am>licable 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 2.25E-13 7.29E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable 'Not Applicable
12/28/1999 l.48E-15 9.00E-14 2.25E·l4 6.00E-16 2.00E-14 5.00E-15 S.57E-16 9.00E-13 2.25E-13 6.19E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 l.OOE-16 i..OOE-14 2.25E-14 1.0GE-16 2.00E·14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.23E-15 6.00E·l3 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/26/2000 3.47E-16 9.00E-14 2.2SE·14 3.46E-16 2.00E-14 5.00E-15 3.62E-16 9.00E-13 2.25E-13 4.SOE-15 6.00E-13 l.50E-13 lllotAnal\fZed Not Applicable Not Applicable
9/26/2000 2.51E-16 9.00E-14 2.2SE·14 1.78E-16 2.00E-14 5.00E-15 3.25E-16 9.00E-13 2.25E-13 8.55E-15 6.00E-13 1.SOE-13 Not Analyzed Not Am>licable 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 ~.25E-14 1.00E-15 2.00E-14 5.00E-15 1.00E-15 9.00E-13 2.25E-13 7.19E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/29/2001 l.52E-16 9.00E-14 2.25E-14 1.44E-16 2.00E-14 5.00E-15 1.77E-16 9.00E-13 2.25E-13 7.21E-15 6.00E-13 1.SOE-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 1,SOE-13 Not Analyzed Not Applicable -Not Ap.Jllicable
12/31/2001 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 1.39E-15 6.00E-13 l.SOE-13 Not Analy_zed Not Applicable Not 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·l3 8.15E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 ~.SSE-16 9.00E-14 2.25E-14 4.BSE-16 2.00E-14 S,OOE-15 1.06E-16 9.00E-13 2.25E-13 7.65E-15 6.00E-13 l,50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 l.17E-16 9.00E-14 2.25E-14 1.61E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.68E-15 6.00E-13 1.SOE-13 Not Analyzed Not AQplicable Not Applicable
12/30/2002 l.OOE-16 9.00E-14 2.25E-14 l.03E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E·l3 9.46E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 1.20E-16 9.00E-14 2.25E-14 1.12E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 4,68E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable f'(ot Applicable
6/30/2003 2.18E-16 ~.OOE-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.SOE-13 Not Analyzed Not Applicable Not Ap_plicable
9/29/2003 1.00E-16 9.00E-14 2,25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.28E-15 6.00E-13 1.SOE-13 Not Analyzed Not A1211.licable Not Applicable
12/29/2003 1.00E-16 9.00E-14 2.2SE-14 2.54E-16 2.00E-14 5.00E-15 3.35E-16 9.00E-13 2.25E-13 6.25E-15 6.00E-13 1.SOE-13 'Not Anal~d : N_ot A.llfill.cable Not Applicable
3/29/2004 1.00E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l .54E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3,04E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/27/2004 1.00E-16 ~.OOE-14 2.25E·14 1.00E-16 2.DOE-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.OSE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable fllot Applicable
12/27/2004 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.59E-14 6.00E-13 1.SOE-13 Not Anajyzed Not Ap111icable Not Applicable
3/28/2005 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5,00E-15 1.00E-16 9.00E-13 2.25E-13 7.42E-15 6.00E-13 1.SOE-13 Not Anajyzed . Not Applicable Not Applicable
6/29/2005 l.OOE-16 9.00E-14 2.25E·14 l.30E-16 2.00E-14 5.00E-15 l.20E-16 9.00E-13 2.25E-13 7.94E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not ly/plicable
Date Effluent 9E-14 uCi/ml IIHV-lU Effluent 2E-14 uCi/ml BHV-1T230 Effluent 9E-13 uCi/ml BHV-lR Effluent 6E-13 uCi/ml BHV-lPB Effluent 4e-15 uCi/ml BHV-1T232
Concentration Concentration Concentration Concentration Concentration
limit= limit= limit= limit= limit=
ALARAGoal= 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal = 2.2SE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= lE-15 uCi/ml
Pre1994MPC 5E-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=
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=i ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/26/2005 .l.OOE-16 9.00E-14 2.25E-14 2.56E-16 2.00E-14 5.00E-15 2.42E-16 9.00E-13 2.25E-13 1.22E-14 6.00E-13 l.SOE-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 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 3.HE-14 6.00E-13 1.SOE-13 Not Anal~zed Not Applicable _Not Ap_plicable
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 1.SOE-13 Not Analyzed Not ~_plicable Not Applicable
7/3/2006 1.86E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5,00E-15 1.00E-16 9.00E-13 i.25E-13 9.77E-15 6.00E-13 1.SOE-13 Not Anajyzed ·Not Applicable Not Applicable
10/2/2006 1.00E-16 9.00E-14 12.25E-14 1.00E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 l.30E-14 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 1.00E-16 9.00E-14 2.25E-14 1.47E-16 2.00E-14 5,00E-15 1.00E-16 9.00E-13 2.25E-13 l.17E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 2.23E-16 9.00E-14 ,2.25E-14 1.63E-16 2.00E-14 5 OOE-15 l.OOE-16 9.00E-13 .2.25E-13 l.6SE-14 6.00E-13 1.50E-13 Not Analyzed Not A_p_plicable Not Applicable
7/2/2007 3.35E-16 9.00E-14 2.25E-14 1.34E-16 2.00E-14 S.OOE-15 1.36E-16 9.00E-13 '2.2SE-13 1.78E-14 6.00E-13 1.SOE-13 Not Anal~zed Not A_p.11!)cable Not Applicable
9/30/2007 1.lSE-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 1.SOE-13 Not Ana!Yzed Not Applicable Not Applicable
12/31/2007 l.OOE-16 9.00E-14 2.25E-14 1.93E-16 2.00E-14 5.00E-15 LOOE-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 1.SOE-13 NotAna~ed Not Applicable Not Applicable -3/31/2008 1.14E-16 9.00E-14 2.25E-14 1.13E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.44E-15 6.00E-13 1.SOE-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.S2E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2008 7.69E-16 jl.OOE-14 2.25E-14 2.94E-16 2.00E-14 5.00E-15 l.90E-16 9.00E-13 2.2SE-13 7.64E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable -Not All))licable
12/31/2008 1.21E-15 9.00E-14 2.25E-14 4.76E-16 2.00E-14 5.00E-15 3.34E-16 9.00E-13 2.25E-13 1.16E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/15/2009 2.14E-15 jl.OOE-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.SOE-13 Not Analyzed Not A@licable ~ Not Applicable
6/15/2009 5.97E-17 9.00E-14 2.25E-14_ 2.35E-16 2.00E-14 5.00E-15 2.18E-16 9.00E-13 2.25E-13 5.13E-1S 6.00E-13 l.SOE-13 Not Analyzed Not Al!Plicable Not Applicable
9/15/2009 9.SSE-16 9.00E-14 2.25E-14 1.71E-16 2.00E-14 5.00E-15 .9.87E-17 9.00E-13 2.25E-13 9.47E-15 6.00E-13 1.SOE-13 Not Analyzed Not ~plicable Not Applicable
12/15/2009 1.24E-15 9.00E-14 2.25E-14, 9.2SE-17 2.00E-14 5.00E-15 5.60E-17 9.00E-13 2.25E-13 5.95E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2010 1.97E-15 9.00E-14 2.25E,14 2.lSE-16 2.00E-14 5.00E-15 3.27E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
6/30/2010 l.58E-15 9.00E-14 2.25E-14 4.71E-16 2.00E-14 5.00E-15 7.70E-16 9.00E-13 2.2SE-13 4.07E-15 6.00E-13 1.SOE-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.SOE-15 6.00E-13 1.50E-13 Not Anajyzed Not Applicable Not Applicable
12/31/2010 l.27E-15 9.00E-14 225E-14 2.32E-16 2.00E-14 5.00E-15 2.30E-16 9.00E-13 2.25E-13 l.27E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 9.0lE-16 9.00E-14 2.25E-14 1.90E-16 2.00E-14 S.OOE-15 3.64E-16 9.00E-13 2.25E-13 l.09E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not AQglicable
7/4/2011 ,l.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.SOE-13 Not Analyzed Not AJ>_plicable Not Applicable
10/3/2011 2.92E-16 9.00E-14 2.25E-14 l.17E-16 2.00E-14 S.OOE-15 6.76E-17 9.00E-13 2.25E-13 1.14E-14 6.00E-13 1.SOE-13 Not Anajyzed 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 7.2SE-13 1.73E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 7.87E-16 9.00E-14 2.25E-14 2.64E-16 2.00E-14 5.00E-15 3.95E-16 -9.00E-13 2.25E-13 1.25E-14 6.00E-13 l.SOE-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 2.2SE-13 9.55E-15 6.00E-13 l.SOE-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 l .13E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 6.86E-16 9.00E-14 2.25E-14 1.27E-16 2.00E-14 5.00E-15 1.38E-16 • 9.00E-13 2.25E-13 1.54E-14 6.00E-13 1.SOE-13 Not Analyzed Not A_p_plicable Not Applicable
3/25/2013 9.91E-16 9.00E-14 2.25E-14 1.86E-16 2.00E-14 5,00E-15 2.04E-16 9.00E-13 2.25E-13 1.82E-14 6.00E-13 1.50E-13 Not Ana!Yzed Not Applicable , Not Applicable
7/2/2013 1.46E-16 9.00E-14 2.25E-14 3.34E-16 2.00E-14 5.00E-15 3.91E-16 9.00E-13 ?,25E-13 S.78E-15 6.00E-13 l.50E-13 ['Jot Analyzed Not Applicable Not Applicable
9/30/2013 8.89E-16 9.00E-14 2.25E-14 9.13E-17 2.00E-14 5,00E-15 l.05E-16 9.00E-13 2.25E-13 8.00E-15 6.00E-13 1.50E-13 Not Analyzed ·Not Applicable ' Not AMlicable
12/30/2013 5.21E-16 9.00E-14 2.25E-14 4.34E-17 2.00E-14 S.OOE-15 3.70E-17 9.00E-13 2.25E-13 2.59E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not_!~~plkablJ?
3/31/2014 1.07E-15 9.00E-14 2.25E-14 2.07E-16 2.00E-14 5.00E-15 3.69E-16 9.00E-13 2.25E-13 1.24E-14 6.00E-13 l.50E-13 NotAn~ed Not Applicable Not Appiic.ible
6/30/2014 2.24E-15 9.00E-14 2.25E-14 5.14E-16 2.00E-14 5.00E-15 l.09E-15 9.00E-13 2.25E-13 l ,23E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 1.59E-15 9.00E-14 , 2.25E-14 2.00E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.39E-14 6.00E-13 l.50E-13 1.00E-16 4.00E-15 1.00E-15 -
12/29/2014 2.00E-16 9.00E-14 2.25E-14_ 5.00E-17 2.00E-14 5,00E-15 7.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 l.50E-13 7.00E-18 4.00E-15 1.00E-15
3/30/2015 1.90E-15 9.00E-1<1 2.25E-14 3.00E-17 2.00E-14 5.00E-15 6.00E-17 9c00E-13 2.25E-13 2.SOE-14 6.00E-13 1,50E-13 4.00E-18 4,00E-15 1.00E-15
6/29/2015 6.00E-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 7.00E-16 9.00E-13 2.25E-13 9.00E-15 6.00E-13 1.50E-13 1.00E-17 4.00E-15 l.OOE-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 1.50E-13 7.00E-18 4.00E-15 1.00E-15
12/28/2015 ~20E-16 9.00E-14 2.25E-14 5.00E-17 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.50E-13 1.00E-18 4.00E-15 l.OOE-15
3/28/2016 2.00E-16 9.00E-14 2.25E-!4 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.SOE-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 1.50E-13 3.00E-18 ,4.00E-15 1.00E-15
9/27/2016 1.lOE-15 9.00E-14 ;1.25E-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.SOE-13 !l.SOE-18 4.00E-15 1.00E-15
12/27/2016 jl.80E-16 9.00E-14 2.2SE-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 USE-13 1.SOE-14 6.00E-13 l.50E-13 2.00E-18 4.00E-15 1.00E-15
6/26/2017 1.lOE-15 9.00E-,l4 . 2.25E-14 9.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.2SE-13 1.lOE-14 6.00E-13 1.SOE-13 8.00E-18 4.00E-15 l.OOE-15
Date 'Effluent 9E-14uGl7ml BHV-lU Effluent 2E-14 uCi/ml BHV·lT230 Efflu.ent· 9£,.13 uCi/ml ~V-lR Effluent 6E-13 uCi/ml BHV-lPB Effl)l.e_f>(· '4i!"15 uCi/ml BHV·ll'.232
Eoncentration Concentration C!oncentralion Concentration i:~nttatjon
Umit:<; Limit= Uinlt= limit= limit:,
ALA'RA G!)al = USE-14 uC;l/1111 ALARAGoal= SE-15 uCi/ml AlARA' Goal = 2.25£-13 u(iJm1 ALARAGoal= l.SE-13 uCi/ml ~·G4lll= ic-15 ij<:iJml
p:n,_19MM~ SE-~ uO/"'I Pre 1994 MPC SE-14 uCi/ml Pi'e~MPG 2£,U uCl/ml Pre 1994 MPC 4E-UuCl/ml ,Pmi$.1Ml'C Not,Applf;;able
limit= limit= Umlteo Limit= ~iii\ib--
Prel.994 1.2.SE:U uei/ml Prj,1!1,9;1 ~~-13 uS/ml Pre 1994 1E-12 uCi/ml Pl'C 1!§1 ·~,jt i\'i;,1,111<),lble
~RA~: ALAR».GOAl: ALARAGOAL= A~RA§'QAL= -
~one 'EEC -~ECA Cone EFC EFCA ~nc EFG EFC'A Cone EFC EFCA Cone EFC EFCA
9/25/2017 6.JiQE,16 !l.OOE-f4 2.25M4· 6.00E-17 2.00E-14 5.00E-15 LOOE-16 9:00£-13. 2.2SE·l3 1.20E-14 6.00E-13 1.SOE-13 8.!)GE•l8 .4,QOf•LS l ,(~iEl']$
12/26/2017 2'40E-15 9':°00E-14 :Z:iSE-1!1 5.00E-17 2.00E-14 5.00E-15 7,l)OE-1:1 9.®E-13' 2:Z:SE,13 1.BOE-14 6.00E-13 1.SOE-13 1:ooe-11 ~:-WE--15 l.O!IE·15
3/26/2018 i.90E-16 !l.Q0Ed4 2.2?E-1.4 5.30E-17 2.00E-14 5.00E-15 9.lOE-17 ~.00£.-13 2:'25'E•l.3 1.SOE-14 6.00E-13 1.SOE-13 S.3J~.E-1.8 ~,OQE-15 1,b<JGi'S
6/25/2018 8:00E-16 !UlOF14 2,:25&14' 1.20E-16 2.00E-14 5.00E-15 i;sDE-16 9.®E-13 _2.25E-1:3 1.20E-14 6.00E-13 1.SOE-13 930E-18 4.00E-15 . LOOBS.
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TAB2
BHV-2 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-2U Effluent 2E-14 uCi/ml BHV-2T230 ~ffluent 9E-15 uCi/ml iiHV-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 ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-~uCl/1111
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC 8E-14 uCi/ml Pre 1994MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Nol !.'PP Ii cable
Limit= limit= .Limit= Limit= Limit=
Pre 1994 ALARA 1.25E-l2 uCi/ml Pre 1994 5E-l3 uCl/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 l.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 L67E-14 4.00E-12 1.00E-12 Not Analyzed NoLApplfcable Not Applicable
12/14/1981 4.62E-16 5.00E-12 1.~E-12 8.03E-16 8.00E-14 2.00E-14 3.62E-16 2.00E-12 S.OOE-13 1.33E-14 4.00E-12 l.OOE-12 Not Analyzed Not App)lcable, Not Applicable
3/29/1982 7_Q7E-16 5.00E-12 1.25E-12 l.lOE-15 8.00E-14 2.00E-14 7.27E-16 2_00E-12_ 5.00E-13 l.52E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 8.84E-16 5.00E-12 1.25E-12 7.73E-16 8.00E-14 2.00E-14 4.78E-16 2.00E-12 5.00E-13 1.98E-14 4.00E-12 1.00E-12 Not Analyzed Not Agplicable ' Not Applicable
9/27/1982 l.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 r,ot Applicable Not Applicable
1/3/1983 2,64E-15 5.00E-12 1.25E-12 2.55E-16 8.00E-14 2.00E-14 l.98E-16 2.00E-12 5.00E-13 2.85E-14 4.00E-12 l,OOE-12 Not Analyzed Not Applicable Not ApP.licable
4/4/1983 2.14E-16 5.00E-12 1.25E-12 1.02E-16 8.00E-14 2.00E-14 1.57E-16 2.00E-12 5.00E-13 2.48E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1983 2.85E-16 5.00E-12 1.25E-.12 2.06E-16 8.00E-14 2.00E-14 2.24E-16 l.OOE-12 5.00E-13 l.79E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A@licable
10/3/1983 2.70E-16 5.00E-12 1.25E-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 1.00E-12 Not Analyzed Not Applicable Not :Applicable
1/3/1984 2.78E-15 -5.00E-12 1.25E-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 Ap_glicable Not Applicable
4/2/1984 4.28E-16 5.00E-12 1.25E-12 1.75E-16 8.00E-14 2.00E-14 4.57E-17 2.00E-12 5.00E-13 3.55E-14 4.00E-12 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 l.98E-16 2.00E-12 5 OOE-13 l.68E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Aruilicable
10/1/1984 2.69E-16 5.00E-12 l.25E-12 2.66E-17 8.00E-14 2.00E-14 0.00E+OO 2.00E-12 5.00E-13 1.77E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not ~licable
1/2/1985 2.15E-16 5.00E-12 1.25E-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 1.00E-12 Not Analyzed Not Ap_Qlicable Not,Al'l)ll~b.l~
4/1/1985 1.00E-16 5.00E-12 1.25E-12 l.67E-16 8.00E-14 2.00E-14 6.75E-17 2.00E-12 5.00E-13 7.56E-15 4.00E-12 LOOE-12 Not Analyzed Not 1',pplicable Not Applicable
7/1/1985 3.70E-17 !i.OOE-12 1.25E-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 1.00E-12 Not Analy_zed Not Applicable Not Applicable
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 2.15E-l7 2.00E-12 5,00E-13 3.04E-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1986 1.31E-15 5.00E-12 1,25E-12 1.50E-16 8.00E-14 2.00E-14 3.71E-16 2.00E-12 5.00E-13 2.90E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 ?.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 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 6.41E-16 5.00E-12 1.25E-12 1.74E-16 8.00E-14 2.00E-14 3.67E-16 2.00E-12 5.00E-13 1.04E-14 4.00E-12 1.00E-12 'Not Analyzed Not Applicable Not Applicable
12/15/1986 3.56E-16 5.00E-12 1.25E-12-LOOE-16 8.00E-14 2.00E-14 l.OSE-16 2.00E-12 5.00E-13 7.81E-15 4_00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
3/16/1987 5.31E-16 5.00E-12 1.25E-12 1.30E-16 8.00E-14 2.00E-14 7.74E-17 2.00E-12 5.00E-13' 3.80E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable -5/11/1987 4.06E-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 1.00E-12 Not Analyzed Not Al).Plicable Not Applicable
11/2/1987 -3.73E-16 5.00E-12 ·1.25E-12 3.llE-16 8.00E-14 2.00E-14 1-83E-16 2.00E-12 5.00E-13' 1.17E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ApRlicable
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 3.55E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/18/1988 4.63E-16 5.00E-12 1.25E-12 1.49E-16 8.00E-14 2.00E-14 2.30E-16 2.00E-12 5.00E-13 1.18E-14 4.00E-12 l.OOE-12 Not Analyzed Not ApRlicable ['Jot ~plicable
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 l.42E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 4.34E-16 5.00E-12 1.25E-12 6-76E-16 8.00E-14 2.00E-14 1.57E-16 2.00E-12 5.00E-13 2.25E-14 4.00E-12 1.00E-12 Not Analyzed !llot Applicable Not Applicable
2/13/1989 5.80E-16 5.00E-12 1.25E-12 2.85E-16 8.00E-14 2.00E-14 1.SSE-16 2.00E-12 5.00E-13 2.BOE-14 4.00E-12 1.00E-12 r,ot Analyzed Not Applicable Not Applicable
5/15/1989 ,5.06E-16 5.00E-12 1.25E-12 2.28E-16 8.00E-14 2.00E-14 1.63E-16 2.00E-12 5.00E-13 6.05E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
8/14/1989 4.71E-16 5.00E-12 l.25E-12 9.60E-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 5.00E-13 6.65E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1.1/13/1989 1.14E-15 5.00E-12 1.25E-12 4.08E-16 8.00E-14 2.00E-14 4.18E-16 2.00E-12 5.00E-13 1.59E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/12/1990 1.09E-15 5.00E-12 1.25E-12 3.25E-16 8.00E-14 2.00E-14 3.74E-16 2.00E-12 5.00E-13 1.98E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/14/1990 9.32E-16 5.00E-12 : l.25E-12 5.27E-16 8.00E-14 2.00E-14 3.97E-16 2.00E-12 5.00E-13 l.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.66E-16 5.00E-12 1.25E-12 5.49E-16 8.00E-14 2.00E-14 4.75E-17 2.00E-12 S_OQE-13 1.27E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable . Not Applicable
11/12/1990 6.05E-16 5.00E-12 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 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/U/1991 8.72E-17 S.OOE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 1.1_6E-16 5_00E-12 1.25E-12 3.86E-16 8.00E-14 2.00E-14 2.80E-16 2.00E-12 5.00E-13 1.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 9.02E-17 5.00E-12 1.25E-12 8.82E-17 8.00E-14 2.00E-14 7.65E-17 2.00E-12 5.00E-13 1.58E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 4.81E-17 5.00E-12 1.25E-12 3.82E-17 8.00E-14 2.00E-14 2.54E-17 ;2.00E-12 5.00E-13 l.45E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable !llot 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 Anajyzed Not ARplicable Not Applicable
5/11/1992 2.38E-16 5.00E-12 1.25E-12 7.63E-17 8.00E-14 2.00E-14 3.07E-17 2.00E-12 5.00E-13 1.27E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 l.OlE-16 -5.00E-12 1.25E-12 -7.07E-17 8.00E-14 2.00E-14 2.80E-17 :2.00E-12 5.00E-13 1.41E-14 4.00E-12 l,OOE-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 /;.20E-17 5.00E-12 1.25E-12 3.65E-17 8.00E-14 2.00E-14 1.78E-17 ·2.00E-12 5.00E-13 l.71E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
i/9/1993 l.39E-16 S.OOE-12 1.25E-12 2.97E-17 8.00E-14 2,00E-14 6.31E-17 2,00E-12 5.00E-13 3.41E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
S/1.0/1993 1.90E-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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
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 LOOE-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 toncentration
Limit= Limit= limit= Limit= limit=
ALARAGoal= 2.ZSE-14 uCi/ml ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.2SE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ~LARA Goal= lE-15 uCi/ml
Pre 1994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC 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 ~.OOE-12 l.25E-12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 . 2.00E-12 5.00E-13 1.49E-14 4.00E-12 1,00E-12 Not Analyzed Not Applicable Not Applfc:;1,.ble
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 l.OOE-12 t,iot Anal'{zed Not Applicable Not Applicable
5/9/1994 2.16E-16 5.00E-12 l.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 1.00E-12 Not Analyzed Not Applicable Not Apglicable
8/9/1994 9.29E-17 5.00E-12 1.25E-12 2.96E-16 8.00E-14 2.00E-14 3.04E-16 2.00E-12 5.00E-13 l.OOE-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/7/1994 !J.21E-17 5.00E-12 l.25E-12 2.35E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 '.,.OOE-13 1.00E-16 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not ~pplicable
217/1995 1.lBE-16 9.00E-14 2.25E-14 9.70E-17 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.2SE-13 7.42E-15 6.00E-13 1.SOE-13 'Not Analyzed Not Applicable N'ot•Kppll~ble
5/9/1995 l).40E-17 9.00E-14 2.25E-14 l.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 Ap_p_licable
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 i.25E-13 2.38E-16 6.00E-13 l.50E-13 Not Analyzed Not Ap.Plicable 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.SOE-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.SOE-15 6.00E-13 1.50E-13 Not Analyzed ,111ot Jw.11licable Not Applicable
5/6/1996 1.40E-16 9.00E-14 2.25E-14 1.15E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.85E-15 6.00E-13 l.50E-13 Not Analyzed Not Ap_plicable Not Applicable
8/5/1996 143E-16 !').OOE-14 2.25E-14 2.78E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 5.83E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable ~ot ,'jpplrcabre
11/6/1996 1.45E-16 9.00E-14 2.25E-14 1.57E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.19E-14 6.00E-13 l.SOE-13 Not An;!]yzed Not Applicable Not Applicable
2/6/1997 J..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 5.84E-16 6.00E-13 1.SOE-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 l,OOE-16 9.00E-13 2.2SE-13 3.89E-15 6.00E-13 1.50E-13 ['Jot Analyzed Not Applicable Not Applicable
8/11/1997 1.00E-16 9.00E-14 2.25E-14 L09E-16 2.00E-14 5.00E-15 LOOE-16 9.00E-13 2.25E-13 5.69E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/5/1998 .i.SSE-16 _9_.00E-14 2.25E-14 1.07E-16 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 5.llE-15 6.00E-13 1.50E·l3 Not Analyzed Not Applicable Not Applicable
4/28/1998 1.20E-16 9.00E-14 2.25E-14 L71E-16 2.00E-14 5.00E-15 1.28E-16 9.00E-13 2.25E-13 6.40E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable !'.lot ~plicable
7/31/1998 1.47E-16 9.00E-14 2.25E·14 4.24E-16 2,00E-14 5.00E-15 3.39E-16 9.00E-13 2.25E-13 4.BOE-15 6.00E-13 1,SOE-13 Not Analyzed Nb}~pplJ{ii6Je Not Applicable
9/28/1998 l.OOE-16 9.00E-L4 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.SOE-13 Not Analyzed Not Ap_plicable (:Jot Applicable
12/28/1998 2.54E-16 9.00E-14 2.25E-14 2.lSE-16 2.00E-14 5.00E-15 1.38E-16 9.00E-13 2.25E-13 6.BBE-15 6,00E-13 1.SOE-13 Not Analyzed jlJot Applicable ijot Appl[ca.ble
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 1.SOE-13 Not Analyzed Not AQplicable _Not A11plicable
7/3/1999 2.46E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.2SE-13 6.95E-15 6.00E-13 1.50E-13 Not Analyzed 'Not Applicable Not Applicable
9/27/1999 2.BlE-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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/28/1999 S.20E-16 9.00E-14 2.25E-14 2.60E-16 2.00E-14 5.00E-15 l2.01E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/27/2000 1.00E-16 9.liiiW4· z.iSe.14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9,00E~-2.25E-13 7.12E-15 6.00E-13 1.SOE-13 Not Analyzed: NotAppl(c;,ble Not ~11pllcabJ~
6/26/2000 1.lOE-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.16E-16 9.00E-13 2.25E-13 5.07E-15 6.00E-13 1.SOE-13 Not AnaJyzed Not Applicable Not Applicable
9/26/2000 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 S.31E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/26/2000 1.26E-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 9.45E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable , Not A11plicable
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.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 LOOE-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 6.56E-15 6.00E-13 1.SOE-13 Not Analyzed Not Agplicable Not Applicable
9/24/2001 1.00E-16 9.00E-14 2.25E-14 LOOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 6.16E-15 6.00E-13 l,SOE-13 Not Anajyzed ~·oJ.fipp_llcable Not~p)l!'(ca,ble_
12/31/2001 l.OOE-16 /J.OOE-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 OOE-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 'l.OOE-16 9.00E-13 2.25E-13 9.95E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable '"
7/1/2002 1.25E-16 9.00E-14 2.25E-14 1.43E-16 2.00E-14 5.00E·IS 1.00E-16 9.00E-13 2.25E-13 8.25E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 3,69E-15 6.00E-13 1.50E-13 Not Analyzed Not Ap11licable Not·Ap111Jcable
12/30/2002 1.00E-16 /J.OOE-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.91E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 l .. OQE-l6• 9.00E-14 2.25E-14 1.00E-16 2,00E-14 S.OOE-15 1,00E-16 9.00E-13 2.25E-13 6.16E-15 6.00E-13 1.50E·l3 Not Analyzed Not Agplicable Not Applicable
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 S.27E-15 6.00E-13 1.SOE-13 Not Analyzed Not Ap_plicable 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 l.25E-13 7.23E-15 6.00E-13 L50E-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 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 7.80E-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 2.2SE-13 2.04E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 1.00E-16 9.00E-14 2.2SE-14 1.00E-16 .2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 3.09E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable -Not Applicable
9/27/2004 l.OOE-16 '9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 1.73E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Ap£1icable
12/27/2004 l.OOE-16 9.00E-14 2.2SE-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.SOE-13 Not Analyzed Not Ap11licable -Not Ap.11licable
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 8.88E-15 6.00E-13 1,SOE-13 Not Analyzed Not Ap11licable Not Applicable
6/29/2005 1.00E-16 9.00E-14 2.25E-14_ 1.00E-16 2,00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 8.BSE-15 6.00E-13 1.50E-13 Not Analyzed Not AP.l_,licable 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.SOE-13 Not Analyzed Not Applicable Not Agplicable
1/3/2006 1.29E-16 9,00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 4.0BE-16 9.00E-13 2.2SE-13 6.58E-14 6.00E-13 1.SOE-13 Not Analyzed , Not Applicable Not Ap_11licable
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 ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARA Goal= lE-15 uCi/ml
Pre 1994 MPC 5E·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=
Pre 1994 ALARA L25E-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 1E·1Z uCi/ml Pre 1994 Not Applicable
GOAL= ALARAGOAL= ALARAGOAL= ALARAGOAL=
tone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFC A Cone EFC EFCA
4/3/2006 1.02E·16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 1.08E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not '!l!J'llc,lble
7/3/2006 1.00E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not~li~bJe
10/2/2006 1.30E-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 1.68E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 J..24E·l6 9.00E-14 • ·2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 l.25E-13 1.38E-14 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 1.40E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.63E-14 6.00E-13 1.SOE-13 Not Analyzed Not Al1!llicable Not Applicable
7/2/2007 1.04E·l6 9 OOE-14 2.ZSE-14 1.00E-16 2.00E-14 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 1.36E-14 6.00E-13 1.SOE-13 Not Ana!yzed Not Applicable Not Applicable
9/30/2007 1.00E-16 9.00E-14 2.25E-14. 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.2SE-13 8.24E-15 6.00E-13 l .50E-13 Not Analyzed !'Jot Applicable Not Applicable
12/31/2007 1.91E·16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.ZSE-13 l.18E-14 6.00E-13 1.SOE-13 Not Analyz!'d tJot A1111licable Not Applicable
3/30/2008 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 LOOE-16 9.00E-13 2.25E-13 6.49E-15 6.00E-13 l.50E-13 Not Analyzed 'Not Applicable Not Applicable
6/30/2008 1.29E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.OOE-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 S.OOE-15 l.OOE-16 9.00E-13 2.25E-13 8.30E-15 6.00E-13 l .SOE-13 jliot Analyzed Not Applicable Not Applicable
12/31/2008 5.71E-16 9.00E-14 2.25E-14 l.61E-16 2.00E-14 S.OOE-15 1.25E-16 9.00E-13 2.2SE·l3· 2.04E-14 6.00E-13 1.SOE-13 Not Analyzed _Not AITT)licable Not Applicable
3/15/2009 3.96E-16 9.00E-14 2.25E-14 1.38E-16 2.00E-14 p.OOE-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 l.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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 2.43E-16 9.00E-14 2.25E-14 5.28E-17 2.00E-14 5.00E-15 4.84E-17 9.00E-13 2.25E-13 l.19E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 5.72E-16 9.00E-14 .2.25E-14 2.94E·l7 2.00E-14 5.00E-15 2.57E:17 9.00E-13 11.25E-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 l.42E-17 2.00E-14 5.00E-15 4.66E-17 9.00E-13 l.25E·l3· 8.24E-15 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not A@licable
6/30/2010 3.SSE-16 9.00E-14 .2.25E-14 6.64E-17 2.00E-14 S.OOE-15 9.90E-17 9.00E-13 2.25E-13 2.0lE-15 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2010 2.91E·16 9.00E-14 2.25E-14 4.48E-17 2.00E-14 5.00E-15 5.72E-17 9.00E-13 2.25E-13 1.08E-15 6.00E-13 l.50E-13 NotAna~d ' Not Applicable Not ~j!licable
12/31/2010 5.73E-16 9.00E-14 2.25E-14 7.24E-17 2.00E-14 5.00E-15 6.76E-17 9.00E-13 2.25E-13 1.35E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
4/4/2011 3.79E-16 9.00E-14 2.25E-14 4.0lE-17 2.00E-14 5.00E-15 ;).llE-17 9.00E-13 2.25E-13 1.06E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 3.07E-16 9.00E-14 2.25E-14 8.54E-17 2.00E-14 S.OOE-15 9.21E-17 9.00E-13 2.25E-13 7.21E-15 6,00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
10/3/2011 1.17E·l6 9.00E-14 2.25E-14 3.04E-17 2.00E-14 5.00E-15 2.81E-17 9.00E-13 2.25E-13 1.03E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not A11plicable
1/3/2012 3.65E-16 9.00E-14 2.25E-14 2.72E-17 2.00E-14 5.00E-15 4.54E-17 9.00E-13 2.25E-13 1.58E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Al1!llicable
4/3/2012 4.22E·16 9.00E-14 2.25E-14 1.lSE-16 2.00E-14 S.OOE-15 ·2.77E-16 9.00E-13 2.25E-13 1.58E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ApJJlicable
7/2/2012 3.39E·l6 9.00E-14 2.25E-14 l.56E-16 2.00E-14 5.00E-15 1.74E-16 9.00E-13 2.25E-13 8.60E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable . Not A@licable
10/1/2012 3.BE-16 9.00E-14 2.25E-14 4.BE-17 2.00E-14 S.OOE-15 3.04E-17 9.00E-13 2.25E-13 1.03E-14 6.00E-13 l.50E-13 Not Analyzed Not Al1!11icable Not Applicable
12/31/2012 2.76E-16 9.00E-14 2.25E-14 5.41E-17 2.00E-14 5.00E-15 7.0SE-17 9.00E-13 2.25E-13 l .48E-14 6.00E-13 1.SOE-13 Not Anajyzed Not Aj)~ficallle 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-17 9.00E-13 2.25E-13 1.42E-14 6.00E-13 l.50E-13 Not Analyzed Not .;p111icable 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 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 1.76E-16 9 OOE-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 1.SOE-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-17 9.00E-13 2.25E-13 2.50E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ~pllca.ble.
3/31/2014 >i.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 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not App_llcatile
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.SOE-13 Not Ana_lyzed 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 l.lOE-14 6.00E-13 1.SOE-13 9.35E-18 ~-OOE-15 .l.OOE-15
12/29/2014 1.00E-16 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 l.OOE-15
3/30/2015 5.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 5.00E-15 3.00E-17 9.00E-13 2.25E-13 2.30E-14 6.00E-13 l.SOE-13 4.00E-18 4.00E-15 l.O!)E-15
6/29/2015 1.00E-16 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 1.00E-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 l.OOE-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.SOE-13 6.00E-18 4.00E-15 l.OOE-15
12/28/2015 1.00E-16 9.00E-14 ,7.25E-14 5.00E-17 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 . 1.00E-15
3/28/2016 7.00E-16 9.00E-14 2.25E-14 6.00E-18 2.00E-14 5.00E-15 8.00E-17 9.00E-13 ·2.2sE-B 1.SOE-14 6.00E-13 1.SOE-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 1.30E-14 6.00E-13 l.50E-13 4.00E-18 4.00E-15 l.OOE-15
9/27/2016 4.20E-16 9.00E-14 2.25E-14' 6.90E-17 2.00E-14 5.00E-15 8.lOE-17 9.00E-13 2.25E-13 1.00E-14 6.00E-13 l,SOE-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 5.00E-17 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.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 l.50E-13 5.00E-18 4.00E-15 1,00Eal5
6/26/2017 2.00E-17 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.00E-14 6.00E-13 1.50E-13 9.00E-18 4.00E-15 J..OOE-15
9/25/2017 2.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 S.OOE-15 5.00E-17 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
12/26/2017 6.00E-16 9.00E-14 2.25E-14 3.00E-17 2.00E-14 5.00E-15 5.00E-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 9.00E-18 4.00E-15 1.00E-15
3/26/2018 6.70E·17 9.00E-14 2.ZSE-14 1.40E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.SOE-13 5.30E-18 4.00E-15 l.OOE-15
Date Effluefrtt 9f-,U:uCi/ml Bf1V-2U Effluent 2E-14 uCi/ml BHV·2T230 Effluent, 9e;:1s ut,1/n;\I BHVizR· Effluent 6E-13 uCi/ml BHV·2PB Effluent " 4e-JS uCi/ml 'e1:1y-~
Concentrati:on Concentration Cona!ntraticm Concentration (9~ntnli0i)
limit"' Limit= Um'lt ..-Limit= LiJn.lt =
J
~§qal,oa ~E-14uEl/ml AlARAGoal = SE-13 uCi/ml AlARAGpal"' ~~~uer/ml AlARAGoal= l.SE-13 uCi/ml ~~Goal= 1E-i5 uCf/ml
Prelm'MJ>C SE-12-ucil/inl Pre 1994 MPC BE-14 uCi/ml Pre-·MPC W12uCflm1 Pre 1994 MPC 4E-12 uCi/ml Prel994MPC Nof~pliqble
Limit= Limit= linilt,: Limit= Limit.="
Pre ~-AlAR'A ~~11110/ml Pr~~ SE,13\Jq]ml Pre 1994 lE-12 uCi/ml Pre1994 No.t P,,ppllcab\e
GOP,,l;, AlARA G0,1\1' " AlARAGOAL= ~lARAGOAL=
~ EFE_ EF¢A. Cone EFC EFCA Cone, , EEC" EF.CA Cone EFC EFCA Cone. EEC _EfCP,,
6/25/2018 ~'.8®:'l6 9'.00E•l>I 2d5£.14, 4.60E-17 2.00E-14 5.00E-15 J..20E-t:6 . ~.OOE-13 2.fil-13 1.30E-14 6.00E-13 1.SOE-13 1'.SOE-17, ~.ogf=.S . 1,JXIE~~-
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~9-das
Sep-14
Nov-14
Jan-15
Mar-15
May-15
Jul-15
Sep-15
Nov-15
Jan-16
Mar-16
May-16
Jul-16
Sep-16
Nov-16
Jan-17
Mar-17
May-17
Jul-17
Sep-17
Nov-17
Jan-18
Mar-18
May-18
0 0 m I ......
CX)
0 0 r:n ......
-...J
0 0 m I ......
CJ)
0 0 m I ......
01
0 0 r:n ......
.j::,.
0 0 r:n ...... w
0 0 r:n ......
I\)
0 0 m I ...... ......
.(Log .Scale}. o o o 0 0 0 m m m 0 I I
....1. 0 0
0 CO CXl
0 0 m 6 -...J
0 0 m I 0 CJ)
0 0 m I 0 01
0 0 m I 0 .j::,.
0 0 m 6 w
0 0 m 6 I\)
0 0 m 6 ......
......
0 0 m + 0 0
):lo m r-:I:
):lo i: ::JJ (I)
):lo 3.
Ci)(")
0 O QI :::, -0 II (I) .... :::, . -0 ., m 2l. I -• .... 0
(II :::,
C r-(") -• -·3 3 ;:;:
-11
.,::,. m I ....
(II
C (") ::::.: 3
OJ :::c
~ I\)
~ :::r 0
::::!.
C
3 I I\) w
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0 0
::::s (')
(I)
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::!':.
0
::::s en -C
0 =::.: 3 -
TAB3
BHV-3 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-3U Effluent 2E-14 uCi/ml BHV-3T230 ~ffluent 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 ALARA Goal= 1.SE-13 uCi/ml
Pre 1994 MPC SE-12uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC · ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
Limit= Limit= Limit = Limit=
Pre 1994 ALARA l.25E-U uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 1.74E-15 5.00E-12 1.2SE-12 9.02E-16 8.00E-14 2.00E-14 Z.87E-16 2.00E-12 5.00E-13 L54E-14 4.00E-12 1.00E-12
12/14/1981 1.59E-15 S.OOE-12 l 25E-12 S.03E-16 8.00E-14 2.00E-14 1.30E-16 2.00E-12 5.00E-13 2.lSE-14 4.00E-12 1.00E-12
3/29/1982 3.76E-16 5.00E-12 l.25E-12 5.25E-16 8.00E-14 2.00E-14 4.08E-16 '2.00E-12 5.00E-13 1.96E-14 4.00E-12 1.00E-12 -6/30/1982 3.83E-16 S.OOE-12 1.25E-12 2.16E-16 8.00E-14 2.00E-14 1.41E-15 2.00E-12 5.00E-13 2.40E-14 4.00E-12 l .OOE-12
9/27/1982 S.95E-16 5.00E-12 L25E-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 2.0SE-16 S.OOE-12 1.25E-12 1.23E-16 8.00E-14 2.00E-14 l.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 LOOE-12
6/30/1983 3.06E-16 -5.00E-12 1.2SE-12 9.59E-17 8.00E-14 2.00E-14 2.08E-16 2.00E-12 5.00E-13 L?OE-14 4.00E-12 l,OOE-12
10/3/1983 1.91E-16 5.00E-12 1.2SE-12 3.05E-16 8.00E-14 2.00E-14 2.79E-16 2.00E-12 5.00E-13 l.76E-14 4.00E-12 LOOE-12
1/3/1984 3.0lE-16 5.00E-12 l.2SE-1Z 9.51E-17 8.00E-14 2.00E-14 1.00E-16 2.00E-12 S.OOE-13 9.17E-15 4.00E-12 1.00E-12
4/2/1984 8.22E-16 S.OOE-12 l.25~l2 7.52E·16 8.00E-14 2.00E-14 5.20E-17 2.00E-12 5.00E-13 3.47E-14 4.00E-12 1,00E-12
7/2/1984 s:;zsE,-16 S,OOE-12 1'25.fell 6..18E-16 8.00E-14 2.00E-14 1!4,0E·.t:6 2.QQE-12 5.00E•13 l.32E·l4 4.00E-12 1.00E-12
10/1/1984 1.74E-16 S.OOE-12 1.25E-12 7.lOE-17 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.08E·14 4.00E-12 1.00E-12
1/2/1985 1.00E-17 S.OOE-12 L25E-1Z 7.lOE-17 8,00E-14 2.00E-14 7.80E-17 2.00E-12 5.00E-13 2.73E-14 4.00E-12 l.OOE-12
4/1/1985 1.00E-16 • S.OOE-12 01.25E-12 2.76E-16 8.00E-14 2.00E-14 4.lOE-17 2.00E-12 5.00E-13 1.12E-14 4.00E-12 1.00E-12
7/1/1985 l.04E-16 5.00E-12 1.25E-12 LOOE-16 8.00E-14 2.00E-14 1.00E-16 Z.OOE-12 5.00E-13 164E·14 4.00E-12 1.00E-12
9/30/1985 l.OOE-16 5.00E-12 1.25E-1ZJ 1.00E-15 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 L73E-14 4.00E-12 1.00E-12
1/2/1986 l.03E-15 5.00E-12 l.25E-12 3.17E-16 8.00E-14 2.00E-14 l.2SE·16 2.00E-12 5.00E-13 l.21E-17 4.00E-12 1.00E-12
4/1/1986 8.04E-16 S.OOE-12 l.25E-12 1.93E-17 8.00E-14 2.00E-14 l.54E-16 2.00E-12 5.00E-13 1.69E-14 4.00E-12 LOOE-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 ~.OOE-12 5.00E-13 1.97E-14 4.00E-12 1.00E-12
10/27/1986 6.45E-16 5.00E-12 1.25E-12 9.89E-17 8.00E-14 2.00E-14 4.16E-15 2.00E-12 5.00E-13 L64E-14 4.00E-12 1.00E-12
12/15/1986 l.31E-16 5.00E-12 l.25E-12 0.00E+OO 8 OOE-14 2.00E-14 4.16E-17 2.00E-12 S.OOE-13 4.60E-15 4.00E-12 l.OOE-12
3/16/1987 2.0lE-16 S.OOE-12 1.25E-12 L20E·16 8.00E-14 2.00E-14 5.73E-17 2.00E-12 5.00E-13 1.60E-14 4.00E-12 1.00E-12
5/11/1987 2.16E-16 5.00E-12 1.25E-12 1.96E-16 8.00E-14 2.00E-14 7.38E-17 2.00E-12 S.OOE-13 1.59E-14 4.00E-12 1.00E-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.ZSE-12 2.SSE-16 8.00E-14 2.00E-14 3.42E-16 2.00E-12 S.OOE-13 5.61E-14 4.00E-12 1.00E-12
S/18/1988 1.14E-16 5.00E-12 1.25E-12 4.14E-17 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13 1.20E-14 4.00E-12 1.00E-12
8/15/1988 2.0SE-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 1.36E-14 4.00E-12 l.OOE-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 S.OOE-12 1.25E-12 4.78E-17 8.00E-14 2.00E-14 2.47E-17 . 2.00E-12 5.00E-13 3.34E·14 4.00E-12 LOOE-12
5/15/1989 1.0SE-16 S.OOE-12 1.25E-12 1.00E-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 S.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 'l.67E-16 §.OOE-12 1.25E-12 3.87E-l7 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 5.00E-12 1.ZSE-12 LOOE-16 8.00E-14 2.00E-14 3.50E-17 2.00E-12 5.00E-13. 2.37E-14 4.00E-12 1.00E-12
5/14/1990 3.84E-16 5.00E-12 1.ZSE-12 2,54E-16 8.00E-14 2.00E-14 J.02E-16 2,00E-12 5.00E-13 L68E-14 4.00E-12 1.00E-12
8/13/1990 7.Z?E-17 5.00E-12 l.2SE-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 1.00E-12
11/12/1990 1.84E-16 5.00E-12 1.25E-12 L34E-16 8.00E-14 2.00E-14 8.53E-17 2.00E-12 5.00E-13 2.0lE-14 4.00E-12 1.00E-12
2/11/1991 4.66E-17 5.00E-12 L25E-12 8.48E-16 8.00E-14 2.00E-14 '1.94E·l7 ,2.00E-12 5.00E-13 3.69E-14 4.00E-12 1.00E-12
5/13/1991 5.0SE-17 !?.OOE-12 l.25E-12 7.40E-17 8.00E-14 2.00E-14 ·7.00E-18 l.OOE-12 S.OOE-13 l.SOE-14 4.00E-12 1.00E-12
8/12/1991 7.14E-17 5.00E-12 1.2SE-12 6,22E-17 8.00E-14 2.00E-14 7.95E-17 2.00E-12 '.5.00E-13 l.77E-14 4.00E-12 1.00E-12
11/11/1991 1.41E-17 S.OOE-12 l.25E-12 2.19E-18 8.00E-14 2.00E-14 2.75E-17 2.00E-12 5.00E-13 1.18E·l4 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 LOOE-12
5/11/1992 9.18E-17 5.00E-12 1.2SE-!2 S.80E-17 8.00E-14 2.00E-14 3.36E-17 2.00E-12 5.00E-13 1.28E-14 4.00E-12 1.00E-12
8/10/1992 2.00E-18 5.00E-12 1.25E-12 4.19E-17 8.00E-14 2.00E-14 2.00E-18 2.00E-12 5.00E-13 L59E-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 1.07E-17 2.00E-12 5.00E-13'. l.81E-14 4.00E-12 1.00E-12
2/9/1993 7.94E-17 5.00E-12 1.ZSE-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 t:GOE-17 5.00E-12 1.ZSE-12 5.07E·17 8.00E-14 2,00E-14 7.64E·17 2.00E-12 S.OOE-13 L26E-14 4,00E-12 1.00E-12
8/10/1993 6.00E-17 5,00E-12 .J..25E·12 6.00E-18 8.00E-14 2.00E-14 1.00E-16 ,2.00E-12 5.00E-13 1.SOE-14 4.00E-12 1.00E-12
Date Effluent 9E-14 uCi/ml BHV-3U Effluent ZE-14 uCi/ml BHV-3T230 Effluent 9E-13 uCi/ml BHV-3R Effluent 6E-13 uCi/ml BHV-3PB
Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit=
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal = 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml
Pre 1994MPC SE-UuCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC ZE-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml
µmit= Limit= Limit= Limit=
Pre 1994 ALARA 1.25E-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
Cone EFC EFCA Cone EFC EFC A Cone EFC EFCA Cone EFC EFCA
11/8/1993 1.00E-16 5.00E-12 l.25E-12 1.00E-16 8.00E-14 2.00E-14 1.00E-16 2.00E-12 5.00E-13-2.lOE-14 4.00E-12 l,OOE-12
2/7/1994 1.61E-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2.00E-14 2.22E-16 2.00E-12 5.00E-13 2.23E-14 4.00E-12 1.00E-12
5/9/1994 2.77E-16 5.00E-12 l.25E-12 2.80E-17 8.00E-14 2.00E-14 8.37E-18 2.00E-12 S.OOE-13 1,40E-14 4.00E-12 l.OOE-12
8/9/1994 7.39E-17 5.00E-12 'l.25E-12 1.00E-16 8.00E-14 2.00E-14 1.14E-16 l.OOE-12 S.OOE-13 1.00E-16 4.00E-12 1.00E-12
11/7/1994 9.05E-17 5.00E-12 i.ZSE-12 1.00E-16 8.00E-14 2.00E-14 1,00E-16 2.00E-12 5.00E-13 1.00E-16 4.00E-12 1.00E-12
2/7/1995 7.99E-17 9.00E-14 2.25E-14 9.60E-17 2.00E-14 S.OOE-15 9.60E-17 9.00E-13 2.25E-13 9.0SE-15 6.00E-13 l.50E-13
5/9/1995 9.40E-17 9.00E-14 2.25E-14 9,80E-17 2.00E-14 5,00E-15 8.60E-17 9.00E-13 2.25E-13 2.88E-15 6.00E-13 l.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 2.25E-13 1.96E-15 6.00E-13 1.5DE-13
11/11/1995 3.16E-16 9.00E-14 2.251:_-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 1.5DE-13
2/5/1996 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.DOE-14 5.DOE-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
5/6/1996 1.31E-16 9.00E-14 .2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
8/5/1996 3.00E-16 9.DOE-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.ZSE-13 1.31E-14 6.DOE-13 1.50E-13
11/6/1996 3.16E-16 9.00E-14 _2.ZSE-14 1.31E-16 2.DOE-14 5.00E-15 6.58E-17 9.00E-13 2,25E-13 1.91E-14 6.00E-13 1.5DE-13
2/6/1997 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.DOE-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
5/5/1997 l.31E-16 9.00E-14 2.25E-14 1.39E-16 2,00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 l.SOE-13
8/11/1997 3.00E-16 9.00E-14 2.25E-14 3,43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 1.SOE-13
1/5/1998 3.16E-16 9.00E-14 2.ZSE-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 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.ZSE-13 2.69E-14 6.00E-13 1.50E-13
7/31/1998 l.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/28/1998 3.00E-16 9.00E-14 2.ZSE-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
12/28/1998 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 l.91E-14 6.00E-13 l.50E-13
3/29/1999 3.41E-16 9.00E-14 2.25E-14 2,26E-16 2.00E-14 5.00E-15 l.18E-16 09.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
7/3/1999 1.31E-16 9.00E-14 2.ZSE-14 1.39E-16 2.00E-14 5.00E-15 l.82E-16 Jl.OOE-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/27/1999 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 1.SOE-13
12/28/1999 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
3/28/2000 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1,18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.50E-13
6/26/2000 l.31E-16 9.00E-14 2.25E-14' l.39E-16 2.00E-14 5.00E-15 1.82E-16 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 l.31E-14 6.00E-13 l.50E-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 l.50E-13
3/26/2001 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2 .. 00E-14 5.00E-15 l.18E-16 9.00E-13 2.2SE-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 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/24/2001 3.00E-16 9.00E-14 2.ZSE-14 3.43E-16 2.00E-14 .6.00E-15 3.99E-16 .9.00E-13 2.25E-13 1.31E-14 6.00E-13 l.50E-13
12/31/2001 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.SOE-13
4/1/2002 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
7/1/2002 1.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 S.OOE-15 l.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-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 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-.13 . 2.ZSE-13 1.91E-14 6.00E-13 1.SOE-13
3/31/2003 3.41E-16 S.OOE-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
6/30/2003 l.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.ZSE-13 1.53E-14 6.00E-13 l.SOE-13
8/29/2003 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 ;2.25E-13 1.31E-14 6.00E-13 1.SOE-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 S.OOE-15 1.18E-16 9.00E-13 l.25E-13 2.69E-14 6.00E-13 1.SOE-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 1.50E-13
9/27/2004 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
12/27/2004 3.16E-16 9.00E-14 , 2.25E-14 1.31E-16 2.00E-14 5.00E-15 p.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 l.50E-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 l.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.50E-13
9/26/2005 3.00E-16 9.00E-14 225E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 l.50E-13
1/3/2006 3.16E-16 9.00E-14 2.ZSE-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.ZSE-13 1.91E-14 6.00E-13 l.50E-13
Date Effluent 9E-14 uCifml J!HV-3U Effluent ZE-14 uCi/ml BHV-3T230 Effluent 9E-13 uCi/ml BHV-3R Effluent 6E-13 uCi/ml BHV-3PB
Concentration Concentration Concentration Concentration
Limit= Limit= Limit= limit=
ALARAGoal= 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 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
Limit= Limit= Limit= limit=
Pre 1994 ALARA 1.25E-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml
GOAL= GOAL= GOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC 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.lSE-16 9.00E-13 '2.2SE·13 2.69E-14 6.00E-13 l.SOE-13
7/3/2006 L}lE-16 9.00E-14 2.25E-14 L39E-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
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.SOE-13
1/1/2006 3.16E-16 9.00E-14 2.2SE-14 UlE-16 2.00E-14 S.OOE-15 6.58E-17 9.00E-13 2.2SE-13 1.91E-14 6.00E-13 l.SOE-13
4/2/2007 3.41E-16 9.00E-14 2.25E-14. 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.2SE-13 2,69E-14 6.00E-13 1.SOE-13
7/2/2007 1.31E-16 9.00E-14 2.25E-14 l.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
9/30/2007 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5,00E-15 3.99E-16 9.00E·13 2.25E-13 l.31E-14 6.00E-13 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 2.2SE·l3 1.91E-14 6.00E-13 1.SOE-13
3/31/2008 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2,00E-14 5.00E-15 1.18E-16 9.00E-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
6/30/2008 l.31E-16 9.00E-14 2.ZSE-14 1.39E-16 2.00E-14 5.00E-15 1.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 1.SOE-13
9/30/2008 3.00E-16 9.00E-14 2.25E-14 3,43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 l.31E-14 6.00E-13 1.SOE-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.SOE-13
3/15/2009 B.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.2SE-13 2.69E-14 6.00E-13 1.SOE-13
6/15/2009 1.31E-16 9.00E-14 2.2SE-14 1.39E-16 2.00E-14 5.00E·lS 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
9/15/2009 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 ·~.25E-13 1.31E-14 6.00E-13 1.SOE-13
12/15/2009 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.SOE-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.SOE-13
6/30/2010 l.31E-16 9.00E-14 2.25E-14. 1.39E-16 2.00E-14 S.OOE-15 1.82E-16 9.00E-13 2.25E-13 1.53E-14 6.00E-13 l.SOE-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.SOE-13
12/31/2010 3.16E-16 9.00E-14 2.25E-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6,00E-13 1.50E-13
4/4/2011 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 ~.OOE-13 2.25E-13 2.69E-14 6.00E-13 1.SOE-13
7/4/2011 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 1.SOE-13
10/3/2011 3.00E-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 6.00E-15 3.99E-16 9.00E-13 2.ZSE-13 l.31E-14 6.00E-13 1.SOE-13
1/3/2012 3.16E-16 !?.OOE-14 2.ZSE-14 1.31E-16 2,00E-14 S.OOE-15 6.58E-17 9.00E-13 2.ZSE-13 1.91E-14 6.00E-13 1.SOE-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 1.SOE-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 l.SOE-13
10/1/2012 3.00E-16 9.00E-14 -2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.25E-13 1.31E-14 6.00E-13 1.SOE-13
12/31/2012 3.16E-16 _ _9.00E-14 2.25E-14 l.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 1.91E-14 6.00E-13 1.SOE-13
3/25/2013 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.ZSE-13 2.69E·l4 6.00E-13 1.SOE-13
7/2/2013 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
9/30/2013 -3.00E-16 9.00E-14 2.2SE-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2.ZSE-13 1.31E-14 6.00E-13 l.SOE-13
12/30/2013 3_16E-16 9.00E-14 , 2.25E-14 1.31E-16 2.00E-14 S.OOE-15 6_58E-17 9.00E-13 2.ZSE-13 1.91E-14 6.00E-13 1.SOE-13
3/31/2014 3.41E-16 9.00E-14 "2.25E-14 2.26E-16 2.00E-14 5.00E-15 1.18E-16 9.00E-13 2.ZSE-13 2.69E-14 6.00E-13 1.SOE-13
6/30/2014 l.31E-16 9.00E-14 . 2.25E-14 l.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.25E-13 l,53E-14 6,00E-13 1.SOE-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 1.31E-14 6.00E-13 1.SOE-13
12/29/2014 3.16E-16 9.00E-14 2.2SE-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.SOE-13
3/30/2015 3.41E-16 ll.OOE-14 2.2SE-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
6/29/2015 il.31E-16 9.00E-14 2.25E-14 1.39E-16 2.00E-14 5.00E-15 l.82E-16 9.00E-13 2.2SE-13 1.53E-14 6,00E-13 1.SOE-13
9/28/2015 3.00E-16 9.00E-14 2.2SE-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.ZSE-13 1.91E-14 6.00E-13 l.SOE-13
8/28/2016 3.41E-16 9.00E-14 2.25E-14 2.26E-16 2.00E-14 5.00E-15 l.18E-16 9.00E-13 2.2SE·l3 2.69E-14 6.00E-13 1.SOE-13
6/27/2016 i..31E-16 9.00E-14 2.2SE-14 l.39E-16 2.00E-14 5,00E-15 1.82E-16 9.00E-13 2.25E-13 l.53E-14 6.00E-13 1.SOE-13
9/27/2016 3.00E-16 9.00E-14 2.ZSE-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 . 9.00E-13 2-25E-13 1.31E-14 6.00E-13 1.SOE-13
12/27/2016 3.16E-16 9.00E-14 2.2SE-14 1.31E-16 2.00E-14 5.00E-15 6.58E-17 9.00E-13 2.25E-13 l.91E-14 6.00E-13 1.SOE-13
3/27/2017 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
6/26/2017 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.ZSE-13 1.53E-14 6.00E-13 l.SOE-13
9/25/2017 3 OOE-16 9.00E-14 2.25E-14 3.43E-16 2.00E-14 5.00E-15 3.99E-16 9.00E-13 2,25E-13 l ,31E-14 6.00E-13 l.SOE-13 .
12/26/2017 3.16E-16 9.00E-14 2.25E-14 l.31E-16 2,00E-14 5.00E-15 6,SSE-17 9.00E-13 2.2SE-13 1.91E-14 6.00E-13 1.SOE-13
Date tffluent' 9E·14u<ri/ml BHV·)U Effluent 2E-14 uCi/ml BHV·3T230 Efflil1;hf 9E-13 uCi/ml B!1V·3R Effluent 6E-13 uCi/ml BHV-3PB
Concentration Concentration Ge>f)C,:ntf<1tic:,11 Concentration
llr:ni~= Limit= Llmit= limit=
' A~RAGoal= 2.25E-14cuc:i/ml ALARAGoal= SE-15 uCi/ml ~Goal·= z.;me• 13 Wi/ml ALARAGoal = 1.SE-13 uCi/ml
Pre 1994 MPC. SE•UuCl/inl Pre 1994 MPC SE-14 UCl/ml Pre i99il, MPC ' ~e.,ffua/ml Pre 1994 MPC 4E-12 uCi/ml
Umif= Limit= Umit= Limit=
Pre~At.ARA 1.2.SE,ll uClfml Prj!.~AIJ(RA SE-1$!1,q/m1 Pre 1994 ALARA lE-12 uCi/ml
liO~ -Gl,;ftl: GOAL=
--
Collf Ef.C El't"A Cone EFC EFCA C9ij5 t'f"C Em'I\. Cone EFC EFCA
3/26/2018 ~:i11E-16 ~JJ(J1,,14 '.i!..2!lE'·1U 2.26E-16 2.00E-14 5.00E-15 l.18E·16. !l.01'.IE-l'J 2.25&"13 2.69E-14 6.00E-13 1.SOE-13
6/25/2018 1.31.f.ll! 9,00E-14 il.2!,1'011f 1.39E-16 2.00E-14 5.00E-15 l.82.F 16 ·~.aes.13 2.25E-13 1.53E-14 6.00E-13 1.SOE-13
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Sep-07
Sep-OB
Sep-09
Sep-10
Sep-11
Sep-12
Sep-13
Sep-14
Sep-15
Sep-16
Sep-17
0 0 rri ......
--.J
~ -.
...... ......
0 0 0 0 m m I I ...... ......
0) (J1
""""-
(Log Scale)
0 0 m I ......
.j:.
' ~ ~ ~
~
~ t::,,,,•
~ boll
~ -~· -:r --,_ r+ -.... i.. ....... ~ .. --~ _.
-, -,... .,. ---=• ~ ~ ~ ~
~ pie
::a. ~ ~ .t; ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ I::.. ~ ~ ~ ~
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
...... ...... ......
0 0 0 0 0 0 m m m I I I ...... ...... ...... w I\) ......
~
"C "'tl )>m -,-,,::::t <D <D )>-... _.::C C
c.o c.o )>~ c.o c.o -
"'" "'"C) 0 l>S:o o r-"ti ~:::,
~O u !;!
)>C:;-"3,
"' 3 UI -, Ml -· m QI Q ..+ I ~.
DI II ~ 0 -"'" .... :::, II m C , _.I o -• m ... ,3
.!.~3 ;:;: N c,-11
C 0:::: a, 0 3 m :::.:-.!a. 3 c.>
-C 0 ~
a, :::c -;::
c,.)
r-(1)
D)
C. I I\) .....
0
0 0
:::::s C,
C1)
:::::s -..,
D)
::::!'.
0
:::::s C/1 -C:
0 :::::.: 3 ..:;
TAB4
BHV-4 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E-14 uCi/ml BHV-4U Effluent 2E-14 uCi/ml BHV-4T230 Effluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
ALARAGoal = 2.ZSE-14 uCi/ml ALARAGoal = SE-15 uCi/ml AlARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= 1E·15 uCi/ml
Pre1994MPC SE·12 uCi/ml Pre 1994 MP( BE-14 uCi/ml Pre 1994MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= limit= Limit=
Pre 1994 --1.25E-12 uCi/ml Pre 1994 ALARA. SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 !'lot Applicable
ALARAGOAL= GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
9/28/1981 5.20E-15 S.OOE-12 1.25E-12 2.93E-15 8.00E-14 2.00E-14 2.74E-15 2.00E-12 5.00E-13 1.84E-14 4.00E-12 1.00E-12 Not Analyzed ~ot Applicable Not Applicable
12/14/1981 4.53E-15 5.00E-12 ·1.25E-12' 1.78E-15 8.00E-14 2.00E-14 2.29E-15 2.00E-12 5.00E-13 2.54E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
3/29/1982 1.06E-15 5.00E-12 l.25E·12 1.42E-14 8.00E-14 2.00E-14 1.07E-15 2.00E-12 5.00E-13 2.31E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A11plicable
6/30/1982 6.03E-15 5.00E-12 1.25E-12 1.57E-14 8.00E-14 2.00E-14 2.62E-15 2.00E-12 5.00E-13 2.25E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
9/27/1982 l.26E-14 5.00E-12 ;1.25E·12 7.58E-16 8.00E-14 2.00E-14 5.35E-15 2.00E-12 5.00E-13 2.68E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 4.33E-15 5.00E-12 1.25E·12 6,52E-16 8.00E-14 2.00E-14 p.04E-16 2.00E-12 5.00E·l3 2.57E-14 4.00E-12 1.00E-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 1.00E-12 Not Analyzed Not Applicable Not ~plicable
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 OOE-13 1.20E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/3/1983 2.54E-16 S.OOE-12 1.ZSE-12 l.SlE-16 8.00E-14 2.00E-14 2.GSE-16 2.00E-12 5.00E-13 2.50E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
1/3/1984 2.76E-15 5.00E-12 1.25E-12 l.60E-16 8.00E-14 2.00E-14 1.0SE-16 2.00E-12 5.00E-13 l .59E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not ~plicable
4/2/1984 4.27E-16 5 OOE-12 1.2SE-12 2.33E-16 8.00E-14 2.00E-14 6.28E-16 2.00E-12 S.OOE-13 3.67E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
7/2/1984 2.57E-15 5.00E-12 1.25E·12 1.36E-16 8.00E-14 2,00E-14 UlE-16 2.00E-12 5.00E-13 l.58E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap(!licable
10/1/1984 4.18E-16 S.OOE-12 1.25E-12 3.54E-16 8.00E-14 2.00E-14 1.lOE-17 2.00E-12 ~.OOE-13 9.83E-15 4.00E-12 1.00E-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-14 4.00E-12 l,OOE-12 Not Analyzed 'Not Applicable Not Applicable
4/1/1985 1.00E-16 5.00E-12 ·1.2se-12 6.00E-16 8.00E-14 2.00E-14 4.35E-17 2.00E-12 5.00E-13 5.02E-15 4.00E-12 1.00E-12 Not AnaJyzed !'lot Applicable Not Applicable
7/1/1985 9.36E-16 5.00E-12 1.25E-12 2.33E-16 8.00E-14 2.00E-14 2.36E-16 2.00E-12 5.00E-13 7.48E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable t,lot 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 S.OOE-13 7,86E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/2/1986 8.40E-15 5.00E-12 1.25E-12 7.GOE-16 8.00E-14 2.00E-14 2.99E-16 2.00E-12 p.OOE-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not Ap_plicable Not Applicable
4/1/1986 5.79E-15 S.OOE-12 1.25E-12 5.80E-16 8.00E-14 2.00E-14 1.34E-15 2.00E-12 5.00E-13 1.33E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 5.19E-15 5.00E-12 1.25E-12 7.83E-16 8.00E-14 2.00E-14 2.20E-15 '2.00E-12 5.00E-13 7.14E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 4.GOE-15 _5.00E-12 1.25E·12 4,67E-16 8.00E-14 2.00E-14 2.37E-15 2.00E-12 5.00E-13 1.13E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable _Not A11plicable
12/15/1986 2.75E-15 S.OOE-12 .1.25E-12 5.90E-16 8.00E-14 2.00E-14 9.39E-16 2.00E-12 s.ooe-13 1.20E-14 4.00E-12 1.00E-12 Not Analyzed Not A11f11icable Not Applicable
3/16/1987 4.64E-15 5.00E-12 1.25E-12 l.18E-15 8.00E-14 2.00E-14 4.97E-16 2.00E-12 5.00E-13 5.89E-14 4.00E-12 1.00E-12 Not Analyzed Not App_licable Not Applicable
5/11/1987 4.35E-15 5.00E-12 l.25E·12 1.23E-14 8.00E-14 2.00E-14 l 13E-15 2,00E-12 5.00E-13 2.21E-14 4.00E-12 1.00E-12 Not AnaJyzed Not~ppJ~f~ Not Applicable
9/9/1987 6.39E-15 5.00E-12 l.25E-12 1.SOE-14 8.00E-14 2.00E-14 2.26E-15 2.00E-12 5.00E-13 1.57E-14 4.00E-12 l.OOE-12 Not AnaJyzed Not Applicalile Not Applicable
11/2/1987 6.72E-15 S.OOE-12 1.25E-12 4.53E-16 8.00E-14 2.00E-14 2.20E-15 2.00E-12 5.00E-13 2.55E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/16/1988 l.91E-15 5.00E-12 l.25E-12 l.35E-14 8.00E-14 2.00E-14 4.42E-16 2.00E-12 5.00E-13_ 4.44E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap(!licable _
5/18/1988 1.78E-14 S.OOE-12 l.25E·12 4.39E-14 8.00E-14 2.00E-14 4.92E-16 2.00E-12 5.00E-13 1.38E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 7.56E-15 5.00E-12 1.25E·l2 3.31E-14 8.00E-14 2.00E-14 l.51E-15 2.00E-12 5.00E-13 l.97E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/14/1988 _1.47E-14 5.00E-12 1.25E-12 1.56E-15 8.00E-14 2.00E-14 2.57E-15 2.00E-12 5.00E-13 2.12E-14 4.00E-12 l.OOE-12 Not Analyzed Not Ap_plicable Not Applicable
2/13/1989 2.47E-15 5.00E-12 1.25E·l2 3.14E-15 8.00E-14 2.00E-14 6.94E-16 2.,00E-12 5.00E-13' 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not A.l!P.licable Not Ap__p_licable
5/15/1989 2.50E-16 ,5.00E-12 l.25E-12 7.68E-15 8.00E-14 2.00E-14 9.03E-16 2.00E-12 5.00E-13 8.05E-15 4.00E-12 l.OOE-12 Not Analyzed · NotA~ble Not Applicable
8/14/1989 6.SOE-15 6.00E-12 1.25E-12 4.72E-15 8.00E-14 2.00E-14 2.35E-15 2.00E-12 5.00E-13 9.95E-15 4.00E-12 1.00E-12 Not Analyzed Not Applicable f'lot Applicable
11/13/1989 9.63E-15 5.00E-12 1.25E-12 4.05E-15 8.00E-14 2.00E-14 4.03E-15 2.00E-12 S.OOE-13 l.99E-14 4.00E-12 1.00E-12 Not Analyzed Not Applica51e Not Af!~licable
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 1.25E-12 3.58E-15 8.00E-14 2.00E-14 2.33E-15 2.00E-12 5.00E-13' 2.09E-14 4.00E-12 LOOE-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 1.92E-15 '5.00E-12 -1.25E-12 1.87E-15 8.00E-14 2.00E-14 5.06E-16 ';1.00E-12 S.OOE-13 8.86E-15 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 2.91E-15 5.00E-12 1.25E-12 2.25E-17 8.00E-14 2.00E-14 1.08E-15 2.00E-12 5.00E-13 2.19E-14 4.00E-12 l.OOE-12 f'lot 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 -Not Applicable Not Applicable
5/13/1991 1.87E-16 5.00E-12 1.25E-12 2.61E-15 8.00E-14 2.00E-14 3.54E-16 2.00E-12 S.OOE-13 1.40E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable -8/12/1991 4.85E-16 5.00E-12 l.25E-12 4.38E-16 8.00E-14 2.00E-14 1.27E-16 2_.QOE-12 5.00E-13 2.20E-14 4.00E-12 l.OOE-12 Not Analyzed Not I\P.Qlicable Not Applicable
11/11/1991 1.77E-16 5.00E-12 1.25E·12 1.46E-16 8.00E-14 2.00E-14 3.76E-17 2.00E-12 5.00E-13 1.lSE-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
2/10/1992 l.83E-16 5.00E-12 l.25E-12 1.95E-15 8.00E-14 2.00E-14 1.33E-16 --2.00E-12 5.00E-13_ 3.35E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_i!lkaiile
S/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 l.41E-14 4.00E-12 l.OOE-12 Not Analyzed Not A_p__p_licable Not I\PP.IJcabl_e
8/10/1992 /l.09E-17 5.00E-12 1.25E·12 1.15E-16 8,00E-14 2.00E-14 4.50E-17 2.00E-12 5.00E-13 1.57E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 2.07E-16 5.00E-12 1.25E-12 1.00E-16 8.00E-14 2,00E-14 3.62E-17 2.00E-12 5,00E-13 2.24E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not A_1111.licable
2/9/1993 l.73E-16 5.00E-12 1.25E-12 2.76E-17 8.00E-14 2.00E-14 2.89E-17 2.00E-12 5.00E-13 3.08E-14 4.00E-12 l.OOE-12 Not Analy_zed Not A_pplicable Not Applicable
5/10/1993 2.70E-17 5.00E-12 l.25E·12 2.50E-17 8.00E-14 2.00E-14 8.74E-17 2.00E-12 5.00E-13 1.25E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 9.00E-17 S.OOE-12 1.25E·12 1.76E-16 8,00E-14 2.00E-14 O,OOE+OO 2.00E-12 5.00E-13 l.50E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable -Not Applicable
11/8/1993 1.00E-16 5.CJOE-12 1.25E·12 1.00E-16 8.00E-14 2.00E-14 6.00E-17 2.00E-12 5.00E-13 1.75E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Jllot 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 ~ffluent 4e-15 uCi/ml BHV-4T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= limit= limit= limit=
ALARAGoal= 2.25E-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= ' 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml AlARAGoal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC BE-14 uCi/ml Pre 1994 MP( 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= Limit= Limit= pmlt=
Pre 1994 1.25E-12 uCi,ml Pre 1994 ALARA
I
SE-13 uCi/ml Pre 1994 lE-12 uCi/ml />re 1994 Not Applicable
ALARAGOAL= GOAL= , ALARA GOAL = 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 , 1.25E-12 3.38E-16 8.00E-14 2.00E-14 2.21E-16 2.00E-12 5.00E-13 3.0SE-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/9/1994 3.80E-16 §.OOE-12 1.25E-12 2.82E-16 8.00E-14 2.00E-14 3.46E-16 ;1.0oe-12 5.00E-13 1.73E-14 4.00E-12 1.00E-12 Not Anajyzed 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 1.00E-16 2.00E-12 5,00E-13 l.OOE-16 4,00E-12 1.00E-12 Not Analyzed Not Ap.Qlicable Not Ap_QJicable
11/7/1994 6.21E-17 S.OOE-12 1.25E-12 9.70E-17 8.00E-14 2.00E-14 1.96E-16 2.00E-12 S.OOE-13 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1995 3.70E-16 9 OOE-14 2.25E-14 9.SOE-17 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 8.84E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
5/9/1995 9.40E-17 9.00E-14 2.25E-14 2.86E-16 2.00E-14 5.00E-15 l.90E-16 9.00E-13 2.25E-13 2.90E-15 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 1.45E-16 9.00E-14 2.25E-14 2.31E-15 2.00E-14 5.00E-15 7.lOE-17 9.00E-13 2.25E-13 2.70E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable · Not Applicable
11/11/1995 1.43E-14 9.00E-14 2.25E-14 5.70E-15 2.00E-14 5.00E-15 2.61E-15 9.00E-13 2.25E-13 5.60E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 1.19E-14 9.00E-14 2.25E-14 3.80E-16 2.00E-14 5.00E-15 6.lOE-15 9.00E-13 2.25E-13 6.48E-15 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
5/6/1996 4.SSE-16 9.00E-14 2.25E-14 3.57E-15 2.00E-14 5.00E-15 2.84E-16 9.00E-13 2.25E-13 7.68E-15 6.00E-13 1.SOE-13 Not Analyzed Not AJ:!.plicable Not AJ:!.Plicable
8/5/1996 7.78E-16 9.00E-14 2..25E-14 3.SlE-15 2.00E-14 5.00E-15 1.69E-16 9.00E-13 .2.25E-13 4.90E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 1.36E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 4.21E-16 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.50E-13 Not Analyzed . Not Applicable Not Applicable
2/6/1997 1.00E-16 9.00E-14 2.25E-14 1.40E-16 2.00E-14 5.00E-15 1.03E-16 9.00E-13 :Z.25E-13 6.76E-15 6.00E-13 1.SOE-13 Not Analyzed }Jot Applicable Not Applicable
5/5/1997 1.00E-16 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 2.24E-16 9.00E-13 :2.25E-13 4.55E-15 6,00E-13 1.SOE-13 Not Analyzed Not A0!1icable . Not Applicable
8/11/1997 ~.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 Applicable 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 Ap~licable No! Ap~licable
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 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 4.60E-16 9.00E-14 2.25E-14 9.02E-16 2.00E-14 5.00E-15 3.54E-16 9.00E-13 2.25E-13 6.91E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 4.08E-16 9.00E-14 2.25E-14 4.93E-16 2.00E-14 5.00E-15 2.53E-16 9.00E-13 2.25E-13' 4.52E-15 6.00E-13 1.50E-13 Not Analyzed Not AJ:!.Plicable 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 'f.25E-13 6.73E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not iy>plicable
3/29/1999 5.llE-16 19.00E-14 2.25E-14 4.70E-16 2.00E-14 5.00E-15 3.70E-16 9.00E-13 2.ZSE-13 8.96£-15 6.00E-13 1.50E-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 1.28E-16 9.00£-13 2.25E-13 6.40E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable -9/27/1999 1.70E-15 9.00E-14 2.25E-14 7.50E-16 2.00E-14 5.00E-15 4.61E-16 9,00E-13 2.25E-13 7.86E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not AJ<plicable
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 l.OOE-16 ~.OOE-14 2.25E-14 2.13E-16 2.00E-14 5,00E-15 2.ZOE-16 9.00E-13 2.25E-13 5.61E-15 6,00E-13 1.50E-13 Not Analyzed Not Al)plicable Not AJ:!.Plicable
6/26/2000 1.75E'-16 9.00E-14 2.25E-14 3.0SE-16 2.00E-14 5.00E-15 1.llE-16 9.00E-13 2.25E-13 3.92E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2000 3.65E-16 9.00E-14 2.25E-14 2.0lE-16 2.00E-14 5,00E-15 2.24E-16 9.00E-13 2.25E-13 7.79E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/26/2000 2.27E-16 9.00E-14 _2.25E-14 l.OOE-16 2.00E-14 5.00E-15 4.35E-16 9.00E-13 2.25E-13 8.45E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 1.45E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 6.37E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ~__plicable
7/2/2001 1.00E-16 9.00E-14 2.25E-14 l.05E-16 2.00E-14 5.00E-15 1.00E-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 1.91E-16 9.00E-14 2.25E-14 l.OOE-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 Anajyzed Not Applicable Not Applicable
12/31/2001 1.38£-16 9.00E-14 2.25E-14 2.05E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.83E-15 6.00E-13 l .50E-13 Not Analyzed Not AJ:!.Plicable . NoJ A_pplicable
4/1/2002 2.20E-16 9.00E-14 2.25E-14 3.38E-16 2.00E-14 5.00E-15 1.26£-16 9.00E-13 2.25E-13 7.48E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
7/1/2002 1.97E-16 9.00E-14 2.25E-14 4.lOE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.40E-15 6.00E-13 l.SOE-13 Ne>t Analyzed Not Applicable Not Applicable
9/30/2002 2.30E-16 9.00E-14 2.25E-14 2.42E-16 2.00E-14 S.OOE-15 1.56E-16 9.00E-13 2.25E-13 4.21E-15 6.00E-13 l.50E-13 Not Analyzed Not ~plicable 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 Not Analyzed Not Ap_plicable Not Applicable
3/31/2003 2.50E-16 9.00E-14 ·2.25E-14 1.69E-16 2.00E-14 5.00E-15 1.29E-16 9.00E-13 2.25E-13 4.55E-15 6.00E-13 l.50E-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 l.50E-13 Not Analyzed Not Applicable Not ~__plicable
9/29/2003 1.00E-16 9.00E-14 2.25E-14 8.53E-16 2.00E-14 S.OOE-15 3.32E-16 9.00E-13 2.25E-13 8.69E-15 6.00E-13 .1.50E-13 Not Analyzed Not Applicable Not A__pplicable
12/29/2003 1.02E-16 9._QOE-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 Ana!Yzed 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 1.50E-13 Not Analyzed Not Applicable Not Ap__plicable
9/27/2004 l.OOE-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 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 l,37E-14 6.00E-13 l ,50E-13 Not Analyzed Not Applicable Not Applicable
3/28/2005 1.00E-16 9.00E-14 2.25E-14 2.66E-16 2.00E-14 5.00E-15 3.15E-16 9.00E-13 2.25£-13 9.22E-15 6.00E-13 1.50E-13 Not Analyzed Not ~__plicable Not Ap_plicable
6/29/2005 1.47E-16 9.00E-14 2.25E-14 1.45E-15 2.00E-14 S.OOE-15 1.42E-16 9.00E-13 ?-25E-13 9.34E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 2.0lE-16 9.00E-14 2.25£-14 2.06E-16 2.00E-14 5.00E-15 4.80E-16 9.00E-13 2.25E-13 2.12E-14 6,00E-13 1.50E-13 Not Analyzed Not A@licable Not Applicable
1/3/2006 4.54E-16 9.00E-14 ,1.25E-14 1.24E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25£-13 3.60E-14 6.00E-13 1.50E-13 Not Analyzed ·Not Applicable Not A1>plicable ,
4/3/2006 1.99E-16 9.00E-14 2.25E-14 1.32E-16 2.00E-14 5.00E-15 .1.00E-16 9.00E-13 2.25E-13 8.36E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/3/2006 2.76E-16 9.00E-14 2.25£-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-4U Effluent 2E-14 uCi/ml BHV-4T230 ~ffluent 9E-13 uCi/ml BHV-4R Effluent 6E-13 uCi/ml BHV-4PB Effluent 4e-15 uCi/ml BHV-4TZ3Z
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
AlARAGoal = Z.ZSE-14 uCi/ml ALARA Goal= SE-15 uCi/ml ,A.LARA Goal= 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal= lE-15 uClfml --
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 l.ZSE-12 uCi/ml Pre 1994 ALARA SE-13 uCi/ml Pre 1994 lE-12 uCi/ml Pre 1994 j\lot Applicable
ALARAGOAL= GOAL= ALARAGOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA ,Cone EFC EFCA
10/2/2006 ~.97E·16 g.OOE-14 2.25E-14 2.37E-16 2.00E-14 5,00E-15 1.00E-16 '9.00E-13 2.25E-13 1.60E·l4 6.00E-13 1.50E-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
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.SOE-13 Not Analyzed Not Applicable Not A~plicable
7/2/2007 9.41E-16 9.00E-14 2.25E-14 1.46E-16 2.00E-14 5.00E-15 l.99E-16 9.00E-13 2.25E·l30 2.56E-14 6.00E-13 l.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 l.OOE-16 9.00E-13 2.25E-13. 7.57E-15 6.00E-13 1.SOE-13 Not Analy:zed Not Applicable Not Applicable
12/31/2007 1.42E-15 9,00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 9.93E·l5 6,00E-13 1.SOE-13 Not Analyzed Not Applicable Not J\pplicable
3/31/2008 1.2SE·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.SOE-13 Not Analy:zed Not Applicable Not Applicable
6/30/2008 128E-15 9.00E-14 2.25E-i4 1.00E-16 2.00E-14 5.00E-15 3.61E-16 9.00E-13 2.25E-13 1.lSE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not ly)plicable
9/30/2008 2.72E-15 9.00E-14 2.25E-14 1.27E-15 2.00E-14 5.00E-15 7.66E-16 9.00E-13 2.25E·13 l.lOE-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Ap_elicable
12/31/2008 2.88E-15 9.00E-14 2.25E-14 1.lOE-15 2.00E-14 5.00E-15 6.56E-16 9.00E-13 2.25E-13 1.38E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not AJ>.plicable
3/15/2009 1.56E-15 9.00E-14 2.25E-14 4,57E-16 2.00E-14 5.00E-15 2.99E-16 9.00E-13 2.25E-13 4.97E-15 6.00E-13 1.SOE-13 Not Analyzed /\lot A~licable /\lot Applicable
6/15/2009 5.67E-17 9.00E-14 2.25E-14 2.17E-16 2.00E-14 5.00E-15 l.SlE-16 9.00E-13 2.25E-13° 4.47E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/15/2009 4.0SE-15 9.00E-14 2.25E-14 l.45E·15 2.00E-14 5.00E-15 2.52E-16 9.00E-13 2.25E-13 1.24E·14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 6.SOE-15 · 9.00E-14 2.25E-14 3.48E·16 2.00E-14 5.00E-15 1.33E-16 ·~.OOE-13 2.25E-13 7.60E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not A~licable
3/31/2010 6.0lE-15 9.00E-14 2.25E-14-1.26E·16 2.00E-14 5.00E-15 l.34E-16 9.00E-13 2.25E-13 1.19E·14 6.00E-13 1.SOE-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 ;1..66E-16 9.00E-13 2.25E-13 3.27E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2010 4.77E-15 9.00E-14 2.25E-14 l.BOE-15 2.00E-14 S.OOE-15 8.23E-16 9.00E-13 2.25E-13 5.llE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2010 3.93E·15 9.00E-14 2.25E-14 3,90E-16 2.00E-14 S.OOE-15 2.56E·16 9.00E-13 2.25E-13 l.BE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not A~licable
4/4/2011 1.29E-15 9.00E-14 2.25E-14 l.40E-16 2.00E-14 5.00E-15 158E·16 9.00E-13 2.25E-13 1.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.SOE-13 Not Analyzed Not Ai:>_plicable Not Applicable
10/3/2011 1.32E-15 9.00E-14 2.25E-14 7.89E-16 2.00E-14 5.00E-15 1.28E·16 9.00E-13 2.25E-13 1.lSE-14 6.00E-13 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 114E·14 6,00E-13 l.SOE-13 Not Analyzed Not Applicable Not l\pplicable
4/3/2012 2.51E·l5 i,.OOE-14 2.25E·14 5.02E-16 2.00E-14 5.00E-15 2.27E-16 9.00E-13 ;2.25E-13 1.03E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable /\lot ~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 l.SOE-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 S.OOE-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 2.25E-1{ 6.89E-16 2.00E-14 S.OOE-15 3.75E-16 S.OOE-13 2.25E-13 1.56E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 3.04E-15 9 OOE-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 1.50E-13 /\lot Analyzed Not Applicable ,Not Applicable
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·l5 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not ~plicable
9/30/2013 2.98E-15 9.00E-14 2.25E-14 4.49E-16 2.00E-14 5.00E-15 l.54E-16 _9.00E-13 2.25E-13 7.49E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not A_p_plicable
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 1.50E-13 Not Analyzed Not A_pplicable Not Applicable
3/31/2014 4.69E-15 9.00E-14 2.25E-14 1.37E-16 2.00E-14 5.00E-15 3.53E·16 9.00E-13 2.25E-13 1.0BE-14 6.00E-13 l.50E·l3 Not Anajyzed Not Applicable Not Applicable
6/30/2014 4.16E-15 9.00E-14 2.25E014 6,96E-16 2.00E-14 5.00E-15 L77E-15 9.00E-13 2.25E-13 1.06E-14 6.00E-13 1.SOE-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 1.50E-13 l.OlE-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 1.90E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 1.00E-15
3/30/2015 5.90E-15 .9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 2.SOE-14 6.00E-13 1.SOE-13 5,00E-19 4.00E-15 1.00E-15
6/29/2015 1.80E·15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 1.20E·14 6.00E-13 1.SOE-13 1.00E-17 4.00E-15 l.OOE·l?
9/28/2015 5.00E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.00E·lS 6.00E-13 1.SOE-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.SOE-13 8 OOE-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 1.70E-14 6.00E-13 1.SOE-13 2.00E-18 4.00E-15 1.00E-15
6/27/2016 2.90E·15 9.00E-14 2.25E-14-5.00E-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2 25E-13 8.80E-15 6.00E-13 1.SOE-13 /';.OOE-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 1.50E-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.SOE-16 '9.00E-13 2.25E-13 2.20E-14 6.00E-13 1.SOE-13 4.50E·18 4.00E-15 1.00E-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 1.00E-14 6.00E-13 l.50E-13 1.00E-18 J 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 !3.00E-17 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 1.SOE-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 1.60E·14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 l.OOE-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 2,25E-13 2.20E·14 6.00E-13 1.50E-13 2.00E-17 4.00E-15 1.00E-15
3/26/2018 6.80E·l6 9.00E-14 2.25E-14 1.20E·16 2.00E-14 5.00E-15 5.70E-17 9.00E-13 2.25E-13 1.40E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 l.OOE-15
6/25/2018 1.SOE-15 9.00E-14 2.25E-14 8.20E-17 2.00E-14 5,00E-15 3.70E·17 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 1.SOE-13 l.20E-17 4.00E-15 1.00E-15
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60-das
so-das
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go-das
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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
vs-das
88-das
is-das
~9-das
Sep-81
Sep-82
Sep-83
Sep-84
Sep-85
Sep-86
Sep-87
Sep-88
Sep-89
Sep-90
Sep-91
Sep-92
Sep-93
Sep-94
Sep-95
Sep-96
Sep-97
Sep-98
Sep-99
Sep-00
Sep-01
Sep-02
Sep-03
Sep-04
Sep-05
Sep-06
Sep-07
Sep-08
Sep-09
Sep-10
Sep-11
Sep-12
Sep-13
Sep-14
Sep-15
Sep-16
Sep-17
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80-das
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66-das
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96-das
95-das
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86-das
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05-das
59-das
99-das
Ls-das
99-das
99-das
vs-das
8s-das
cs-das
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Sep-14
Nov-14
Jan-15
Mar-15
May-15
Jul-15
Sep-15
Nov-15
Jan-16
Mar-16
May-16
Jul-16
Sep-16
Nov-16
Jan-17
Mar-17
May-17
Jul-17
Sep-17
Nov-17
Jan-18
Mar-18
May-18
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-
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TAB5
BHV-5 AIR SAMPLING GRAPHS AND DAT A TABLE
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 = ;z.2SE-14 uCi/ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.2SE-13 uCijml 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-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
Limit= Limit= limit= Limit= Limit= -Pre 1994 1.2SE-U uCiJ ml Pre 1994 SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= GOAL= ALARAGOAL=
Cone :~FC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC _ ~FCA
9/28/1981 2.44E-15 S.OOE-12 t.2se-12· 1.53E-15 8.00E-14 2.00E-14 7.54E-16 i .OOE-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·l5 8.00E-14 2.00E-14 l.84E-15 2.00E-12 5.00E-13 1.53E·14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable J'-Jot 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 l.OOE-12 Not Analyzed Not l\pplicable Not Applicable
6/30/1982 3.61E-15 5.00E-12 1.2SE-12 7.61E-15 8.00E-14 2.00E-14 1.39E-15 2.00E-12 5.00E-13 1.80E-15 4.00E-12 l.OOE-12 Not Analyzed Not J\p_plicable 'rliot AJ!lllicable
9/27/1982 1.71E-14 5.00E-12 __ 1.25E-12 9.46E·15 8.00E-14 LOOE-14 3.SOE-15 2.00E-12 5.00E-13 2.35E-14 4.00E·12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 1.90E-14 5.00E-12 1.25E-12 S.77E·15 8.00E-14 2.00E-14 9.34E-17 2.00E-12 5.00E-13 4.32E-14 4.00E-12 l.OOE-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 Not Applicable Not Applicable
6/30/1983 7.62E·16 5.00E-12 1.25E-12 3.25E-15 8.00E-14 2.00E-14 6.28E-15 2.00E-12 5.00E-13 2.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/3/1983 4.86E·16 5.00E-12 _ J.25E-12 l.lOE-15 8.00E-14 2.00E-14 3.63E-16 2.00E-12 5.00E-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 1.2SE-12 9.69E-16 8.00E-14 2.00E-14 9.60E-16 2.00E-12 5.00E-13 1.83E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
4/2/1984 1.64E-15 S.OOE-12 1.25E-12 1.34E-15 8.00E-14 2.00E-14 3.88E-15 :Z.OOE-12 S.OOE-13 4.67E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable _ Not A_p_11licable
7/2/1984 _1.12E-15 S.OOE-12 . t.25E-12 1.92E-15 8.00E-14 2.00E-14 3.31E-15 2.00E-12 5.00E-13 2.21E-14 4.00E-12 1.00E-12 Not 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 5.00E-12 1.25E-12 6.71E-16 8.00E-14 2.00E-14 4.94E-16 2.00E-12 5.00E-13 2.42E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
4/1/1985 2.36E-16 5.00E-12 1.25E-12 5.43E-16 8.00E-14 2.00E-14 2.71E-16 2.00E-12 5.00E-13 1.25E-14 4.00E-12 l.OOE-12 Not Analyzed Not l\~licable 'Not Ap_glicable
7/1/1985 J.SSE-16 S.OOE-12 1.25E-12 4.00E-16 8.00E-14 2.00E-14 6.90E-16 2.00E-12 S.OOE-13 2.15E·14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A]!glicable
9/30/1985 7.47E-15 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 Applicable
1/2/1986 1.75E-14 5.00E-12 1.25E-12 7.24E-15 8.00E-14 2,00E-14 3.83E-15 2.00E-12 5.00E-13 1.BE-16 4.00E-12 1.00E-12 Not Analyzed Not ApE!!!.cable Not Applicable
4/1/1986 2.99E-14 5.00E-12 1.25E-12 7.64E-15 8.00E-14 LOOE-14 1.SlE-14 2.00E-12 5.00E-13 2.22E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
6/30/1986 2.23E·14 S.OOE-12 .1.25E-12 5.19E-15 8.00E-14 2.00E-14 1.0SE-14 2.00E-12 5.00E-13 2.16E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 2.33E-14 S.OOE-12 l.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 5.35E-15 8.00E-14 2.00E-14 1.47E-14 2.00E-12 5.00E-13 2.82E-14 4.00E-12 1.00E-12 Not Analyzed Not AP.plicable Not A~plicable
3/16/1987 2.0GE-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.SOE-14 S.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 ?.GSE-14 5.00E-12 l.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 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/2/1987 1.SOE-14 5.00E-12 t.25E-12 7.09E-15 8.00E-14 2.00E-14 7.20E-15 :i.ooe-12 5.00E-13 1.77E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not A_p_.111icable
2/16/1988 1.0lE-14 S.OOE-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 1.78E-14 5.00E-12 1.25E-12 8.14E-15 8.00E-14 2.00E-14 7.43E-15 2.00E-12 .5.00E-13 2.12E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/15/1988 l.79E-14 5.00E-12 .1.25E-12 l.49E-14 8.00E-14 2.00E-14 S.34E-15 :i.ooe-12 5.00E-13 2.45E-14 4.00E-12 1.00E-12 Not Analyzed Not I\Pplicable Not Applicable
11/14/1988 4.46E-14 5.00E-12 -·1.2SE-12 l.39E-14 8.00E-14 2.00E-14 1.17E-14 2.00E-l.2 5.00E-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 l.25E-12 5.54E-15 8.00E-14 2.00E-14 7.20E-15 2,00E-12 5.00E-13 5.02E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
5/15/1989 2.03E·14 .6.00E-12 1.25E-12 7.05E-15 8.00E-14 2.00E-14 9.56E-16 2.00E-12 5.00E-13 1.43E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
8/14/1989 2.SlE-15 S.OOE-12 l .25E-12 3.78E-15 8.00E-14 2.00E-14 9.26E-15 '2.00E-12 5.00E-13 l.SOE-14 4.00E-12 1.00E-12 Not Analyzed Not ApplLcable Not Applicable
11/13/1989 S.38E-14 5.00E-12 __ 1.25E-12 8.0lE-15 8.00E-14 2.00E-14 1.SlE-14 2.00E-12 5.00E-13 4.09E-14 4.00E-12 1.00E-12 Not~ed Not Applicable Not Applicable
2/12/1990 4.48E-14 5.00E-12 1.25E-12 1.48E·l4 8.00E-14 2.00E-14 l.28E-14 2.00E-12 :5.00E-13 3.88E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not A.{lplicable
5/14/1990 2.18E-14 5.00E-12 1.25E-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 l ,OOE-12 Not Analyzed Not Applicable -Not Applicable
8/13/1990 ',!.53E·15 S.OOE-12 1.25e-12· 1.70E·14 8.00E-14 2.00E-14 3.27E-15 2.00E-12 :S.OOE-13 1.27E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/12/1990 1.llE-14 5.00E-12 1.25E-12 5.27E·15 8.00E-14 2.00E-14 5.38E-15 2.00E-12 5,00E-13 1.56E-14 4,00E-12 l.OOE-12 Not Analyzed Not Applicable Not AP.plicable
2/11/1991 6.3SE-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 1.00E-12 Not Analyzed Not Applicable Not Applicable
5/13/1991 1.22E-15 5.00E-12 1.25E-12 6.14E-15 8.00E-14 2.00E-14 4.41E-15 2.00E-12 5.00E-13 2.50E-14 4,00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/12/1991 7.84E-16 5.00E-12 _1.25E-12 l.43E-15 8.00E-14 2.00E-14 4.47E-16 2.00E-12 5.00~-1J 1.84E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
11/11/1991 5.37E-16 5.00E-12 . °1.2SE-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 l .OOE-12 Not Analyzed Not A~licable Not A~licable
2/10/1992 3.54E-16 5.00E-12 1.25E-12 1.18E-16 8.00E-14 2.00E-14 4.08E-17 2.00E-12 5.00E-13 3.69E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable • NotA~cable
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 5.00E-13 1.43E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/10/1992 5.32E-15 5.00E-12 l.25E-12 3.36E-16 8.00E-14 2.00E-14 l.65E-16 2.00E-12 ~.OOE-13 l.59E-14 4,00E-12 l ,OOE-12 Not Analyzed Not Applicable Not Applicable
11/9/1992 3.66E-16 5.00E-12 · ·1.2se-12 2.25E-16 8.00E-14 2.00E-14 1.0SE-16 2.00E-12 5.00E-13 2.24E-14 4.00E-12 l .OOE-12 Not Analyzed Not Applicable Not Applicable
2/9/1993 2.0SE·l6 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 fllot Analyzed Not Applicable • Not Applicable
5/10/1993 4.80E·16 5.00E-12 1.25E-12 8.25E-16 8.00E-14 2.00E-14 1.26E-15 2.00E-12 . 6.00E-13 1.83E-14 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
8/10/1993 8.30E-16 5.00E-12 1.2SE-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 ~ffluent 9E-14 uCi/ml BHV-SU Effluent ZE-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
Umit= Limit= Limit= Limit= Limit=
ALARAGoal= Z.ZSE-14 ugf_ml ALARA Goal= SE-15 uCi/ml ALARAGoal= 2.ZSE-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ALARAGoal= lE-15 uCi[ml
P,el994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994 MPC ZE-12 uCi7ml pre 1994 MPC 4E-12 uCi/ml Pre 1994 MPC Not Applicable
limit= limit= Limit= Limit= Limit=
)>re 1994 1.ZSE-12 uCi/ml Pre 1994 SE-13 uCi/ml Pre 1994 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGOAL= ALARAGOAL= GOAL= ALARAGOAL=
Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cont 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 S.OOE-13 2.34E-14 4.00E-12 1.00E-12 Not Analyzed " Not Applicable Not Applicable
2/7/1994 3.lSE-16 5.00E-12 .1.25E-12 1.00E-16 8.00E-14 2.00E-14 5.lSE-16 2.00E-12 5.00E-13 3.64E-14 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap_plicable
S/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 1.00E-12 Not Analyzed Not Applicable Not Applicable
8/9/1994 2.67E-15 5.00E-12 1.25E-12 1.llE-15 8.00E-14 2.00E-14 4.95E-16 2.00E-12 .5.00E-13 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not A(!plicable Not Applicable
11/7/1994 9.21E-17 5.00E-12 l.25E-12 1.59E-15 8.00E-14 2.00E-14 1 66E-15 2.00E-12 '5.00E-13 1.00E-16 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
2/7/1995 1.51E-15 9.00E-14 2.25E-14 9.SOE-16 2.00E-14 5.00E-15 9.70E-17 9.00E-13 2.25E-13 9.35E-15 6.00E-13 1.50E-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 1.66E-16 9.00E-14 2.25E-14 1.67E-15 2.00E-14 5.00E-15 3.90E-15 9.00E-13 2.25E-13 5.60E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A.J!plicable
11/11/1995 2.04E-14 9.00E-14 2.25E-14 6.70E-15 2.00E-14 5.00E-15 7.65E-15 g.OOE-13 2.25E-13 4.47E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Ap.J!licable
2/5/1996 ~.50E-14 9.00E-14 2.25E-14 3.58E-14 2.00E-14 5.00E-15 2.39E-14 9.00E-13 2.25E-13 7.30E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
5/6/1996 1.76E-15 9.00E-14 2.25E-14 3.57E-15 2.00E-14 5.00E-15 9.55E-16 9.00E-13 2.25E-13 7.54E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
8/5/1996 2.37E-15 -9.00E-14 2.25E-14 8.lSE-15 2.00E-14 5.00E-15 7.46E-16 9.00E-13 2.25E-13 5.75E-15 6.00E-13 1.50E-13 Not Analyzed t,lot Applicable Not Applicable
11/6/1996 3.53E-15 9.00E-14 2.25E-14 5.31E-15 2.00E-14 5.00E-15 9.39E-16 9.00E-13 2.25E-13 1.21E-14 6.00E-13 1.50E-13 'Not Analyzed Not Applicable Not Applicable
2/6/1997 1.84E-16 _19.00E-14 • 2.25E-14. 2.0lE-16 2.00E-14 5.00E-15 1.87E-16 9.00E-13 2.25E-13 6.14E-15 6.00E-13 l.50E-13 Not Analyzed Not ~pplicable Not Applicable
5/5/1997 5.75E-16 9.00E-14 2.25E-14 7.24E-16 2.00E-14 5.00E-15 !'i.07E-16 9.00E-13 2.25E-13 4.75E-15 6.00E-13 l.SOE-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 .S.05E-16 9.00E-13 2.25E-13 4.92E-15 6.00E-13 1.50E-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 L50E-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 1.72E-15 9.00E-13 2.25E-13 7.35E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 7.49E-16 9.00E-14 2.25E-14 1.49E-15 2.00E-14 5.00E-15 8.34E-16 9.00E-13 2.25E-13 7.0lE-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/28/1998 1.07E-15 9.00E-14 2.25E-14 9.20E-16 2.00E-14 5.00E-15 6.32E-16 9.00E-13 2.25E-13 3.95E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
12/28/1998 8.SlE-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 1.43E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/29/1999 3.75E-15 9.00E-14 2.25E-14 2.45E-15 2.00E-14 5.00E-15 2.39E-15 9.00E-13 2.25E-13 8.46E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/3/1999 1.53E-15 9.00E-14 2.25E-1{ 8.65E-16 2.00E-14 5.00E-15 6.52E·l6 9.00E-13 2.25E-13 7.20E-15 6.00E-13 1.SOE-13 Nat Analyzed Not Applicable Not Applicable
9/27/1999 5.83E-15 9.00E-14 2.25E-14 3.52E-15 2.00E-14 5.00E-15 2.55E-15 '9.00E-13 2.25E-13 8.22E-15 6.00E-13 1.50E-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 ~.OOE-13 2.25E-13 7.56E-15 6.00E-13 1.50E-13 Not Analyzed Not ~plicable Not A_pplicable
3/27/2000 2.06E-15 9.00E-14 2.25E-14 L27E-15 2.00E-14 5.00E-15 1.09E-15 09.00E-13 2.25E-13 7,72E-15 6.00E-13 1.50E-13 Not Analyzed Not Applical)le Not Applicable
6/26/2000 J..SOE-15 9.00E-14 2.25E-14 1.24E-15 2.00E-14 5.00E-15 1.0lE-15 9.00E-13 2.25E-13 4.36E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2000 'L04E-15 9.00E-14 2.25E-14 5.45E-16 2.00E-14 5.00E-15 6.0lE-16 9.00E-13 2.25E-13 7.67E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/26/2000 1..48E·l5 9.00E-14 2.25E-14 7.56E-16 2.00E-14 5,00E-15 6.84E-16 9.00E-13 2.25E-13 7.00E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/26/2001 4.27E-16 9.00E-14 2.25E-14 2.19E-16 2.00E-14 5,00E-15 1.89E-16 9.00E-13 2.25E-13 6.13E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 4.52E-16 9.00E-14 2_.25E-14 4.02E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 7.48E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/24/2001 4.65E-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 1.SOE-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 5.00E-15 3.64E-16 9.00E-13 2.25E-13 4.72E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/1/2002 1.26E-15 9.00E-14 2.25E-14 7.53E-16 2.00E-14 5.00E-15 7.19E-16 9.00E-13 2.25E-13 9.65E-15 6.00E-13 1.SOE-13 Not Analyzed Not Ap_plicable Not Applicable
7/1/2002 1.02E-15 9.00E-14 2.25E-14 1.03E-15 2.00E-14 5.00E-15 3.39E-16 9.00E-13 2.25E-13 7.20E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2002 ?-82E-16 9.00E-14 2.25E-14 9.28E-16 2.00E-14 5.00E-15 3.14E-16 9.00E-13 2.25E-13 4.48E·l5 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/30/2002 l.OOE-16 9.00E-14 2.25E-14 7.67E-16 2.00E-14 5.00E-15 3.48E-16 9.00E-13 l.25E-13 9.56E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
3/31/2003 l.13E-15 9.00E-14 "2.25E-14 7.41E-16 2.00E-14 5,00E-15 4.41E-16 9.00E-13 225E-13 6.68E-15 6.00E-13 l .50E-13 Not Ana!yzed Not ~_plicable Not A!J.Plicable
6/30/2003 ~.35E-16 9.00E-14 1.25E-14 5.0BE-16 2.00E-14 5.00E-15 2.51E-16 9.00E-13 2.25E-13 1.34E-15 6.00E-13 l.50E-13 Not Analyzed Not~plicable Not Applicable
9/29/2003 1.51E·16 9.00E-14 j 2.25E-14 1.02E-16 2.00E-14 5,00E-15 1.00E-16 9.00E-13 2.25E-13 7.28E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/29/2003 ~.52E-16 9.00E-14 2.25E-14 l.54E-16 2.00E-14 5.00E-15 1.51E-16 9.00E-13 2.25E-13 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,14 1.12E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 '2.25E-13 8.82E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
6/27/2004 'l.18E-16 9.00E-14 2.25E-14 3.llE-16 2.00E-14 5.00E-15 1.25E-16 9.00E-13 .2.25E-13 2.47E-15 6.00E-13 l.50E-13 !',lot Analyzed Not Applicable Not Applicable
9/27/2004 1.16E-16 9.00E-14 2.25E-14 L72E-16 2.00E-14 5.00E-15 l.lSE-16 9.00E-13 2.25E-13 l.lOE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
12/27/2004 l.14E-16 9.00E-14 2.25E-14 1.06E-16 2.00E-14 5,00E-15 l.OOE-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 l.OOE-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.S7E-15 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
6/29/2005 1.83E-16 (1.00E-14 2.25E-14 3.81E-16 2.00E-14 5.00E-15 3.09E·16 /j.OOE-13 2.25E-13 l.06E-14 6.00E-13 l .50E-13 Not Analyzed Not Applicable Not Applicable
9/26/2005 2.87E-16 9.00E-14 2.25E-14 8.21E-16 2.00E-14 5,00E-15 3.71E-14 9.00E-13 2.25E-13 6.28E-14 6.00E-13 l .50E-13 Not Analyzed ]\lot Applicable Not Applicable
1/3/2006 ,8.74E-16 !l.OOE-14 2.25E-14 3.79E-16 2.00E-14 5.00E-15 1.31E-16 9.00E-13 2.25E-13 4.32E·l4 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
Date 'effluent 9E-14 uCi/ml BHV-SU Effluent ZE-14 uCi/ml BHV-5T230 Effluent 9E-13 uCi/ml BHV-SR Effluent GE-13 uCi/ml BHV-SPB Effluent 4e-15 uCi/ml -BHV-5T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= limit= Limit=
ALARAGoal= 2.25E-14 uCj/ml_ ALARA Goal= SE-15 uCi/ml AlARAGoal= 2.25E-13 ug/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 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 ALARA lE-12 uCi/ml Pre 1994 Not Applicable
ALARAGDAL= ALARAGOAL= GOAL= /ILARAGOAL=
Cone ~FC 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 5.00E-15 l .llE-16 9.00E-13 2.25E-13 9.34E-15 6,00E-13 1.SOE-13 Not Analyied Not ~_plicable Not Applicable
7/3/2006 3.0SE-16 9.00E-14 2.ZSE-14 l.lOE-16 2,00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.25E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
10/2/2006 9.14E-16 9.00E-14 2,25E-14 4.9SE·16 2.00E-14 5.00E-15 '1.86E-16 9.00E-13 2.25E-13 1.67E·l4 6,00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 9.49E-16 9.00E-14 2.25E-14 6.SlE-16 2.00E-14 5.00E-15 2.02E-16 9.00E-13 2.25E-13 L31E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
4/2/2007 l.OSE-15 ~.OOE-14 2.25E-14 8.22E-16 2.00E-14 5.00E-15 2.26E-16 9.00E-13 2.25E-13 1.64E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2007 1.54E-15 9.00E-14 2.25E-14 8.16E-16 2.00E-14 S.OOE-15 4.76E-16 9.00E-13 2.25E-13 2.12E-14 6.00E-13 l.SOE-13 NotAna)}'zed Not A111>licable _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 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.02E-14 6.00E-13 l.50E-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-13 Not Analyzed Not Applicable Not Applicable
6/30/2008 3.BE-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.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2008 7.0SE-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 l.lSE-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 1.SOE-13 Not Analyzed Not A111>licable Not Applicable
3/15/2009 4.13E-15 9.00E-14 2.25E-14 l.39E-15 2.00E-14 5.00E-15 l.41E-15 9.00E-13 2.25E-13 4.66E-15 6.00E-13 1.SOE-13 Not Analyzed Not A111>licable Not Applicable
6/15/2009 2.31E-16 9.00E-14 2.25E-14 7.79E-16 2.00E-14 5,00E-15 6.37E-16 9.00E-13 2.25E-13 4.l SE-15 6,00E-13 1.SOE-13 ,Not Analyzed Not ARplicable 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 2.2SE·13· l.21E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/15/2009 5.77E-15 _9.00E-14 2.25E-14 3.13E-16 2.00E-14 5.00E-15 l.92E-16 9.00E-13 2.25E-13 2.48E-15 6.00E-13 1.SOE-13 r,Jot Anajyzed Not Applicable Not Applicable
3/31/2010 4.78E-1S 9.00E-14 2.25E-14 3.73E-16 2.00E-14 5.00E-15 4.19E-16 9.00E-13 ;t.25E-13 l.30E-14 6.00E-13 1.50E-13 Not Analyzed Not Al1l!fu:able Not Applicable
6/30/2010 4.35E-15 9.00E-14 2.25E-14 7.84E-16 2.00E-14 5.00E-15 l.OSE-15 9.00E-13 '2.2SE-13 4.40E-15 6.00E-13 l.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-13 3.78E-1S 6.00E-13 l.SOE-13 Not Analyzed Not A11plicable Not Applicable
12/31/2010 8.52E-15 9.00E-14 2.25E-14 l.45E-15 2.00E-14 5.00E-15 1.29E-15 9.00E-13 2.25E-13 l.33E-14 6.00E-13 1,50E-13 Not Analyzed Not Applicable Not A!>Jllicable
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 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/4/2011 6.98E-15 lJ.OOE-14 2.25E-14 2.03E-15 2.00E-14 5.00E-15 2.52E-15 9.00E-13 2.25E-13 1.08E-14 6.00E-13 1.SOE-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-13 Not Analyzed Not A111>licable Not Applicable
1/3/2012 4.44E-15 9.00E-14 2.25E-14 2.14E-15 2.00E-14 5.00E-15 1.53E-15 9.00E-13 ~.25E-13 2.05E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/3/2012 5.52E-1S 9.00E-14 2.25E-14 3.24E-15 2.00E-14 5.00E-15 1.79E-15 9.00E-13 2.25E-13 1.55E-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2012 5.87E-15 9.00E-14 -2.25E-14 3.06E-1S 2.00E-14 5.00E-15 1.21E-1S 9.00E-13 2.25E-13 1.llE-14 6.00E-13 l.SOE-13 Not Analyzed , Not ApRlicable Not Applicable
10/1/2012 6.73E-15 .[3.00E-14 2.25E-14 2.59E-15 2,00E-14 5.00E-15 2.43E-1S jl.OOE-13 2 25E-13 UOE-14 6.00E-13 1.SOE-13 Not Analyzed Not A,mlicable Not A11plicable
12/31/2012 4.SOE-15 9.00E-14 2.25E-14 l.62E-15 2.00E-14 5.00E-15 l.79E-15 , 9.00E-13 2.25E-13 l.74E-14 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
3/25/2013 6.66E-1S 9.00E-14 2.25E-14 1.48E-1S 2.00E-14 S.OOE-15 l.12E-15 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
7/2/2013 7.35E-15 9.00E-14 -2.25E-14 1.72E-15 2.00E-14 5.00E-15 2.02E-15 9.00E-13 2.25E-13 6.67E-15 6.00E-13 l.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 2.78E-15 9.00E-14 2.25E-14 6.92E-16 2.00E-14 5.00E-15 3.29E-16 .9.00E-13 2.25E-13 6.62E-15 6.00E-13 l.SOE-13 Not Analyied 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 l.SOE-13 Not Analyzed Not Applicable Not A11plicable
3/31/2014 4.74E-15 9.00E-14 2.25E-14 l.42E-15 2.00E-14 5.00E-15 ~.48E-15 9.00E-13 2.25E-13 1.50E-14 6.00E-13 l.50E-13 Not Analyzed Not ApJ!licable Not Applicable
6/30/2014 8.lSE-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 l.42E-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 1.32E-14 9.00E-14 2.25E-14 7.76E-16 2.00E-14 S.OOE-15 1.04E-15 .9.00E-13 2.25E-13 l.23E-14 6.00E-13 1.50E-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 S.OOE-15 $.OOE-16 jl.OOE-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 8.00E-18 .4.00E-15 1.00E-15
3/30/2015 1.00E-14 9.00E-14 2.25E-14 5.00E-16 2.00E-14 5.00E-15 ,2.lOE-15 9.00E-13 2.25E-13 3.lOE-14 6.00E-13 l.SOE-13 3.00E-18 4.00E-15 1.00E-15 -6/29/2015 4.60E-15 9.00E-14 2.2SE-14 8.00E-16 2.00E-14 S.OOE-15 :3.70E-15 9.00E-13 2.2SE-13 1.40E-14 6.00E-13 l.50E-13 2 OOE-17 4.00E-15 LOOE-15
9/28/2015 1.20E-14 , 9.00E-14 2.25E-14 4.00E-16 2.00E-14 S.OOE-15 9.80E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1,50E-13 l.OOE-17 4.00E-15 l.OOE-15
12/28/2015 7.40E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.90E-16 9.00E-13 2.25E-13 2.20E-14 6.00E-13 l.SOE-13 2.00E-17 4.00E-15 l.OOE-15
3/28/2016 1.40E-15 9.00E-14 J.25E-14 6.00E-16 2,00E-14 5.00E-15 6.20E-1S 9.00E-13 .2.25E-13 2.30E-14 6.00E-13 l.50E-13 6.00E-17 4,00E-15 1.00E-15
6/27/2016 3.90E-15 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 ;G.OOE-16 9.00E-13 2.25E-13. 1.SOE-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 l.OOE,15
9/27/2016 7.lOE-15 9.00E-14 2 25E-14 7.60E-16 2.00E-14 5.00E-15 l.lOE-15 9.00E-13 2.25E-13 2.90E-16 6.00E-13 1.50E-13 3.00E-17 4.00E-15 1.00E-15
12/27/2016 5.lOE-15 9.00E-14 2.25E-14 6.60E-16 2.00E-14 5.00E-15 9.60E-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.50E-13 1.30E-17 4.00E-15 • ·1.ooE-15
3/27/2017 7.SOE-15 9.00E-14 2.25E-14 3.00E-16 2.00E-14 S.OOE-15 2.lOE-15 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 l.SOE-13 2.00E-17 4.00E-15 l.OOE-15
6/26/2017 8.00E-16 9.00E-14 2.2SE-14 3.00E-16 2.00E-14 5.00E-15 l .OOE-15 9.00E-13 2.2SE-13 1.30E-14 6.00E-13 l.SOE-13 6.00E-18 4.00E-15 l.OOE-15
9/25/2017 2.70E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 l.50E-13 4.00E-18 4.00E-15 .. 1.00E-15
12/26/2017 1.40E-14 9.00E-14 2.25E-14 4.00E-16 2,00E-14 5,00E-15 3,00E-16 9.00E-13 2.25E-13 l.60E-14 6.00E-13 l.50E-13 1.00E-17 4.00E-15 l.OOE-15
3/26/2018 7.lOE-16 9.00E-14 2.25E-14 l.70E-16 2.00E-14 5.00E-15 l.SOE-16 9.00E-13 2.25E-13, l.40E-14 6.00E-13 l.50E-13 2.00E-17 4.00E-15 l.OOE-15
Date Efflu'1!1t 9E-U!J9/ml !!HV·SU Effluent ZE-14 uCi/ml 8HV-5Il30 Effluent 9,E--U u<li/ml BHV-SR Effluent 6E-13 uCi/ml BHV·SPB Effl!,lent 4e-15u6/ml BHV-5T232
Concentration Concentration Co.l'!<;!!!)lf;;i!tl~n Concentration C~tqtio,i
ufuit,.. limit= Umit"' Limit= l,lmlt·= -~~i,~,-~ iµs:l;;.Hu.¢'.i/ml AlARAGoal = SE-15 uCi/ml ~A'-Go_al= Z,25E.13 uc.l[ml AlARAGoal= 1.SE-13 uCi/ml ALA'RA Goal., 1£.15ud/ml
l!re il.994 MPC se~.12 uef/nll Pre 1994 MPC 8E-14 uCi/ml P(e~MPC 2e;12-ui;l/ml Pre 1994 MPC 4E-1Z uCi/ml ~1994MP'C Not Appll~bfe
limit=" limit= limft= limit= !.Jml~=
Pre®a 1.lli--"2 ~/ml Prl! 1!!.94 SE-13'11G/ml Pre 1994 ALARA lE-UuCi/ml Pre1994 Not Applic;ible
ALARAG04L~ ALAIU\~QM;; GOAL= ALARAGE>Ai=
C::onc EFC EFG~ Cone EFC EFCA c.~n~ ~~ EFC;A Cone EFC EFCA GQ:nc EFe ~f(;A
6/25/2018 2.®-E?T:; 9.00E,1-4 •Z.'25E-14 2.40E-16 2.00E-14 5.00E-15 S.90Ee16 9;001:-13 Z.25E--J3 UOE-14 6.00E-13 LSOE·l3 9A9E-18 !I.Q()l:-lsl l ,Oj:)1:-15
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TAB6
BHV-6 AIR SAMPLING GRAPHS AND DATA TABLE
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-6T232
Concentration Concentration Concentration Concentration Concentration
Limit= limit= Limit= limit= Limit=
-
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.25E-13 uCi/ml ALARA Goal= l.SE-13 uCi/ml ~LARA Goal= lE-15 uCiL___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
pmit= 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=
tone EFC -EFCA Cone EFC EFCA tone 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.pOE-13 4.00E-12 l.OOE-12 Not Analyzed Not A(.Jplicable Not Applicable
12/14/1981 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 A11!11icable 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 l.OOE-12 Not Analyzed Not Applicable Not Applicable
6/30/1982 -5.00E-12 l.25E-lt: 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 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
1/3/1983 5.00E-12 l.25E-12 8.00E-14 2.00E-14 J.OOE-12 5.00E-13 4.00E-12 l.OOE-12 NotAna~ed Not Applicable ~plicable
4/4/1983 5.00E-12 l.25E-12 8.00E-14 2.00E-14 i.OOE-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable -
-6/30/1983 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4,00E-12 l.OOE-12 NotA~zed Not Applicable Not Applicable
10/3/1983 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 Anajyzed Not Ap!11icable Not~icable
1/3/1984 ~.OOE-12 I 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4,00E-12 1.00E-12 Not Analy_zed Not Applicable Not Applicable
4/2/1984 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Ap(.Jlicable
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 Anajyzed Not A(.J(.Jlicable Not Applicable
10/1/1984 5.00E-12 , 1.25E-12 8.00E-14 2.00E-14 2.00E-12 : 6.00E-13_ 4.00E-12 l.OOE-12 Not Analyzed _ Not Ap!11icable Not Applicable
1/2/1985 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 N-ot Applicable Not Applicable
4/1/1985 -S.OOE-12 '. L25E-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 S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
9/30/1985 5.00E-12 j [.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 Ap.R[icable
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 Apglicable Not Applicable
4/1/1986 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 Ana_lyzed Not Apglicable , Not ApJ?licable
6/30/1986 5.00E-12 .. 1.25E-12 8.00E-14 2,00E-14 2.00E-12 -:S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed Not Applicable Not Applicable
10/27/1986 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 Applicable Not Applicable
12/15/1986 5.00E-12 ' l.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not Ana_!yzed Not Aµ.plicable I Not Ap_plicable
3/16/1987 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
5/11/1987 !i.OOE-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 -. 8.00E-13_ 4.00E-12 l.OOE-12 Not!'.ln~ed : Not A(.J(.Jfu:able J Not Applicable
9/9/1987 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 :S.OOE-13 4.00E-12 l.OOE-12 Not Analyzed · Not Applicable Not Applicable
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 S.OOE-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 AQ!11icable Not Applicable
5/18/1988 -2,00E-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
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 J l)iot Applicable Not Applicable
11/14/1988 :S.OOE-12 l,25E-12 8.00E-14 2.00E-14 2.00E-12 8.00E-13 4.00E-12 1.00E-12 Not An a lyzed Not Applicable Not Applicable : 2/13/1989 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 l.OOE-12 Not Analyzed • Not Applicable Not Applicable
5/15/1989 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 l.OOE-12 Not Analyzed -Not Apj)licable Not Applicable
11/13/1989 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 Analy_zed Not Ap.J)licable Not A~icable
2/12/1990 -· _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 ~
5/14/1990 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1,00E-12 Not Analyzed Not Applicable Not Applicable
8/13/1990 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
11/12/1990 5.00E-12 1,25E-12 8.00E-14 2.00E-14 2_.!)0E-12 S.OOE-13 4.00E-12 1.00E-12 Not Analyzed · Not Applicable Not Applicable
2/11/1991 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
5/13/1991 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 _
8/12/1991 5.00E-12 l.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 1.00E-12 NotAnal~ed Not Applicable Not A~icable
11/11/1991 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 S.OOE-13 4.00E-12 l.OOE-12 Not~zed ( Not Applicable Not Ag111icable
2/10/1992 5.00E-12 1.25E-12 8.00E-14 2.00E-14 -2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed !"ot Applicable Not Applicable
5/11/1992 5.00E-12 1.25E-12 8.00E-14 2.00E-14 '?,OOE-12 S.OOE-13 4.00E-12 1.00E-12 !'Jot Analyzed Not Applicable Not Applicable
8/10/1992 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 :S.OOE-13 4.00E-12 1.00E-12 iilot Analy_zed Not Applicable Not Ap!11icable
11/9/1992 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 Ana_!yzed • Not A_~icable Not Ag11licable
2/9/1993 5.00E-12 .. l.25E-12 8.00E-14 2.00E-14 2.00E-12 ; 5.00E-13 4.00E-12 1.00E-12 )ilot Analyzed -.Not Applicable Not Applicable
5/10/1993 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
8/10/1993 -};.OOE-12 1.25E-12 8.00E-14 2.00E-14 ~.OOE-12 -S.OOE.-13 4.00E-12 1.00E-12 Not Analyzed Not Applicable Not Applicable
Date Effluent 9E-14 uCi/ml BHV-6U. ~ffluent 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
<;oncentration Concentration Concentration Concentration Concentration
limit= Limit= Limit= Limit= Limit=
ALARAGoal = 2.ZSE-14 uC![ml ALARA Goal= SE-13 uCi/ml ALARAGoal = 2.ZSE-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml Pre 1994 MPC 8E-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=
..
tone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC . EFCA
11/8/1993 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
2/7/1994 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 ARplicable
5/9/1994 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not AnaJyzed Not AQE!licable Not Applicable
8/9/1994 ;i.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
11/7/1994 5.00E-12 1.25E-12 8.00E-14 2.00E-14 2.00E-12 5.00E-13 4.00E-12 1.00E-12 Not Analyzed Not ApQlicable Not Applicable -2/7/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed · Not Applicable Not Applicable
5/9/1995 9_.00E-14 2.25E-14 2.00E-14 5.00E-15 '9,00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
8/9/1995 ~.OOE-14 2.2SE-_14 2.00E-14 5.00E-15 -9.00E-13 2.25E-13 6.00E-13 l.50E-13 NotAnal~ Not Applicable Not Apglicable
11/11/1995 9.00E-14 2.25E-14 2.00E-14 5.00E-15 -9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Applicable
2/5/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 2.00E-13 2.25E-13 6.00E-13 1.50E-13 ['Jot Analyzed Not AQ.Plicable _ .Not Applicable
5/6/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not ARplicable · 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 l.50E-13 Not Analyzed Not Applicable Not Applicable
11/6/1996 9.00E-14 2.25E-14 2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 l.50E-13 Not Analyzed Not AP,plicable _ Not AQ.Plicable
2/6/1997 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 AQQlicable Not Applicable
5/5/1997 !l.OOE-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 1.50E-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
4/28/1998 9.00E-14 j1.25E-14 2.00E-14 S.OOE-15 '9,00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/31/1998 9.00E-14 '2.25E-14 2.00E-14 5,00E-15 -· ~.OOE-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not 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 Agplicable
12/28/1998 9.00E-14 2.25E-14 .2.00E-14 5.00E-15 9.00E-13 2.25E-13 6.00E-13 1.50E-13 Not Analyzed Not Applicable _ Not AQ.Qlicable
3/29/1999 9.00E-14 ;z.2sE-14 2.00E-14 5.00E-15 9.00E-13 2.2SE-13 6.00E-13 1.50E-13 Not Analyzed Not ApQlicable Not Applicable
7/3/1999 9.00E-14 £,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
9/27/1999 3.03E-15 9.00E-14 -2.25E-14 1.37E-15 2.00E-14 5.00E-15 8.72E-16 9.00E-13 2.25E-13 7.55E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Aeplicable
12/28/1999 5.0lE-15 9.00E-14 2 .. 25E-14 2.89E-15 2.00E-14 5.00E-15 l.31E-15 9.00E-13 2.25E-13 8.lOE-15 6,00E-13 1.50E-13 Not Analyzed Not APQlicable Not Applicable
3/30/2000 J.46E-16 9.00E-14 ' 2.25E-14 5.25E-16 2.00E-14 5.00E-15 ~.OOE-16 ~.OOE-13 2.25E-13 7.83E-15 6.00E-13 1.50E-13 ['Jot Analyzed No~icable • 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 l.50E-13 Not Analyzed Not Applicable Not Applicable
9/25/2000 3.75E-16 ~.OOE-14 2.25E-14 2.23E-16 2,00E-14 5.00E-15 1.91E-16 9.00E-13 2.25E-13 6.41E-15 6,00E-13 1.50E-13 Not Analyzed Not Applicable __ Np_t 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 ;z.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 6.15E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
7/2/2001 1.81E-16 9.00E-14 2.25E-14 1.66E-16 2.00E-14 5,00E-15 _1.00E-16 9.00E-13 ,2.25E-13 6.95E-15 6.00E-13 1.50E-13 Not Analyzed • ))lot Applicable Not Applicable
9/24/2001 3.08E-16 9.00E-14 :Z.25E-14 1.0lE-16 .2.00E-14 5.00E-15 P7E-16 9.00E-13 2.25E-13 8.59E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable _ Not Applicable
12/31/2001 3.31.E-16 9.00E-1.4 , l 25E-14 1.25E-16 2.00E-14 5.00E-15 _1.09_E-16 9.00E-13 J2.25E-13 3.14E-15 6.00E-13 1.50E-13 Not Analyzed 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 l 96E-16 9.00E-13 2.25E-13 8.61E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable J
7/1/2002 3.68E-16 9.00E-1!1 : 2.25E-14 4.41E-16 2.00E-14 5.00E-15 l .76E-16 9.00E-13 : 2.25E-13 8.20E-15 6.00E-13 1.50E-13 NotA~zed _ Not Applicable ·' ·Not Ap..P!k_able
9/30/2002 3.67E-16 9.00E-14 7.25E-14 5.60E-16 2.00E-14 5.00E-15 1.SOE-16 9.00E-13 2.25E-13 5.55E-15 6.00E-13 l.50E-13 Not Analyzed Not Applicable Not Ap-plicable
12/30/2002 !,OOE-16 9.00E-14 2.25E-_l.4 3.43E-16 2.00E-14 5,00E-15 1.67E-16 9.00E-13 l2.25E-13 1.35E-14 6,00E-13 1.50E-13 Not Analyzed Not Applicable Not Al!.P!icable
3/31/2003 l.98E-16 9.00E-14 2.25E-14 1.68E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 7.25E-13 7.77E-15 6.00E-13 1.50E-13 Not Analyzed /',lot Applicable Not Applicable
6/30/2003 1.18E-16 9.00E-14 I 2.25E-14 1.15E-16 2,00E-14 5.00E-15 1.00E-16 9.00E-13 '. 2.25E-13 5.92E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ApQlicable
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 1.50E-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 AQ.Plicable Not AQ.Plicable
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 ApQlicable Not Applicable
6/27/2004 1.00E-16 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 '2.25E-13 3,55E-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.38E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 '. 2.25E-13 1.22E-14 6.00E-13 1.50E-13 Not Analyzed_: Not ApP.licable Not ApJJlicable
12/27/2004 1.05E-16 9.00E-14 '2.25E-14 1.72E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 , 2.25E-13 1.52E-14 6.00E-13 1.50E-13 Not Analyzed · Not Applicable Not Applicable
3/28/2005 !,OOE-16 ~.OOE-14 :Z.25E-14 1.00E-16 2.00E-14 5.00E-15 1.00E-16 ~.OOE-13 :Z.25E-13 9.34E-15 6.00E-13 1.50E-13 ['Jot Analyzed Not Applicable Not Applicable
6/29/2005 1.28E-16 9.00E-14 2.25E,14 l.OlE-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 .2.25E-13 9.85E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicagle
9/26/2005 1.98E-16 9.00E-14 I 2.25E-14 5.98E-16 2.00E-14 5.00E-15 3.55E-16 9.00E-13 2.25E-13 1.71E-14 6.00E-13 1.SOE-13 'Not Analyzed )\lot Applicable J Not AP.plicable
1/3/2006 7.67E-16 -9.00E-14 . 2.25E-14 2.88E-16 2.00E-14 5.00E-15 3.60E-15 9.00E-13 '2.25E-13 4.85E-14 6.00E-13 1.SOE-13 )llot Analy_zed · Not APQlicable Not AQ.Plicable
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-6T232
Cloncentration Concentration €'.oncentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
AlARAGoal= 2.25E-14 uCi[ml ALARA Goal= SE-13 uCi/ml A!,ARAGoal = 2.25E-13 uCi/ml ALARA Goal= 1.SE-13 uCi/ml ALARAGoal = lE-15 uCi/ml
Pre 1994 MPC SE-12 uCi/ml -Pre 1994 MPC BE-14 uCi/ml Pre 1994 MPC 2·ec12 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 ~re 1994 Not Applicable
ALARAGOAL= ALARAGOAL= ALARA GOAL= ALARAGOAL=
Cone "EFC ·eFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA Cone EFC EFCA
4/3/2006 2.92E-16 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 1.llE-14 6.00E-13 1.50E-13 Not Analyzed Not AllPlicable )'Jot ARfllicable
7/3/2006 3.25E-16 9.00E-14 '2.25E-14 2.36E-16 2.00E-14 5.00E-15 l.OBE-16 9.00E-13 :2.25E-13 l.lOE-14 6.00E-13 1.50E-13 Not~zed ,Not AllPlicable _Not A0)1icable
10/2/2006 5.03E-16 9.00E-14 2.25E-14 1.49E-16 2.00E-14 5.00E-15 l.19E-16 9.00E-13 2.25E-13 2.BE-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
1/1/2007 8.31E-16 -9.00E-14 2.25E-14 2.49E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 2.25E-13 1.?0E-14 6.00E-13 1.SOE-13 Not An~lyzed 'Not Applicable Not Applicable
4/2/2007 5.36E-16 9.00E-14 2.25E-14 3.15E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 l.43E-14 6.00E-13 1.50E-13 Not Analyzed 'Not Applicable Not Applicable
7/2/2007 l.OSE-15 9.00E-14 _2.25E-14 2.lSE-16 2.00E-14 S.OOE-15 l.54E-16 9.00E-13 2.25E-13. 2.04E-14 6.00E-13 l.50E-13 Not Analyzed )'lot Applicable Not Applicable
9/30/2007 3.92E-16 9.00E-14 2.25E-14 l.02E-16 2.00E-14 5.00E-15 1.00E-16 9.00E-13 ·2.25E-13. 6.38E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
12/31/2007 2.92E-15 9.00E-14 2.25E-14 l.55E-15 2.00E-14 5.00E-15 '3.16E-16 9,00E-13 2.25E-13 9.19E-15 6.00E-13 1.50E-13 Not Analyzed )'Jot ~Jill.cable Not Ap..iili!;_able
3/31/2008 4.34E-16 -~ 9.00E-14 2.25E-14 3.51E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 5.99E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not A@licable
6/3102008 l.SSE-15 9.00E-14 2.25E-14 9.00E-16 2.00E-14 5.00E-15 4.04E-16 9.00E-13 2.25E-13 7.41E-15 6.00E-13 1.50E-13 ~ot Analyzed Not Applicable Not Applicable
9/30/2008 4.82E-15 "9.00E-14 ,2.25E-14_ 2.lOE-15 2.00E-14 5.00E-15 l.27E-15 -. 9.00E-13 2.25E-13 l.OOE-14 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not ~pplicable
12/31/2008 4.SOE-15 9.00E-14 2.25E-14 l.70E-15 2.00E-14 5.00E-15 l.25E-15 9.00E-13 2.25E-13 1.49E-14 6.00E-13 1.50E-13 Not Ana!'Lzed Not Agplicable Not AllPlicable
3/15/2009 2.77E-15 9.00E-14 2.25E-14 l.OlE-15 2.00E-14 5.00E-15 7.82E-16 9.00E-13 ;1.25E-13 6.46E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not [\QPlicable
6/15/2009 1.41E-16 9.00E-14 2.25E-14 2,67E-16 2.00E-14 S.OOE-15 1.SlE-16 9.00E-13 2.25E-13 5.76E-15 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not ~plicable
9/15/2009 4.87E-15 9.00E-14 _2.25E-14 4.32E-16 2.00E-14 5.00E-15 2.23E-16 ., 9.00E-13 2.25E-13 8.98E-15 6.00E-13 1.50E-13 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 1.15E-16 9.00E-13 2.25E-13 6.44E-15 6,00E-13 l,50E-13 Not Analyzed 'Not Applicable Not Applicable
3/31/2010 9.63E-15 -9.00Ecl4 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 Applicable Not Applicable
6/30/2010 ·3.62E-15 9.00E-14 2.25E-14 3.94E-16 2.00E-14 5.00E-15 4.89E-16 9.00E-13 ·2.25E-13 4.30E-15 6.00E-13 1.SOE-13 Not Analyzed Not A_p_plicable Not~licable
9/30/2010 5.42E-15 9.00E-14 _2.25E-14 l.08E-15 2.00E-14 5.00E-15 p,68E-16 ' 9.00E-13 J.25E-13. 3.98E-15 6,00E-13 1.50E-13 Not Analyzed )'Jot Applicable Not Applicable
12/31/2010 l.24E-14 ~ 9.00E-14 2.25E-14 l.21E-15 2.00E-14 5.00E-15 l.OOE-15 9.00E-13 2.25E-13-l.53E-14 6.00E-13 1.SOE-13 Not Analyzed 'Not Applicable Not Applicable
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 l.29E-14 6.00E-13 l.50E-13 Not Analyzed _Not A0Jlicable_ 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 02.25E-13 7.97E-15 6.00E-13 l.SOE-13 Not Analyzed Not Apglicable" Not Applicable
10/3/2011 2.0SE-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 1.50E-13 Not Analyzed Not Applicable Not Applicable
1/3/2012 3.14E-15 9.00E-14 2.251;-14 1.09E-15 2.00E-14 5.00E-15 7.65E-16 ' 9.00E-13 2.25E-13 1.89E-14 6.00E-13 1.SOE-13 Not Ana!'Lzed Not Applicable Not ~_plicable
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.SOE-13 /'lot 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.SOE-13 Not Analyzed .~plicable Not Applicable
10/1/2012 6.63E-15 9.00E-14 ·2.2SE-14 l.31E-15 2.00E-14 5.00E-15 l.22E-15 9.00E-13 2.25E-13 1.34E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
12/31/2012 3.83E-15 9.00E-14 2.25E-14 1.18E-15 2.00E-14 5.00E-15 !l.30E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not AQPlicable
3/25/2013 4.52E-15 .. 9 .. 00E-14 2.25E-14 7.93E-16 2.00E-14 5.00E-15 B,.91E-16 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not ~plicable
7/2/2013 5.91E-15 9.00E-14 2.25E-14 6.74E-16 2.00E-14 5.00E-15 7.BSE-16 9.00E-13 2.25E-13J 5.18E-15 6.00E-13 1.50E-13 Not Analyzed Not Applicable Not Applicable
9/30/2013 2.68E-15 : 9.00E-14 2.25E-14_ 3.97E-16 2.00E-14 5.00E-15 1.04E-16 9.00E-13 02.25E-13 6.13E-15 6.00E-13 l,SOE-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 S.OOE-15 1.0SE-16 9.00E-13 2.25E-13 2,67E-14 6.00E-13 l.50E-13 /'lot Analyzed Not AllPlicable Not Applicable
3/31/2014 8.92E-15 9.00E-14 2.25E-14 7.68E-16 2.00E-14 5.00E-15 l.50E-15 9.00E-13 2.25E-13 l.61E-14 6.00E-13 1.50E-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 S.OOE-15 6.72E-16 9.00E-13 2.25E-13 1.20E-14 6.00E-13 1.SOE-13 Not Analyzed Not Applicable Not Applicable
9/30/2014 l.20E-14 9.00E-14 2.25E-14 5.54E-16 2.00E-14 S.OOE-15 6'.lBE-16 '. 9.00E-13 2.25E-13 1.38E-14 6.00E-13 1.SOE-13 1.00E-16 4.00E-15 l.OOE-15
12/29/2014 5.00E-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 2.30E-14 6.00E-13 1.SOE-13 8.00E-18 4.00E-15 l.OOE-15
3/30/2015 2.SOE-14 -9.00E-14 ?-25E-14 2,00E-16 2.00E-14 5,00E-15 4,00E-16 ' 9.00E-13 2.25E-13 2.SOE-14 6.00E-13 1.SOE-13 ·1.00E-18 4.00E-15 l.OOE-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 l.70E-14 6.00E-13 1.50E-13 l.OOE-17 4.00E-15 LOOE-15
9/28/2015 l.OOE-14 9.00E-14 2.25E-14 2,00E-16 2.00E-14 5,00E-15 3.00E-16 9.00E-13 ,2,25E-13 l.lOE-14 6,00E-13 l.50E-13 2.00E-18 /I.OOE-15 l.OOE-15
12/28/2015 8.40E-16 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 S.OOE-15 1.00E-16 ~ 9.00E-13 2.25E-13, 2.00E-14 6.00E-13 1.50E-13 6.00E-18 i!.OOE-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 1.50E-13 1.00E-17 ~OOE-15 _l.OOE-15
6/27/2016 l.20E-14 9.00E-14 2.25E-14 l.OOE-16 2.00E-14 5.00E-15 6.00E-15 9.00E-13 :2.2SE-13 2.lOE-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 l.OOE-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 1.50E-13 l.20E-17 4.00E-15 1.00E-15
12/27/2016 8.90E-15 '9.00E-14 _2.25E-14 3.30E-16 2.00E-14 5.00E-15 4.SOE-16 ' 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 l.50E-13 9,50E-18 4.oo~:1s 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 ·2.2SE-13 1.50E-14 6.00E-13 1.SOE-13 3.00E-18 <I.OOE-15 l.OOE-15
6/26/2017 2.30E-15 9.00E-14 2.25E-14 7.00E-17 2.00E-14 S.OOE-15 2.00E-16 9.00E-13 2.25E-13' 1.lOE-14 6.00E-13 l.50E-13 1:l.OOE-18 /I.OOE-15 l.OOE-15
9/25/2017 3.SOE-15 9.00E-14 2.2SE-14 2.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 l.90E-14 6.00E-13 1.SOE-13 1.00E-17 ti.OOE-15 1.00E-15
12/26/2017 l.40E-14 9.00E-14 2.25E-14 4.00E-16 2.00E-14 5.00E-15 l.OOE-17 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 l.OOE-17 f,t.OOE-15 l.OOE-15
3/26/2018 1.20E-15 9.00E-14 2.25E-14 l.lOE-16 2.00E-14 5.00E-15 l.lOE-16 -9.00E-13 ,2.25E-13-l.50E-14 6.00E-13 l.SOE-13 9.00E-18 )1.00E-15 1.00E-15 -
Date Effluent SE-1i1uafm1 BHVi6U Effluent 2E-14 uCi/ml BHV-6T230 Effluent, 9E-13 uGi{mt BHV-6R Effluent 6E-13 uCi/ml BHV-6PB Effluent 4t-1SuP/ml ~'61"23Z
Concen_tratio~ Concentration ~n'cen~'tlon Concentration eo~Jiir,,!fon
limit~ Limit= Umit= Limit= Umit=
ALA~~I:. 2,251:-14 uOJinl ALARAGoal = SE-13 uCi/ml A~RA Go;ala= D5E-l3 ud/ml ALARAGoal= 1.SE-13 uCi/ml ')LARA QM= al1,,2$u!ii{rijl
1!n1 1994 1',1PC SH2UCi]mf Pre 1994 MPC BE-14 uCi/ml Pre~MPC:: -2&;U uCiJml Pre 1994 MPC 4E-12 uCi/ml erel.994 MPC Not Applicable.
limit" Limit= Umlt-= Limit= Unilt=
Pre"1994 l~~,,u UCl/ml ~1994 si;.a u<;;Jin1 Pre 1994 lE-12 uCi/ml Pr~~. Not AJP}!,¢lble
,l'~RA. GOAl" ~OOAI.= ALARAGOAL= A~RAGOAL=
Cl<lnp EEC i;~A Cone EFC EFCA Eonc EE€ EFC:A• Cone EFC EFCA Cone Ef:C ~Ft.A•
6/25/2018 3,<itiE-15 !!:W'Ed4 ~~t-14 9.70E-17 2.00E-14 5.00E-15 1.i;)eg,16 fef!lt:13 ~~S&l3 1.20E-14 6.00E-13 l.SOE-13 1/llOE-l-7 4,0QE-1S· l.QOE-15
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5/18/1988
2/13/1989
11/13/1989
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5/13/1991
2/10/1992
11/9/1992
8/10/1993
5/9/1994
2/7/1995
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4/28/1998
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9/27/1999
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6/30/2003
3/29/2004
12/27/2004
9/26/2005
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4/2/2007
12/31/2007
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12/31/2010
10/3/2011
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4/28/1998
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3/31/2010
12/31/2010
10/3/2011
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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 liHV-7R Effluent 6E-13 uCi/ml BHV-7PB Effluent 4e-15 uCi/ml BHV-7T232
Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= limit= Limit= -
ALARAGoal = 2.25E-14 uCi/ml ALARA Goal= SE-13 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/inl 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=
~ -
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 1.00E-15 --
3/30/2015 6.00E-15 9.00E-14 2.25E-14 8.00E-17 2.00E-14 5.00E-15 i.OOE-16 9.00E-13 2.25E-13 2.SOE-14 6.00E-13 1.50E-13 7.00E-18 " 4.00E-15 ·1.ooE-15
~
6/29/2015 1.40E-15 9.00E-14 .2.25E-14 4.00E-16 2.00E-14 5.00E-15 1.30E-15 9.00E-13 2.25E-13 1.70E-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 1.00E-15
9/28/2015 4.20E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5,00E-15 4.00E-16 9.00E-13 ;1.25E-13 1.00E-14 6.00E-13 1.50E-13 6,00E-18 4.00E-15 -1.00E-15
~
12/28/2015 3.60E-16 9.00E-14 2.25E-14 7.00E-17 2.00E-14 5.00E-15 2.00E-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 I 1.00E-15 ··' -
3/28/2016 8.00E-16 '9.00E-14 J l.25E-14 1.00E-16 2.00E-14 5,00E-15 1.00E-15 9.00E-13 7.25E-13 1.70E-14 6.00E-13 1.50E-13 5.00E-18 4.00E-15 1.00E-15 -
6/27/2016 1.SOE-15 9.00E-14 2.25E-14 9.00E-17 2.00E-14 5,00E-15 9.00E-16 9.00E-13 2.25E-13 1.SOE-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15
9/27/2016 2.60E-15 9.00E-14 2.25E-14 1.70E-16 2.00E-14 5,00E-15 4.lOE-16 9.00E-13 2.25E-13 2.80E-15 6.00E-13 1.50E-13 5.SOE-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.SOE-16 9.00E-13 ;2.25E-13 1.SOE-14 6.00E-13 1.50E-13 4.80E-18 4.00E-15 1.00E-15
3/27/2017 3.30E-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 l.40E-15 9.00E-13 i!.25E-13 1.40E-14 6.00E-13 1.50E-13 3.00E-18 4.00E-15 1.00E-15
6/26/2017 3.40E-15 9,00E-14 l.25E-14 4.00E-16 2.00E-14 5.00E-15 1.SOE-15 9.00E-13 2.25E-13 1.40E-14 6.00E-13 1.50E-13 2.00E-17 4.00E-15 1.00E-15 -
9/25/2017 l.20E-15 9.00E-14 ., 2.25E-14 6.00E-17 2-00E-14 5.00E-15 l.OOE-16 9.00E-13 . 2.25E-13 1.90E-14 6.00E-13 1.50E-13 4.00E-18 4.00E-15 1.00E-15
12/26/2017 4.60E-15 9.00E-14 2.25E-14 2.00E-16 2.00E-14 5.00E-15 l.OOE-16 9.00E-13 2.25E-13 2.lOE-14 6.00E-13 1.50E-13 1.00E-17 4.00E-15 "t.OOE-15 -
3/26/2018 4.lOE-16 9.00E-14 2.25E-14 1.20E-16 2.00E-14 5.00E-15 2.60E-16 9.00E-13 "2.25E-13 1.80E-14 6.00E-13 1.50E-13 8.70E-18 4.00E-15 1.00E-15 ~
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TAB8
BHV-8 AIR SAMPLING GRAPHS AND DATA TABLE
Date Effluent 9E·14 uCi/ml BHV·SU Effluent 2E-14 uCi/ml BHV-8T230 Effluent 9E-13 uCl/ml BHV·SR Effluent 6E-13 uCi/ml BHV-8PB Effluent 4e·l5 uCi/ml BHV-8T232
,Concentration Concentration Concentration Concentration Concentration
Limit= Limit= Limit= Limit= Limit=
AJARA. Goal = t-~N~~/ml AlARAGoal = SE-13 uCi/ml ALAM· Goal .. 2.tse-13 uQ/mt ALARAGoal= 1.SE-13 uCl/ml A~~Goal=-°1E01S uCi/ml
Pre l994MPC SE-12 uCi/ml Pre 1994 MPC SE-14 uCi/ml Pre 1994MPC 2E-12 uCi/ml Pre 1994 MPC 4E-12 uCi/ml Pre 1994MPC Nol Applicable
Limit= 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 Not Applicatile
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 2.2SE·l3, 9.90E-15 6.00E-13 1.SOE-13 9.00E-18 4.00E-15 1.00E-15 .
3/30/2015 1.80E-15 9.00E-14 2.25E-14 4.00E-17 2.00E-14 5.00E-15 4.00E-17 9.00E-13 2.25E-13 9.40E-15 6,00E-13 1.50E-13 1.00E-16 4.00.E-15 1.00E-15
6/29/2015 5.00E-16 !:J.OOE-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 1.50E-13 7.00E-18 4;0!)MS, 1.00E-15
9/28/2015 1.80E-15 9.00E-14 2.25E-14 4.00E-17 2.00E-14 S.OOE-15 4.00E-16 ~.OOE-13 2.25E-13 8.00E-15 6.00E-13 1.50E·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 S.OOE-15 9.00E-16 9.00E-13 2.25E-13 2.00E-14 6.00E-13 1.SOE-13 4.00E-18 4.00E-15 1.00E-15
3/28/2016 2.00E-16 9.00E-14 2.25E-14 2.00E-17 2.00E-14 S.OOE-15 3.00E-16 9.00E-13 2.25E-13 1.60E-14 6.00E-13 l.SOE-13 2.00E-18 4.00E-15 l.OOE-15
' 6/27/2016 1.lOE-15 9.00E-14 2.25E-14 1.00E-16 2.00E-14 5.00E-15 1.90E-15 9.00E-13 2.25E-13 1.lOE-14 6.00E-13 l.SOE-13 2.00E-18 4.00E-15 l.OOE-15
9/27/2016 1.20E-15 9.00E-14 2.25E-14 8.40E-17 2.00E-14 5.00E-15 3.30E-16 9.00E-13 2.25E-13 7.60E-15 6.00E-13 l 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 S.OOE-15 8.SOE-17 9.00E-13 2.25E-13 l.40E-14 6.00E-13 l.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 l.30E-15 ,9.00E-13 2.25E-13 8.70E-15 6,00E-13 l.SOE-13 1.00E-18 4.00E-15 1.00E-15
6/26/2017 1.00E-16 9.00E-14 2 25E-14 5.00E-17 2.00E-14 5.00E-15 4.00E-16 9.00E-13 2.25E-13 7.80E-15 6.00E-13 1.SOE-13 5.00E-19 4.00E-15 1.00E-15
9/25/2017 6.00E-16 9.00E-14 2.2SE·14 B.OOE-17 2.00E-14 S.OOE-15 1.00E-16 9.00E-13 2.25E-13 l.20E-14 6.00E-13 l.SOE-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 1.50E-13 7.00E-18 4.00E-15 l.OOE-15
3/26/2018 2.30E-16 9.00E-14 2.25E-14 5.80E-17 2.00E-14 S.OOE-15 8.30E-17 9.00E-13 2.25E-13 l.30E-14 6.00E-13 1.50E-13 S.lOE-18 4.00E-15 1.00E-15
6/25/2018 9.40E-16 9.00E-14 2.25E·14 1.20E-16 2.00E-14 5.00E-15 3.00E-16 9.00E-13 2.25E-13 8.80E-15 6.00E-13 1.50E-13 8.SOE-18 4.00E-15 1.00E-15
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ATTACHMENT C
BHV AIR SAMPLING LABORATORY RESULTS AND QA/QC
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: 1st Quarter Air 2018
Lab ID: C 18030835-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium 2.7E-10 mg/L
Uranium, Activity 1.9E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 21 O 1.5E-14 uCi/mL
Lead 210 precision (±) 4.3E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 9.2E-17 uCi/mL
Radium 226 precision (±) 2.4E-17 uCi/mL
Radium 226 MDC 1.1 E-17 uCi/mL
Thorium 230 5.3E-17 uCi/mL
Thorium 230 precision (±) 1.0E-17 uCi/mL
Thorium 230 MDC 8.5E-18 uCi/mL
Thorium 232 5.3E-18 uCi/mL
Thorium 232 precision (±) 3.7E-18 uCi/mL
Thorium 232 MDC 5.4E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1780 pCi/Filter
Lead 210 precision (±) 532 pCi/Filter
Lead 210 MDC 40.0 pCi/Filter
Radium 226 11 .3 pCi/Filter
Radium 226 precision (±) 2.9 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 6.5 pCi/Filter
Thorium 230 precision (±) 1.2 pCi/Filter
Thorium 230 MDC 1.0 pCi/Filter
Thorium 232 0.65 pCi/Filter
Thorium 232 precision (±) 0.46 pCi/Filter
Thorium 232 MDC 0.66 pCi/Filter
Uranium, Activity 22.8 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.4E+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 1.8E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 9.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
u
u
MCU
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 11 :34 / eli-h
SW6020 04/19/18 11 :34 / eli-h
E909.0 04/09/18 19:07 / meh
E909.0 04/09/18 19:07 I meh
E909.0 04/09/18 19:07 I meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 I arh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 I sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 3 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-001
Client Sample ID: BHV-1
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 2.1 E-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.
122995700
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date I By
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 40
El'.E RGY .. ' ,\ '
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BHV-1
REPORT DATE: April 30, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl 8030835-001 na1u l.9E-16
I st Quarter Air 2018 23°'fh SE-17
Air Volume in mLs 226Ra 9E-17
J.23E+ll 210Pb l.SE-14
232Th SE-18
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
lE-17
2E-17
4E-15
4E-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
8E-18
IE-17
3E-16
SE-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
lE-16 9E-14 2.lE-01
IE-16 3E-14 2E-Ol
IE-16 9E-13 lE-02
2E-15 6E-13 2.4E+OO
NIA 6E-15 9E-02
Page 5 of 40
EI\ERGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-001
Client Sample ID: BHV-1
Analyses Result Units
METALS, IN AIR
Uranium 1.2E-09 mg/L
Uranium, Activity 8.0E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision(±) 3.6E-15 uCi/mL
Lead 210 MDC 3.2E-16 uCi/mL
Radium 226 2.5E-16 uCi/mL
Radium 226 precision (±) 5.8E-17 uCi/mL
Radium 226 MDC 1.9E-17 uCi/mL
Thorium 230 1.2E-16 uCi/mL
Thorium 230 precision (±) 2.3E-17 uCi/mL
Thorium 230 MDC 8.8E-18 uCi/mL
Thorium 232 9.3E-18 uCi/mL
Thorium 232 precision (±) 1.8E-18 uCi/mL
Thorium 232 MDC 8.6E-18 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 1460 pCi/Filter
Lead 21 O precision (±) 436 pCi/Filter
Lead 210 MDC 38.8 pCi/Filter
Radium 226 30.2 pCi/Filter
Radium 226 precision (±) 7.1 pCi/Filter
Radium 226 MDC 2.3 pCi/Filter
Thorium 230 14.9 pCi/Filter
Thorium 230 precision (±) 2.8 pCi/Filter
Thorium 230 MDC 1.1 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.22 pCi/Filter
Thorium 232 MDC 1.0 pCi/Filter
Uranium, Activity 96.3 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 3.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.6E-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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date I By
SW6020 07/12/18 15:04 / eli-h
SW6020 07/12/18 15:04 / eli-h
E909.0 07/11/1818:50 I meh
E909.0 07/11/18 18:50 I meh
E909.0 07/11 /18 18:50 I meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 I arh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13: 38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 3 of 40
EN:RGY Trust our People. Trust our Data.
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Billin11s, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-001
Client Sample ID: BHV-1
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 8.9E-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.
120733500
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
FIELD 06/25/18 00:00 I ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 4 of 40
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPL~ ID: BHV-1 -..
REPORT DATE: July 24, 2018
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
C 18060968-001 na<u 8E-16 NIA
2nd Quarter Air 2018 230Th IE-16 2E-17
Air Volume in mLs 226Ra 3E-16 6E-17
l.21E+I I 2'°Pb l.2E-14 4E-15
232Th 9E-18 2E-18
+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
MDCµCi/mL
NIA
9E-18
2E-17
3E-16
9E-18
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
lE-16 9E-14 9E-OI
lE-16 3E-14 4E-01
lE-16 9E-13 3E-02
2E-15 6E-13 2.0E+OO
NIA 6E-15 2E-01
Page 5 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-002
Client Sample ID: BHV-2
Analyses Result Units
METALS, IN AIR
Uranium 9.8E-11 mg/L
Uranium, Activity 6.7E-17 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.6E-15 uCi/mL
Lead 210 MDC 3.1 E-16 uCi/mL
Radium 226 4.0E-17 uCi/mL
Radium 226 precision (±) 1.4E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.4E-17 uCi/mL
Thorium 230 precision (±) 2.7E-18 uCi/mL
Thorium 230 MDC 4.9E-18 uCi/mL
Thorium 232 5.3E-18 uCi/mL
Thorium 232 precision (±) 2.8E-18 uCi/mL
Thorium 232 MDC 3.8E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1490 pCi/Filter
Lead 210 precision(±) 445 pCi/Filter
Lead 210 MDC 37.5 pCi/Filter
Radium 226 4.9 pCi/Filter
Radium 226 precision (±) 1.7 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 1.8 pCi/Filter
Thorium 230 precision (±) 0.34 pCi/Filter
Thorium 230 MDC 0.60 pCi/Filter
Thorium 232 0.65 pCi/Filter
Thorium 232 precision (±) 0.34 pCi/Filter
Thorium 232 MDC 0.47 pCi/Filter
Uranium, Activity 8.2 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 4.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 5.0E-02 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 9.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCU
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 11 :38 / eli-h
SW6020 04/19/18 11 :38 / eli-h
E909.0 04/09/18 19:46 I meh
E909.0 04/09/18 19:46 I meh
E909.0 04/09/18 19:46 I meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 40
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 7.0E-02
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.
122850000
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 40
El'\ERGY
"· , .
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-HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BHV-2
REPORT DATE: April 30, 2018
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
C 18030835-002 natu 7E-17 NIA
1st Quarter Air 2018 23°Th IE-17 3E-18
Air Volume in mLs 226Ra 4E-17 IE-17
l.23E+II 210Pb 1.2E-14 4E-15
232Th 5E-18 3E-18
+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
MDCµCi/mL
NIA
5E-18
IE-17
3E-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.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 7E-02
IE-16 3E-14 5E-02
IE-16 9E-13 4E-03
2E-15 6E-13 2.0E+OO
NIA 6E-15 9E-02
Page 8 of40
EN:RGY Trust our People. Trust our Data.
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Billings, MT BOO. 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: 2nd Quarter Air 2018
Lab ID: C 18060968-002
Client Sample ID: BHV-2
Analyses Result Units
METALS, IN AIR
Uranium 5.5E-10 mg/L
Uranium, Activity 3.8E-16 uCi/mL
RADIONUCLIDE$ -IN AIR
Lead 210 1.3E-14 uCi/mL
Lead 210 precision (±) 3.8E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 1.2E-16 uCi/mL
Radium 226 precision (±) 3.1E-17 uCi/mL
Radium 226 MDC 1.9E-17 uCi/mL
Thorium 230 4.6E-17 uCi/mL
Thorium 230 precision (±) 8.8E-18 uCi/mL
Thorium 230 MDC 5.2E-18 uCi/mL
Thorium 232 1.5E-17 uCi/mL
Thorium 232 precision (±) 2.9E-18 uCi/mL
Thorium 232 MDC 5.3E-18 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 1470 pCi/Filter
Lead 210 precision(±) 440 pCi/Filter
Lead 210 MDC 39.2 pCi/Filter
Radium 226 14.2 pCi/Filter
Radium 226 precision (±) 3.6 pCi/Filter
Radium 226 MDC 2.2 pCi/Filter
Thorium 230 5.4 pCi/Filter
Thorium 230 precision (±) 1.0 pCi/Filter
Thorium 230 MDC 0.61 pCi/Filter
Thorium 232 1.8 pCi/Filter
Thorium 232 precision (±) 0.33 pCi/Filter
Thorium 232 MDC 0.62 pCi/Filter
Uranium, Activity 44.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.1E+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 1.5E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.5E-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
MCL/
RL QCL
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date I By
SW6020 07 /12/18 15:22 I eli-h
SW6020 07/12/18 15:22 I eli-h
E909.0 07/11/18 19:34 / meh
E909.0 07/11 /18 19:34 / meh
E909.0 07/11/18 19:34 / meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E908.0 07/13/18 08:20 / cnh
E908.0 07 /13/18 08:20 / cnh
E908.0 07 /13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07 /13/18 08:20 / cnh
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 6 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 811.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-002
Client Sample ID: BHV-2
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
4.2E-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.
117283400 L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
07 /20/18 14:42 I dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
06/25/18 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 7 of 40
E~RGY
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: BHV-2
REPORT DATE: July 24, 2018
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
C 18060968-002 natu 4E-16 NIA
2nd Quarter Air 2018 230Th 5E-17 9E-18
Air Volume in mLs 226Ra IE-16 3E-17
1.17E+l 1 210Pb 1.3E-14 4E-15
232Th lE-17 3E-18
+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
MDCµCi/mL
NIA
5E-18
2E-17
3E-16
5E-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 4E-OI
IE-16 3E-14 2E-OI
IE-16 9E-13 IE-02
2E-15 6E-13 2.IE+OO
NIA 6E-15 2E-OI
Page 8 of40
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: 1st Quarter Air 2018
Lab ID: C 18030835-003
Client Sample ID: BHV-4
Analyses Result Units
METALS, IN AIR
Uranium 1.0E-09 mg/L
Uranium, Activity 6.8E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.4E-14 uCi/mL
Lead 210 precision(±) 4.2E-15 uCi/mL
Lead 210 MDC 3.2E-16 uCi/mL
Radium 226 5.7E-17 uCi/mL
Radium 226 precision(±) 1.8E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.2E-16 uCi/mL
Thorium 230 precision (±) 2.3E-17 uCi/mL
Thorium 230 MDC 6.0E-18 uCi/mL
Thorium 232 4.0E-18 uCi/mL
Thorium 232 precision (±) 3.2E-18 uCi/mL
Thorium 232 MDC 4.9E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1720 pCi/Filter
Lead 210 precision (±) 514 pCi/Filter
Lead 210 MDC 39.9 pCi/Filter
Radium 226 7.1 pCi/Filter
Radium 226 precision (±) 2.2 pCi/Filter
Radium 226 MDC 1.4 pCi/Filter
Thorium 230 15.1 pCi/Filter
Thorium 230 precision (±) 2.9 pCi/Filter
Thorium 230 MDC 0.74 pCi/Filter
Thorium 232 0.50 pCi/Filter
Thorium 232 precision (±) 0.39 pCi/Filter
Thorium 232 MDC 0.60 pCi/Filter
Uranium, Activity 83.5 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.3E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 6.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 7.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
u
u
MCL/
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 11 :40 / eli-h
SW6020 04/19/18 11 :40 / eli-h
E909.0 04/09/18 19:58 / meh
E909.0 04/09/18 19:58 / meh
E909.0 04/09/18 19:58 / meh
E903.0 04/10/18 08:34 I arh
E903.0 04/10/18 08:34 I arh
E903.0 04/10/18 08:34 / arh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/iB 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 9 of 40
E~RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 888.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD NIA
Uranium Natural, % of EFF 7.5E-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.
122965000
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 40
EI\ERGY
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HIGH VOLUME AIR SAMPLING REPORl'
CLIENT: Energy ,Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BHV-4
REPORT DA:TE: April 30, 2018 I"
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
CJ 8030835-003 ""U 6.8E-16 NIA
I st Quarter Air 2018 230Th IE-16 2E-17
Air Volume in mLs 220Ra 6E-17 2E-17
1.23E+l 1 210Pb l.4E-14 4E-15
232Th 4E-18 3E-18
+LLD's are from NRC Reg. Guide 4.14
*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
6E-18
lE-17
3E-16
5E-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.* % Erlluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 7.5E-Ol
IE-16 3E-14 4E-01
IE-16 9E-13 6E-03
2E-15 6E-13 2.3E+OO
NIA 6E-15 7E-02
Page 11 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-003
Client Sample ID: BHV-4
Analyses Result Units
METALS, IN AIR
Uranium 2.3E-09 mg/L
Uranium, Activity 1.5E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.1E-14 uCi/mL
Lead 210 precision (±) 3.3E-15 uCi/mL
Lead 210 MDC 3.1E-16 uCi/mL
Radium 226 3.7E-17 uCi/mL
Radium 226 precision (±) 1.5E-17 uCi/mL
Radium 226 MDC 1.8E-17 uCi/mL
Thorium 230 8.2E-17 uCi/mL
Thorium 230 precision (±) 1.6E-17 uCi/mL
Thorium 230 MDC 6.8E-18 uCi/mL
Thorium 232 1.2E-17 uCi/mL
Thorium 232 precision (±) 2.4E-18 uCi/mL
Thorium 232 MDC 7.6E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1310 pCi/Filter
Lead 21 o precision (±) 393 pCi/Filter
Lead 210 MDC 37.2 pCi/Filter
Radium 226 4.4 pCi/Filter
Radium 226 precision (±) 1.8 pCi/Filter
Radium 226 MDC 2.1 pCi/Filter
Thorium 230 9.8 pCi/Filter
Thorium 230 precision (±) 1.9 pCi/Filter
Thorium 230 MDC 0.81 pCi/Filter
Thorium 232 1.5 pCi/Filter
Thorium 232 precision (±) 0.28 pCi/Filter
Thorium 232 MDC 0.91 pCi/Filter
Uranium, Activity 183 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.8E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 4.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 2.7E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27 /18
Matrix: Filter
Method Analysis Date / By
SW6020 07 /12/18 15:24 I eli-h
SW6020 07 /12/18 15:24 / eli-h
E909.0 07/11/18 19:46 / meh
E909.0 07/11/18 19:46 / meh
E909.0 07/11/18 19:46 / meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 I cnh
E908.0 07/17/18 08:46 / cnh
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/1813:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/1813:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/1813:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 9 of 40
E"-ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-003
Client Sample ID: BHV-4
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD NIA
Uranium Natural, % of EFF 1.7E+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.
119694900
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
FIELD 06/25/18 00:00 I•••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 10 of 40
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) nc
PROJECT: 2nd Quarter Air 2018
• I SAMPLE ID: BHV -4
REPORT DATE: July 24, 2018 •
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
CI 8060968-003 natu I.SE-15
2nd Quarter Air 2018 23°"fh 8E-17
Air Volume in mLs 226Ra 4E-17
1.20E+ll 210Pb l.lE-14
232Th lE-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
2E-17
2E-17
3E-15
2E-18
*Effluent Concentration from the NEW 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
7E-18
2E-17
3E-16
8E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.888.7175 • Helena, MT 877.472.0711
L.L.D.+
µCi/mL
lE-16
lE-16
IE-16
2E-15
NIA
. "'
I -
II
II
1,I
Effluent Cone.*
µCi/mL
9E-14
3E-14
9E-13
6E-13
6E-15
% Effluent
Concentration
l .7E+OO
3E-OI
4E-03
l.8E+OO
2E-01
Page 11 of 40
EN:RGY Trust our People. Trust our Data.
www.energylab.co,n
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: 1st Quarter Air 2018
Lab ID: C 18030835-004
Client Sample ID: BHV-5
Analyses Result Units
METALS, IN AIR
Uranium 1.1 E-09 mg/L
Uranium, Activity 7.1 E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 21 O 1.4E-14 uCi/mL
Lead 210 precision (±) 4.1 E-15 uCi/mL
Lead 210 MDC 3.2E-16 uCi/mL
Radium 226 1.5E-16 uCi/mL
Radium 226 precision (±) 3.6E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.7E-16 uCi/mL
Thorium 230 precision (±) 3.1E-17 uCi/mL
Thorium 230 MDC 2.3E-17 uCi/mL
Thorium 232 -8.1E-19 uCi/mL
Thorium 232 precision (±) 1.1E-17 uCi/mL
Thorium 232 MDC 2.2E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1650 pCi/Filter
Lead 210 precision(±) 493 pCi/Filter
Lead 210 MDC 39.0 pCi/Filter
Radium 226 18.7 pCi/Filter
Radium 226 precision (±) 4.4 pCi/Filter
Radium 226 MDC 1.4 pCi/Filter
Thorium 230 20.1 pCi/Filter
Thorium 230 precision (±) 3.8 pCi/Filter
Thorium 230 MDC 2.7 pCi/Filter
Thorium 232 -0.098 pCi/Filter
Thorium 232 precision (±) 1.4 pCi/Filter
Thorium 232 MDC 2.7 pCi/Filter
Uranium, Activity 86.4 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.3E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 2.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 5.5E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF -1 .0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
u
u
MCU
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 11 :57 / eli-h
SW6020 04/19/18 11 :57 / eli-h
E909.0 04/09/18 20:09 I meh
E909.0 04/09/18 20:09 I meh
E909.0 04/09/18 20:09 I meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 I arh
E903.0 04/10/18 08:34 I arh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 12 of40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.888.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 7.9E-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.
121542800
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date I By
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 13 of40
E~RGY
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.. ,..
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i HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc , I I .... ..
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
I I I .J
~I I~• ~ ~ .. -~ ............ ~ ~~ ..... , --... I
,~ ·1-L: PROJECT: 1st Quarter Air 2018
. . SAMPLE ID: BHV-5 I i.,: • I _{'I) -•
• -.· 1
ft:..
)1
... ,. J Ill -J.. ~j--r r' I J I • -. ~ ,.. 'ii," ~
~.. • 'T I l I
REPORT DATE: April 30, 2018 -..
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
C 18030835-004 natu 7. IE-16 NIA
1st Quarter Air 2018 23°'fh 2E-16 3E-17
Air Volume in mLs 226Ra 2E-16 4E-17
l.22E+l 1 210Pb 1.4E-14 4E-15
232Tb -8E-19 IE-17
+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
r•" 4 Ill
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 7.9E-Ol
2E-17 IE-16 3E-14 6E-01
IE-17 IE-16 9E-13 2E-02
3E-16 2E-15 6E-13 2.3E+OO
2E-17 NIA 6E-15 -IE-02
Page 14 of40
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: 2nd Quarter Air 2018
Lab ID: C 18060968-004
Client Sample ID: BHV-5
Analyses Result Units
METALS, IN AIR
Uranium 3.9E-09 mg/L
Uranium, Activity 2.6E-15 uCi/mL
RADIONUCLIDE$ -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.7E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 5.9E-16 uCi/mL
Radium 226 precision (±) 1.2E-16 uCi/mL
Radium 226 MDC 1.9E-17 uCi/mL
Thorium 230 2.4E-16 uCi/mL
Thorium 230 precision (±) 4.6E-17 uCi/mL
Thorium 230 MDC 1.3E-17 uCi/mL
Thorium 232 9.4E-18 uCi/mL
Thorium 232 precision (±) 1.8E-18 uCi/mL
Thorium 232 MDC 1.3E-17 uCi/mL
RADIONUCLIDE$ -IN AIR -PER FILTER
Lead 210 1500 pCi/Filter
Lead 210 precision (±) 447 pCi/Filter
Lead 210 MDC 39.4 pCi/Filter
Radium 226 70.8 pCi/Filter
Radium 226 precision (±) 14.4 pCi/Filter
Radium 226 MDC 2.3 pCi/Filter
Thorium 230 29.4 pCi/Filter
Thorium 230 precision (±) 5.6 pCi/Filter
Thorium 230 MDC 1.5 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.22 pCi/Filter
Thorium 232 MDC 1.5 pCi/Filter
Uranium, Activity 318 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2. 1 E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 7.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 8.2E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.6E-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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date / By
SW6020 07 /12/18 15:26 / eli-h
SW6020 07 /12/18 15:26 I eli-h
E909.0 07/11/18 19:58 / meh
E909.0 07/11/18 19:58 / meh
E909.0 07/11/18 19:58 / meh
E903.0 07/17/18 10:59 I arh
E903.0 07/17/18 10:59 I arh
E903.0 07/17/18 10:59 / arh
E908.0 07/17/18 08:46 I cnh
E908.0 07/17/18 08:46 I cnh
E908.0 07/17/18 08:46 I cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 12 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.888. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-004
Client Sample ID: BHV-5
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 2.9E+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.
120283500
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
FIELD 06/25/18 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 13 of 40
El'\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
HIGH VOLUME AIR SAMPLING REPORT
CLIBNT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: BHV-5
REPORT1>ATE: July 24, 2018
Quarter/Date Sampled Radionuclide Air Volume
C 18060968-004 natu
2nd Quarter Air 2018 230Th
Air Volume in mLs 226Ra
1.20E+l 1 zwPb
232Th
+LLD's are from NRC Reg. Guide 4.14
-JI I
Concentration
µCi/mL
2.6E-15
2E-16
6E-16
1.2E-14
9E-18
Counting
Precision
µCi/mL
NIA
SE-17
IE-16
4E-15
2E-18
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
I
~ -I I
• I I I-,a·· ·. al· ~ I
~1-~1 ~ ~ ..
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 2.9E+OO
IE-17 IE-16 3E-14 8E-01
2E-17 IE-16 9E-13 7E-02
3E-16 2E-15 6E-13 2.IE+OO
IE-17 NIA 6E-15 2E-01
Page 14 of 40
EN:RGY ;
Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 868.686. 7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-005
Client Sample ID: BHV-6
Analyses Result Units
METALS, IN AIR
Uranium 1.8E-09 mg/L
Uranium, Activity 1.2E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 21 O 1.5E-14 uCi/mL
Lead 210 precision (±) 4.6E-15 uCi/mL
Lead 210 MDC 3.4E-16 uCi/mL
Radium 226 1.1E-16 uCi/mL
Radium 226 precision (±) 2.7E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.1E-16 uCi/mL
Thorium 230 precision (±) 2.2E-17 uCi/mL
Thorium 230 MDC 1.9E-17 uCi/mL
Thorium 232 9.0E-18 uCi/mL
Thorium 232 precision (±) 1.7E-18 uCi/mL
Thorium 232 MDC 1.7E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1880 pCi/Filter
Lead 21 O precision (±) 559 pCi/Filter
Lead 210 MDC 41 .8 pCi/Filter
Radium 226 13.2 pCi/Filter
Radium 226 precision (±) 3.3 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 13.9 pCi/Filter
Thorium 230 precision (±) 2.6 pCi/Filter
Thorium 230 MDC 2.3 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.21 pCi/Filter
Thorium 232 MDC 2.1 pCi/Filter
Uranium, Activity 145 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.6E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 1.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 3.8E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.5E-01 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
u
u
MCU
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 11 :59 / eli-h
SW6020 04/19/18 11 :59 I eli-h
E909.0 04/09/18 20:19 / meh
E909.0 04/09/18 20:19 / meh
E909.0 04/09/18 20: 19 / meh
E903.0 04/10/18 08:34 I arh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 I arh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 15 of40
,EN:RGY Trust our People. Trust our Data.
www.energylab.com
BIiiings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 888.688.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 1.3E+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.
122136000
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCU
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
FIELD 03/26/18 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 16 of 40
EN:RGY
, I I I , H ~
Trust our People. Trust our Data.
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BHV-6 -REPORT DATE: April 30, 2018
Quarter/Date Sampled Radionuclide Air Volume
Cl 8030835-005 nalu
l st Quarter Air 2018 230Tb
Air Volume in mLs 226Ra
l.22E+ll z10Pb
232Tb
+LLD's are from NRC Reg. Guide 4.14
r, •.L
Concentration
µCi/mL
l.2E-15
lE-16
lE-16
l.5E-14
9E-18
• ,
Counting
Precision
µCi/mL
NIA
2E-17
3E-17
5E-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
1 1· I ..
MDCµCi/mL
NIA
2E-17
lE-17
3E-16
2E-17
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
IL
•
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
lE-16 9E-14 l.3E+OO
lE-16 3E-14 4E-Ol
lE-16 9E-13 lE-02
2E-15 6E-13 2.6E+OO
NIA 6E-15 lE-01
Page 17 of 40
EI\ERGY Trust our People. Trust our Data.
www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-005
Client Sample ID: BHV-6
Analyses Result Units
METALS, IN AIR
Uranium 4.4E-09 mg/L
Uranium, Activity 3.0E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.6E-15 uCi/mL
Lead 210 MDC 3.3E-16 uCi/mL
Radium 226 1.0E-16 uCi/mL
Radium 226 precision (±) 2.9E-17 uCi/mL
Radium 226 MDC 1.9E-17 uCi/mL
Thorium 230 9.7E-17 uCi/mL
Thorium 230 precision (±) 1.8E-17 uCi/mL
Thorium 230 MDC 2.2E-17 uCi/mL
Thorium 232 1.4E-17 uCi/mL
Thorium 232 precision (±) 2.7E-18 uCi/mL
Thorium 232 MDC 2.1E-17 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1420 pCi/Filter
Lead 210 precision (±) 423 pCi/Filter
Lead 210 MDC 39.0 pCi/Filter
Radium 226 12.2 pCi/Filter
Radium 226 precision (±) 3.4 pCi/Filter
Radium 226 MDC 2.3 pCi/Filter
Thorium 230 11.5 pCi/Filter
Thorium 230 precision (±) 2.2 pCi/Filter
Thorium 230 MDC 2.6 pCi/Filter
Thorium 232 1.7 pCi/Filter
Thorium 232 precision (±) 0.33 pCi/Filter
Thorium 232 MDC 2.5 pCi/Filter
Uranium, Activity 358 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % ofEFF 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 3.2E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.4E-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
0.20
Report Date: 07/24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date/ By
SW6020 07 /12/18 15:27 / eli-h
SW6020 07 /12/18 15:27 I eli-h
E909.0 07111/18 20:09 / meh
E909.0 07/11/18 20:09 / meh
E909.0 07/11/18 20:09 / meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07 /13/18 08:20 / cnh
RADCALC 07/20/1813:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/1813:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 15 of 40
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www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.686. 7175 • Helena, MT 877 .472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-005
Client Sample ID: BHV-6
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 3.3E+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.
119179100
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27 /18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 07 /20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07 /20/18 14:42 I dmf
FIELD 06/25/18 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 16 of 40
EN:RGY
, , ,11 )111 '
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HIGHVOLU AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: BHV-6 I 11
REPORT DATE: July 24, 2018 I I I
Quarter/Date Sampled Concentration Counting
Air Volume Radionuclide µCi/mL Precision
µCi/mL
C 18060968-005 ""U 3.0E-15 NIA
2nd Quarter Air 2018 230Th IE-16 2E-17
Air Volume in mLs 226Ra IE-16 3E-17
1.19E+l 1 z10Pb 1.2E-14 4E-15
232Th IE-17 3E-18
+LLD's are from NRC Reg. Guide 4.14
*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
2E-17
3E-16
2E-17
Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
•
II
1 I ~ • 1
• -i
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
IE-16 9E-14 3.3E+OO
lE-16 3E-14 3E-01
IE-16 9E-13 IE-02
2E-15 6E-13 2.0E+OO
NIA 6E-15 2E-01
Page 17 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LA BORA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-006
Client Sample ID: BHV-7
Analyses Result Units
METALS, IN AIR
Uranium 6.0E-10 mg/L
Uranium, Activity 4.1 E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.8E-14 uCi/mL
Lead 21 O precision (±) 5.5E-15 uCi/mL
Lead 210 MDC 3.6E-16 uCi/mL
Radium 226 2.6E-16 uCi/mL
Radium 226 precision (±) 5.6E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 1.2E-16 uCi/mL
Thorium 230 precision (±) 2.3E-17 uCi/mL
Thorium 230 MDC 2.2E-18 uCi/mL
Thorium 232 8.7E-18 uCi/mL
Thorium 232 precision (±) 1.7E-18 uCi/mL
Thorium 232 MDC 1.6E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 2280 pCi/Filter
Lead 210 precision (±) 678 pCi/Filter
Lead 210 MDC 44.7 pCi/Filter
Radium 226 32.2 pCi/Filter
Radium 226 precision (±) 6.9 pCi/Filter
Radium 226 MDC 1.3 pCi/Filter
Thorium 230 15.2 pCi/Filter
Thorium 230 precision (±) 2.9 pCi/Filter
Thorium 230 MDC 0.27 pCi/Filter
Thorium 232 1.1 pCi/Filter
Thorium 232 precision (±) 0.20 pCi/Filter
Thorium 232 MDC 0.20 pCi/Filter
Uranium, Activity 50.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % ofEFF 3.1E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 3.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.5E-01 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 12:01 / eli-h
SW6020 04/19/18 12:01 / eli-h
E909.0 04/09/18 20:29 / meh
E909.0 04/09/18 20:29 I meh
E909.0 04/09/18 20:29 I meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.688.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD N/A
Uranium Natural, % of EFF 4.5E-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.
123304800
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 04/30/18
Collection Date: 03/26/18
Date Received: 03/29/18
Matrix: Filter
QCL Method Analysis Date I By
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of40
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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
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BH -7 ••
REPORT DATE: April 30, 2018 I'
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
Cl 8030835-006 ""u 4.IE-16
!st Quarter Air 2018 230Th IE-16
Air Volume in mLs 226Ra 3E-16
1.23E+l l 210Pb 1.8E-14
232To 9E-18
+LLD's are from NRC Reg. Guide 4.14
..
~ 1 11 ~
I' I ~ I ..
Counting
Precision
µCi/mL
NIA
2E-17
6E-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
ir:-· T I
F
T1r·\-~ i ' 1 'l'. • '1 I -. , :r : \. ..
•
L.L.D.+ Effluent Cone.* % Effluent MDCµCi/mL µCi/mL µCi/mL Concentration
NIA IE-16 9E-14 4.5E-OI
2E-18 IE-16 3E-14 4E-01
IE-17 IE-16 9E-13 3E-02
4E-16 2E-15 6E-13 3.IE+OO
2E-18 NIA 6E-15 IE-OJ
Page 20 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-006
Client Sample ID: BHV-7
Analyses Result Units
METALS, IN AIR
Uranium 2.3E-09 mg/L
Uranium, Activity 1.6E-15 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.2E-14 uCi/mL
Lead 210 precision (±) 3.7E-15 uCi/mL
Lead 210 MDC 3.2E-16 uCi/mL
Radium 226 4.3E-16 uCi/mL
Radium 226 precision (±) 9.2E-17 uCi/mL
Radium 226 MDC 2.0E-17 uCi/mL
Thorium 230 2.2E-16 uCi/mL
Thorium 230 precision (±) 4.1E-17 uCi/mL
Thorium 230 MDC 3.0E-18 uCi/mL
Thorium 232 1.7E-17 uCi/mL
Thorium 232 precision (±) 3.2E-18 uCi/mL
Thorium 232 MDC 2.1E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1490 pCi/Filter
Lead 210 precision (±) 444 pCi/Filter
Lead 210 MDC 39.3 pCi/Filter
Radium 226 52.5 pCi/Filter
Radium 226 precision (±) 11 .1 pCi/Filter
Radium 226 MDC 2.4 pCi/Filter
Thorium 230 26.4 pCi/Filter
Thorium 230 precision (±) 5.0 pCi/Filter
Thorium 230 MDC 0.37 pCi/Filter
Thorium 232 2.1 pCi/Filter
Thorium 232 precision (±) 0.39 pCi/Filter
Thorium 232 MDC 0.26 pCi/Filter
Uranium, Activity 189 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 2.1E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 5.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 7.3E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 2.8E-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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date / By
SW6020 07/12/18 15:29 I eli-h
SW6020 07/12/18 15:29 I eli-h
E909.0 07/11/18 20:21 I meh
E909.0 07/11 /18 20:21 I meh
E909.0 07/11/18 20:21 I meh
E903.0 07/17/18 10:59 I arh
E903.0 07/17/18 10:59 I arh
E903.0 07/17/18 10:59 I arh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13: 38 / dmf
RADCALC 07 /20/18 13: 38 / dmf
RADCALC 07 /20/18 13: 38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/1813:38/dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 I dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 18 of 40
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BIiiings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-006
Client Sample ID: BHV-7
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.7E+OO %
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.
120959800 L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07 /20/18 14:42 / dmf
06/25/18 00:00 / •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 19 of 40
EN:RGY
,I ', ,, J '
Trust our People. Trust our Data.
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HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: BHV-7
REPORT DATE: July 24, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C 18060968-006 natu l.6E-15
2ndQuarter Air 2018 230Th 2E-16
Air Volume in mLs 226Ra 4E-16
l.21E+l 1 210Pb l.2E-14
232Th 2E-17
+LLD's are from NRC Reg. Guide 4.14
Counting
Precision
µCi/mL
NIA
4E-17
9E-17
4E-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
3E-18
2E-17
3E-16
2E-18
-
Billings, MT 800.735.4489 • Casper, WV 888.235.0515
Gillette, WV 866.686.7175 • Helena, MT 877.472.0711
..
......
I I ---1 -
L.L.D.+ Effluent Cone.* % Effluent
µCi/mL µCi/mL Concentration
lE-16 9E-14 l.7E+OO
IE-16 3E-14 7E-01
lE-16 9E-13 SE-02
2E-15 6E-13 2.IE+OO
NIA 6E-15 3E-01
Page 20 of40
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www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C18030835-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium 3.5E-10 mg/L
Uranium, Activity 2.3E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 1.3E-14 uCi/mL
Lead 210 precision (±) 3.8E-15 uCi/mL
Lead 210 MDC 3.1E-16 uCi/mL
Radium 226 8.3E-17 uCi/mL
Radium 226 precision (±) 2.2E-17 uCi/mL
Radium 226 MDC 1.1E-17 uCi/mL
Thorium 230 5.8E-17 uCi/mL
Thorium 230 precision (±) 1.1E-17 uCi/mL
Thorium 230 MDC 1.8E-18 uCi/mL
Thorium 232 5.1 E-18 uCi/mL
Thorium 232 precision (±) 1.7E-18 uCi/mL
Thorium 232 MDC 1.5E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1550 pCi/Filter
Lead 210 precision (±) 462 pCi/Filter
Lead 210 MDC 38.1 pCi/Filter
Radium 226 10.2 pCi/Filter
Radium 226 precision (±) 2.7 pCi/Filter
Radium 226 MDC 1.4 pCi/Filter
Thorium 230 7.1 pCi/Filter
Thorium 230 precision (±) 1.3 pCi/Filter
Thorium 230 MDC 0.23 pCi/Filter
Thorium 232 0.63 pCi/Filter
Thorium 232 precision (±) 0.21 pCi/Filter
Thorium 232 MDC 0.18 pCi/Filter
Uranium, Activity 28.9 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 21 O, % of EFF 2.1E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 9.0E-03 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.9E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 9.0E-02 %
Thorium 232, EFF Year 6.0E-15 uCi/mL
Report RL -Analyte reporting limit.
Definitions: QCL -Quality control limit.
MDC -Minimum detectable concentration
Qualifiers
MCL/
RL QCL
2.5E-14
1.7E-20
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
Date Received: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 12:03 I eli-h
SW6020 04/19/18 12:03 / eli-h
E909.0 04/09/18 20:37 / meh
E909.0 04/09/18 20:37 / meh
E909.0 04/09/18 20:37 / meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 I arh
E903.0 04/10/18 08:34 / arh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 / sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 21 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 868.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD NIA
Uranium Natural, % of EFF 2.6E-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.
122983600
uCi/mL
%
uCi/mL
uCi/mL
L
Qualifiers RL
MCL/
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
FIELD 03/26/18 00:00 I •••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of 40
EI\ERGY
,, I,
;
Trust our People. Trust our Data.
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I • HIGH VOLUME AIR SAMPLING REPORT • I -.__
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
SAMPLE ID: BHV-8 -REPORtl' DATE: April 30, 2018
Quarter/Date Sampled Concentration Counting
Radionuclide Precision Air Volume µCi/mL µCi/mL
CI 8030835-007 nalu 2.3E-16 NIA
I st Quarter Air 2018 230Tb 6E-17 !E-17
Air Volume in mLs 226Ra 8E-17 2E-17
I.23E+II 2lllPb I.3E-14 4E-15
232Tb 5E-18 2E-18
+LLD's are from NRC Reg. Guide 4. I 4
*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
MDC µCi/mL
NIA
2E-18
lE-17
3E-16
!E-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 2.6E-OI
!E-16 3E-14 2E-01
IE-16 9E-13 9E-03
2E-15 6E-13 2.IE+OO
NIA 6E-15 9E-02
Page 23 of 40
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www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-007
Client Sample ID: BHV-8
Analyses Result Units
METALS, IN AIR
Uranium 1.4E-09 mg/L
Uranium, Activity 9.4E-16 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 8.8E-15 uCi/mL
Lead 210 precision (±) 2.6E-15 uCi/mL
Lead 210 MDC 2.8E-16 uCi/mL
Radium 226 3.0E-16 uCi/mL
Radium 226 precision (±) 6.5E-17 uCi/mL
Radium 226 MDC 2.0E-17 uCi/mL
Thorium 230 1.2E-16 uCi/mL
Thorium 230 precision (±) 2.3E-17 uCi/mL
Thorium 230 MDC 3.2E-18 uCi/mL
Thorium 232 8.5E-18 uCi/mL
Thorium 232 precision (±) 1.6E-18 uCi/mL
Thorium 232 MDC 1.9E-18 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 1070 pCi/Filter
Lead 210 precision (±) 319 pCi/Filter
Lead 210 MDC 33.9 pCi/Filter
Radium 226 36.3 pCi/Filter
Radium 226 precision (±) 7.9 pCi/Filter
Radium 226 MDC 2.4 pCi/Filter
Thorium 230 14.9 pCi/Filter
Thorium 230 precision (±) 2.8 pCi/Filter
Thorium 230 MDC 0.38 pCi/Filter
Thorium 232 1.0 pCi/Filter
Thorium 232 precision (±) 0.20 pCi/Filter
Thorium 232 MDC 0.23 pCi/Filter
Uranium, Activity 114 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 1.5E+OO %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 3.0E-02 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 4.1 E-01 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 1.4E-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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
Method Analysis Date / By
SW6020 07/12/18 15:31 / eli-h
SW6020 07/12/18 15:31 / eli-h
E909.0 07111/18 20:32 / meh
E909.0 07/11 /18 20:32 I meh
E909.0 07/11 /18 20:32 I meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E908.0 07 /13/18 08:20 I cnh
E908.0 07/13/18 08:20 I cnh
E908.0 07/13/18 08:20 I cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 / cnh
E908.0 07/13/18 08:20 I cnh
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
RADCALC 07 /20/18 14:42 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting lim it.
Page 21 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-007
Client Sample ID: BHV-8
Analyses Result Units
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Thorium 232, LLD
Uranium Natural, % of EFF
Uranium Natural, EFF Year
Uranium Natural, LLD
N/A uCi/mL
1.0E+OO %
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.
120738300 L
Qualifiers RL
MCL/
Report Date: 07/24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
07 /20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
06/25/18 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 22 of 40
EI\ERGY
,, ' ,I '
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... HIGH VOLUME A:IR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: BHV-8 • I I
-I • • • REPORT D4._TE: July 24, 2018 '
Quarter/Date Sampled Concentration Counting
Air Volume Radionuclide µCi/mL Precision
C 18060968-007 natu 9E-16
2nd Quarter Air 2018 230Th IE-16
Air Volume in mLs 226Ra 3E-16
l.21E+l l 210Pb 8.8E-15
232Th 9E-18
+LLD's are fromNRC 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
µCi/mL
NIA
2E-17
7E-17
3E-15
2E-18
MDC µCi/mL
NIA
3E-18
2E-17
3E-16
2E-18
Billings, MT BOO. 735.4489 • Casper, WY BBB.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 lE+OO
lE-16 3E-14 4E-OI
lE-16 9E-13 3E-02
2E-15 6E-13 l.5E+OO
NIA 6E-15 lE-01
Page 23 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Lab ID: C 18030835-008
Client Sample ID: Blanks
Analyses Result Units
METALS, IN AIR
Uranium 0.0014 mg/L
Uranium, Activity 9.2E-10 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 -9.3E-10 uCi/mL
Lead 210 precision (±) 2.5E-09 uCi/mL
Lead 210 MDC 4.3E-09 uCi/mL
Radium 226 2.1E-09 uCi/mL
Radium 226 precision (±) 1.3E-09 uCi/mL
Radium 226 MDC 1.4E-09 uCi/mL
Thorium 230 3.1E-10 uCi/mL
Thorium 230 precision (±) 2.4E-10 uCi/mL
Thorium 230 MDC 3.7E-10 uCi/mL
Thorium 232 2.3E-10 uCi/mL
Thorium 232 precision (±) 1.5E-10 uCi/mL
Thorium 232 MDC 2.0E-10 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 -0.93 pCi/Filter
Lead 210 precision(±) 2.5 pCi/Filter
Lead 210 MDC 4.3 pCi/Filter
Radium 226 2.1 pCi/Filter
Radium 226 precision (±) 1.3 pCi/Filter
Radium 226 MDC 1.4 pCi/Filter
Thorium 230 0.31 pCi/Filter
Thorium 230 precision (±) 0.24 pCi/Filter
Thorium 230 MDC 0.37 pCi/Filter
Thorium 232 0.23 pCi/Filter
Thorium 232 precision (±) 0.15 pCi/Filter
Thorium 232 MDC 0.20 pCi/Filter
Uranium, Activity 0.92 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF -2.0E+05 %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 2.3E+05 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 1.0E+06 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 3.8E+06 %
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
u
u
MCL/
RL QCL
3.0E-06
2.1E-12
0.20
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
Method Analysis Date / By
SW6020 04/19/18 12:05 I eli-h
SW6020 04/19/18 12:05 I eli-h
E909.0 04/09/18 20:49 / meh
E909.0 04/09/18 20:49 I meh
E909.0 04/09/18 20:49 I meh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E903.0 04/10/18 08:34 / arh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 / cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 I cnh
E908.0 04/18/18 08:55 / cnh
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/1816:17 /sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16: 17 / sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
RADCALC 04/23/18 16:20 I sec
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Page 24 of 40
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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: 1st Quarter Air 2018
Lab ID: C 18030835-008
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
1.0E+06 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1 L
Qualifiers RL
MCL/
Report Date: 04/30/18
Collection Date: 03/26/18
DateReceived: 03/29/18
Matrix: Filter
QCL Method Analysis Date / By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
04/23/18 16:20 / sec
04/23/18 16:20 / sec
04/23/18 16:20 / sec
04/23/18 16:20 / sec
03/26/18 00:00 / ***
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 25 of 40
EN:RGY
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-· HIGH VOLUME AIR SAMPLING REPORT
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 1st Quarter Air 2018
AMPLE ID: Blanks -
REPORT DATE: April 30, 2018 •
Quarterillate Sampled Radionuclide Air Volume
C 18030835-008 na•u
1 st Quarter Air 2018 230Tb
Air Volume in mLs 226Ra
l.24E+ll z10Pb
232Tb
. ',. r 4
I
r
,
Concentration
µCi/mL
7E-18
2E-18
2E-17
-7E-18
2E-18
. , • • ~ .. • • •
-I ... f
'I I, ... ~ ...
Counting
Precision MDCµCi/mL
µCi/mL
NIA NIA
2E-18 3E-18
lE-17 lE-17
2E-17 3E-17
lE-18 2E-18
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
• I •
,
•
• ...
-~· .... ·L,~ I
I I -I I it,
• I -.r .' _Tl ,
L.L.D.+ Effluent Cone.*
µCi/mL µCi/mL
lE-16 9E-14
lE-16 3E-14
lE-16 9E-13
2E-15 6E-13
NIA 6E-15
. -I
.L
I •
I'. .
-1
% Effluent
Concentration
8E-03
8E-03
2E-03
-lE-03
3E-02
NOTE: This report uses 124,000,000 Lair for comparison purposes, the routine report uses a 1 L system default.
+LLD's are from NRC Reg. Guide 4.14
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
Page 26 of 40
EI\ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.886.7175 • Helena, MT 877.472.0711
LABO RA TORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-008
Client Sample ID: Blanks
Analyses Result Units
METALS, IN AIR
Uranium 0.0015 mg/L
Uranium, Activity 1.0E-09 uCi/mL
RADIONUCLIDES -IN AIR
Lead 210 5.0E-09 uCi/mL
Lead 210 precision (±) 2.2E-09 uCi/mL
Lead 210 MDC 2.8E-09 uCi/mL
Radium 226 5.6E-09 uCi/mL
Radium 226 precision (±) 2.7E-09 uCi/mL
Radium 226 MDC 2.6E-09 uCi/mL
Thorium 230 1.1 E-09 uCi/mL
Thorium 230 precision (±) 2.0E-10 uCi/mL
Thorium 230 MDC 2.6E-10 uCi/mL
Thorium 232 2.7E-10 uCi/mL
Thorium 232 precision (±) 1.8E-10 uCi/mL
Thorium 232 MDC 2.7E-10 uCi/mL
RADIONUCLIDES -IN AIR -PER FILTER
Lead 210 5.0 pCi/Filter
Lead 210 precision(±) 2.2 pCi/Filter
Lead 210 MDC 2.8 pCi/Filter
Radium 226 5.6 pCi/Filter
Radium 226 precision (±) 2.7 pCi/Filter
Radium 226 MDC 2.6 pCi/Filter
Thorium 230 1.1 pCi/Filter
Thorium 230 precision (±) 0.20 pCi/Filter
Thorium 230 MDC 0.26 pCi/Filter
Thorium 232 0.27 pCi/Filter
Thorium 232 precision (±) 0.18 pCi/Filter
Thorium 232 MDC 0.27 pCi/Filter
Uranium, Activity 1.0 pCi/Filter
RADIOCHEMISTRY AIR FILTER COMPLIANCE
Lead 210, % of EFF 8.4E+05 %
Lead 210, EFF Day 6.0E-13 uCi/mL
Lead 210, LLD 2.0E-15 uCi/mL
Radium 226, % of EFF 6.3E+05 %
Radium 226, EFF Week 9.0E-13 uCi/mL
Radium 226, LLD 1.0E-16 uCi/mL
Thorium 230, % of EFF 3.6E+06 %
Thorium 230, EFF Year 3.0E-14 uCi/mL
Thorium 230, LLD 1.0E-16 uCi/mL
Thorium 232, % of EFF 4.5E+06 %
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
0.20
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27 /18
Matrix: Filter
Method Analysis Date / By
SW6020 07/12/18 15:33 / eli-h
SW6020 07/12/18 15:33 / eli-h
E909.0 04/14/18 23:08 / meh
E909.0 04/14/18 23:08 / meh
E909.0 04/14/18 23:08 / meh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E903.0 07/17/18 10:59 / arh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07 /17 /18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07/17/18 08:46 / cnh
E908.0 07 /17 /18 08:46 I cnh
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07 /20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 13:38 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 I dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
RADCALC 07/20/18 14:42 / dmf
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 24 of 40
EN:RGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
GIiiette, WY 886.888.7175 • Helena, MT 811.472.0711
LABORATORY ANALYTICAL REPORT
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Lab ID: C 18060968-008
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
1.1E+06 %
9.0E-14 uCi/mL
1.0E-16 uCi/mL
1.0 L
Qualifiers RL
MCL/
Report Date: 07 /24/18
Collection Date: 06/25/18
DateReceived: 06/27/18
Matrix: Filter
QCL Method Analysis Date I By
RADCALC
RADCALC
RADCALC
RADCALC
FIELD
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
07/20/18 14:42 / dmf
06/25/18 00:00 I•••
MCL -Maximum contaminant level.
ND -Not detected at the reporting limit.
Page 25 of 40
EN:RGY
( ,,. ' .1
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
HIGH VOLUME AIR SAMPCING REPORT ~--_
CLIENT: Energy Fuels Resources (USA) Inc
PROJECT: 2nd Quarter Air 2018
SAMPLE ID: Blanks
REPORT DATE: July 24, 2018
Quarter/Date Sampled Concentration Radionuclide Air Volume µCi/mL
C18060968-008 "''U 8E-15
2nd Quarter Air 2018 230Th 9E-15
Air Volume in mLs 226Ra SE-14
l.24E+08 210Pb 4E-14
232Th 2E-15
•
I -
I. .. -n -••
Counting L.L.D.+ Precision MDCµCi/mL
µCi/mL µCi/mL
NIA NIA lE-16
2E-15 2E-15 lE-16
2E-14 2E-14 lE-16
2E-14 2E-14 2E-15
lE-15 2E-15 NIA
NOTE: This report uses 124,000,000 L air for comparison purposes, the routine report uses a 1 L system default.
+LLD's are from NRC Reg. Guide 4.14
*Effluent Concentration from the NEW 10 CFR Part 20 -Appendix B -Table 2
Year for Natural Uranium
Year for Thorium-230, Thorium-232
Week for Radium-226
Day for Lead-210
I I
• ••
Effluent Cone.*
µCi/mL
9E-14
3E-14
9E-13
6E-13
6E-15
-
I
% Effluent
Concentration
9E+OO
3E+Ol
5E+OO
7E+OO
4E+Ol
Page 26 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 888.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
April 30, 2018
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C18030835
Project Name: 1st Quarter Air 2018
Quote ID: C4886 -Quarterly Air Analysis
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 3/29/2018 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C 18030835-001 BHV-1 03/26/18 00:00 03/29/18 Filter Composite of two or more samples
Client Provided Field Parameters
Metals, Total
Digestion, Total Metals,
Radiochemistry
Radiochemistry Air Filter Compliance
Calculations
RAD-AIR, Routine Radiological
Reports
RAD Alternate Unit Reporting Air
Filters
Lead 210
Radium 226
Thorium, Isotopic
C 18030835-002 BHV-2 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-003 BHV-4 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-004 BHV-5 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-005 BHV-6 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-006 BHV-7 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-007 BHV-8 03/26/18 00:00 03/29/18 Filter Same As Above
C 18030835-008 Blanks 03/26/18 00:00 03/29/18 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:
Digitally signed by
Tracey Archer
Date: 2018.04.30 11 :31 :57 -06:00
Page 1 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686. 7175 • Helena, MT 877.472.0711
~-~~~~~~-
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
1st Quarter Air 2018
C18030835
ORIGINAL SAMPLE SUBMITIAL(S)
All original sample submittals have been returned with the data package.
SUBCONTRACTING ANALYSIS
Report Date: 04/30/18
CASE NARRATIVE
Subcontracting of sample analyses to an outside laboratory may be required. If so, ENERGY LABORATORIES will utilize its
branch laboratories or qualified contract laboratories for this service. Any such laboratories will be indicated within the
Laboratory Analytical Report.
BRANCH LABORATORY LOCATIONS
eli-b -Energy Laboratories, Inc. -Billings, MT
eli-g -Energy Laboratories, Inc. -Gillette, WY
eli-h -Energy Laboratories, Inc. -Helena, MT
Tests associated with analyst identified as ELI-H were subcontracted to Energy Laboratories, 3161 E.Lyndale Ave., Helena,
MT, EPA Number MT00945.
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER.WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELi's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Helena, MT Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Analyte Result
Method: SW6020
Units
Report Date: 04/23/18
Work Order: C 18030835
RL %REC Low Limit High Limit RPO RPDLimit Qual
Analytical Run: ICPMS205-H_ 180419A
Lab ID: ICV Initial Calibration Verification Standard 04/19/18 11 :03
Uranium 0.0569 mg/L
Method: SW6020
Lab ID: MB-51406 Method Blank
Uranium 3E-05 mg/L
Lab ID: C18030835-001AD1L Serial Dilution
Uranium 2.65E-10 mg/L
Lab ID: LCS2-51406 Laboratory Control Sample
Uranium 0.0980 mg/L
Lab ID: LFB-51406 Laboratory Fortified Blank
Uranium 0.0492 mg/L
Lab ID: C18030835-001 AMS Sample Matrix Spike
Uranium 7.04E-10 mg/L
Lab ID: H18040115-001AD1L Serial Dilution
Uranium 7.73E-08 mg/L
Lab ID: LFB-51410 Laboratory Fortified Blank
Uranium 0.0491 mg/L
Lab ID: H18040270-001AD1L Serial Dilution
Uranium 6.91 E-11 mg/L
Lab ID: LFB-51470 Laboratory Fortified Blank
Uranium 0.0487 mg/L
Qualifiers:
RL -Analyte reporting limit.
N -The analyte concentration was not sufficiently high to calculate a
RPO for the serial dilution test.
0.00030 95 90 110
Batch: 41210
Run: ICPMS205-H_ 180419A 04/19/18 11 :32
3E-06
Run: ICPMS205-H_180419A 04/19/18 11 :36
1.5E-10 0 0 3.0 20
Run: ICPMS205-H_180419A 04/19/18 11 :42
3.0E-06 93 70 130
Run: ICPMS205-H_180419A 04/19/18 11 :44
3.0E-06 103 80 120
Run: ICPMS205-H_180419A 04/19/18 11 :46
1.5E-10 108 75 125
Run: ICPMS205-H_180419A 04/19/18 12:27
1.1 E-08 0 0 20 N
Run: ICPMS205-H_180419A 04/19/18 12:36
3.0E-06 103 80 120
Run: ICPMS205-H_ 180419A 04/19/18 12:53
1.5E-10 0 0 20
Run: ICPMS205-H_ 180419A 04/19/18 13:06
3.0E-06 103 80 120
ND -Not detected at the reporting limit.
Page 27 of 40
El'.ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 888.888.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Analyte
Method: E903.0
Lab ID: LCS-51406
Radium 226
Lab ID: MB-51406
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C 18030835-00JAMS
Radium 226
Lab ID: C18030835-00JAMSD
Radium 226
Qualifiers:
RL -Analyte reporting limit.
Count Result Units
Laboratory Control Sample
83.9 pCi/L
3 Method Blank
0.3 pCi/L
0.2 pCi/L
0.3 pCi/L
Sample Matrix Spike
7.23E-07 pCi/L
Sample Matrix Spike Duplicate
6.94E-07 pCi/L
MDC -Minimum detectable concentration
Report Date: 04/25/18
Work Order: C 18030835
RL %REC Low Limit High Limit
Run: TENNELEC-3_ 180404A
88 80 120
Run: TENNELEC-3_ 180404A
Run: TENNELEC-3_ 180404A
87 70 130
Run: TENNELEC-3_ 180404A
RPD RPDLimit Qual
Batch: 51406
04/10/18 08:34
04/10/18 08:34
04/10/18 08:34
84 70 130 4.2
04/10/18 08:34
20
ND -Not detected at the reporting limit.
Page 28 of 40
El'ERGY Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 1st Quarter Air 2018
Analyte
Method: E908.0
Lab ID: LCS-51406
Thorium 230
Lab ID: C18030835-007 AMS
Thorium 230
Lab ID: C18030835-007 AMSD
Thorium 230
Lab ID: MB-51406
Thorium 230
Thorium 230 precision (±)
Thorium 230 MDC
Thorium 232
Thorium 232 precision (±)
Thorium 232 MDC
Qualifiers:
RL -Analyte reporting limit.
Count Result Units
Laboratory Control Sample
26.3 pCi/L
Sample Matrix Spike
4.64E-07 pCi/L
Sample Matrix Spike Duplicate
4.67E-07 pCi/L
6 Method Blank
0.3 pCi/L
0.2 pCi/L
0.3 pCi/L
-0.07 pCi/L
0.1 pCi/L
0.3 pCi/L
MDC -Minimum detectable concentration
Report Date: 04/25/18
Work Order: C 18030835
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_ 18041 OB
110 80 120
Run: EGG-ORTEC_180410B
105 70 130
Run: EGG-ORTEC_180410B
106 70 130 0.7
Run: EGG-ORTEC_ 18041 OB
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 51406
04/18/18 08:55
04/18/18 08:55
04/18/18 08:55
20
04/18/18 08:55
u
u
Page 29 of 40
E"-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: 1st Quarter Air 2018
Analyte Count Result Units
Method: E909.0
Lab ID: LCS-51406 Laboratory Control Sample
Lead 210 180 pCi/L
Lab ID: MB-51406 Method Blank
Lead 210 0.2 pCi/L
Lab ID: C18030835-001 AMS Sample Matrix Spike
Lead 210 1 . 78E-05 pCi/L
Lab ID: C18030835-001 AMSD Sample Matrix Spike Duplicate
Lead 210 1.82E-05 pCi/L
Report Date: 04/25/18
Work Order: C18030835
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: PACKARD 3100TR_180403A
104 80 120
Run: PACKARD 3100TR_180403A
Run: PACKARD 3100TR_180403A
110 70 130
Run: PACKARD 3100TR_180403A
134 70 130 2.2
Batch: 51406
04/09/18 10:55
04/09/18 12:00
u
04/09/18 19: 16
04/09/18 19:32
20 S
-The RPO for the MSD is high. The individual spike recoveries are within range, the MB is acceptable, and the LCS is acceptable.
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 30 of 40
EN:RGY Trust our People. Trust our Data.
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Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: Kasey Vidick
Reviewed Date: 3/30/2018
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 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
n/a°C
Yes D
Yes D
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.688.7175 • Helena, MT877.472.0711
C18030835
Date Received: 3/29/2018
Received by: dcq
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 D
Not Present 0
Not Applicable 0
No VOA vials submitted 0
Not Applicable 0
Lab measurement of analytes considered field parameters that require analysis within 15 minutes of sampling such as
pH, Dissolved Oxygen and Residual Chlorine, are qualified as being analyzed outside of recommended holding time.
Solid/soil samples are reported on a wet weight basis (as received) unless specifically indicated. If moisture corrected,
data units are typically noted as -dry. For agricultural and mining soil parameters/characteristics, all samples are dried
and ground prior to sample analysis.
Contact and Corrective Action Comments:
None
Page 31 of 40
Sheet 1 of 1
CHAIN OF CUSTODY
Samples Shipped to: _E ..... n_erg..,""""y-L-ab;..;o ..... ra;..;t.;..;ie ... s ________ Contact: Garrln Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221 ·
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Prolect Samplers Name Samplers Slanature
1st Quarter Air 2018 Garrin Palmer I ,/;,u~A ~ -=,:;;(~/ -
Time
Sample ID Date Collected Collected Laboratory Analvsis Reauested
BHV-1 12/26/2017 -3/26/18 NA U~AT, TH-230, Ra-226 Pb-210, TH-232
BHV-2 12/26/2017 • 3/26/1 f NA U-NAT, TH-230 Ra-226, Pb-210, TH-232
BHV-4 12/26/2017 -3/26/1S NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-5 12/26/2017 -3/26/1f NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-6 12/26/2017 -3/26/1 E NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
BHV-7 12/26/2017 -3/26/16 NA U-NAT TH-230 Ra-226, Pb-210, TH-232
BHV-8 12/26/2017 -3/26/H NA U-NAT TH-230, Ra-226. Pb-210, TH-232
Blanks 12/26/2017 -3/26/1 f NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
e_ \Pr">':a..D~~
Comments: Please send report to Kathv Weinel at [e-mail]
Relinquished By:(Slgnature
&-~
Relinquished By:(Signature)
Date/Time Received By:(Signature)
;-...---1~1,201 a
1230
Date/Time Received By:(Signature)
~Q.N,,.I Q~
Date/Time
Date/Time
3}dq fill
It)$
.._
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.01058 1
First Monitoring Quarter 2015
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
[ill [ill "' -
Week I Filter Start Stop Start Stop • Starting Stopping
# Number Date Date Time Time M_anometer Manomete1
(m.H20) (in.H20)
9471079 12/26/2017 1/2/2018 87046 59 87213.92 10039 8 4.0 4.0
2 9471071 1/2/2018 1/8/2018 87213.92 87361.1 8830.8 4.0 4.0 4.0 1.0 274.1 623.1 1.07 0.96 33.73 8434.0 4.6193 4.7165 97.2
3 9471058 1/8/2018 1/15/2018 87361.1 87525.36 9855.6 4.0 4.0 4.0 2.6 275.8 621.0 1.08 0.95 33.57 9368.9 4.6431 4.6999 56,8 0.0061 97.8
4 9471055 1/15/2018 1/22/2018 87525.36 87692.98 10057.2 4.0 4.0 4.0 0.6 273.8 620.3 1.07 0.95 33.67 9589,7 4.6093 4.6991 89.8 0.0094 99.8
5 9471042 1/22/2018 1/29/2018 87692.98 87861.45 10108.2 4.0 4.0 4.0 -0.7 272.5 623.3 1.07 0.96 33.84 9685.6 4.6404 4.7139 73.5 0.0076 100.3
6 9471039 1/29/2018 2/5/2018 87861.45 88029.99 10112.4 4.0 4.0 4.0 6.5 279.7 621.03 1.08 0.94 33.33 9545.2 4.6320 4.7341 102.1 0.0107 100.3
7 9471026 2/5/2018 2/12/2018 88029.99 88201.97 10318.8 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9772.6 4.6220 4.7430 121.0 0.0124 102.4
8 9471023 2/12/2018 2/20/2018 88201.97 88393.12 11469.0 4,0 4.0 4.0 2.7 275.8 616.96 1.08 0.95 33.46 10865.6 4.6482 4.8874 239.2 0.0220 113.8
9 9471010 2/20/2018 2/26/2018 88393.12 88537.4 8656.8 4.0 4.0 4.0 -3.3 269.9 617.72 1.07 0.96 33.85 8296.8 4.6507 4.7243 73,6 0.0089 85.9
10 9471007 2/26/2018 3/5/2018 88537.4 88701.7 9858.0 4.0 4.0 4.0 3.8 277.0 617.22 1.08 0.95 33.39 9321.4 4.6114 4,8024 191.0 0.0205 97.8
11 9415194 3/5/2018 3/12/2018 88701.7 88867.56 9951.6 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9405.0 4.6850 4.8044 119.4 0.0127 98.7
12 9415191 3/12/2018 3/19/2018 88867.56 89036.68 10147.2 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0.94 33.23 9549,I 4.7220 4,9181 196.1 0.0205 100.7
13 9415178 3/19/2018 3/26/2018 89036.68 89207.02 10220.4 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0.94 33.20 9609.2 4.7409 4.8603 119.4 0,0124 101.4 ..
Totals 129625.8 14.02 12.34 435.70 122995.7 60.457 62.042 1584.5 0.1657
Averages 9971.2 4.0 4.0 4.0 2.9 276.l 619.59923 1.08 0.95 33.52 9461.2 4.651 4.772 121.9 0.0121 I 98.9
Comments:
Insert weekly flow check values in yellow columns.
·.::~ •.t.[ ""~~·~ ·~· .1, --.~tf; .. 'X.. '. L •.•,_.__ ~~ .! • _
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4nOl7 First Monitoring Quarter 2014
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 b= -0.01058 Updated: 7/30/14
Orifice SIN: 8091779
llH llH
Week Filter Start Stop Start Stop •• Starting Stopping
# Number Date Date Time Time ~ ~i~o:,~;'
Manometer
(in H,O)
l 9471078 12/26/2017 1/2/2018 97653.94 97823.12 10150.8 4,0 4.0
2 9471070 1/2/2018 1/8/2018 97823.12 97966.49 8602.2 4.0 4.0 4.0 1.0 274.1 623.06 1.07 0.96 33.73 8215.7 4.6370 4.7913 154.3 0.0188 85.3
3 9471059 1/8/2018 1/15/2018 97966.49 98132.69 9972 4.0 4.0 4.0 2.6 275.8 621.03 1.08 0.95 33,57 9479.6 4.6173 4.7127 95.4 0.0101 98.9
4 9471054 1/15/2018 1/22/2018 98132.69 98301.24 10113 4.0 4.0 4.0 0.6 273.8 620.26 1,07 0.95 33.67 9642.9 4.6278 4.7213 93.5 0.0097 100.3
5 9471043 1/22/2018 1/29/2018 98301 24 98469.47 10093.8 4.0 4.0 4.0 -0.7 272.5 623.3 l.07 0.96 33.84 9671.8 4.6328 4.7577 124.9 0.0129 100.l
6 9471038 1/29/2018 2/5/2018 98469.47 98638 10111.8 4.0 4,0 4.0 6,5 279,7 621.03 1.08 0.94 33.33 9544.7 4.6282 4.8698 241 6 0.0253 100.3
7 9471027 215/2018 2112/2018 98638 98809.19 10271.4 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9727.7 4.6495 4.8587 209.2 0.0215 101.9
8 9471022 2/12/2018 2/20/2018 98809.19 99000.61 11485.2 4,0 4.0 4,0 2.7 275.8 616.96 1.08 0.95 33.46 10880.9 4.6341 4.8566 2225 0.0204 113.9
9 9471011 2/20/2018 2126/2018 99000.61 99141.19 8434.8 4.0 4.0 4.0 -3.3 269,9 617.72 1.07 0.96 33.85 8084.0 4.6319 4.7003 68.4 0.0085 83.7
10 9471007 2/2612018 3/5/2018 99141.19 99309.14 10077 4,0 4.0 4.0 3.8 277.0 617.22 1.08 0.95 33.39 9528.5 4.6214 4.8292 207.8 0.0218 100.0
11 9415195 3/5/2018 3/12/2018 99309.14 99474.91 9946.2 4.0 4.0 4.0 5.4 278.5 620.01 l.08 0.95 33.38 9399.9 4.6741 4 8346 160.5 0.0171 9S.7
12 9415190 3/12/2018 3/19/2018 99474.91 99644,26 10161 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0.94 33.23 9562,1 4.7135 4.8578 144.3 0.0151 100.8
13 9415179 3119/2018 3/26/2018 99644.26 99811.85 10055.4 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0.94 33.20 9454,0 4.7148 4.8066 91.8 0,0097 99.8
---Totals 129474.6 14.02 12.34 435.70 122850.0 60.423 62.377 1954.2 0.2054
Averages 9959.6 4.0 4.0 40 2.9 276.1 619.59923 1.08 0.95 33.52 9450.0 4.648 4.798 150.3 0.0158 I 98.8
Insert week[y flow check values in yellow columns.
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.01058 1
First Monitoring Quarter 2014
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
t.H t.H
Week I Filter I Start Stop Start Stop I Starting Stopping
# Number Date Date Time Time Manometer Manometer
(in. H20) (in. H20)
9471077 12/26/2017 1/2/2018 3209.98 3380.92 10256.4 4.0 4.0
2 9471069 1/2/2018 1/8/2018 3380.92 3523.35 8545.8 4.0 4.0 4.0 1.0 274.1 623.06 1.07 0.96 33.73 8161.8 4.6020 4.6687 66.7
3 9471060 1/8/2018 1/15/2018 3523.35 3690.03 10000.8 4.0 4.0 4.0 2.6 275.8 621.03 1.08 0.95 33,57 9506.9 4.6035 4.6530 49.5 0.0052 99.2
4 9471053 1/15/2018 1/22/2018 3690.03 3854.64 9876.6 4.0 4.0 4.0 0.6 273.8 620.26 1.07 0.95 33 67 9417.5 4.6262 4.7049 78.7 0.0084 98.0
5 9471044 1/22/2018 1/29/2018 3854.64 4021.94 10038.0 4.0 4.0 4.0 -0.7 272.5 623.31 1.07 0.96 33.84 9618.3 4.6439 4.6927 48.8 0.0051 99.6
6 9471037 1/29/2018 2/5/2018 4021.94 4190.09 10089.0 4.5 4.0 4.3 6.5 279.7 621.03 1.12 0.97 34.35 9813.9 4.6296 4.7054 75.8 0.0077 100.l
7 9471028 2/5/2018 2/12/2018 4190.09 4362.04 10317.0 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33-45 9770.9 4.6441 4.7170 72.9 0.0075 102.4
8 9471021 2/12/2018 2/20/2018 4362.04 4554.39 11541.0 4.0 4.0 4.0 2.7 275.8 616.96 1.08 0.95 33.46 10933.8 4.6376 4.8386 201.0 0.0184 114.5
9 9471012 2/20/2018 2/26/2018 4554.39 4698.77 8662.8 4.0 4.0 4.0 -3.3 269.9 617.72 1.07 0.96 33.85 8302.5 4.6398 4.6977 57.9 0.0070 85.9
10 9471005 2/26/2018 3/5/2018 4698.77 4861.59 9769.2 4.0 4.0 4.0 3.8 277.0 617.72 1.08 0.95 33.41 9241.2 4.6128 4.7266 113.8 0.0123 96.9
11 9415196 3/5/2018 3/12/2018 4861.59 5027.79 9972.0 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9424.3 4.6979 4,7499 52.0 0.0055 98.9
12 9415190 3/12/2018 3/19/2018 5027.79 5198.03 10214.4 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0.94 33.23 9612.4 4.7257 4.8298 104.1 0.0108 101.3
13 9415180 3/19/2018 3/26/2018 5198.03 5364,71 10000.8 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0.94 33.20 9402.7 4.7503 4,8238 73.5 0.0078 99.2
Totals 129283.8 14.05 12.37 436.73 122965.0 60.439 61.519 1079.7 0 I 125
Averages 9944.9 4.0 4.0 4.0 2.9 276.1 619.63769 1.08 0.95 33,59 9458.8 4.649 4.732 83.1 0.0081 I 98.7
Comments:
:Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 b= -0.01058
Orifice SIN: 8091779
fill fill
Week Filter Start Stop Start Stop :11 Srarung Stopping
# Number Date Date Time Time a ~. l Manometer Manometer ~ • ' -(in. H20) (in.H20)
1 9471076 12/26/2017 1/2/2018 96298.05 96469.4 10281 4.0 4.0
2 9471068 1/2/2018 1/8/2018 96469.4 96611.45 8523.0 4.0 4.0 4.0 L.0 274.1 623.06 1.07 0.96 33.73 8140.0 4.6139 4.7309 117.0 0.0144 84.6
3 9471061 1/8/2018 1/15/2018 96611.45 96778.15 10002.0 4.0 4.0 4.0 2.6 275.8 621.03 1.08 0.95 33.57 9508.1 4.6154 4,6765 61 .1 0.0064 99.2
4 9471052 1/15/2018 1/22/2018 96778.15 96943.22 9904.2 4,0 4,0 4,0 0,6 273.8 620.26 1,07 0.95 33.67 9443.8 4.6434 4.7516 108.2 0.0115 98.3
5 9471045 1/22/2018 1/29/2018 96943.22 97095.97 9165.0 4.0 4.0 4.0 ·0.7 272.5 623.3 1.07 0.96 33.84 8781.8 4.6390 4.7404 101.4 0.0115 90.9
6 9471036 1/29/2018 2/5/2018 97095.97 97261.15 9910.8 4.0 4.0 4.0 6.5 279.7 621.03 1.08 0.94 33.33 9354.9 4.6239 4.7323 108.4 0.0116 98.3
7 9471029 2/5/2018 2/12/2018 97261.15 97430.41 10155.6 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9618.0 4.6190 4.7435 124.5 0.0129 100.8
8 9471020 2/12/2018 2/20/2018 97430.41 97622.78 11542,2 4,0 4,0 4,0 2,7 275.8 616.96 1.08 0.95 33.46 10934.9 4.6486 4,8483 199.7 0.0183 114.5
9 9471013 2/20/2018 2/26/2018 97622.78 97767.5 I 8683.8 4.0 4.0 4.0 ·3.3 269.9 617.72 1.07 0.96 33.85 8322.7 4.6208 4.6779 57.1 0.0069 86.1
10 9471004 2/26/2018 3/5/2018 97767.51 97929.97 9747.6 4.0 4.0 4.0 3.8 277.0 617.22 1.08 0,95 33.39 9217.0 4.6213 4,7435 122,2 0,0133 96.7
II 9415197 3/5/2018 3/12/2018 97929,97 98096,17 9972.0 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9424.3 4.8165 4.8874 70.9 0.0075 98.9
12 9415188 3/12/2018 3/19/2018 98096. 17 98266.74 10234.2 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0.94 33.23 9631.0 4.7210 4.8530 132,0 0.0137 101.5
13 9415181 3/19/2018 3/26/2018 98266,7 98433.09 9981 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0.94 33.20 9384.1 4,7150 4.7968 81.8 0.0087 99.0
Totals 128102.4 I 14.02 12.34 435.70 121542.8 60.511 61.911 1400.5 0.1485
Averages 9854.0 4.0 4.0 4.0 2.9 276.1 619.59923 I 08 0.95 33.52 9349.4 4.655 4.762 107.7 0.0114 I 97.8
Comments:
Insert weekly flow check values in yellow columns.
Energy Fuels Resources -White Mesa Mill I Calibration Date: 10/4/2017
b= -O.OI058 I First Monitoring Quarter 2014 rew:rr·.-. Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
. _i_._·: .\ t>~.:.• 1 Orifice SIN: 8091779
t.H t.H I Weeki Filter Start Stop Start Stop . Starting Stopping
# Number Date Date Time Time I Manometer Manometer
' (in.H20) (in H20) --
9471075 12/26/2017 1/2/2018 12671.71 12842.64 10255.8 4.0 4.0 4.0 2.6 275.7 622.04 1.08 0.95 33.60 9758.2 4.6184 4.7263 107.9 0.0111 101.7
2 9471067 1/2/2018 1/8/2018 12842.64 12985.03 8543.4 4.0 4.0 4.0 1.0 274.1 623.06 1.07 0.96 33.73 8159.5 4.5935 4.7009 107.4 0.0132 84.8
3 9471062 1/8/2018 1/15/2018 12985.03 13151.7 10000.2 4.0 4.0 4.0 2.6 275.8 621.03 1.08 0.95 33.57 9506.4 4.6189 4.6871 68.2 0.0072 99.2
4 9471051 1/15/2018 1/22/2018 13151.7 13316.44 9884.4 4.0 4.0 4.0 0.6 273.8 620.26 1.07 0.95 33.67 9424.9 4.6089 4.6889 80.0 0.0085 98.1
5 9471046 1/22/2018 1/29/2018 13316.44 13483.62 10030.8 4.0 4.0 4.0 -0.7 272.5 623.3 1.07 0.96 33.84 9611.4 4.6146 4.6750 60.4 0.0063 99.5
6 9471035 1/29/2018 2/5/2018 13483.62 13651.87 10095 4.0 4.0 4.0 6.5 279.7 621.03 1.08 0.94 33.33 9528.8 4.6276 4.7368 109.2 0.0115 100.1
7 9471030 2/5/2018 2/12/2018 13651.87 13823.77 10314 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9768.0 4.6564 4.9149 258.5 0.0265 102.3
8 9471019 2/12/2018 2/20/2018 13823.77 14016.07 11538 4.0 4.0 4.0 2.7 275.8 616.96 1.08 0.95 33.46 10930.9 4.6343 4.8326 198.3 0.0181 114.5
9 9471014 2/20/2018 2/26/2018 14016.07 14160.48 8664.6 3.0 4.0 3.5 -3.3 269.9 617.72 1.00 0.90 31.68 7772.2 4.6460 4.6884 42.4 0.0055 86.0
10 9471003 2/26/2018 3/5/2018 14160.48 14323.29 9768.6 4.0 4.0 4.0 3.8 277.0 617.22 1.08 0.95 33.39 9236.9 4.6221 4.7824 160.3 0.0174 96.9
11 9415198 3/5/2018 3/12/2018 14323.29 14489.48 9971.4 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9423.7 4.7976 4.8866 89.0 0.0094 98.9
12 9415187 3/12/2018 3/19/2018 14489.48 14659.72 10214.4 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0.94 33.23 9612.4 4_7437 4.9467 203 0 0.0211 101.3
13 9415182 3/19/2018 3/26/2018 14659.72 14826.4 10000.8 4.0 4,0 4.0 6,6 279.8 616.45 1.09 0.94 33.20 9402,7 4.7359 4,8405 104,6 0.0111 99.2
Totals 129281.4 13.95 12.28 433.53 122136.0 60.518 62.107 1589.2 0.1667
Averages 9944.7 3.9 4.0 4.0 2.9 276.1 619.59923 1.07 0.94 33.35 9395.1 4.655 4.777 122.2 0.0128 I 98_7
Comments: Replaced Elapsed time indicator on 7 /I I /2016
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.01058 1
First Monitoring Quarter 2014
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
llli llli
Week i Filter Start Stop Start Stop 11 ,-, Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in. H20)
1 9471074 12/26/2017 1/2/2018 4868.92 5036.86 10076.4 4.0 4.0
2 9471066 1/2/2018 1/8/2018 5036.86 5183.37 8790.6 4.0 4,0 4.0 1.0 274.1 623.06 1.07 0.96 33.73 8395.6 4.6204 4.7466 126.2 0.0150 87.2
3 9471063 1/8/2018 1/15/2018 5183.37 5348.24 9892.2 4,0 4,0 4.0 2.6 275.8 621.03 1.08 0.95 33.57 9403.7 4.6405 4.7136 73.1 0.0078 98.1
4 9471050 1/15/2018 1/22/2018 5348.24 5515.24 10020.0 4.0 4.0 4.0 0.6 273.8 620.26 1.07 0.95 33.67 9554.2 4.5975 4.7250 127.5 0.0133 99.4
5 9471047 1/22/2018 1/29/2018 5515.24 5683.93 10121.4 4.0 4.0 4.0 -0.7 272.5 623.3 1.07 0.96 33.84 9698.2 4.6210 4.7313 110.3 0.0114 100.4
6 9471034 1/29/2018 2/5/2018 5683.93 5852.27 10100.4 4.5 4.0 4.3 6.5 279.7 621.03 1.12 0.97 34,35 9825.0 4.6376 4.7774 139.8 0.0142 100.2
7 9471031 2/5/2018 2/12/2018 5852.27 6024.39 10327.2 4.0 4,0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9780.5 4.6273 4.8260 198.7 0.0203 102.5
8 9471018 2/12/2018 2/20/2018 6024.39 6215.6 11472.6 4.0 4.0 4.0 2.7 275.8 616.96 1.08 0.95 33.46 10869.0 4.6250 4.9379 312.9 0.0288 113.8
9 9471015 2/20/2018 2/26/2018 6215.6 6359.77 8650.2 4.0 4.0 4.0 -3.3 269.9 617.72 1.07 0.96 33.85 8290.5 4.6260 4.6994 73.4 0.0089 85.8
10 9471002 2/26/2018 3/5/2018 6359.77 6523.2 9805.8 4.0 4.0 4.0 3.8 277.0 617.22 1.08 0.95 33.39 9272.0 4.6053 4.8577 252.4 0.0272 97.3
11 9415199 3/5/2018 3/12/2018 6523.2 6690.2 10020.0 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9469.6 4,7681 4.8755 107.4 0.0113 99.4
12 9415186 3/12/2018 3/19/2018 6690.2 6859.31 10146.6 4.0 4.0 4.0 6,1 279.3 616.45 1.09 0.94 33.23 9548.6 4.7356 4.9071 171.5 0.0180 100.7
13 9415183 3/19/2018 3/26/2018 6859.31 7029.67 10221.6 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0.94 33.20 9610.3 4.6969 4.8045 107.6 0.0112 101.4 -..... -~·----. Totals 129645.0 14,05 12.37 436.72 123304.8 60.410 62.328 19184 0.1997
Averages 9972.7 4.0 4.0 4.0 2.9 276.1 619.59923 1.08 0.95 33.59 9485.0 4.647 4.794 147.6 0.0154 I 98.9
Comments: Time lnd1cator was found broken on 4/10/2017. Replaced Time Indicator on 4/10/2017.
Insert weekly flow check values in yellow columns.
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.010581
First Monitoring Quarter 2014
Period: December 26, 2017 -March 26, 2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779 ..
LI.H LI.H
Week I Filter I Start
I
Stop
I
Start
I
Stop 1• Srarting Stopping
# Number Date Date Time Time .• Manometer Manometer
(in.H20) (in.H20)
I 9471073 12/26/2017 1/2/2018 11330.02 11497.41 10043.4 4.0 4.0 4.0 2.6 275.7 622.04 1.08 0.95 33.60 9556.l 4.6218 4.7052 83.4 0.0087 99.6
2 9471065 1/2/2018 1/8/2018 11497.41 11644.3 8813.4 4.0 4.0 4,0 1.0 274.1 623.06 1.07 0.96 33.73 8417.4 4.6189 4.6995 80.6 0.0096 87.4
3 9471064 1/8/2018 1/15/2018 11644.3 11808.7 9864.0 4.0 4.0 4.0 2.6 275.8 621.03 l.08 0.95 33.57 9376.9 4.6148 4.6619 47.l 0.0050 97.9
4 9471049 1/15/2018 1/22/2018 11808.7 11976.24 10052.4 4.0 4.0 4.0 0.6 273.8 620.26 1.07 0.95 33.67 9585.1 4.6118 4.6674 55.6 0.0058 99.7
5 9471048 1/22/2018 1/29/2018 11976.24 12144.71 10108.2 4.0 4.0 4.0 -0.7 272.5 623.3 1.07 0.96 33.84 9685.6 4.6085 4.6496 41.1 0.0042 100.3
6 9471033 1/29/2018 2/5/2018 12144.71 12313.03 10099.2 4.0 4.0 4.0 6 . .5 279.7 621.03 1.08 0.94 33.33 9532.8 4.6016 4,6651 63.5 0.0067 100.2
7 9471032 2/5/2018 2/12/2018 12313.03 12485.07 10322.4 4.0 4.0 4.0 3.9 277.0 619.25 1.08 0.95 33.45 9776.0 4.6557 4.7399 84.2 0.0086 102.4
8 9471017 2/12/2018 2/20/2018 12485.07 12676.24 11470.2 4.0 4.0 4.0 2.7 275.8 616.96 1.08 0.95 33.46 10866.7 4.6530 48208 167.8 0.0154 113.8
9 9471016 2/20/2018 2/26/2018 12676.24 12820.44 8652.0 4.0 4.0 4.0 -3.3 269,9 617,72 1.07 0.96 33.85 8292,2 4.6471 4.7407 93.6 0.0113 85.8
10 9471001 2/26/2018 3/5/2018 12820.44 12984.78 9860.4 4.0 4.0 4.0 3.8 277.0 617.22 l.08 0.95 33.39 9323.7 4.5876 4.7784 190.8 0.0205 97.8
II 9415200 3/5/2018 3/12/2018 12984.78 13150.8 9961.2 4.0 4.0 4.0 5.4 278.5 620.01 1.08 0.95 33.38 9414.1 4.7643 4.8339 69.6 0.0074 98.8
12 9415185 3/12/2018 3/19/2018 13150.8 13319.9 10146.0 4.0 4.0 4.0 6.1 279.3 616.45 1.09 0,94 33,23 9548.0 4,7267 4.8502 123.5 0.0129 100.7
13 9415184 3/19/2018 3/26/2018 13319.9 13490.24 10220.4 4.0 4.0 4.0 6.6 279.8 616.45 1.09 0,94 33.20 9609.2 4.7246 4.8452 120.6 0.0126 101.4
-----------· -. ~ -Totals 129613.2 I 14.02 12.34 435.70 122983.6 60.436 61.658 1221.4 0.1287
Averal(es 9970.2 4.0 4,0 4.0 2.9 276.1 619.59923 1.08 0.95 33.52 9460.3 4.649 4.743 94.0 0.0099 I 98.9
Comments:
Insert weekly 'flow check values irr_yellow,columns. -··--. ._ .... -~ _ . ._ I •.:..~
G~columw~ca'jeuln~ a--er.i'1:1;,5'f1li"in ·~ IIICI ~lio~.
Blan~s.1
•
I Period: December 26, 2017 -March
26 2018
Week Filte.r Start Stelf) Net # Nlllmber Date · Bate
1 9471072 26-Dec-17 02-Jan-18 4.6163
2 9471057 02-Jan-18 08-Jan-18 4.6210
3 9471056 08-Jan-18 15-Jan-18 4.6083
4 9471041 15-Jan-18 22-Jan-18 4.6260
5 9471040 22-Jan-18 29-Jan-18 4.6421
6 9471025 29-Jan-18 05-Feb-18 4.6521
7 9471024 05-Feb-18 12-Feb-18 4.6462
8 9471009 12-Feb-18 20-Feb-18 4.6368
9 9471008 20-Feb-18 26-Feb-18 4.6312
10 9415193 26-Feb-18 05-Mar-18 4.6881
11 9415192 05-Mar-18 12-Mar-18 4.7026
12 9415177 12-Mar-18 19-Mar-18 4.7532
13 9415176 19-Mar-18 26-Mar-18 4.7677
Totals
Trust our People. Trust our Data.
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Billings, MT 800.735.4489 • Casper, WY 888.235.051
Gillette, WY 866.686.7175 • Helena, MT 877.472.071
ANALYTICAL SUMMARY REPORT
July 24, 2018
Energy Fuels Resources (USA) Inc
225 Union Blvd Ste 600
Lakewood, CO 80228-1826
Work Order: C18060968
Project Name: 2nd Quarter Air 2018
Quote ID: C4886 -Quarterly Air Analysis
Energy Laboratories, Inc. Casper WY received the following 8 samples for Energy Fuels Resources (USA) Inc on 6/27/2018 for
analysis.
Lab ID Client Sample ID Collect Date Receive Date Matrix Test
C 18060968-001 BHV-1 06/25/18 00:00 06/27 /18 Filter Composite of two or more samples
Client Provided Field Parameters
Metals, Total
Digestion, Total Metals,
Radiochemistry
Radiochemistry Air Filter Compliance
Calculations
RAD-AIR, Routine Radiological
Reports
RAD Alternate Unit Reporting Air
Filters
Lead 210
Radium 226
Thorium, Isotopic
C 18060968-002 BHV-2 06/25/18 00:00 06/27/18 Filter Same As Above
C 18060968-003 BHV-4 06/25/18 00:00 06/27 /18 Filter Same As Above
C 18060968-004 BHV-5 06/25/18 00:00 06/27/18 Filter Same As Above
C 18060968-005 BHV-6 06/25/18 00:00 06/27/18 Filter Same As Above
C 18060968-006 BHV-7 06/25/18 00:00 06/27/18 Filter Same As Above
C 18060968-00 7 BHV-8 06/25/18 00:00 06/27/18 Filter Same As Above
C 18060968-008 Blanks 06/25/18 00:00 06/27/18 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:
Digitally signed by
Tracey Archer
Date: 2018.07.24 17:07:22 -06:00
Page 1 of 40
Er\E RGY ~~ Trust our People. Trust our Data. lllil:iilll www.energylab.com
Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 886.686.7175 • Helena, MT 877.472.0711
CLIENT:
Project:
Work Order:
Energy Fuels Resources (USA) Inc
2nd Quarter Air 2018
C18060968
ORIGINAL SAMPLE SUBMITTAL(S)
All original sample submittals have been returned with the data package.
SUBCONTRACTING ANALYSIS
Report Date: 07 /24/18
CASE NARRATIVE
Subcontracting of sample analyses to an outside laboratory may be required. If so, ENERGY LABORATORIES will utilize its
branch laboratories or qualified contract laboratories for this service. Any such laboratories will be indicated within the
Laboratory Analytical Report.
BRANCH LABORATORY LOCATIONS
eli-b -Energy Laboratories, Inc. -Billings, MT
eli-g -Energy Laboratories, Inc. -Gillette, WY
eli-h -Energy Laboratories, Inc. -Helena, MT
Tests associated with analyst identified as ELI-H were subcontracted to Energy Laboratories, 3161 E.Lyndale Ave., Helena,
MT, EPA Number MT00945.
ISO 17025 DISCLAIMER:
The results of this Analytical Report relate only to the items submitted for analysis.
ENERGY LABORATORIES, INC. -CASPER.WY certifies that certain method selections contained in this report meet
requirements as set forth by the above accrediting authorities. Some results requested by the client may not be covered
under these certifications. All analysis data to be submitted for regulatory enforcement should be certified in the sample
state of origin. Please verify ELi's certification coverage by visiting www.energylab.com
ELI appreciates the opportunity to provide you with this analytical service. For additional information and services visit our
web page www.energylab.com.
Page 2 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686. 7175 • Helena, MT 877 .472.0711
QA/QC Summary Report
Prepared by Helena, MT Branch
Client: Energy Fuels Resources (USA) Inc Report Date: 07/19/18
Work Order: C18060968 Project: 2nd Quarter Air 2018
Analyte
Method: SW6020
Lab ID: ICV
Uranium
Method: SW6020
Lab ID: MB-51885
Uranium
Lab ID: C18060968-001AD1L
Uranium
Lab ID: LFB-51885
Uranium
Lab ID: C18060968-001AMS
Uranium
Method: SW6020
Lab ID: LCS2-51885
Uranium
Qualifiers:
RL -Analyte reporting limit.
Result Units RL %REC Low Limit High Limit RPO RPDLimit Qual
Initial Calibration Verification Standard
0.0556 mg/L 0.00030
Method Blank
0.0003 mg/L
Serial Dilution
1.23E-09 mg/L 1.5E-10
Laboratory Fortified Blank
0.0441 mg/L 1.5E-10
Sample Matrix Spike
1.59E-09 mg/L 1.5E-10
Laboratory Control Sample
0.0924 mg/L 1.5E-10
93
88
102
90
Analytical Run: ICPMS205-H_ 180712C
07/12/18 11 :32
110
Run: ICPMS205-H_180712C
Run: ICPMS205-H_180712C
0 0
Run: ICPMS205-H_ 180712C
75 125
Run: ICPMS205-H_ 180712C
75 125
Run: ICPMS205-H_180717A
4.6
Batch: 42187
07/12/18 15:02
07/12/18 15:06
20
07/12/1815:10
07/12/1815:12
Batch: 42187
07/17/1811:19
88 85 115
ND -Not detected at the reporting limit.
Page 27 of 40
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Billings, MT 800.735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Analyte Count Result Units
Method: E903.0
Lab ID: LCS-51885
Radium 226
Lab ID: MB-51885
Radium 226
Radium 226 precision (±)
Radium 226 MDC
Lab ID: C18060968-002AMS
Radium 226
Lab ID: C18060968-002AMSD
Radium 226
Qualifiers:
RL -Analyte reporting limit.
3
MDC -Minimum detectable concentration
Laboratory Control Sample
82.6 pCi/L
Method Blank
0.5 pCi/L
0.3 pCi/L
0.5 pCi/L
Sample Matrix Spike
8.20E-07 pCi/L
Sample Matrix Spike Duplicate
8.14E-07 pCi/L
Report Date: 07/20/18
Work Order: C 18060968
RL %REC Low Limit High Limit
Run: G542M_ 180710D
87 80 120
Run: G542M_ 180710D
Run: G542M_ 18071 OD
87 70 130
Run: G542M_180710D
86 70 130
ND -Not detected at the reporting limit.
RPO RPDLimit Qual
0.8
Batch: 51885
07/17/18 10:59
07/17/18 10:59
u
07/17/1810:59
07/17/18 10:59
20
U -Not detected at minimum detectable concentration
Page 28 of 40
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 8&6.68&.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Analyte Count Result Units
Method: E90B.O
Lab ID: LCS-51885
Thorium 230
Lab ID: C18060968-007 AMS
Thorium 230
Lab ID: C18060968-007 AMSD
Thorium 230
Lab ID: MB-51885
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
27.5 pCi/L
Sample Matrix Spike
5.53E-07 pCi/L
Sample Matrix Spike Duplicate
5.34E-07 pCi/L
Method Blank
1 pCi/L
0.2 pCi/L
0.3 pCi/L
-0.04 pCi/L
0.1 pCi/L
0.3 pCi/L
Report Date: 07 /20/18
Work Order: C 18060968
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: EGG-ORTEC_ 18071 OA
113 80 120
Run: EGG-ORTEC_ 18071 OA
108 70 130
Run: EGG-ORTEC_180710A
103 70 130 3.6
Run: EGG-ORTEC_180710A
ND -Not detected at the reporting limit.
U -Not detected at minimum detectable concentration
Batch: 51885
07/13/18 08:20
07 /13/18 08:20
07 /13/18 08:20
20
07/13/18 08:20
u
Page 29 of 40
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Billings, MT 800. 735.4489 • Casper, WY 888.235.0515
Gillette, WY 866.686.7175 • Helena, MT 877.472.0711
QA/QC Summary Report
Prepared by Casper, WY Branch
Client: Energy Fuels Resources (USA) Inc
Project: 2nd Quarter Air 2018
Analyte
Method:
Lab ID:
Lead 210
E909.0
LCS-518B5
Lab ID: MB-51885
Lead 210
Lead 210 precision (±)
Lead 210 MDC
Lab ID: C18060968-001AMS
Lead 210
Count Result Units
Laboratory Control Sample
170 pCi/L
3 Method Blank
0.5 pCi/L
1 pCi/L
2 pCi/L
Sample Matrix Spike
1.59E-05 pCi/L
Report Date: 07/20/18
Work Order: C 18060968
RL %REC Low Limit High Limit RPD RPDLimit Qual
Run: PACKARD 3100TR_180709A
95 80 120
Run: PACKARD 31 OOTR_ 180709A
Run: PACKARD 31 OOTR_ 180709A
134 70 130
Batch: 51885
07/11/18 10:55
07/11 /18 12:02
u
07/11/18 19:01
s
-Spike response is not in range for this analysis. Since the LCS and the RPD recoveries are in range, the response is considered to be matrix related.
Lab ID: C18060968-001AMSD Sample Matrix Spike Duplicate
Lead 210 1.50E-05 pCi/L
Qualifiers:
RL -Analyte reporting limit.
MDC -Minimum detectable concentration
U -Not detected at minimum detectable concentration
Run: PACKARD 3100TR_ 180709A
96 70 130 5.4
ND -Not detected at the reporting limit.
S -Spike recovery outside of advisory limits.
07/11/1819:17
20
Page 30 of 40
El'J:RGY Trust our People. Trust our Data.
www.energylab.com
Work Order Receipt Checklist
Energy Fuels Resources (USA) Inc
Login completed by: Dorian Quis
Reviewed by: Kasey Vidick
Reviewed Date: 6/28/2018
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 0
Yes D
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes 0
Yes D
n/a°C
Yes D
Yes D
Billings, MT B00.735.4489 • Casper, WY BBB.235.0515
Gillette, WY BBB.686.7175 • Helena, MT 877.472.0711
C18060968
Date Received: 6/27/2018
Received by: ens
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 D
Not Present 0
Not Applicable 0
No VOA vials submitted 0
Not Applicable 0
Lab measurement of analytes considered field parameters that require analysis within 15 minutes of sampling such as
pH, Dissolved Oxygen and Residual Chlorine, are qualified as being analyzed outside of recommended holding time.
Solid/soil samples are reported on a wet weight basis (as received) unless specifically indicated. If moisture corrected,
data units are typically noted as -dry. For agricultural and mining soil parameters/characteristics, all samples are dried
and ground prior to sample analysis.
Contact and Corrective Action Comments:
None
Page 31 of 40
,-_/,.,.~
1
-11.t,,~NERGYFUELS RESOURCES
CHAIN OF CUSTODY
Sheet 1 of 1
Samples Shipped to: _E_n ... er....,Q .... Y"""L.;..abo;;;.;;.;.ra.;;;.;t.;..ie ... s ________ Contact: Garrln Palmer
2393 Salt Creek Hwy. Ph: 435 678 2221
Casper WY, 82601 [e-mail]
Chain of Custody/Sampling Analysis Request
Project Samoters Name Samplers Signature
2nd Quarter Air 2018 Garrin Palmer I ~;~.-· a//A.,
Time
Sample ID Date Collected Collected Laboratorv Analvsis Reauested
BHV-1 3/26/18 • 6/25/18 NA U-NAT, TH·230 Ra-226, Pb-210, TH·232
BHV-2 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226. Pb-210, TH-232
BHV-4 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226, Pb-210. TH-232
BHV-5 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226, Pb-210 TH-232
BHV-6 3/26/18 -6/25/18 NA U-NAT, TH-230. Ra-226, Pb-210, TH-232
BHV-7 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226, Pb-210. TH-232
BHV-8 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
Blanks 3/26/18 -6/25/18 NA U-NAT, TH-230, Ra-226, Pb-210, TH-232
l '. \ f;J./1'f ...rQ, _f>.)
Comments: Please send report to Kathy Weinel at [e-mail]
V/17/ Date/Time I\ Relinquished By:(Si=-~
Relinquished By:(Slgnature} Date/Time
-
~ .._ ~-._ I, ;,;v.-• .. ;,-".-.,t t,•r. '• ~ .. , • I
Ii '
1.--:.__ -:.._ __ .. d,:~
Week I Filter I Slan
# Number Date
9415175 3/26/2018
2 9415162 4/2/2018
3 9415159 4/9/2018
4 9415152 4/16/2018
5 9415138 4/23/2018
6 9415135 4/30/2018
7 9415122 5nl2018
8 9415119 5/14/2018
9 9415111 5121/2018
10 9415103 5/2912018
11 9471996 6/412018
12 9471988 6/1112018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
.6H
Stop Start Stop Starting
Date Time Time Manometer
(in. H20)
4/2/2018 89207.02 89375.55 101 l 1.8 4.0
4/9/2018 89375.55 89539.87 9859.2 4.0
4/16/2018 89539.87 89707.99 10087.2 4.0
4/23/2018 89707.99 89879.1 10266.6 4.0
4/30/2018 89879.1 90047.37 10096.2 4.0
5n12018 90047.37 90211.4 9841.8 4.0
5/14/2018 90211.4 90380.37 10138.2 4.0
512 1/2018 90380.37 90547.72 10041.0 4.0
5129/2018 90547.72 90738.98 11475.6 4.0
6/412018 90738.98 90883.96 8698.8 4.0
6/1 112018 90883.96 91050.23 9976.2 4.0
6/1812018 91050.23 91218.96 10123.8 4.0
91387.02 10083.6 4.0
130800.0 ,~~-·
10061.5 4.0
ClOI-nrt c:afculbled IWfll(leS from die 111111 CUlliGII
.6H
Stopping
Manometer
(in.H20)
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: 10/4/2017
Calibration Slope & Intercept:
Orifice S/N: 8091779 r=
4.0 12.2 285.4 616.5 1.10
4.0 10.8 283.9 618.5 1.09
4.0 10.9 284.1 617.7 1.10
4.0 16.8 290.0 618.0 1.11
4.0 12.7 285.8 619.50 1.10
4.0 19.8 293,0 616.71 1.11
4.0 18.1 291.3 616.71 l.l I
4.0 19.3 292.5 617.47 l.l I
4.0 22.0 295.1 618.74 t.12
4.0 23.3 296.4 617.98 l.12
4.0 23.3 296.4 619.50 1.12
4.0 24.8 297.9 618.24 1.12
l"'W"~ --. ~·~)I.~•;' -, -1_ ~:" :'-G.. 14.41 ..... ':I .
4.0 17 8 291.0 617.93923 1.11
m= 1.24782 b= -0.01058
0.93 32.87 9177.3 4.7601
0.93 33.01 9429.9 4.7347
0.93 32.98 9589.0 4.7591
0.92 32.65 9334.5 4.7672
0.93 32.93 9177.0 4.7962
0,92 32.45 9315.0 4.7639
0.92 32.54 9253.1 4.7446
0.92 32.50 10559.8 4.7556
0.92 32.38 7976.7 4.7496
0.91 32.29 9121.9 4.6197
0.92 32.33 9268.5 4.6156
0.91 32.21 9198.3 4.6108
12.00 423.75 120733.5 61.446
0.92 32.60 9287.2 4.727
First Monitoring Quarter 2015
Updated: 7/30/14
5.0006 240.5 0.0262
5.1019 367.2 0 0389 100.1
5.2220 462.9 0.0483 101.9
5.1072 340.0 0.0364 100.2
5.0286 232.4 0.0253 97.6
5.1639 400.0 0.0429 100.6
4.9643 219.7 0.0237 99.6
5.1359 380.3 0.0360 113.8
5.0838 334.2 0.0419 86.3
4.8985 278.8 0.0306 99.0
4.8888 273.2 0.0295 100.4
4.8100 199,2 0.0217 100.0
65.326 3880.1 0.4177
5.025 298.5 0.0321
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.010581
First Monitoring Quarter 2014
BIIV-2 I Period: March 26, 2018 -June 25,2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7 /30/14
Orifice SIN: 8091779
t.H t.H
Week I Filter I Start I Stop I Start I Stop lr¥1 Swting Stopping
# Number Date Date Time Time ; .... : ...... _ Manometer Manometer
(in.H20) (in.H20) --···--J-. -·· -···---
I 9415174 3/26/2018 4/2/2018 99811.85 99981.99 10208.4 4.0 3.5 3.8 17.7 290.9 617,72 1.07 0.89 31.57 9124.9 4.7824 4.9343 151.9 0.0166 101.3
2 9415163 4/2/20] 8 4/9/2016 0 120.78 7246.8 4.0 4.0 4.0 12.2 285-4 616.45 1.10 0.93 32.87 6745.6 4.754] 4.9356 181.5 0.0269 71.9
3 9415158 4/9/2016 4/16/2018 120.78 288.93 10089.0 4.0 4.0 4.0 10 8 283.9 618.49 1.09 0.93 33.01 9431.5 4.7514 5.1902 438.8 0.0465 JOO.I
4 9415151 4/16/2018 4/23/2018 288.93 457.45 10111.2 4.0 4.0 4.0 10.9 284_] 617.72 1.10 0.93 32,98 9443.8 4.7395 5.2443 504.8 0.0535 100.3
5 9415139 4/23/2018 4/30/2018 457.45 627.75 10218.0 4.0 4.0 4.0 16.8 290.0 618.0 l.11 0,92 32.65 9447.1 4.7785 5.2571 478.6 0.0507 101.4
6 9415134 4/30/2018 5/7/2018 627.75 792.34 9875.4 4.0 4.0 4.0 12.7 285.8 619.50 I.LO 0.93 32.93 9208.3 4.7776 5.0141 236.5 0.0257 98.0
7 9415123 5/7/2018 5/14/2018 792.34 961.28 10136.4 4.0 4.0 4.0 19.8 293.0 616.50 l.11 0.92 32.44 9311.8 4.7672 5.1489 381.7 0.0410 100.6
8 9415118 5/14/2018 5/21/2018 961.28 1128.07 10007.4 4.0 4.0 4.0 LS.I 291.3 616.71 l.11 0.92 32.54 9222.2 4.7553 5.0450 289.7 0.0314 99.3
9 9415110 5/21/2018 5/29/2018 1128.07 1319.35 11476.8 4.0 4.0 4.0 19.3 292.5 617.47 1.11 0.92 32.50 10560.9 4.7729 5.2704 497.5 0.0471 113.9
10 9415102 5/29/2018 6/4/2018 1319.35 1464.92 8734.2 4.0 30 3.5 22.0 295.1 618.74 1.04 0.86 30.31 7495.8 4.7883 5.2327 444.4 0.0593 86.6
II 9471995 6/4/2018 6/1 L/2018 1464.92 1630.61 9941.4 4.0 4.0 4.0 23.3 296.4 617.98 l.L2 0.91 32.29 9090.1 4.6055 5.0206 415.1 0.0457 98.6
12 9471987 6/LJ/2018 6/18/2018 1630.61 1799.06 10107.0 4.0 3.5 3.8 23 3 296.4 619.50 1.08 0,89 31.31 8961.5 4.6317 5.0100 378.3 0.0422 1003
13 9471975 6/18/2018 6/25/2018 1799.06 1967.88 10129.2 4,0 4.0 4.0 24.8 297.9 618.24 1.12 0.91 32.21 9239.9 4.6174 4.9745 357.1 0.0386 100.5
Totals 128281.2 14.27 11.88 419.63 117283.4 61.522 66.278 4755.9 0.5252
Averages 9867.8 4.0 3.8 3.9 17.8 291.0 617.92308 l.10 0.91 32.28 9021.8 4.732 5.098 365.8 o.0404 I 97.9
Comments:
Insert weekly flow check values in yellow columns. •a POI
,:mn·columns a,:e cal"tlhllul <l'-crage..< ti:mn,tb.c,IJlCl ,;t.1rio.n.
. ',
•.
.. . ,." ~ ·-.~ , .. --· --... _J
Week I Filter Start
# Number Date
9415173 3n6/2018
2 9415164 4/2/2018
3 9415157 4/9/2018
4 9415150 4/16/2018
5 9415140 4/23/2018
6 9415133 4130/2018
7 9415124 5/7/2018
8 9415117 5/14/2018
9 9415109 5/21/2018
lO 9415101 5/29/2018
11 9471994 6/412018
12 9471986 6/11/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
~H
Stop Stan Stop Starting
Dale Time Time Manometer
(in. H20)
4/2/2018 5364.71 5536.9 10331.4 4.0
4/9/2018 5536.9 5700.22 9799.2 4,0
4/16/2018 5700.22 5844.04 8629.2 4.0
4/23/2018 5844.04 6013.07 10141.8 4.0
4/30/2018 6013.07 6184.43 10281.6 4.0
5/7/2018 6184.43 6347.36 9775.8 3.5
5/14/2018 6347 36 6516.2 10130.4 4.0
5/21/2018 6516.2 6683.5 10038.0 4.0
5/29/2018 6683.5 6876.27 11566.2 4.0
6/4/2018 6876.27 7019,9 8617.8 4.0
6/11/2018 7019.9 7186.2 9978.0 4.0
6/18/2018 7186.2 7355.94 10184.4 4.0
7523.18 10034.4 4.0
.Ml
Stopping
Mnnometer
(in.H20)
3.5
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
5.0
4.0
4.5
4.0
129508.2 ·' _ .. ::--~"....&. ;_ ,.
9962.2 4.0 4.1
4.0 12.2
4.0 10.8
4.0 10.9
4.0 16.8
3.8 12.7
4.0 19.8
4.0 18.l
4.0 19.3
4.5 22.0
4.0 23.3
4.3 23.3
4.0 24.8
iii-:~·-. :--~ ..... , . '
4.0 17.8
Calibration Date: I 0/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
285.4 616.45 I.JO
283.9 618.49 1.09
284.l 617.72 J.10
290.0 617.98 I.JI
285.8 619.50 1.06
293.0 616.71 I.II
291.3 616.71 1.11
292.5 617.47 l.l l
295.1 618.74 1.18
296.4 617.98 1.12
296.4 619.50 1.15
297.9 618.24 1.12 ... ... 'c',. :"': 14.44
291.0 617.93923 I.II
m= 1.24782
0.93 32.87
0.93 33.01
0.93 32.98
0.92 32.65
0.90 31.89
0.92 32.45
0.92 32.54
0.92 32.50
0.97 34.33
0.91 32.29
0.94 33.32
0.91 32.21
12.02 424.62
0 92 32.66
9121.5 4.7452 4.8802
8066.9 4.7487 4.9699
9472.4 4.7929 5.1835
9505.9 4.7918 5.0357
8828.2 4.7702 4.9123
9307.8 4.7862 5.1709
9250.4 4.7783 5.0212
10643.2 4.7343 5.2208
8378.l 4.7563 5.0433
9123.5 4.6262 4.8648
9608.7 4.6054 4.8285
9153.4 4.6140 4.7660
119694.9 61.531 64.778
9207.3 4.733 4.983
First Monitoring Quarter 2014
Updated: 7/30/14
135.0 0.0148 97.2
221.2 0.0274 85.6
390.6 0.0412 100.6
243,9 0.0257 102.0
142.1 0.0161 97.0
384.7 0.0413 100.5
242.9 0.0263 99.6
486.5 0.0457 114.7
287.0 0.0343 85.5
238.6 0.0262 99.0
223.l 0.0232
152.0 0.0166
3247.l 0.3495
249.8 0.0269
! •
' -. ~
I ' . I ' '• lt
la • .. ~ -... ·-· --· "--·
Weeki Filit:r Sran
# Nwnbcr Dale
9415172 3/26/2018
2 9415165 4/2/2018
3 9415156 4/9/2018
4 9415149 4/16/2018
5 9415141 4/23/2018
6 9415132 4/30/2018
7 9415125 5/7/2018
8 9415116 5/14/2018
9 9415108 5/21/2018
10 9472000 5/29/2018
11 9471993 6/4/2018
12 9471985 6/11/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
AH
Stop Swt Stop Starting
Dale Time Time Manometer
(in.H,Ol
4/2/2018 98433.09 98605.67 10354.8 4.0
4/9/2018 98605.67 98769.1 9805.8 4.0
4/16/2018 98769.1 98912.42 8599.2 4.0
4/23/2018 98912.42 99081.8 10162.8 4.0
4/30/2018 99081.8 99252.81 10260.6 4.0
5/7/2018 99252.81 99415.61 9768.0 4.0
5/14/2018 99415.61 99584.55 10136.4 4.0
5/21/2018 99584.55 99751.87 10039.2 4.0
5/29/2018 99751.87 99945.02 11589.0 4.0
6/4/2018 -55 88.63 8617.8 4.0
6/11/2018 88.63 254.95 9979.2 4.0
6/18/2018 254.95 424.32 10162.2 4.0
591.57 10035.0 4.0
129510.0 7; . : .,,.~.
Avera_ges 9962.3 4.0
AH
St0111Mng
Manomeler
(in. H,O)
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
5.0
4.0
4.5
4.0 ·;-~." ,.~
4.1
4.0 17.7
4.0 12.2
4.0 10.8
4.0 10.9
4.0 16.8
4.0 12.7
4.0 19.8
4.0 18.1
4.0 19.3
4.5 22.0
4.0 23,3
4.3 23.3
4.0 24.8
. ·. O:,J,¥~-~ "C
4.1 17.8
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
r-
290.9 617.72 1.11
285.4 616.45 1.10
283.9 618.49 1.09
284.1 617.72 1.10
290.0 618.0 1.11
285.8 619.50 1.10
293.0 616.71 I.II
291.3 616.71 1.11
292.5 617.47 l.11
295.1 618.74 l.18
296.4 617.98 l.12
296.4 619.50 1.15
297.9 618,24 1.12
IG,:-' .\$. ; :.,J' • 7 '· -14.51
291.0 617.93923 l.12
m= 1.24782
0.92 32.59
0.93 32.87
0.93 33.01
0.93 32.98
0.92 32.65
0.93 32.93
0,92 32.45
0.92 32.54
0.92 32.50
0.97 34.33
0.91 32.29
0.94 33.32
0,91 32.21
12.08 426.69
0.93 32.82
9556.9 4.8205
9127.6 4.7730
8038.8 4.7457
9492.0 4.7988
9486,5 4.7923
9108.1 4.7783
9313.4 4.7860
9251.5 4.7791
10664.2 4.7542
8378.1 4.6269
9124.6 4.6207
9587.8 4.6027
9154.0 4.6274
120283.5 61.506
9252.6 4.731
First Monitoring Quarter 2014
Updated: 7/30/14
4.9431 122.6 0.0128 102.7
4.9550 182.0 0.0199 97.3
4.9624 216.7 0.0270 85.3
5.4200 621.2 0.0654 100.8
5,2644 472.1 0.0498 101.8
5.0578 279.5 0.0307 96.9
5.6498 863.8 0,0927 100.6
5.0449 265.8 0.0287 99.6
5.5449 790.7 0.0741 115.0
5.1689 542.0 0.0647 85.5
4,9367 316.0 0.0346 99.0
4.9714 368.7 0.0385
4.8531 225.7 0.0247
66.772 5266.8 0.5637
5.136 405.1 0.0434 I 98.8
Commcnis: A negat:i1te number was insened on 6/4118 to compensate for the time indicator rolling over to zero afte1• 1t reached L 0,000.
ln""1 weekly flow check values in yellow columns.
* Time indicator reset after 10000 on 6/4/ I 8. A negative number was inse1ted on the start time to compensate for the meter rolling over after 10,000.
·-... ,
Week I Filier I Swt I # Number Dute
9415171 3/26/2018
2 9415166 4/2/2018
3 9415155 4/9/2018
4 9415148 4/16/2018
5 9415142 4/23/2018
6 9415131 4/30/2018
7 9415126 5/7/2018
8 9415115 5/14/2018
9 9415107 5/21/2018
10 9471999 5/29/2018
11 9471992 6/4/2018
12 9471984 6/11/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
Ml
Slop I Sun I Stop -Starting 0,11., Time Time Manometer
(io. H20)
4/2/2018 14826.4 14998.61 10332.6 4.0
4/9/2018 14998.61 15161.97 9801.6 4.0
4/16/2018 15161.97 15325.3 9799.8 4.0
4/23/2018 15325.3 15474.75 8967.0 4.0
4/30/2018 15474.75 15646,09 10280.4 4.0
5nt2018 15646.09 15809.1 9780.6 4.0
5/14/2018 15809.1 15977.93 10129.8 4.0
5/21/2018 15977.93 16145.18 10035.0 4.0
5/29/2018 16145,18 16337.95 11566.2 4.0
6/4/2018 16337.95 16481.23 8596.8 4.0
6/11/2018 16481.23 16647.86 9997.8 4.0
6/18/2018 16647.86 16817.59 10183.8 4.0
16984.82 10033.8 4.0
129505.2 r.,:; ..... ._,
9961.9 4.0
Ml
Stopping
Manocne1.,,-
(in. H,0)
4.0 4.0
5.0 4.5
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
3.0 3.5
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
3.5 3.8
4.0 4.0 ~--;._,, ~ .-~~--~
4.0 4.0
17.7
12.2
10.8
10.9
16.8
12.7
19.8
18.1
19.3
22.0
23.3
23.3
24.8
~111.,,,..
17.8
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice S/N: 8091779 r=
290.9 617.72 I.I I
285.4 616.45 1.17
283.9 618.49 1.09
284.1 617.72 1.10
290.0 618.0 1.l 1
285.8 619.50 1.10
293.0 616,71 1.04
291.3 616.71 1.11
292.5 617.47 1.11
295.1 618.74 1.12
296.4 617.98 1.12
296.4 619.50 1.08
297.9 618.24 1.12 -re,......_..,. .... 4:. ' ,. -. I ,..._.• •• • 14.37
291.0 617.93923 I.I I
m= 1.24782
0.92 32.59
0.99 34.85
0.93 33.01
0.93 32.98
0.92 32.65
0.93 32.93
0.86 30.37
0.92 32.54
0.92 32.50
0.92 32.38
0.91 32.29
0.89 31.31
0.91 32.21
11.97 422.63
0.92 32.51
b= -0.01058
9536.5 4.7618
9672.9 4.8016
9161.2 4,7304
8375.2 4.7709
9504.8 4.7950
9119.9 4.7615
8710.8 4.7710
9247.6 4.7410
10643.2 4.7581
7883.2 4.6275
9141.6 4.6370
9029.6 4.6072
9152.9 4.6251
119179.1 61.388
9167.6 4.722
First Monitoring Quarter 2014
Updated: 7/30/14
4.9058 144.0 0.0151 102.5
5.0019 200.3 0.0207 97.2
5.1529 422.5 0.0461 97.2
5.1843 413.4 0.0494 89.0
5.0547 259.7 0.0273 102.0
4.9503 188.8 0.0207 97.0
5.1871 416.1 0.0478 100.5
4.9890 248.0 0.0268 99.6
5.2348 476.7 0.0448 114.7
5.1809 553.4 0.0702 85.3
4.8586 221.6 0.0242 99.2
4.8680 260.8 0.0289 101.0
4.8186 193.5 0.0211
65.387 3998.8 0.4432
5.030 307.6 0.0341 I 98.8
-· ·~.
I --
Week I Filter I Smn
# Numhc:r C>ale
9415170 3/26/2018
2 9415167 4/2/2018
3 9415154 4/9/2018
4 9415147 4/16/2018
5 9415143 4/23/2018
6 9415130 4/30/2018
7 9415127 5/7/2018
8 9415114 5/14/2018
9 9415106 5/21/2018
10 9471998 5/29/2018
11 9471991 6/4/2018
12 9471983 6/11/2018
13 9471979 6/18/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
AH
Stop Start Stop Smnmg
Dare Time Time Maru;,meter
(in. H20)
4/2/2018 7029.67 7197.99 10099.2 4.0
4/9/2018 7197.99 7362.68 9881.4 4.0
4/16/2018 7362.68 7531.21 10111.8 4.0
4/23/2018 7531.21 7702.49 10276.8 4.0
4/30/2018 7702.49 7870.76 10096.2 4.0
5/7/2018 7870.76 8034.72 9837.6 4.0
5/14/2018 8034.72 8203.56 10130.4 4.0
5/21/2018 8203.56 8371.16 10056.0 4.0
5/29/2018 8371.16 8562.88 11503.2 4.0
6/4/2018 8562.88 8707.31 8665.8 4.0
6/11/2018 8707.31 8874.l 10007.4 4.0
6/18/2018 8874.1 9042.15 10083.0 4.0
6/25/2018 9042.15 9210.36 10092.6 4.0
AH
Stopping
Ma11omete
(in. H101 I
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4,0
5,0
4.0
3.5
4.0
Totals 130841.4 ,-,--,,~~
Averages 10064.7 4.0 4.0
4.0
4,0
4.0
4.0
4.0
4.0
4.0
4.0
4,0
4.5
4.0
3.8
4.0
f!!·~"'
4.0
Time Indicator was found broken on 4/10/2017. Replaced Time Indicator on 4/l 0/20 l 7.
lnsen Yi-eekly flow check values tn yellow columns,
r•q
17.7
12.2
10.8
10.9
16.8
12.7
19.8
18.1
19.3
22.0
23.3
23.3
24.8
,~ . .-
17.8
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
-
(lnmH~
290.9 617.72 I.I I
285.4 616.45 1.10
283.9 618.49 1.09
284.1 617.72 1.10
290.0 618.0 I.I I
285.8 619.50 l.10
293.0 616.71 I.I I
291.3 616.71 I.I I
292,5 617.47 I.II
295.1 618.74 l.18
296.4 617.98 l.12
296.4 619.50 1.08
297.9 618.24 1.12
~ ·;; .. ~l·~ : '"e.•-' 14.44
291.0 617.93923 l.11
m= 1.24782
0.92 32.59
0.93 32.87
0.93 33.0l
0.93 32.98
0.92 32,65
0.93 32,93
0.92 32.45
0.92 32.54
0.92 32.50
0.97 34.33
0.91 32.29
0.89 31.31
0.91 32.21
12.03 424.68
0.93 32.67
b= -0.01058
9321.0 4.7563
9198.0 4.7545
9452.9 4.7304
9598.5 4.7881
9334.5 4.7632
9173.0 4.7678
9307.8 4.7790
9266.9 4.7485
10585.2 4.7575
8424.8 4.6187
9150.4 4.6199
8940.2 4.6056
9206.5 4,6267
120959.8 61.316
9304.6 4.717
First Monitoring Quarter 2014
Updated: 7/30/14
4.9349 178.6 0.0192 100.2
5.1375 383.0 0.0416 98.0
5.1529 422.5 0.0447 100.3
5.3151 527.0 0.0549 102.0
5.1605 397.3 0.0426 100.2
4.9394 171.6 0.0187 97.6
5.1598 380.8 0.0409 100.5
4.9326 184.1 0.0199 99.8
5.1172 359.7 0.0340 114.1
5.0739 455.2 0.0540 86.0
4.9746 354.7 0.0388 99.3
4.9403 334.7 0.0374 100.0
4.8501 223.4 0.0243
65.689 4372.6 0.4709
5.053 336.4 0.0362 I 99.8
[. -~\\·~·
I . -.
·--~ ..._..;, i~--.:_.; __ •
Week I Filter Smn
# Numbet D:ile
9415169 3/26/2018
2 9415168 4/2/2018
3 9415153 4/9/2018
4 941514o 4/16/2018
5 9415144 4/23/2018
6 9415129 4/30/2018
7 9415128 5/7/2018
8 9415113 5/14/2018
9 9415105 5/21/2018
10 9471997 5/29/2018
11 9471990 6/412018
12 9471982 6/11/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25 ,2018
AH
Stop Stan Stop Starting
Daie Time Time Manometer
(in. H20)
4/2/2018 13490.24 13685.68 11726.4 4.0
4/9/2018 13685.68 13823.31 8257.8 4.0
4/16/2018 13823.31 13991.79 10108.8 4.0
4/23/2018 13991.79 14163.07 10276.8 4.0
4/30/2018 14163.07 14331.33 10095.6 4.0
5nt2018 14331.33 14495.3 9838.2 4.0
5/14/2018 14495.3 14664.15 10131.0 4.0
5/21/2018 14664.15 14831.63 10048.8 4.0
5/29/2018 14831.63 15022.8 11470.2 4.0
6/4/2018 15022.8 15167.9 8706.0 4.0
6/11/2018 15167.9 15334.ll 9972.6 4.0
6/18/2018 15334.ll 15502.78 10120.2 4.0
15670.94 10089.6 4.0
'otals 130842.0 ·:.-··-(0..,1
,verages 10064.8 4.0
~omments:
lnsen v.,oekl¥ flow check values in yellow colllQIIIS.
Un:en.~~ Cllblaled;a~ (rom die aia 111111011.
AH
Stopping
Manometer
(in.H20)
4.0
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
5.0 4.5
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
3.5 3.8
3-5 3.8
l·...; .--;~JI,;: .~ .. ;...
4.0 4.0
12.2
10.8
10.9
16.8
12.7
19.8
18.1
19.3
22.0
23.3
23.3
24.8
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
285.4 616.45 1.10
283-9 618.49 1.09
284.1 617.72 1.10
290.0 618.0 Lil
285,8 619.50 1.10
293.0 616.71 1.18
291.3 616.71 I.I I
292.5 617.47 1.11
295.l 618.74 l.12
296.4 617.98 1.12
296.4 619.50 1.08
297.9 618.24 1.09
~-~-B:' a .;. ·,.:i, -...-,~ 14.40
17.8 291.0 617.93923 I.I J
m= 1.24782
0.93 32.87
0.93 33.0l
0.93 32.98
0.92 32.65
0.93 32.93
0.97 34.40
0.92 32.54
0.92 32.50
0.92 32.38
0.91 32.29
0.89 31.31
0.88 31-20
12.00 423.67
0.92 32.59
b= -0.01058
7686.7 4.7600
9450.0 4.7403
9598.5 4.8000
9333.9 4.7721
9173.6 4.7558
9868.7 4.7662
9260.3 4.7590
10554.8 4.7510
7983.3 4.6248
9ll8.6 4.6058
8973.2 4.6088
8913.7 4.5927
120738.3 61.297
9287.6 4.715
First Monitoring Quarter 2014
Updated: 7/30/14
4.8929 132.9 0.0173 81.9
5.0397 299.4 0.0317 100.3
5.2709 470.9 0.0491 102.0
5.0523 280.2 0.0300 100.2
4.8764 120.6 0.0131 97.6
5.0658 299.6 0.0304 100.5
4.9126 153.6 0.0166 99.7
5.0453 294.3 0.0279 113.8
4.9146 289.8 0.0363 86.4
4.7792 173.4 0.0190 98.9
4.8022 193.4 0.0216 100.4
4.7061 113.4 0.0127
64.205 2908.8 0.3137
4.939 223.8 0.0241
. .J... ~,. ; .
~.-' .
: _· .
Period: March 26, 2018 -June
25 2018
Week Filter
# Number
Start Stop Net Date Date
1 9415161 26-Mar-18 02-A r-18 4.7536
2 9415160 02-Apr-18 09-Apr-18 4.7508
3 9415145 09-Apr-18 16-A r-18 4.7884
4 9415137 16-A r-18 23-A r-18 4.7779
5 9415136 23-Apr-18 30-Apr-18 4.7689
6 9415121 30-Apr-18 07-May-18 4.7750
7 9415120 07-Ma -18 14-Ma -18 4.7822
8 9415112 14-May-18 21-May-18 4.7734
9 9415104 21-Ma -18 29-Ma -18 4.7369
10 9471989 29-May-18 04-Jun-18 4.6103
11 9471981 04-Jun-18 11-Jun-18 4.6106
12 9471973 11-Jun-18 18-Jun-18 4.5711
13 9471972 18-Jun-18 25-Jun-18 4.6257
Totals
ATTACHMENT D
AIR PARTICULATE LOADING GRAPHS AND SUPPORTING DATA
0 0 0 ~ I-'
0 0 0 I-' 0 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 to
I 1/5/2011 < I I-'
4/5/2011 )>
+ 7/5/2011 -· ""'I
to 10/5/2011 ~
I ,...
< OJ I 1/5/2012 ,... N -·
+
4/5/2012 0 ::::,
7/5/2012 "'tJ to I 10/5/2012 OJ < ""'I I .I>, ,...
1/5/2013 -· n
+ 4/5/2013 C -OJ to 7/5/2013 ,... I tD < I 10/5/2013 V, r-
+
1/5/2014 0
OJ
4/5/2014 a.
to -· I 7/5/2014 ::::, < OQ I CTI 10/5/2014 -
+ 1/5/2015 3
OQ
to 4/5/2015 ........
I 3 < 7/5/2015 I w '-I -f 10/5/2015
1/5/2016
to I 4/5/2016 < I 00 7/5/2016
10/5/2016
1/5/2017
4/5/2017
7/5/2017
10/5/2017
1/5/2018
4/5/2018
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
10/5/2010
1/5/2011
4/5/2011
7/5/2011 D:J
:I: 10/5/2011 < I 1/5/2012 ~
4/5/2012 ""CJ A> 7/5/2012 .., ,... -· 10/5/2012 n
C 1/5/2013 -A>
+ 4/5/2013 ,...
tD CD 7/5/2013 r-I
0 < r 10/5/2013 A> ....
1/5/2014 Q. -· :::J 4/5/2014 (7Q
7/5/2014 -3 10/5/2014 (7Q
1/5/2015 .......
3 4/5/2015 w -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
1/5/2018
4/5/2018
0 !=> I-' 0 0 0 0 I-' 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 c::,
:::c 10/5/2011 < I 1/5/2012 N
4/5/2012 "'C QJ 7/5/2012 ""I ,... -· 10/5/2012 n
C 1/5/2013 -QJ + 4/5/2013 ,...
tD
CJ 7/5/2013 r-I
0 < I 10/5/2013 QJ N
1/5/2014 Q. -· ::::J 4/5/2014 (1Q
7/5/2014 -3 10/5/2014 (1Q
1/5/2015 .......
3 4/5/2015 w -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
1/5/2018
4/5/2018
0 0 !=::> I-' 0 0 0 0 0 I-' 0 0 0 0 I-' 0 0 0 I-' 0 0 0 I-' 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 O:J :::c 10/5/2011 < I 1/5/2012 ~
4/5/2012 "'C DJ 7/5/2012 ""I "' -· 10/5/2012 n
C 1/5/2013 -DJ
+ 4/5/2013 "' tD
CJ 7/5/2013 r-I
0 < I 10/5/2013 DJ .i:,.
1/5/2014 Q. -:::::s 4/5/2014 (1Q
7/5/2014 -3 10/5/2014 (1Q
1/5/2015 ........
3 4/5/2015 w -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
1/5/2018
4/5/2018
0 0 0 ....
C) C) C) ....
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 CJ :::c 10/5/2011 < I 1/5/2012 U1
4/5/2012 "'C QJ 7/5/2012 .., ,... -· 10/5/2012 n
C 1/5/2013 -QJ
+ 4/5/2013 ,...
tD a, 7/5/2013 r-:::c
0 < 10/5/2013 I
QJ u,
1/5/2014 a. -· ::::J 4/5/2014 (7Q
7/5/2014 -3 10/5/2014 -(7Q
1/5/2015 ........
3 4/5/2015 -w -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
1/5/2018
4/5/2018
0 0 0 I-'
0 0 I-' 0 0 0 0 I-' 0 0 I-' 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 en
4/5/2012 ""C QJ 7/5/2012 ""I ~ -· 10/5/2012 n
C 1/5/2013 -QJ
+ 4/5/2013 ~
tD CJ 7/5/2013 r-I
0 < I 10/5/2013 QJ cr,
1/5/2014 Q. -· ::::s 4/5/2014 OQ
7/5/2014 -3 10/5/2014 OQ
1/5/2015 ........
3 4/5/2015 w -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
1/5/2018
4/5/2018
0 0 0
0 0 !=' .... .... .... ....
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
12/5/2015 0:,
1/5/2016 :::c
2/5/2016 < I
3/5/2016 ......
4/5/2016 "'ti QJ
5/5/2016 ""I ,... -· 6/5/2016 n
C
+
7/5/2016 -
8/5/2016
QJ ,...
tD
CJ 9/5/2016 :r: r-< 10/5/2016 0 .:.i QJ
11/5/2016 Q. -· 12/5/2016 :::::s
1/5/2017 (1Q -2/5/2017 3
3/5/2017 (1Q ........
4/5/2017 3
5/5/2017 w -6/5/2017
7/5/2017
8/5/2017
9/5/2017
10/5/2017
11/5/2017
12/5/2017
1/5/2018
2/5/2018
3/5/2018
4/5/2018
5/5/2018
6/5/2018
0 0 0
0 0 0
0 0 0 !=> I-' I-' I-' I-' I-'
9/29/2014
11/29/2014
I ~
1/29/2015
3/29/2015
5/29/2015
7/29/2015
9/29/2015 ~ ~ I 0,
:I:
11/29/2015 1 ~ ...z:J~ I < I
00
1/29/2016 1 ~I I "tJ a,
""' ~
3/29/2016 1 .. r ~ I -· n
C -
+ 5/29/2016 1 It a,
~
tD OJ I 7/29/2016 r-< 0 00 a,
9/29/2016 1 ~ I C. -· ::::s
(1Q
11/29/2016 1 .... . • r=-" I -3
1/29/2017 1 1 a. -I "I (1Q
~C.: .........
3
3/29/2017 1 ~ I
w -
5/29/2017
7/29/2017
9/29/2017
11/29/2017
1/29/2018
3/29/2018
5/29/2018
~-~-~ ~_: ~ ', ~-7'~<:•1 u-_ -~ --~~-~-~~
Week I filter I Stan
# Number Date
9471079 12/26/2017
2 9471071 1/2/2018
3 9471058 1/8/2018
4 9471055 1/15/2018
5 9471042 1/22/2018
6 9471039 1/29/2018
7 9471026 2/5/2018
8 9471023 2/12/2018
9 9471010 2/20/2018
10 9471007 2/26/2018
11 9415194 3/5/2018
12 9415191 3/12/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
6H
Stop Start Stop Starting
Date Time Time Manometer
(in.H20)
1/2/2018 87046.59 87213.92 10039,8 4.0
1/8/2018 87213.92 8736 I.I 8830.8 4.0
1/15/2018 87361.1 87525.36 9855.6 4.0
1/22/2018 87525.36 87692.98 10057.2 4,0
1/29/2018 87692.98 87861.45 10108.2 4.0
2/5/2018 87861.45 88029.99 10112.4 4.0
2/12/2018 88029.99 88201.97 10318.8 4.0
2/20/2018 88201.97 88393.12 11469.0 4.0
2/26/2018 88393.12 88537.4 8656.8 4,0
3/5/2018 88537.4 88701.7 9858.0 4.0
3/12/2018 88701.7 88867.56 9951.6 4.0
3/19/2018 88867.56 89036.68 10147.2 4.0
89207.02 10220.4 4.0
6H
Stopping
Manometer
(in.H20)
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
129625.8 ,· ...... /·~ L:
9971.2 4.0 4.0
Insert weekly flow check values in yellow columns.
iGR,,m, colllJIIIIS an, calculllled 11\'llfflsi:s fl:om 11te,mcr station.
10/4/2017
m= 1.24782
4.0 1.0 274.l 623.1 1.07 0.96 33.73
4.0 2.6 275.8 621.0 1.08 0.95 33.57
4.0 0.6 273.8 620.3 1.07 0.95 33.67
4.0 -0,7 272.5 623.3 1.07 0.96 33.84
4.0 6.5 279.7 621 .03 1.08 0,94 33.33
4.0 3.9 277.0 619.25 1.08 0.95 33.45
4.0 2.7 275.8 616.96 1.08 0.95 33.46
4.0 -3.3 269.9 617.72 1.07 0.96 33.85
4.0 3.8 277.0 617.22 1.08 0.95 33.39
4.0 5.4 278.5 620.01 1.08 0.95 33.38
4.0 6.1 279.3 616.45 1.09 0.94 33.23
4.0 6.6 279 8 616.45 1.09 0.94 33.20
14.02 12.34 435.70
4.0 2.9 276.1 619.59923 1.08 0.95 33.52
8434.0 4.6193
9368.9 4.6431
9589.7 4.6093
9685.6 4.6404
9545.2 4.6320
9772.6 4.6220
10865.6 4.6482
8296.8 4.6507
9321.4 4.6114
9405.0 4.6850
9549.l 4.7220
9609.2 4.7409
122995.7 60.457
9461.2 4.651
First Monitoring Quarter 2015
Updated: 7/30/14
4.7165 97,2 0.0115 87.6
4.6999 56.8 0.0061 97.8
4.6991 89.8 0.0094 99.8
4.7139 73.5 0.0076 100.3
4.7341 102.1 0.0107 100.3
4.7430 121.0 0.0124 102.4
4.8874 239.2 0.0220 113.8
4.7243 73.6 0.0089 85.9
4.8024 191.0 0.0205 97.8
4.8044 I 19.4 0.0127 98.7
4.9181 196.l 0.0205 100.7
4.8603 119.4 0.0124 101.4
62.042 1584.5 0.1657
4.772 121.9 0.0121 I 98.9
wr.c-~,~ ~ ::--<:: ..• -o:;,;
.. . ·. '~ . i~ · .,.-,;'." ·1
,~~~---.!.-i..,.!! ... l .. r1
Weeki Filter Stan
# Number Date
9471078 12/26/2017
2 9471070 1/2/2018
3 9471059 l/8/2018
4 9471054 1/15/2018
5 9471043 1/22/2018
6 9471038 1/29/2018
7 9471027 2/5/2018
8 9471022 2/12/2018
9 9471011 2/20/2018
10 9471007 2/26/2018
11 9415195 3/5/2018
12 9415190 3/12/2018
13 9415179 3/19/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
6H
Stop Stan Stop Starting
Date Time Time Manometer
(in.H20)
1/2/2018 97653.94 97823.12 10150.8 4.0
1/8/2018 97823.12 97966.49 8602.2 4.0
1/15/2018 97966.49 98132.69 9972 4.0
1/22/2018 98132.69 98301.24 10113 4.0
1/29/2018 98301.24 98469.47 10093.8 4.0
2/5/2018 98469.47 98638 10111.8 4.0
2/12/2018 98638 98809.19 10271.4 4.0
2/20/2018 98809.19 99000..61 11485.2 4.0
2/26/2018 99000.61 99141.19 8434.8 4.0
3/5/2018 99141.19 99309,14 10077 4.0
3/12/2018 99309.14 99474.91 9946.2 4.0
3/19/2018 99474.91 99644,26 10161 4.0
3/26/2018 99644.26 99811.85 10055.4 4.0
129474.6
9959.6 4.0
6H
Stopping
Manometer
(in.H10)
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: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779 ..am===::===,aiiiiiiiii:iiii"'"
1.0 274.1 623,06 1,07
2.6 275.8 621.03 1.08
0.6 273.8 620.26 1.07
-0.7 272.5 623.3 1.07
6.5 279.7 621.03 1.08
3.9 277.0 619.25 1.08
2.7 275.8 616.96 1.08
-3.3 269.9 617.72 1.07
3.8 277.0 617.22 1.08
5.4 278.5 620.01 1.08
6.1 279.3 6 I 6.45 1.09
6.6 279.8 616.45 1.09
--14.02
2.9 276.1 619.59923 1.08
m= 1.24782
0.96 33.73
0.95 33 .57
0.95 33.67
0.96 33 .84
0.94 33.33
0.95 33.45
0.95 33.46
0.96 33.85
0.95 33.39
0.95 33.38
0.94 33.23
0.94 33.20
12.34 435.70
0.95 33.52
8215.7 4.6370
9479.6 4.6173
9642.9 4.6278
9671.8 4.6328
9544.7 4.6282
9727.7 4,6495
10880.9 4.6341
8084.0 4,6319
9528.5 4.6214
9399.9 4.6741
9562.l 4.7135
9454.0 4,7148
122850.0 60.423
9450.0 4.648
First Monitoring Quarter 2014
Updated: 7/30/14
4.7913 154.3 0.0188 85.3
4.7127 95.4 0.0101 98.9
4.7213 93.5 0.0097 100.3
4.7577 124.9 0.0129 100.1
4.8698 241.6 0.0253 100.3
4.8587 209.2 0.0215 101.9
4.8566 222.5 0.0204 I 13.9
4.7003 68.4 0.0085 83.7
4.8292 207.8 0.0218 100.0
4.8346 160.5 0.0171 98.7
4.8578 144.3 0.0151 100.8
4.8066 91.8 0.0097
62.377 1954.2 0.2054
4.798 150.3 o.0158 I 98.8
. ' -
'
:"-::ZiC1.:.!m ~ ,•,
0 v'~
Week Filter Stan
# Number Date
1 9471077 L2/26/2017
2 9471069 1/2/2018
3 9471060 1/812018
4 9471053 1115/2018
5 9471044 1122/2018
6 9471037 1/2912018
7 9471028 2/5/2018
8 947[021 2/12/2018
9 94710[2 2/2012018
10 9471005 212612018
11 9415196 3/5/2018
12 9415190 3/L212018
Comments:
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
11.H
Stop Siart Stop Starting
Date Time Time Manometer
(in.H,O)
1/212018 3209.98 3380.92 10256.4 4.0
11812018 3380.92 3523.35 8545.8 4.0
1/15/2018 3523.35 3690.03 10000.8 4.0
1122/2018 3690.03 3854.64 9876.6 4.0
1/29/2018 3854.64 4021.94 10038.0 4.0
2/512018 4021.94 4190.09 10089.0 4.5
2/1212018 4L90.09 4362.04 L03L7.0 4.0
2/20/2018 436204 4554.39 11541.0 4.0
212612018 4554.39 4698.77 8662.8 4.0
3/5/2018 4698.77 4861.59 9769.2 4.0
3/12/2018 4861.59 5027.79 9972.0 4,0
3/[9/2018 5027,79 5198.03 10214.4 4.0
5364.71 10000.8 4,0
Totals [29283.8 : -·
Averages l 9944.9 4.0
Insert weekly flow check values in yellow columns.
l("mcn ~~ $10 ca'-"l"ad IMf:ipP ~,Ille mc1 s&_l!jiaJ1
II.If
Stopping
Manomete,
(in.H,O)
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: 10/4/2017
m= 1.24782
4.0 1.0 274.1 623.06 1.07 0.96 33.73
4.0 2.6 275.8 621.03 LOS 0.95 33.57
4.0 0.6 273.8 620.26 1.07 0.95 33.67
4.0 -0.7 272.5 623.31 1.07 0.96 33,84
4.3 6.5 279.7 62L.03 1.12 0.97 34.35
4.0 3.9 277.0 619.25 1.08 0.95 33.45
4.0 2.7 275.8 616.96 1.08 0.95 33.46
4.0 -3.3 269.9 617.72 1.07 0.96 33.85
4.0 3.8 277,0 617.72 1.08 0.95 33.41
4,0 5.4 278.5 620.01 1.08 0.95 33.38
4,0 6.1 279.3 616.45 L.09 0.94 33.23
4.0 6.6 279.8 616.45 1.09 0.94 33.20
~ .> 14.05 . -I 12.37 436.73
4.0 2.9 276.1 619.63769 1.08 0.95 J 33.59
8L61.8 4,6020 4.6687
9506.9 4.6035 4.6530
9417.5 4,6262 4.7049
9618.3 4.6439 4.6927
9813.9 4,6296 4.7054
9770.9 4.6441 4.7170
10933.8 4.6376 4.8386
8302.5 4.6398 4.6977
9241.2 4.6128 4.7266
9424.3 4.6979 4.7499
9612.4 4.7257 4.8298
9402.7 4.7503 4.8238
122965.0 60.439 61.519
9458.8 4.649 4.732
First Monitoring Quarter 2014
Updated: 7/30/14
66.7 0.0082
49.5 0.0052 99.2
78.7 0.0084 98.0
48.8 0.0051 99.6
75.8 0.0077 100.J
72.9 0,0075 102.4
201.0 0.0184 114.5
57.9 0,0070 85,9
113.8 0.0123 96.9
52.0 0.0055 98.9
104.1 0.0108 101.3
73.5 0.0078
1079.7 0.1125
83.1 o.oos1 I 98.7
~--.=-,·
Week Filter Start
# Number Date
I 9471076 12/26/2017
2 9471068 1/2/2018
3 9471061 l/8/2018
4 9471052 1/15/2018
5 9471045 1/22/2018
6 9471036 1/29/2018
7 9471029 2/5/2018
8 9471020 211212018
9 9471013 2/2012018
10 9471004 2/2612018
II 9415197 31512018
12 9415188 3112/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
6H
Stop Start Stop Starting
Date Time Time Manometer
(in.H,O)
1/2/2018 96298.05 96469.4 10281 4.0
I /8/2018 96469.4 96611.45 8523.0 4.0
1/15/2018 %611.45 96778.15 10002.0 4.0
1/22/2018 96778.15 96943.22 9904.2 4.0
1/29/2018 96943.22 97095.97 9165.0 4.0
21512018 97095.97 97261.lS 9910.8 4.0
2/12/2018 97261.15 97430.41 10155.6 4.0
2120/2018 97430.41 97622.78 11542.2 4.0
2/26/2018 97622.78 97767.51 8683.8 4.0
31512018 97767.51 97929.97 9747.6 4.0
3/1212018 97929.97 98096.17 9972.0 4.0
3119/2018 98096.17 98266.74 10234.2 4.0
98433.09 9981 4.0
6H
Stopping
Manomete,
(in.H,O)
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
128102.4 ... ; I:' -__ ,
9854.0 4.0 4.0
:mea columlli:lll\lcalcillatot n~f,:om the~ uacfol1
4.0 1.0
4.0 2.6
4.0 06
4.0 -0.7
4.0 6.5
4.0 3.9
4.0 2.7
4.0 -3.3
4.0 3.8
4.0 5.4
4.0 6.1
4.0 6.6
' f. I: ..
4.0 2.9
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
274.1 623.06 L.07
275.8 621.03 1.08
273.8 620,26 1.07
272.5 623.3 1.07
279.7 621.03 L.08
277.0 619.25 1.08
275.8 616.96 LOS
269.9 617.72 1.07
277.0 617.22 I.OS
278.5 620.01 1.08
279.3 616.45 1.09
279.8 616.45 1.09
14.02
276.l 619.59923 1.08
m= 1.24782
0.96 33.73
0.95 33.57
0.95 33.67
0.96 33.84
0.94 33.33
0.95 33.45
0.95 33.46
0.96 33.85
0.95 33.39
0.95 33.38
0.94 33,23
0.94 33.20
12.34 435.70
0.95 33.52
8140.0 4.6139
9508.1 4.6154
9443.8 4.6434
8781.8 4.6390
9354.9 4.6239
9618.0 4.6190
10934.9 4.6486
8322.7 4.6208
9217.0 4.6213
9424.3 4.8165
9631.0 4.7210
9384.1 4.7150
121542.8 60.51 I
9349.4 4.655
First Monitoring Quarter 2ff! 4
Updated: 7/30/14
4.7309 117.0 0.0144
4.6765 61.l 0.0064 99.2
4.7516 !08.2 0.0115 98.3
4.7404 101.4 0.0115 90.9
4.7323 108.4 0.0116 98.3
4.7435 124,5 0.0129 100.8
4.8483 199.7 0.0183 114.5
4.6779 57.l 0.0069 86.l
4.7435 122.2 0.0133 96.7
4.8874 70.9 0.0075 98.9
4.8530 132,0 0.0137 101.5
4.7968 81.8 0.0087
61.911 1400.5 0.1485
4.762 107.7 0.0114 I 97.8
....-..... ~.· ·-~~ I ~·-~-;\.;-...... ,·, i:~--;-1---=-~
:-. -· ,,. '(":: -.·. \
-.:,.~~~·.::.:~-~
Week i Filter Start
# Number Dn1e
I 9471075 12/26/2017
2 9471067 1/2/2018
3 9471062 1/8/2018
4 9471051 1/15/2018
5 9471046 1/22/2018
6 9471035 1/29/2018
7 9471030 2/5/2018
8 9471019 2/12/2018
9 9471014 2/20/2018
IO 9471003 2/26/2018
11 9415198 3/5/2018
12 9415187 3/12/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
llli
Stop Start Stop Starting
Date Time Time Manometer
(in.H20)
1/2/2018 12671.71 12842.64 10255.8 4.0
1/8/2018 12842.64 12985.03 8543.4 4.0
1/15/2018 12985.03 13151.7 10000.2 4.0
1/22/2018 13151.7 13316.44 9884.4 4.0
1/29/2018 13316.44 13483.62 10030.8 4.0
2/5/2018 13483.62 13651.87 10095 4.0
2/12/2018 13651.87 13823.77 10314 4.0
2/20/2018 13823.77 14016.07 11538 4.0
2/26/2018 14016.07 14160.48 8664.6 3.0
3/5/2018 14160.48 14323.29 9768.6 4.0
3/12/2018 14323.29 14489.48 9971.4 4,0
3/19/2018 14489.48 14659.72 10214.4 4.0
14826.4 10000.8 4.0 .
129281.4 •
9944.7 3.9
llli
Stopping
Manometer
(in.H20)
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: 10/4/2017
Calibration Slope & Intercept: m= 1.24782
Orifice SIN: 8091779
:m
4.0 1.0 274.1 623.06 1.07 0.96 33.73
4.0 2.6 275.8 621.03 1.08 0.95 33.57
4.0 0.6 273.8 620.26 1.07 0.95 33.67
4.0 -0.7 272.5 623.3 1.07 0.96 33.84
4.0 6.5 279.7 621.03 1.08 0.94 33.33
4.0 3.9 277.0 619.25 1.08 0.95 33.45
4.0 2.7 275,8 616,96 1.08 0.95 33.46
3.5 -3.3 269.9 617.72 1.00 0.90 31.68
4.0 3.8 277.0 617.22 1.08 0.95 33.39
4.0 5.4 278.5 620.01 1.08 0.95 33.38
4.0 6.1 279.3 616.45 1.09 0.94 33.23
4.0 6.6 279.8 616.45 1.09 0.94 33.20 . . .. ,. i 13.95 12.28 433.53
4.0 2.9 276.1 619.59923 1.07 0.94 33.35
b= -0.01058
8159.5 4.5935
9506.4 4.6189
9424.9 4.6089
9611.4 4.6146
9528.8 4.6276
9768.0 4.6564
10930.9 4.6343
7772.2 4.6460
9236.9 4.6221
9423.7 4.7976
9612.4 4.7437
9402.7 4.7359
122136.0 60.518
9395.1 4.655
First Monitoring Quarter 2014
Updated: 7/30/14
4.7009 107.4 0.0132
4.6871 68-2 0.0072 99.2
4.6889 80.0 0.0085 98.1
4.6750 60.4 0.0063 99.5
4.7368 109.2 0.0115 JOO.I
4.9149 258.5 0.0265 102.3
4.8326 198.3 0.0181 I 14.5
4.6884 42.4 0.0055 86.0
4.7824 160.3 0.0174 96.9
4.8866 89.0 0.0094 98.9
4.9467 203.0 0.0211 101.3
4.8405 104.6 0.0111
62.107 1589.2 0.1667
4.777 122.2 o 0128 I 98.7
i~-~J r,. .. ; .· rl·.,·'-I
~i~~;.J:~~
Week I Filter I Stan
# Number Date
1 9471074 12/26/2017
2 9471066 1/2/2018
3 9471063 1/8/2018
4 9471050 1/15/2018
5 9471047 1/22/2018
6 9471034 1/29/2018
7 9471031 2/5/2018
8 9471018 2/12/2018
9 9471015 2/20/2018
10 9471002 2/26/2018
II 9415199 3/5/2018
12 9415186 3/12/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
611
Stop Stan Stop Starting
Date Time Time Manometer
(in.H20)
1/2/2018 4868.92 5036.86 10076.4 4.0
1/8/2018 5036.86 5183.37 8790.6 4.0
1/15/2018 5183.37 5348.24 9892.2 4.0
1/22/2018 5348.24 5515.24 10020.0 4.0
1/29/2018 551524 5683.93 10121.4 4.0
2/5/2018 5683.93 5852.27 10100.4 4.5
2/12/2018 5852.27 6024.39 10327.2 4.0
2/20/2018 6024.39 6215.6 11472.6 4.0
2/26/2018 6215.6 6359.77 8650.2 4.0
3/5/2018 6359.77 6523.2 9805.8 4.0
3/12/2018 6523.2 6690.2 10020.0 4.0
3/19/2018 6690.2 6859.31 10146.6 4.0
7029.67 10221.6 4.0
129645.0 1.-. ::·,. ~
9972.7 4.0
Qt=a collllim$ :n ca1C11J111eil ._.~ Imm the mcc 'uli<111.
611
Stopping
Manometer
(in.H20)
4.0
4.0 4.0
4.0 4.0
4.0 4.0
4.0 4.0
4.0 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 _;.;c ., ·.· :_:'",ii
4.0 4.0
1.0
2.6
0.6
-0.7
6.5
3.9
2.7
-3.3
3.8
5.4
6.1
6.6
_-,:, :•
2.9
Calibration Date: 10/4/2017
Calibration Slope & Intercept: m= 1.24782 b= -0.01058
First Monitoring Quarter 2014
Updated: 7/30/14
Orifice SIN: 8091779
-...._-----:-:----,J.----.-.,y-,....--.-~r~ -. ~-----,------.--· ---=---~-;--:..11
Pp •' ,-•.·-·/ ·~1-"~ ·r: ... ·~ • •I .• • J.• •• 11 7:;& ,_· __ ":,~_ ;_.->, .-· .·-·:·' .-::._ ·: ->--_·1: ·.. : :_ i .. ,: _ ~--··:·: : .. _.\ .. I
m-
622.04 1.08 0.95 33.60 9587.5 4.6087 .7263 117.6 0.0123 100.0
274.1 623.06 1.07 0.96 33.73 8395.6 4.6204 4.7466 126.2 0.0150 87.2
275.8 621 03 1.08 0.95 33.57 9403.7 4.6405 4.7136 73.l 0.0078 98.1
273.8 620.26 1.07 0.95 33.67 9554,2 4,5975 4.7250 127.5 0.0133 99.4
272.5 623.3 1.07 0.96 33.84 9698.2 4.6210 4.7313 110.3 0.0114 100.4
279.7 621.03 1.12 0.97 34.35 9825.0 4.6376 4.7774 139.8 0.0142 100.2
277.0 619.25 1.08 0.95 33.45 9780.5 4.6273 4.8260 198.7 0.0203 102.5
275.8 616.96 1.08 0.95 33.46 10869.0 4.6250 4.9379 312.9 0.0288 113.8
269,9 617.72 1.07 0.96 33.85 8290.5 4.6260 4.6994 73.4 0.0089 85.8
277.0 617.22 1.08 0.95 33.39 9272.0 4.6053 4.8577 252.4 0.0272 97.3
278.5 620.01 J.08 0.95 33.38 9469.6 4.7681 4.8755 107.4 0.0113 99.4
279.3 616.45 1.09 0.94 33.23 9548.6 4.7356 4.9071 171.5 0.0180 100.7
279.8 616.45 1.09 0.94 33.20 9610.3 4.6969 4.8045 107.6 0.0112 -. -, 14.05 12.37 436.72 123304.8 60.410 62.328 1918.4 0.1997
276.1 619.59923 1.08 0.95 33.59 9485.0 4.647 I 4.794 I 147.6 0.0154 I 98.9
~~""'-·.~:~ ~~··· .. ':,~-' -~-, .. -:..,__ ., ... .-1 :::-:a..:-.:..:·~~
Week Filter Start
# Number Date
1 9471073 12/26/2017
2 9471065 1/2/2018
3 9471064 1/8/2018
4 9471049 1/15/2018
5 9471048 1/22/2018
6 9471033 1/29/2018
7 9471032 2/5/2018
8 9471017 2/12/2018
9 9471016 2/20/2018
10 9471001 2/26/2018
II 9415200 3/5/2018
12 9415185 3/12/2018
Energy Fuels Resources -White Mesa Mill
Period: December 26, 2017 -March 26, 2018
6H
Stop Start Stop Starting
Date Time Time Manometer
(in.H20)
1/2/2018 11330.02 11497.41 10043.4 4.0
1/8/2018 11497.41 11644.3 8813.4 4.0
1/15/2018 11644.3 11808.7 9864,0 4.0
1/22/2018 11808.7 11976.24 10052.4 4.0
1/29/2018 11976.24 12144.71 10108.2 4.0
2/5/2018 12144,71 12313.03 10099.2 4.0
2/12/2018 12313.03 12485.07 10322.4 4.0
2/20/2018 12485.07 12676.24 11470.2 4.0
2/26/2018 12676.24 12820.44 8652.0 4.0
3/5/2018 12820.44 12984.78 9860.4 4.0
3/12/2018 12984.78 13150.8 9961.2 4.0
3/19/2018 13150.8 13319.9 10146.0 4.0
1 13 ! 9415184 ! 311912018 I 312612018 1 13490.24 10220.4 4.0
6H
Stopping
Manometer
(in. H20)
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
Ou:1 129613.2 -... ~ .. -f. J :...~ >=J
Averages l 9970.2 4.0 4.0
Comments:
Insert weekly flow check values in yellow columns.
t<JiecA colilfflris on, c'ilcuhucdJave~ From 1be m111 <UillOO.
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 8091779
a &a, * w
4.0 1.0 274.1 623.06 1.07
4.0 2.6 275.8 621.03 1.08
4.0 0.6 273.8 620.26 1.07
4.0 -0.7 272.5 623.3 1.07
4.0 6.5 279.7 621.03 1.08
4.0 3.9 277.0 619.25 1.08
4.0 2.7 275.8 616.96 1.08
4.0 -3.3 269.9 617.72 1.07
4.0 3.8 277.0 617.22 1.08
4.0 5.4 278.5 620.0l 1.08
4.0 6.1 279.3 616.45 1.09
4.0 6.6 279.8 616.45 1.09
-~ . .\ .. • ,.·-.--. .-'. 4 -14.02 .• ...... -. '
4.0 2.9 276.1 619.59923 1.08
m= 1.24782 b= -0.01058
0.96 33.73 8417.4 4.6189
0.95 33.57 9376.9 4.6148
0.95 33.67 9585.1 4.6118
0.96 33.84 9685.6 4.6085
0.94 33.33 9532.8 4.6016
0.95 33.45 9776.0 4.6557
0.95 33.46 10866.7 4.6530
0.96 33.85 8292.2 4.6471
0.95 33.39 9323.7 4.5876
0.95 33.38 9414.1 4.7643
0.94 33.23 9548.0 4,7267
0.94 33.20 9609.2 4,7246
12.34 435.70 122983.6 60.436
0.95 33.52 9460.3 4.649
First Monitoring Quarter 2014
Updated: 7/30/14
4.6995 80.6 0.0096 87.4
4.6619 47.1 0,0050 97.9
4.6674 55.6 0.0058 99,7
4.6496 41.1 0.0042 100.3
4.6651 63.5 0.0067 100.2
4.7399 84.2 0.0086 102.4
4.8208 167.8 0.0154 113.8
4.7407 93.6 0.0113 85.8
4.7784 190.8 0.0205 97.8
4.8339 69.6 0.0074 98.8
4.8502 123.5 0.0129 100.7
4,8452 120.6 0.0126 IOL4
61.658 1221.4 0. 1287 l '-.t -
4.743 94.0 0.0099 I 98.9
~ ~1 ';I ~~": •. '-
1-. '\ -~-. . . -"~
• ); t • j I '~ ; 1' • ' "'
~!:-~·~~ .... ' .''-\;--....
Week Filter
# Number
1 9471072
2 9471057
3 9471056
4 9471041
5 9471040
6 9471025
7 9471024
8 9471009
9 9471008
10 9415193
11 9415192
12 9415177
13 9415176
Totals
Period: December 26, 2017 -March
26.2018
Start
Date
26-Dec-17
02-Jan-18
08-Jan-18
S1op
Date
02-Jan-18
08-Jan-18
15-Jan-18
15-Jan-18 I 22-Jan-18
22-Jan-18 29-Jan-18
29-Jan-18 05-Feb-18
05-Feb-18 12-Feb-18
12-Feb-18 20-Feb-18
20-Feb-18 26-Feb-18
26-Feb-18 05-Mar-18
05-Mar-18 12-Mar-18
12-Mar-18 19-Mar-18
19-Mar-18 26-Mar-18
Net
4.6163
4.6210
4.6083
4.6260
4.6421
4.6521
4.6462
4.6368
4.6312
4.6881
4.7026
4.7532
4.7677
FJ~ ... -.. -~~ =:-~'t," """' r'l
~~
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
t.H AH
Week I Filter I Start I Stop I Start I Stop I~ Starting Stopping
# Number Dare Date Time Time ~ Manomete, Manometer
(in. H20) (in. H20)
Calibration Date: 10/4/2017
Calibration Slope & Intercept: m= 1.24782
Orifice S/N: 8091779
b= -0.01058
First Monitoring Quarter 2015
Updated: 7/30/14
9415175 3/26/2018 4/2/2018 89207.02 89375.55 IOI I 1.8 4.0 4.0 4.0 17.7 290.9 617.72 1.11 0.92 32.59 9332.7 4.7685 4.9202 151.7 0.0163 100.3
2 9415162 4/2/2018 4/9/2018 89375.55 89539.87 9859.2 4.0 4,0 4.0 12.2 285.4 616.5 1.10 0,93 32.87 9177.3 4.7601 5.0006 240.5 0.0262 97.8
3 9415159 4/9/2018 4/16/2018 89539.87 89707.99 10087.2 4.0 4.0 4.0 10.8 283.9 618.5 l.09 0.93 33.0l 9429.9 4.7347 5.1019 367.2 0.0389 100.l
4 9415152 4/16/2018 4/23/2018 89707,99 89879.l 10266.6 4.0 4.0 4.0 10.9 284.l 617.7 l.10 0.93 32.98 9589.0 4.7591 5.2220 462.9 0.0483 101.9
5 9415138 4/23/2018 4/30/2018 89879.l 90047.37 10096.2 4.0 4.0 4.0 16.8 290.0 618.0 1.11 0.92 32.65 9334.5 4.7672 5.1072 340.0 0.0364 100.2
6 9415135 4/30/2018 5/7/2018 90047.37 90211.4 9841.8 4.0 4.0 4.0 12.7 285.8 619.50 1.10 0.93 32.93 9177.0 4.7962 5.0286 232.4 0.0253 97.6
7 9415122 5/7/2018 5/14/2018 90211.4 90380.37 10138.2 4.0 4.0 4.0 19.8 293.0 616.71 1.1 l 0.92 32.45 9315.0 4.7639 5.1639 400.0 0.0429 100.6
8 9415119 5/14/2018 5/21/2018 90380.37 90547.72 10041.0 4.0 4.0 4.0 18.1 291.3 616.71 l.l l 0.92 32.54 9253.1 4.7446 4.9643 219.7 0.0237 99.6
9 9415111 5/21/2018 5/29/2018 90547.72 90738.98 l 1475.6 4.0 4.0 4.0 19.3 292.5 617.47 1.11 0.92 32.50 10559.8 4.7556 5,1359 380.3 0.0360 113.8
10 9415103 5/29/2018 6/4/2018 90738.98 90883.96 8698.8 4.0 4.0 4.0 22.0 295.1 618.74 l.12 0.92 32.38 7976.7 4.7496 5.0838 334.2 0.0419 86.3
11 9471996 6/4/2018 6/11/2018 90883.96 91050.23 9976.2 4.0 4.0 4.0 23.3 296.4 617.98 l.l2 0.91 32,29 9121.9 4.6197 4.8985 278.8 0.0306 99.0
12 9471988 6/11/2018 6/18/2018 91050.23 91218.96 10123.8 4.0 4.0 4.0 23.3 296.4 619.50 l.12 0.92 32.33 9268.5 4.6156 4.8888 273.2 0.0295 100.4 DI] o. DI 18/2018 018 8.9D 91387.02 10083.6 4.0 4.0 4.0 24.8 297.9 618.24 1.12 0.91 32.21 9198.3 4.6108 4.8100 199.2 0.0217 100.0 -130800.0 ' c· .. -;, , · ·.-· · :~ ~ · s '.! •· · · ,. -~ -. 14.41 12.00 423.75 120733.5 61.446 65.326 3880.1 0.4177 ---=.,..;=-----------.......... -~==.i....;.1.;.00;.;6=1.5 4.o 4.o 4.o 11.8 291.0 611.93923 1.11 o.92 32.60 9281.2 4.121 5.025 298.5 0.0321 I 99.8 -Ou:1
0.\IP.rao"'
Insert weekly flow check values in ,yellow columns.
~ • -I • ~• ~ .,-',
,~Ii columns in c.al)n,hu~ 1•<en1&=1 l'rom Ille met itnrinn.
Energy Fuels Resources -White Mesa Mill Calibrafion Date: 10/4/2017
b= -0.ot 0581
First Monitoring Quarter 2014
Period: March 26, 2018 -June 25,2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
t.H t.H
Week Filter Start Stop Start Stop II ,om,, Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in.H20)
l 9415174 3/26/2018 4/2/2018 9981 l.85 99981.99 10208.4 4.0 3.5
2 9415163 4/2/2018 4/9/2016 0 120.78 7246.8 4.0 4,0 4.0 12.2 285.4 616,45 1.10 0.93 32.87 6745.6 4-7541 4c9356 1815 0.0269
3 9415158 4/9/2016 4/16/2018 120.78 288.93 10089.0 4.0 4.0 4.0 10.8 283,9 618.49 1.09 0.93 33.01 9431 5 4.7514 5.1902 438,8 0.0465 JOO.I
4 9415151 4/16/2018 4/23/2018 288.93 457.45 10111.2 4.0 4.0 4.0 10.9 284.1 617.72 L.10 0.93 32.98 9443.8 4.7395 5.2443 504.8 0.0535 100.3
5 9415139 4/23/2018 4/30/2018 457.45 627.75 10218.0 4.0 4.0 4.0 16.8 290.0 618.0 L.l I 0.92 32.65 9447.1 4.7785 5.2571 478.6 0.0507 101.4
6 9415134 4/30/2018 5nt2018 627.75 792.34 9875.4 4.0 4.0 4.0 12.7 285.8 619.50 1.10 0.93 32.93 9208.3 4.7776 5.0141 236.5 0.0257 98.0
7 9415123 5nt2018 5/14/2018 792.34 961.28 10136.4 4.0 4.0 4.0 19.8 293.0 616.50 I.JI 0.92 32.44 9311.8 4.7672 5.1489 381.7 0.0410 100,6
8 9415118 5/14/2018 5/21/2018 961.28 1128.07 10007.4 4.0 4.0 4.0 18.1 291 ,3 616.71 I.II 0,92 32,54 9222.2 4.7553 5.0450 289.7 0.0314 99 3
9 9415110 5/21/2018 5/29/2018 1128.07 1319.35 11476.8 4.0 4.0 4.0 19.3 292.5 617.47 I.I I 0.92 32.50 10560.9 4.7729 5.2704 497.5 0.0471 113.9
10 9415102 5/29/2018 6/4/2018 1319.35 1464.92 8734.2 4,0 3.0 3.5 22.0 295.1 618.74 1.04 0.86 30.31 7495.8 4.7883 5.2327 444.4 0.0593 86.6
11 9471995 6/4/2018 6/11/2018 1464.92 1630.61 9941.4 4.0 4.0 4.0 23,3 296.4 617.98 1.12 0,91 32.29 9090.1 4.6055 5.0206 415.1 0.0457 98.6
12 9471987 6/11/2018 6/18/2018 1630.61 1799.06 10107.0 4.0 3.5 3.8 23.3 296.4 619.50 1.08 0.89 31.3 I 8961.5 4.6317 5.0100 378.3 0.0422 100.3
13 9471975 6/18/2018 6/25/2018 1799.06 1967.88 10129.2 4.0 4.0 4.0 24.8 297.9 618.24 1.12 0.91 32.21 9239,9 4.6174 4.9745 357,l 0.0386 100.5
128281.2 14.27 11.88 419.63 117283.4 61 522 66.278 4755.9 0.5252
9867.8 4.0 3.8 3.9 17.8 291.0 617.92308 1.10 0.91 32.28 9021 8 4.732 5.098 365.8 o.0404 I 97.9
Corrunents:
Insert weekly flow check values in yellow columns.
er·u·mns: ~::· -: '.calc:u··-. ; _!JI· :100: .-a·,~~·-·;_ • rom the met srolion.
~~=-:1~~ •. n:~f ~ ... ·\ ~-/ ' ./r_• T,I ~
Week I Filter I Start
# Number Date
9415173 3/2612018
2 9415164 412/2018
3 9415157 4/9/2018
4 9415150 4/16/2018
5 9415140 4/23/2018
6 9415133 4130/2018
7 9415124 5n/2018
8 9415117 5/14/2018
9 9415109 5/21/2018
LO 9415101 5/29/2018
II 9471994 614/2018
9471986 6/11/2018
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
dH
Stop Start Stop Starting
Date Time Time Manometel'
(in.H20)
412/2018 5364-71 5536.9 10331.4 4.0
4/9/2018 5536.9 5700.22 9799.2 4.0
4/16/2018 5700.22 5844.04 8629.2 4.0
4/23/2018 5844,04 6013.07 1014!.8 4.0
4/30/2018 6013.07 6184.43 10281.6 4.0
5n12018 6184.43 6347.36 9775.8 3.5
5/14/2018 6347.36 6516.2 10130.4 4.0
5/21/2018 6516.2 6683.5 10038.0 4.0
5/29/2018 6683.5 6876.27 11566.2 4.0
6/4/2018 6876.27 7019.9 8617.8 4.0
6/11/2018 7019.9 7186.2 9978.0 4.0
6/18/2018 7186.2 7355.94 10184.4 4.0
7523.18 10034.4 4.0
129508.2 .
9962.2 4.0
dH
Stopping
Manometer
(in.H20)
3.5
4.0
4.0
4.0
4.0
4.0
4.0
4.0
4,0
5.0
4.0
4.5
4.0
-
4.1
4.0 12.2
4.0 10.8
4.0 10.9
4.0 16.8
3.8 12.7
4.0 19.8
4.0 18.1
4.0 19.3
4.5 22.0
4.0 23.3
4.3 23.3
4.0 24.8
·~ :
4.0 17.8
Calibration Date: 10/4/2017
Calibration Slope & Intercept:
Orifice SIN: 809 I 779
285.4 616.45 1.10
283.9 618.49 1.09
284.1 617.72 1.10
290.0 617.98 I.I I
285.8 619.50 1.06
293.0 616.71 I.I I
291.3 616.71 I.I I
292.5 617.47 I. LI
295.1 618.74 1.18
296.4 617.98 1.12
296.4 619.SO 1.15
297.9 618 24 1.12 . 14.44
291.0 617.93923 1.11
m= 1.24782
0.93 32.87
0.93 33.01
0.93 32.98
0.92 32.65
0.90 31.89
0.92 32.45
0.92 32.54
0.92 32.50
0.97 34.33
0.91 32.29
0.94 33.32
0.91 32.21
12.02 424.62
0.92 32.66
9121.5 4.7452 4.8802
8066.9 4.7487 4.9699
9472.4 4,7929 5.1835
9505.9 4.7918 5.0357
8828.2 4.7702 4.9123
9307.8 4.7862 5.1709
9250.4 4.7783 5.0212
10643.2 4.7343 5.2208
8378.1 4.7563 5.0433
9123.5 4.6262 4.8648
9608.7 4.6054 4.8285
9153.4 4.6140 4.7660
119694.9 61.531 64.778
9207.3 4.733 4.983
First Monitoring Quarter 2014
Updated: 7/30/14
135.0 0.0148
221.2 0.0274 85.6
390.6 0.0412 100.6
243.9 0.0257 102.0
142.1 0.0161 97.0
384.7 0.0413 100.5
242.9 0.0263 99.6
486.5 0.0457 114.7
287.0 0.0343 85.5
238.6 0.0262 99.0
223.1 0.0232
152.0 0.0166
3247.1 0.3495
249.8 0.0269 I 98.8
Energy Fuels Resources -White Mesa Mill 'Calibration Date: 10/4/2017 First Monitoring Quarter 2014
Period: March 26, 2018 -June 25,2018 Calibration Slope & Intercept: m= 1.24782 b= -O.Q1058 Updated: 7/30/14
Orifice SIN: 8091779
ll.H ll.H
Weeki Filter Start Stop Start Stop Starting Stopping
# Number Date Date Time Time Manometer Manometer
(in.H20) (in.H20)
9415172 3/26/2018 4/2/2018 98433.09 98605,67 10354.8 4.0 4,0
2 9415165 4/2/2018 4/9/2018 98605.67 98769.1 9805.8 4.0 4.0 4.0 12.2 285.4 616.45 1.10 0.93 32.87 9127.6
3 9415156 4/9/2018 4/16/2018 98769.1 98912.42 8599.2 4.0 4.0 4.0 10.8 283.9 618.49 1.09 0.93 33.01 8038.8 4.7457 4.9624 216.7 0.0270 85,3
4 9415149 4/16/2018 4/23/2018 98912.42 99081.8 10162.8 4,0 4.0 4.0 10.9 284.1 617.72 1.10 0,93 32.98 9492.0 4.7988 5.4200 621.2 0.0654 100.8
5 9415141 4/23/2018 4/30/2018 99081.8 99252.81 10260.6 4.0 4.0 4.0 16.8 290.0 618.0 I.I I 0.92 32.65 9486.5 4-7923 5.2644 472.1 0.0498 101.8
6 9415132 4/30/2018 5n/2018 99252.81 99415.61 9768.0 4.0 4.0 4.0 12.7 285.8 619.50 l.10 0.93 32.93 9108.1 4.7783 5.0578 279.5 0.0307 96.9
7 9415125 5n/2018 5/14/2018 99415.61 99584.55 10136.4 4,0 4.0 4.0 19.8 293.0 616.71 1.11 0.92 32.45 9313.4 4.7860 5.6498 863.8 0.0927 100.6
8 9415116 5/14/2018 5/21/2018 99584.55 99751.87 10039.2 4.0 4.0 4.0 18.1 291.3 616.71 I.II 0.92 32.54 9251.5 4.7791 5.0449 265.8 0.0287 99.6
9 9415108 5/21/2018 5/29/2018 99751.87 99945.02 11589.0 4.0 4,0 4,0 19.3 292.5 617.47 1.11 0.92 32.50 10664.2 4,7542 5.5449 790.7 0.0741 115.0
10 9472000 5/29/2018 6/4/2018 -55 88.63 8617.8 4.0 5.0 4.5 22.0 295.1 618.74 1.18 0.97 34.33 8378.1 4.6269 5.1689 542.0 0.0647 85.5
11 9471993 6/4/2018 6/11/2018 88,63 254.95 9979.2 4.0 4.0 4.0 23.3 296.4 617.98 1.12 0.91 32.29 9124.6 4.6207 4.9367 3160 0.0346 99.0
9471985 6/11/2018 6/18/2018 254.95 424.32 10162,2 4.0 4,5 4.3 23,3 296.4 619.50 1.15 0.94 33.32 9587.8 4,6027 4.9714 368.7 0.0385 100.8
591.57 10035.0 40 4.0 4.0 24,8 297.9 618.24 ],]2 0.91 32.21 9154.0 4.6274 4.8531 225.7 0.0247 99.6
f. ---. ~ J. -
129510.0 -... . .. ' 14.51 12.08 426.69 120283.5 61.506 66,772 5266.8 0.5637
9962.3 4.0 4.1 4.1 17.8 291.0 617.93923 1.12 0.93 32.82 9252.6 4.731 5.136 405.1 0.0434 98.8
Comn,cnis: -A rn,gat,vc number was insencd on 614118 to compensate for the time indicator rolling over to zero ~her ,t reached 10.000.
lnsen weekly flow check values in yellow columns.
i=i co1w£oii me calculntcd li~ from Ille met smion.. * Time indicator reset after 10000 on 6/4/18. A negative number was inserted on the start time to compensate for the meter rolling over after I0,000.
\L.--~~m·--1~-~p-~-~: I== f·--7" •. 1 r'. ' ~ [
~~-! .....
Week i Filter I Start
# Number Date
9415171 3/26/2018
2 9415166 4/2/2018
3 9415155 4/9/2018
4 9415148 4/16/2018
5 9415142 4/23/2018
6 9415131 4/30/2018
7 9415126 5/7/2018
8 9415115 5/14/2018
9 9415107 5/21/2018
10 9471999 5/29/2018
11 9471992 6/4/2018
12 9471984 6/11/2018
13 9471978 6/18/2018 ---. ...
Energy Fuels Resources -White Mesa Mill
Period: March 26, 2018 -June 25,2018
tlH
I Stop I Start I Stop • Starting
Date Time Time Manometer
(in.H20)
4/212018 14826.4 14998,61 10332,6 4,0
4/9/2018 14998,61 15161.97 9801.6 4.0
4/16/2018 15161.97 15325.3 9799.8 4.0
4/23/2018 15325.3 15474.75 8967.0 4.0
4/30/2018 15474.75 15646.09 10280.4 4.0
5/7/2018 15646.09 15809.1 9780.6 4.0
5/14/2018 15809.1 15977.93 10129.8 4.0
5/21/2018 15977.93 16145.18 10035.0 4.0
5/29/2018 16145.18 16337.95 11566.2 4.0
6/4/2018 16337.95 16481.23 8596.8 4.0
6/11/2018 16481.23 16647.86 9997.8 4.0
6/18/2018 16647.86 16817.59 10183.8 4.0
6/25/2018 16817.59 16984.82 10033.8 4.0 -~---.--Totals . ·, 129505.2 "
Averages 9961.9 4.0
:r.rceu colW!I~ !UC ~ll\!'Cd •~·from I~ ~ statiQTI.
.O.H
Stopping
Manometei
(in.H20)
4,0
5.0
4.0
4.0
4.0
4.0
3.0
4.0
4.0
4.0
4.0
3.5
4.0 ..
4.0
4.0
4.5
4.0
4.0
4.0
4.0
3.5
4.0
4.0
4.0
4.0
3.8
4.0
~
4.0
Calibration Date: I 0/4/2017
Calibration Slope & Intercept:
Orifice S/N: 8091779 &a ==::===iiiiiiiiiiiiF
17.7 290.9 617.72 Lil
12.2 285.4 616.45 1.17
10.8 283.9 618.49 1.09
10.9 284.1 617.72 LIO
16.8 290.0 618.0 Lil
12.7 285.8 619.50 LIO
19.8 293.0 616.71 1.04
18.1 291.3 616.71 1.11
19.3 292.5 617.47 Lil
22 0 295.1 618.74 l.12
23.3 296.4 617.98 LI2
23.3 296.4 619.50 1.08
24.8 297.9 618.24 Ll2
14.37
17.8 291.0 617.93923 Lll
m= 1.24782
0.92 32.59
0.99 34.85
0.93 33.01
0.93 32.98
0.92 32.65
0.93 32.93
0.86 30.37
0.92 32.54
0.92 32.50
0.92 32.38
0.91 32.29
0.89 31.31
0.91 32.21
11.97 422.63
0.92 32.51
b= -O.Ql058
9536.5 4.7618
9672.9 4.8016
9161.2 4.7304
8375.2 4.7709
9504.8 4.7950
9119.9 4.7615
8710.8 4.7710
9247.6 4.7410
10643.2 4.7581
7883.2 4.6275
9141.6 4.6370
9029.6 4.6072
9152.9 4.6251
119179.1 61.388
9167.6 4.722
First Monitoring Quarter 2014
Updated: 7/30/14
4.9058 144,0 0.0151 102.5
5.0019 200.3 0.0207 97.2
5.1529 422.5 0.0461 97,2
5.1843 413.4 0.0494 89.0
5.0547 259.7 0.0273 102.0
4.9503 188.8 0.0207 97.0
5.1871 416.1 0.0478 100.5
4.9890 248.0 0.0268 99.6
5.2348 476.7 0.0448 114.7
5.1809 553.4 0.0702 85.3
4.8586 221.6 0.0242 99.2
4.8680 260.8 0.0289 101.0
4.8186 193.5 0.0211 99.5
65.387 3998.8 0.4432
5,030 307.6 0.0341 I 98.8
'Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.010581
First Monitoring Quarter 2014
Period: March 26, 2018 -June 25,2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
-11.H 11.H
Week I Filter I Start I Stop I Start I Stop • Starting Stopping
# Number Date Date Time Time Manomete, Manometer
(in.H20) (in. H20) -
9415170 3/26/2018 4/2/2018 7029,67 7197.99 10099,2 4.0 4,0 4.0 17.7 290.9 617.72 I.II 0.92 32.59 9321.0 4.7563 4.9349 178.6 0.0192 100.2
2 9415167 4/2/2018 4/9/2018 7197.99 7362.68 9881.4 4.0 4.0 4.0 12.2 285.4 616.45 I.IO 0.93 32.87 9198.0 4.7545 5.1375 383.0 0.0416 98.0
3 9415154 4/9/2018 4/16/2018 7362.68 7531.21 10111.8 4.0 4.0 4.0 10.8 283.9 618.49 1.09 0.93 33.01 9452_9 4.7304 5.1529 422.5 0.0447 100.3
4 9415147 4/16/2018 4/23/2018 7531.21 7702.49 10276.8 4.0 4.0 4.0 10.9 284.1 617.72 1.10 0.93 32.98 9598.5 4.7881 5.3151 527.0 0.0549 102.0
5 9415143 4/23/2018 4/30/2018 7702.49 7870.76 10096.2 4.0 4.0 4.0 16.8 290.0 618.0 I.I I 0.92 32.65 9334.5 4.7632 5.1605 397.3 0.0426 100.2
6 9415130 4/30/2018 5/7/2018 7870.76 8034.72 9837.6 4.0 4.0 4.0 12.7 285.8 619.50 1,10 0.93 32.93 9173.0 4_7678 4.9394 171.6 0.0187 97,6
7 9415127 5/7/2018 5/14/2018 8034.72 8203.56 10130.4 4.0 4.0 4.0 19.8 293.0 616.71 I.I I 0.92 32.45 9307.8 4.7790 5.1598 380.8 0.0409 100.5
8 9415114 5/14/2018 5/21/2018 8203.56 8371.16 10056.0 4.0 4.0 4.0 18.1 291.3 616.71 1.11 0.92 32.54 9266.9 4.7485 4.9326 184.1 0.0199 99.8
9 9415106 5/21/2018 5/29/2018 8371.16 8562.88 11503.2 4.0 4.0 4.0 19.3 292.5 617.47 I.I I 0.92 32.50 10585.2 4.7575 5.1172 359.7 0.0340 114,l
LO 9471998 5/29/2018 6/4/2018 8562.88 8707.31 8665.8 4.0 5.0 4.5 22.0 295.1 618.74 1.18 0.97 34.33 8424.8 4.6187 5.0739 455.2 0.0540 86.0
11 9471991 6/4/2018 6/11/2018 8707.31 8874.1 10007.4 4.0 4.0 4.0 23.3 296,4 617.98 1.12 0.91 32.29 9150.4 4.6199 4.9746 354.7 0.0388 99.3
12 9471983 6/11/2018 6/18/2018 8874.1 9042.15 10083.0 4.0 3.5 3.8 23.3 296.4 619.50 1.08 0.89 31.31 8940.2 4.6056 4.9403 334.7 0.0374 100.0
13 9471979 6/18/2018 6/25/2018 9042.15 9210.36 10092.6 4.0 4.0 4.0 24.8 297.9 618.24 1.12 0.91 32.21 9206.5 4.6267 4.8501 223.4 0.0243 100.1
130841.4 :.~ ... : ?'· -. I -.:: 14.44 12.03 424.68 120959.8 61.316 65.689 4372.6 0.4709 -· ~· . :.! --I
10064.7 4.0 4.0 4.0 17.8 291.0 617.93923 I.II 0.93 32.67 9304.6 4.717 5.053 336.4 0.0362 99.8
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.
er-CQ!ilnl"s llR: t11IC11lll!C!li ~•ven1~ fm,n the nlCl>.'\IIILion.
Energy Fuels Resources -White Mesa Mill Calibration Date: 10/4/2017
b= -0.010581
First Monitoring Quarter 2014
Period: March 26, 2018 -June 25,2018 Calibration Slope & Intercept: m= 1.24782 Updated: 7/30/14
Orifice SIN: 8091779
dH Ml
Week I Filter Start Stop Start Stop Starting Stopping
# Number Date Date Time Time Manomete, Manometer
(in.H20) (in.H20)
9415169 3/26/2018 4/2/2018 13490.24 13685.68 11726.4 4.0 4.0 4.0 17.7 290.9 617.72 I.II 0.92 32.59 10822.9 4.7601 4.8474 87.3 0.0081 116.3
2 9415168 4/2/2018 4/9/2018 13685.68 13823.31 8257.8 4.0 4.0 4.0 12.2 285.4 616.45 1.10 0.93 32.87 7686.7 4.7600 4.8929 132.9 0.0173 81.9
3 9415153 4/9/2018 4/16/2018 13823.31 13991.79 10108.8 4.0 4.0 4.0 10.8 283.9 618.49 1.09 0.93 33.01 9450.0 4.7403 5.0397 299.4 0.0317 100.3
4 9415146 4/16/2018 4/23/2018 13991.79 14163.07 10276.8 4.0 4.0 4.0 10.9 284.1 617.72 1.10 0.93 32.98 9598.5 4.8000 5.2709 470.9 0.0491 102.0
5 9415144 4/23/2018 4/30/2018 14163.07 14331.33 10095.6 4.0 4.0 4.0 16.8 290.0 618.0 I.I I 0.92 32.65 9333.9 4.7721 5.0523 280.2 0.0300 100.2
6 9415129 4/30/2018 5/7/2018 14331.33 14495.3 9838.2 4.0 4.0 4.0 12.7 285.8 619.50 l.10 0.93 32.93 9173.6 4.7558 4.8764 120.6 0.0131 97.6
7 9415128 5/7/2018 5/14/2018 14495.3 14664.15 10131.0 4.0 5.0 4.5 19.8 293.0 616.71 1.18 0.97 34.40 9868.7 4.7662 5.0658 299.6 0.0304 100.5
8 9415113 5/14/2018 5/21/2018 14664.15 1483 1.63 !0048.8 4.0 4.0 4.0 18.1 291.3 616.71 I.I I 0.92 32.54 9260.3 4.7590 4.9126 153.6 0.0166 99.7
9 9415105 5/21/2018 5/29/2018 14831.63 15022.8 11470.2 4.0 4.0 4.0 19.3 292.5 617.47 I.I I 0.92 32.50 10554.8 4.75 IO 5.0453 294.3 0.0279 113.8
10 9471997 5/29/2018 6/4/2018 15022.8 15167.9 8706.0 4.0 4.0 4.0 22.0 295.1 618.74 1.12 0.92 32.38 7983.3 4.6248 4.9146 289.8 0.0363 86.4
II 9471990 6/4/2018 6/11/2018 15167.9 15334.11 9972.6 4.0 4.0 4.0 23.3 296.4 617.98 1.12 0.91 32.29 9118.6 4.6058 4.7792 173.4 0.0190 98.9
12 9471982 6/11/2018 6/18/2018 15334.11 15502.78 10120.2 4.0 3.5 3.8 23.3 296.4 619.50 1.08 0.89 31.31 8973.2 4.6088 4.8022 193.4 0.0216 100.4
15670.94 10089.6 4,0 3.5 3.8 24.8 297.9 618.24 1.09 0.88 31.20 8913.7 4.5927 4.7061 113.4 0.0127 JOO.I
130842.0 .
-... .. ~ : ... -. .. ,_ . ., . .,. 14.40 12.00 423.67 120738.3 61.297 64.205 2908.8 0.3137
10064.8 4.0 4.0 4.0 17.8 291.0 617.93923 I.II 0.92 32.59 9287.6 4.715 4.939 223.8 0.0241 I 99.8
n col~l!(e CJl)cu~ ~~from~ ~,sllltron.
Iii , ~,ii ' : • ~: I ~ • -: • _.. In-· ;-~1~ ' . ·~'
_. I it,._ l _ •, (!, , ..., ~ -
Week Filter
# Number
1 9415161
2 9415160
3 9415145
4 9415137
5 9415136
6 9415121
7 9415120
8 9415112
9 9415104
10 9471989
11 9471981
12 9471973
13 9471972
Totals
Period: March 26, 2018 -June
25 2018
Sfart' Ste-I!) Net D.ate Date
26-Mar-18 02-A r-18 4.7536
02-A r-18 09-A r-18 4.7508
09-Apr-18 16-Apr-18 4.7884
16-A r-18 23-A r-18 4.7779
23-A r-18 30-Apr-18 4.7689
30-A r-18 07-Ma -18 4.7750
14-Ma -18 4.7822
21-Ma -18 4.7734
29-Ma -18 4.7369
04-Jun-18 4.6103
04-Jun-18 11-Jun-18 4.6106
11-Jun-18 18-Jun-18 4.5711
18-Jun-18 25-Jun-18 4.6257
ATTACHMENT E
ENVIRONMENTAL GAMMA GRAPHS AND SUPPORTING DATA
l White Mesa Mill Ambient Gamma Levels Over Time BHV-1 I
50.00 -r----------------------------------------------------------,
~00 I
®00 I
~oo I
30.00
....
Q)
t::::
ell 25.00 :,
CT ..._
E Q) a:
E 20.00
15.00
10.00 -t-------------------------------------ft---------------------------1----1
5.00 I a I-I a I 11116 I-H l---1-1-\-J-l_..H---I--\ I 1" a JI 11 I
Ysat-. .... tr.M r 1 ¥• I 1 "I 1 • i ••• • • • 1 'lt 9/30/1981 9/30/1984 9/30/1987 9/30/1990 9/30/1993 9/30/1996 9/30/1999 9/30/20o2 9/30/20os 9/30/20o8
9/30/2011 9/30/2014 9/30/2017
Background (BHV-3) Subtracted from BHV-1
--4--Seriesl
! White Mesa Mill Ambient Gamma Levels Over Time BHV-2 !
50.00 ...... -------------------------------------------------------,
45.00 ..,_ ______________________________________________________ _,
40.00 +--------------------------------------------------------1
35.00 ..,_ ______________________________________________________ _,
30.00 ,_
Q)
t'. ct! ::::,
C" -25.00
E Q) a:
E 20.00
15.00
10.00 -------------------------------------------------------------;
5.00 I 1r II I IW a -• 1'f -• I
0.00
30-Sep.Bl 30-Sep.89 30-Sep.97 30-sep.os 30-Sep.13
Background (BHV-3) Subtracted from BHV-2
-+-BHV-2
j White Mesa Mill Ambient Gamma Levels Over Time BHV-3 !
60.00 ..-----------------------------------------------------------------------,
50.00
40.00
....
Q)
t:: ca :::,
O'" 30.00 --E Q) er:
E
20.00
10.00 -t----------------------------------------------------------------------1
0.00 -,...------1------;----~---~---,-------+---~---~---,-------+---~---~---,-------+---~--.....
3o..sep..el 30..seP-84 30..seP-87 30.Sep.90 30..sep.93 3o.sep.96 3o.sep.99
30..seP-02 30..seP-os 30.sep-08 30.Sep.ll 30..seP-14 30-Sep.17
-BHV-3
I White Mesa Mill Ambient Gamma Levels Over Time BHV-4 j
50.00 ..------------------------------------------------,
45.00 -----------------------------------------------------------1
40.00 I
35.00 +------------------------------------------------------1
30.00
I,_,
Q)
t:::: ctS 25.00
:J
C" -E Q) CI: 20.00
E
15.00
10.00 +---l+----------------------------------------------------1
5.00 I • I a llf W' I\ I
0.00
30-Sep.81 ~s ~ ~s ~s ~Se ~Se ~Se ~Se ~e ~e ep.84 "eP-87 ep.90 ep.93 P-95 P-99 P-02 P-Os P-Os P-11 30-Sep.14 30-Sep.17
Background (BHV-3) Subtracted from BHV-4
_._ BHV-4
I White Mesa Mill Ambient Gamma Levels Over Time BHV-s I
50.00 ...-------------------------------------------------------,
45.00 .f.-------------------------------------------------------1
40.00 -11----------------------------------------------------1
35.00 -11---------------------------------------------------------t
30.00 ,._
Q)
t
(lj
:::J
C" -25.00
E Q) a: E 20.00
15.00 I
10.00 -I I
5.00 I 11 1• &.: 1-.-nn.. 1~11 • -11 ±I l:k-H W' I IHJ\ ..... ~I I I
o.oo •• -..... •• ... ·-. .• . .. -•• I
30-Sep.Bl 30.sep.84 30.sep.87 30-Sep.90 30.sep.93 30-Sep.95 30-Sep.99 30-Sep.02 30-se 30-se 3o.se 1J-05 P-08 1J· l l 30.sep.l4 30-Sep.ll
Background (BHV-3) Subtracted from BHV-5
-4-BHV-5
I White Mesa Mill Ambient Gamma Levels Over Time BHV-6 !
50.00
45.00
40.00
35.00
30.00 j I
,._
Q)
t
C'CS 25.00
::::l O" ---E
Q) a: 20.00
E
15.00
10.00
• ~-.! .. ,~ A_A ~-~ -~ La ----.... -~-_,,, ---
5.00
0.00
30-Sep.Bl 30-Sep.84 30-Sep.87 30-Sep.90 30-Sep.93 30-Sep.96 30-Sep.99 30-Sep-o2 30-seP-os 30-seP-os 30-Sep.ll 30-Sep.14 30.Sep.17
Background (BHV-3) Subtracted from BHV-6
~BHV-6
l White Mesa Mill Ambient Gamma Levels Over Time BHV-7 l
SO.OD
45.00
40.00
35.00
30.00
,_
Q) ~!> t
ctS 25.00 :J CT .__
E Q) a: 20.00
E
15.00
10.00
~
--J ~---~--: ------------. ---
5.00
0.00
l-seP-l4 l-Dec-l4 l-Mar-is l-Jun-15 l-seP-15 l-Dec-15 l-Mar-16 l-Jun-15 l-Sep.16 l-Dec-l5 l-Mar-i7 l-Jun-i7 l-Sep.27 l-Dec-l7 l-Mar-l8 l-Jun-l8
Background (BHV-3) Subtracted from BHV-7
.......,_BHV-7
j White Mesa Mill Ambient Gamma Levels Over Time BHV-a !
50.00
45.00
40.00
35.00
30.00
,._
(I) t cu 25.00 ::::,
Ci ---E (I) er: 20.00
E
15.00
10.00 ~
--: --J ~--= ;; ~ ----------~-.-----. ' -----
5.00
0.00
l-Sep.14 l-Dec-14 l-A.1ar-1s l-Jun.15 1-seP·ls l-Dec-15 l-Atlar-15 l-Jur,.16 l-Sep.16 l-Dec.15 l·Atlar-17 l-111,.,.11 l-Sep.17 l -Dec-17 l-A.1ar-1e l-111,.,.18
Background (BHV-3) Subtracted from BHV-8
-BHV-8
White Mesa Mill First Quarter 2018 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 1/3/2018 4/3/2018 90 35.6 0.02 0.396 2.77
1 V205 Control Room 1/3/2018 4/3/2018 90 42.9 0.02 0.477 3.34
2 BHV-6 1/3/2018 4/3/2018 90 31.2 0.01 0.347 2.43
3 Ore Stor. -Barrel Area 1/3/2018 4/3/2018 90 358.5 0.17 3.983 27.88
4 Vanadium Precip.Area 1/3/2018 4/3/2018 90 208.7 0.10 2.319 16.23
5 Yellowcake Drying Area 1/3/2018 4/3/2018 90 373.4 0.17 4.149 29.04
6 Leach 1/3/2018 4/3/2018 90 139.7 0.06 1.552 10.87
7 SAG Mill Control Room 1/3/2018 4/3/2018 90 237.3 0.11 2.637 18.46
8 Yellowcake Precip. 1/3/2018 4/3/2018 90 629 0.29 6.989 48.92
9 Central Control Room 1/3/2018 4/3/2018 90 92.5 0.04 1.028 7.19
10 Ore pad -decontamination pad 1/3/2018 4/3/2018 90 102.2 0.05 1.136 7.95
11 North East Corner Ore Pad 1/3/2018 4/3/2018 90 281.9 0.13 3.132 21.93
12 Met. Lab 1/3/2018 4/3/2018 90 91.3 0.04 1.014 7.10
13 Filter Press Room 1/3/2018 4/3/2018 90 150 0.07 1.667 11.67
14 BHV-1 1/3/2018 4/3/2018 90 35 0.02 0.389 2.72
15 BHV-2 1/3/2018 4/3/2018 90 34.1 0.02 0.379 2.65
16 BHV-3 1/3/2018 4/3/2018 90 34 0.02 0.378 2.64
17 BHV-4 1/3/2018 4/3/2018 90 32 0.01 0.356 2.49
18 BHV-5 1/3/2018 4/3/2018 90 36 0.02 0.400 2.80
19 SAG Mill 1/3/2018 4/3/2018 90 264 0.12 2.933 20.53
20 Tails 1/3/2018 4/3/2018 90 42.8 0.02 0.476 3.33
21 CCD 1/3/2018 4/3/2018 90 83.6 0.04 0.929 6.50
22 North SX 1/3/2018 4/3/2018 90 0.00 0.000 0.00
23 Administration Building 1/3/2018 4/3/2018 90 78.2 0.04 0.869 6.08
24 Admin Parking Lot 1/3/2018 4/3/2018 90 76.3 0.04 0.848 5.93
25 Yellowcake Packaging 1/3/2018 4/3/2018 90 311.4 0.14 3.460 24.22
26 Yellowcake Storage 1/3/2018 4/3/2018 90 1075.5 0.50 11.950 83.65
27 Bucking Room 1/3/2018 4/3/2018 90 285.4 0.13 3.171 22.20
28 Mill Lunch Room 1/3/2018 4/3/2018 90 54 0.03 0.600 4.20
29 South SX 1/3/2018 4/3/2018 90 153.4 0.07 1.704 11.93
30 Mtce. Super.'s Office 1/3/2018 4/3/2018 90 47.9 0.02 0.532 3.73
31 Ore Feed Grizzly 1/3/2018 4/3/2018 90 309.1 0.14 3.434 24.04
32 Sc alehouse 1/3/2018 4/3/2018 90 208.6 0.10 2.318 16.22
33 Sample Plant (OBS) 1/3/2018 4/3/2018 90 229.5 0.11 2.550 17.85
34 Front Gate 1/3/2018 4/3/2018 90 177.9 0.08 1.977 13.84
45 AF -Barrel Dump Station 1/3/2018 4/3/2018 90 167.4 0.08 1.860 13.02
46 AF Circuit -South 1/3/2018 4/3/2018 90 112.6 0.05 1.251 8.76
47 AF Circuit -North 1/3/2018 4/3/2018 90 1254.4 0.58 13.938 97.56
51 North Control# 1 1/3/2018 4/3/2018 90 39 0.02 0.433 3.03
52 North Control# 2 1/3/2018 4/3/2018 90 35.7 0.02 0.397 2.78
CaF2 Barrel Dump Station -
53 Operator Station 1/3/2018 4/3/2018 90 139.8 0.06 1.553 10.87
64 KF Barrel Dump Station 1/3/2018 4/3/2018 90 279 0.13 3.100 21.70
70 BHV-7 1/3/2018 4/3/2018 90 30.8 0.01 0.342 2.40
71 BHV-8 1/3/2018 4/3/2018 90 30.1 0.01 0.334 2.34
White Mesa Mill Second Quarter 2018 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 4/3/2018 7/5/2018 93 42.7 0.02 0.459 3.21
1 V205 Control Room 4/3/2018 7/5/2018 93 52 0.02 0.559 3.91
2 BHV-6 4/3/2018 7/5/2018 93 37.4 0.02 0.402 2.82
3 Ore Stor. -Barrel Area 4/3/2018 7/5/2018 93 365.7 0.16 3.932 27.53
4 Vanadium Precip.Area 4/3/2018 7/5/2018 93 155.6 0.07 1.673 11.71
5 Yellowcake Drying Area 4/3/2018 7/5/2018 93 423.1 0.19 4.549 31.85
6 Leach 4/3/2018 7/5/2018 93 199.9 0.09 2.149 15.05
7 SAG Mill Control Room 4/3/2018 7/5/2018 93 291.4 0.13 3.133 21.93
8 Yellowcake Precip. 4/3/2018 7/5/2018 93 523.8 0.23 5.632 39.43
9 Central Control Room 4/3/2018 7/5/2018 93 92.4 0.04 0.994 6.95
10 Ore pad -decontamination pad 4/3/2018 7/5/2018 93 124 0.06 1.333 9.33
11 North East Corner Ore Pad 4/3/2018 7/5/2018 93 330.4 0.15 3.553 24.87
12 Met. Lab 4/3/2018 7/5/2018 93 95.3 0.04 1.025 7.17
13 Filter Press Room 4/3/2018 7/5/2018 93 145.6 0.07 1.566 10.96
14 BHV-1 4/3/2018 7/5/2018 93 38.9 0.02 0.418 2.93
15 BHV-2 4/3/2018 7/5/2018 93 41.3 0.02 0.444 3.11
16 BHV-3 4/3/2018 7/5/2018 93 39.1 0.02 0.420 2.94
17 BHV-4 4/3/2018 7/5/2018 93 39.8 0.02 0.428 3.00
18 BHV-5 4/3/2018 7/5/2018 93 40.3 0.02 0.433 3.03
19 SAG Mill 4/3/2018 7/5/2018 93 329.5 0.15 3.543 24.80
20 Tails 4/3/2018 7/5/2018 93 52.2 0.02 0.561 3.93
21 CCD 4/3/2018 7/5/2018 93 98.4 0.04 1.058 7.41
22 North SX 4/3/2018 7/5/2018 93 67.8 0.03 0.729 5.10
23 Administration Building 4/3/2018 7/5/2018 93 45.5 0.02 0.489 3.42
24 Admin Parking Lot 4/3/2018 7/5/2018 93 80.7 0.04 0.868 6.07
25 Yellowcake Packaging 4/3/2018 7/5/2018 93 422.8 0.19 4.546 31.82
26 Yellowcake Storage 4/3/2018 7/5/2018 93 894.4 0.40 9.617 67.32
27 Bucking Room 4/3/2018 7/5/2018 93 322.3 0.14 3.466 24.26
28 Mill Lunch Room 4/3/2018 7/5/2018 93 56.6 0.03 0.609 4.26
29 South SX 4/3/2018 7/5/2018 93 106.1 0.05 1.141 7.99
30 Mtce. Super.'s Office 4/3/2018 7/5/2018 93 54.6 0.02 0.587 4.11
31 Ore Feed Grizzly 4/3/2018 7/5/2018 93 378.1 0.17 4.066 28.46
32 Scalehouse 4/3/2018 7/5/2018 93 225.9 0.10 2.429 17.00
33 Sample Plant (OBS) 4/3/2018 7/5/2018 93 216.4 0.10 2.327 16.29
34 Front Gate 4/3/2018 7/5/2018 93 200.2 0.09 2.153 15.07
45 AF -Barrel Dump Station 4/3/2018 7/5/2018 93 309.4 0.14 3.327 23.29
46 AF Circuit -South 4/3/2018 7/5/2018 93 96.1 0.04 1.033 7.23
47 AF Circuit -North 4/3/2018 7/5/2018 93 151.8 0.07 1.632 11.43
51 North Control# 1 4/3/2018 7/5/2018 93 45.7 0.02 0.491 3.44
52 North Control # 2 4/3/2018 7/5/2018 93 41.1 0.02 0.442 3.09
CaF2 Barrel Dump Station -
53 Operator Station 4/3/2018 7/5/2018 93 135.5 0.06 1.457 10.20
64 KF Barrel Dump Station 4/3/2018 7/5/2018 93 291.3 0.13 3.132 21.93
70 BHV-7 4/3/2018 7/5/2018 93 37.1 0.02 0.399 2.79
71 BHV-8 4/3/2018 7/5/2018 93 37.6 0.02 0.404 2.83
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 6 I I I I 0 0 0 0 0 0 CX> --.J 0) u, +'" (,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
8/27/1990 JJ D) I N 8/27/1991 N en 8/27/1992 0
8/27/1993 0 :::J (')
8/27/1994 Cl)
:::J
8/27/1995 -... D) -8/27/1996 o·
t 8/27/1997 :::J r.n
z 8/27/1998 :::J m < 8/27/1999 Cl)
(C
T 8/27/2000 Cl) -D)
8/27/2001 -z o· :E 8/27/2002 :::J -8/27/2003 C t 0
8/27/2004 :::::.: " CJ) (C :E 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 6 I I I I 6 I 0 0 0 0 0 CX) ....... CJ) c.n .i:,. u) I\)
8/27/1981
8/27/1982
8/27/1983
8/27/1984
8/27/1985
8/27/1986
8/27/1987
8/27/1988
8/27/1989 .,,
8/27/1990 C" I
8/27/1991 N ....
0 8/27/1992 0 0 8/27/1993 ::::,
(')
8/27/1994 CD ::::,
8/27/1995 -..,
&» -8/27/1996 o· t 8/27/1997 ::::, u,
z 8/27/1998 5' m < 8/27/1999 CD
' cg
8/27/2000 CD -&» z 8/27/2001 -::: o·
8/27/2002 ::::, -t 8/27/2003 C 0
8/27/2004 :::::::
C/l ;:,.:
::: cg
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 -1
(Log Scale)
_. _. _. _. _.
a a a a a a a 0 0 0 0 0 0 0 m m m m m m m I 6 6 6 6 I I 0 0 0 co -..J 0) 0, .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
12/1/2015
1/1/2016 C: I z 2/1/2016 ~ 3/1/2016 0
4/1/2016 0 ::::,
5/1/2016 (')
(?)
6/1/2016 ::::, -"'I
7/1/2016 I» -
t 8/1/2016 er ::::, rn
z 9/1/2016 ::::,
m 10/1/2016 < (?)
' 11/1/2016 (Q
(?)
12/1/2016 -I» -z 1/1/2017 o· ~ ::::,
2/1/2017 -C t 3/1/2017 0 :::::::
(/) 4/1/2017 ~
~ (Q
5/1/2017 -
6/1/2017
7/1/2017
8/1/2017
9/1/2017
10/1/2017
11/1/2017
12/1/2017
1/1/2018
2/1/2018
3/1/2018
4/1/2018
5/1/2018
6/1/2018
(Log Scale)
...... ...... ......
0 0 0 0 0 0 0 0 0 0 0 0 0 0 rn rn rn m rn m m I I I I 6 I I
0 0 0 0 0 0
OJ --.J CJ) u, ~ 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
12/1/2015
1/1/2016 -I :::c I
2/1/2016 I\) w
3/1/2016 I\)
0
4/1/2016 0 ::::,
5/1/2016 C'J CD
6/1/2016 ::::, -...
7/1/2016 I» -
8/1/2016 s·
t ::::,
0 9/1/2016 5' z m 10/1/2016 < CD 11/1/2016 (Q
t CD
12/1/2016 -I» -z 1/1/2017 5· :E ::::,
2/1/2017 -C
t 3/1/2017 0 :::::
4/1/2017 ~ (/J (Q :E 5/1/2017 -
6/1/2017
7/1/2017
8/1/2017
9/1/2017
10/1/2017
11/1/2017
12/1/2017
1/1/2018
2/1/2018
3/1/2018
4/1/2018
5/1/2018
6/1/2018
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 3.90E-04
4th '81 20-0ct-81 l .40E-04
2nd'82 15-Apr-82 l.31E-04
3rd '82 Ol-Jul-82 l.60E-04
4th '82 30-Nov-82 2.67E-06
2nd '83 13-Apr-83 9.36E-05
3rd '83 Ol-Jul-83 l.12E-04
4th '83 30-Jan-84 l.09E-04
2nd'84 28-Jun-84 3.47E-04
4th '84 14-Nov-84 5.61E-04
2nd'85 27-Mar-85 !.OSE-03
3rd '85 I 5-Jul-85 8.20E-05
4th '85 09-0ct-85 l.l5E-04
2nd '86 24-Mar-86 5.72E-04
3rd '86 lO-Jul-86 5.01 E-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.SOE-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
l st '91 JO-Anr-91 l.20E-04
2nd '91 l l-Jun-91 9.lOE-05
3rd '91 20-Nov-91 4.50E-04
1st '92 22-Apr-92 3.60E-05
2nd'92 lO-Jun-92 l.OOE-05
3rd '92 JO-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
!st '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 1.SOE-05
3rd '95 I 5-Nov-95 5.50E-05
1st '96 23-Apr-96 5.20E-05
2nd '96 * 3 I-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.lOE-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-OO l.50E-04
2nd '00 22-Jun-OO l.20E-06
4th '00 21-Dec-OO l.60E-06
1st 'Ol 30-Apr-01 l.OOE-06
2nd'OI 14-Jun-01 2.30E-06
4th 'OJ 17-Dec-01 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
Ra-226 MDC¥ Pb-210
ERROR LLDuCi/Kg VALUE
(uCi/Kg) (S.OE-08) (uCi/Kg)
l.OOE-05 5.00E-08 l.lOE-03
l.OOE-05 5.00E-08 6.80E-04
l.30E-05 I.OOE-06 4.90E-04
l.OOE-05 5.00E-08 8.00E-04
l.07E-06 I.OOE-06 J.08E-04
6.20E-06 8.00E-09 4.97E-04
I .20E-05 6.00E-06 l.84E-04
8.00E-06 4.00E-06 7.80E-04
l.20E-05 2.00E-09 3.75E-03
J .99E-04 2.00E-07 7.82E-03
3.00E-05 2.00E-06 3.22E-03
7.00E-06 3.00E-06 7.70E-04
l.OOE-05 3.00E-06 5.lOE-04
2.lOE-05 4.00E-06 2.49E-03
l.30E-05 3.00E-06 l.57E-03
5.00E-05 3.00E-06 6.80E-04
7.00E-05 5.00E-08 l.50E-03
3.00E-05 5.00E-08 9.50E-04
4.00E-05 5.00E-08 l.70E-03
7.00E-05 5.00E-08 l.40E-03
2.20E-05 5.00E-08 l.50E-04
4.00E-05 *** l.lOE-03
2.00E-05 *** 2.30E-04
5.00E-05 7.00E-06 2.04E-03
3.00E-05 4.00E-06 3.30E-04
2.00E-05 5.00E-08 3.20E-04
2.00E-05 5.00E-08 3.30E-04
2.00E-05 5.00E-06 3.00E-04
l.60E-05 2.00E-07 l .90E-04
4.00E-05 5.00E-08 l.09E-03
l.OOE-05 2.00E-06 l.SOE-04
7.00E-06 2.00E-07 7.50E-05
3.SOE-05 3.00E-06 7.lOE-04
2.20E-05 3.00E-06 2.80E-04
l .50E-05 3.00E-06 4.30E-05
2.70E-05 3.00E-06 5.30E-04
4.00E-05 3.00E-05 4.40E-04
l .20E-06 9.00E-08 3.00E-05
l.50E-05 I.70E-07 1.70E-04
5.40E-06 1.60E-07 l.40E-04
l.50E-06 I .50E-07 5.lOE-05
5.00E-06 l .80E-07 6.70E-05
2.SOE-06 l.SOE-07 3.20E-05
2.50E-06 l.80E-07 l.40E-04
4.70E-07 l.21E-07 4.lOE-05
4.30E-07 l.33E-07 2.IOE-05
l.20E-06 5.60E-07 l.40E-04
9.lOE-05 9.lOE-05 <4.50E-04
1.20E-06 6.30E-08 4.00E-05
l.OOE-06 8.20E-08 8.70E-05
3.00E-06 l.20E-07 3.00E-04
l.40E-06 8.30E-08 l.40E-04
l.OOE-06 2.30E-07 2.IOE-05
3.00E-06 l.20E-07 l.60E-04
l.OOE-07 2.80E-07 l.60E-04
l.lOE-06 3.70E-07 5.IOE-05
l.OOE-07 2.40E-07 <l.2E-06
2.00E-07 9.90E-08 3.80E-06
2.40E-06 l.20E-07 3.57E-05
l.80E-06 7.60E-07 4.50E-05
2.81E-06 7.60E-07 5.31 E-05
3.60E-06 7.60E-07 l.29E-04
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR LLD uCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg) uCi/Kg (uCi/Kg) (uCi/Kg) uCi/Kg
(2.0E-07) (2.0E-07)t
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
8.00E-05 !.OOE-06 NS NA NA NS NA NA
7.00E-05 8.00E-05 NS NA NA NS NA NA
l.70E-04 I.OOE-07 NS NA NA NS NA NA
9.00E-06 l.OOE-05 NS NA NA NS NA NA
9.30E-05 I.OOE-04 NS NA NA NS NA NA
l .20E-05 I.OOE-06 NS NA NA NS NA NA
6.20E-05 6.00E-05 NS NA NA NS NA NA
l.60E-04 4.00E-08 NS NA NA NS NA NA
3.30E-04 7.00E-08 NS NA NA NS NA NA
l.40E-04 2.00E-05 NS NA NA NS NA NA
l.30E-04 2.00E-04 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
l.OOE-04 l.OOE-05 NS NA NA NS NA NA
l.70E-03 2.00E-04 NS NA NA NS NA NA
3.00E-05 3.00E-06 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
4.00E-05 l.OOE-06 NS NA NA NS NA NA
l.OOE-04 l.OOE-06 NS NA NA NS NA NA
I.OOE-04 1.00E-06 NS NA NA NS NA NA
4.40E-04 1.00E-06 NS NA NA NS NA NA
l.OOE-01 *** NS NA NA NS NA NA
2.00E-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 I.OOE-06 NS NA NA NS NA NA
2.00E-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
7.00E-05 2.00E-05 NS NA NA NS NA NA
3.00E-05 2.00E-05 NS NA NA NS NA NA
3.50E-05 2.00E-05 NS NA NA NS NA NA
6.00E-05 2.00E-05 NS NA NA NS NA NA
6.00E-05 2.00E-04 NS NA NA NS NA NA
6.lOE-06 4.45E-06 NS NA NA NS NA NA
l.lOE-05 8.30E-07 NS NA NA NS NA NA
l.30E-05 7.90E-07 NS NA NA NS NA NA
4.50E-06 7.60E-07 NS NA NA NS NA NA
l.OOE-05 8.80E-07 NS NA NA NS NA NA
4.50E-06 l.80E-07 NS NA NA NS NA NA
NS NA NA NS NA NA
7.lOE-06 9.30E-07 NS NA NA NS NA NA
3.60E-06 6.JOE-07 NS NA NA NS NA NA
7.30E-07 6.66E-07 NS NA NA NS NA NA
4.60E-06 1.lOE-07 NS NA NA NS NA NA
4.50E-04 4.50E-04 NS NA NA NS NA NA
l.80E-06 3.20E-07 NS NA NA NS NA NA
5.00E-06 4.lOE-07 NS NA NA NS NA NA
l.OOE-05 6.00E-05 NS NA NA NS NA NA
4.70E-06 4.20E-07 NS NA NA NS NA NA
l.OOE-06 l.lOE-06 NS NA NA NS NA NA
8.00E-06 5.90E-07 NS NA NA NS NA NA
l.OOE-05 I .40E-06 NS NA NA NS NA NA
5.00E-06 l.90E-06 NS NA NA NS NA NA
l.OOE-07 2.40E-07 NS NA NA NS NA NA
2.00E-07 5.00E-07 NS NA NA NS NA NA
2.97E-06 6.00E-07 NS NA NA NS NA NA
2.61E-06 l.OOE-05 NS NA NA NS NA NA
3.90E-06 1.00E-05 NS NA NA NS NA NA
6.l5E-06 1.00E-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHEAST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
1st '03 21-Mar-03 9.lOE-06
2nd '03 1 O-Jun-03 2.50E-05
4th '03 20-Nov-03 5.70E-05
1st '04 08-Apr-04 9.38E-05
2nd '04 12-Jun-04 5.63E-05
4th '04 30-Nov-04 8.41E-05
1st '05 21-Apr-05 5.60E-05
2nd '05 13-Jun-05 9.lOE-06
4th '05 IO-Nov-05 6.00E-05
1st '06 03-Apr-06 8.00E-05
2nd '06 16-Jun-06 4.lOE-05
4th '06 28-Nov-06 1.17E-04
1st '07 30-Mar-07 9.70E-05
2nd '07 I-Jun-07 I .30E-05
4th '07 23-Nov-07 7.00E-05
1st '08 22-Apr-08 3.60E-06
2nd '08 18-Jun-08 3.20E-05
4th '08 12-Dec-08 l.50E-04
1st '09 28-Apr-09 5.90E-04
2nd '09 l 7-Jun-09 l.90E-05
4th '09 18-Dec-09 1.?0E-04
1st '10 13-May-10 2.20E-04
2nd '10 18-Jun-10 6.50E-05
4th '10 20-Dec-lO 2.30E-05
2nd 'I I 23-Jun-l l 2.40E-07
3rd '11 27-Jul-l l 4.90E-06
4th '11 23-Nov-l I 7.20E-06
2nd '12 l l-Apr-12 4.40E-05
3rd '12 l l-Jun-12 2.20E-05
4th '12 06-Nov-12 3.lOE-05
2nd '13 30-Apr-13 1.14E-04
3rd '13 20-Jun-13 8.91E-05
4th '13 14-Nov-13 I .37E-04
2nd '14 16-Apr-14 9.90E-05
3rd '14 IO-Jun-14 2.60E-05
4th '14 25-Nov-14 2.98E-05
I st '15 21-Apr-l 5 7.15E-04
2nd '15 15-Jun-15 l.52E-04
4th '15 23-Nov-15 2.34E-04
2nd '16 14-Apr-16 4.0SE-04
2nd '16 14-Jun-16 5.92E-05
4th '16 l l-Nov-16 4.56E-05
2nd '17 13-Apr-17 1.71E-04
2nd '17 19-Jun-17 2.40E-05
4th '17 02-Nov-17 8.03E-05
2nd'l8 26-Apr-18 9.48E-05
2nd '18 20-Jun-18 l.92E-04
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
l.30E-06 3.60E-07
l.30E-06 3.60E-07
3.50E-06 I .50E-07
3.70E-06 1.IOE-07
3.40E-06 l.80E-07
5.50E-06 2.00E-08
3.00E-06 I .40E-07
l.50E-06 l.80E-07
3.00E-06 1.1 OE-I 0
5.00E-06 5.00E-08
3.lOE-06 5.00E-08
4.60E-06 l.90E-07
4.40E-06 l.90E-07
l.60E-06 l.90E-07
8.20E-06 2.00E-07
3.00E-06 5.20E-07
3.20E-06 l.80E-06
5.20E-06 9.90E-07
l.35E-05 l.50E-06
l .45E-06 4.90E-07
5.90E-06
7.20E-06 l.lOE-06
3.40E-06 7.60E-07
1.?0E-06 5.20E-07
l.40E-07 l.80E-07
6.30E-07 3.20E-07
7.50E-07 2.90E-07
l.90E-06 3.60E-07
8.40E-07 l.lOE-07
4.82E-07 4.63E-08
l.74E-06 5.34E-07
2.16E-06 l .42E-06
3.87E-06 4.71E-06
l.OlE-06 3.91E-07
8.46E-07 9.19E-07
I .23E-06 l.30E-06
8.01 E-06 3.50E-06
3.48E-06 2.60E-06
5.79E-06 3.89E-06
7.26E-06 5.42E-06
2.70E-06 4.00E-06
2.IOE-06 3.47E-06
(5.00E-08)
4.59E-06 4.06E-06
(5.00E-08)
9.69E-07 1.15E-06
(5.00E-08)
2.18E-06 2.31E-06
(5.00E-08)
l.83E-06 1.16E-6
(5.00E-08)
4.37E-06 3.52E-6
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLDuCi/Kg VALUE ERROR
(uCi/Kg) (uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg)
1.13E-05 1.61E-06 3.36E-06 NS NA
3.26E-06 2.00E-06 7.38E-08 NS NA
4.05E-05 5.82E-06 8.30E-07 NS NA
5.88E-05 3.00E-06 5.50E-07 NS NA
6.42E-05 5.90E-06 9.00E-07 NS NA
2.48E-04 1.40E-05 3.00E-07 NS NA
5.80E-05 4.00E-06 6.90E-07 NS NA
1.IOE-05 l.20E-05 9.00E-07 NS NA
1.70E-06 6.40E-07 5.50E-10 NS NA
3.40E-04 I .20E-05 1.00E-06 NS NA
l.16E-04 6.IOE-06 1.00E-06 NS NA
3.28E-04 9.50E-06 9.50E-07 NS NA
3.40E-04 8.70E-06 8.4-07 NS NA
l.20E-04 6.60E-06 9.70E-07 NS NA
5.00E-04 2.00E-05 l.20E-06 NS NA
2.30E-04 l.40E-05 l.OOE-06 NS NA
6.90E-05 3.50E-05 5.50E-05 NS NA
3.60E-04 2.90E-05 3.90E-05 NS NA
3.40E-04 l.30E-05 l.50E-06 NS NA
3.60E-05 I.IOE-05 l.80E-05 NS NA
4.80E-04 1.20E-05 NS NA
I .90E-04 1.90E-05 2.90E-05 NS NA
l.40E-04 1.90E-05 2.90E-05 NS NA
I.OOE-05 l.50E-06 2.30E-06 NS NA
<2.9E-06 l.70E-06 2.90E-06 NS NA
9.SOE-05 2.IOE-06 2.50E-06 NS NA
8.80E-08 4.30E-07 7.20E-07 NS NA
2.JOE-04 2.00E-06 l.OOE-06 NS NA
l.30E-04 7.60E-06 5.90E-06 NS NA
4.26E-04 3.72E-06 6.52E-07 NS NA
2.65E-04 4.41E-06 5.37E-06 NS NA
l .42E-04 3.68E-06 6.l?E-06 NS NA
5.33E-04 l.45E-05 2.27E-05 NS NA
l.99E-04 3.14E-06 3.38E-06 NS NA
5.60E-05 3.08E-06 7.12E-06 NS NA
2.46E-04 5.38E-06 7.41 E-06 NS NA
5.85E-04 l.27E-05 2.51 E-05 6.36E-04 2.70E-05
4.49E-04 l .50E-05 3.33E-05 3.IIE-04 I .58E-05
9.34E-04 l .36E-05 l .37E-05 2.73E-04 l.91E-05
l.34E-03 2.16E-05 2.93E-05 l.69E-04 l.29E-05
2.61E-04 2.09E-05 4.92E-05 2.lOE-04 5.52E-06
2.70E-04 1.43E-05 3.81E-05 3.94E-05 5.94E-06
(l.OOE-06)
6.l lE-04 l.34E-05 2.l 7E-05 2.38E-04 5.71E-06
(I.OOE-06)
7.52E-06 l.72E-06 5.42E-06 l.31E-04 4.21E-06
(l.OOE-06)
6.13E-04 1.IOE-05 l.58E-05 l.15E-04 3.99E-06
(l.OOE-06)
4.53E-04 9.39E-06 I .57E-05 3.15E-04 6.25E-06
(l.OOE-06)
4.65E-04 l.19E-05 2.37E-05 2.97E-04 6.57E-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
8.62E-06 I.OlE-04
6.45E-06 4.19E-05
6.31 E-06 6.67E-06
5.76E-06 l.66E-05
l.70E-06 4.27E-06
5.02E-06 2.IOE-06
(2.00E-07)
2.31E-06 l.54E-05
(2.00E-07)
1.15E-06 7.18E-06
(2.00E-07)
l.74E-06 1.04E-05
(2.00E-07)
l.87E-06 3.36E-06
(2.00E-07)
l.85E-06 l.92E-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
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.IOE-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 l.05E-06
(2.00E-07)
l.41E-06 2.88E-06
(2.00E-07)
1.58E-06 l.22E-06
(2.00E-07)
¥ The value in the MDC column is the sample-specific minimum detectable concentration. The MDC is based on the sample moisture, composition and other sample-specific variables. The value in
parantheses is the method-specific lower limit of detection (LLD), which is a limit representing the detection capability of the measurement system. The LLDs in the data package are referred to as
the Reporting limit (RL).
(Log Scale) ...... ...... ...... ...... ......
0 0 0 0 0 0 0 0 0 0 0 0 0 0 m m m m m m m I 6 I I I I I 0 0 0 0 0 0 CX) ---.I 0) 01 ~ w I\J
01-Aug-81 :E 01 -Jul-82 ::c
01-Jun-83 =i m 01-May-84 s:: 01-Apr-85 m en 01-Mar-86 )>
01-Feb-87 s::
01-Jan-88 r r
01-Dec-88 I
01-Nov-89 z
0
01-0ct-90 JJ -f
t 01-Sep-91 ::c m
01-Aug-92 )>
:IJ en Ill 01-Jul-93 -f "' N 01-Jun-94 0 0)
"T1
T
01-May-95 s::
01-Apr-96 r -u r O" "' 01-Mar-97 JJ ..... C> 0 01-Feb-98 C.
f 01-Jan-99 o· :::,
01-Dec-99 C
C (') z 01-Nov-OO a: )> -I 01-0ct-01 CD
0 t 01-Sep-02 0 :::, 01-Aug-03 (')
-I CD I 01-Jul-04 :::, "' -c..:, 01-Jun-05 "'I
N C> -01-May-06 o· :::,
01-Apr-07 en
01-Mar-08 :::,
< 01-Feb-09 CD co 01-Jan-10 CD -01-Dec-10 C> -01-Nov-11 s· :::,
01-0ct-12 -C
01-Sep-13 0 :::::.:
01-Aug-14 -" co
01-Jul-15 -
01-Jun-16
01-May-17
01-Apr-18
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 '8 1 20-0ct-81 2.00E-04
2nd '82 I 5-Apr-82 l.04E-04
3rd '82 OJ -Jul-82 2.00E-OS
4th '82 30-Nov-82 2.36E-06
2nd '83 13-Apr-83 8.S8E-05
3rd '83 Ol -Jul-83 l.l9E-04
4th '83 30-Jan-84 9.78E-OS
2nd '84 28-Jun-84 2.08E-04
4th '84 14-Nov-84 6.0SE-04
2nd'85 27-Mar-85 l.lOE-04
3rd '85 l 5-Jul-85 6.JOE-OS
4th '85 09-0ct-85 l.07E-04
2nd '86 24-Mar-86 8.86E-04
3rd '86 JO-Jul-86 6.66E-04
4th '86 I 8-Dec-86 5.20E-04
2nd'87 20-Apr-87 4.JOE-04
3rd '87 OS-Jun-87 l.60E-04
4th '87 22-Dec-87 3.60E-04
2nd '88 l 9-Apr-88 2.60E-04
3rd '88 28-Jul-88 3.IOE-OS
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 l.70E-04
3rd '90 17-0ct-90 8.80E-OS
I st '91 JO-Apr-91 3.00E-04
2nd '91 l l-Jun-91 3.lOE-04
3rd '91 20-Nov-91 5.00E-04
1st '92 22-Apr-92 2.00E-05
2nd '92 I O-Jun-92 6.SOE-06
3rd '92 JO-Jun-92 l.20E-04
1st '93 13-Apr-93 I.SOE-OS
2nd '93 26-Jun-93 5.20E-OS
3rd '93 12-0ct-93 5.JOE-OS
!st '94 11-May-94 J.20E-04
2nd '94 19-Jul-94 3.73E-05
3rd '94 28-Nov-94 2.40E-04
1st '95 l l-Apr-95 8.40E-05
2nd '95 06-Jul-95 l.90E-05
3rd '95 15-Nov-95 l.20E-04
I st '96 23-Apr-96 8.30E-05
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96 3.60E-05
1st '97 21-Apr-97 3.30E-05
3rd '97 05-Sep-97 5.40E-06
4th '97 20-Nov-97 8.90E-06
1st '98 23-Mar-98 <9.20E-05
2nd'98 l 6-Jun-98 < 6.SOE-08
4th '98 05-Nov-98 4.20E-OS
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 '00 21-Aor-OO 3.?0E-05
2nd '00 22-Jun-OO 2.90E-05
4th '00 21-Dec-00 2.30E-06
1st '01 30-Apr-01 2.JOE-05
2nd '01 14-Jun-01 l.30E-06
4th 'Ol 17-Dec-OI 3.?0E-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) (5.0E-08) (uCi/Kg)
5.00E-05 S.OOE-08 7.IOE-03
I.OOE-05 S.OOE-08 8.30E-04
9.00E-06 7.00E-06 6.40E-04
1.00E-05 S.OOE-08 2.20E-04
9.SOE-07 I.OOE-06 8.00E-05
l.36E-05 2.00E-08 3.53E-04
J.JOE-05 5.00E-06 l .58E-04
7.00E-06 2.00E-06 2.16E-03
I.OOE-05 3.00E-09 l.60E-03
l.64E-04 2.00E-07 2.58E-03
8.00E-06 3.00E-06 8.63E-04
6.00E-06 2.00E-06 5.40E-04
6.00E-06 2.00E-06 3.80E-04
l .80E-05 2.00E-06 4.40E-03
J .80E-05 3.00E-06 4.78E-03
I.OOE-04 3.00E-06 1.70E-03
I.OOE-04 5.00E-08 I.60E-03
3.00E-OS 5.00E-08 S.SOE-04
5.00E-05 5.00E-08 l .80E-03
5.00E-05 5.00E-08 l .90E-03
l.90E-05 S.OOE-08 J.60E-04
5.00E-05 *** 1.?0E-03
3.00E-OS *** 7.40E-04
6.00E-OS 7.00E-06 l.OOE-03
3.00E-05 4.00E-06 4.80E-04
2.00E-05 S.OOE-08 3.20E-04
J.60E-05 5.00E-08 2.90E-04
3.00E-05 5.00E-06 4.IOE-04
3.00E-05 2.00E-07 4.?0E-04
4.00E-OS 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-OS 3.00E-06 1.21 E-03
l.?OE-05 3.00E-06 2.IOE-04
1.90E-05 3.00E-06 l.?OE-05
2.30E-05 3.00E-06 7.JOE-04
I.OOE-05 3.00E-05 9.80E-04
l.60E-06 8.40E-08 7.80E-05
I.SOE-OS l.?OE-07 2.60E-04
6.JOE-06 l .50E-07 J.20E-04
I .50E-06 l .40E-07 4.50E-05
6.SOE-06 l.40E-07 l.OOE-05
3.30E-06 l.90E-07 6.80E-05
2.SOE-06 l.60E-07 8.SOE-05
2.30E-06 J.?OE-07 4.40E-05
3.50E-07 l.56E-07 3.20E-05
7.20E-07 5.40E-07 3.40E-04
9.20E-05 9.20E-05 <4.60E-04
6.50E-08 6.SOE-08 <3.20E-07
l.OOE-06 l.lOE-07 l.?OE-04
J .OOE-06 l.OOE-07 l.40E-04
J .40E-06 8.30E-08 9.20E-05
3.00E-06 2.20E-07 2.SOE-05
l.OOE-06 2.40E-07 2.?0E-04
I.OOE-06 3.30E-07 2.80E-04
l.40E-06 3.70E-07 3.30E-04
J.OOE-06 l .50E-07 <7.6E-07
4.00E-08 l.20E-07 l.80E-06
7.67E-07 8.30E-08 6.72E-05
2.40E-06 7.60E-07 l.28E-04
4.32E-06 7.60E-07 8.33E-05
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR LLDuCi/Kg VALUE ERROR LLD VALUE ERROR LLD
(uCi/Kg) (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-OS l.OOE-06 NS NA NA NS NA NA
5.00E-OS 4.00E-05 NS NA NA NS NA NA
9.00E-05 l.OOE-07 NS NA NA NS NA NA
J.OOE-05 l.OOE-05 NS NA NA NS NA NA
J.90E-OS l.OOE-05 NS NA NA NS NA NA
J.30E-OS l.OOE-05 NS NA NA NS NA NA
3.40E-04 3.00E-04 NS NA NA NS NA NA
7.00E-05 3.00E-08 NS NA NA NS NA NA
l.JOE-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
J.OOE-04 6.00E-05 NS NA NA NS NA NA
I.OOE-04 l.OOE-06 NS NA NA NS NA NA
4.00E-05 l.OOE-06 NS NA NA NS NA NA
J.OOE-04 J.OOE-06 NS NA NA NS NA NA
J.OOE-04 J.OOE-06 NS NA NA NS NA NA
4.00E-05 J.OOE-06 NS NA NA NS NA NA
I.OOE-04 *** NS NA NA NS NA NA
3.00E-05 *** NS NA NA NS NA NA
7.00E-OS J .40E-05 NS NA NA NS NA NA
2.00E-OS 2.20E-05 NS NA NA NS NA NA
2.00E-OS 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
1.00E-04 l.OOE-06 NS NA NA NS NA NA
I .40E-OS l.OOE-05 NS NA NA NS NA NA
2.00E-OS J.OOE-06 NS NA NA NS NA NA
8.00E-OS 2.00E-05 NS NA NA NS NA NA
3.00E-OS 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
J.60E-04 2.00E-04 NS NA NA NS NA NA
7.JOE-06 4.20E-07 NS NA NA NS NA NA
l.30E-05 8.30E-07 NS NA NA NS NA NA
J.JOE-05 7.50E-05 NS NA NA NS NA NA
4.30E-06 7.20E-07 NS NA NA NS NA NA
5.SOE-06 7.JOE-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.?0E-06 l.JOE-07 NS NA NA NS NA NA
4.60E-04 4.60E-04 NS NA NA NS NA NA
3.20E-07 3.20E-07 NS NA NA NS NA NA
I.OOE-05 5.SOE-07 NS NA NA NS NA NA
7.00E-06 l.OOE-07 NS NA NA NS NA NA
4.00E-06 4.20E-07 NS NA NA NS NA NA
l.OOE-06 l.lOE-06 NS NA NA NS NA NA
l.OOE-05 l.20E-06 NS NA NA NS NA NA
2.00E-OS l.?OE-06 NS NA NA NS NA NA
5.00E-05 l.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 J.OOE-05 NS NA NA NS NA NA
4.32E-06 l.OOE-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
NORTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
4th '02 15-Dec-02 l.50E-04
1st '03 21-Mar-03 5.00E-05
2nd'03 10-Jun-03 5.60E-05
4th '03 20-Nov-03 3.20E-04
!st '04 08-Apr-04 6.29E-05
2nd '04 J 2-Jun-04 6.51 E-05
4th '04 30-Nov-04 7.SOE-05
!st '05 21-Apr-05 4.90E-05
2nd '05 13-Jun-05 2.30E-05
4th '05 IO-Nov-05 7.40E-05
1st '06 03-Apr-06 l.OOE-04
2nd '06 !6-Jun-06 9.50E-05
4th '06 28-Nov-06 8.l 3E-05
1st '07 30-Mar-07 4.30E-05
2nd'07 l-Jun-07 5.IOE-05
4th '07 23-Nov-07 7.30E-05
1st '08 22-Apr-08 2.80E-06
2nd '08 J 8-Jun-08 3.20E-06
4th '08 J 2-Dec-08 7.30E-05
!st '09 28-Apr-09 5.25E-05
2nd'09 l 7-Jun-09 2.30E-05
4th '09 I 8-Dec-09 5.SOE-05
1st 'JO l 3-May-10 l.90E-04
2nd '10 18-Jun-lO 2.30E-05
4th 'JO 20-Dec-lO 8.60E-06
2nd 'I I 23-Jun-l l 2.IOE-07
3rd 'I I 28-Jul-l l 4.20E-06
4th']] 23-Nov-l l 7.70E-06
2nd '12 l l-Apr-12 l .SOE-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 IO-Jun-14 2.53E-05
4th '14 25-Nov-14 7.4lE-05
!st '15 21-Apr-15 l .31E-04
2nd '15 l 5-Jun-15 2.39E-04
4th '15 23-Nov-15 l.03E-04
2nd '16 14-Apr-16 1.28E-04
2nd '16 14-Jun-16 5.91E-05
4th '16 ll-Nov-16 2.66E-04
2nd '17 13-Apr-l 7 3.84E-05
2nd '17 19-Jun-17 l.56E-04
4th '17 02-Nov-17 2.24E-04
2nd '18 26-Apr-18 2.63E-04
2nd '17 20-Jun-18 2.13E-04
Ra-226 MDC¥
ERROR LLDuCi/Kg
(uCi/Kg) (5.0E-08)
6.20E-06 7.60E-07
3.40E-06 2.71 E-06
2.00E-06 4.IOE-07
8.20E-06 1.70E-07
4.IOE-06 2.00E-07
3.40E-06 I .30E-07
4.60E-06 2.00E-08
2.70E-06 l.30E-07
2.IOE-06 l.50E-07
3.SOE-06 l.20E-IO
6.00E-06 5.00E-08
5.90E-06 5.00E-08
4.IOE-06 2.20E-07
2.60E-06 1.70E-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.SOE-06
6.IOE-06 9.40E-07
2.00E-06 7.70E-07
9.IOE-07 3.90E-07
l .20E-07 l.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
l .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
l.90E-06 J .53E-06
4.2lE-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.l 7E-06 2.0IE-06
(5.00E-08)
2.93E-06 7.38E-7
(5.00E-08)
4.85E-06 3.93E-06
(5.00E-08)
Pb-210 Pb-210 MDC¥ U-NAT U-NAT
VALUE ERROR LLDuCi/Kg VALUE ERROR
(uCi/Kg) (uCi/Kg) (l.OE-06) (uCi/Kg) (uCi/Kg)
3.l6E-04 J .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 I .25E-05 8.30E-07 NS NA
l .94E-05 4.00E-06 l.OOE-06 NS NA
l .87E-05 3.90E-06 6.50E-07 NS NA
4.45E-04 l .40E-05 3.00E-07 NS NA
l .27E-04 4.80E-06 6.50E-07 NS NA
4.70E-05 5.IOE-06 7.60E-07 NS NA
2.40E-06 8.IOE-08 5.80E-IO NS NA
6.54E-04 l.50E-05 I.OOE-06 NS NA
4.48E-04 l.40E-05 I .OOE-06 NS NA
3.25E-04 1.12E-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 l.OOE-06 NS NA
l.40E-04 3.30E-05 5.50E-05 NS NA
4.40E-04 2.50E-05 3.20E-05 NS NA
l.90E-04 l.50E-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 l.80E-05 2.90E-05 NS NA
1.IOE-07 6.80E-07 1.IOE-06 NS NA
<2.2E-06 l.30E-06 2.20E-06 NS NA
2.30E-04 2.SOE-06 2.30E-06 NS NA
<5.8E-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.!8E-07 NS NA
2.24E-04 4.46E-06 4.68E-06 NS NA
l.06E-04 2.30E-06 3.28E-06 NS NA
4.65E-04 1.l 7E-05 1.SOE-05 NS NA
5.70E-05 2.21 E-06 4.52E-06 NS NA
7.68E-05 2.0SE-06 3.66E-06 NS NA
2.98E-04 6.48E-06 l.06E-05 NS NA
6.33E-04 l.17E-05 l .45E-05 3.35E-04 2.4lE-05
l.OSE-03 2.02E-05 3.25E-05 5.24E-04 2.41E-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
l.73E-04 2.02E-05 5.42E-05 3.l 5E-05 l.90E-06
l .28E-03 2.57E-05 4.95E-05 4.33E-04 2.58E-05
(l.OOE-06)
8.85E-04 l.51E-05 2.23E-05 6.97E-04 l.21E-05
(l.OOE-06)
1.15E-04 3.l SE-06 6.07E-06 3.29E-04 6.61E-06
(l.OOE-06)
9.23E-04 l.34E-05 l.94E-05 3.34E-04 9.09E-06
(l.OOE-06)
5.85E-04 9.12E-06 8.17E-6 4.60E-04 7.74E-06
(l.OOE-06)
6.02E-04 l.28E-05 2.33E-05 4.98E-04 9.07E-06
(J.OOE-06)
*2nd quarter of 1996 San Juan County, Utah, was declared a disaster area due to drought, no samples were collected during this period
MDC¥ Th-232
LLD VALUE
uCi/Kg (uCi/Kg)
(2.0E-07)
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.l 7E-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.IIE-06
(2.00E-07)
l.44E-06 l.58E-05
(2.00E-07)
3.50E-06 l.52E-05
(2.00E-07)
l.56E-06 5.49E-06
(2.00E-07)
2.43E-06 9.46E-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
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 J.47E-06
7.58E-07 l.03E-06
(2.00E-07)
9.91E-07 l.15E-06
(2.00E-07)
l .37E-06 5.35E-07
(2.00E-07)
l.35E-06 l.80E-07
(2.00E-07)
2.15E-06 3.47E-6
(2.00E-07)
l.05E-06 l.07E-6
(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 6 I ' I ' 0 0 0 0 0 0 (X) -...i 0) c.n .i,.. vJ I\)
01-Aug-81 =E :J:
01-Jul-82 ~
01-Jun-83 m
01-May-84 s: m
01-Apr-85 CJ)
)>
01-Mar-86 s: -01-Feb-87 r
01-Jan-88 r
I
01-Dec-88 z
0 01-Nov-89 lJ
01-0ct-90 --t
t :J:
01-Sep-91 =E m :IJ 01-Aug-92 -CJ) '!' I\) 01-Jul-93 -t I\) 0 0)
01-Jun-94 .,,
T 01-May-95 s: -r iJ 01-Apr-96 r er I\) 01-Mar-97 lJ ~
0 SI)
01-Feb-98 a.
t 01-Jan-99 s· ::,
C C 01-Dec-99 (') z 01-Nov-OO a: )>
-i (I)
01-0ct-01 0 t 01-Sep-02 0 ::,
-i 01-Aug-03 (')
I (I)
I\) 01-Jul-04 ::,
c.J -I\) "'I
01-Jun-05 SI) -01-May-06 s· ::,
01-Apr-07 en
01-Mar-08 s·
~ 01-Feb-09 cc
01-Jan-10 (I) -01-Dec-10 SI) -01-Nov-11 s· ::,
01-0ct-12 -C
01-Sep-13 0 c:::.:
01-Aug-14 ~ cc
01-Jul-15 -
01-Jun-16
01-May-17
01-Apr-18
WHITE MESA MILL
FORAGE RADIONUCLIDE DATA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
3rd '81 27-Aug-81 9.SOE-04
4th '81 20-0ct-81 3.00E-05
2nd'82 15-Apr-82 l.37E-05
3rd '82 OI-Jul-82 3.40E-04
4th '82 30-Nov-82 I .75E-05
2nd "83 13-Apr-83 7.13E-04
3rd '83 OJ-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 IO-Jul-86 3.78E-04
4th '86 18-Dec-86 2.60E-04
2nd '87 20-Apr-87 4.IOE-04
3rd '87 05-Jun-87 2.90E-04
4th '87 22-Dec-87 l.80E-04
2nd '88 19-Apr-88 2.30E-04
3rd '88 28-Jul-88 l.50E-04
2nd '89 07-Apr-89 3.JOE-04
3rd '89 06-Jun-89 l.30E-04
4th '89 07-Nov-89 4.30E-04
1st '90 17-Apr-90 2.50E-04
2nd '90 20-Jun-90 l.lOE-04
3rd '90 l 7-0ct-90 6.JOE-05
1st '91 JO-Aor-91 3.40E-05
2nd '91 I I-Jun-91 8.00E-05
3rd '91 20-Nov-91 6.SOE-05
1st '92 22-Aor-92 l.60E-05
2nd '92 10-Jun-92 l.90E-05
3rd '92 10-Jun-92 l.60E-05
I st '93 I 3-Apr-93 2.60E-05
2nd '93 26-Jun-93 3.00E-05
3rd '93 12-0ct-93 3.IOE-05
1st '94 l l-May-94 2.00E-05
2nd '94 I 9-Jul-94 I .75E-05
3rd '94 28-Nov-94 l.OOE-04
J st '95 I I-Apr-95 l.70E-05
2nd '95 06-Jul-95 6.40E-06
3rd '95 I 5-Nov-95 2.30E-05
1st '96 23-Apr-96 4.20E-05
2nd '96 * 31-Jul-96
3rd '96 14-Nov-96 2.JOE-05
1st '97 2 I-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-Aor-99 2.40E-05
3rd '99 07-Jul-99 2.23E-05
4th '99 02-Dec-99 l.SOE-04
2nd '00 21-Apr-OO l.OOE-04
2nd '00 22-Jun-OO I .30E-06
4th '00 21-Dec-00 l.20E-06
1st '01 30-Apr-01 l.80E-06
2nd 'OJ 14-Jun-01 2.60E-06
4th '01 l 7-Dec-01 2.63E-06
1st '02 07-May-02 3.SOE-05
2nd'02 07-Jul-02 4.02E-05
4th '02 15-Dec-02 8.JOE-05
Ra-226 MDC¥ Pb-210
ERROR LLD uCi/Kg VALUE
(uCi/Kg) (5.0E-08) (uCi/Kg)
2.00E-05 5.00E-08 l .SOE-04
3.00E-06 5.00E-08 l .SOE-04
3.00E-06 3.00E-06 3.80E-04
2.00E-05 5.00E-08 3.68E-03
3.00E-06 2.00E-06 7.92E-04
7.30E-05 9.00E-08 2.51 E-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
l.OOE-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.SOE-04
3.00E-05 5.00E-08 2.40E-03
5.00E-05 5.00E-08 2.90E-03
3.00E-05 5.00E-08 4.30E-03
4.00E-05 *** 4.20E-03
2.00E-05 *** l.50E-03
5.00E-05 I .40E-05 3.SOE-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.JOE-04
l.lOE-05 5.00E-06 2.20E-04
6.00E-06 2.00E-07 l.20E-04
I .40E-05 5.00E-08 9.IOE-04
7.00E-06 2.00E-06 3.20E-04
I.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
l.70E-06 7.60E-08 l.30E-04
9.00E-06 I.SOE-07 2.60E-04
l.50E-06 l.60E-07 l.60E-04
6.00E-07 I .40E-07 4.40E-05
2.20E-06 1.70E-07 6.60E-05
2.20E-06 l.70E-07 I.OOE-04
2.00E-06 l.60E-07 l.90E-04
4.20E-07 I .40E-07 3.30E-05
3.20E-07 J.26E-07 l.90E-05
9.SOE-07 5.90E-07 l.30E-04
7.90E-05 7.90E-05 <3.90E-04
l.40E-07 3.30E-08 <l.7E-07
l.OOE-06 7.60E-08 2.SOE-04
l.OOE-06 l.20E-07 l.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 LIOE-04
I.OOE-07 2.40E-07 2.00E-04
9.00E-07 2.40E-07 l.20E-04
l.OOE-07 I.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 l.36E-04
2.34E-06 7.60E-07 7.04E-05
3.90E-06 7.60E-07 2.87E-04
Pb-210 MDC¥ U-NAT U-NAT MDC¥ Th-232 Th-232 MDC¥
ERROR 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
l.OOE-05 l.OOE-06 NS NA NA NS NA NA
2.00E-05 J.OOE-06 NS NA NA NS NA NA
4.00E-05 4.00E-05 NS NA NA NS NA NA
2.70E-04 J.OOE-07 NS NA NA NS NA NA
4.00E-06 2.00E-05 NS NA NA NS NA NA
3.00E-04 3.00E-04 NS NA NA NS NA NA
4.30E-05 4.00E-05 NS NA NA NS NA NA
I .OOE-04 4.00E-05 NS NA NA NS NA NA
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
I.OOE-04 7.00E-05 NS NA NA NS NA NA
l.80E-04 3.00E-05 NS NA NA NS NA NA
7.00E-04 l.OOE-04 NS NA NA NS NA NA
l.OOE-04 I.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 I.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
l.OOE-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 I.OOE-06 NS NA NA NS NA NA
l.OOE-05 I.OOE-06 NS NA NA NS NA NA
l.OOE-05 2.00E-07 NS NA NA NS NA NA
5.00E-05 I.OOE-06 NS NA NA NS NA NA
2.00E-05 J.OOE-05 NS NA NA NS NA NA
2.00E-05 I.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
I .20E-05 7.40E-07 NS NA NA NS NA NA
I .50E-05 8.JOE-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 J .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
J.70E-07 i.70E-07 NS NA NA NS NA NA
l.OOE-05 3.80E-07 NS NA NA NS NA NA
8.00E-06 6.20E-07 NS NA NA NS NA NA
7.00E-06 5.90E-07 NS NA NA NS NA NA
I.OOE-06 l.OOE-06 NS NA NA NS NA NA
7.00E-06 6.IOE-07 NS NA NA NS NA NA
I.OOE-05 I .20E-06 NS NA NA NS NA NA
3.00E-05 1.20E-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
5.61 E-06 I.OOE-05 NS NA NA NS NA NA
4.IJE-06 l.OOE-05 NS NA NA NS NA NA
8.54E-06 l.OOE-05 NS NA NA NS NA NA
WHITE MESA MILL
FORAGE RADIONUCLIDE DA TA
SOUTHWEST OF MILL
SAMPLED SAMPLED Ra-226
QTR. DATE
VALUE
(uCi/Kg)
!st '03 21-Mar-03 3.70E-05
2nd '03 JO-Jun-03 I .30E-05
4th '03 20-Nov-03 l.60E-04
1st '04 08-Apr-04 I .40E-04
2nd '04 I 2-Jun-04 6.SJE-05
4th '04 30-Nov-04 8.40E-05
1st '05 2 I-Apr-05 l.?OE-05
2nd'05 13-Jun-05 l .SOE-05
4th '05 10-Nov-05 3.SOE-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
1st '07 30-Mar-07 3.00E-05
2nd '07 l-Jun-07 I.IOE-04
4th '07 23-Nov-07 5.60E-05
1st '08 22-Apr-08 3.20E-05
2nd '08 I 8-Jun-08 l .25E-05
4th '08 12-Dec-08 9.20E-05
Isl '09 28-Apr-09 2.60E-05
2nd '09 17-Jun-09 2.40E-05
4th '09 I 8-Dec-09 3.JOE-05
1st '10 13-May-10 2.00E-05
2nd 'JO 18-Jun-10 I.JOE-05
4th 'IO 20-Dec-10 6.70E-06
2nd '11 23-Jun-l l <l.?E-07
3rd '11 27-Jul-l 1 l.60E-05
4th '11 23-Nov-l l 7.80E-07
2nd'l2 l l-Apr-12 5.00E-06
3rd '12 l l-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 '1 3 14-Nov-13 l.l8E-04
2nd '14 16-Apr-14 4.65E-05
3rd '14 IO-Jun-14 l.23E-05
4th '14 25-Nov-14 1.16E-04
l st '15 21-Apr-15 2.27E-04
2nd '15 l 5-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 l l-Nov-16 8.39E-05
2nd '17 13-Apr-l 7 3.05E-05
2nd '17 19-Jun-17 3.98E-05
4th '17 02-Nov-17 9.70E-05
2nd '18 26-Apr-18 5.16E-05
2nd '18 20-Jun-18 5.14E-05
Ra-226
ERROR
(uCi/Kg)
2.60E-06
l.OOE-06
l.30E-05
7.70E-06
3.20E-06
5.70E-06
1.60E-06
l.60E-06
2.IOE-06
6.00E-06
2.SOE-06
3.20E-06
2.20E-06
4.60E-06
5.20E-06
2.30E-06
2.20E-06
4.IOE-06
2.90E-06
l.40E-06
2.30E-06
2.IOE-06
l .30E-06
9.!0E-07
6.90E-08
l.OOE-06
2.50E-07
6.00E-07
6.20E-08
3.41 E-07
l.19E-06
l.06E-06
3.39E-06
l.08E-06
4.97E-07
2.25E-06
5.0IE-06
1.SSE-06
6.96E-06
4.lOE-06
l.SSE-06
2.7 IE-06
2.30E-06
l.l7E-06
3.12E-06
1.2 JE-06
2.70E-06
MDC¥ Pb-210 Pb-210 MDC¥ U-NAT U-NAT
LLDuCi/Kg VALUE ERROR LLDuCi/Kg VALUE ERROR
(5.0E-08) (uCi/Kg) (uCi/Kg) (1.0E-06) (uCi/Kg) (uCi/Kg)
2.4JE-06 2.69E-05 2.0IE-06 3.73E-06 NS NA
5.20E-07 <I .OOE-07 I .OOE-07 NS NA
I .20E-07 I .42E-04 6.42E-06 5.90E-07 NS NA
J.JOE-07 6.JOE-06 2.70E-06 5.50E-07 NS NA
J.SOE-07 5.27E-05 4.90E-06 7.60E-07 NS NA
3.00E-08 3.39E-04 1.60E-05 3.00E-07 NS NA
1.30E-07 4.SOE-05 3.SOE-06 6.SOE-07 NS NA
1.40E-07 7.00E-05 5. IOE-06 6.90E-07 NS NA
8.60E-IO l.20E-06 4.SOE-08 4.30E-IO NS NA
5.00E-08 3.30E-04 1.IOE-05 l.OOE-06 NS NA
5.00E-08 l.37E-04 6.00E-06 I.OOE-06 NS NA
I .60E-07 2.98E-04 8.SOE-06 8.20E-07 NS NA
l.70E-07 3.20E-04 7.90E-06 8.40E-07 NS NA
2.3-07 3.20E-04 1.IOE-05 l.lOE-06 NS NA
5.00E-08 6.40E-04 l.90E-05 l.OOE-06 NS NA
7.20E-07 2.30E-04 I .SOE-05 l.OOE-06 NS NA
l.80E-06 5.00E-05 3.00E-05 4.80E-03 NS NA
9.60E-07 4.IOE-04 3.00E-05 4.00E-05 NS NA
l.40E-06 3.70E-05 l.50E-06 2.50E-05 NS NA
3.90E-07 3.SOE-05 7.90E-06 I .30E-05 NS NA
2.IOE-04 8.40E-06 NS NA
9.40E-07 5.60E-05 l .50E-05 2.40E-05 NS NA
6.60E-07 7.80E-05 l.60E-05 2.50E-05 NS NA
4.80E-07 8.00E-07 7.90E-07 l.30E-06 NS NA
1.70E-07 <2.5E-06 l.SOE-06 2.50E-06 NS NA
2.60E-07 9.50E-05 l.60E-06 1.70E-06 NS NA
2.30E-07 <5.9E-07 3.50E-07 5.90E-07 NS NA
3.00E-07 <7.0E-07 7.00E-07 l.OOE-06 NS NA
l.lOE-07 <2.5E-07 l .30E-06 2.20E-06 NS NA
4.25E-08 4.45E-04 4.01 E-06 8.57E-07 NS NA
5.39E-07 3.62E-04 6.30E-06 9.90E-06 NS NA
l.96E-06 6.71E-05 2.93E-06 6.24E-06 NS NA
2.97E-06 5.92E-04 l.27E-05 1.62E-05 NS NA
7.35E-07 2.l3E-04 5.93E-06 1.31E-05 NS NA
6.97E-07 2.46E-05 l.84E-06 4.63E-06 NS NA
l.53E-06 4.43E-04 l.04E-05 l .94E-05 NS NA
4.08E-06 5.90E-04 1.16E-05 I .67E-05 4.33E-04 1.86E-05
2.71E-06 5.29E-04 l.61E-05 3.36E-05 7.78E-05 8.47E-06
9.64E-06 8.94E-04 l.43E-05 2.03E-05 4.88E-04 2.91E-05
3.65E-06 7.99E-04 2.0SE-05 4.12E-05 2.JOE-04 2.24E-05
3.85E-06 1.95E-04 2.l 8E-05 5.93E-05 7.04E-05 3.17E-06
3.21E-06 1.21E-03 2.15E-05 3.78E-05 1.27E-03 4.84E-05
(5.00E-08) (I.OOE-06)
4.61E-06 6.14E-04 l.26E-05 l.7 IE-05 8.20E-04 I .28E-05
(5.00E-08) (l.OOE-06)
l.04E-06 5.25E-05 2.68E-06 5.93E-06 l.77E-04 4.52E-06
(5.00E-08) (1.00E-06)
3.05E-06 6.36E-04 l.14E-05 1.72E-05 2.52E-04 7.28E-06
(5.00E-08) (l.OOE-06)
8.lOE-07 3.83E-04 8.29E-06 l.51E-05 4.02E-04 6.92E-06
(5.00E-08) (l.OOE-06)
4,37E-06 9.22E-05 7.25E-06 2.0SE-05 1.49E-04 4.7LE-06
(5.00E-08) (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
5.14E-06 3.31E-05
6.43E-06 l.08E-05
9.00E-06 7.92E-06
l .39E-05 5.58E-05
l.92E-06 3.70E-06
1.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)
l.50E-06 4.93E-06
(2.00E-07)
2.17E-06 3.18E-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 l.14E-06
1.28E-06 1.21E-06
7.67E-07 3.20E-07
5.42E-06 2.IOE-06
8.0SE-07 J.04E-06
l.OSE-06 l.32E-06
(2.00E-07)
7.40E-07 1.21 E-06
(2.00E-07)
l.l2E-06 1.0?E-06
(2.00E-07)
l.05E-06 2.I IE-06
(2.00E-07)
1.99E-06 3.69E-06
(2.00E-07)
5.81 E-07 7.45E-07
(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 I I 6 6 I I + 0 0 0 0 0 0 0 CX) --..J 0) (]1 .i:,. w I\) _. 0
01-Aug-81 ' ~ ::c
01-Jul-82 =i
01-Jun-83 m
is: 01-May-84 m
01-Apr-85 en >
01-Mar-86 is:
01-Feb-87 r-r-
01-Jan-88 I
01-Dec-88 en
0
01-Nov-89 C -I
t 01-0ct-90 ::c
01-Sep-91 ~ m ::IJ 01-Aug-92 en i:i' -I I\)
I\) 01-Jul-93 0 en
01-Jun-94 .,,
T 01-May-95 is: -r-"U 01-Apr-96 r-O' ~ 01-Mar-97 JJ
0 SI)
01-Feb-98 a.
t er
01-Jan-99 :::,
C
C 01-Dec-99 C, z 01-Nov-OO a: :t> -I (D
t 01-0ct-01 0
01-Sep-02 0 :::,
C, -I 01-Aug-03 (D I rG 01-Jul-04 :::, -(,) ""I I\) SI) 01-Jun-05 -01-May-06 o· :::,
01-Apr-07 t/1
:::, 01-Mar-08 <
01-Feb-09 (D
(Q
01-Jan-10 (D -SI) 01-Dec-10 -o·
01-Nov-11 :::,
01-0ct-12 -C
01-Sep-13 0 =:::.:
01-Aug-14 ;:,ic:
(Q -01-Jul-15
01-Jun-16
01-May-17
01-Apr-18
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: May 25, 2018
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Contact:
Project:
Lakewood, Colorado 80228
Ms. Kathy W einel
Vegetation Analysis
Client Sample ID: North East
Sample ID: 449032001
Matrix: SOLID
Collect Date:
Receive Date:
26-APR-18 10:00
30-APR-18
Collector: Client
Parameter Qualifier Result Uncertainty
lad Alpha Spec Analysis
'\lphaspec Th-232, Solid "As Received"
~horium-232 3.36E-06 +/-1.41 E-06
'\lphaspec U, Solid "As Received"
Jranium-233/234 0.000148 +/-2.69E-06
Jranium-235/236 I.OIE-05 +/-7.88E-07
Jranium-238 0.000157 +/-2. 77E-06
lad Gas Flow Proportional Counting
]FPC, Pb2 l 0, Solid "As Received"
,ead-210 0.000453 +/-9.39E-06
]FPC, Total Alpha Radium, solid "As Received"
~otal Radium 9.84E-05 +/-I.83E-06
rhe following Prep Methods were performed:
v1ethod Description
MDC RL
2.88E-06 2.00E-07
7.74E-07 2.00E-07
4.60E-07 2.00E-07
5.98E-07 2.00E-07
l.57E-05 l.OOE-06
1.16E-06 5.00E-08
Analyst
Project:
Client ID:
Units PF
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
DNMI00101
DNMI001
DF Analyst Date
HAKB 05/24/18
HAKB 05/22/18
KSDI 05/22/18
KSDI 05/21/18
Date Time Prep Batch ---)ry Soil Prep Dry Soil Prep GL-RAD-A-021 CXCl
The following Analytical Methods were performed: -----------
\1ethocl_ Descr!J)tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.I Modified
;urrogate/Tracer Recovery Test
ihorium-229 Tracer
Jranium-232 Tracer
,ead Carrier
3ari um Carrier
~otes:
Alphaspec Th-232, Solid "As Received"
Alphaspec U, Solid "As Received"
GFPC, Pb210, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
:::ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
05/01/18
Result
0956 1760390
Analyst Comments
Nominal Recovery%
73.6
86.5
95.8
103
Time Batch Method
0908 1760395
1332 1760396
0626 1762781
1748 1762780
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: May 25, 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 East
449032001
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
Company :
Address:
Contact:
Project: -----Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www .gel.com
Certificate of Analysis
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis -------North East
453309001
Vegetation
20-JUN-18 13:00
26-JUN-18
Client
Project:
Client ID:
Report Date:
DNMIOOIOI
DNMIOOI
July 25, 2018
Parameter Qualifier Result Uncertainty MDC RL Units PF DF Analyst Date Time Batch Method
lad Alpha Spec Analysis
\lphaspec Th-232, Solid "Dry Weight Corrected"
~horium-232 l.92E-05 +/-1.58E-06 l.22E-06
\lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 0.000142 +/-2.89E-06 5.97E-07
Jranium-235/236 7.14E-06 +/-7.39E-07 6.91E-07
Jranium-238 0.000148 +/-2.94E-06 5.59E-07
lad Gas Flow Proportional Counting
}FPC, Pb2 l 0, Solid "Dry Weight Corrected"
,ead-210 0.000465 +/-1.19E-05 2.37E-05
}FPC, Total Alpha Radium, solid "Dry Weight Corrected"
·otal Radium 0.000192 +/-4.37E-06 3.52E-06
rhe following Pre Methods were performed: --------vl et hod 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 Mod/ EPA 903.0 Mod
2.00E-07
2.00E-07
2.00E-07
2.00E-07
l.OOE-06
5.00E-08
Analyst
CXCl
uCi/kg MXS2 07/16/18 1509 1778700
uCi/kg MXS2 07/16/18 1509 1778701
uCi/kg
uCi/kg
uCi/kg LXB3 07/18/18 1703 1777221
uCi/kg KSDl 07/24/18 1813 1783273
Date Time Prep Batch
06/26/18 1305 1777197
Ana.Jyst Comments
Result Nominal Recovery% Acceptable Limits ;urro~te/Tracer Recovery Test -----------rhorium-229 Tracer Alphaspec Th-232, Solid "Dry Weight Corrected"
Jranium-232 Tracer Alphaspec U, Solid "Dry Weight Corrected"
,ead Carrier GFPC, Pb210, Solid "Dry Weight Corrected"
3arium Carrier GFPC, Total Alpha Radium, solid "Dry Weight
Corrected"
"fotes:
:::ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
84. 7 (15%-125%)
77.9 (15%-125%)
118 (25%-125%)
123 (25%-125%)
2
3
4
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: July 25, 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 East
453309001
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: May 25, 2018
Company:
Address:
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Contact:
Project:
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis
Client Sample ID: North West
Sample ID: 449032002
Matrix: SOLID
Collect Date:
Receive Date:
26-APR-18 09: 15
30-APR-18
Collector: Client
Parameter Qualifier Result Uncertainty
lad Alpha Spec Analysis
'\.lphaspec Th-232, Solid "As Received"
'horium-232 5.49E-06 +/-2. l 5E-06
'\.lphaspec U, Solid "As Received"
Jranium-233/234 0.000217 +/-3.36E-06
Jranium-235/236 l.33E-05 +/-9.31E-07
Jranium-238 0.00023 +/-3.45E-06
lad Gas Flow Proportional Counting
}FPC, Pb210, Solid "As Received"
.ead-210 0.000585 +/-9. l 2E-06
}FPC, Total Alpha Radium, solid "As Received"
~otal Radium 0.000263 +/-2.93E-06
fhe following Prep Methods were performed:
MDC
3.47E-06
6.72E-07
4.89E-07
3.96E-07
8. l 7E-06
7.38E-07
----v1ethod Description
)ry Soil Prep Dry 011 Prep GL~RAD-A-021
The following Analytical Methods were performed:
\1ethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Modified
Test
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
l.OOE-06
5.00E-08
Analyst
CXCI
Project:
Client ID:
DNMI00101
DNMI001
Units PF DF Analyst Date
uCi/kg HAKB 05/22/18
uCi/kg HAKB 05/22/18
uCi/kg
uCi/kg
uCi/kg KSDI 05/22/18
uCi/kg KSD1 05/21/18
Date Time Prep Batch
05/01/18 0956 1760390
Anal st Comments
Result Nominal ;urrogate/Tracer Recovery
rhorium-229 Tracer
Jranium-232 Tracer
------------Recovery%
63 .5
79.8
92.4
98.9
,ead Carrier
3arium Carrier
~otes:
Alphaspec Th-232, Solid "As Received"
Alphaspec U, Solid "As Received"
GFPC, Pb210, Solid "As Received"
GFPC, Total Alpha Radium, solid "As Received"
:=ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Time Batch Method
1314 1760395
1332 1760396
0626 1762781
1748 1762780
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: May 25, 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 West
Sample ID: 449032002
Qualifier Result Uncertainty MDC
Column headers are defined as fol lows:
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:
DNMIOOlOl
DNMJOOI
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: July 25, 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
North West
453309002
Vegetation
20-JUN-I 8 12:30
26-JUN-18
Client
Parameter Qualifier Result Uncertainty
tad Alpha Spec Analysis
'\lphaspec Th-232, Solid "Dry Weight Corrected"
~horium-232 9.46E-06 +/-1.05E-06
'\lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 0.000238 +/-3.97E-06
Jranium-235/236 l.32E-05 +/-1.06E-06
Jranium-238 0.000247 +/-4.04E-06
tad Gas Flow Proportional Counting
}FPC, Pb2 I 0, Solid "Dry Weight Corrected"
,ead-210 0.000602 +/-1.28E-05
}FPC, Total Alpha Radium, solid "Dry Weight Corrected"
"otal Radium 0.000213 +/-4.85E-06
MDC
l.07E-06
8.32E-07
7.82E-07
8.12E-07
2.33E-05
3.93E-06
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
I.OOE-06
5.00E-08
[he following Prep Methods were P._e_r_fo_rm_e_d_: _________ _
vlethod Description '-------------)ry 'oil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\.1ethod Descri tion --~-------------DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Mod/ EPA 903.0 Mod
iurrogate/Tracer Recovery
['horium-229 Tracer
Test
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"
Jranium-232 Tracer
,ead Carrier
3arium Carrier
\Jotes:
Analyst
CXCl
=:ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Project:
Client ID:
DNMIOOIOI
DNMI001
Units PF OF Analyst Date
uCi/kg MXS2 07/16/18
uCi/kg MXS2 07/16/18
uCi/kg
uCi/kg
uCi/kg LXB3 07/18/18
uCi/kg KSDI 07/24/18
Date Time Prep Batch
06/26/18 1305 1777197
Anal st Comments
Result Nominal --------Recovery%
87.9
77.5
117
104
Time Batch Method
1509 1778700
1509 1778701
1703 1777221
1813 1783273
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: July 25 , 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 West
Sample ID: 453309002
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 OF Analyst Date Time Batch Method
Company:
Address:
Contact:
Project:
Client Sample ID:
Sample ID:
Matrix:
Collect Date:
Receive Date:
Collector:
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy W einel
Vegetation Analysis
South West
449032003
SOLID
26-APR-18 08:30
30-APR-18
Client
Project:
Client ID:
Report Date: May 25, 2018
DNMI00101
DNMI001
Parameter Qualifier Result Uncertainty MDC RL Units PF DF Analyst Date Time Batch Method ----
lad Alpha Spec Analysis
\lphaspec Th-232, Solid "As Received"
~horium-232 4.93E-06 +/-1.99E-06 3.69E-06
\lphaspec U, Solid "As Received"
Jranium-233/234 0.000191 +/-2.99E-06 7.05E-07
Jranium-235/236 l.34E-05 +/-8.86E-07 4.41E-07
Jranium-238 0.000198 +/-3.04E-06 3.57E-07
lad Gas Flow Proportional Counting
:iFPC, Pb210, Solid "As Received"
,ead-210 0.000383 +/-8.29E-06 l.51E-05
:iFPC, Total Alpha Radium, solid "As Received"
"otal Radium 5.16E-05 +/-l.21E-06 8.IOE-07
I11e following Prep Methods were perfmmed:
Vlethod Description
5ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Modified
,urrogate/Tracer Recovery
rhorium-229 Tracer
Jranium-232 Tracer
Test
Alphaspec Th-232, Solid "As Received"
Alphaspec U, Solid "As Received"
GFPC, Pb210, Solid "As Received" ,ead Carrier
3arium Carrier GFPC, Total Alpha Radium, solid "As Received"
'llotes:
2.00E-07
2.00E-07
2.00E-07
2.00E-07
J.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
05/01/18
Result
HAKB 05/22/18 1314 1760395
HAKB 05/22/18 1332 1760396
KSDI 05/22/18 0626 1762781
KSDl 05/21/18 1748 1762780
Time Prep Batch 0956 --,-7~60_3_9_0 ___ _
A!)<!!)'st Comments __ _
Nominal Recovery%
69.7
81.4
91
105
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
Company :
Address:
Contact:
Project:
Client Sample ID:
Sample ID:
Certificate of Analysis
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Ms. Kathy Weinel
Vegetation Analysis -----South West
449032003
Project:
Client ID:
Report Date: May 25, 2018
DNMIOOIOI
DNMI001
Parameter Qualifier Result Uncertainty MDC RL Units PF DF Analyst Date Time Batch Method
Column headers are defined as follows:
OF: Dilution Factor
DL: Detection Limit
MDA: Minimum Detectable Activity
MDC: Minimum Detectable Concentration
Le/LC: Critical Level
PF: Prep Factor
RL: Reporting Limit
----
SQL: Sample Quantitation Limit
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Certificate of Analysis
Report Date: July 25, 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 W einel
Vegetation Analysis
South West
453309003
Vegetation
20-JUN-18 12:00
26-JUN-18
Client
Qualifier Result Uncertainty
lad Alpha Spec Analysis
\.lphaspec Th-232, Solid "Dry Weight Corrected"
:horium-232 3.18E-06 +/-5.8 IE-07
\.lphaspec U, Solid "Dry Weight Corrected"
Jranium-233/234 7.12E-05 +/-2.05E-06
Jranium-235/236 4.41E-06 +/-5 .91 E-07
Jraniurn-238 7.30E-05 +/-2.07E-06
lad Gas Flow Proportional Counting
:iFPC, Pb210, Solid "Dry Weight Corrected"
.ead-210 9.22E-05 +/-7 .25E-06
:iFPC, Total Alpha Radium, solid "Dry Weight Corrected"
'otal Radium 5.14E-05 +/-2.70E-06
rhe following Prep Methods were performed:
Vlethod Description
)ry Soil Prep Dry Soil Prep GL-RAD-A-021
The following Analytical Methods were performed:
\1ethod Descri tion
DOE EML HASL-300, Th-01-RC Modified
DOE EML HASL-300, U-02-RC Modified
DOE RP280 Modified
EPA 900.1 Mod/ EPA 903.0 Mod
;;urrogate/Tracer Recovery Test --~---------
MDC
7.54E-07
9.16E-07
6.92E-07
5.60E-07
2.08E-05
4.37E-06
f ho r i um -229 Tracer Alphaspec Th-232, Solid "Dry Weight Corrected"
Jranium-232 Tracer Alphaspec U, Solid "Dry Weight Corrected"
,ead Carrier GFPC, Pb210, Solid "Dry Weight Corrected"
3arium Carrier GFPC, Total Alpha Radium, solid "Dry Weight
Corrected"
~otes:
RL
2.00E-07
2.00E-07
2.00E-07
2.00E-07
l.OOE-06
5.00E-08
Analyst
-X'i
::'.ounting Uncertainty is calculated at the 68% confidence level (I-sigma).
Project:
Client ID:
DNMI00101
DNMIOOI
Units
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
uCi/kg
Date
06/26/18
Result
PF DF Analyst Date
MXS2 07/16/18
MXS2 07/16/18
LXB3 07/18/18
KSDI 07/24/18
Time Prep Batch
1305 1777197
Anal st Comments
Nominal Recovery%
92.2
90
121
106
Time Batch Method
1509 1778700
1509 1778701
1723 1777221
1813 1783273
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: July 25, 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
453309003
Parameter Qualifier Result Uncertainty MDC RL ------'------
Column headers are defined as follows:
DF: Dilution Factor
DL: Detection Limit
MDA: Minimum Detectable Activity
MDC: Minimum Detectable Concentration
Le/LC: Critical Level
PF: Prep Factor
RL: Reporting Limit
SQL: Sample Quantitation Limit
Project:
Client ID:
DNMI00101
DNMIOOI
Units PF DF Analyst Date Time Batch Method
C€f 4• I Laboratories LLc $ 00
a member of The GEL Group INC
PO Box ~0712 Char1eS1on. SC 29417
2040 Sa~age Road Charleston. SC 29407
P 843,556.8171
F 843 766.1178
May 25, 2018
Ms. Kathy Weinel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
WorkOrder:449032
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on April 30, 2018. 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,
le~tJ~for
Julie Robinson
Project Manager
111111111111 111111111111 · 11111
gel.com
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 449032
Case Narrative
1:
May 25, 2018
Laboratory Identification:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 449032
Sample receipt: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on April 30, 2018
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:
Case Narrative:
Laboratory ID
449032001
449032002
449032003
Client ID
North East
North West
South West
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.
i ettut~for
Julje 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
p . t roJec s amp ers N ame s amp ers Si t 1gna ure
Early Spring Vegetation I k~d-2018 Garrin Palmer
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
North East 4/26/2018 1000 Ra 226, U-Nat, Th-232, PB 210
North West 4/26/2018 915 Ra 226, U-Nat, Th-232, PB 210
South West 4/26/2018 830 Ra 226, U-Nat, Th-232, PB 210
* Please use caution when handling samples. Some
plants have thorns.
Comments: Please send report to Kathy Weinel at [e-mail]
Relinquished By:(Signature)
Relinquished By:(Signature) Date/Time
I ma! I Laboratories '-Le fp._
Carrier and Tracking Number
Suspected Hamn! lnfonnnllon
Shipped as a DOT Hazardous?
COC/Samples rruuked or classified as
mdioacti ve?
Is package, COC, and/or Samples marked HAZ?
Sample Receipt Criteria
1 Shipping containecs received intact and
sealed?
2 Chain of custody documents included
with shipment?
3 Samples requiring cold preservation
within (0 5 6 deg. C)?"
4 Daily check perfom1ed and passed on IR
temperature gun?
5 Sample containers 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 ID's on COC match IO's on
bottles?
10 Date & Lime on COC match date & time
on bottles?
11 Number of containers received match
number indicated on COC?
12 Are sample containecs i:dentifinbh: as
GEL rovided?
13 COC fonn is properly signed in
relinquished/received sections?
Com~nts (Use Continuation Form if needed):
SAMPLE RECEIPT & REVIEW FORM
03~
Courier Other
*If Net Counts> lOOcpm on samples not marked "radioactive", contact lhe Radiation Safely Group for further
jnvestigalioo.
Hazard Class Shipped: UN#:
aximum Net Counts Observed* (Observed Counts· Area Background Counts): --A,,'---CPM / mR/Br
Classltled as: Rad I Rad 2 Rad 3
If yes, select Hazards below, and contact the GEL Safety Group.
PCB's Flammable Foreign Soil RCRA Asbestos Beryllium Other:
Comments/Qualifiers (Required for Non-Conforming Items)
Circle Applicable: Seals broken Damaged contniner Leaking container Other (describe)
TEMP: Jt/0 Pn:serv.>tion Method: Wet Ice Ice Packs Dry ice Non Other:
•nu temperatures are recorded in Celsius
Circle Applicable: Seals broken Damaged contnioer Lcol<ing container Other (describe)
SM1plc ID's ond Contoincr, Affected:
If Yes, Are Encores or Soil Kits present? Yes_No_ (lfyes, take to VOA Freezer)
Do VOA vials contain acid preservation? Yes No_ NI A. (If unknown, select No)
VOA vials free ofheadspace? Yes No_N/A
Sample ID's and containers affected:
ID's mid tests affected:
SM1plc !D's and containers affected:
Sample !D's affected:
Snmp!c !D's affe,:ted:
PM (or PMA) review: Initials __ ,1~~\A_L ___ Date __ 5--i) .... l----i~~\ ~g~· _ Page _I_ of_l_
GL-CHL-SR-001 Rev 5
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 449032
Client SDG: 449032
Early Spring Vegetation 2018
Project Manager:
Project Name:
Purchase Order:
Package Level:
EDD Format:
Julie Robinson
DNM100101 Vegetation Analysis
DW16138
LEVEL3
EIM_DNMI
Collect
GELID Client Sample ID Client Sample Desc. Date & Time
449032001 North East
449032002 North West
449032003 South West
Client Sample ID
-001 North East
-002 North West
-003 South West
Status Tests/Methods
REVW Alphaspec Th-232, Solid
REVW Alphaspec U, Solid
26-APR-18 10:00
26-APR-18 09:15
26-APR-18 08:30
Product
Reference
U-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 U, Solid U-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 U, Solid U-Natural
REVW GFPC, Total Alpha Radium, solid Ra226
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
Work Order Due Date: 30-MAY-18
Package Due Date:
EDD Due Date:
Due Date:
BXL3
Receive Time # of
Date & Time Zone Cont.
30-APR-18 09:25 -2 1
30-APR-18 09:25 -2 1
30-APR-1 B 09:25 -2 1
Fax Date PM Comments
28-MAY-18
29-MAY-18
30-MAY-18
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Client Matrix
Client Matrix
Client Matrix
Report Date: 25-MAY-18
Work Order: 449032
Page 1 of 3
Collector: C
Prelogin #: 20160443172
Project Workdef ID: 1310529
SDG Status: Closed
Logged by:
Fax Days to Prelog Lab Field
Due Date Process CofC# Group QC QC
30
30
30
Receive
Aux Data Codes
SOLID
SOLID
SOLID
GEL Laboratories LLC -Login Review Report
Product: ASP_ THS Workdef ID: 1370540 In Product Group? No
Method: 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# Parmname
Product: GFC PBS WorkdeflD: 1310600 In Product Group? No -
Method: DOE RP280 Modified
Product Description: GFPC, Pb210, Solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS 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: 25-MA Y-18
Work Order: 449032
Page 2 of 3
Group Reference:
Path: No Ash pCi/g
Product Reference:
Moisture Correction: "As Received"
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: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
Group Reference:
Path: Standard
Product Reference: Ra226
Moisture Correction: "As Received"
Parm Included Included Custom
Function in Sample? in QC? List?
REG y y Yes
GEL Laboratories LLC -Login Review Report
Product: ASP _UUS VVorkdeflD: 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: 25-MA Y-18
Work Order: 449032
Page 3 of 3
Product Reference: LI-Natural
Moisture Correction: "As Received"
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 of25 May 2018
State Certification
Alaska 17-018
Arkansas 88-0651
CUA 42D0904046
California 2940
Colorado SCOOOl2
Connecticut PH-0169
Delaware SC00012
DoD ELAP/ ISO 17025 A2LA 2567.01
Florida NELAP E87156
Foreign Soils Permit P330-15-00283,P330-15-00253
Georgia SCOOOl2
Georgia SDWA 967
Hawaii SC00012
Idaho Chemistry SCOOOl2
Idaho Radiochemistry SCOOOl2
Illinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332
Kentucky SDW A 90129
Kentucky Wastewater 90129
Louisiana NELAP 03046 (AI33904)
Louisiana SDWA LA18001 I
Maryland 270
Massachusetts M-SCOl2
Michigan 9976
Mississippi SCOOOl2
Nebraska NE-OS-26-13
Nevada scooo 122018-1
New Hampshire NELAP 205415
New Jersey NELAP SC002
New Mexico SCOOOl2
New York NELAP 11501
North Carolina 233
North Carolina SOWA 45709
North Dakota R-158
Oklahoma 9904
Pennsylvania NELAP 68-00485
Puerto Rico SCOOOl2
S. Carolina Radiochem 10120002
South Carolina Chemistry 10120001
Tennessee TN 02934
TexasNELAP Tl04704235-18-13
UtahNELAP SC000122018-26
Vermont VT87156
Virginia NELAP 460202
Washington C780
West Virginia 997404
Radiochemistry
Technical Case Narrative
Energy Fuels Resources (DNMI)
SDG #: 449032
Product: Alphaspec Th-232, Solid
Analytical Method: DOE EML HASL-300, Th-01-RC Modified
Analytical Pro edure: GL-RAD-A-038 REV# 17
Analytical Batch: 1760395
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1760390
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
449032001
449032002
449032003
1204019952
1204019953
1204019954
Client Sam pie Identification
North East
N011h West
South West
Method Blank (MB)
44903200l(North East) Sample Duplicate (DUP)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" 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) 1.nformation
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
1204019952 (MB) Thorium-232 Result 0.000000403 < MDA 0.00000275 > RDL 0.0000002 uCi/kg
Technical Information
Recounts
Sample 1204019954 (LCS) was recounted due to a peak shift. The recount is reported. Sample 449032001
(North East) was recounted due to detector error. The recount is 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: 1760396
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1760390
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#
449032001
449032002
449032003
1204019955
1204019956
1204019957
44903200l(North East) Sample Duplicate (DUP)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" 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
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
1204019955 Uranium-233/234 Result: l .33E-06 uCi/kg > MDA: 5.63E-07 uCi/kg > RDL: 2.00E-07
(MB) uCi/kg
Uranium-235/236 Result: 4.63E-07 uCi/kg > MDA: 4.43E-07 uCi/kg > RDL: 2.00E-07
uCi/kg
Uranium-238 Result: 7.95E-07 uCi/kg > MDA: 5. l 7E-07 uCi/kg > RDL: 2.00E-07
uCi/kg
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
1204019956 (North EastDUP) Uranium-235/236 RPD 28.1 * (0.00%-20.00%) RER 2.27 (0-3)
Technical Information
Recounts
Sample 1204019955 (MB) was given additional clean-up steps and recounted in order to improve the resolution.
The recount is reported.
Product: Dry Weight
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1760390
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
449032001
449032002
449032003
Client Sample Identification
North East
North West
South West
The samples in this SDG were analyzed on an "as received" basis.
Data Summary:
There are no exceptions, anomalies or deviations from the specified methods. All sample data provided in this
report met the acceptance criteria specified in the analytical methods and procedures for initial calibration,
continuing calibration, instrument controls and process controls where applicable.
Product: GFPC, Total Alpha Radium, solid
Analytical Method: EPA 900.1 Modified
Analytical Procedure: GL-RAD-A-010 REV# 17
Analytical Batch: 1762780
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
.Preparation Batch: 1760390
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sam pie ID#
449032001
449032002
449032003
1204024971
1204024972
1204024973
1204024974
Client Sample Identification
North East
North West
South West
Method Blank (MB)
449032001(North East) Sample Duplicate (DUP)
44903200l(North East) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" 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
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
1204024971 (MB) Total Radium Result: 8.46E-07 uCi/kg > MDA: 7.85E-07 uCi/kg > RDL: 5.00E-08 uCi/kg
Technical Information
Recounts
Sample 1204024971 (MB) was recounted due to a suspected blank false positive. The recount is reported.
Miscellaneous Information
Additional Comments
The matrix spike, 1204024973 (North EastMS), aliquot was reduced to conserve sample volume.
Product: GFPC, Pb210, Solid
Analytical Method: DOE RP280 Modified
Analytical Prncedure: GL-RAD-A-018 REV# 14
Analytical Batch: 1762781
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 22
Preparation Batch: 1760390
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
449032001
449032002
449032003
1204024975
1204024976
1204024977
1204024978
Client Sample Identification
North East
North West
South West
Method Blank (MB)
449032001(North East) Sample Duplicate (DUP)
449032001(North East) Matrix Spike (MS)
Laboratory Control Sample (LCS)
The samples in this SDG were analyzed on an "as received" 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) lnformatfon
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
1204024976 (North EastDUP) Lead-210 RPD 27.3* (0.00%-20.00%) RER 1.4 (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
1204024975 (MB) Lead-210 Result 0.00000414 < MDA 0.0000114 > RDL 0.000001 uCi/kg
Certification Statement
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless otherwise noted in the analytical case narrative.
GEL LABORATORIES LLC
2040 Savage Road Charleston SC 29407 -[phone] -www.gel.com
Qualifier Definition Report
for
DNMIOOl Energy Fuels Resources (USA), Inc.
Client SDG: 449032 GEL Work Order: 449032
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: 9-l O ~ ~ · IY.<.J 41 11 tJ
Date: 25 MAY 2018
Name: Heather McCarty
Title: Analyst II
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summarr Reoort Date: May 25, 2018 Energy Fuels Resources (USA), Inc. Page 1 of 225 Union Boulevard
Suite 600
Lakewood, Colorado
Contact: Ms. Kathy Weinel
Workorder: 449032
[>armname NOM C Units RPO% REC% Ra~ge Anlst Date Time
Rad Alpha Spec
3atch 1760395
QC1204019953 449032001 DUP
Thorium-232 3.36£-06 6.32£-06 uCi/kg 61.1 (0% -100%) HAKB 05/22/18 13: 1,
Uncertainty +/-1.41£-06 +/-2.00E-06
QC1204019954 LCS
Thorium-232 0.000127 0.000133 uCi/kg 105 (75%-125%) 05/24/18 09:0
Uncertainty +/-8.16E-06
QC1204019952 MB
Thorium-232 u 4.03E-07 uCi/kg 05/22/18 13: 1,
Uncertainty +/-8.14E-07
3atch 1760396
QC1204019956 449032001 DUP
Uranium-233/234 0.000148 0.000171 uCi/kg 14.4 (0%-20%) HAKB 05/22/18 13:3
Uncertainty +/-2.69E-06 +/-2.91E-06
Uranium-235/236 1.0IE-05 1.34E-05 uCi/kg 28.1 * (0%-20%)
Uncertainty +/-7.88E-07 +/-9.14E-07
Uranium-238 0.000157 0.000172 uCi/kg 9.27 (0%-20%)
Uncertainty +/-2. 77E-06 +/-2.92E-06
QC1204019957 LCS
Uranium-233/234 6.71E-05 uCi/kg 05/22/18 13:3
Uncertainty +/-1.65E-06
Uranium-235/236 6.81£-06 uCi/kg
Uncertainty +/-5.92E-07
Uranium-238 6.71£-05 6.53E-05 uCi/kg 97.2 (75%-125%)
Uncertainty +/-1.63£-06
QC 1204019955 MB
Uranium-233/234 1.33E-06 uCi/kg 05/24/18 13 :2
Uncertainty +/-2.88£-07
Uranium-235/236 4.63E-07 uCi/kg
Uncertainty +/-2.00E-07
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summarl'.
Workorder: 449032 Page 2 of ---Parmname NOM Sam C Units RPO% REC% Ran2e Anlst Date Time
Rad Alpha Spec
3atch 1760396
Uranium-238 7.95E-07 uCi/kg HAKB 05/24/18 13 :2
Uncertainty +/-2.34E-07
Rad Gas Flow
3atch 1762780
QC1204024972 449032001 DUP
Total Radium 9.84E-05 0.000101 uCi/kg 2.65 (0%-20%) KSD1 05/21/18 17:4
Uncertainty +/-l .83E-06 +/-l.90E-06
QC1204024974 LCS
Total Radium 0.00265 0.00254 uCi/kg 95.9 (75%-125%) 05/21/18 16:4
Uncertainty +/-2.72E-05
QCl204024971 MB
Total Radium 8.46E-07 uCi/kg 05/24/18 16: l
Uncertainty +/-2.58E-07
QC1204024973 449032001 MS
Total Radium 0.00594 9.84E-05 0.00457 uCi/kg 75.3 (75%-125%) 05/22/18 16:0
Uncertainty +/-l.83E-06 +/-4.58E-05
3atch 1762781
QC1204024976 449032001 DUP
Lead-210 0.000453 0.000597 uCi/kg 27.3* (0%-20%) KSDI 05/22/18 06:31
Uncertainty +/-9.39E-06 +/-l.07E-05
QC1204024978 LCS
Lead-210 0.0047 0.00467 uCi/kg 99.2 (75%-125%) 05/22/18 06:31
Uncertainty +/-7 .20E-05
QC1204024975 MB
Lead-210 u 4.14E-06 uCi/kg 05/22/18 06:31
Uncertainty +/-3.42E-06
QC1204024977 449032001 MS
Lead-210 0.0112 0.000453 0.0115 uCi/kg 99.2 (75%-125%) 05/22/18 06:31
Uncertainty +/-9.39E-06 +/-0.000179
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
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary
Workorder: 449032
Parmname NOM SamJ!le Q_ua_I __ ~QC Units RPO%
> 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
REC% Range Anlst
NI
ND
NJ
Q
R
u
UI
UJ
UL
X
y
Not considered detected. The associated number is the reported concentration, which may be inaccurate due to a low bias.
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
I\
h
QC Samples were not spiked with this compound
RPD of sample and duplicate evaluated using +I-RL. Concentrations are <5X the RL. Qualifier Not Applicable for Radiochemistry.
Preparation or preservation holding time was exceeded
Page 3 of
Date Time
NI A indicates that spike recovery limits do not apply when sample concentration exceeds spike cone. by a factor of 4 or more or %RPD not applicable.
/\ The Relative Percent Difference (RPD) obtained from the sample duplicate (DUP) is evaluated against the acceptance criteria when the sample is greater than
five times (5X) the contract required detection limit (RL). In cases where either the sample or duplicate value is less than 5X the RL, a control limit of +I-the
RL is used to evaluate the DUP result.
* Indicates that a Quality Control parameter was not within specifications.
For PS, PSD, and SDIL T results, the values listed are the measured amounts, not final concentrations.
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless qualified on the QC Summary.
m@• I Laboratories LLC
a member of The GEL Group INC
PO Box :l0712 Charteston. SC 29417
2040 Savage Road Charteston. SC 29407
P 843.556.8171
F 843.766.1178
July 26, 2018
Ms. Kathy Weinel
Energy Fuels Resources (USA), Inc.
225 Union Boulevard
Suite 600
Lakewood, Colorado 80228
Re: Vegetation Analysis
Work Order: 453309
Dear Ms. Weinel:
GEL Laboratories, LLC (GEL) appreciates the opportunity to provide the enclosed analytical results for the
sample(s) we received on June 26, 2018. 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,
ie~t~for
Julie Robinson
Project Manager
1111111111 UII I 11111111111 11111
gel.com
Energy Fuels Resources (USA), Inc.
Vegetation Analysis
SDG: 453309
Case Narrative
1,
July 26, 2018
Labora tory Identifi cation:
GEL Laboratories LLC
2040 Savage Road
Charleston, South Carolina 29407
[phone]
Summary:
Receipt Narrative
for
Energy Fuels Resources (USA), Inc.
SDG: 453309
Sample receipt: The samples arrived at GEL Laboratories LLC, Charleston, South Carolina on June 26, 2018
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:
Case Narrative:
Laboratory ID
453309001
453309002
453309003
Client ID
North East
North West
South West
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.
l e~tl::}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
p . roJect s amplers N ame Samplers Signature
Late Spring Vegetation I /C-~4A~{)j4 A.. 2018 Garrin Palmer
'--"
Time
Sample ID Date Collected Collected Laboratory Analysis Requested
North East 6/20/2018 1300 Ra 226, U-Nat, Th-232, PB 210
North West 6/20/2018 1230 Ra 226, U-Nat, Th-232, PB 210
South West 6/20/2018 1200 Ra 226, U-Nat, Th-232, PB 210
Weights:
North East: 3185 Grams
North West: 3450 Grams
South east: 3540 Grams
* Please use caution when handling samples. Some
plants have thorns.
Comments: Please send report to Kathy Weinel at kweinelc@energyfuels .com
Relinquished By:(Signature)
Relinquished By:(Signature)
Date/Time Received By:(Signature)
12,$/l t"..
~
Date/Time
[m I Laboraiories u;
Client:
Received By: ZKW
Carrier and Trucking Number
Suspected Hamrd lnfonnntion
Shipped as a DOT Hazardous?
COC/Samples marked or classified a.~
radioactive?
ls package, COC, and/or Samples marked HAZ'I
Sample Receipt Criteria
1 Shipping containers received intact and
sealed?
2 Chain of custody documcnts included
with shipment?
3 Samples requiring cold preservation
within (0 ~ 6 deg. C)?*
4 Daily check performed and passed on IR
temperature gun?
S Sample containers 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 ID's on COC match ID's on
bottles?
10 Date & time on COC match date & time
·on bottles?
11 Number of containers received match
"umber indicated on COC?
12 Are sample containers identifiable as
GEL rovided?
13 COC form i~ properly signed in
relinquished/received sections?
Comments (Use Continuation Fonn if needed):
SAMPLE RECEIPT & REVIEW FORM
Date Received: \._Q ,Z_i.JZ I l 't:;>
Cin:~ble:
FedEx Express FedEx Ground ~ Field Services Courier Other
,!! ., *JC Net Counts> lOOcpm on samples not marked "radioactive", contact the Radiation Safely Group for further
,... Z: investigation.
an! Clas.~ Shipped: UN#:
Maximum Net Counts Observed• (Observed Counts -Area Background Counts): __Q_@ji) mR/Hr
Classified BS: Rad 1 Rad 2 Rad 3
yes, select Hazards below, and conLact the GEL Safety Group.
PCB's Flammable Foreign Soil RCRA Asbestos Beryllium Other.
Conunents/Qualifiers (Required for Non-Confonnlng lteDL'l)
Circle Applicable: Seals broken Damaged contniner I..caking container Other (describe)
Preserwtion Method: Wet Ice Ice Packs Dry ice on Other.
'all temperatures an, recorded in Celsius TEMP: 2-J'C..
Temperature Device Serial #: __ ""'IR...a.3c....-"""1""-8 __ _
Socond,uy 'fompcralun: Device Serial# (If Applicable):
Circle Applicable: Seals broken Damaged container Leaking container Other (describe)
If Yes, Are Encores or Soil Kits present? Yes_ No_ (If yes, take to VOA Freezer)
Do VOA vials contain acid preservation? Yes_ No_ NIA_ (If unknown, select No)
VOA vials free ofheadspace? Yes_ No_ NIA_
ample ID's and containers affected:
UY, and tests affected:
S~le ID's and containe~ affected:
Sample !D's affected:
Sample !D's affected:
PM (or PMA) review: Initia1s __ :::r-+-\,_V'-....;L=--Date --'""6+a~++'-'--Page _j_ of _l_
GL-CHL-SR-001 Rev 5
GEL Laboratories LLC -Login Review Report
GEL Work Order/SDG: 453309
Client SDG: 453309
Late Spring Vegetation 2018
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
453309001 North East
453309002 North West
453309003 South West
Client Sample ID
-001 North East
-002 North West
-003 South West
Status Tests/Methods
REVW Alphaspec Th-232, Solid
REVW Alphaspec U, Solid
20-JUN-18 13:00
20-JUN-18 12:30
20-JUN-18 12:00
Product
Reference
U-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 U, Solid U-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 U, Solid U-Natural
REVW GFPC, Total Alpha Radium, solid Ra226
REVW GFPC, Pb210, Solid
REVW Laboratory Composite -Dry prep
instructions
Work Order Due Date: 26-JUL-18
Package Due Date:
EDD Due Date:
Due Date:
JAR1
Receive Time # of
Date & Time Zone Cont.
26-JUN-18 09:15 -2
26-JUN-18 09:15 -2
26-JUN-18 09:15 -2
Fax Date PM Comments
24-JUL-18
25-JUL-18
26-JUL-18
Lab
Matrix
VEGETATION
VEGETATION
VEGETATION
Report Date: 26-JUL-18
Work Order: 453309
Page 1 of 3
Collector: C
Prelogin #: 20180673982
Project Workdef ID: 1310529
SDG Status: Closed
Logged by:
Fax Days to
Due Date Process CofC#
Prelog Lab Field
Group QC QC
30
30
30
Aux Data
Receive
Codes
GEL Laboratories LLC -Login Review Report
Product: ASP_ THS Workdef ID: 1370540 In Product Group? No
Method: 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# Parmname
Product: GFC PBS -WorkdeflD: 1310600 In Product Group? No
Method: DOE RP280 Modified
Product Description: GFPC, Pb210, Solid
Samples: 001, 002, 003
Parmname Check: All parmnames scheduled properly
CAS# Parmname
14255-04-0 Lead-210
Product: GFCTORAS WorkdeflD: 1310679 In Product Group? No
Method: EPA 900.1 Mod/ EPA 903.0 Mod
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:26-JUL-18
Work Order: 453309
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: Group Reference:
Path: Standard
Report Date: 26-JUL-18
Work Order: 453309
Page 3 of 3
Product Reference: LI-Natural
Moisture Correction: "Dry Weight Corrected"
Client RDL or
PQL & Unit
Reporting Parm Included Included Custom
.0000002
.0000002
.0000002
Units Function in Sample? in QC? List?
uCi/kg
uCi/kg
uCi/kg
REG
REG
REG
y
y
y
y
y
y
Yes
Samples
Include? Comments
y
y
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry.
FOR VEGETATION: After logging in, change from DRY to WET in sample inquiry. Log
with lab comp.
Peer Review by: ____________ _ Work Order (SDG#), PO# Checked? ____ _ C of C signed in receiver location? _____ _
\
(
l
Laboratory
Certifications
List of current GEL Certifications as of26 July 2018
State Certification
Alaska 17-018
Arkansas 88-0651
CUA 4200904046
California 2940
Colorado SC00012
Connecticut PH-0169
Delaware SC00012
DoD ELAP/ ISOl 7025 A2LA 2567.01
Florida NELAP E87156
Foreign Soils Permit P330-15-00283,P330-15-00253
Georgia SC00012
Georgia SDW A 967
Hawaii SC00012
Idaho Chemistry SC00012
Idaho Radiochemistry SCOOOl2
Illinois NELAP 200029
Indiana C-SC-01
Kansas NELAP E-10332
Kentucky SOWA 90129
Kentucky Wastewater 90129
Louisiana NELAP 03046 (AI33904)
Louisiana SDW A LA18001 I
Maryland 270
Massachusetts M-SCOl2
Michigan 9976
Mississippi SC00012
Nebraska NE-OS-26-13
Nevada scooo 122018-1
New Hampshire NELAP 205415
New Jersey NELAP SC002
New Mexico SC00012
New York NELAP 11501
North Carolina 233
North Carolina SDWA 45709
North Dakota R-158
Oklahoma 9904
Pennsylvania NELAP 68-00485
Puerto Rico SCOOOl2
S. Carolina Radiochem 10120002
South Carolina Chemistry 10120001
Tennessee TN 02934
TexasNELAP Tl04704235-18-13
UtahNELAP SCOOOI22018-26
Vermont VT87156
Virginia NELAP 460202
Washington C780
West Virginia 997404
Radiochemistry
Technical Case Narrative
Energy Fuels Resources (DNMI)
SDG #: 453309
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: 1778700
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1777197
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
453309001
453309002
453309003
1204061586
1204061587
1204061588
Client Sample Identification
North East
North West
South West
Method Blank (MB)
45330900l(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 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
1204061587 (North EastDUP) Thorium-232 RPO 27.9* (0.00%-20.00%) RER 2.16 (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
1204061586 (MB) Thorium-232 Result 0.00000205 < MDA 0.00000399 > RDL 0.0000002 uCi/kg
Technical Information
Recounts
Sample 1204061586 (MB) was given additional clean-up steps and recounted in order to improve the resolution.
The recount is 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: 1778701
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1777197
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#
453309001
453309002
453309003
1204061589
1204061590
1204061591
45330900l(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 (QC) Information
Method Blank Criteria
The blank result (see below) is equal to the MDC but less than the required detection limit.
Sample Analyte Value
1204061589 Uranium-238 Result: 1.48E-07 uCi/kg > MDA: 1.48E-07 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
1204061589 (MB) Uranium-233/234 Result 0.000000131 < MDA 0.000000863 > RDL 0.0000002 uCi/kg
Uranium-235/236 Result 0.000000244 < MDA 0.000000585 > RDL 0.0000002 uCi/kg
Product: Dry Weight
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1777197
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
453309001
453309002
453309003
Client Sample Identification
North East
North West
South West
The samples in this SDG were analyzed on an "as received" basis.
Data Summary:
There are no exceptions, anomalies or deviations from the specified methods. All sample data provided in this
report met the acceptance criteria specified in the analytical methods and procedures for initial calibration,
continuing calibration, instrument controls and process controls where applicable.
Product: GFPC, Pb210, Solid
Analytical Method: DOE RP280 Modified
Analytical Procedure: GL-RAD-A-018 REV# 14
Analytical Batch: 1777221
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1777197
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
453309001
453309002
453309003
1204058201
1204058202
1204058203
1204058204
Client Sample Identification
North East
North West
South West
Method Blank (MB)
45330900l(North East) Sample Duplicate (DUP)
45330900l(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.
Qua lity Control (QQ Information
Duplication Criteria between QC Sample and Duplicate Sample
The 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
1204058202 (North EastDUP) Lead-210 RPD 33.2* (0.00%-20.00%) RER 1.66 (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
1204058201 (MB) Lead-210 Result 0.0000198 < MDA 0.0000203 > RDL 0.000001 uCi/kg
Technical Information
Recounts
Sample 1204058201 (MB) was recounted due to a suspected blank false positive. The recount is reported.
Miscellaneous Information
Additional Comments
The matrix spike, 1204058203 (North EastMS), aliquot was reduced to conserve sample volume.
Product: GFPC, Total Alpha Radium, solid
Analytical Method: EPA 900.1 Mod/ EPA 903.0 Mod
Analytical Procedure: GL-RAD-A-010 REV# 17
Analytical Batch: 1783273
Preparation Method: Dry Soil Prep
Preparation Procedure: GL-RAD-A-021 REV# 23
Preparation Batch: 1777197
The following samples were analyzed using the above methods and analytical procedure(s).
GEL Sample ID#
453309001
453309002
453309003
Client Sample Identification
North East
North West
South West
Method Blank (MB) 1204071564
1204071565
1204071566
1204071567
453309003(South West) Sample Duplicate (DUP)
453309003(South 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 (OC) Information
Matrix Spike (MS) Recovery
Matrix spike (See Below) recovery requirement not met due to the matrix of the sample.
Sample Analyte Value
1204071566 (South WestMS) Total Radium 55.7* (75%-125%)
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
1204071564 (MB) Total Radium Result 0.00000284 < MDA 0.00000291 > RDL 0.00000005 uCi/kg
Technical Information
Sample Re-prep/Re-analysis
Samples were reprepped due to low recovery. The re-analysis is being reported.
Recounts
Sample 1204071566 (South WestMS) was recounted due to low recovery. The recount is reported.
Miscellaneous Information
Additional Comments
The matrix spike, 1204071566 (South WestMS), aliquot was reduced to conserve sample volume.
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: 453309 GEL Work Order: 453309
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.
ReviewNalidation
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:~~~
Date: 25 JUL 2018
Name: Theresa Austin
Title: Group Leader
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary Reoort Date: July 25, 2018 Energy Fuels Resources (USA), Inc. Page I of
225 Union Boulevard
Suite 600
Lakewood, Colorado
Contact: Ms. Kathy Weinel
Workorder: 453309
Parmname NOM C Units RPO% REC% Range Anlst Date Time
lfad Alpha Spec
3atch 1778700
QC1204061587 453309001 DUP
Thorium-232 l.92E-05 2.54E-05 uCi/kg 27.9* (0%-20%) MXS2 07116/18 15:0'
Uncertainty +/-I .58E-06 +/-1.74E-06
QC1204061588 LCS
Thorium-232 0.000132 0.000129 uCi/kg 97.5 (75%-125%) 07/16/18 15:0·
Uncertainty +/-3.49E-06
QC1204061586 MB
Thorium-232 u 2.05E-06 uCi/kg 07/19/18 23:1
Uncertainty +/-l .27E-06
3atch 1778701
QC1204061590 453309001 DUP
Uranium-233/234 0.000142 0.000158 uCi/kg 10.8 (0%-20%) MXS2 07/16/18 15:0·
Uncertainty +/-2.89E-06 +/-2. 78E-06
Uranium-235/236 7.14E-06 7.08E-06 uCi/kg 0.813 (0%-20%)
Uncertainty +/-7.39E-07 +/-6.63E-07
Uranium-238 0.000148 0.000162 uCi/kg 8.69 (0%-20%)
Uncertainty +/-2.94E-06 +/-2.8 IE-06
QC1204061591 LCS
Uranium-233/234 6.65E-05 uCi/kg 07/16/18 15:21
Uncertainty +/-1. 98E-06
Uranium-235/236 3.32E-06 uCi/kg
Uncertainty +/-5.lOE-07
Uranium-238 6.73E-05 6.98E-05 uCi/kg 104 (75%-125%)
Uncertainty +/-2.04E-06
QC1204061589 MB
Uranium-233/234 u l.3 IE-07 uCi/kg 07/16/18 15:0·
Uncertainty +/-2.42E-07
Uranium-235/236 u 2.44E-07 uCi/kg
Uncertainty +/-1.93E-07
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summar:y
Workorder: 453309 Page 2 of
Parm name NOM Sample Qual C Units RPO% REC% Ran e Anlst Date Time
[{ad Alpha Spec
3atch 1778701
Uranium-238 u 1.48E-07 uCi/kg MXS2 07/16/18 15:0·
Uncertainty +/-1.1 OE-07
[{ad Gas Flow
3atch 1777221
QC 1204058202 453309001 DUP
Lead-210 0.000465 0.000332 uCi/kg 33.2* (0%-20%) LXB3 07/18/18 17:2
Uncertainty +/-1. I 9E-05 +/-1.05E-05
QC 1204058204 LCS
Lead-210 0.00826 0.0064 uCi/kg 77.6 (75%-125%) 07/18/18 08:2
Uncertainty +/-9.7JE-05
QC1204058201 MB
Lead-210 u 1.98E-05 uCi/kg 07/19/18 07:5·
Uncertainty +/-6.28E-06
QC1204058203 453309001 MS
Lead-210 0.036 0.000465 0.0292 uCi/kg 79.9 (75%-125%) 07/18/18 08:2
Uncertainty +/-1.l 9E-05 +/-0.00043
3atch 1783273
QC1204071565 453309003 DUP
Total Radium 5.14E-05 4.69E-05 uCi/kg 9.26 (0%-20%) KSD1 07/24/18 18:1
Uncertainty +/-2. 70E-06 +/-3.09E-06
QC1204071567 LCS
Total Radium 0.0052 0.00496 uCi/kg 95.4 (75%-125%) 07/24/18 15:2,
Uncertainty +/-7.40E-05
QC1204071564 MB
Total Radium u 2.84E-06 uCi/kg 07/24/18 18: 1
Uncertainty +/-9.66E-07
QC1204071566 453309003 MS
Total Radium 0.0216 5.14E-05 0.0121 uCi/kg 55.7* (75%-125%) 07/25/18 05:4
Uncertainty +/-2. 70E-06 +/-0.000218
Notes:
Counting Uncertainty is calculated at the 68% confidence level (]-sigma).
The Qualifiers in this report are defined as follows:
** Analyte is a surrogate compound
< Result is less than value reported
GEL LABORATORIES LLC
2040 Savage Road Charleston, SC 29407 -[phone] -www.gel.com
QC Summary
453309 Workorder:
l'armname NOM ----'-S=a_m le Q_ll_ll_!_ __ QC Units_-----'R""P"-'D% REC%
> 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
Range Anlst
NI
ND
NJ
Q
R
u
UI
UJ
UL
X
y
Not considered detected. The associated number is the reported concentration, which may be inaccurate due to a low bias.
Consult Case Narrative, Data Summary package, or Project Manager concerning this qualifier
/\
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 %RPO 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 SOIL T results, the values listed are the measured amounts, not final concentrations.
Where the analytical method has been performed under NELAP certification, the analysis has met all of the
requirements of the NELAC standard unless qualified on the QC Summary.
ATTACHMENT G
STACK SAMPLE LABORATORY RESULTS
Prepared for:
Energy Fuels Resources
6425 S Hwy 91
Blanding, Utah 84511
Date of Report:
July 3, 2018
SECOND QUARTER
RADIONUCLIDE EMISSIONS TEST
CONDUCTED AT
ENERGY FUELS RESOURCES
SOUTH YELLOW CAKE SCRUBBER
YELLOW CAKE DRYER BAGHOUSE
BLANDING, UT AH
MAY 14-16, 2018
by:
TETCO
391 East 620 South
American Fork, UT 84003
Phone [phone]
Fax [phone] fax
CERTIFICATION OF REPORT INTEGRITY
Technical Emissions Testing Company (TETCO) certifies that this report represents the truth as
well as can be derived by the methods employed. Every effort was made to obtain accurate and
representative data and to comply with procedures set forth in the Federal Register.
Reviewer: '° J/4/L--
Mike McNamara
Date:_7_/_3~/ _fit _______ _
Alex Moore
Reviewer: __ ~_......_' __ .,-_?_Z._o_~ __ c _____ _
Date: 1 ~-I~
II
TABLE OF CONTENTS
PAGE
Introduction
Test Purpose ......................................................................................................................... I
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 lrregularities .................................................................................. .4
Percent lsokinetic 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 ...................................................................................... ]
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
I Facility Schematic Representation South Y eJlow 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 detennine the total radionuclide emissions from the South
Yell ow Cake Scrubber and the Yell ow Cake Dryer Baghouse exhausts in terms of Curies per dry
standard cubic foot (Ci/dscf).
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
Yell ow 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 Yell ow 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 SYC Scrubber was completed May 14-15, 2018 and the second run on
May 15-16, 2018.
One run was completed on the Yell ow Cake Dryer Baghouse May 16, 2018.
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 radionucJides:
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
Reed Kitchen
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
Test Participants
Test Facility
State Agency
TETCO
Deviations from EPA Methods
None.
Quality Assurance
Logan Shumway
None
Reed Kitchen
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
Discussion of Errors or Irregularities
None
Percent lsokinetic Sampling
Each test run was isokinetic within the± I 0% of 100% criterion specified in the Federal Register.
Isokinetic values for each test run are presented in Table II.
Table II.
Run#
I
2
Percent Isokinetic Sampline:
South Yellow Cake Yellow Cake Dryer
Scrubber Baghouse
102
103 ....... 101
-----------------
4
None
Percent lsokinetic 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 JI.
Table II.
Run#
I
2
Percent lsokinetic Sampling
South Yellow Cake Yell ow Cake Dryer
Scrubber Baghouse
102
103 --IOI
-----..J...--------
4
SOURCE OPERATION
Process Control Devices Operation
All process control devices were operated nonnally. Recorded scrubber water flow, pressure, and
baghouse ~p readings are found on the test run sheets or in Appendix D.
Process Representativeness
The facility was operated nonnally. Production data was retained by Energy Fuels Resources.
5
SAMPLING AND AN AL YTICAL PROCED URES
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 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 III 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 walJ.
Table III. Sam
Sample Point
l
2
3
4
5
6
Sampling Train Description
Distance (inches) from Inside Wall
SYC Scrubber Dryer Baghouse
0.85 0.70
3.19 2.34
9.56 4.74
11.90 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 316 stainless steel probe liner was used for the
tests. Figure 4 in Appendix E is a sketch of the Methods 5/1 14 sampling train.
Sample boxes were prepared for testing by following the prescribed procedures outlined in
Methods 5/1 14.
Sampling and Analytical Procedures
All sampling and analytical test procedures were as specified in 40 CFR 60, Appendix A,
Methods 5/114.
Quality Assurance
All equipment setup, sampling procedures, sample recovery, and equipment calibrations were
carried out according to the procedures specified in 40 CFR 60 and the Quality Assurance
Handbook for Air Pollulion Measuremenl Syslems.
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
TABLE IV
COMPLETE RESULTS
ENERGY FUELS CORPORATION, BLANDING, UTAH
SOUTH YELLOWCAKE SCRUBBER EXHAUST
Symbol Descrietion Dimensions Run #I Run #2
5/14, 15/18 5/15,16/18
Filter# 2,3 4,5
Begin Time Test Began 5/14/2018 15:05 13:28
End Time Test Ended Sil 5/2018 12:52 11:40
Pb111 Meter Barome1ric Pre$Sure In Hg Abs 24.40 24.40
~H Orifice Pressure Drop In. H,O 1.250 1.065
y Meter Calibration Y Factor dimensionless 0.995 0.995
Vm Volume Gas Sampled--Meter Conditions cf 372.239 347.433
T"' A\'g Meter Temperature 'l 86.4 85.1
..J~p Sq Root Velocity Head Root In H,O 0.6987 0.7187
Wlwc Weight Water Collected Grams 375.2 306.7
T, Dura1ion of Tesl Minu1es 480 480
cp Pitot Tube Coefficient Dimensionless 0.84 0.84
Dn Nozzle Diameter Inches 0.2364 0.2255
CO2 Volume% Carbon Dioxide Percent 2.50 2.30
02 Volume% Oxygen Percent 17.50 16.90
N2 &CO Volume% Nitrogen and Carbon Monoxide Percent 80.00 80.80
Vmstd Volume Gas Sampled (Standard) dscf 292.975 273.951
Vw Volume Water Vapor scr 17.691 14.461
Bws(mcasnrcdl Fraction H,O in Stack Gas (Measured) Frac1ion 0.057 0.050
B W s (sanoratcd) Fraction H,O in Stack Gas (Saturated) f-rac1ion 0.102 0.098
Bws Fraction H,O in Stack Gas * fraction 0.057 0.050
xd Fraction of Dry Gas Fraction 0.943 0.950
Md Molecular Wt Dry Gas lb/lbmol 29.10 29.04
Ms Molecular Wt Stack Gas lb/lbmol 28.47 28.49
%1 Percenl lsokinetic Percenl 103.1 102.2
Ts Avg Stack Temperahore "F I 08.4 106.9
As Stack Cross Sectional Area Sq F1 0.887 0.887
PG Stack Static Pressure In. H,O -0.350 -0.350
Pbr Sample Pon Barometric Pressure In, Hg. Abs 24.33 24.33
Ps Stack Pressure In Hg. Abs 24.304 24.304
Os Stack Gas Volumetric flow Rate (Std) dscfm 1.72E+03 1.79E+03
Q. Stack Gas Volumetric Flow Rate (Actual) cfin 2.42E+03 2.49E+03
v. Velocity of Stack Gas fpm 2.73E+03 2.80E+03
Curies Radionuclides per sample pCi 14249.38 13501.30
Radionuclides per blank pCi 0.22 0.22
Net Curies Net Radionuclides per sample pCi 14249.16 13501.08
Crad Concentration of Radionuclides pCi/dscr 48.636 49.283
ERrad Emission Rate of Radionuclides pCi/lu 5.026E+06 5.281E+06
* lfihe measured moisture content is greater than the salUrated moisture level (supersaturated},
the saturated moisture value will be used in all calculations (40 CFR 60. Method 4, Section 12.1. 7).
Run I average nozzle between .2545 for 3 hours and .2255 for 5 hours
AVG
107.7
1.75[+03
2.45E+03
2.77E+03
48.959
5.154E+06
SVC Scrubber
TABLE V
COMPLETE RESULTS, PM
ENERGY FUELS CORPORATION, BLANDING, UTAH
YELLOW CAKE DRYER BAGHOUSE
Symbol
Date
Filter#
Begin
End
Pb"'
~H
y
Vm
T"' -.J~p
Description
Dale
Time Tesl Began
Time Tesl Ended
Meler Baromelric Pressure
Orifice Pressure Drop
Meier Calibralion Y faclor
Volume Gas Sampled--Meler Condi1ions
Avg Meler Temperature
Sq Rool Veloci1y Head
Wlwc Weigh! Wa1er Collec1ed
T1 D11ra1ion ofTes1
CP Pi101 Tube Coefficienl
D11 Nozzle Oiameler
CO2 Volume% Carbon Dioxide
02 Volume% Oxygen
N 2 & CO Volume% Nirrogen and Carbon Monoxide
V msld Volume Gas Sampled (Slandard)
Vw Volume Waler Vapor
Bw, Frac1ionH20inS1ackGas
Xd Fraction of Ory Gas
Md Molecular W1 Dry Gas
Ms Molecular W1. Slack Gas
o/ol Percent lsokinelic
T5 Avg Slack Temperalnre
A, Slack Cross Sectional Area
PG Slack Static Pressure
Pbp Sample Por1 Baromcrric Pressure
P s Slack Pressure
Q. Slack Gas VolumelTic Flow Rale (Sid)
Q. Slack Gas Volume1ric Flow Ra1e (Aclual)
V 5 Veloci1y ofS1ack Gas
Curies Radionuclides per sample
Curies Radionuclides per blank
Net Curies Nel Radionuclides per sainple
Crad Concen1ra1io11 of Radionuclides
ERrad Emission Ra1e of Radionuclides
Dimensions
111 H!!, Abs
In. Hp
dimensionless
cf
"F
Rool In HzO
Grams
Minutes
Dimensionless
Inches
Percenl
Percenl
Percen1
dscf
scf
Fraction
fraction
lb/lbmol
lb/lbmol
Percenl
Sq. Fi.
111 H20
In Hg. Abs
In Hg Abs
dscnn
cfm
fpm
pCi
pCi
pCi
pCi/dscf
pCi/hr
Run #I
5/16/2018
8: 17
10:21
24.50
1.688
0.998
99.250
68.9
0.8053
3.8
120
0.84
0.2270
0.00
20.90
79.10
81.381
0.179
0.002
0.998
28.84
28.81
100.5
88.4
1.396
-0.38
24.43
24.402
3.35E+03
4.28E+03
3.06E+03
42 .14
0.22
41 .92
0.515
I .036E+05
Dryer Baahouse 13
Method 5 Nomenclature
%1 = percent isokinetic as a percent
As = stack cross-sectional area (ft3)
ASAf> =see~
Btu = unit heat value (British thermal unit)
Bws = fraction of water in stack gas
Cr = concentration of front half particulate matter (gr/dscf, lb/dscf, etc.)
Cmeial = concentration of metals (ppm, µg/ft3, etc.). Atomic symbol replaces "metal"
CO2 = percent carbon dioxide in the stack gas
Cp = Pitot tube coefficient
Cx (avg) = average concentration of x
Cx <corr) = concentration of x corrected to the required percent 02
Deq = equivalent diameter for rectangular stack
l'.1H = orifice pressure drop (inches H20)
l'.1H@ = orifice pressure (inches H20)
Dn = nozzle diameter (inches)
Dn des = calculated desired nozzle size (inches)
l'.1P = stack flow pressure differential (inches H20)
D, = diameter of the stack (feet)
EA = percent excess air
ERr = emission rate of front half particulate (lb/hr)
ERmmBiu = emission rate per mmBtu or ton of fuel etc.
ERx = emission rate of compound. Specific compound replaces x
K-fact = multiplier of test point Af> to determine test point .1H
L = length of rectangular stack (inches)
Md = molecular weight of stack gas, dry basis (lb/lb-mol)
Mliher = mass of particulate on filter (mg)
Mr = mass of particulate matter on tilter and in front wash (mg)
mmBtu = million Btu
Mp = mass of particulate matter in front wash including probe (mg)
M, = molecular weight of stack gas, wet basis (g/gmol)
N2 = percent nitrogen in the stack gas
02 = percent oxygen in the stack gas
JAf> = average of the square roots of .1P (may also be referred to as AS.1P)
Pb111 = absolute barometric pressure at the dry gas meter (inches Hg)
Pbp = absolute barometric pressure at the sample location (inches Hg)
Pa = stack static pressure (inches H20)
P, = absolute stack pressure (inches Hg)
P,id = absolute pressure at standard conditions (29.92 inches Hg.)
e = time length of test (minutes)
Oa = stack gas volumetric flow rate (acfm)
Os = stack gas volumetric flow rate (dscfm)
Ow = wet stack gas std. volumetric flow (ft3/min, wscfm)
Tm = meter temperature (°F)
T, = stack temperature (°F)
Tsid = absolute temperature at standard conditions (528°R)
Tt = see e
Vm = sample volume (ft3) at meter conditions
Ymsid = volume standard (dscf), sample volume adjusted to 68°F and 29.92 inches Hg.
Method 5 Nomenclature
Vs = velocity of stack gas (f pm)
V w = volume water vapor (scf) at 68°F and 29.92 inches Hg.
W = width of rectangular stack (inches)
Wtwc = weight of the condensed water collected (grams)
Xd = fraction of dry gas
Y = meter calibration Y-factor (dimensionless)
Method 5 Sample Equations
Yms1d · (Ts +460) · 1039 %1=-~-~-~-o--
() · Vs · P s · Xd · D~
D~n A,.=-., 4
Yw Bws = ----Vmstd + Yw
Mrp · 0.01543 Cr = ----'---Vms1<1
20.9 -desired %02
Cx (con) = Cx (avg)· 20 9 I m O . -aclua 70 2
2-L ·W
Deq = L+W r -'-'-------;:========
Dndes = 0.0269 · (Pbm +0.0735)
(Tm +460) · Cp · Xd Ps · Af>
%02 -0.5 · %CO EA=----------0.264 · %N2 -(%02 -0.5 · %CO)
ERr = Cr · Q5 • 0.00857
ERx
ERmmBtu = mmBtu/hr
846.72 · Dn4 · ~H@ · C~ · X~ ·Md· Ps · (Tm +460)
K-fact = t.H Ms· (Ts+ 460) · (Pbm + m)
Md = CO2 · 0.44 + 02 · 0.32 + N2 · 0.28
M, = Md · X<1 + l 8 · Bws
PG P. = Pbp+-., 13 .6
Qa = Vs ·As
Qa · Xd · P s · T std Q,=-----' (T + 460) · P.~t<l
Q -Q,
w -xd
T," (Pbm + :;: )
Vmsid = Vm · Y · ---'-----'-(Tm +460) · Pstd
V., = 85 .49 · 60 · Cp · v'Af> ·
Yw = Wtwc ·0.04715
X<l = 1-Bws
~--
APPENDIXB
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
Date
Barometric Pressure
Pbm in Hg Pbp in Hg
B Static Pressure (PG) in H20
Estimated Moisture (Bw,) 1-3 %
Sample Height from Ground 65 feet
Sample Height from Console feet
Comments: -----------------------
S1ack Diame1er 12.75" Reference 0.0"
Pons are 7.0' Upstream from next disturbance
Pons are 30.0' Downstream from las! disturbance
Pon Diameter Type Particulate
Num of Pons 2 Num. Points 8
Traverse Percent Distance From: Ports
Point Diameter ID Reference A B C D E F
1 6.70% 0.85 0.85
2 25.00% 3.19 3.19
3 75.00% 9.56 9.56
4 93.30% l 1.90 11.90
Averages:
Ts ___ _ LFlow -----
~p 'V~P
KEY=>1 ~T_s ___ ~_P __ L_F_l_ow_.l
__ 511 I 4_ Field Data Sheet
1,..--TETCO /}
Filter ~ Sample Box /.? "s ---
Location: South Y II
Operator: ----'.__-1---------
Plant: En£'1Fuels' ~ l
Date \~ tst'. 1\\6 \ \j
Port TraYerse Time ] OGM
Point Clock Min (9) en·~
t>P ii 6H fin H,0) /I Vacuum I r I --· · · j .... '• •••
~ __ 1 ll -\l.5~05 I
1
1
2
2
2
3
3
'rJ-
i L ... , ~11 1-II .. . . 11-.... II • · 1 • IL..........L..JI • -, ..... -I . t= I . I II --I . ----, -...... ~ ,::.;A ._.j -I I • F'*I F.------.c-1 i ..., , _ a1-.~il ,__ -1/. ..., 'z -1 -
4
-I k,-s
~"
{ ... "
2
2,) 2
.f O 2
t, 3
1.J 3
~ " 3
1 4
t" 4
..{0 4
'~i. . ""t
·~ 1, 'I -~" ., 1-~o' V I..{ I '{ +-Total -. "" 3, it .1.,zi ~ _ -zSD IO~·~ ~~·~ Average ,/ . , ... G-1
Commems:
Page _l_of_l_ Run# t
r 0 N
Stack Diameter 12.75" .. Port Reference Q'.'.__
Pons are _7' __ Upstream from next disturbance
Pons are 30' Downstream from last disturbance
Assumed Moisture 3.5 %
Probe /·P & Cp~
Nozzle Calibration ,$'"" . zri , is-'{ . ·"U;.-s-· -z..<>'
Avg Dn • ~~S'"'inches
Gas Bag ~:;:J,-'
Console_~--=--
Y-Factor O ·"i ~
6H@ l·Si _> H10
Barom:tr[f5e)res ,t; 'Z..
Pili~ m Hg
Pb Z:'f. i ~ · °'· -z.., P m·Hg
P,; -D-3f ~~
LukChcdt. Pre :J;~ _ ,Po SJ
fl>/mm O · () C W D · 0 0 ~ b' O"O'
.,.clnHs '1-0 z_() IS
Pitot Rate O , c)
lnH,O ~-~
t) .c)
'Ls
6. C>
9. !'
Water Collected 3 7S: "Z-
T;M:::. "!fl ~0 ~ ~-~.....____:. ___ cclm~
K = :0.Jo'"""<;. .@.Tm !(-··/'· -.@_T.,
~t~
k c~t) Rate( ft3/m~ bGM after leak check fVac("Hg) f Rate( ft3/min)
C · "O * 2'!.~ _1,l
o~oo~
*' (,1,....J
-LO 0 '-()~~ -.
i\J~"~l, ~l, . (, \"' ,o
'l ~ &--\
__ 5/114_ Field Data Sheet
~ '11. OTETCO
Filter _I _ Sample Box 6 Page_l_of_l _ Run# -Z...
Plant Energy ~els ~ "/Jr::. I \
Date\~~ \ 2 \~f f !,\ f K
Location: S'.Qftow Cake Dryer Scrubbet
Operator: "')
Point
DGM 6P ii 6H l
0
in H,OJ II Vacuum II Te~peratures :'>1 II DGM T~np (T ... J Traverse II Time Ii Port i 0 N
Stack Diameter 12.75" __ Port Referenre Q'.'.__
2
2
2
3
3
3 -
4
4
~ ~~ 1:i.10
2
2
2
3
3
4
Total
Average
Comments:
~ J v"-";~,.Jh
I" \Y'
\''
; '-i~-~~3.; 1"i.i,~1l1-is.s'r
.; ·t\~"i' \-o~~
. -..
-'l,, S'~ ~
l Dk·°\
o~rl~'ti ~ak check Vac ("Hg)
I<('
Rate( ft3/min) D,ou<., DGM azer llak \eek '2 I l#• (:'.)
Vac ("Hg)
-Zl)
1.f0~1'
~s--1
Ports are
Ports are
Rate( ft3/min)
0 .()() ~
_7_' __ Upstream from next disturbanre
30' Downstream from last disturbance
Assumed Moisture &,
Probe l Y ~'lo
Cp __QM
Noz~ibration
..J:__ -~ . vzJ~ .z,,1,h
AvgD, ·;;~
Gas Bag 6
Console ~
Y-Factor~~
6Hc;_ II •·-$'_[[ ? in HiO
Barometric Pressures
in Hg "Z, ~. oC>
Leak Check
ftJ/min
vac in Hg
Pitol Rate
In H10
Pbm 'Z.~-<.f 0
Pb, '2 '3}
Po"" o-~5
Pre
O.·~ r:,1-
~
Q•O.-
1·S
in Hg ?,, J.. • '( 3
~~t0·1'o
0· O o ~ fo_S,J i!o ~ I~ ----
Q:.Q
Gf.5
l). 0
~
Water Collected ;> C)(p . ~
Time Sampled t-lB·o g ~ Q;J;, :'.~ t'..,jrJ cdm,n
K= @Tm
K= @Tm
1, _.,\ ,,
Preliminary
Facility Enernv Fuels
~ Stack Identification Yellow Cake Dryer Baghouse
N>-Date
Barometric Pressure
Pbm in Hg PbP in Hg
t-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"
Ports are 4.75' Upslream from nei<I disturbance
Ports are 37.83' Downs1ream from last disturbance
Port Diameter Type Particulate
Num. of Ports 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 s). ·rz ..
2 14.60% 2.34 2.34 ~
3 29.60% 4.74 4.74 fl '> 'f ...
4 70.40% 11.26 11.26 ?J(., 1(
5 85.40% 13.66 13.66
6 95.60% 15.30 15.30 ~& .,o
Averages:
Ts ___ _ L. Flow -----
ilP ,,fap -----
KEY=>
~~.!.!_-fil Field Data Sheet
Plant: Energy Fuels
Date: 511 'o i / 'Q
Triverse Time DGM aP 6H [ .. H,01
Point Clock Min (9) en', (inll:0) Desired Actual
1 PJ. 1'1--0 I~ J{,, . Y 2-5° ,ft; 7~ l,l., I I. l> I
2 lo ~"i4.;40 .~ 7 i. ~ I /.~ l
3 2,0 1&i < i.. SJo .1.,,( l, (,~ [,(. Cf
4 ·~o (.Cto.$ fc, ' 7 '1 L,c{ ? ,,:;
5 '-fc t..C..'t.~~o 17'-f i '"1 '2.-l.°r'Z,
6 5o 1#7S ~1q~ • ~ 1-i.1 <{ /, 14
1 'I'. 2.1 (..-0 1v; s, q57-. S'"S [. Y.:, /.'1 ~
2 ")O <,,'14 ,~{0 .i,d j , t..3 1-< .• .3
3 9,o ~oz. 87-< ., ( I. I., '1. I.(/'\
4 qo '1-I l . 1.:?u · 10 I ·6'2..-I, •f?? ~
5 ico ':11CJ.C.C/O ·S'i I ' { '.) i ,{ 3
6 Uc "l-2.+ ~ 1-( 159 l, {J I ,{1
!Q' Z,( lTi I") / / -:t,) ,.[,.,', \
Filter O) TETCO (\
Sample Box--12__
Vacuum
(inllEII
.5
3
L/
'-I
'S ,c:;
,;
4
l/
LI .. ,
l/
Location: Yellowcake Dryer Baghouse
Operator: M, . iM ~ ; J tM,,\C,tJ-
Temperatures,),
Stack (T,) Probe Probe Out Filter EfTluent
'o"]-r Z,/o z{t z.n 4~
£,'=+--'2 {~ l,c l7o 4~ s·-:i "'210 2Yt... ?. LI\,.., YtA
9,. +-7, 7.Cr 2.1''0 7,--0 4 9.
8 P1 ·,uo -Z.-:\'l!, c~o) 1, 9
Bi 2.'io 2. ]'7 231' 49
B'l Z·{l
"2. "''
l.lf~ 52
89 2.<./ -z... 2 ;'i. 2, ;' 2., 51
Ser z 30 2 ,;-I " ( I c; i
'O'l Z'3°t ·z <t°l 7 '-iq c;'l,
9o 2'18 7.4'1 'l4~ _c; /
<to z o/ct l ;'J Uc 17
Total q9 , -z,{O ./ .,14 l.(,3i v' ~/~lO~I /
1,0,7..;o
·--· ... -6oS 3 ,.lib£? €>S,t../
Comments: Time BaghouseM> Time Baqhouse M> 5 ?) o-..C I e... 'I :7 s·.w '3 t q '],.( 7.£>
g :Lio L , p"I '\ .... , l-,<JJ
'\ ·.co 2,t? 1c '.o{ 1.,0
l of _I Page -I Run# -
DOM Temp (T 81
i B
I Ao N
Out In
r..., 6 {
(:, (J (o ( Stack Diameter 16" __ Port Reference _0.0"_
fe,9
ti
7 <,
17_
71
lt
7')
7'd A,
~(
b )_ " ~ (~ ~<,
(., (.,
~~
(..€
lS
t.?9
le)
71
Ports are
Pons are
l~ 5~ ./
kn 0.
!1L_ Upstream from next disturbance
37.8' Downstream from last disturbanc~
Assumed Moisture %, ---
Probe 2. ·7 (a -· l Cp _QM
No22Je Calibration --"
iZ:if:~~~
AvgD0 •~inches ~
Gas Bag Ambient Air
Console --1---
Y-Factor ~
6Hc I. ]b 4-in H,O
Barometric Pressures
Pb., 2 4 · SO in Hg
Pb0 Z '-I , "1 > in Hg
Pu -• J ~ in H20
Leak Che<k: Pre ./ Post
0 ·<.;0'z..
1'2 .00
R'lmin O C'O )
var in Hg Z O. () Q
Pi101 Ra« () ·U ___Q:_()
In H,O lQ_ ~
Water Collected ")-(
Time Sampled (Z,,Q
Review ~
K= _@1'.:
--,, ~·1n
,'\J on.1e C u.L ;~ lk.... +.o(I
, 11. 1-.-n~ . v:=r _ Tl1'
/~J e. Or. .2B
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
APPENDIX C
C
Method 5
Facility: l~11t:rg> Fu~I::; Date: S/1"1 J /{ / 1'o
Stack Identification: 5yt... · -Su.Jku: Method: 5
IMPINGERS
Filter Number:
0:L
IMPINGERS
Filter Number:
JMPjNGf:RS
Filter Number:
Sample Box:~£>""'----Run: ----
lmpmger Number
2 3 I 4 I 5
lnilial Volume of liquid (H20) in impingers, (ml)
Final (g) ___ ---1,---=--1-.c..........--'---1.-+--'-------+----+----
I nitial (g) ..-.,.c...:.--<--+""-'...__._-+-=;__;;;..;..._+--1-~"'-'---+----+----
Net (g) ========================::!::::::::====::!=!:=:!:::::::!:===~===
Total (g) ;J 7 £, ?_. =========
Run: J-Sample Box:-~---
lmpmger Number
.J... ,,.L 6
JOO
Initial (g)...._,'----+1-~~---~--+-----+----1----
Net (g) :::::!:::====t:=~===t===!=========;:::::*=:::::!::::=============
Run: ----Sample Box: ___ _
lmpmger Number
2 I 3 I ,,,,!,, I s 6
lni1ial Volume of liquid (H20) in 1mpmgcrs, (ml)
l(II) ((It) I [ SG I
Final (g) ___ -+----+----.f-----+----+----
lnitial (gl ___ -1-----1----+-------1,----+----
Net tgl ===================::::::!:===~===
Total (g) ========
<..)
(ocation Plant____._D,,_',..f.._\l'\_; ~.,___iJ_V'\ __ ift't __ ~----=----l:_-_K~ --------------------
Analytical Method ____________ ._
Tes,
0!:~
Gas Bag No. ~-0 7 ~
Ambient Temp =!0.
Operator__.~1----->,--. __
Date 4G'\,u\\~
Test No. z:
G~B,gNo.~
Ambient Temp
Operator
Date -----TestNo. -----Gas Bag No. -----Ambient Temp ____ _
Operator -----
Gas
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N2 (Net is I 00 Minus
Actual 02 Reading).
Gas
CO2
0 2 (Net is Actual 02
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 0 2 Reading).
Gas
0 2 (Net is Actual 0 2
Reading Minus Actual
CO2 Reading).
N2 (Net is 100 Minus
Actual 0 2 Reading).
Aclual Nel
Reading
Aclual
Reading
't.-;
1 '1·-V
Aclual
Reading
Nu
1 ·..,
I lo·"\
Net
RUN
2
Aclual Nel
Rudin&
i< ,...--
2.-~
RUN
2
Aclual Ner
Reading
z., -z '"3
\~-t. I l, ·1
RUN
2
Aclual Net
Rcadinc
to2 was determined using a gas analyzer
CO is not measured, as it has the same molecular weight as N2
3
Aclual Net
Reading
i-~ i.S-
3
Aclual Ner
Reading
2•) 2·)
\ l· z:.. r l,·~
3
Aclual Net
Reading
Average
Net
Volume
l-,· ~
Average
Net
Volume
2· 3
/ l,,'1
Average
Net
Volume
Method 5
Facilily: Em::rg>· Fuels Date: --------
Stack Identification: '(r;;,}/0u Cd&.-8t,~S,e, Method: --------5
IMPINGf:RS
Filter Number:
0\
IMPINGERS
Filter Number:
IMPJNGERS
Filter Number:
Run: ----Sample Box: A
Impinger Number
2
1,9 l,"{, l
Total (g) ] ,8
Run: ----Sample Dox: ___ _
..L 2 I ..1.,,, I 4 I s
]mpinger Number
Jni1ial Volume or liquid IHLO) in impingers, (ml)
100 100 ! ! SG !
Final (g) ----+-----+-----+-----+-----+-----
T nit i a I (gl----1-----1-----1-----1-----1-----
Nel (!ll =============================
Total (g) ========
Run: ----Sample Box.: ___ _
lmpmger Number
_L 2 I 3 I 4 I 5 6
Initial Volume ofhquid (H10) in impinge.rs, (ml)
lOO too I I SG I
Final (g) ----+-----+-----+-----+-----+-----
1 nit i a I (!l) ____ l-----1-----1-----1------1-----
Nel (g) =============================
Total (gl ======== --------
'i/t~/16
.. ,a~ /IM't:
··-· ..... --JNTER-MOU,,. JAIN LAU~
Client Name
Inter-Mountain Labs
Sheridan, WY and Gillette, WY
SAMPLE
~ 1·'l'!'l!la1 I 1'JI I Al-~--:-·1 _LJ.Za I ...._ I .-I
IDENTIFICATION Matrix IContainersl :,· I Ii?-L~il,:i= Pi; J~·~l-"Y 'I
[RI FedEx
D USPS
D Hand Carried
D Other
Inter-Mountain Labs. Inc.
Solid
Filter
Other
15:05 02,03 SVC Scrubber RUN 1 FT I
13:28 04,05 SYC Scrubber RUN 2 FT
8:17 01 Yellow Cake Dryer B~ghouse FT
15:05 102,03 SYC Scrubber RUN 1 OT
13:28
8:17
SL
SD
FT
OT
04,05 SYC Scrubber RUN 2
101 Yellow Cake Dryer Baghouse
Standard turnaround
11;1)RUSH -5 Working Days
m URGENT -< 2 Working Days
OT
OT
www.intermountainlabs.com
I
1
1
1
1
1
I I I \ 1 1 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
Page 1 of 1
#WEB
REMARKS I
.JConduct /Blanks
1
Fuels Blandino: Logan Shumwa
Rev4.6 Web
~I: Inter-Mountain Labs r-r. i .;·, ".'~?CHAIN Qf.·CUSTODY RECORD.,;.;-~ ,t' ,• • . . I . ·-.~,, -Page 1 of 1
Sheridan, WY and Gillette. WY Alf shaded fields must be completed. #WEB IH TCk-M OUN'f41H L.A.0 S This 1s a legal documenl any misrepresentation may be construed as fraud
Client Name Projecl Identification Sampler (Signature/Attestalion of Authenticity) Telephone#
En -FueJa rt.~· ~~·('1 South Yiiow ~ SQ'ubber._Dryer ,,
~-4.3&818-4113 ' ,,_ 1 ~ --Report Address Contact Name ......... ,_. ---... "" ... ··-·-. -· ..
11 lait D South -1: ''.iP~ ~!'./:; Dun or Paui l<Jtc6en -~.r,.~~;,,'.~
....... Fork, Utah,~ i ... ,."· ;f.:\l .. l ~~~~ ... J:.~ tt'fl.. .. ~ ';i Emal! 'l -"l, ~,, ..... \ Invoice Address Phone ~ r~ EFRf ®-:ounla--:-Pa,ilile-. --Purchase Order# Quote# . -"~ ' \ '\ \ 0 Union Bvld.8ula IOO .LalcewOOd co.aG228 -~ ----~ I /.'fl REMARKS --~ I 1. ! TIME SAMPLE #of ! ] Conduct /Blanks
,,
IDENTIFICATION Matrix Containers I I ~i ~-
15:05 02,03 SYC Scrubber RUN 1 FT 1 X X X X X X X
13:28 04,05 SYC Scrubber RUN 2 FT 1 X X X X X X X
8:17 01 Yellow Cak.e Dryer Baghouse FT 1 X X X X X X X
15:05 02,03 SYC Scrubber RUN 1 OT 1 X X X X X X X
13:28 04,05 SYC Scrubber RUN 2 OT 1 X X X X X X X
8:17 01 Yellow Cake Dryer_Baghouse OT 1 X X X X X X X
Compliance Monitoring ?
0 FedEx Soil SL
0 USPS Solid SD
Program (SOWA, NPDES .... ) -·. --,._, __ _ PWSID /Permit# -::-_ ----•c-o_n_t_ac-t'-'a"-1-=E-n.:.e.:.r _F_u_e_ls--=-B-la-n-,di:-n-. L_o_a_n_S::-:h_u_m_w_a--t
0 Hand Carried Filter FT Chlorinated? •
D Other Other OT Rus/1 & Urgem .Surch,1r9es will be applied Lab
Inter-Mountain Labs Inc www.intermountainlabs com Rev 4.6 Web
~~I: Your Environmental Monitoring Partner
Inter-Mountain Labs----------------------------------------
'"' .. ·"'0uH r"1" ,us 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 7/2/2018
391 East 620 South Report ID S1805352001
American Fork. UT 84003
ProjectName: South Yellow Cake Scrubber, Dryer Work Order: S1805352
Lab ID: S1805352-001 Collection Date: 5/18/2018 3:05:00 PM
ClientSample ID: 02,03 SVC Scrubber RUN 1 filter & beaker Date Received: 5/22/2018 8:07:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 2.67E-5 µCi/Sample 2E-06 6E-14 OTW01 06/09/2018 1524 MB
Lead 210 Precision(±) 3.0E-6 µCi/Sample OTWOl 06/09/2018 1524 MB
Radium 226 5E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 06/06/2018 1637 MB
Radium 226 Precision (±) 2E-7 µCi/Sample SM 7500RAB 06/06/2018 1637 MB
Radium 228 -3.6E-6 µCi/Sample 1 E-06 2E-13 Ga-Tech 06/28/2018 1208 WN
Radium 228 Precision(±) 7.1 E-6 µCi/Sample Ga-Tech 06/28/2018 1208 WN
Thorium 230 2.lE-6 µCi/Sample 2E-07 3E-15 ACW10 06/27/2018 816 MB
Thorium-230 Precision (±) 6E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 228 4E-8 µCi/Sample 2E-07 3E-15 ACW10 06/27/2018 816 MB
Thorium-228 Precision (±) 1 E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 232 4E-8 µCi/Sample 2E-07 3E-15 ACW10 06/27/2018 816 MB
Thorium-232 Precision (±) 1 E-7 µCi/Sample ACW10 06/27/2018 816 MB
Uranium 234 6.8E-3 µCi/Sample 4E-07 9E-15 ACWOl 06/27/2018 000 MB
Uranium 234 Precision (±) 1.3E-3 µCi/Sample ACWOl 06/27/2018 000 MB
Uranium 235 4.2E-4 µCi/Sample 4E-07 9E-15 ACWOl 06/27/2018 000 MB
Uranium 235 Precision (±) 8.4E-4 µCi/Sample ACWOl 06/27/2018 000 MB
Uranium 238 7.0E-3 µCi/Sample 4E-07 9E-15 ACWOl 06/27/2018 000 MB
Uranium 238 Precision (±) 1.4E-3 µCi/Sample ACWOl 06/27/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 06/11/20181331 MS
Uranium 15000 µg/Sample 9E-15 EPA 200.8 05/24/2018 2057 MS
These results apply only to lhe samples tested. RL -Reporting Limit
Qualifiers: B Analyte detected in the associated Method Blank C Calculated Value
E Value above quantitation ranqe G Analyzed at IML Gillette laboratory
H Holdinq times lor preparation or analysis exceeded J Analyte detected below guantilation limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Not Detected at the Reportinq Limit O Outside the Range or Dilutions
S Spike Recovery outside accepted recovery limits U Analysis reponed under the reporting limit
X Matrix Effect
~ Reviewed by: -~--------------
Wade Nieuwsma, Assistant Laboratory Manager Page 1 or 3
.~(.jtt: Your Environmental Monitoring Partner
Inter-Mountain Labs
IHJH .. •MOUIHAIH UtG5 1673 Terra Avenue. Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 7/2/2018
391 East 620 South Report ID S 1805352001
American Fork, UT 84003
ProjectName: South Yellow Cake Scrubber. Dryer Work Order: S1805352
Lab ID: S1805352-002 Collection Date: 5/18/2018 1: 28:00 PM
ClientSample ID: 04,05 SVC Scrubber RUN 2 filter & beaker Date Received: 5/22/2018 8:07:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RRDL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 210 4.54E-5 µCi/Sample 2E-06 6E-14 OTW01 06/09/2018 1524 MB
Lead 210 Precision(±) 5.7E-6 µCi/Sample OTW01 06/09/2018 1524 MB
Radium 226 8E-7 µCi/Sample 2E-07 9E-14 SM 7500RAB 06/06/2018 1637 MB
Radium 226 Precision (±) 2E-7 µCi/Sample SM 7500RAB 06/06/2018 163 7 MB
Radium 228 1.26E-5 µCi/Sample 1E-06 2E-13 Ga-Tech 06/28/2018 1512 WN
Radium 228 Precision (±) 9.9E-6 µCi/Sample Ga-Tech 06/28/2018 1512 WN
Thorium 230 2.4E-6 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-230 Precision (±) 6E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 228 1 E-7 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-228 Precision(±) 1 E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 232 OE-7 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-232 Precision (±) OE-7 µCi/Sample ACW10 06/27/2018 816 MB
Uranium 234 6.0E-3 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 234 Precision (±) 1.2E-3 µCi/Sample ACW01 06/27/2018 000 MB
Uranium 235 4.4E-4 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 235 Precision (±) 8.7E-4 µCi/Sample ACW01 06/27/2018 000 MB
Uranium 238 7.0E-3 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 238 Precision (±) 1.4E-3 µCi/Sample ACW01 06/27/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 06/11/2018 1334 MS
Uranium 16600 µg/Sample 1 9E-15 EPA 200.8 05/24/2018 2120 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 ranqe G Analyzed at IML Gillelle laboratory
H Holdinq 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 Reportin!J Limit 0 Outside the Ranqe of Dilutions
S Spike Recovery outside accepted recovery limits U Analysis reported under the reportinq limit
X Matrix Effect
~ /J ---4' .r
Reviewed by: ... ~'-""'--C,,e/-------------------
Wade Nieuwsma, Assistant Laboratory Manager Page 2 of 3
,~i,. . Im~ Inter-Mountain Labs
Your Environmental Monitoring Partner
IN'rflll:~MOUl'olf~lf( \.AIJS 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
Company: Energy Fuels (White Mesa) Date Reported 7/2/2018
391 East 620 South Report ID S1805352001
American Fork, UT 84003
Project Name: South Yellow Cake Scrubber, Dryer Work Order: S1805352
Lab 10: S1805352-003 CollectionDate: 5/16/2018 8:17:00 AM
ClientSample 10: 01 Yellow Cake Dryer Baghouse Date Received: 5/22/2018 8:07:00 AM
COC: WEB FieldSampler:
Matrix: Filter
Comments
Analyses Result Units Qual RL RROL Method Date Analyzed/lnit µCi/ml
Radionuclides -Filter
Lead 21 O 1.59E-5 µCi/Sample 2E-06 6E-14 OTW01 06/09/2018 1524 MB
Lead 210 Precision(±) 2.7 µCi/Sample OTW01 06/09/20181524 MB
Radium 226 1.6E-6 µCi/Sample 2E-07 9E-14 SM 7500RAB 06/06/2018 1637 MB
Radium 226 Precision (±) 2E-7 µCi/Sample SM 7500RAB 06/06/2018 1637 MB
Radium 228 -9.7E-6 µCi/Sample 1 E-06 2E-13 Ga-Tech 06/28/2018 1815 WN
Radium 228 Precision (±) 8.5E-6 µCi/Sample Ga-Tech 06/28/2018 1815 WN
Thorium 230 8E-7 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-230 Precision (±) 4E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 228 4E-8 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-228 Precision (±) 1 E-7 µCi/Sample ACW10 06/27/2018 816 MB
Thorium 232 OE-7 µCi/Sample 3E-15 3E-15 ACW10 06/27/2018 816 MB
Thorium-232 Precision(±) OE-7 µCi/Sample ACW10 06/27/2018 816 MB
Uranium 234 1.1 E-5 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 234 Precision (±) 4.8E-6 µCi/Sample ACW01 06/27/2018 000 MB
Uranium 235 3.6E-6 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 235 Precision (±) 2.9E-6 µCi/Sample ACW01 06/27/2018 000 MB
Uranium 238 9.2E-6 µCi/Sample 4E-07 9E-15 ACW01 06/27/2018 000 MB
Uranium 238 Precision (±) 4.5E-6 µCi/Sample ACW01 06/27/2018 000 MB
Metals -Total
Thorium 232 ND µg/Sample 45 3E-15 EPA 200.8 06/11/2018 1337 MS
Uranium 19 µg/Sample 9E-15 EPA 200.8 05/24/2018 2126 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 quanlilation ran\'.je G Analyzed at IML Gillette laboratory
H Holdinq times for preparation or analysis exceeded J Analyte detected below quantitalion limits
L Analyzed by another laboratory M Value exceeds Monthly Ave or MCL or is less than LCL
ND Nol Detected at the Reportinq Limit 0 Outside the Ran\'.je of Dilutions
S Spike Recovery outside accepted recovery limits U Analysis reported under the reportinq limit
X Matrix Effect
~/J.-4" ~ Reviewed by:~~~'-~--._____ ________ _
Wade Nieuwsma, Assistant Laboratory Manager Page 3 of 3
.... ~II: Your Environmental Monitoring Partner
Inter-Mountain Labs-----------------------------------------
uin1E-"·"'ou .. n"1" LABS 1673 Terra Avenue. Sheridan. Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1805352
Project: South Yellow Cake Scrubber, Dryer
Lead 210 in Filters
LCS-682 (06/08/18 17:59)
Analyte
Lead 210
Lead 210 in Filters
MS-682 (06/08/18 17:59)
Analyte
Lead 210
Lead 210 in Filters
MSD-682 (06/08/18 17:59)
Analyte
Lead 210
Radium 228 by Ga/Tech
MB-510 (06/27/18 23:04)
Analyte
Radium 228
Radium 228 by Ga/Tech
LCS-510 (06/28/18 02:08)
Analyte
Radium 228
Radium 228 by Ga/Tech
MS-510 (06/28/18 08:16)
Analyte
Radium 228
Radium 228 by Ga/Tech
Qualifiers:
MSD-510 (06/28/18 21:18)
Analyte
Radium 228
B Analyte detected in the associated Method Blank
G Analyzed at IML Gillette laboratory
J Analyte detec1ed below quantitation limits
ND Not Detected at the Reporting Limit
R RPO outside accepted recovery limits
X Matrix Effect
Date: 7/2/2018
Report ID: S1805352001
Sample Type LCS Units: µCi/Sample
RunNo: 158098 PrepDate: 05/29/18 0:00 BatchlD R158098
Result RL Spike Rer Samp %REC % Rec Limits Qual
1E-05 2E-06 1E-05 93.8 80 -147
Sample Type MS Units: µCi/Sample
RunNo: 158098 PrepDate: 05/29/18 0:00 Batch ID Rl 58098
Result RL Spike Rer Samp %REC % Rec Limits Qual
1 E-05 2E-06 1E-05 ND 97.2 80 -143
Sample Type MSD Units: µCi/Sample
RunNo: 158098 PrepDate: 05/29/18 0:00 BatchlD R158098
Result RL Cone %RPO %REC % RPO Limits Qual
1 E-05
Sample Type MBLK
2E-06 1 E-05 6.66
Units: µCi/Sample
90.4 20
RunNo: 158641 PrepDate: 06/04/18 12:00 BatchlD 14718
Resull RL Spike Ref Samp %REC % Rec Limits Qual
ND
Sample Type LCS
lE-06
Units: µCi/Sample
RunNo: 158641
Result
PrepDate: 06/04/18 12 :OD BatchlD 14718
RL Spike Rer Samp %REC % Rec Limits Qual
3E-05
Sample Type MS
1 E-06 4E-05 80.8
Units: µCi/Sample
65.9-132
RunNo: 158641 PrepDate: 06/04/18 12:00 BatchlD 14718
Result RL Spike Ref Samp %REC % Rec Limits Qual
4E-05
Sample Type MSD
1E-06 4E-05 ND
Units: µCl/Sample
PrepDate: 06/04/18 12:00
90.l 50-130
E
H
L
0
s
BatchlD 14718 RunNo: 1 58641
Result RL Cone %RPO %REC % RPD Limits Qual
4E-05 1 E-06 4E-05 9.16 98.8 20
Value above quantitation range
Holding times for preparation or analysis exceeded
Analyzed by another laboratory
Outside the Range or Dilutions
Spike Recovery outside accepted recovery limits
Page 1 of 3
Your Environmental Monitoring Partner ,,,~m-1::
Inter-Mountain Labs-----------------------------------------
lMUR·MOUNTAIN L'A8S 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT:
Work Order:
Energy Fuels (White Mesa)
S1805352
Project: South Yellow Cake Scrubber. Dryer
Radium 226 Air Filter Analysis
MB-1865 (06/06/18 16: 3 7)
Analyte
Radium 226
Radium 226 Air Filter Analysis
LCS-1865 (06/06/1816:37)
Analyte
Radium 226
Radium 226 Air Filter Analysis
MS-1865 (06/06/18 16:3 7)
Analyte
Radium 226
Thorium Air Filter Analysis
MB-606 (06/27/1808: 16)
Analyte
Thorium-230
Thorium Air Filter Analysis
LCS-606 (06/26/18 22:03)
Analyte
Thorium-230
Thorium-232
Uranium Isotopic Filters
MB-37 (06/27/18 00:00)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
LCS-37 (06/27/18 00:00)
Analyte
Uranium 234
Uranium 235
Uranium 238
Uranium Isotopic Filters
LCSD-37 (06/27/18 00:00)
Analyte
Qualifiers: B
G
J
ND
R
X
Uranium 234
Uranium 238
Analyte detected in the associated Method Blank
Analyzed al IML Gilleue laboratory
Analyte detected below quanlitalion limils
Not Detected at the Reponing Limit
RPD outside accepted recovery limits
Matrix Effect
Sample Type MBLK
Date: 7/2/2018
Report ID: S 1805352001
Units: µCl/Sample
RunNo: 157872 PrepDate: 05/23/18 0:00 BatchlD 14635
Result RL Spike Rel Samp %REC % Rec Limits Qual
ND
Sample Type LCS
2E -07
Units: µCi/Sample
RunNo: 157872 PrepDate: 05/23/18 0:00 BatchlD 14635
Result RL Spike Rel Samp %REC % Rec Limits Qual
7E-06 2E-07 7E-06 99.1 67.1 -122
Sample Type MS Units: µCi/Sample
RunNo: 157872 PrepDate: 05/23/18 0:00 BatchlD 14635
Result RL Spike Rel Samp %REC % Rec Limits Qual
7E-06
Sample Type MBLK
2E-07 7E-06 D.0000002 94.1
Units: µCi/Sample
65 -131
RunNo: 158603 PrepDate: 06/12/18 0:00 BatchlD R158603
Result RL Spike Rel Samp %REC % Rec Limits Qual
ND 2E-07
Sample Type LCS Units: µCi/Sample
RunNo: 158603 PrepDate: 06/12/18 0:00 BatchlD Rl 58603
Result RL Spike Rel Samp %REC % Rec Limits Qual
9E-06
1 E-05
Sample Type MBLK
2E-07
2E-07
1E-05
1 E-05
Units: µCl/Sample
69.4
102
68 -146
50 -150
Run No: 158580 PrepDate: 06/22/18 0:00 BatchlD R158580
Result RL Spike Rel Samp %REC % Rec Limits Qual
ND
NO
ND
4E-07
4E-07
4E-07
Sample Type LCS Units: µCl/Sample
RunNo: 158580
Result
6E-06
5E-07
7E-06
PrepDate: 06/22/18 0:00
RL Spike Rel Samp
4E-07 8E-06
4E-07 4E-07
4E-07 8E-06
Batch ID Rl 58580
%REC % Rec Limits
85.1 50 -150
125 50 -150
93_7 50 -150
Sample Type LCSD Units: µCi/Sample
E
H
L
0
s
RunNo: 158580
Result
PrepDate: 06/22/18 0:00
7E-06
8E-06
RL
4E-07
4E-07
Value above quantitation range
Cone %RPO
6E-06 13.7
7E-06 4.22
Holding limes lor preparation or analysis exceeded
Analyzed by another laboratory
Outside the Range or Dilutions
Spike Recovery outside accepted recovery limits
Batch ID Rl 58580
%REC % RPO Limits
97.6 20
97.7 20
Page 2 of 3
Qual
Qual
/~I: Your Environmental Monitoring Partner
Inter-Mountain Labs-----------------------------------------
hntR-Mou,..,.,,H l4'0S
CLIENT:
Work Order:
Project:
1673 Terra Avenue. Sheridan, Wyoming 82801 ph: [phone]
ANAL VTICAL QC SUMMARY REPORT
Energy Fuels (White Mesa)
S1805352
South Yellow Cake Scrubber, Dryer
Date: 7/2/2018
ReportlD: S1805352001
Total (3050) Metals by EPA 200.8 · Soil
MBLK (06/11/18 12:42)
Units: mg/Kg
Analyte
Sample Type MBLK
RunNo: 157992
Result RL Spike Rel Samp %REC % Rec Limits Qual
Thorium
Total (3050) Metals by EPA 200.8 -Soil
LCS (05124118 20:35)
Analyte
Uranium
Total (3050) Metals by EPA 200.8 -Soil
S1805352-001AS (05124/18 21:09)
Analyte
Uranium
Total (3050) Metals by EPA 200.8 -Soil
Qualifiers:
S1805352-001AMSD (05/24/18 21:14)
Analyte
Uranium
B Analyte delected in the associated Melhod Blank
G Analyzed al !ML Gilleue laboratory
J Analyte detecled below quantitalion limits
ND Nol Detec1ed at !he Reporting Limit
R RPD oulside accepted recovery limils
X Malrix Errecl
ND
Sample Type LCS
RunNo: 157444
Result
94
Sample Type MS
RunNo:157444
Result
33700
Sample Type MSD
RunNo: 157444
Result
33700
45
RL
RL
RL
Units: µg/Sample
Spike Ref Samp
1E02
Units: µg/Sample
Spike Ref Samp
2E04 15000
Units: µg/Sample
Cone %RPO
33700 0.0750
E Vatue above quaniitation range
H Holding times ror preparation or analysis exceeded
L Analyzed by another laboratory
0 Outside !he Range of Dilulions
s Spike Recovery oulside accepted recovery limits
%REC % Rec Limits Qual
94.4 85 -115
%REC % Rec Limits Qual
92.8 70 -130
%REC % RPO Limits Qual
92.9 20
Page 3 of 3
APPENDIX D
South Yellow Cake Scrubber
Figure 1. 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 (~p readings on Field Sheet)
D
F,c;1;,y Energy Fuels
t
a
!
y
Stack Identification: South Yellow Cal<e Scrubber
l+--0 --.1
p
a: Distance upstream from next disturbance, feet 7' ----------
P: Distance downstream from last disturbance, feet 30'
y: Distance of Sample Level to Ground, feet 65' ---------
11__ 75' 0: Stack Inside Diameter, inches ________ _
Estimated Moisture, percent
Estimated Temperature, °F
Estimated Velocity, fpm
Control Unit
Type:
Scrubber
Number of Ports
4-8cYo
]00-120 ---------
2.000 ---------
2
Figure I. Facility Schematic Representation
Process
Type:
Yello\v Cake Prnc1.:ssing
Facilicy Energy Fuels
t
a
!
y
Stack Identification: yell ow Cake Dryer Baghouse
l+--0~1
~
a: Distance upstream from next disturbance, inches 57" ----------
~: Distance downstream from last disturbance, inches 454"
y: Distance of Sample Level to Ground, feet ---------65'
0: Stack Inside Diameter, inches 16" ----------
Estimated Moisture, percent 0-2%
Estimated Temperature, °F ---------l'.25
Estimated Velocity, fpm 1.400
Control Unit
Type:
Baghouse
Number of Ports 2
Figure 2. Facility Schematic Representation
Process
Type:
Yc>llow Cake Processing
Facility Energy Fuels
Location South Yellow cake
Date
South South
Demister Humidy Scrubber Scrubber
Run# Time Spray Spray Venturi Inlet Pressure
f 5:°.'CJO l q. .. y '-(.1(' 32 ·°] 'l . '7 , 1 C,-']O t '1-·'r <...l·Z-3 2. s-Z·i
t t,: oo t'f ·Y 4 ·"2-~ 2 ·4 2·~ .
lc,!JO [ 7.y <-l' L ) ~. ,: 2.y
l --(,:bl) I "1-·'t L\. -~ ?.; 7' 1.,,. i.1
I 1" ;3o ll,q ~-4 ,-,.1.--i,. '1
L ~ : [)V 1'-1"6 '-\ • '-7 .-;, 7. V' 'l. '1 ,
( <(. !$~ r1-c; ~--,r _.$ 5. V c.·~
I °I. :ov ( f'y Y·r .s, . L-'2 -~
~.·o v t 1-1 '-{. 1 > 1 · c,~ "3. 0
~: 30 , ,,~ t-t I '1 -~ I· v )' D .
~; 0 () I-+, 1-Y·4 5'. + '?'0
'i.'30 \1·1 \{ ·Y 1 I· '::J ,·C>
JO.' OD I 1·'{ '-{. ~ ~ r-3 5·6
I lo: ~ o ( 1 ·" ~-~1-. 'I· L/ ?·;
I I: DD \-1 · -1 q ·9 3, ! . 5 3. z. . . , , .. 30 ( f. 't l\. ~ } I -& 3. 1..
\ -1 ll, oO 11u ~ ·"1 s l• ~ )·)
12: 30 It· Y 4~ ~ /. }-~-./ r,. OD l +-,C) '-(. 7 32... z._ 5. c./
Facility Energy Fuels
Location South 'fellow cr,e
Date 2 _,~,/t _x;::
South South
Demister Humidy Scrubber Scrubber
Run# Time Spray Spray Venturi Inlet Pressure
,z._,..-I ~:30 I q.'1 4.i5-'-3(. f )·/
t '{ .' 06 I 9-. '1 ~-~ '31. f 1 . '
lv/;30 I ·1-, 7 '-I ·1 31· j ~-7
, s-' "() I 1' ·°7 ,_/. T' ~ {. i ~-I
I"'. :]O /r·~ ·1-1 l-} ~. (
/' : OD I J,y 1.-{. y > l . --+ 1 . "L.
l 1/ ({, ~ 'SO / 'f--~ '-{ ·f '3 Ly 3. 'L
I:,: D 0 I ~-5 y.4 31 .; ). I
i".t/ '.3D l 1-· '1' ... \.~ -s \ ·9 ~-(
-:,.:so I +-i i.-l ·r 3 z.._.o ~. f
t:o G> { ·+-~ l{ ·y ~ ( · 1 's ,1
~·.:su I -~-y L{. i ~(. °l ,./
~:oo ( }·){ ~·1 32 .r s.\
91.JV tr·"' <-l ·Y ~l ·( -; . I
\0 : 00 t 1-• i "f ·4 ,1-<o ~. l
10;,o { ~ . () 4·y ~z....D 5· 1
tl;()D {~·(.) ~·°) ,-z·t) s·'
l\, .3 0 ,-1 + . q. c., ~ ,. "l 1 -I
'V ,-i.oo ( -.; . ~ L( ·'1 s. S"' :s . I
APPENDIX E
Calibration of the console dry gas meter(s), pi tot tubes, nozzles diameters, and temperature
sensors were carried out in accordance with the procedures outlined in the Quality Assurance
Handbook. The appropriate calibration data are presented in the following pages. The nozzle
calibrations are recorded on the first page of the field data sheets.
Figure 3 Schematic of Method 5/114 Sampling Train
Meter Box Calibration Data and Calculations Forms
Post-test Dry Gas Meter Calibration Data Forms
Type S Pitot Tube Inspection Data
Sample Box Temperature Sensor Calibration
E
Temperature Sensor
i
~Probe
Type S Pitot
Tube
Te~~~~~tlre
Nozzle t-atTraced
Gooseneck j
~ l3a&a-lired
/ Pn:ibe ---
/
Type S Pitot
Tube -0
Temperature
Sensor
Glass Filter
Holder
Heated Area
ln,:iinger Train Qxional, May Be Replaced
S,, kl Equivalent Conasnser
l Temperature
Sensor
,--------------
lmpingers
Stack
Wall Manometer Temperature Water
Sensors. Empty Silica
Gel
Orifice
Dry Gas
Meter
By-pass
Valve
Air-Tight
Pump
Figure 3 Schematic of Method 5/114 Sampling Train
METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES
1) Select lhree critical orifices to calibrate the dry gas meter which bracket lhe expected operating range.
2) Record barometric pressure before and after calibration procedure.
•a-·-t~! t
3) Run at lested vacuum (from Orifice Calibralion Report), for a period of lime
necessary to achieve a minimum total volume of 5 cubic feet.
4) Record data and information in the GREEN cells. YELLOW ceHs are calculated
TECHNICIAN: D. Olsen
DATE: 1217117 METER SERIAL#: 68092
METER PART#: Console S CRJTICAL ORIFICE SET SERIAL-, 1453S
INITIAL
BAROMETRIC PRESSURE In H : 25.80
eou1PMENT 1D•: Console #5
TEMPERATURES 'F K' I TESTED
FACTOR VACUUM
ORIFICE# l RUN# I (AVG) (In Hg)
DGM READINGS (FT>)
INITIAL I FINAL I NET (V ml
AMBIENT I DGM INLET I DGM OUTLET I DGM
INITIAL FINAL INITIAL FINAL AVG
G
G
G
2
3
2
3
0.B137
0.8137
0.8137
0.5317
0.5317
0,5317
0.3307
0.3307
0.3307
13 788.709
13 794.175
13 801.826
13 753.316
13 768.845
13 764.369
14 770.202
14 775.678
14 782.264
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
794.175
801.B26
808.397
758.846
764.369
769.926
775.678
782,264
788.416
5.466
7.651
6.571
5.529
5.624
6.657
5.476
6.686
6.152
60 78 78
60 78 79
60 79 82
62 62 65
62 65 66
62 66 66
62 67 69
62 67 71
62 71 74
78
81
88
62
69
74
69
69
74
81
88
90
62
70
68
69
74
77
78.8
81.5
84.8
62.8
67.5
68.5
68.5
70.3
74.0
FINAL
26.BO
ELAPSED
TIME(MIN)
0
§ 0
0
§ 00
0
12.50
15.00
14.00
AVG (P • .,)
25.80
2.90
2.90
2.90
1.10
1.10
1.10
0.41
0.41
0.41
(1)
V.,(STD)
~
6.4873
~
4,8316
4.7837
~
4.7239
6.66Z7
5.2623
2018 Pre-Calibration
IF YVARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE REC A LIBRA TED
(2)
V.,(STD)
4.6045
6.4463
6.6254
AVG=
4.8047
4.8047
~
AVG=
4.6694
5.6032
5.2297
AVG=
(3)
y
0.988
0.994
0.998
0.993
~
~
1.000
1.000
0.988
0.990
~
0.991
1
y
VARIATION(%)
-0.15
0.50
::Q.lli
The lollowing equations are used lo calculate lhe standard volumes of air passed through the DGM, Vm (std), and lhe crijical onfice, V 0
(sld), and the DGM calibration faclor. Y These equations are automatically calculaled in the spreadsheel above AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 0.995
(1)
(2)
(3)
~·m,.,,, = K' • Vm ~ f'ba,· + (t.11 ii 3.6)
Tm
Phar • 0 / -K'• I er, . ..,, -../Tamb
= Net volume of gas sample passed through DGM. corrected to standard conditions
K, = 17.64 "R/in. Hg (English). 0.3858 "Kimm Hg (Metric)
T., = Absolule DGM avg temperature ("R -English, "K -Metric)
= Volume of gas sample passed through the crrtical orifice. corrected to standard conditions
T..,.. = Absolule ambienl tempera1ure ("R -English, "K • Metric)
K' = Average K' factor from Crilical Orifice Calibrabon
f-'cr. ff./) Y= --
Vm,,,J1
= DGM calibration factor
AVERAGE 6H@=I 1.513
:,.H@ = ( 0.75 0 )2 llH (Vm(std))
V~(sld) Vm
TEMPERATURE SENSORS 'F
REFERENCE IN OUT
32 33 32
72 73 73
201 201 201
1.639
!,ill
.Lill
1.499
1.485
1.483
i,m.
1,lli
1ill
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 alter ca~bration procedure.
,a-·-"! UI '-'":,.'"
~-~: ~:--:.
3) Run at tested vacuum (from Orifice Caibration Report). for a periOd of time
necessary to achieve a minimum total vok.Jme of 5 cubic feel.
4) Record data and information in the GREEN cells. YELLOW ceDs are calculated.
TECHNICIAN: M. McN•mara t----~------'
DATE: 12/1412016 METER SERIAL#: 28152
METER PART#: Console 9 CRITICAL ORIFICE SET SERIAL#: 14535
K' I TESTED
FACTOR VACUUM
ORIFICE# I RUN# I (AVG) (In Hg)
G
G:
2
3
G:
0.8137
0.8137
0.8137
0.5317
0.5317
0.5317
0.3307
0.3307
0.3307
13
13
13
13
13
13
13
13
13
DGM READINGS (Fr
INITIAL
617.923
623.888
629.877
595.618
602.474
611.022
579.000
584.171
589.565
FINAL
623.888
629.877
635.870
602.474
611.022
616.493
584.171
689.565
594.940
NET (Vm)
5.965
5.989
5.993
6.856
8.548
5.471
5.171
5.394
5.375
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
INITIAL
BAROMETRIC PRESSURE In H : 24.95
Eau1PMENT 1D ., Console #9
TEMPERATURES °F
AMBIENT I DGM INLET I DGM OUTLET I DGM
INITlAl FINAL I INITIAi. ANAi. AVG
65 74 75
66 75 75
66 75 75
68 71 72
73 72 75
72 75 75
64 66 70
66 70 72
68 72 71
71
71
72
69
69
70
65
69
68
71
72
80
69
70
71
69
68
69
72.8
73.3
75.5
70.3
71.5
72.8
67.5
69.8
70.0
FINAL
~
-i ELAPSED
TIME(MIN)
9 --
5.50
5.50
5.50
8.00
12.00
12.50
AVG (Pb.,)
24.95
3.00
3.00
1.20
0.45
0.45
(1)
Vm(STD)
~
4.9896
4.9720
5.7141
7.1075
4,5384
4.3227
!:!ill
~
2018 Pre-Calibration
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V"(STD)
4.8747
ml!!!
!!rm!
AVG=
5.7749
7,1847
4.6025
AVG=
4.3266
~
4.4898
AVG=
(3)
y
~
0.976
0.980
0.979
.1,211
1Jill
Lill
.1.ill
1,QQ.1
1.ill
~
1,ill
l
y
V .ARIA TION (%)
::1.!1
1.44
0.47
The following equations are used to calculate the standard v°"mes ol air passed through lhe DGM. V. (std). aod lhe critical orifice.
V0 (std). and the DGM calibration factor. Y These equations are automatically calculated in the spreadsheet above. AVERAGE ORY GAS METER CALIBRATION FACTOR, Y = I 0.998
(1)
(2)
(3)
Vm,.,.,, = K, • Vm • Pb,;,r +(All / 13.6)
Tm
= Net volume of gas sample passed through DGM, corrected lo standard conditions
K, = 17.64 "R/in. Hg (English). 0.3858 "Kimm Hg (Metric)
Tm = Absolute DGM avg. temperature (0R -English. "K -Metric)
Pbar • 0 / -IC'• 1 er,:,.,' -.,,'T<1mb
l'cr,,HI, y ~ __ . v,,.,,,,..1
= Voome of gas sample passed through the critical orifice, corrected to standard condrtions
r .... = Absolute ambient temperature ("R -English, "K -Metric)
K' = Average K' fac1orfrom Critical Orifice Calibration
= DGM calibration factor
AVERAGE 6H@ =1 1.704
6H@=
(
0.75 8 )2 £'.H (Vm(sld))
V,,(sld) Vm
TEMPERATURE SENSORS 0f
REFERENCE IN OUT
32 33 32
64 65 65
203 203 202
1.791
.till
.u!2
.till
.1.ill
~
Lill
!,gr
.1..lli
,_ p!:,. METHOD 5 DRY GAS METER CALIBRATION USING CRITICAL ORIFICES .----~ lu,d,11 \. r, I\ l Ud·•• ~il,o I[-
«;~ 7.Jl
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: Reed Kitchen
DATE: 5/21/18 METER SERIAL#: 26144
METER PART#: Console 5 :RITICAL ORIFICE SET SERIAL#: 1453S
K' TESTED
~~~~~~----, FACTOR I VACUUM DGM READINGS (FT')
ORIFICE# I RUN# I (AVG) (in Hg) INITIAL FINAL
0.5317 12.5
0_5317 12.5
0.5317 12.5
398.956 403.968
403.968 409_018
409.018 414_117 G: o:rn± o:rn±
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
NET(Vml
5.012
5.050
5.099
INITIAL
BAROMETRIC PRESSURE (in H : 25.32
Eou1PMENT 1D ., Console #5
TEMPERATURES °F
AMBIENT I DGM INLET I DGM OUTLET I DGM
1NITrAL FINAL J INITIAL FINAL AVG
79 74 83 71 74 75.5
79 78 84 74 76 78.0
79 72 86 76 79 78.3
I I I I I I
I I I I I I
FINAL
25_32
ELAPSED
TIME(MIN)
0
7.287
7.313
7.357
AVG (P • .,)
25.32
DGM 1!.H
(in H,O)
1_02
1.02
1.02
§§
§§
(1)
Vm (STD)
4.1952
~
~
Post Calibration
Energy Fuels
IF Y VARIATION EXCEEDS 2_00%,
ORIFICE SHOULD BE RECALIBRATED
(2)
V0 (STDI
4.2268
4.2419
~
AVG=
AVG=
AVG=
(3)
y
1.008
1.008
1.005
1.007
l
y
VARIATION(%)
.!!,QQ
The following equations are used lo calculate lhe standard volumes of air passed through the DGM, Vm (sld), and lhe critical orifice,
V • (std). and the DGM calibration factor, Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 1.007
(1)
(2)
(3)
Vmr,.-<1) = K, •V,11 .. Pbar+ (Alf ; 13,6)
'/'111
= Net volume of gas sample passed through DGM, corrected to standard conditions
K, = 17 64 'Rtrn. Hg (English), 0,3858 'Kimm Hg (Metric)
Tm = Absolute DGM avg temperature ('R -English, °K -Metric)
Va·,,.;, "-K'• Phor • 0 JTm11b = 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 Calibratron
Vai,,.J y = -----= DGM calibration factor ,,,,,.,,,,')
AVERAGE t.H~ =I 1.423 !
6H"'=
(
0.75 8 )2 6H (Vrn(std)\
V"(std) Vm /
TEMPERATURE SENSORS °F
REFERENCE IN OUT
1.427
1.421
1.420
METHOD 5 ORY GAS METER CALIBRATION USING CRITICAL ORIFICES '.#M&IPN:'&N01fi
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 feel
4) Record data and information in the GREEN cells, YELLOW eels are calculated.
TECHNICIAN: R~ed Kite hen .----,------
DATE: 512V18
METER PART#: Console 9
METER SERIAL#: 28152
CRITICAL ORIFICE SET SERIAL#: 1453S
K' TESTED
~---~----, FACTORIVACUUM DGM READINGS (FD_
ORIFICE # I RUN # I (AVG) (In Hg) INITIAL FINAL
0.6808 11.9
0.6808 11.9
0.6808 11.9
744.004 749.065
749.065 754.091
754.091 759.157 G:
D:ffi§
D:ffi§
USING THE CRITICAL ORIFICES AS CALIBRATION STANDARDS:
NET (Vm)
5.061
5.026
5.066
_ INITIAL
BAROMETRIC PRESSURE (in H j; 25,31
Eou1PMENT 1D ., Console #9
TEMPERATURES "F
AMBIENT I DGM INLET I DGM OUTLET J DGM
INITIAL FINAL I INITIAL FINAL AVG
65 69 72 68 68 69.3
67 70 75 68 68 70.3
68 71 77 68 69 71.3
I I I I I I
I I I I I I
FINAL AVG(P .. ,)
~ 25.31
ELAPSED
TIME{MINI DGM l!.H
0 (in H20)
5.66 2.03
5.61 2.03
5.65 2.03
§§
§§
(1)
V.,(STO)
4.2971
~
4.2851
Post Calibration
IF Y VARIATION EXCEEDS 2.00%,
ORIFICE SHOULD BE RECALIBRATED
l
(2) (3) I VARIA:ON('/,) Vor(STD) y
4.2562 !illQ
~ 0.988
4.2403 0.990
AVG= 0.989 0.00
AVG=
AVG;
The following equations are used lo calculate the standard volumes of air passed through lhe DGM, Vm (std). and the critical orifice, v. {std). and Ille DGM calibration factor. Y. These equations are automatically calculated in the spreadsheet above. AVERAGE DRY GAS METER CALIBRATION FACTOR, Y = I 0.989
(1)
(2)
(3)
v,,,r,·d) = K, •Vm • Pbar •·(llH /13.6) Tm
= Net volume of gas sample passed through DGM. corrected to standard conditions
K, = 17 .64 'Rlin Hg (English). 0.3858 'Kimm Hg (Metric)
T .. = Absolute DGM avg temperature (0R -English, 'K • Metric)
Vffud :: K .. Pba,· • 0
' ./Tmnb = Volume of gas sample passed through the critical orifice. corrected to standard conditions
T,., = Absolute ambienl 1emperature ('R -English. 'K -Metric)
K' = Average K' factor from Critical Orifice Calibration
= DGM calibration factor Ve,-,,.,) Y--~----
--V'!ll(Hi)
AVERAGE 6H@ =I 1.716 l
6H-=
(
0.75 0 )
2
6H (V00(std))
v.,(std) v ..
TEMPERATURE SENSORS 'F
REFERENCE IN OUT
1.713
1.717
1.717
Type S Pilot Tube Inspection Data
Date: __ 1_2/_1_1'----/2_0_1.c.7 __ Pilot Tube Identification: _____ ..:.l--=-8---=G=------
Technician: M McNamara
t PA
Ps D,= 0.375 ,n, Is PA=Pe? Yes
Is I 05 • D, :, p A & p" :, I 50 • D, 0 Yes
PA~ 0 453 in.
Pn = 0 453 In.
a,< 10° 01= 2
O.i < 100 a,= 2 0
Pr< 5°
Z:, 0.125 in. Z = O.oJ I in. ------
W :.003125 in W = 0.027 m ------
W > 3 inches w = ___ s'-----__ in
Z > 314 inch Z = 1.5 in. ------
~ rx '"' ·-·.:-·-~ -:·-3]----------
0
Y 2'. 3 inches Y = _ ___;;J_l_l_2 __ in
The pilot tube meets the specifications for a calibration factor ofO 84? Yes
Tempera!Ure Sensor Calibration
Reference· Omega CLJ5 I 2A
Continuity Check Yes Probe Heat Check 248 Yes
I emperature temperature t cmperature
Source K.elerence Sensor Difference
(Medium) ("F) ("F) ("F)
Probe AIR 64 64 0
AIR 64 64 0
ICE WATER 35 35 0 Stack
BOIL WATER 204 204 0
SILICONE OIL
Type S Pi101 Tube Inspection Data
Dale: 12/11/2017 Pi101 Tube lden1ifica1ion: 27 G-2 -------------------
Technician: M McNamara ------------------
t PA
Pa D = I 0 375 m Is PA=P0 9 Yes ---------Is 1.05 • D, $ PA & P11 :S 1.50 • D, 9 ____ Y_e_s ___ _
PA= 0 469 in
,?8"' 0.469 in
~'· Jl, < 50 Jl, "' ___ o ___ a
~P,
Zs O 125 in. Z = 0.006 in. ------
y W :SO 03125 in. W = 0.001 in. ------
W > 3 inches W= 5 in. ------
Z > 3/4 inch Z = ___ 0_8_75 __ m
~n ,, ... ,,. ..... 0
~ ·+·:tJ-·--· ------Y ~ 3 inches Y = 3 3/4 in. ------
The pi101 tube meets lhe specifica1ions for a calibration factor of0.849 Yes
Temperature Sensor Calibration
Reference· Omega Cl 3512A -
Continuity Check Yes Probe Heat Check 248 Yes
I empera1ure I cmpcraturc I emperature
Source l{elerence Sensor Difference
(Medium) ("F) ("F) (OF)
Probe AIR 64 66 2
AIR 64 65 I
Slack ICE WATER 34 33 I
BOIL WATER 204 203 I
SILICONE OIL
TETCO
Sample Box Temperature Sensor Calibration
Date: 2/20/18 Calibrator: Alex Moore Reference: Ome!!:a CL35 I 2A
Thermocouple Temperature Temperature Temperature
Unit ID Location Source Reference Sensor Difference
(Medium) (°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 34 ~ Oven (4) Water 204 204
Oven (3) Water 33 34
E Water 204 205
Water 33 34 I Oven (4) Water 204 205 I
F Oven Water 33 33 0
Water 204 205 I
G Oven Water 33 34 I
Water 204 204 0
H Oven Water 33 32 -I
Water 204 205 I
--Water 33 32 -I
' lmpinger Oul A Water 204 204 0
-· lmpinger Out B Water 33 33 0
Water 204 205 I . Water 33 33 0 lmpinger Out C Water 204 204 0 ;•;:, lmpinger Out D Water 33 33 0
Water 204 203 -1
~;;, lmpinger Out E Water 33 33 0
Water 204 202 -2
'(/,~
lmpinger OUl F Water 33 33 0 ~ Water 204 203 -I
lmpinger Out G Water 33 33 0
' Waler 204 202 -2
1\ lmpinger Oul H Water 33 33 0
Water 2Qtl 203 -I
lmpinger Out I Water 33 33 0
Water 204 202 -2
r~~ lmpinger Out J Waler 33 33 0
Water 204 202 -2
~-..... L.--· lmpinger Out K Water 33 33 0
' .. '!--=-~Jf. Water 204 203 -I
APPENDIX F
The testing followed the same procedures as outlined in previous protocols and tests at this
facility.
ATTACHMENT H
SURFACE WATER GRAPHS AND FIELD DATA SHEETS
U)
C 0 +:i C'IS ... -C
Cl) u
C
0 (.)
Cl)
"'C
u ::::s
C 0
"'C -C'IS-a: .e
"'C 0
Cl) ::::s .?-
0 U)
U)
C
~
Cl)
Cl) ...
(.)
"'C 0 0
== C
0 ~
(.)
~
•
l!) 0 I
UJ 0 ~
T"""
•
... l<J
•
~
CD I"-0 0 I UJ UJ 0 0 ~ ~
T""" T"""
• ..
... • •
14 • •
~ 14
~'
I
Ill
10
•• •
• I
• ...
4
~
••
• I •
~
~ ~
~ •
10
4
! I
0 • 4 ' 0
4 II 4 •• •
CX) 0)
0 0 UJ I UJ 0 0 ~ ~
(a1e:>"'§ 601) T"""
u
• • • II
II II ... II
~
•• ... u •• II
••
11
6'a v<=%,
~
<O •• C\J C\J
·• 11
•• , I
ct!
cla a: Ve ..
~ 0 ~ C') L C;I u ..c:: I-•
II cii ·• •• ••
••
z
c9~ ::)
c5'L • ~
•Ill I I
• I
·• •• • ·•
·• i I
I
••
•• 111 • I
I I I I I I ••• I I ·• II •
i
0 T"""
T""" T"""
I I UJ UJ 0 0 ~ ~
T""" T"""
1.00E~06
1.00E-07
1.00E-08
-.!! cu u cn1 .OOE-09
C)
0 ....I -
1.00E-10
1.00E-11
1.00E-12
fb<o
":,.'OJ ~"'
..... •
. = -----~ .
~ ..__OJ ~ ~
Cottonwood Creek Suspended Radionuclide Concentrations (uCi/ml)
•
.
-... • --& ••
---...
" • .... -.... ... .. i .. ~ .. .. • &
. . .... . -. ... -= .----~ --. . ... ---------------------~ ---------------&
---
I
BC) B°-' B<o B<o ~' ~ ~'o ~O;, ~ .... ~ OJ ~,OJ <,}'OJ ~,OJ ~ r65 ~ ~
~t,;;. ~'{C r}'v ~'v
rc}'V n}~ .... ~t,;;. ~,r:::s rc}'o n}~ ~ci; q}'V ~t,;;.
'
I • U-Nat. • Th-230 • Ra-226 I
...
-... -
.. • -• ... --... -
& ---
-
,<o ,(\ ~~ ~ ~ n}'v ~'v ~'v ~' .... ~ '6-
1.000E+OO
1.000E-01
1.000E-02
1.000E-03
1.000E-04
1.000E-05 -Cl)
ffOOOE-06
Cl)
Cl
jOOOE-07 -
1.000E-08
1.000E-09
1.000E-10 I ! •
1.000E-11
1.000E-12
1.000E-13
~O;, RS rd-re '\~
Westwater Creek Dissolved Radionuclide Concentrations
(uCi/ml)
-a -
"(::) ~ ,..._<o
""
~"'\,
~~re
~"":, ~re ~"
• U-Nat. •Th-230 • Ra-226 ]
....
~
..._~
~ 1 ..._'1)
~
..._ro ~ <d-"<:.::,
-Cl)
0.1
0.01
0.001
0.0001
0.00001
j.000001
Cl)
<ffi)ooooo1
..J -1 E-08
1 E-09
1 E-10
1 E-11
1 E-12
1 E-13
I
~O:,
/\.~
i
Westwater Creek Suspended Radionuclide Concentrations (uCi/ml)
~"<::)
\"~ ""
I
\"'l, ~" ~"":)
'8-"t;.
•
• U-Nat • Th 230 • Ra-226 I
!
....
'"l). 1 "'V
I
•
~,r:o
~..._<::s
,P·
(
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)~nwood Cr~ Westwater Canyon Other (describe) ____ _
DATE: __ •~'~•~& ............ ____ _
pH BUFFER 7.0 __ 7___.,_. ~0~-
SPECIFIC CONDUCTIVITY 1000
,.., \ \ STEAM DEPTH: ·&-
pH of WATER ___ 7-'--~ o___;;,_3 _____ _
COND umhos 1·2-Zi
pH Units 7. o '-\
Temp°C ~. zl;.
COND µmhos I '2Y7
pH units 7~oz.
Temp °C S~1':i
Comments:
BY: G:f?
(Sampler's initials)
pH BUFFER 4.0 _ __.Y~Q_,__ __ _
µMHOs
TEMP _~S~,~16,__ __
CONDµmhos I 2.S3
pH units '7.01
Temp°C S.to
COND µmhos 12:io
pH units 7.03
Temp°C S. 16
r ·
(:
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 M estwater CanY<m):}ther (describe) ____ _
BY: _ _..6:""-'-"-'-p_,_,___ ___ _
(Sampler's initials)
pH BUFFER 7.0 __ 7L...:_c.....;IJ,cc_ __
SPECIFIC CONDUCTIVITY _ __._( 0=--=0--=() ____ ..c;;µ=MH=O=s
STEAM DEPTH:
pH of WATER ___________ _ TEMP ______ _
COND =µmh===os:a.,._ ____ _ COND µmh==os~----
pH Units ______ _ pH units ______ _
Temp °C -------Temp°C ______ _
CONDµ_=rnh==-o~s ____ _ CONDµ=mh==-o~s ____ _
pH units -------pH units ______ _
Temp °C ______ _ Temp°C ~------
Comments:
3 /7,1 /1 i: -Acc-,'v ,tl cu,. s:-t. ed: 1:217 C-c« IL ...,.,e,..1 ~~i . .S'c-c. pka f.C>
3/-z,7/1i -t.... i-
1~
-CHAIN OF CUSTODY RECORD -f .· Page l of \ Inter-Mountain Labs All shaded fields must be completed. Sheridan, WV and Gillette, WY # 17206 9 IH'rl!R-MOUHTAIH LABS This is a legal document: any misrepresentation may be construed as fraud.
Client Name Project Identification Sampler (Slgnature/~estat~lhentlcity) Telephone#
~ ""'-,.r-av ~,,, ls --I st-~ .1J t...r.\-c.-r s.. fi..C...C.c... w.-.tcr I ---'135 671 411.S: ---~ ..,,.., .... . _ _. -
Report Address -' Contact Name ANALYSES/PARAMETERS
Z.2$ "'""'"~ a'"'°"" I $ ,J rte.. 60() 140..~V w c.-~ ""'-C.-l -
L. 0.. ""1,,JOc,(k l C,() 802-2-f Email 11,,_.,.,.: .... .J lfi>_ ,.~.-~.c:.v~, •• tc •. c:.o.~ ., .
Invoice Address Phone _3c,3~ 3st(} 'f 1~1.f -• I Purchase Order # Quote # -e ~ -----,,6_0 REMARKS
:E LABID DATE I TIME SAMPLE # of w
!:: (Lab Use Only) SAMPLED IDENTIFICATION Matrix Containers
_"5 LS>6~:~,\ 3/27/Jg Di"U />..~A -~ol C..r~ w·T l X X .A10 .... ~1 {f~r c..lA._
Aloi\,. or-~s~vc.cl
'
.. ,
I
' .
: .
,
.. '
IIIIIJ1.1:••lm11, 11-. -. -·•= ... -. -•, .... . ---. : ... ., ... -.. , .. ""'i .,~.
I 9°0
,, /-.-.I~~ :P..b . ./ !':.---'.& ~/lo.,~ .,,_,_, .~ ~ Pr!J~,,,-() ~oPt/li< /~tD7\ ...... , r• ,, ~ ........ ~ l --5·
' •• 1 . -
I ---
-II i~:.J.J~1~(•131~1:lll:t1•,r~,11JIJHII r•1•:t:::i,,m.-1·,-1;;ll".l".11~1-j~J:ll 11,1,L'l•~•ta •••J• 1111 :I~ J•1 :lll I I ~II••
UPS Water INT Check desi__Iid.s«vice Compliance Monitoring? N
:J Fed Express Soil SL "'Standard turnaround Program (SOWA, NPDES, ... ) '-"'
CJ US Mail Solid SD a RUSH -5 Working Days PWSID / Permit #
g 1 URGENT -< 2 Working Days -0 Hand Carried Filter FT Chlorinated? Y/NJ
:J Other Other OT Rush & Urgent Surcharges will be applied Sample DisposaJr(a!) Client
Inter-Mountain Labs. Inc. www.1ntermountainlabs.com Rev4.6
,...~I: Your Environmental Monitoring Partner
-Inter-Mountain Labs ---------------------------------
,N,•R-MouNT.o.tN LAH 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
CLIENT:
Project:
Lab Order:
Energy Fuels {White Mesa)
1st Quarter Surface Water '18
S1803357
Sample Cottonwood Creek was received on March 29, 2018.
Date: 4/6/2018
CASE NARRATIVE
Report ID: S1803357001
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
...... ~... Your Environmental Monitoring Partner :.tm:C Inter-Mountain Labs---------------------------------------
oHroR-MouHT,.,H .,.as 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
Sample Analysis Report
CLIENT: Energy Fuels (White Mesa)
6425 S. Highway 191
Blanding, UT 84511
Project:
Lab ID:
1st Quarter Surface Water '18
S1803357-001
Client Sample ID: Cottonwood Creek
Analyses
General Parameters
Total Dissolved Solids (180)
Total Suspended Solids
Result
790
11
RL Qual
10
5
Date Reported: 4/6/2018
Report ID: S1803357001
Work Order: S1803357
Collection Date: 3/27/2018 8:20:00 AM
Date Received: 3/29/2018 12:00:00 PM
Sampler: GP
Units
mg/L
mg/L
Matrix: Water
COC: 172069
Date Analyzed/lnit
03/29/2018 1459 NLG
03/29/2018 1525 NLG
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 quanlitation 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 U Analysis reported under the reporting limit
X Matrix Effect
M_, /1 .-4" <"
Reviewed by: ~ '-------------Wade Nieuwsma, Assistant Laboratory Manager Page 1 of 1
"'l~m-·'"" L Inter-Mountain Labs----------------------------------------
Your Environmental Monitoring Partner
1HT1A-MouHTA1H LA8S 1673 Terra Avenue, Sheridan, Wyoming 82801 ph: [phone]
ANALYTICAL QC SUMMARY REPORT
CLIENT: Energy Fuels (White Mesa) Date: 4/6/2018
Work Order: S1803357 Report ID: S1803357001
Project: 1st Quarter Surface Water '18
Solids By SM 2540 Sample Type MBLK Units: mg/L
DI 1 (03/29/1815:12) RunNo: 155765
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Suspended Solids ND 5
DI (03/29/18 14:33) RunNo: 155865
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
CONTROL (03/29/18 15: 13) RunNo: 155765
Analyte Result RL Spike Ref Samp %REC % Rec Limits Qual
Total Suspended Solids 96 5 100 96.0 80 -110
CONTROL (03/29/18 14:34) RunNo: 155865
Analyte Result RL Spike RefSamp %REC % Rec Limits Qual
Total Dissolved Solids (180) 220 10 226 99.1 80 -110
Solids By SM 2540 Sample Type LCSD Units: mg/L
CONTROL DUP (03/29/18 15:14) RunNo: 155765
Analyte Result RL Cone %RPO %REC % RPD Limits Qual
Total Suspended Solids 96 5 96 0 20
Solids By SM 2540 Sample Type DUP Units: mg/L
S1803355-002B (03/29/18 14:45) RunNo: 155865
Analyte Result RL Ref Samp %RPO %REC % RPD Limits Qual
Total Dissolved Solids (180) 230 10 220 2.67 20
S 1803355-012B (03/29/18 14:56) RunNo: 155865
Analyte Result RL Ref Samp %RPO %REC % RPD Limits Qual
Total Dissolved Solids (180) 200 10 210 1.96 20
Qualifiers: B Analyte detected in the associated Method Blank E Value above quantitation range
G Analyzed at IML Gillette laboratory H Holding times for preparation or analysis exceeded
J Analyte detected below quantitation limits L Analyzed by another laboratory
ND Not Detected at the Reporting Limit 0 Outside the Range of Dilutions
R RPD outside accepted recovery limits s Spike Recovery outside accepted recovery limits
X Matrix Effect
Page 1 of 1
(
White Mesa Mill-Standard Operating Procedures
Book# 11: Environmental Protection Manual, Section 2. l
Date: 04/14 Revision: EFR-3
Page 5 ofS
Attachment A
FIELD WATER ANALYSIS SURF ACE WATER
WHITE MESA MILL
LOCATION (Circle one):Cottonwood Creek Gtwater canyog))ther (describe) ____ _
DATE: 6 I 1.1 " t
pH BUFFER 7.0 _____ _
BY: G-P
(Sampler's initials)
pH BUFFER 4.0 _____ _
SPECIFIC CONDUCTIVITY ________ """'µMH=~O-s
STEAM DEPTH:
pH of WATER __________ _ TEMP ~------
COND µmhos CONDµmhos
pH Units pH units
Temp°C Temp°C
COND µmhos COND µmhos
pH units pH units
Temp°C Temp°C
Comments:
' I
1 •
...
,,
l .• '.
~ (1.) (1.) 1--< u
1--< (1.) .... (I) ~ .... VJ (1.) ~
00 ....... -.... .......
N -.... \0
.,. ,, , ...
., .~ .•
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)~onwood CreB) Westwater Canyon Other (describe) ____ _
DATE:_-.s _._/ za=.;2=4/ ........ 1 ....... s: __ _ BY: _ __,_G~P _____ _
(Sampler's initials)
pH BUFFER 7.0 __ F----=--::;-__..0""'----
SPECIFIC CONDUCTIVITY _----Ll .,.,Ot..llQ~D------µ=MH=O=s
STEAM DEPTH: AIA
pH of WATER __________ _
COND =µmh=-===os=--------
pH Units ______ _
Temp °C ______ _
CONDµ=mh==-o~s ____ _
pH units ______ _
Temp °C ______ _
Comments:
TEMP ______ _
CONDµ=mh==os:;__ ___ _
pH units ______ _
Temp°C ______ _
CONDµ=mh~os"-------
pH units -------
Temp 0C ______ _
ATTACHMENT I
SOIL SAMPLE GRAPHS, DATA TABLE, LABORATORY RESULTS AND QA/QC
Soil samples are collected during the third quarter. This attachment has been
deliberately left blank.
ATTACHMENT J
RADON MONITORING GRAPHS AND DATA
pCi\L
0 0 0 0 0 0 0 0
0 ...... i\:i u.) ~ 01 0) " CX>
1/2/2013
+ 3/29/2013
OJ I 7/1/201 < I u.) -CT 10/1/2013 ll)
(")
" cc 12/24/2013 ...... 0
C
:::::i a. 4/2/2014 -
6/27/2014
+ 9/30/2014
OJ 1/7/2015 CD I < :::c: I ...... ~ :;E 4/2/2015
;:;: ...... :::r
OJ 6/29/2015 :::r:, ll)
(")
" D> cc 9/28/2015 ...... c.. 0 C 0 :::::i a. 1/4/201 ::, (/)
C I
CT I\) ..+ ...... 4/4/201 I\) ll) (") I\) ..+ (I) a. 7/5/2016
10/10/2016
+ 1/5/2017
OJ
I 3/29/2017 < I ......
() 7/5/2017
ll)
(")
C 9/29/2017 ~ (I) a.
m 1/2/2018
() r
4/2/2018
7/5/2018
~Oc/9/L
~Oc/c/v
....J CJ
~0G/6c/6 w
"O Q) -(\1
:::J (.)
(\1
L~OG/6G/£ CJ
C\J I > ::r: L~OG/9/~ cc
~OG/0 ~/0 ~ +
~OG/9/L
C\I
C\I "O Q)
C\I -(.)
I ~
C: -~OG/PH .0
0 :::J
Cf)
"C "O
9 ~0G/8G/6 C: ca :::J
~ 0 ,._
C)
9~0G/6G/9 ~
C\I (.)
(\1 > cc
~OG/G/17 ..c: -J: ~ m ~Oc/LH C\I I > ::r: cc
v~Oc/0£/6 + ~OG/Lc/9
~OG/G/17 -"O C:
~OG/VG/G ~ :::J e
C)
~
~OGH/0~ (.)
(\1 e
~OGH/L ('I)
I > ::r: cc
~0G/6c/£
+ ~OG/G/~
co I"-<O LO s::t ('I) C\J T""" 0
c:i c:i 0 c:i c:i 0 c:i c:i
1\!~d
pCi\L
0 0 0 0 0 0 0 0
0 ..... i\, w +:>, 01 0) ....... CX>
1/2/2013
3/29/2013
7/1/2013
10/1/2013
12/24/2013
4/2/2014
6/27/2014
9/30/2014
1/7/2015 . ~ a,
+
4/2/2015 ::c:
~
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:r < :D I 9/28/2015 (.,.) m C.
1/4/2016 I I ... I I I I I I 0 :,
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10/10/2016
1/5/2017
3/29/2017
7/5/2017
9/29/2017
1/2/2018
4/2/2018
7/5/2018
pCi\L
0 0 0 0 0 0 0 0
0 ..... i\:i (,) :i:,.. CJ1 0) :....i (X) --1/2/2013
+ OJ 3/29/2013
I < 7/1/201 I (,)
rr
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+ 9/30/2014 OJ I < 1/7/2015 I +:>,
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0 C: 9/28/2015 :xJ ::::, a. m (J)
C: 1/4/2016 Q. O'" -0 -,
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7/5/201 I\)
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OJ I 1/5/2017
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4/2/2018
0
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o' Q)
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7' co ...... 0
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+
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~ ;::.: ::::,-6/29/2015
OJ Q)
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7/5/2018
0
i\,
0 ~ 0 O>
pCi\L
~ CX> ...... ...... ......
i\, ~
......
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m :c
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::0 m
C.
0 ::::,
I I\)
I\)
I\)
~
pCi\L
9 0 0 0 0 0 0 0 0
0 ...... i\, (,.) :,::.. 0, Ol :..-i CX> (0
1/2/2013
t 3/29/2013
7/1/201 OJ J: < I 10/1/201 (,J
a' ll)
(") 12/24/2013 " co a C: 4/2/2014 :, a. -
+
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1/7/2015 0:,
J: m < I 4/2/2015 :c 0)
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0:,
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O" I\) -n3 I\)
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10/10/2016
t 1/5/2017
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ll)
0 C: 9/29/201 ii>'" -CD a.
m 1/2/2018
() r
4/2/2018
7/5/2018
BWG/9/L
8 ~OG/G/P
B~OG/GH ....J
() w
"O Q) -L~OG/6G/6 <ti
::::,
(.)
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()
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C\I L~OG/6G/8 + C\I I
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9 ~OG/0 ~/0 ~ CJ) ,__ "O C > ::::,
0 ....
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..c
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+
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0 0 0 0 0 0 0 0
1\!0d
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 O.D7 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 O.Q7 0 0.5 0.03 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 0.71 0 0.34 0.2 0.4 0.5 0.7 1.43
4/4/2016 0 0.71 0.1 0.34 0.2 0 0.5 0.7 1.43
7/5/2016 0.1 0.71 0 0.34 0.07 0 0.5 0.23 1.43
10/10/2016 0.06 0.71 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 0.34 0.16 0.14 0.5 0.25 1.43
9/29/2017 0.06 0.71 0 0.34 0.24 0 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
4/2/2018 0.08 0.71 0 0.34 0.24 0.25 0.5 0.41 1.43
7/5/2018 0.05 0.71 0 0.34 0.11 0.03 0.5 0.24 1.43
* -Measurements obtained from BHV-3 have been designated as background due to BHV-3's remoteness from the Mill site. The
results in the table above are the above-background results with background (BHV-3) subtracted. Any negative values are
reported as zero for graphical purposes.
NA -Not Available -the canister was damaged. No data reported.
NS -Not Sampled -EFRI installed and began radon sampling at BHV-7 and BHV-8 in the fourth quarter of 2014.
BHV-6
BHV-6 Calculated
(pCi/L) ECL
0.4 0.83
0.1 0.83
0 0.83
0 0.83
0.73 0.83
0.24 0.83
0.03 0.83
0.2 0.83
0.2 0.83
0.23 0.83
0.3 0.83
0.3 0.83
0.1 0.83
0.1 0.83
0 0.83
0.08 0.83
0.19 0.83
0.35 0.83
0.19 0.83
0 0.83
0.27 0.83
0.14 0.83
0.08 0.83
BHV-7 BHV-8
BHV-7 Calculated BHV-8 Calculated
(pCi/L) ECL (pCi/L) ECL
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
NS 1.12 NS 0.71
0.2 1.12 0.1 0.71
0.33 1.12 0.03 0.71
0.2 1.12 0.2 0.71
0 1.12 0.1 0.71
0.2 1.12 0.1 0.71
0 1.12 0 0.71
0 1.12 0 0.71
0.03 1.12 0 0.71
0 1.12 0.14 0.71
0.13 1.12 0.16 0.71
0.11 1.12 0.11 0.71
0.06 1.12 0 0.71
0.11 1.12 0.25 0.71
0.14 1.12 0.17 0.71
0.08 1.12 0.00 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
4/2/2018 1.9
7/5/2018 0.76
a,
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0
rodo nova
lhe gobal leader in radon rnoosu-ement
Test results
RADON MONITORING REPORT
Issued by an Accredited Laboratory
REPORT NUMBER
4843270: 1
REPORT DATE
04/11/2018
REPORT PAGE 2 ( 4 )
PRINT DATE
04/11/2018
Detector Start date Stop date Location Detector comment Location type Avg Radon
Conc.pCi/1
Total Radon
Exp pCl-days/1
568749-6 01/02/2018 04/02/2018 BHY-1-1
550500-3 01/02/2018 04/02/2018 BHV-2-1
530330-0 01/02/2018 04/02/2018 BHV-4-1
530148-6 01/02/2018 04/02/2018 BHV-5-1
569132-4 01/02/2018 04/02/2018 BHY-6-1
553653-7 01/02/2018 04/02/2018 BHV-7-1
554962-1 01 /02/2018 04/02/2018 BHV-8-1
555223-7 01/02/2018 04/02/2018 BHV-2A-l
550230-7 01/02/2018 04/02/2018 OFFJCE-1
530103-1 01 /02/2018 04/02/2018 BLACK MESA I
Comment to the results
Tryggve Ronnqvist (Electronically signed)
Signature Radonova Laboratories AB Laboratory Measurement Specialist
This report may only be reproduced in full, unless the issuing laboratory has given
prior written approval.
Out-door 0.32 ± 0.11 28 ±9
Out-door 0.24 ± 0.11 21 ± 9
Out-door 0.49 ± 0.11 44± II
Out-door 0.65 ± 0.11 59± II
Out-door 0.38 ± 0.11 34 ± 9
Out-door 0.38 ± 0.11 34±9
Out-door 0.41 ± 0.11 37 ± 9
Out-door 0.24 ± 0.11 23 ± 9
In-door 1.9 ± 0.25 167 ± 23
Out-door 0.24 ± 0.11 21 ±9
Radonova Inc.
900 Oakmont Lane Suite 207,Westmont IL 60559
Telephone: [phone] E-mail: [e-mail]
DISCLAIMER -Radonova Inc. makes no warranty of any kind, express or implied, as regard to the use, operation or analysis of any Radonova Inc. monitor. Radonova Inc. specifically disclaims implied warranties of
merchantability and fitness for a particular purpose. Radonova Inc. is not responsible for any damage, including consequential damages, to persons or property resulting from the use of the monitor or the resulting data.
4511
"' _J
us
rodonovo
The global leader in radon measurement
Energy Fuels Resouces
David Turk
6425 S. Highway 191
PO Box 809
84511 Blanding
United States
17121
The analysis results are located on page 2 of this document.
RADON MONITORING REPORT
Issued by an Accredited Laboratory
107831-AL, 107830-RT
REPORT NUMBER REPORT PAGE 1 ( 4 )
4843270: 1
REPORT DATE PRINT DATE
04/11/2018 04/11/2018
MEASUREMENT PERFORMED FOR
6425 S HWY 191
84511 Blanding
REPORT RECEIVER(S)
Energy Fuels Resouces
Description of the measurement
The measurement was perfonned with a closed high-sensitivity alpha-track detector.
The detector(s) arrived to Radonova Laboratories AB 04/04/2018. They were measured 04/10/2018
Property data and address
6425 S HWY 191
84511 Blanding Transit Detector 1:
Transit Detector 2:
Transit Detector 3:
Measurement method: closed alpha-track high sensitivity detector
433593
461708
462749
The radon measurement was performed with a closed alpha-track detector following the quality assurance guidance given in EPA 402-R-95-012.
The detector container is manufactured from electrically conducting plastic. Through a small slit (filter), radon gas enters the detector. The track-detecting
material (film) inside the detector is hit by alpha particles generated by the radon entering the container and the decay products formed from it. On the film, the
alpha particles make small tracks which are enlarged through chemical etching and later counted in a microscope in order to determine the radon exposure.
Transit detectors are used for the return delivery of the high-sensitivity detectors in order to make a more accurate background subtraction.
Radonova Laboratories AB is accredited (no. 1489) by SWEDAC to conduct radon-gas measurements using the closed alpha-track detector method. The analysis
equipment is checked daily and the detectors are calibrated at regular intervals.
NRPP Licenses: 107831 AL, 107830 RT
Measured radon concentrations
For each detector, the measured value of the radon concentration is given. For each value an uncertainty associated with the measurement to a 95% confidence
level also given. For example a measurement result of 4.0 ± 0.5 pCi/1 means that the radon concentration is most likely contained in the range 3.5-4.5 pCi/1 .
If the start or end date of the measurement has not been provided, the radon concentration cannot be calculated. In such cases, the total exposure in pCi*days/1
will be reported.
More information about radon measurements and mitigation can be found in the AARST and EPA publications:
ANSI/AARST Protocol for Conducting Measurements of Radon and Radon-Decay Products in Schools and Large Buildings
ANSI/AARST Protocol for Conducting Radon and Radon Decay Product Measurements in Multifamily Buildings.
ANSI/AARST Radon Mitigation Standards for Schools and Large Buildings.
ANSI/AARST Radon Mitigation Standards for Multifamily Buildings.
EPA Radon Measurements in Schools, EPA 402-R-92-0 14, July 1993.
A Citizen· s Guide to Radon
Home Buyer's and Seller's Gudie to Radon
Consumer's Gudie to Radon Reduction
For more information about the interpretation of your test results or about other radon related issues we suggest contacting your state radon office.
Signature on the report
With the signature on the report, the person responsible for the radon analysis at Radonova Laboratories AB hereby certifies that the measurement procedures
follows the guidance in accordance with EPA 402-R-95-012 and that the demands from SWEDAC are fulfilled .
DISCLAIMER -Radonova Inc. makes no warranty or any kind, express or implied, as regard to the use, operation or analysis of any Radonova Inc, monitor. Radonova Inc. specifically disclaims implied warranties of
merchantability and fitness for a particular purpose. Radonova Inc. is not responsible for any damage, including conseciuential damages, to persons or property resulting rrom the use or the monitor or the resulting data.
"' ..J
rodonovo RADON MO NITO RI N G REPORT
Issued by an Accredited Laboratory 1he global leader in radon measurement
REPORT NUMBER REPORT PAGE 2 ( 6 )
4855635:]
REPORT DATE PRINT DATE
07/13/2018 07/13/2018
Test results
Detector Start date Stop date Location Detector comment Location type Avg Radon
Cone. pCi/1
Total Radon
Exp pO-days/1
604411-9 04/02/2018 07/05/2018 BHV-1-1
278064-1 04/02/2018 07/05/2018 BHV-2-1
607947-9 04/02/2018 07/05/2018 BHV-4-1
615628-5 04/02/2018 07/05/2018 BHV-5-1
604320-2 04/02/2018 07/05/2018 BHV-6-1
607619-4 04/02/2018 07/05/2018 BHV-7-1
606241-8 04/02/2018 07/05/2018 BHV-8-1
278119-3 04/02/2018 07/05/2018 BHV-2A-l
615236-7 04/02/2018 07/05/2018 OFFICE-I
606143-6 04/02/2018 07/05/2018 BLACK MESA I
Comment to the results
Tryggve Ronnqvist (Electronically signed)
Signature Radon ova Laboratories AB Laboratory Measurement Specialist
This report may only be reproduced in full, unless the issuing laboratory has given
prior written approval.
Out-door 0.16 ± 0.11 16 ± I I
Out-door <0.11 < 11
Out-door 0.14 ± 0.11 14 ± II
Out-door 0.35 ± 0.11 34± II
Out-door 0.19 ± 0.11 18 ± II
Out-door 0.19 ± 0.11 17± I I
Out-door 0.11 ± 0.09 10±9
Out-door < 0.11 < 11
In-door 0.76 ± 0.14 71 ± 14
Out-door < 0.11 < II
Radonova Inc.
900 Oakmont Lane Suite 207,Westmont IL 60559
Telephone: [phone] E-mail: [e-mail]
DISCLAIMER -Radonova Inc. makes no warranty of any kind, express or implied, as regard to the use, operation or analysis of any Radonova Inc. monitor. Radonova Inc. specifically disclaims implied warranties of
merchantablllty and fitness for a particular purpose. Radonova Inc. is not responsible for any damage, including consequential damages, to persons or property resulting from the use of the monitor or the resultlng data.,
4511
"" .J
us
rodo nova
The gbbd leader in radon measu-ement
Energy Fuels Resouces
David Turk
6425 S. Highway 191
PO Box 809
84511 Blanding
United States
17121
The analysis results are located on page 2 of this document.
RADON MONITORING REPORT
Issued by an Accredited Laboratory
REPORT NUMBER
4855635: I
REPORT DATE
07/13/2018
MEASUREMENT PERFORMED FOR
REPORT RECEIVER(S)
Energy Fuels Resouces
REPORT PAGE 3 ( 6 )
PRINT DATE
07/13/2018
Description of the measurement
The measurement was performed with a closed high-sensitivity alpha-track detector.
The detector(s) arrived to Radonova Laboratories AB 07/09/2018 . They were measured 07/13/2018
Property data and address
Transit Detector 1:
Transit Detector 2:
Transit Detector 3:
Measurement method: closed alpha-track high sensitivity detector
532568
559505
The radon measurement was performed with a closed alpha-track detector following the quality assurance guidance given in EPA 402-R-95-012.
The detector container is manufactured from electrically conducting plastic.Through a small slit (filter), radon gas enters the detector.The track-detecting
material (film) inside the detector is hit by alpha particles generated by the radon entering the container and the decay products formed from it. On the film, the
alpha particles make small tracks which are enlarged through chemical etching and later counted in a microscope in order to determine the radon exposure.
Transit detectors are used for the return delivery of the high-sensitivity detectors in order to make a more accurate background subtraction.
Radonova Laboratories AB is accredited (no. 1489) by SWEDAC to conduct radon-gas measurements using the closed alpha-track detector method. The analysis
equipment is checked daily and the detectors are calibrated at regular intervals.
NRPP Licenses: 107831 AL, 107830 RT
Measured radon concentrations
For each detector, the measured value of the radon concentration is given. For each value an uncertainty associated with the measurement to a 95% confidence
level also given. For example a measurement result of 4.0 ± 0.5 pCi/1 means that the radon concentration is most likely contained in the range 3.5-4.5 pCi/1 .
If the start or end date of the measurement has not been provided, the radon concentration cannot be calculated. In such cases, the total exposure in pCi*days/1
will be reported.
More information about radon measurements and mitigation can be found in the AARST and EPA publications:
ANSI/AARST Protocol for Conducting Measurements of Radon and Radon-Decay Products in Schools and Large Buildings
ANSI/AARST Protocol for Conducting Radon and Radon Decay Product Measurements in Multifamily Buildings.
ANSI/AARST Radon Mitigation Standards for Schools and Large Buildings.
ANSI/AARST Radon Mitigation Standards for Multifamily Buildings.
EPA Radon Measurements in Schools, EPA 402-R-92-014, July 1993.
A Citizen's Guide to Radon
Home Buyer's and Seller's Gudie to Radon
Consumer's Gudie to Radon Reduction
For more information about the interpretation of your test results or about other radon related issues we suggest contacting your state radon office.
Signature on the report
With the signature on the report, the person responsible for the radon analysis at Radonova Laboratories AB hereby certifies that the measurement procedures
follows the guidance in accordance with EPA 402-R-95-012 and that the demands from SWEDAC are fulfilled.
DISCLAIMER -Radonova Inc. makes no warranty or any kind, express or implied, as regard to the use, operation or analysis of any Radonova Inc~ monitor. Radon ova Inc. specifically disclaims implied warranties of
merchantability and fitness ror a particular purpose. Radonova Inc, is not responsible for any damage, including conseciuential damages, to persons or property resulting rrom the use of the monitor or the resulting dat.a,
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-s uCi/ml or 10 pCi/1) is applicable when radon daughters are not present. Both limits
represent the concentration at which a member of the public would receive a 50 mrem dose
assuming 100% (8760 hours) occupancy.
At the White Mesa Mill, the assumption of 100% equilibrium of radon progeny with parent Rn-
222 is unrealistic given the short half-lives of the nuclides considered and the short travel time to
the monitoring locations. Radon emanates from the ground (or mill tailings) without daughters
present, and the daughters grow in over time. It is therefore necessary to evaluate radon daughter
equilibrium at each air monitoring station utilizing site-specific wind speed and distance
information to derive site-specific Effluent Concentration Limits (ECLs) for each station.
Such disequilibrium situations and alternative calculations are anticipated by the regulations and,
in particular, R313-15-302(3) provides a means by which the licensee may adjust the effluent
concentration values in 10 CFR Part 20 Appendix B, Table 2, which are incorporated by
reference into R313-15-302(2)(b)(i), to account for disequilibrium. The regulatory purpose of
such an adjustment is to appropriately take into account the actual characteristics of the measured
effluents, including radioactive decay equilibrium.
An established (EPA, 1986) outdoor equilibrium formula to determine the appropriate
Equilibrium Factor for use in calculating the ECL for disequilibrium conditions was used. The
EPA expression of the outdoor Equilibrium Factor (EF) is derived by the following equation:
EF = 1.0-0.0479exp<-114·39J _ 2.1963exp<-1138·6) + l.2442exp<-1123A)
[Where: tis the travel time in minutes (distance/wind speed)]
Once the Equilibrium Factor has been determined, the ECL for each air monitoring station is
determined by dividing the 0.1 pCi/1 limit (for situations when daughters are present) by the
Equilibrium Factor (EF).
Results
By utilizing the above formula, the appropriate (equilibrium adjusted) ECLs for the location was
calculated. In developing the ECLs, distances and corresponding travel times have been
determined by:
• assuming a nominal centroid located approximately at the vanadium dryer stack,
• calculating average wind speeds appropriate for each direction from the centroid to each
monitoring station location, and
• using Google Earth to develop the distances.
Meteorological data collected at the Mill's Met Station were utilized to compute the average
wind speed for different directions. These data are applicable and sufficient for the purpose of
these calculations.
It should be noted when comparing actual measurement values to the derived ECLs that the
derived ECL provides ample protection for members of the public. More specifically, if dose
calculations had been performed utilizing current ICRP 65 dose conversion conventions, the
ECLs established here would represent approximately 25 mrem for continuous exposure at the
monitoring stations. Therefore these values can serve as appropriate ALARA goals, since they
yield doses well below the 100 mrem standard for individual members of the public.
References
United States Environmental Protection Agency (EPA). (1986). Final rule for radon-222
emissions from licensed uranium mill tailings. Washington, D.C.: Office of Radiation Programs,
U.S. Environmental Protection Agency.
ATTACHMENT K
CELL 2 RADON FLUX DATA
Cell2
2018 Radon Flux Measurement Program
First Half 2018 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. Box 809
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 ..................................................................................................................... 2
5 .1 Equipment Preparation ....................................................................................................... 2
5.2 Sample Locations, Identification, and Placement.. ........................................................... 2
5.3 Sample Retrieval ............................................................................................................... 3
5.4 Environmental Conditions ................................................................................................ 3
6. SAMPLE ANALYSIS ..................................................................................................................... 3
6.1 Apparatus ........................................................................................................................... 3
6.2 Sample Inspection and Documentation ............................................................................. 4
6.3 Background and Sample Counting .................................................................................... 4
7. QUALITY CONTROL (QC) AND DATA VALIDA TI ON ........................................................... 4
7 .1 Sensitivity .......................................................................................................................... 5
7.2 Precision ............................................................................................................................. 5
7.3 Accuracy ............................................................................................................................ 5
7 .4 Completeness ..................................................................................................................... 5
8. CALCULATIONS ........................................................................................................................... 5
9. RESULTS ........................................................................................................................................ 6
9.1 Mean Radon Flux ............................................................................................................... 6
9.2 Site Results ......................................................................................................................... 7
References ............................................................................................................................................ 8
Figure 1 ................................................................................................................................................ 9
Appendix A. Charcoal Canister Analyses Support Documents
Appendix B. Recount Data Analyses
Appendix C. Radon Flux Sample Laboratory Data, Including Blanks
Appendix D. Sample Locations Map (Figure 2)
i
1. INTRODUCTION
During March 25-26, 2018 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 first half of the year 2018.
Tellco was contracted to provide radon canisters, equipment, and canister-placement personnel as well
as lab analysis of samples collected. Energy Fuels personnel provided support for loading and
unloading charcoal from the canisters. This report details the procedures employed by Energy Fuels
and Tellco to obtain the results presented in Section 9.0 of this report.
2. SITE DESCRIPTION
The White Mesa Mill facility is located in San Juan County in southeastern Utah, six miles south of
Blanding, Utah. The mill began operations in 1980 for the purpose of extracting uranium and
vanadium from feed stocks.
Cell 2, which has a total area of approximately 270,624 m2, has been filled and covered. This cell is
comprised of one region, a soil cover of varying thickness. There was no standing liquid and were no
exposed tailings within Cell 2 during this sampling.
3. REGULATORY REQUIREMENTS FOR CELL 2
Radon emissions from the uranium mill tailings for Cell 2 at this site are regulated by the State of
Utah's Division of Waste Management and Radiation Control (DWMRC). In accordance with
DWMRC requirements specified in correspondence dated july 23, 2014, Energy Fuels must measure
the radon flux on Cell 2 in accordance with 40 CFR 61, Appendix B, Method 115, "Monitoring for
Radon-222 Emissions" semiannually. The average annual measured radon flux for Cell 2 shall not
exceed a value 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 IO-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 ~ inch thick layer of foam and
secured with a retaining ring under 1 ~ 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 ofradioactive 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 March 25, 2018, 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., COl ... ClOO). This
ID was written on an adhesive label and affixed to the top of the canister. The sample ID, date, and
2
time of placement were recorded on the radon flux measurements data sheets for the set of one
hundred measurements.
Prior to placing a canister at each sample location, the retaining ring, screen, and foam pad of each
canister were removed to expose the charcoal support grid. A pre-measured charcoal charge was
selected from a batch, opened and distributed evenly across the support grid. The canister was then
reassembled and placed face down on the surface at each sampling location. Care was exercised not
to push the device into the soil surface. The canister rim was "sealed" to the 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 March 26, 2018 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. Upon completion of on-site activities, the
field equipment was alpha and beta-gamma scanned by Energy Fuels Radiation Safety personnel and
released for unrestricted use.
5.4 Environmental Conditions
A rain gauge 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.
6. SAMPLE ANALYSIS
6.1 Apparatus
Apparatus used for the analysis:
• Single-or multi-channel pulse height analysis system, Ludlum Model 2200 with a
Teledyne 3" x 3" sodium iodide, thallium-activated (Nal(Tl)) detector.
3
• Lead shielded counting well approximately 40 cm deep with 5-cm 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 within a few days following the original count.
7. QUALITY CONTROL (QC) AND DATA VALIDATION
Charcoal flux measurement QC samples included the following intra-laboratory analytical frequency
objectives:
• Blanks, 5 percent, and
• Recounts, 10 percent
4
All sample data were subjected to validation protocols that included assessments of sensitivity,
precision, accuracy, and completeness. As described below, all Method 115-required data quality
objectives (EPA, 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 0.05 pCi/m2-s, with an
average of approximately 0.03 pCi/m2-s. The lower limit of detection (LLD) was approximately 0.03
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 10 percent of the total number of samples analyzed. The precision values of recount
measw-ements that were above 1 pCi/m2-sec, expressed as relative percent difference (RPD), ranged
from 1.2 to 6. 7 percent RPD with an average of approximately 3.0 percent RPD. This complies with
the precision objective of 10 percent.
7.3 Accuracy
Accuracy of field measurements was assessed daily by counting two laboratory control samples with
known Ra-226 content. Accuracy of these lab control sample measurements, expressed as percent
bias, ranged from approximately -1.0 percent to + 1.0 percent. The arithmetic average bias of the lab
control sample measurements was approximately -0.2 percent (see Appendix A). This complies with
the accuracy objective of+/-10 percent bias.
7.4 Completeness
One hundred samples from the Cell 2 cover region were verified as valid, representing 100 percent
completeness, which complies with the completeness objective of 85 percent.
8. CALCULATIONS
Radon flux rates were calculated for charcoal collection samples using calibration factors derived
from cross-calibration to sources with known total activity with identical geometry as the charcoal
containers. A yield efficiency factor was used to calculate the total activity of the sample charcoal
containers. Individual fi(?ld sample result values presented were not reduced by the results of the field
blank analyses.
5
In practice, radon flux rates were calculated by a database computer program. The algorithms utilized
by the data base program were as follows:
Equation 8.1:
pCi Rn-222/m2sec = [Ts* A *b*'~.s<.Wi.?s)
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, for M-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:
Gr oss Samp l e , cpm Background Sample, cpm --------+----------
Samp leCount, t,min Bac kground Count,t,min
Error,2a-= 2 X -'------------------------X Sample Concentration
Net,cpm
Equation 8.3:
_ 2.71 + (4.65)(S~
LLD -[Ts*A*b*O.s(dl') ,?S)J
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
9. RESULTS
9.1 Mean Radon Flux
Referencing 40 CFR, Part 61, Subpart W, Appendix B, Method 115 -Monitoring for Radon-222
Emissions, Subsection 2.1. 7 -Calculations, "the mean radon flux for each region of the pile and for
the total pile shall be calculated and reported as follows:
(a) The individual radon flux calculations shall be made as provided in Appendix A EPA
86(1 ). The mean radon flux for each region of the pile shall be calculated by summing all
individual flux measurements for the region and dividing by the total number of flux
measurements for the region.
6
(b) The mean radon flux for the total uranium mill tailings pile shall be calculated as follows:
At
Where: Is = Mean flux for the total pile (pCi/m2 -s)
Ji = Mean flux measured in region i (pCi/m2-s)
Ai = Area of region i (m2)
At = Total area of the pile (m2)"
40 CFR 61, Subpart W, Appendix B, Method 115, Subsection 2.1.8, Reporting states "The results of
individual flux measurements, the approximate locations on the pile, and the mean radon flux for each
region and the mean radon flux for the total stack [pile] shall be included in the emission test report. Any
condition or unusual event that occurred during the measurements that could significantly affect the results
should be reported."
9.2 Site Results
Site Specific Sample Results (reference Appendix C)
(a) The mean radon flux for the Cell 2 region at the site is as follows:
Cell 2 -Cover Region = 3.1 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 = 3.1 pCi/m2-s
(3.1)(270,624) = 3.1
270,624
As shown above, the arithmetic mean of the radon flux rate measurements representing the first half
of the year 2018 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.
7
References
U. S. Environmental Protection Agency, Radon Flux Measurements on Gardinier and Royster
Phosphogypsum Piles Near Tampa and Mulberry, Florida, EPA 520/5-85-029, NTIS #PB86-
161874, January 1986.
U.S. Environmental Protection Agency, Title 40, Code of Federal Regulations, January 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 JO, Code of Federal Regulations, Part 40, Appendix A,
January 2017.
8
Figure 1
Large Area Activated Charcoal Canisters Diagram
fJG [
9
r-in Tt1ti:::k
S'<:<<,bbd• f',,j
,/2.,,., rtin:k
S.:.rut-:rl!, P•,2
I '2,in Tl,,.:;~ Cil1otcu.:1,
.S ••~tu>• I Q'r ~I
Fta, .. ;r,~r
Su11~;
10.,~ '*~
l'',1CEr>'1C'"IJc
ENERGY FUELS RESOURCES
WHITE MESA MILL, BLANDING, UTAH
2018 NESHAPs RADON FLUX MEASUREMENTS
CELL2
SAMPLING DATES: 03/25/18-03/26/18
ANALYSIS DATES: 03/27/18-03/28/18
SYSTEM COUNT Bkg Counts (1 min. each)
I.D. DATE #1 #2
M-01/D-21 3/27/2018 142 148
M-01/D-21 3/27/2018 143 133
M-01/D-21 3/28/2018 127 138
M-01/D-21 3/28/2018 130 122
M-01/D-21 3/27/2018 142 148
M-01/D-21 3/27/2018 143 133
M-01/0-21 3/28/2018 127 138
M-01/0-21 3/28/2018 130 122
M-02/D-20 3/27/2018 145 151
M-02/D-20 3/27/2018 141 153
M-02/D-20 3/28/2018 115 129
M-02/D-20 3/28/2018 135 119
M-02/D-20 3/27/2018 145 151
M-02/0-20 3/27/2018 141 153
M-02/0-20 3/28/2018 115 129
M-02/0-20 3/28/2018 135 119
#3
149
141
121
136
149
141
121
136
144
140
137
128
144
140
137
128
ACCURACY APPRAISAL TABLE
FIRST HALF 2018
Source Counts (1 min. each) AVG NET
#1 #2 #3 cpm
10407 10398 10157 10174
10223 10160 10173 10046
10347 10364 10128 10151
10208 10241 10167 10076
10310 10104 10125 10033
10100 10111 10201 9998
10238 10004 10151 10002
10160 10123 10273 10056
10136 10286 10317 10100
10281 10088 10160 10032
10142 10305 10225 10097
10215 10362 10065 10087
10198 10050 10224 10011
10146 10128 10227 10022
10165 10102 10119 10002
10096 10137 10110 9987
YIELD FOUND SOURCE
cpm/pCi pCi ID
0.1698 59920 GS-04
0.1698 59166 GS-04
0.1698 59782 GS-04
0.1698 59340 GS-04
0.1698 59089 GS-05
0.1698 58883 GS-05
0.1698 58907 GS-05
0.1698 59223 GS-05
0.1701 59375 GS-04
0.1701 58975 GS-04
0.1701 59359 GS-04
0.1701 59298 GS-04
0.1701 58852 GS-05
0.1701 58920 GS-05
0.1701 58799 GS-05
0.1701 58713 GS-05
AVERAGE PERCENT BIAS FOR ALL ANALYTICAL SESSIONS:
KNOWN %BIAS
pCi
59300 1.0%
59300 -0.2%
59300 0.8%
59300 0.1%
59300 -0.4%
59300 -0.7%
59300 -0.7%
59300 -0.1%
59300 0.1%
59300 -0.5%
59300 0.1%
59300 0.0%
59300 -0.8%
59300 -0.6%
59300 -0.8%
59300 -1.0%
-0.2%
CHARCOAL CANISTER ANALYSIS SYSTEM
s1TE LocATioN: W h \ +-c M e-s °' M -, \ \ 1 3 \ c" vi d: V\~ ,, v\ Tt\ h.
CLIENT: EV\ e_f~T f 1.Ae.\ 2 K e5oc.A{ce 5 (u SA")
Calibration Check Log
System ID: ____._"tA~--O_l-'/'--·D ..... 1 _-_2_\ __ _ Calibration Date: ' / I f / I 7 • DueDate: ·-,////I B
Scaler SIN: __ 5~_1 =S~t~:L ____ High Voltage: i l (p 3 Window: 4 42 Thrshld: 2.20
Detector SIN: ~(_")_~~I =5~3~3 ___ Source ID/SN: )< f:\ 2 2-(., /GS-DY Source Activity: 5 j, 3 I.( p C
Blank Canister Bkgd. Range, cpm: 2 a= ~i~D~u ___ to ISi 3a= 95
Gross Source Range, cpm: 2a= 0)0, 5 \ to lO 4-55 3a=
Technician: VLe C:r2o/'==
to _ __,_I-"'(£'-'?-.__
1059!:;"" '3 B :;i. Y to
1?i1--
All counts times are one minute.
Date By BackITTound Counts ( I min. each) Source Counts (I min. each) ok?
#1 #2 #3 Avg. #1 #2 #3 Averaj!;e YIN
-; Jz7 /J ,;,, 'f)'U., 11.p ... J 4'0 140) 1'1'1,., I CLJ.o .. ·1 ro·~~~ } 101i;--10'?2-l '-1
l;J 7.7'}11P, '.>2.L JLt'~ l's3 1UI l";i1\ ro-i.'"2-~ I o·l lo( i0\'"1": IO I f3.;;; </
i,, fY', J l' ~ 1 >1.£, , .,_--, llB I ')_ \ i"l.OI IO~i.4--? jt)'~/.J.. ·101·.:> ~ IO >-f10 " 2; r..,9,·1 IQ-)10_ l"'.l (J 11.."'l. i-,. L, '·"2.?'l i02..0 ~ iO:i.a.1 ,o 1"37 I 02..0 ~ ..j -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.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: \,1\)\,\,-\-~· tv\<.St?\ ~{1 \ \ J "I?I C1V1d 'i nj I LA ti\~
CLIENT: E v\ e v-~1 ~ "'e \s 'i<. e,sov-v ~ e 5' ( 0.. SI\.)
Calibration Check Log
System ID: ~fv'\_-_a_i_/_J>_-_2-_I___ Calibration Date: '7 / 17 / 17 Due Date: 7 / 11 / I 8
Scaler SIN:--~?-· .__I _5_1_2. ___ High Voltage: \ l lL>3 Window: 4.42 Thrshld: 2.20
o 27-fo/
Detector SIN: _ __,,,O.__Y_.__1 _5_3__.;:;:3'----Source ID/SN: I'<\ L& S -D5 Source Activity: 59~ 3 I< f' c .. ·.
Blank Canister Bkgd. Range, cpm: 2 o = I O 4' to l 5 l 3 o = 0) S"
Gross Source Range, cpm: 2 o = ~ '1 4 B to I O Lf 3 5 ; o = q B '2. I
Technician: y .-i-(-1,-Pf=: J) J,,-C_
All counts times are one minute.
Date By Backirround Counts (1 min. each) Source Counts (l min. each)
#1 #2 #3 Avg. #1 #2 #3
3t:n/lE VJU... I 1..#-.-Z.. 11.L.P. j 4-°I i4\. 0?.10 1a1nt+ ID J-:2c:;
1~1 -zil ll ~ 4/U,-1y.~~ \t,, ~ l '4' l~O\ n1vo t0 II r ID201 . .,, /2A/l'O 1>tJl,, I "'2..--, 1~e l "2..J 1"7~ D.:l.~~ I ODDLI, i0/51
:,b.0 l tP !~ 120 I 2-7-,~ .. n .... ?\ Oit'oO i0123 101,~ ..
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.
to __ (~~~-_-i... __
,0557 to
ok?
Average YIN
iOl130 " ,o J--z,·1 'Y
IC) I~ I v
1 D le~ ./J
I
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: w \f\·, ~ r-A c" S", M \ \ \. '3 \ t"! hd. I Wj \ UM~
CLIENT: C. V\ e Ve;) 'f Fv1.. e \ s 'R e 5 o LA i,r ~-t?S (__,l.J... 5 A J
Calibration Check Log
System ID: _M--'--· _0_·2--_,_/_t)_·-_-:2-_o __ _ Calibration Date: 7 / IJ / I I Due Date: ·7 / I 1 / I 5
I •
Scaler SIN: __ S~l _5_~~3 ____ High Voltage: f;8 8 Window:
Source ID/SN: ~u. z &5-· 0 lf
4 42 Thrshld: 2.20
Source Activity: S~ ,"3 K.. p C.; Detector SIN: 0 Y I .5 3 ::2
0 ISl Blank Canister Bkgd. Range, cpm: 2 cr = __ l_l ___ to ___ .:..___ 3 cr = Dj6 to {~8
Gross Source Range, cpm: 2cr= ?')0)52. to ,olf88 3cr= 9B18 to 1o{o"J-2-
Technician: 't2 z (,; t=-= Du ..
All counts times are one minute
Date By Backe ound Counts (l min. each) Source Counts (1 min. each 1 ok?
#1 #2 #3 Av2. #1 #2 #3 Average YIN
3~1/ 'R Vu? ; 4,:; isl 14,t.J. \W1 I Cl -.LA Io~-"" iL'l ln~i7 I 0·"'2;-t i, 'I
"3/?.."7' / fJJ Dtl2 1c.+ I ,,~ I 1./-0 11..t'<" /n~OJ I 00 Qlt3 Io lbD 101,v '" 1°3'/~) (13 IJ2-.e, II~ I 2.0\ 1 ~-, t~, 10 I L+'2-\O~nc:" 10·2""2.~ 10"2..~4 0
1'/26 J IA Du'-13S' JIG) ,"'2~ ,,_, 102,s 10"3'12... l00bS 10"'2..\4 <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.
CHARCOAL CANISTER ANALYSIS SYSTEM
SITE LOCATION: W h' A-e.. M e~r\ IV\.' \ \ , }s lc1"' cl-~ Y\C1 1 \.A+c,i h
CLIENT: S."' e v-~i F\Ac\s ·ie_sov\rc:L S ,U,"-${1)
Calibration Check Log
Calibration Date: '7 / 11 / l 1 Due Date: ·, f i 7 / l 8
High Voltage: e 8 8 Window: _..:,4c,:,.4.,._2 _ Thrshld: 2.20
System ID: ,v\ -0 J.... [v ·-2-D
Scaler SIN: 5 l 5 (; 3
Detector SIN: 0 L1 ( 5 3 2. Source l~/SN: R"'v-c..;&s·-O 5 Source Activity: 5:~1. ?J.KpC.,;
Blank Canister Bkgd. Range, cpm: 2 cr = \ I O to I 51 3 O' = 0\ 5 to I f..t.,c5
Gross Source Range, cpm: 2 cr = °Jq I I to 1 0 Lt (p O 3 O' = 0 f Pf~ to I 05 8?-
Technician: _~.:::...7--=--l __ L1J_1_-~_._ __ Y._'?-_' .t.'-
All cowits times are one minute
Date By Backirround Counts (1 min. each) Source Counts ( 1 min. each) ok?
#1 #2 #3 Avg. #1 #2 #3 Averae:e YIN
3 '2..7/lA. '71--t:-· 145 I c:;-I I Llc.J. J '-t'"? i CI~ 1\1 100~ l ,.,-,-,L.1 tO l~t " ~ 1211
) 19> ~ I 1.4-I ,~ 1417 Jl.4-~ I Ol'l,t-'" -~~ -, 0·7..:.,, IO 1"11 " ~j 71' I Jrl.. r:n,.£,-1 l" i 7~0) 1'2 ·1 1-z...1 1Dllo~ 10/0? I ()11~ I O I '2..0\ " B .,tPJ'lr~ ~ I "2. .::;-' I n. 1 '"'i.. P, 1"7-1 I r.1""10.-l~ I t, 1'~"1 i ,n. I I r1 11) I \ 4 v
I I .., • I 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: D V\ l\ \AS 7oc-+-o··-g V"~ Wl
Standard Weight (g): 3 0 D, 0 ~ (4-WIS
Date Pre-check (g) Post-check (g) O.K. ±0.1 %?
? /'1.1 I I B '2-qq,c, 300,0 yi!.5
3/PBl t'B ·300.0 300,c, Vt!''!?
j
By
"):""' ',I,,, .A -...,.., -,r
'pt '1:;·
.
Appendix B
Recount Data Analyses
B
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: C SURFACE: SOIL
AREA: COVER DEPLOYED: 3 25 18 RETRIEVED: 3
COUNTED BY: DLC FIELD TECHNICIANS: CE, DLC,TE
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
RECOUNT CANISTER ANALYSIS:
AIR TEMP MIN: 29°F
26 18 CHARCOAL BKG:
DATA ENTRY BY: DLC
147
PROJECT NO.: 18004.01
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
g.
g.
GRID S~ll?LE RETRIV WALYSIS M'ID-TI:t-1E CNT GROSQ GROSS RADON ± LLD PRECISION
E.0CAT!ON I. D. RR MIN HR MI:N !-1Q D~ YR. HR MIN (MIN) CO(J.NTS WT IN pCi/I!J' s pCi/m' s pCi/m' s % RPD
ClO ClO 9 39 9 23 3 27 18 16 37 2 1257 218.9 0.87 0.1 0.03
RECOUNT ClO 9 39 9 23 3 28 18 10 9 2 1098 218.9 0.83 0.1 0.04 4.6%
C20 C20 9 49 9 26 3 27 18 16 46 1 5366 219.8 9.5 1. 0 0.03
RECOUNT C20 9 49 9 26 3 28 18 10 8 1 4646 219.8 9.3 0.9 0.04 1. 7%
C30 C30 9 39 9 23 3 27 18 17 2 1 1182 219.5 1.9 0.2 0.03
RECOUNT C30 9 39 9 23 3 28 18 10 12 2 1991 219.5 1.8 0.2 0.04 6.7%
C40 C40 9 50 9 27 3 27 18 17 14 1 4861 216.9 8.6 0.9 0.03
RECOUNT C40 9 50 9 27 3 28 18 10 11 1 4187 216.9 8.4 0.8 0.04 2.6%
C50 cso 9 39 9 59 3 27 18 17 26 1 1466 219.3 2.3 0.2 0 .03
RECOUNT cso 9 39 9 59 3 28 18 10 15 1 1322 219.3 2.4 0.2 0 .04 1.3%
C60 C60 9 50 9 28 3 27 18 17 37 1 3328 219.0 5.8 0.6 0.03
RECOUNT C60 9 50 9 28 3 28 18 10 15 1 2920 219.0 5.8 0.6 0.04 1.2%
C70 C70 9 36 9 47 3 27 18 17 52 1 1288 219.5 2.0 0.2 0.03
RECOUNT C70 9 36 9 47 3 28 18 10 16 1 1180 219.5 2.1 0.2 0.04 2.6%
C80 c00 9 51 9 39 3 27 18 18 8 1 1322 215.8 2.1 0.2 0.03
RECOUNT C80 9 51 9 39 3 28 18 10 16 1 1135 215.8 2.0 0.2 0.04 5.1%
C90 C90 9 52 9 43 3 27 18 18 22 2 1195 220.7 0.82 0.1 0.03
RECOUNT C90 9 52 9 43 3 28 18 10 19 2 1044 220.7 0.77 0.1 0.04 6.1%
ClOO ClOO 9 55 9 44 3 27 18 18 36 2 1354 218.9 0.97 0.1 0.03
RECOUNT ClOO 9 55 9 44 3 28 18 10 19 2 1169 218.9 0.90 0.1 0.04 7.3%
AVERAGE PERCENT PRECISION FOR THE CELL 2 COVER REGION: 3.9%
Page 1 of 1
Appendix C
Radon Flux Sample Laboratory Data (including Blanks)
C
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: C SURFACE: SOIL
AREA: COVER DEPLOYED: 3 25 18 RETRIEVED: 3
COUNTED BY: DLC FIELD TECHNICIANS: CE, DLC,TE
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
AIR TEMP MIN: 29°F
26 18 CHARCOAL BKG:
DATA ENTRY BY: DLC
147
PROJECT NO.: 18004.01
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV ANALYSIS MID-TIME CNT GROSS .. GROSS RADON ± LLD
g.
g.
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m' s pCi/m2 s pCi/m' s COMMENTS:
COl COl 9 30 9 20 3 27 18 16 24 2 1002 218.2 0.6 0.06 0.03
CO2 CO2 9 31 9 20 3 27 18 16 24 2 1018 217.8 0.7 0.07 0.03
C03 C03 9 32 9 20 3 27 18 16 26 2 1035 217.9 0.7 0.07 0.03
C04 C04 9 33 9 21 3 27 18 16 27 3 1346 216.7 0.5 0.05 0.03
cos cos 9 34 9 21 3 27 18 16 31 3 1233 218.1 0.5 0.05 0.03
C06 C06 9 35 9 21 3 27 18 16 31 2 1931 218.4 1. 5 0.15 0.03
C07 C07 9 36 9 22 3 27 18 16 34 2 1870 218.9 1.4 0.14 0.03
cos cos 9 37 9 22 3 27 18 16 34 1 2400 217.0 4.1 0.41 0.03
C09 C09 9 38 9 22 3 27 18 16 37 3 1298 218.4 0.5 0.05 0.03
ClO ClO 9 39 9 23 3 27 18 16 37 2 1257 219.3 0.9 0.09 0.03
Cll Cll 9 40 9 23 3 27 18 16 40 1 1562 218.7 2.6 0.26 0.03
Cl2 Cl2 9 41 9 23 3 27 18 16 40 1 1258 215.2 2.0 0.20 0.03
C13 C13 9 42 9 24 3 27 18 16 42 1 3722 218.7 6.5 0.65 0.03
Cl4 C14 9 43 9 24 3 27 18 16 42 1 1882 218.7 3.2 0.32 0.03
Cl5 Cl5 9 44 9 24 3 27 18 16 43 1 1305 219.0 2.1 0.21 0.03
Cl6 Cl6 9 45 9 25 3 27 18 16 43 1 1087 217.3 1. 7 0.17 0.03
C17 C17 9 46 9 25 3 27 18 16 45 1 5283 218.4 9.4 0.94 0.03
C18 C18 9 47 9 25 3 27 18 16 45 1 10896 218.0 19.6 1. 96 0.03
C19 Cl9 9 48 9 26 3 27 18 16 46 1 6201 218.8 11. 0 1.10 0.03
C20 C20 9 49 9 26 3 27 18 16 46 1 5366 219.8 9.5 0.95 0.03
C21 C21 9 30 9 20 3 27 18 16 49 2 1111 218.6 0.7 0.07 0.03
C22 C22 9 31 9 20 3 27 18 16 48 1 2640 218.3 4.5 0.45 0.03
C23 C23 9 32 9 20 3 27 18 16 52 3 1003 216.6 0.3 0.04 0.03
C24 C24 9 33 9 21 3 27 18 16 52 2 1002 218.2 0.6 0.06 0.03
C25 C25 9 34 9 21 3 27 18 16 56 3 1155 216.7 0.4 0.05 0.03
C26 C26 9 35 9 21 3 27 18 16 56 2 1029 213.5 0.7 0.07 0.03
C27 C27 9 36 9 22 3 27 18 16 59 3 1022 219.0 0.4 0.04 0 .03
C28 C28 9 37 9 22 3 27 18 16 59 2 1333 217.8 0.9 0.09 0.03
C29 C29 9 38 9 22 3 27 18 17 3 3 1007 217.1 0.3 0.04 0.03
C30 C30 9 39 9 23 3 27 18 17 2 1 1182 219.5 1. 9 0.19 0.03
C31 C31 9 40 9 23 3 27 18 17 5 1 2917 221.3 5.0 0.50 0.03
C32 C32 9 41 9 23 3 27 18 17 5 1 1338 217.9 2.2 0.22 0.03
C33 C33 9 42 9 24 3 27 18 17 8 2 1002 219.1 0.6 0.06 0.03
C34 C34 9 43 9 24 3 27 18 17 7 1 1014 218.6 1.6 0.16 0.03
C35 C35 9 45 9 24 3 27 18 17 10 2 1346 217.5 1. 0 0.10 0.03
C36 C36 9 46 9 25 3 27 18 17 10 2 1581 218.1 1.2 0.12 0.03
C37 C37 9 47 9 25 3 27 18 17 12 1 3520 219.4 6.2 0.62 0.03
Page 1 of 3
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: C SURFACE: SOIL
AREA: COVER DEPLOYED: 3 25 18 RETRIEVED: 3
COUNTED BY: DLC FIELD TECHNICIANS: CE, DLC,TE
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
AIR TEMP MIN: 29°F
26 18 CHARCOAL BKG:
DATA ENTRY BY: DLC
147
PROJECT NO.: 18004.01
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
emrb SAMPLE DEPLOY RETRIV ANALYSIS MID-TIME CN'l' G~OSS GROSS RADON ± LLD
g.
g.
LOCATION I. D. HR MIN H;R MIN MO DA YR HR MIN (MIN) eoUNTS WT IN pCi/m2 S pCi/m' $ pCi/m2 S COMMENTS:
C38 C38 9 48 9 26 3 27 18 17 12 1 14617 219.0 26.4 2.64 0.03
C39 C39 9 49 9 26 3 27 18 17 14 1 4214 218 .3 7.4 0.74 0.03
C40 C40 9 50 9 27 3 27 18 17 14 1 4861 216 .9 8.6 0.86 0 .03
C41 C41 9 30 9 56 3 27 18 17 16 2 1135 217.9 0 .7 0.07 0.03
C42 C42 9 31 9 56 3 27 18 17 16 2 1238 218.1 0.8 0.08 0.03
C43 C43 9 32 9 56 3 27 18 17 19 3 1006 219.9 0.3 0.04 0.03
C44 C44 9 33 9 57 3 27 18 17 18 1 2855 216.2 4.8 0.48 0.03
C45 C45 9 34 9 57 3 27 18 17 22 2 1483 216.6 1.1 0 .11 0.03
C46 C46 9 35 9 57 3 27 18 17 22 2 1690 219.8 1.2 0.12 0.03
C47 C47 9 36 9 58 3 27 18 17 24 1 7763 220.1 13.5 1. 35 0.03
C48 C48 9 37 9 58 3 27 18 17 24 1 2585 219.5 4.3 0.43 0.03
C49 C49 9 38 9 58 3 27 18 17 26 1 1001 218.3 1.5 0.15 0.03
cso C50 9 39 9 59 3 27 18 17 26 1 1466 219.3 2.3 0.23 0.03
C51 C51 9 40 9 59 3 27 18 17 28 2 1517 217.5 1.1 0 .11 0.03
C52 C52 9 41 9 59 3 27 18 17 27 1 1224 218.0 1. 9 0.19 0.03
C53 C53 9 42 10 0 3 27 18 17 31 2 1020 218.4 0.6 0.06 0.03
C54 C54 9 43 9 30 3 27 18 17 31 2 1355 219.1 1.0 0.10 0.03
C55 C55 9 44 9 30 3 27 18 17 33 2 1130 217.8 0.8 0.08 0.03
C56 C56 9 45 9 30 3 27 18 17 33 1 6168 217.9 11. 0 1.10 0.03
C57 C57 9 47 9 29 3 27 18 17 35 1 2234 218.7 3.8 0.38 0.03
C58 C58 9 48 9 29 3 27 18 17 35 1 11342 216.2 20.5 2.05 0.03
C59 C59 9 49 9 28 3 27 18 17 37 1 5435 218.8 9.7 0.97 0.03
C60 C60 9 50 9 28 3 27 18 17 37 1 3328 219.0 5.8 0.58 0.03
C61 C61 9 46 9 27 3 27 18 17 39 2 1515 218 .4 1.1 0 .11 0.03
C62 C62 9 45 9 27 3 27 18 17 39 2 1656 220 .0 1.2 0.12 0.03
C63 C63 9 44 9 27 3 27 18 17 42 2 1124 216.9 0.8 0.08 0.03
C64 C64 9 43 9 28 3 27 18 17 42 1 1267 218.1 2.0 0.20 0.03
C65 C65 9 42 9 28 3 27 18 17 45 3 1244 218.5 0.5 0.05 0.03
C66 C66 9 41 9 28 3 27 18 17 44 1 4786 219.6 8.5 0.85 0.03
C67 C67 9 40 9 29 3 27 18 17 49 3 1002 214 .8 0.3 0.04 0.03
C68 C68 9 38 9 29 3 27 18 17 49 3 1400 219.1 0.6 0.06 0.03
C69 C69 9 37 9 47 3 27 18 17 52 2 1268 219.4 0.9 0.09 0.03
C70 C70 9 36 9 47 3 27 18 17 52 1 1288 219.5 2.0 0.20 0.03
C71 C71 9 35 9 47 3 27 18 17 54 2 1620 219 .1 1. 2 0.12 0.03
C72 C72 9 34 9 48 3 27 18 17 54 1 1496 219.5 2.4 0.24 0.03
C73 C73 9 33 9 48 3 27 18 17 57 2 1011 219.6 0.6 0.06 0.03
C74 C74 9 32 9 48 3 27 18 17 56 1 1074 220.2 1. 7 0.17 0.03
Page 2 of 3
CLIENT: ENERGY FUELS RESOURCES PROJECT: RADON FLUX MEASUREMENTS, WHITE MESA MILL
PILE: 2 BATCH: C SURFACE: SOIL
AREA: COVER DEPLOYED: 3 25 18 RETRIEVED: 3
COUNTED BY: DLC FIELD TECHNICIANS: CE, DLC,TE
COUNTING SYSTEM I.D.: M01/D21, M02/D20 CAL. DUE: 7/17/18
AIR TEMP MIN: 29°F
26 18 CHARCOAL BKG:
DATA ENTRY BY: DLC
147
PROJECT NO.: 18004.01
WEATHER: NO RAIN
cpm Wt. Out:
TARE WEIGHT:
180.0
29.2
GRID SAMPLE DEPLOY RETRIV ANAL YSIS MID-TIME CNT GROSS GROSS RADON ± LLD
g.
g.
LOCATION I. D. HR MIN HR MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m's pCi /m2 s pCi /m2 s COMMENTS:
C75 C75 9 31 9 49 3 27 18 17 50 2 1001 217.5 0.6 0.06 0.03
C76 C76 9 30 9 49 3 27 18 18 1 4 1002 216.1 0.2 0.03 0.03
C77 C77 9 48 9 38 3 27 18 18 4 1 1543 216.8 2.5 0.25 0.03
C78 C78 9 49 9 38 3 27 18 18 5 3 1177 219.1 0.4 0.05 0.03
C79 C79 9 50 9 38 3 27 18 18 9 3 1309 214.3 0.5 0.05 0.03
C80 C80 9 51 9 39 3 27 18 18 8 1 1322 215.8 2.1 0.21 0.03
C81 C81 9 52 9 39 3 27 18 18 12 2 1248 220.6 0.9 0.09 0.03
C82 C82 9 53 9 39 3 27 18 18 13 3 1010 217.2 0.3 0.04 0.03
C83 C83 9 54 9 40 3 27 18 18 15 1 1968 220.4 3.3 0.33 0 .03
C84 C84 9 55 9 40 3 27 18 18 15 1 1528 219.6 2.5 0.25 0 .03
c05 c05 9 58 9 51 3 27 18 18 17 2 1631 219.7 1.2 0.12 0.03
C86 C86 9 59 9 51 3 27 18 18 17 1 1581 216.9 2.6 0.26 0.03
C87 C87 10 0 9 50 3 27 18 18 20 2 1577 212.7 1.2 0.12 0.03
C88 C88 10 1 9 50 3 27 18 18 20 2 1930 220.0 1.5 0.15 0.03
C89 C89 9 51 9 43 3 27 18 18 22 2 1084 215.3 0.7 0.07 0.03
C90 C90 9 52 9 43 3 27 18 18 22 2 1195 220.7 0.8 0.08 0.03
C91 C91 9 53 9 43 3 27 18 18 25 3 1311 217.0 0.5 0.05 0.03
C92 C92 9 54 9 42 3 27 18 18 25 3 1415 217.9 0.6 0.06 0.03
C93 C93 9 55 9 42 3 27 18 18 28 2 1666 217.2 1.3 0.13 0.03
C94 C94 9 56 9 42 3 27 18 18 27 1 1018 217.2 1.6 0.16 0.03
C95 C95 9 57 9 41 3 27 18 18 31 2 1195 217.2 0.8 0.08 0.03
C96 C96 9 58 9 41 3 27 18 18 31 1 1252 217.2 2.0 0.20 0.03
C97 C97 9 59 9 41 3 27 18 18 33 1 11278 216.8 20.5 2.05 0.03
C98 C98 9 53 9 44 3 27 18 18 34 2 1141 217.7 0.8 0.08 0.03
C99 C99 9 54 9 44 3 27 18 18 37 4 1047 216.8 0.2 0.04 0.03
ClOO ClOO 9 55 9 44 3 27 18 18 36 2 1354 218.9 1. 0 0.10 0.03
AVERAGE RADON FLUX RATE FOR THE CELL 2 COVER REGION: 3 .1 pCi/m2 s
0.2 MIN
BLANK CANISTER ANALYSIS: 26.4 MAX
GRID SAMPLE RETRIV ANALYSIS MID-TIME CNT GROSS GROSS RADON ± LLD
.,LOCATION I. D. HR MIN H,R MIN MO DA YR HR MIN (MIN) COUNTS WT IN pCi/m'S, pCi/m's pCi/m2 s COMMENTS:
C BLANK 1 C BLANK 1 9 15 9 25 3 27 18 10 3 10 1600 208.5 0.02 0.02 0.03 CONTROL
C BLANK 2 C BLANK 2 9 15 9 25 3 27 18 10 3 10 1763 208.2 0.05 0.02 0.03 CONTROL
C BLANK 3 C BLANK 3 9 15 9 25 3 27 18 10 14 10 1562 208.9 0.02 0.02 0.03 CONTROL
C BLANK 4 C BLANK 4 9 15 9 25 3 27 18 10 14 10 1671 208.8 0.03 0.02 0.03 CONTROL
C BLANK 5 C BLANK 5 9 15 9 25 3 27 18 10 25 10 1581 208.6 0.02 0.02 0.03 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 I 0 0 0 0 0 0 0 0 0 0 0 0 0 (01 CO2 (03 C04 cos C06 (07 COB (09 (10 (11 (12 (13
0 0 0 0 0 0 0 0 0 0 0 0 0 C21 C22 (23 C24 C25 (26 C27 C28 C29 00 01 02 03
0 0 0 0 0 0 0 0 0 0 (44 (45 (46 (47 (48 (49 (SO CSl C52 (53
-CELL2-C76 0 0 0 0 0 0 0 0 C74 C73 C72 C71 C70 (69 (68
0 0 0 (86 (85 (84
0 0 0 0 0 (14 (15 (16 (17 (18
0 0 0 0 0 04 05 06 07 08
0 0 0 0 0 (54 C55 C56 (57 (58
0 0 0 0 0 (67 (66 (65 (64 (63
0 0 0 0 0 C83 (82 (81 CBO 09
0 0 0 0 (94 (93 (92 (91
0 0 (19 C20
0 0
09 (40
0 0 (59 (60
0 0 \ (62 (61
0 0 • C78 C77
0 0
(90 (89
;
WHITE MESA MILL
BLANDING, UTAH
NESHAPS 2018
CELL2
FIRST HALF 2018
03/25/18-03/26/18
PREPARED FOR
ENERGY FUELS RESOURCES
LEGEND
(01 0 -SAMPLE LOCATION ON
COVERED AREAS
FIGURE 2
N
t
SCALE IN FEET
200 100 0 200 400
rr,,fo
ENVIRONMENTAL, LLC
THIS DRAWING IS THE PROPERTY OF TELLCO
ENVIRONMENTAL, LLC, AND IS NOTTO BE
REPRODUCED, MODIFIED OR USED FOR ANY
OTHER PROJECT OR EXTENSION OF THIS PROJECT
EXCEPT BY AGREEMENT WITH TELLCO.